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CENTRE OF ADVANCED FACULTY TRAINING<br />

IN PLANT PATHOLOGY<br />

(Indian Council <strong>of</strong> Agricultural Research, New Delhi)<br />

Proceedings <strong>of</strong> <strong>the</strong> 27 th Training<br />

on<br />

“<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong><br />

<strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens”<br />

January 22 to Februady 11, 2013<br />

Dr.. Karuna Viishunavatt,, Diirecttor,, CAFT<br />

Dr.. Yogendra Siingh,, Course Coordiinattor<br />

Dr.. R..P.. Siingh,, Co--course Coordiinattor<br />

G.B. Pant University <strong>of</strong> Agriculture and Technology<br />

Pantnagar- 263 145 (Uttarakhand)


PREFACE<br />

<strong>Plant</strong>s are constantly exposed to a wide range <strong>of</strong> fungal, bacterial and viral pathogens and globally,<br />

enormous losses <strong>of</strong> <strong>the</strong> crops are caused by plant diseases. While no overall estimation <strong>of</strong> <strong>the</strong> loss caused by<br />

soil borne plant diseases in India has been made, it must be considerable and varying from crop to crop.<br />

The future <strong>of</strong> sustainable agriculture in India will increasingly rely on <strong>the</strong> integration <strong>of</strong> biotechnology with<br />

traditional agricultural practices. Although genetic engineering promises enhanced yields and disease<br />

resistance, it is also important to recognize that plants exist in intimate associations with microorganisms,<br />

some <strong>of</strong> which cause plant disease while o<strong>the</strong>rs protect against disease. Understanding plant microbe<br />

interactions, identifying and utilizing microorganisms or microbial products to control plant disease and<br />

enhance crop production are integral parts <strong>of</strong> sustainable agriculture.<br />

In view <strong>of</strong> above, <strong>the</strong> 21 day training under Center <strong>of</strong> Advanced Faculty Training in <strong>Plant</strong> Pathology<br />

was designed to give an updated in<strong>for</strong>mation/knowledge on “<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong><br />

<strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> pathogens” to <strong>the</strong> participants, so that <strong>the</strong>y can deal with <strong>the</strong> opportunity<br />

and applicability <strong>of</strong> emerging technologies <strong>for</strong> enhancing <strong>the</strong> agricultural productivity. Excellent response<br />

was received from all over India <strong>for</strong> participation in this training. Twenty five participants representing<br />

twelve states, who actively participated in <strong>the</strong> programme, were exposed to <strong>the</strong> recent advances made<br />

towards various aspects <strong>of</strong> plant microbe interactions through series <strong>of</strong> lectures, practicals and field visits.<br />

We are grateful to <strong>the</strong> ICAR <strong>for</strong> sponsoring this 27 th advanced training programme in series, and 6 th under<br />

<strong>the</strong> banner <strong>of</strong> <strong>the</strong> newly created Centre <strong>of</strong> Advanced Faculty Training in <strong>Plant</strong> Pathology at Pantnagar. We<br />

are highly grateful to Shri. Subhash Kumar, IAS, Vice-Chancellor <strong>for</strong> his constant support, guidance and<br />

encouragement in making <strong>the</strong> training a great success. We are highly obliged to Dr. J. Kumar, Dean<br />

Agriculture <strong>for</strong> his keen interest, unending support and guidance received during <strong>the</strong> course <strong>of</strong> <strong>the</strong> training<br />

programme. We like to put on record <strong>the</strong> help and guidance received from All <strong>the</strong> Deans and Directors in<br />

<strong>the</strong> successful conduct <strong>of</strong> training programme. We sincerely acknowledge <strong>the</strong> services <strong>of</strong> our guest speakers<br />

Dr. Serge Savary, Director <strong>of</strong> Research, Phytopathologist, INRA, France; Dr. L. Willocquet, In-charge <strong>of</strong><br />

Research, Phytopathologist, INRA, France;<br />

Dr. U.S. Singh, Sought-East Asia Coordinator, IRRI, New<br />

Delhi; Dr. R.K. Khetarpal, Science Director (Asia) and Country Director (India), CABI; Dr. Rakesh<br />

Pandey, Scientist, Central Institute <strong>of</strong> Medicinal &Aromatic <strong>Plant</strong>s and Dr. Y.P. Singh, Principal Scientist,<br />

Forest Pathology Division, Forest Research Institute, Dehradun. We would like to place on record <strong>the</strong> help<br />

and logistic support received from Dr. Anjuli Agarwal, Officer In-charge, Majhera Research Station and her<br />

team and also <strong>for</strong> delivering lecture during exposure visit <strong>of</strong> participants. Several scientists from various<br />

departments such as Farm Mach.& Power Engineering; Microbiology; Biological Sciences; Molecular<br />

Biology and Genetic Engineering; <strong>Soil</strong> Science; Veterinary Anatomy; Agronomy; Agrometerology;<br />

KNSCCF and <strong>the</strong> University library in addition to <strong>the</strong> <strong>Plant</strong> Pathology rendered all possible help and<br />

delivered scientific lectures and designed practical exposure to <strong>the</strong> participants. We acknowledge <strong>the</strong>ir<br />

contributions with utmost gratitude and sincerity.<br />

.<br />

Dr. R.P. Singh Dr. Yogendra Singh Dr. K. Vishunavat<br />

Co-course Coordinator Course Coordinator Director, CAFT<br />

Pantnagar<br />

February 11, 2013


CONTENTS<br />

Sl. No. Title Speaker Page<br />

Welcome Address Dr. K. Vishunavat i-iii<br />

1. Department <strong>of</strong> <strong>Plant</strong> Pathology Dr. K. Vishunavat 1-24<br />

2. <strong>Management</strong> <strong>of</strong> Pests in Protected Cultivation- Dr. H.S. Tripathi 25-29<br />

Problems & Perspectives<br />

3. <strong>Soil</strong> Solarization <strong>for</strong> Biocontrol <strong>of</strong> <strong>Plant</strong> Pathogens Dr. Yogendra Singh 30-37<br />

4. Microbial <strong>Interactions</strong> in Phyllosphere and Dr. P.C. Srivastava 38-44<br />

Rhizosphere<br />

5. Exploiting Nematophagus Fungi <strong>for</strong> <strong>the</strong> Dr. Rakesh Pandey 45-46<br />

<strong>Management</strong> <strong>of</strong> Root-Knot Nematodes<br />

6. <strong>Soil</strong> Fertility in Organic Farming System Dr. D.K. Singh 47-56<br />

7. The Role <strong>of</strong> <strong>Soil</strong> Micr<strong>of</strong>auna in Maintaining <strong>Soil</strong> Dr. Navneet Pareek 57-60<br />

Health<br />

8. <strong>Soil</strong> Degradation- A Threat to Sustainable Dr. Ramesh Chandra 61-66<br />

Agriculture<br />

9. Role <strong>of</strong> <strong>Plant</strong> Growth Promoting Rhizobacteria in Dr. Anita Sharma 67-72<br />

Crop Improvement<br />

10. Implication <strong>of</strong> PGPR <strong>for</strong> Rhizospheric Colonization Dr. Reeta Goel 73-74<br />

and <strong>Plant</strong> Growth Promotion<br />

11. <strong>Microbe</strong>s and Intellectual Property Rights Dr. H.S. Chawla 75-79<br />

12. Induced Resistance: A Novel Strategy <strong>for</strong> <strong>Plant</strong> Dr. P.K. Shrotria 80-88<br />

Protection against Diseases<br />

13. Characterization <strong>of</strong> Macro- and Meteorological Dr. H.S. Kushwaha 89-97<br />

Variables <strong>for</strong> Disease <strong>Management</strong><br />

14. Role <strong>of</strong> Organic Amendments in <strong>the</strong> <strong>Management</strong> Dr. R.P. Singh 98-101<br />

<strong>of</strong> <strong>Soil</strong> Borne <strong>Plant</strong> Pathogens<br />

15. Evaluation and Selection <strong>of</strong> Promising Trichoderma Dr. A.K. Tewari 102-105<br />

Isolates <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong> Borne Fungal<br />

<strong>Plant</strong> Pathogens<br />

16. Biodeterioration <strong>of</strong> Seed in Storage and its Control Dr. K. Vishunavat 106-115<br />

by Microbial Antagonists<br />

17. Reduced Risk Pesticides: The Best Alternative to Dr. S.N. Tewari 116-122<br />

Ensure Food Safety without Compromising<br />

Environment Quality<br />

18. Trichoderma as Inducer <strong>of</strong> <strong>Plant</strong> Resistance to Dr. R.P. Singh 123-128<br />

Diseases<br />

19. Influence <strong>of</strong> Environmental Parameters on Dr. A.K. Tewari 129-130<br />

Trichoderma Strains with Biocontrol Potentials<br />

-i-


20. Smut Fungi: Potential Pathogens and Biocontrol Dr. K. Vishunavat 131-135<br />

Agents<br />

21. Biocontrol <strong>of</strong> Fungal Phytopathogens by Dr. Lakshmi Tewari 136-140<br />

Trichoderma spp.<br />

22. Biological Control <strong>of</strong> <strong>Plant</strong> Diseases under Different Dr. V.S. Pundhir 141-146<br />

Environments<br />

23. <strong>Microbe</strong>s and <strong>Soil</strong> Quality Dr. K.P. Raverkar 147-155<br />

24. Suppressive <strong>Soil</strong>s in <strong>Plant</strong> Disease <strong>Management</strong> Dr. K.P. Singh 156-164<br />

25. Pesticides: Past, Present and Future R.P. Srivastava 165-176<br />

26. Isolation, Identification and Quantification <strong>of</strong> Dr. Roopali Sharma 177-179<br />

Trichoderma<br />

27. Mechanism <strong>of</strong> Mycoparasitism and Antibiosis Dr. Roopali Sharma 180-183<br />

28. Mass Production and Formulation Technology <strong>of</strong> Dr. Roopali Sharma 184<br />

Trichoderma<br />

29. Identification <strong>of</strong> Pseudomonas and Bacillus isolates Dr. J. Kumar 185-187<br />

using Biolog System<br />

30. Biochemical Tests <strong>for</strong> Identification <strong>of</strong> Bacterial Dr. Yogendra Singh 188-191<br />

Pathogens<br />

31. Visit to Meteorological Observatory and Automatic Dr. H.S. Kushwaha 192-197<br />

Wea<strong>the</strong>r Station in Cropped Field at N.E.B. CRC<br />

--- i<br />

Annexure- I (Committee members)<br />

Annexure- II (List <strong>of</strong> Participants)<br />

Annexure- III (List <strong>of</strong> Speakers)<br />

Annexure- IV (Training Course Schedule)<br />

--- i-iii<br />

--- i-ii<br />

--- i-iv<br />

-ii-


WELCOME ADDRESS<br />

by<br />

Dr. K. Vishunavat<br />

Director CAFT<br />

Pr<strong>of</strong>. & Head, <strong>Plant</strong> Pathology, College <strong>of</strong> Agriculture<br />

G.B. Pant University <strong>of</strong> Agriculture & Technology, Pantnagar- 263 145<br />

on<br />

January 22, 2013<br />

Good morning and welcome to <strong>the</strong><br />

Inaugural Session <strong>of</strong> <strong>the</strong> 27 th CAFT training on<br />

“<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> Interaction <strong>for</strong><br />

<strong>Management</strong> <strong>of</strong> <strong>Soil</strong> -borne <strong>Plant</strong> Pathogens”.<br />

Dr. J.P. Singh,<br />

Director Experiment<br />

Station, Dr. Y.V Singh , acting Dean Agriculture<br />

,Dr. Y Singh, Course Coordinator <strong>of</strong> <strong>the</strong> present<br />

training, Deans and Directors, Jt. Directors,<br />

Officers, Heads <strong>of</strong> Departments, Senior faculty<br />

members, Colleagues, Staff members,<br />

<strong>the</strong><br />

trainees from different universities, Students, Press<br />

& Media, Ladies & Gentle men.<br />

It is indeed a pleasure in welcoming <strong>the</strong>, Dr<br />

J.P. Singh, Director Experiment Station and Chief<br />

Guest <strong>of</strong> <strong>the</strong> function who has consented to grace<br />

<strong>the</strong> occasion despite at a very short notice. We all<br />

are all very thankful to you.<br />

I am also pleased in welcoming Dr. Y.B<br />

Singh, acting Dean, College <strong>of</strong> Agriculture who<br />

readily agreed to grace <strong>the</strong> occasion.<br />

I would also like to welcome Dr. S.C.<br />

Saxena, a honourary faculty in <strong>the</strong> college <strong>of</strong><br />

agriculture.<br />

I welcome Dean, College <strong>of</strong> technology Jt.<br />

Director Research Dr. Ramesh Chandra who are<br />

present here in <strong>the</strong> hall and have spared <strong>the</strong>ir<br />

valuable time to grace this occasion.<br />

I also extend <strong>the</strong> warm welcome to all The<br />

Heads and faculty members <strong>of</strong> various<br />

departments who have also responded to our<br />

invitation. I welcome all <strong>of</strong> you to <strong>the</strong> function.<br />

I extend <strong>the</strong> special welcome to <strong>the</strong><br />

participants <strong>of</strong> <strong>the</strong> training programme from<br />

different universities who have traveled a long<br />

distance to reach Pantnagar.<br />

I welcome you all<br />

and assure you a com<strong>for</strong>table stay within our<br />

means.<br />

I also welcome all staff members, students,<br />

press and media and o<strong>the</strong>rs who are present in <strong>the</strong><br />

hall and have made <strong>the</strong> arrangements <strong>for</strong> this<br />

inaugural session.<br />

Ladies and gentlemen, Department <strong>of</strong><br />

<strong>Plant</strong> Pathology came into existence and<br />

accredited by ICAR as early as in 1961 just a year<br />

after <strong>the</strong> foundation <strong>of</strong> <strong>the</strong> university in 1960.<br />

The department has a bequest <strong>of</strong> having<br />

legendaries like Drs. Y.L. Nene and R.S Singh who<br />

have laid <strong>the</strong> foundation <strong>of</strong> strong commitment to,<br />

sound education, research and extension in <strong>Plant</strong><br />

Pathology at Pantnagar. Dr. Y.L. Nene, first head<br />

<strong>of</strong> <strong>the</strong> department <strong>of</strong> plant pathology, and a FAO<br />

award recipient <strong>for</strong> his out standing contribution <strong>for</strong><br />

<strong>the</strong> management <strong>of</strong> khaira disease and Dr. Singh,<br />

a prolific writer who has written 9 books in <strong>the</strong> field<br />

<strong>of</strong> <strong>Plant</strong> pathology. His book “<strong>Plant</strong> Diseases” has<br />

its 9th edition and is known as “Geeta” in plant<br />

pathology. Under <strong>the</strong> capable leadership, <strong>of</strong> <strong>the</strong>se<br />

great plant pathologists, department expanded to<br />

include many dedicated faculty members whose<br />

contributions made <strong>the</strong> department a recognized<br />

leader in <strong>the</strong> area <strong>of</strong> plant pathology in <strong>the</strong> country.<br />

With this sound background, <strong>the</strong> next<br />

generation is also attentively keeping pace with <strong>the</strong><br />

changes evolved in <strong>the</strong> modern agriculture and are<br />

focused to work on <strong>the</strong> thrust area <strong>of</strong> plant<br />

pathology.<br />

At present <strong>the</strong> department includes 08<br />

pr<strong>of</strong>essors, one honorary pr<strong>of</strong>essor from INRA,<br />

France, 06 Associate Pr<strong>of</strong>essors and 06 Assistant<br />

Pr<strong>of</strong>essors with 18 technical and 5 supporting<br />

-i-


staffs. The entire fraternity <strong>of</strong> plant pathology is<br />

committed <strong>for</strong> Department’s education, research<br />

and extension programme.<br />

The department has a well-knit under<br />

graduate (U.G.) and post graduate (P.G.)<br />

programme with updated course curricula. It <strong>of</strong>fers<br />

six U.G. and thirty six P.G. courses. The great<br />

diversity <strong>of</strong> areas <strong>of</strong> expertise and interests present<br />

in <strong>the</strong> Department leads to diversity in <strong>the</strong>sis titles.<br />

So far almost 335 M.Sc. and 198 Ph.D. students<br />

have earned degrees from <strong>the</strong> Department.<br />

The department is actively engaged in <strong>the</strong><br />

research work on both fundamental and applied<br />

aspects in <strong>the</strong> domains <strong>of</strong> ecology <strong>of</strong> soil borne<br />

plant pathogens, epidemiology and <strong>for</strong>ecasting,<br />

biological control and IPM, molecular diagnostics,<br />

pathogen population biology, disease resistance,<br />

seed pathology, fungicides, nematology,<br />

phytovirology, phytobacteriology and biology &<br />

technology <strong>of</strong> mushroom production.<br />

The distinguished faculty <strong>of</strong> <strong>the</strong> department<br />

has brought in a number <strong>of</strong> national and<br />

international research grants besides a series <strong>of</strong><br />

AICRPs. For a number <strong>of</strong> AICRPs such as those <strong>of</strong><br />

Oilseeds, Potato, Seeds, and maize, <strong>the</strong> faculty<br />

members <strong>of</strong> <strong>the</strong> department render services as <strong>the</strong><br />

Project Coordinators also.<br />

Individual staff members with in <strong>the</strong><br />

department have long been recognized <strong>for</strong> <strong>the</strong>ir<br />

leadership role in <strong>the</strong> science <strong>of</strong> <strong>Plant</strong> Pathology.<br />

By way <strong>of</strong> <strong>the</strong>ir significant contributions, faculty<br />

members <strong>of</strong> this department have been assigned<br />

to work at national level. Many <strong>of</strong> <strong>the</strong> faculty<br />

members have earned International positions.<br />

Also a number <strong>of</strong> faculty members have served as<br />

president, vice presidents, and zonal president <strong>of</strong><br />

several pr<strong>of</strong>essional societies.<br />

Over <strong>the</strong> years, <strong>the</strong> plant pathology faculty<br />

members and students have won over 40 national<br />

and international awards.<br />

The Department has a unique<br />

distinction <strong>of</strong> producing 60 books, both in Hindi and<br />

English published not only by Indian but also<br />

reputed international publishers, besides a series<br />

<strong>of</strong> technical bulletins, working sheets, lab manuals,<br />

compendia and extension literature.<br />

The Department has a molecular and<br />

referral lab <strong>for</strong> quality evaluation <strong>of</strong> biocontrol<br />

agents notified by central insecticide board in<br />

respect to bio-pesticides. Similarly, <strong>the</strong> Department<br />

also holds strength in mushroom research and<br />

trainings.<br />

The contributions made towards teaching,<br />

research and extension by <strong>the</strong> department is<br />

recognized by ICAR and in 1995, ICAR upgraded<br />

<strong>the</strong> department to <strong>the</strong> status <strong>of</strong> CAS in <strong>Plant</strong><br />

Pathology and subsequently to CAFT in 2009 with<br />

<strong>the</strong> major mandate to train scientific faculty from all<br />

over <strong>the</strong> country in important and innovative areas<br />

<strong>of</strong> <strong>Plant</strong> Pathology. So far 26 trainings have been<br />

conducted and 534 scientists from 25 states have<br />

participated.<br />

The topic <strong>of</strong> <strong>the</strong> present training “<strong>Managing</strong><br />

<strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong><br />

<strong>Soil</strong>-borne <strong>Plant</strong> Pathogens” under CAFT is well<br />

thought <strong>of</strong> in <strong>the</strong> present agriculture scenario<br />

where <strong>the</strong> cost <strong>of</strong> soil borne plant pathogens to<br />

society and <strong>the</strong> environment far exceeds <strong>the</strong> direct<br />

costs to growers and consumers. The use <strong>of</strong><br />

chemical pesticides to control soil borne pathogens<br />

has caused significant changes in air and water<br />

quality, altered natural ecosystems resulting in<br />

direct and indirect affects on wildlife, and caused<br />

human health problems.<br />

Yield failures due to acute soil borne<br />

diseases such, vascular wilts, take-all disease in<br />

cereals, root rots, scab and nematode diseases<br />

have been even more severe and at times may<br />

even destroy entire agriculture industries.<br />

<strong>Soil</strong> borne plant pathogens are complex<br />

not only in <strong>the</strong>ir behavioral pattern but also in <strong>the</strong>ir<br />

biochemical constituents. It becomes still complex<br />

when soil microbial inhabitants interact with <strong>the</strong>se<br />

plant pathogens. The level <strong>of</strong> this interaction is also<br />

influenced by soil conditions such as soil structure,<br />

pH, moisture, oxygen, nutrients, cropping pattern,<br />

and o<strong>the</strong>r intrinsic factors which affect <strong>the</strong> growth<br />

and activity <strong>of</strong> <strong>the</strong> non-pathogenic organisms.<br />

Consequently, whenever <strong>the</strong> soil environment<br />

changes, <strong>the</strong>re is potential <strong>for</strong> ei<strong>the</strong>r a positive or<br />

negative influence on soil-borne plant pathogens.<br />

-ii-


Hence, it is not very easy to control <strong>the</strong>se<br />

pathogens. Understanding and dealing with soil<br />

borne pathogens is a very difficult and challenging<br />

task.<br />

A natural soil system is a reservoir <strong>of</strong><br />

millions <strong>of</strong> microorganisms which constantly<br />

communicate with each o<strong>the</strong>r and maintain life's<br />

processes in an orderly way. The management <strong>of</strong><br />

plant pathogens by naturally occurring<br />

microorganisms in an agro-ecosystem has existed<br />

long be<strong>for</strong>e as <strong>the</strong> crop cultivation started. There<br />

are many diverse groups <strong>of</strong> microorganisms in soil.<br />

<strong>Soil</strong> microbial diversity confers protection against<br />

soil borne plant diseases. However, in practice, <strong>the</strong><br />

ground reality is very different. The health status <strong>of</strong><br />

<strong>the</strong> soil is constantly under threat due to <strong>the</strong><br />

repeated use <strong>of</strong> chemicals and crop cultivation<br />

patterns which ultimately reduce <strong>the</strong> immunity <strong>of</strong><br />

<strong>the</strong> plants towards diseases. The population <strong>of</strong><br />

pathogens when multiply beyond <strong>the</strong> thresh hold<br />

level create macro imbalances resulting in disease<br />

development and loss <strong>of</strong> productivity. An<br />

understanding <strong>of</strong> <strong>the</strong> interactions which occur<br />

among different groups <strong>of</strong> soil flora and fauna may<br />

help to manipulate <strong>the</strong>m in a manner which<br />

achieves favorable effects on plant growth.<br />

At <strong>the</strong> time when <strong>the</strong>re is growing demand<br />

to do away with chemical, due to many problems<br />

such as pests developing resistance, resurgence<br />

<strong>of</strong> once minor pest into a major problem,<br />

environmental and food safety hazards, and an<br />

adverse effects on <strong>the</strong> non target organisms (such<br />

as pollinators, parasitoids, predators and wild<br />

animals), Identifying, understanding and utilizing<br />

microorganisms or microbial products to control<br />

plant disease and enhance crop production are<br />

becoming more central parts <strong>of</strong> sustainable<br />

agriculture.<br />

Biologically-based pest management <strong>of</strong>fers<br />

potential management <strong>of</strong> soil borne disesase while<br />

causing no or minimal detrimental environmental<br />

impact. Biological control practices need an<br />

integrative approach, and more knowledge than<br />

chemical control. Some <strong>of</strong> <strong>the</strong> benefits <strong>of</strong> utilizing<br />

microorganisms include: reduced dependence on<br />

chemical pesticides, lack <strong>of</strong> development <strong>of</strong><br />

pathogen resistance to biological control<br />

organisms, more selective action against<br />

pathogens and not against beneficial organisms;<br />

biodegradability <strong>of</strong> microbial pesticides and <strong>the</strong>ir<br />

by-products; reduced danger to humans or<br />

animals; improvement <strong>of</strong> soil quality and health;<br />

increased food safety; long term solutions <strong>for</strong><br />

management <strong>of</strong> soil-borne pathogens; and<br />

management <strong>of</strong> plant diseases in natural<br />

ecosystems.<br />

Bioagents can be introduced in an attempt<br />

to control diseases. This can be done by way <strong>of</strong><br />

organic amendments that stimulate <strong>the</strong> naturally<br />

occurring antagonists or by integrating microbial<br />

populations by way <strong>of</strong> natural organic fertilizers<br />

with microbial supplements. In both cases, <strong>the</strong><br />

products are applied prior to disease development<br />

as <strong>the</strong>y are preventive and not curative.<br />

Biological control <strong>of</strong> soil borne plant<br />

pathogens is though a slow and deliberate<br />

process, but <strong>the</strong> results are more stable, consistent<br />

and lasting compared to <strong>the</strong> chemical control.<br />

However, issues such as method <strong>of</strong> application,<br />

<strong>for</strong>mulation <strong>of</strong> biocontrol microorganisms and<br />

timing <strong>of</strong> application need to be given emphasis.<br />

Though, <strong>the</strong> complexity <strong>of</strong> plant–soil–<br />

microbial interactions is so varied, that a complete<br />

understanding <strong>of</strong> all <strong>the</strong> relationships involved is<br />

unlikely to be achieved. Never<strong>the</strong>less, <strong>the</strong><br />

consequences <strong>of</strong> beneficial biological interactions<br />

that stimulate crop yields and improve plant health<br />

can be evaluated relatively simply and a number <strong>of</strong><br />

general management strategies can be devised,<br />

accordingly.<br />

I will not go much into <strong>the</strong> details about <strong>the</strong><br />

topic because it would be introduced to more<br />

elaborately by Dr. J.P. Singh, Chief Guest <strong>of</strong> <strong>the</strong><br />

function.<br />

With <strong>the</strong>se words I welcome you all and<br />

assure a fruitful and com<strong>for</strong>table stay to <strong>the</strong><br />

participants <strong>of</strong> this 27th training programme <strong>of</strong><br />

CAFT in <strong>Plant</strong> Pathology.<br />

Thank you very much!<br />

* * * * * * * * *<br />

-iii-


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

DEPARTMENT OF PLANT PATHOLOGY<br />

Establishment <strong>of</strong> University – 1960<br />

Department created and Accredited – 1961<br />

M. Sc. (Ag) Programme – 1963<br />

Ph. D. Programme – 1965<br />

Courses<br />

Staff position<br />

Ist course – Introductory <strong>Plant</strong> Pathology<br />

Ist Instructor – Dr. Y. L. Nene<br />

Ist HOD – Dr. Y. L. Nene<br />

06 UG courses<br />

37 PG courses<br />

08 Pr<strong>of</strong>essor<br />

02 Honorary Pr<strong>of</strong>essor<br />

06 Associate Pr<strong>of</strong>essor<br />

06 Assistant Pr<strong>of</strong>essor<br />

01 Subject Matter Specialist<br />

18 Technical staff<br />

05 Supporting staff<br />

The G.B. Pant University <strong>of</strong> Agriculture & Technology (earlier known as U.P. Agriculture<br />

University) was established in 1960. Department <strong>of</strong> <strong>Plant</strong> pathology was created and accredited by ICAR<br />

in 1961. The postgraduate degree programme leading to M.Sc. (Ag.) <strong>Plant</strong> Pathology and Ph.D. <strong>Plant</strong><br />

Pathology were started in 1963 and 1965, respectively.<br />

Faculty <strong>of</strong> <strong>Plant</strong> Pathology is highly qualified and includes 08 pr<strong>of</strong>essors, 02 Honorary Pr<strong>of</strong>essor,<br />

06 Associate Pr<strong>of</strong>essor, 06 Assistant Pr<strong>of</strong>essor and 01 Subject Matter Specialist with 18 technical staff<br />

and 05 supporting staffs.<br />

Sl. No. Name <strong>of</strong> Faculty members Designation Area <strong>of</strong> specialization<br />

1 Dr. (Mrs. ) Karuna<br />

Vishunavat<br />

Pr<strong>of</strong>.&Head-cum-<br />

Director, CAFT<br />

2 Dr. J. Kumar Pr<strong>of</strong>essor & Dean<br />

Agriculture<br />

Seed Pathology<br />

<strong>Plant</strong> disease management<br />

on small farm, IPM, Biological<br />

control, Pathogen population<br />

biology.<br />

3 Dr. R.P. Awasthi Pr<strong>of</strong>essor Oilseed crop diseases<br />

4 Dr. K.S. Dubey Pr<strong>of</strong>essor Soybean diseases<br />

- 1 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

5 Dr. V.S. Pundhir Pr<strong>of</strong>essor Potato Pathology &<br />

Epidemiology <strong>of</strong> Crop Disease<br />

6 Dr. Pradeep Kumar Pr<strong>of</strong>essor Maize Pathology & Fruit<br />

Pathology<br />

7 Dr. R.K. Sahu Pr<strong>of</strong>essor Sugarcane Pathology<br />

8 Dr. K.P. Singh Pr<strong>of</strong>essor Epidemiology & <strong>Management</strong><br />

<strong>of</strong> Pulse Diseases<br />

9 Dr. S.C. Saxena Honorary Pr<strong>of</strong>essor Maize Pathology<br />

10 Dr. Sergey Savary Honorary Pr<strong>of</strong>essor Epidemiology<br />

11 Dr. Vishwanath Associate Pr<strong>of</strong>essor Soybean Pathology &<br />

Rapeseed Mustard diseases<br />

12 Dr. Yogendra Singh Senior Research<br />

Officer<br />

13 Dr. R.P. Singh Senior Research<br />

Officer<br />

14 Dr. K.P.S. Kushwaha Senior Research<br />

Officer<br />

15 Dr. A.K. Tewari Senior Research<br />

Officer<br />

Sorghum diseases<br />

16 Dr. Satya Kumar Associate Pr<strong>of</strong>essor Nematology<br />

17 Dr. L.B. Yadav Assistant Pr<strong>of</strong>essor Mycology<br />

Microbial ecology, fungicides<br />

& Vegetable Pathology<br />

Pulse Pathology, Mycology<br />

(Mushroom)<br />

Oilseed crops diseases & Biocontrol<br />

18 Dr. (Mrs.) Roopali Sharma Junior Research<br />

Officer<br />

19 Dr. Bijendra Kumar Junior Research<br />

Officer<br />

20 Dr. S.K. Mishra Junior Research<br />

Officer<br />

21 Dr. (Mrs.) Deepshikha Junior Research<br />

Officer<br />

22 Dr. (Mrs.) Geeta Sharma Junior Research<br />

Offcer<br />

23 Dr. (Mrs.) N. W. Zaidi Subject Matter<br />

Specialist (on EOL)<br />

Biological control, IPM<br />

Technology<br />

Small Millets Pathology<br />

Mushroom Biotechnology and<br />

Mushroom Biology<br />

Wheat diseases<br />

Mushroom Breeding, its<br />

Diseases & spawn production<br />

Biological control <strong>of</strong> plant<br />

disease & IPM<br />

TEACHING<br />

The department <strong>of</strong> plant pathology has made immense contribution in <strong>the</strong> area <strong>of</strong> teaching,<br />

research and extension. A well-knit UG and PG programme with updated and modern syllabi is<br />

already in operation in <strong>the</strong> department. The department <strong>of</strong>fers 6 courses <strong>for</strong> undergraduate<br />

students. There are 37 postgraduate courses leading to M.Sc. (Ag.) and Ph.D. degrees in <strong>Plant</strong><br />

Pathology. Since <strong>the</strong> inception <strong>of</strong> <strong>the</strong> department 335 M.Sc. (Ag.) and 198 Ph.D. students have<br />

- 2 -


een awarded degrees.<br />

Under graduate courses<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Sl. No. Course N0. Course name Credit<br />

1. APP-312 Introductory <strong>Plant</strong> Pathology 3(2-0-3)<br />

2. APP-314 Crop Diseases & <strong>the</strong>ir <strong>Management</strong> 2(1-0-3)<br />

3. APP-330 Diseases <strong>of</strong> Fruit and Vegetable Crops 2(1-0-3)<br />

4 APP/APE-322 Integrated Pest & Disease <strong>Management</strong> 2(1-0-3)<br />

5. APP-381 Mushroom Cultivation 1(0-0-1x2)<br />

6. APP-382 Biological Control <strong>of</strong> <strong>Plant</strong> Pathogens 2(0-0-2x2)<br />

Post graduate courses<br />

Sl. No. Course No. Course name Credit<br />

1. APP-401 Introductory <strong>Plant</strong> Pathology 3(2-0-1)<br />

2. APP-410 Diseases <strong>of</strong> Field Crops 3(2-0-1)<br />

3. APP-430 Diseases <strong>of</strong> Horticultural Crops 3(2-0-1)<br />

4 APP-507 Disease <strong>of</strong> Field and Medicinal <strong>Plant</strong>s 3(2-0-1)<br />

5. APP-508 Disease <strong>of</strong> Fruits, and Ornamental Crops 3(2-0-1)<br />

6. APP-509 Disease <strong>of</strong> Vegetable and Spice Crops 3(2-0-1)<br />

7. APP/ENT- 514 Insects Vector <strong>of</strong> <strong>Plant</strong> Viruses and o<strong>the</strong>r 2(1-0-1)<br />

Pathogens<br />

8. APP-515 Biological Control <strong>of</strong> <strong>Plant</strong> Diseases 3(2-0-1)<br />

9. APP-516 Integrated Disease <strong>Management</strong> 3(2-0-1)<br />

10. APP-517 Mushroom Production Technology 3(2-0-1)<br />

11. APP-519 Post Harvest Diseases 3(2-0-1)<br />

12. APP/ENT-520 <strong>Plant</strong> Quarantine 2(2-0-0)<br />

13. BBB-599 Mycology 3(2-0-1)<br />

14. APP-600 Master’s Seminar 1(0-0-1)<br />

15. APP-601 Special Problem 1<br />

16. APP-602 <strong>Plant</strong> Virology 3(2-0-1)<br />

17. APP-603 <strong>Plant</strong> Bacteriology 3(2-0-1)<br />

18. APP-604 Principles <strong>of</strong> <strong>Plant</strong> Pathology 3(3-0-0)<br />

19. APP-606 Principles <strong>of</strong> <strong>Plant</strong> Disease <strong>Management</strong> 3(2-0-1)<br />

20. APP-607 <strong>Plant</strong> Biosecurity and Biosafety 2(2-0-0)<br />

21. APP-611 Chemicals in <strong>Plant</strong> Disease <strong>Management</strong> 3(2-0-1)<br />

22. BBB-615 Advanced Mycology 3(2-0-1)<br />

23. APP-616 Advanced <strong>Plant</strong> Virology 3(2-0-1)<br />

24. APP-617 Advanced Bacteriology 3(2-0-1)<br />

25. APP-618 Principles and Procedures <strong>of</strong> Certification 1(1-0-0)<br />

26. APP-622 Techniques in Phytonematology 1(0-0-1)<br />

27. APP-624 Cultural & Chemical Control <strong>of</strong> <strong>Plant</strong> Parasitic 2(1-0-1)<br />

Nematodes<br />

28. APP-630 Phytonematology 2(1-0-1)<br />

29. APP-690 Master’s Thesis Research 20<br />

30. APP-704 Molecular Basis <strong>of</strong> Host Pathogen Interaction 3(2-0-1)<br />

31. APP-710 Seed Health Technology 3(2-0-1)<br />

32. APP-712 Ecology <strong>of</strong> <strong>Soil</strong>borne <strong>Plant</strong> Pathogens 3(2-0-1)<br />

33. APP-713 Disease Resistance in <strong>Plant</strong>s 2(2-0-0)<br />

34. APP-718 Epidemiology and Forecasting <strong>of</strong> <strong>Plant</strong> 3(2-0-1)<br />

Diseases<br />

35. APP-788 Doctoral Seminar I 1(0-0-1)<br />

- 3 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

36. APP-789 Doctoral Seminar II 1(0-0-1)<br />

37. APP-790 Ph.D. Thesis Research 45<br />

Books Published<br />

The department has unique distinction <strong>of</strong> producing 33 books published by not only Indian<br />

but also reputed international publishers like Elsevier Science (UK), Gordon and Beach (UK),<br />

Prentice Hall (USA), CRC Press (USA), Science Publisher (USA), Lewis Publishers (USA) etc.<br />

The Department has produced 17 text books in Hindi and has also published 13 technical<br />

bulletins. The faculty members have written/prepared several laboratory manuals, reference<br />

books, working sheets on diseases, bulletins, extension pamphlets, etc. <strong>for</strong> <strong>the</strong> benefit <strong>of</strong> U.G. and<br />

P.G. students <strong>of</strong> plant pathology as well as <strong>for</strong> <strong>the</strong> farmers.<br />

• <strong>Plant</strong> Disease 8 th Edition by R.S. Singh<br />

• An Introduction to Principles <strong>of</strong> <strong>Plant</strong> Pathology 4 th Edition by R.S. Singh<br />

• <strong>Plant</strong> Pathogens: The Fungi by R.S. Singh<br />

• <strong>Plant</strong> Pathogens: The Viruses & Viroids by R.S. Singh<br />

• <strong>Plant</strong> Pathogens: The Prokaryotes by R.S. Singh<br />

• Integrated Disease <strong>Management</strong> by R.S. Singh<br />

• Diseases <strong>of</strong> Fruit Crops by R.S. Singh<br />

• Fungicides in <strong>Plant</strong> Disease Control by P.N. Thapliyal and Y.L. Nene<br />

• Diseases <strong>of</strong> Annual Edible Oilseed Crops Vol.-I by S.J. Kolte<br />

• Diseases <strong>of</strong> Annual Edible Oilseed Crops Vol.-II by S.J. Kolte<br />

• Diseases <strong>of</strong> Annual Edible Oilseed Crops Vol.-III by S.J. Kolte<br />

• Diseases <strong>of</strong> Linseed & Fibre Flex by S.J. Kolte<br />

• Castor Diseases & Crop Improvement by S.J. Kolte<br />

• <strong>Plant</strong> Diseases <strong>of</strong> International Importance Vol.I: Diseases <strong>of</strong> Cereals & Pulses by<br />

U.S. Singh, A. N. Mukhopadhyay, J. Kumar, and H.S. Chaube<br />

• <strong>Plant</strong> Diseases <strong>of</strong> International Importance Vol.II: Diseases <strong>of</strong> Vegetables & Oil Seed<br />

Crops by H.S. Chaube, U.S. Singh, A. N. Mukhopadhyay & J. Kumar<br />

• <strong>Plant</strong> Diseases <strong>of</strong> International Importance Vol.III: Diseases <strong>of</strong> Fruit Crops by Drs. J.<br />

Kumar, H.S. Chaube, U. S. Singh & A. N. Mukhopadhyay<br />

• <strong>Plant</strong> Diseases <strong>of</strong> International Importance Vol.IV: Diseases <strong>of</strong> Sugar, Forest &<br />

<strong>Plant</strong>ation Crops A. N. Mukhopadhyay, J. Kumar, H.S. Chaube & U.S. Singh<br />

• Pathogenesis & Host Specificity in <strong>Plant</strong> Diseases Vol.I: Prokaryotes by U. S. Singh,<br />

Keisuke Kohmoto and R. P. Singh<br />

• Pathogenesis & Host Specificity in <strong>Plant</strong> Diseases Vol. II: Eukaryotes by Keisuke<br />

Kohmoto, U.S. Singh and R. P. Singh<br />

• Pathogenesis & Host Specificity in <strong>Plant</strong> Diseases Vol. III: Viruses & Viroids by R. P.<br />

Singh, U.S. Singh and Keisuke Kohmoto.<br />

- 4 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Aromatic Rices by R.K. Singh, U.S. Singh and G. S. Khush<br />

• A Treatise on <strong>the</strong> Scented Rices <strong>of</strong> India by R.K. Singh and U.S. Singh<br />

• Scented Rices <strong>of</strong> Uttar Pradesh & Uttaranchal by R. K. Singh and U.S. Singh<br />

• <strong>Plant</strong> Disease <strong>Management</strong> : Principles & practices by H.S. Chaube and U.S. Singh<br />

• Molecular Methods in <strong>Plant</strong> Pathology by R. P. Singh and U.S. Singh<br />

• <strong>Soil</strong> Fungicides Vol.-I by A.P. Sinha and Kishan Singh<br />

• <strong>Soil</strong> Fungicides Vol.-II by A.P. Sinha and Kishan Singh<br />

• Experimental & Conceptual <strong>Plant</strong> Pathology Vol.I: Techniques by R.S. Singh, U. S.<br />

Singh, W.M. Hess & D.J. Weber<br />

• Experimental & Conceptual <strong>Plant</strong> Pathology Vol. II: Pathogenesis and Host<br />

Specificity by R.S. Singh, U. S. Singh, W.M. Hess & D.J. Weber<br />

• Experimental & Conceptual <strong>Plant</strong> Pathology Vol.III: Defense by R.S. Singh, U. S.<br />

Singh, W.M. Hess & D.J. Weber<br />

• Seed Pathology, 2 volumes by V.K. Agarwal<br />

• Phytopathological Techniques by K. Vishunavat and S.J. Kolte<br />

• Crop Diseases & Their <strong>Management</strong> by H.S. Chaube & V.S. Pundhir<br />

• Seed borne diseases <strong>of</strong> crops & <strong>the</strong>ir management by V.K. Agrawal & Y.L. Nene<br />

• <strong>Plant</strong> Pathogens: <strong>the</strong> Nematodes by R.S. Singh<br />

• Disease <strong>of</strong> vegetables crops by R.S. Singh<br />

• Introductory <strong>Plant</strong> Pathology by H.S. Chaube & Ram Ji Singh<br />

• Seed Health Testing: Principles and Protocols by Karuna Vishunavat<br />

• Fundamentals <strong>of</strong> Seed Pathology by Karuna Vishunavat<br />

• Mushroom Production Technology by R.P. Singh & H.S. Chaube<br />

• The Elements <strong>of</strong> <strong>Plant</strong> Virology: Basic concepts and practical class exercises by S.J.<br />

Kolte & A.K. Tewari<br />

• A text book <strong>of</strong> Comprehensive <strong>Plant</strong> Pathology by Karuna Vishunavat and S.J. Kolte<br />

• Ec<strong>of</strong>riendly Innovative Approaches in <strong>Plant</strong> Disease <strong>Management</strong> by V.K. Singh, Y.<br />

Singh and A. Singh (2012)<br />

Books in Hindi<br />

• lfCt;ksa ds jksx& th0 ,l0 nwcs] vesfjdk flag ¼1976½<br />

• Qlyksa ds jksx &,0,u0 eq[kksik/;k;] vkj0 ,0 flag ¼1976½<br />

• Qyksa ds jksx& ih0 ,u0 Fkify;ky] ,l0 ih0 ,l0 csuhoky ¼1976½<br />

• ikS/kksa ds jksx &vkj0 ,l0 flag ¼1976½<br />

• doduk'kh ,oa ikni jksx fu;a=.k& okbZ0 ,y0 uSu (1976)<br />

• Qlyksa ds jksxksa dh jksdFkke& laxeyky ¼1984½<br />

- 5 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• e'k:e mRiknu rduhdh& vkj0 ih0 flag] v”kksd pkS/kjh] iznhi dqekj ¼1997½<br />

• feysV ds jksx&,0 ih0 flUgk ,oa ts0 ih0 mik/;k; (1997)<br />

• lfCt;ksa ds jksx& ,l0 ,u0 fo”odekZ] ,p0 ,l0 pkSos ,oa ,0ih0 flUgk (2003)<br />

• Qyksa ds jksx & ,l0 ,u0 fo”odekZ ¼2006½<br />

• lfCt;ksa ds jksxksa dh jksdFkke & ,l0 ,u0 fo'odekZ ¼2000½<br />

• cht jksx foKku& oh0 ds0 vxzoky ¼1999½<br />

• eDdk ds jksx& laxe yky ¼1993½<br />

• /kku ds jksx & vkj0 ,0 flag ,oa ts0 lh0 HkV~V ¼1995½<br />

• Qly&lCth&Qy jksx] igpku ,oa izcU/k & ;ksxsUnz flag ,oa vf[kys'k flag<br />

• O;ogkfjd e”k:e mRiknu & ds0ih0,l0 dq”kokgk] ds0ds0 feJk<br />

• lfCt;ksa ds izeq[k jksx ,oa mudk izcU/ku&“kksHkukFk fo”odekZ<br />

Manuals<br />

• Chemicals in <strong>Plant</strong> Disease Control by Y.L. Nene, R.K. Tripathi, P.N. Thapliyal & S.C.<br />

Saxena (1974)<br />

• <strong>Management</strong> <strong>of</strong> <strong>Soil</strong> Borne <strong>Plant</strong> Diseases by R.S. Singh (1980)<br />

• Biocontrol <strong>of</strong> Fungal <strong>Plant</strong> Disease by A.N. Mukhopadhyay, H.S. Chaube, U.S. Singh &<br />

S.C. Saxena (1994)<br />

• Identification <strong>of</strong> <strong>Plant</strong> Diseases and <strong>the</strong>ir Control by A. N. Tewari (2000)<br />

• Epidemiology in <strong>Plant</strong> Diseases by V.S. Pundhir (2000)<br />

• Disease resistance in plants by V.S. Pundhir (2001)<br />

• Seed Pathology: A Practical Manual by K. Vishunavat (2002)<br />

• Laboratory Methods in <strong>Plant</strong> Pathology by Pradeep Kumar, Y.P.S. Rathi, & H.S. Tripathi<br />

(2002)<br />

• Phytovirology: Laboratory Manual by Y.P.S. Rathi, H.S. Tripathi & Pradeep Kumar<br />

(2002)<br />

• Diagnosis <strong>of</strong> <strong>Plant</strong> Diseases by A.N. Tewari (2002)<br />

• Identification <strong>of</strong> <strong>Plant</strong> Disease by A.N. Tewari (2003)<br />

• Introductory <strong>Plant</strong> Pathology (UG) by Y.P.S. Rathi, P. Kumar, & H.S. Tripathi (2003)<br />

• Diagnosis <strong>of</strong> <strong>Plant</strong> Diseases: Laboratory Manual by A.N. Tewari (2004)<br />

• Mushroom Cultivation: Laboratory Manual by R.P. Singh (2004)<br />

• Crop Diseases and <strong>the</strong>ir <strong>Management</strong> by H.S. Chaube, V.S. Pundhir & S.N.<br />

Vishwakarma (2004)<br />

- 6 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Laboratory Manual <strong>of</strong> Forest Pathology by K. P.Singh, J. Kumar and P. Srinivas (2007)<br />

• Integrated Pest <strong>Management</strong> by Ruchira Tiwari, S.C.Saxena and Akhilesh Singh (2008)<br />

Technical Bulletins<br />

• Ascochyta blight <strong>of</strong> chickpea by H.S. Chaubey (1987)<br />

• Botrytis grey mold <strong>of</strong> chickpea: survival and management by Y.P.S. Rathi and H.S.<br />

Tripathi (1993)<br />

• Studies on sterility mosaic <strong>of</strong> pegion pea (Cajanus cajan (L) Millsp.) by Y.P.S. Rathi<br />

(1983)<br />

• Studies on Fusarium by R.S. Singh (1975)<br />

• Epidemiology and management <strong>of</strong> karnal bunt disease <strong>of</strong> wheat by Amerika Singh<br />

(1994)<br />

• <strong>Plant</strong> parasitic soil nematodes <strong>of</strong> India by K. Sitaramaiah, R.S. Singh, K.P. Singh and<br />

R.A. Sikora (1971)<br />

• False smut <strong>of</strong> rice by R.A. Singh (1984)<br />

• Disease controling potential <strong>of</strong> some fungicides in soil as affected by Physicochemical<br />

biological factors (IV volumes) by H.S. Chaube et al. (1993)<br />

• A Handbook on Scientific Writing by Y.P. S. Rathi (1998)<br />

• Major Diseases <strong>of</strong> Soybean and <strong>the</strong>ir <strong>Management</strong> by Pradeep Kumar and Y.P.S. Rathi<br />

(2005)<br />

• Disease Free Seed Production <strong>of</strong> Soybean by K. Vishunavat (2002)<br />

• Indian Minimum Seed Certification Standards by K. Vishunavat, K., R.S. Verma, P. K.<br />

Shrotria, S.N. Tiwari, and Omvati Verma (2003)<br />

• Studies on Epidemiology and <strong>Management</strong> <strong>of</strong> Rust <strong>of</strong> Field Pea by H.S. Tripathi (2003)<br />

Extension Bulletin<br />

• Crop Diseases: Farmers Question and our Answer- H.S. Chaube<br />

• Qlyksa ds jksx% fdlkuksa ds iz'u gekjs mRrj& ,p0 ,l0 pkScs<br />

• [kjhQ Qlyksa dh mUur [ksrh ,oe~ vU; d`f"k O;olk;&ds- ih- flag ¼2008½<br />

• jch Qlyksa dh mUur [ksrh ,oe~ vU; d`f"k O;olk;&ds- ih- flag ¼2008½<br />

• /kku dh [ksrh esa ,dhd`r uk'khtho izcU/k& ;w0 ,l0 flag<br />

• e`nk lkSjhdj.k& ,p0 ,l0 pkScs ,oa ,l0 ,u0 fo'odekZ<br />

• lsc ds eq[; jksx dhV ,oa mudk lesfdr izcU/ku& ds0 ih0 flag ,oa ts0 dqekj<br />

• lfCt;ksa esa lesfdr uk'khtho izcU/ku& ts0 dqekj<br />

RESEARCH<br />

Research work in <strong>the</strong> department began since <strong>the</strong> inception <strong>of</strong> <strong>the</strong> University. With <strong>the</strong><br />

addition <strong>of</strong> new programme and staff strength, <strong>the</strong> research activities got diversified<br />

- 7 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

encompassing, Ecology <strong>of</strong> soil borne plant pathogens, Epidemiology and Forecasting, Biological<br />

control and IPM, Molecular Biology and Population Biology, Seed Pathology, Fungicides,<br />

Nematology, Phytovirology, Phytobacteriology and Biology & Technology <strong>of</strong> Mushroom<br />

Production. The department has several research projects funded by national and international<br />

funding agencies. The department is guiding <strong>the</strong> research work at <strong>the</strong> regional station such as<br />

Bharsar, Kashipur, Lohaghat, Majhera and Ranichauri on pathological aspects. The scientists <strong>of</strong><br />

<strong>the</strong> department have won many national and international awards.<br />

The department is actively engaged in <strong>the</strong> research work on both fundamental and applied<br />

aspects in frontier areas <strong>of</strong> plant pathology. The plant protection technology developed by <strong>the</strong><br />

department is being effectively communicated to <strong>the</strong> farming community <strong>of</strong> state <strong>of</strong> Uttarakhand.<br />

The department has to cater <strong>the</strong> needs <strong>of</strong> not only farmers <strong>of</strong> <strong>the</strong> plain but also <strong>of</strong> hills located at<br />

different altitudes. In hills crops, diseases and cropping practices vary a lot depending on altitudes<br />

and <strong>the</strong>y are quite different from plain. This <strong>of</strong>fers a big challenge to <strong>the</strong> Centre <strong>of</strong> Advanced<br />

Faculty Training in <strong>Plant</strong> Pathology.<br />

Significant Contribution<br />

• Cause and control <strong>of</strong> Khaira disease <strong>of</strong> rice<br />

• Development <strong>of</strong> selective media <strong>for</strong> isolation and enumeration <strong>of</strong> Pythium and Fusarium<br />

• Mechanism <strong>of</strong> biological control in soil amended with organic matters<br />

• Biology and characterization <strong>of</strong> legume viruses<br />

• Ecology <strong>of</strong> soil – borne pathogens (Fusarium, Pythium, Rhizoctonia solani, Sclerotium r<strong>of</strong>sii)<br />

• Mechanism <strong>of</strong> absorption, translocation and distribution <strong>of</strong> fungicides in plants<br />

• Methods <strong>for</strong> quantitative estimation <strong>of</strong> fungicides like metalaxyl, organotin compounds, carbendazim<br />

etc.<br />

• Hormonal action <strong>of</strong> fungicides<br />

• Phenolics in <strong>Plant</strong> disease resistance<br />

• Biological control with introduced antagonists<br />

• Etiology & management <strong>of</strong> mango mal<strong>for</strong>mation<br />

• Etiology and management <strong>of</strong> shisham wilt.<br />

• Epidemiology and Genetics <strong>of</strong> Karnal bunt fungus<br />

• Population biology <strong>of</strong> rice blast fungus, Magnapor<strong>the</strong> grisea<br />

• Mechanism <strong>of</strong> intra-field variability in Rhizoctonia solani<br />

• <strong>Soil</strong> solarization<br />

• Mushrooms – Development <strong>of</strong> strains, and production technologies<br />

• Role <strong>of</strong> Ps. fluorescens in sporophores development <strong>of</strong> A. bisporus<br />

• Compost <strong>for</strong>mulation with Sugarcane baggase + Wheat Straw, 2:1 developed to reduce cost <strong>of</strong><br />

cultivation <strong>of</strong> Agaricus bisporus.<br />

• Developed chemical treatment (Formalin 15ml + Bavistin 0.5g/10kg compost) <strong>of</strong> long method<br />

compost to avoid <strong>the</strong> moulds in cultivation <strong>of</strong> A. bisporus.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Recommended supplementation <strong>of</strong> substrate with 2% mixture <strong>of</strong> Neem cake + Wheat straw + Rice<br />

bran + Soybean meal <strong>for</strong> Pleurotus spp. cultivation.<br />

• Standardized cultivation <strong>of</strong> Auricularia polytricha using sterilized wheat straw supplemented with<br />

wheat bran (5%).<br />

• Standardized cultivation <strong>of</strong> Lentinula edodes with substrate<br />

popular sawdust.<br />

• Systemic induced resistance in brassica.<br />

• Use <strong>of</strong> siderophore producing Pseudomonads <strong>for</strong> early fruiting<br />

and enhanced yield <strong>of</strong> Agaricus bisporus.<br />

Lentinula edodes<br />

• Use <strong>of</strong> Pseudomonas fluorescens <strong>for</strong> control <strong>of</strong> mushroom<br />

diseases caused by Verticillium, Sepedonium, Trichoderma and Fusarium.<br />

• Pleurotus sajor-caju and P. florida recommended <strong>for</strong> commercial cultivation using soybean straw /<br />

Paddy straw / Wheat straw / Mustard straw.<br />

• Standardized cultivation technology <strong>for</strong> Hypsizygus almarius<br />

using wheat straw supplemented with wheat bran.<br />

• Standardized cultivation <strong>of</strong> Calocybe indica using wheat<br />

straw as a substrate with casing <strong>of</strong> FYM + Spent Compost +<br />

Sand (2:1:1).<br />

• A relay cropping schedule developed <strong>for</strong> Tarai region <strong>of</strong><br />

Uttarakhand: two crops Agaricus bisporus (Sept. - March), four crops Calocybe indica<br />

Pleurotus spp. (Sept.- Nov. and Feb.,- April) and three crops <strong>of</strong> Calocybe<br />

indica (March-October).<br />

• Developed two strains <strong>of</strong> Agaricus bisporus, Pant 31 and Pant 52, now included in multilocational<br />

testing under coordinated trials.<br />

• Development and commercialization <strong>of</strong> seven hybrids <strong>of</strong> oyster mushroom.<br />

• Associated with multilocational testing and release <strong>of</strong> <strong>the</strong> strains NCS-100, NCS-102, NCH-102 <strong>of</strong><br />

A. bisporus.<br />

• 120 mushroom species from different locations in Uttarakhand<br />

have been collected and preserved in <strong>the</strong> museum <strong>of</strong> <strong>the</strong><br />

centre.<br />

• Of <strong>the</strong> collected mushrooms five Auricularia, four species <strong>of</strong><br />

Pleurotus and two species <strong>of</strong> Ganoderma have been brought<br />

under cultivation.<br />

• Developed / standardized technology <strong>for</strong> production <strong>of</strong> traditional<br />

value added mushroom products viz. ‘Sev’, ‘Warian’, ‘Papad’<br />

and ‘Mathri’.<br />

Ganoderma lucidum<br />

• Isolated a high value cater pillar mushroom<br />

Cordyceps sinensis from high altitudes <strong>of</strong><br />

Uttarakhand and analysed <strong>for</strong> antioxidative<br />

properties.<br />

Cordyceps sinensis<br />

- 9 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

MAJOR ACHIEVEMENTS<br />

‣ Twenty seven wheat lines, combining better agronomic characteristics and resistance to diseases<br />

including Karnal bunt have been identified (Shanghi-4, BW 1052, HUW 318, Lira/Hyan’S’ VUI’S’,<br />

CUMPAS 88, BOBWHITE, SPRW 15/BB/Sn<br />

64/KLRE/3/CHA/4/GB(K)/16/VEE/ GOV/AZ/MU, NI9947, Raj 3666,<br />

UP 1170, HS 265, HD 2590, HS317, PH 130, PH 131, PH 147, PH<br />

148, PH 168, HW 2004, GW 188, MACS 2496, CPAN 3004, K8804,<br />

K8806, ISWYN-29 (Veery”S”) and Annapurna).<br />

‣ Foliar blight <strong>of</strong> wheat has now been assumed as a problem in Tarai<br />

areas <strong>of</strong> U.P and foothills <strong>of</strong> Uttarakhand. Bipolaris sorokiniana -<br />

Dreschlera sorokiniana, was found associated with <strong>the</strong> disease in<br />

this area. Karnal bunt <strong>of</strong> wheat caused by Tilletia indica Mitra, is widely distributed in various<br />

Western and Eastern districts <strong>of</strong> U.P while <strong>the</strong> North hills and Sou<strong>the</strong>rn dry areas are free from <strong>the</strong><br />

disease.<br />

‣ Multiple disease control in wheat has been obtained by seed treatment with Raxil 2DS @<br />

1.5g/Kg seed + one foliar spray fungicide Folicur 250 EW (Tebuconazole) @ 500ml/ha, which<br />

controls loose smut, brown rust, yellow rust, powdery mildew and leaf blight disease very<br />

effectively.<br />

‣ The mixture <strong>of</strong> HD 2329 + WH 542 + UP 2338 produced highest yield recording 11.67 per cent<br />

higher as compared to average yield <strong>of</strong> <strong>the</strong>ir components.<br />

‣ Among new fungicides Raxil 2DS (Tebuconazole) @ 1.0, 1.5, 2.0 and 2.5g/kg seed, Flutriafol<br />

and Dividend @ 2.5g/Kg seed were found highly effective in controlling <strong>the</strong> disease. Raxil 2DS<br />

@ 1.5g/Kg seed as slurry treatment gave complete control <strong>of</strong> loose smut.<br />

‣ New techniques <strong>for</strong> embryo count and seedling count <strong>for</strong> loose smut, modified partial vacuum<br />

inoculation method <strong>of</strong> loose smut, creation <strong>of</strong> artificial epiphytotics <strong>of</strong> Karnal bunt, NaOH seed<br />

soaked method <strong>for</strong> Karnal bunt detection and detached leaf technique <strong>for</strong> screening against<br />

leaf blight using pathogen toxin developed.<br />

‣ The major emphasis has been on <strong>the</strong> screening <strong>of</strong> maize germplasms to various diseases with<br />

special reference to brown stripe downy mildew, banded leaf and sheath blight and Erwinia<br />

stalk rot. A sick-plot has been developed to ensure natural source <strong>of</strong> inoculum. Efficient<br />

techniques <strong>for</strong> mass multiplication <strong>of</strong> inoculum and screening <strong>of</strong> germplasms have been<br />

developed to create epiphytotic conditions. The selected genotypes have been utilized <strong>for</strong><br />

evolving agronomically adaptable varieties. Several promising hybrids and composites have<br />

developed and released following interdisciplinary approach.<br />

‣ Studies on estimation <strong>of</strong> yield losses, epidemiological parameters on various economically<br />

important diseases <strong>of</strong> maize have been worked out to evolve suitable control measures and<br />

have been recommended to farmers in <strong>the</strong> region.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

‣ Based on <strong>the</strong> survey and surveillance studies <strong>the</strong> in<strong>for</strong>mation on <strong>the</strong> occurrence <strong>of</strong> various<br />

diseases in UP and Uttarakhand, a disease map has been prepared and monitored to finalize <strong>the</strong><br />

out breaks <strong>of</strong> one or more diseases in a given area based on wea<strong>the</strong>r parameters. It will help <strong>the</strong><br />

growers to be prepared to save <strong>the</strong> crop from recommended plant protection measures.<br />

‣ A repository <strong>of</strong> >600 isolates <strong>of</strong> biocontrol agents developed at Pantnagar & Ranichauri. These<br />

isolates are suited <strong>for</strong> different crops & agro-ecological conditions.<br />

‣ Standard methods developed <strong>for</strong> testing hyphal and sclerotial colonization.<br />

‣ Isolate <strong>of</strong> T. virens capable <strong>of</strong> colonizing sclerotia <strong>of</strong> Rhizoctonia, Sclerotium and Sclerotinia<br />

isolated <strong>for</strong> <strong>the</strong> first time. It may have great potential.<br />

‣ 16 new technologies related with mass multiplication and <strong>for</strong>mulation <strong>of</strong> microbial bio-agents<br />

developed and are in <strong>the</strong> process <strong>of</strong> being patented.<br />

‣ Several genotypes including SPV 462, SPV 475, SPV 1685, SPH 1375, SPH 1420, CSV 13,<br />

CSV 15, CSH 14, CSH 16, CSH 18, G-01-03, G-09-03, GMRP 91, RS 629, UTFS 45, UTMC<br />

523 and AKR 150 have been identified with high level <strong>of</strong> resistance to anthracnose and zonate<br />

leaf spot diseases.<br />

‣ Biocontrol agents T. harzianum and P. fluorescens have been found effective in increasing <strong>the</strong><br />

growth <strong>of</strong> plants and reducing <strong>the</strong> severity <strong>of</strong> zonate leaf spot. G. virens and T. viride have<br />

been found most effective against anthracnose pathogen <strong>of</strong> sorghum.<br />

‣ The cause <strong>of</strong> Khaira as zinc deficiency was established <strong>for</strong> <strong>the</strong> first time and zinc sulphate<br />

+slacked lime application schedule was developed <strong>for</strong> <strong>the</strong> control <strong>of</strong> <strong>the</strong> disease<br />

‣ Inoculation technique was developed to create “Kresek” phase in rice seedlings. Pre-planting root<br />

exposure technique in a suspension <strong>of</strong> 10 8 cells/ml <strong>for</strong> 24 hrs gave <strong>the</strong> maximum “Kresek”. Root<br />

inoculation, in general was found better <strong>for</strong> development <strong>of</strong> wilt symptoms than shoot inoculation.<br />

‣ A simple technique has been developed to detect <strong>the</strong> pathogen in and/or on seeds. The<br />

presence <strong>of</strong> viable pathogen has been demonstrated from infected seeds stored at room<br />

temperature up to 11 months after harvest.<br />

‣ The disease is sporadic in occurrence <strong>of</strong>ten becomes serious in nature. Chemical control trials<br />

showed that <strong>the</strong> disease can effectively be controlled by giving 2-3 foliar sprays <strong>of</strong><br />

streptocycline @ 15 g/ha.<br />

‣ A number <strong>of</strong> new fungicides along with recommended ones and botanicals were tested against<br />

sheath blight. Foliar sprays with Anvil, Contaf, Opus, Swing and RIL F004 @ 2 ml/l and Tilt @<br />

1 ml/l were found highly effective in controlling sheath blight. Foliar sprays with Neem gold @<br />

20 ml /lit. or Neem azal @ 3ml/lit. was found significantly effective in reducing sheath blight<br />

and increasing grain yield.<br />

‣ Foliar sprays with talc based <strong>for</strong>mulations <strong>of</strong> <strong>the</strong> bioagents (Trichoderma harzianum, or<br />

Pseudomonas fluorescence, rice leaf isolates) were found effective in reducing sheath blight<br />

and increasing grain yield. Foliar sprays with <strong>the</strong> bioagents (T.harzianum) or P. fluorescens)<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

given 7 days be<strong>for</strong>e inoculation with R. solani was highly effective against <strong>the</strong> disease.<br />

‣ Seed or soil treatment with T. harzianum or P. fluorescens @ 2, 4 or 8 g/kg enhanced root and<br />

shoot growth and fresh and dry weight <strong>of</strong> rice seedlings.<br />

‣ Seed treatment with fungorene followed by one spray <strong>of</strong> carbendazim (@ 0.05% at tillering at<br />

diseases appearance) and two sprays <strong>of</strong> Hinosan @ 0.1% at panicle initiation and 50%<br />

flowering was most effective and economical treatment in reducing <strong>the</strong> disease intensity and<br />

increasing <strong>the</strong> yield.<br />

‣ For <strong>the</strong> first time, true sclerotia were observed in Kumaon and Garhwal regions at an altitude <strong>of</strong><br />

900 m above. True sclerotia have a dormancy period <strong>of</strong> approximately six months. Exposure <strong>of</strong><br />

sclerotia to near ultraviolet radiation <strong>for</strong> an hour breaks <strong>the</strong> dormancy and increased<br />

germination.<br />

‣ Effect <strong>of</strong> different physical factors and extracts on <strong>the</strong> germination <strong>of</strong> true sclerotia was studied.<br />

Maximum germination was observed at 25 0 C and at pH 6.0, in fluorescent light. Among <strong>the</strong><br />

substratum, maximum germination occurred on moist sand. <strong>Soil</strong> extract was more favourable<br />

than o<strong>the</strong>r extracts. The number <strong>of</strong> stipes and mature head <strong>for</strong>mation was directly correlated<br />

with <strong>the</strong> size and weight <strong>of</strong> <strong>the</strong> sclerotia.<br />

‣ The viability <strong>of</strong> <strong>the</strong> 3 propagules namely; conidia, pseudo and true sclerotia stored under<br />

different conditions showed that conidia remain viable from 2-3 months, pseudo- sclerotia from<br />

4-6 months and true sclerotia up to 11 months at room temperature and under field conditions.<br />

True sclerotia buried at different depth (2.5 to 10 cm) in soil germinated well, but scleroita<br />

buried at 15 cm depth did not germinate and rotted.<br />

‣ Discoloured grains <strong>of</strong> various types were grouped according to <strong>the</strong>ir symptoms. The fungi<br />

responsible <strong>for</strong> each type <strong>of</strong> symptoms were identified. Ash grey discolouration <strong>of</strong> glumes<br />

separated by dark brown band was caused by Alternaria alternata and Nigrospora oryzae.<br />

Spots with dark brown margin and ash grey centre by Curvularia lunata and Alternaria<br />

alternata, light yellow to light brown spots by C. pallescens, Fusarium equiseti and N. oryzae,<br />

Brown to black dot by Phyllosticta oryzae Dark brown to black spot and specks by Drechslera<br />

victoriae, D. rostratum and D. oryzae, light to dark brown glumes by Sarocladium oryzae and<br />

D. oryzae, and light to dark brown spots by D. Australiense.<br />

‣ Rice varieties Manhar, Narendra 80, Saket 7, Ajaya, Bansmati, 385 showed higher incidence<br />

(34.1 to 41.8%) whereas Sarju 52, UPR 1561-6-3, Pusa 44, Jaya, Pant Dhan 10 and improved<br />

Sharbati exhibited lower (18.4-22.3%) incidence <strong>of</strong> seed discolouration. Bipolaris oyzae<br />

caused highest seed discolouration which is followed by Fusarium monili<strong>for</strong>me, curvularia<br />

lunata and Fusarium graminium in all <strong>the</strong> test varieties.<br />

‣ On <strong>the</strong> basis <strong>of</strong> <strong>the</strong> symptoms pattern and transmissibility <strong>of</strong> <strong>the</strong> pathogen through grafting and<br />

eriophyied mite (Aceria cajani), presence <strong>of</strong> <strong>for</strong>eign ribonucleic protein and nuclear inclusion<br />

like bodies in <strong>the</strong> phloem cell indicated <strong>the</strong> viral (RNA virus) nature <strong>of</strong> <strong>the</strong> pathogen <strong>of</strong> sterility<br />

- 12 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

mosaic <strong>of</strong> pigeon pea. The vector mite <strong>of</strong> <strong>the</strong> pathogen was found on lower surface <strong>of</strong> leaves<br />

<strong>of</strong> Canavis sativus and Oxalis circulata weeds in this area. Mild mosaic, ring spot and severe<br />

mosaic symptoms were observed in different as well as same cultivar. This observation reveals<br />

<strong>the</strong> presence <strong>of</strong> variation in <strong>the</strong> pathogen.<br />

‣ Germplasm lines/ cultivars screened viz; ICP 14290, ICP 92059,ICP 8093, KPBR 80-2-2, PL<br />

366, ICPL 371, Bahar, NP (WR) 15.were found resistan against Phytophthora stem blight <strong>of</strong><br />

pea.<br />

‣ Some resistant donors <strong>for</strong> mungbean yellow mosaic virus have been identified i.e. UPU-<br />

1,UPU-2,UPU-3, UG-370, PDU-104, NDU-88-8, UG-737, and UG-774. The varieties thus<br />

evolved include PU-19, PU- 30, and PU-35., Many, resistant lines/cultivars identified: ML-62,<br />

ML-65, Pant M-4, Pant M-5, ML-131, NDM 88-14, ML-682, PDM-27, ML- 15, ML-803, ML-682<br />

and 11/ 395 and <strong>for</strong> Urdbean leaf crinkle virus, SHU 9504, -9513,-9515, -9516, -9520, -9522, -<br />

9528, KU 96-1, UG 737 and TPU-4.<br />

‣ Seed treatment with carbendazim (0.1%) followed by two prophylactic sprays <strong>of</strong> carbendazim<br />

(0, 05%) or Dithane M-45 @ 0.25% was found most effective in reducing disease severity <strong>of</strong><br />

anthracnose disease. In early sown crop high disease severity was observed while in late<br />

sown crop low disease severity was recorded. Inter cropping with cereals or pulses have no<br />

effect on anthracnose severity.<br />

‣ Propiconazol 0.1%, carbendazim 0.1%, hexaconazol 0.1%, mancozeb 0.25% sprayed plots<br />

have low disease severity and high grain yield against Cercospora leaf spot.<br />

‣ Studies on integrated management <strong>of</strong> wilt/root rot/collar rot showed that Seed treatment with<br />

fungicide alone or in combination with o<strong>the</strong>r fungicides/ bio agents were found effective.<br />

Among <strong>the</strong> fungicides seed treatment with Bavistin + Thiram (1:2), vitavax + Thiram (1:2),<br />

vitavax, Bavistin, Bayleton, Bio agent Gliocladium virens + Vitavax<br />

and Pseudomonas fluorescence) decreased <strong>the</strong> seedling mortality,<br />

improved germ inability, plant stand and yield.<br />

‣ Eleven thousand germplasm lines/ breeding populations F 2 , F 3, F 4<br />

and F 5 generations were screened. Many germplasm/ accessions<br />

were found resistant/ tolerant to Botrytis gray mould viz; ICC 1069,<br />

ICC 10302, ICCL 87322, ICC 1599, -15980, - 8529, ICCV 88510, E100Y (M) BG 256, BG261,<br />

H86-73, IGCP 6 and GNG 146.<br />

‣ Lentil entries evaluated under sick plot <strong>for</strong> wilt/root rot/ collar rot diseases. The following lines<br />

were found promising viz; LL 383, PL 81-17, LH 54-8, DPL-58, DPL 14, Jawahar Massor- 3,<br />

DPL 112, IPL-114, L 4147 and Pant L 639.<br />

‣ The promising germplasm lines/ cultivars are as follows: DPL 62, PL-406, L 4076, TL 717, E<br />

153, IPL 101, IPL 105, PL- 639, LH 84-8, and Precoz .<br />

‣ The field pea lines were found promising JP 141, Pant P-5, KFPD 24 (swati), HUDP 15, KFPD-<br />

- 13 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

2, HFP-4, P1361, EC-1, P-632, P 108-1, KPMR 444, KF 9412, DPR 48, T-10, KPMRD348,<br />

DDR13, IM9102, KFP 141 and KPMR 467 against powdery mildew and JP 141, Pant P-5, P<br />

10, FP 141, KDMRD 384, HUDP-9, HUP-2 and T-10 were found promising against rust<br />

disease.<br />

‣ Mid-September planting or early October planting <strong>of</strong> rapeseed-mustard has been found to<br />

escape from Alternaria blight (Alternaria brassicae) downy mildew (Peronospora parasitica)<br />

and white rust (Albugo candida) diseases as against mid and late October planting. In general<br />

high occurrence <strong>of</strong> <strong>the</strong> floral infection (staghead phase) <strong>of</strong> white rust and downy mildew during<br />

flowering period has been found to be associated with reduced period, i.e. 2-6 hours, <strong>of</strong> bright<br />

sunshine/day concomitant with <strong>the</strong> mean maximum temperature <strong>of</strong> 21-25 0 C, <strong>the</strong> mean<br />

minimum temperature <strong>of</strong> 6-10 0 C and higher total rainfall up to 166 mm. Bright sunshine hours<br />

/day has a significant negative correlation whereas total rainfall has a significant positive<br />

correlation with staghead development.<br />

‣ All <strong>the</strong> three important foliar diseases <strong>of</strong> rapeseed-mustard could be effectively controlled by<br />

following integrated package <strong>of</strong> balanced N 100 P 40 K 40 application, early October sowing and<br />

treating <strong>the</strong> seed with Apron 35 SD @ 6g kg -1 seed followed by spray <strong>of</strong> mixture <strong>of</strong> metalaxyl +<br />

mancozeb (i.e Ridomil MZ 72 WP @ 0.25%) at flowering stage and by spray <strong>of</strong> mancozeb or<br />

iprodione @ 0.2% at pod <strong>for</strong>mation stage. In situations where Sclerotinia stem rot and / or<br />

powdery mildew appeared to be important in a particular crop season, a spray <strong>of</strong> mixture <strong>of</strong><br />

carbendazim (0.05%) + mancozeb (0.2%) was found to give excellent cost effective control <strong>of</strong><br />

<strong>the</strong> diseases with significant increase in seed yield <strong>of</strong> <strong>the</strong> crop.<br />

‣ Among <strong>the</strong> botanicals, leaf extracts <strong>of</strong> Eucalyptus globosus (5%) and Azadirchta indica (5%)<br />

have been proved to exhibit greater antifungal activity against A. brassicae and Albugo<br />

candida and showed significant reduction in <strong>the</strong> severity <strong>of</strong> Alternaria blight and white rust<br />

diseases which was rated to be at par with mancozeb fungicide spray.<br />

‣ Some abiotic chemical nutrient salts such as calcium sulphate (1%), zinc sulphate(0.1%) and<br />

borax (0.5%) and biocontrol agents such as Trichoderma harzianum and non-aggressive D<br />

pathotype <strong>of</strong> A.brassicae have been shown to induce systemic host resistance in mustard<br />

against aggressive “A” pathotype <strong>of</strong> A. brassicae and virulent race(s) <strong>of</strong> A. candida.<br />

‣ The staghead phase in B. juncea has been investigated to be due to A. candida and not due P.<br />

parasitica. Tissues at <strong>the</strong> staghead phase become more susceptible to P. parasitica than<br />

normal tissues <strong>of</strong> <strong>the</strong> same plant.<br />

‣ B. juncea genotypes (EC 399296, EC 399299, EC 399301, EC 399313, PAB-9535, Divya<br />

Selection-2 and PAB 9511), B. napus genotypes (EC 338997, BNS-4) and B. carinata (PBC-<br />

9221) have been shown to possess resistance to white rust coupled with high degree <strong>of</strong><br />

tolerance to Alternaria blight. Reduced sporulation is identified to be <strong>the</strong> major component <strong>for</strong><br />

slow blighting.<br />

- 14 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

‣ B. juncea (RESJ 836), B. rapa (RESR 219) and B. napus (EC 339000) have been selected <strong>for</strong><br />

resistance to downy mildew and <strong>for</strong> high yield per<strong>for</strong>mance. Total 52 genotypes <strong>of</strong> mustard<br />

representing at least 12 differential resistance sources, 23 lines <strong>of</strong> yellow sarson representing<br />

6 differential resistance sources and 54 lines <strong>of</strong> B. napus representing 3 differential resistance<br />

sources to downy mildew have been identified.<br />

‣ A new short duration (95-100 days) short statured (85- 96 cm) plant type <strong>of</strong> mustard strain<br />

‘DIVYA’ possessing high degree <strong>of</strong> tolerance to Alternaria blight suitable <strong>for</strong> intercropping with<br />

autumn sown sugarcane and potato yielding with an average <strong>of</strong> 15-22 q ha -1 has been<br />

developed. This ‘Mustard DIVYA’ plant type is now recommended as a source <strong>for</strong> breeding<br />

more and more improved varieties <strong>of</strong> mustard as it has been proved to have good general<br />

combining ability <strong>for</strong> short stature characteristics.<br />

‣ Seed treatment with mancozeb @ 0.2% + thiram @ 0.2% has been found to control seed,<br />

seedling and root rot diseases <strong>of</strong> groundnut. However seed treatment with thiram @ 0.2% +<br />

vitavax @ 0.2% has been found to control collar rot (Sclerotium rolfsii) <strong>of</strong> groundnut. Two<br />

sprays <strong>of</strong> carbendazim @ 0.05% have been found to give excellent control <strong>of</strong> early and late<br />

leaf spot (tikka disease) <strong>of</strong> groundnut.<br />

‣ Mid September planting <strong>of</strong> sunflower was found to escape <strong>the</strong> occurrence <strong>of</strong> major diseases<br />

like Sclerotinia wilt and rot, Sclerotium wilt, charcoal rot and toxemia. Severity <strong>of</strong> Alternaria<br />

blight was found to be negligible and did not cause any reduction in yield. The crop could be<br />

harvested by 15 th December. The yield obtained was 16 q/ha.<br />

‣ The average percent loss has been noted in <strong>the</strong> range <strong>of</strong> 50.6 to 80.7 percent due to Alternaria<br />

blight disease under Kharif conditions. However, <strong>the</strong> percent loss in oil has been shown in <strong>the</strong><br />

range <strong>of</strong> 21.6 to 32.3. To control <strong>the</strong> disease, total 4 sprays <strong>of</strong> mancozeb @ 0.3% at 10 day<br />

interval have been found effective.<br />

‣ A repository <strong>of</strong> about 5000 rice blast isolates was made from 30 locations in Indian Himalayas at<br />

Hill Campus, Ranichauri. Blast pathogen population from <strong>the</strong> region was analyzed using molecular<br />

markers and phenotypic assays. Most locations sampled and analyzed had distinct populations<br />

with some containing one or a few lineages and o<strong>the</strong>rs were very diverse. Within an<br />

agroecological region migration appeared to be high. The structure <strong>of</strong> some populations could be<br />

affected to some extent by sexual recombination.<br />

‣ Magnapor<strong>the</strong> grisea isolates derived from Eleusine coracana, Setaria italica and Echinochloa<br />

frumentaceum collected from a disease screening nursery were cross compatible. The<br />

chromosome number <strong>of</strong> each isolate was found to be six or seven. Similarity <strong>of</strong> karyotypes was<br />

found among isolates with in a lineage though between lineages some variability was noticed. A<br />

remarkable similarity between karyotypes <strong>of</strong> Eleusine coracana and Setaria italica was observed. All<br />

<strong>of</strong> <strong>the</strong>se isolates were fertile and mated with each o<strong>the</strong>r to produce productive peri<strong>the</strong>cia. The<br />

existing data however showed no evidence <strong>of</strong> genetic exchange among host-limited M. grisea<br />

- 15 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

populations in Indian Himalayas.<br />

‣ No strong relationship appeared between <strong>the</strong> number <strong>of</strong> virulences in a pathotyope and its frequency<br />

<strong>of</strong> detection. The frequency <strong>of</strong> virulent phenotype to a cultivar and susceptibility <strong>of</strong> that cultivar in <strong>the</strong><br />

field did not correspond. The number <strong>of</strong> virulences per isolate was in general less than <strong>the</strong> number<br />

<strong>of</strong> virulences per pathotype, which indicated predominance <strong>of</strong> isolates from pathotypes with fewer<br />

virulences. There was a tendency <strong>for</strong> <strong>the</strong> pathotypes to have fewer virulences. The frequency <strong>of</strong><br />

virulence among rare pathotypes was higher than common pathotypes against all <strong>the</strong> differential<br />

NILs, including two-gene pyramids. These rare pathotypes could be <strong>the</strong> potential source <strong>of</strong><br />

resistance breakdown <strong>of</strong> <strong>the</strong> novel resistance genes.<br />

‣ Blast resistant gene Pi-2(t) appeared to have <strong>the</strong> broadest and Pi-1(t) <strong>the</strong> narrowest resistant<br />

spectra. Compatibility to Pi-2 (t) gene did not appear to limit compatibilities with o<strong>the</strong>r resistant<br />

genes. Loss <strong>of</strong> avirulence to all <strong>the</strong> five major gene tested may carry a serious fitness penalty.<br />

Major gene Pi-2 and gene combination Pi-1,2 showed least compatibilities and hold promise<br />

in managing blast in <strong>the</strong> region. In <strong>the</strong> overall Himalayan population, gene combinations in<br />

general were effective at most locations. Combination <strong>of</strong> Pi-1+2 genes was effective at most<br />

locations until <strong>the</strong> year tested. However, three gene pyramid [Pi-1(t) + Pi-2(t)+Pi-4(t)] resisted<br />

infection at all locations.<br />

‣ It was inferred that <strong>the</strong> pathotype composition <strong>of</strong> <strong>the</strong> blast pathogen composition in <strong>the</strong> Indian<br />

Himalayas was very complex and diversifying <strong>the</strong> resistance genes in various rice breeding<br />

programmes should prove to be a useful strategy <strong>for</strong> disease management.<br />

‣ A common minimum programme under bio-intensive IPM in vegetables in Uttaranchal hills was<br />

designed that is extended to over 2000 farmers from 20 villages in district Tehri Garhwal.<br />

‣ Epidemiological considerations in <strong>the</strong> apple scab disease management led to <strong>the</strong> development<br />

<strong>of</strong> disease prediction models. Relation <strong>of</strong> degree-day accumulations to maturation <strong>of</strong><br />

ascospores, and potential ascospore dose (PAD) were found to be useful <strong>for</strong> predicting <strong>the</strong><br />

total amount <strong>of</strong> inoculum in an orchard <strong>the</strong>reby effectively improving apple scab management.<br />

‣ Out <strong>of</strong> 71 genotypes tested against red rot <strong>of</strong> sorghum caused by Colletotrichum falcatum, four<br />

genotypes viz; Co Pant 92226, Co Pant 96216, Co Pant 97222 and CoJ 83 were found<br />

resistant and ano<strong>the</strong>r 24 exhibited fairly good tolerance.<br />

‣ Seed treatment with Thiram + Carbendazim (2:1) @ 3g/kg seed or Vitavax 0.2% controlled <strong>the</strong><br />

seed and seedling rots and improved <strong>the</strong> seedling emergence without any adverse effect on<br />

<strong>the</strong> nodulation and invariably yield were increased. Seed treatment with Trichoderma<br />

harizianum, T. viride or Pseudomonas fluorescens @ 10g/kg controlled seed and seedling rots<br />

and increased plant emergence.<br />

‣ Purple seed stain disease can be effectively controlled by seed treatment with thiram +<br />

carbendazim (2:1) @ 3 g/kg seed followed by two sprays <strong>of</strong> benomyl or Carbendazim @ 0.5<br />

kg/ha.<br />

- 16 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

‣ Rhizoctonia aerial blight <strong>of</strong> soybean can be effectively controlled by two sprays <strong>of</strong> carbendazim<br />

@ 0.5 kg/ha. Seed treatment with T. harzianum or Pseudomonas fluorescens 10g/kg seed +<br />

soil treatment with pant Bioagent-3 mixed with FYM @50q/ha followed by two sprays <strong>of</strong> T.<br />

harzianum @ 0.25% reduced <strong>the</strong> disease severity <strong>of</strong> RAB.<br />

‣ Pod blight and foliar diseases caused by Colletrotichum dematium var truncatum could be<br />

effectively controlled by <strong>the</strong> use <strong>of</strong> carbednazim 0.05%, Mancozeb 0.25%, Copperoxychloride<br />

0.3%, Thiophanate methyl 0.05%, Chlorothalonil 0.25%, Hexaconazole 0.1% and<br />

Propiconazole 0.1%. First spray should be given as soon as disease appear and second spray<br />

after 15 days <strong>of</strong> first spray.<br />

‣ Rust disease <strong>of</strong> soybean could be effectively controlled with three sprays <strong>of</strong> Benomyl 0.05%,<br />

Mancozeb 0.25% or Zineb 0.25%, at 50, 60 and 70 days after sowing. Varieties Ankur, PK-<br />

7139, PK-7394, PK-7121, PK-7391 were resistant.<br />

‣ Charcoal rot disease can be effectively controlled by seed treatment with Trichoderma<br />

harzianum @ 0.2% + vitavax @ 0.1%.<br />

‣ Pre-mature drying problem Soybean can be minimized by seed treatment with carbendazim +<br />

Thiram (2:1) @ 3g/kg seed followed by two sprays with carbendazim, mancozeb and<br />

Aure<strong>of</strong>ungin. Varieties PSS-1, PS-1042, PK-1162, PK-1242 and PK-1250 were found to be<br />

superior <strong>for</strong> premature drying problem.<br />

‣ Integrated disease management (IDM) modules based on combined use <strong>of</strong> cultural practices,<br />

fungicides <strong>for</strong> fungal disease, insecticide <strong>for</strong> virus disease and host resistance were evaluated<br />

against RAB and Soybean yellow Mosaic virus diseases.<br />

‣ Bacterial pustules can be successfully controlled by two sprays at 45 and 55 days after<br />

planting with a mixture <strong>of</strong> Blitox-50 (1.5 kg/ha) + Agrimycin-100 (150g/ha) or streptocycline<br />

(150 g/ha) + copper sulphate (1kg/ha).<br />

‣ Soybean yellow Mosaic can be very effectively controlled by four sprays with oxymethyl<br />

demoton @ 1l/1000 lit/ha at 20, 30, 40 and 50 days after planting. <strong>Soil</strong> application with Phorate<br />

10G @ 10 kg/ha and Furadan 3G @ 17.5 kg/ha controlled <strong>the</strong> disease. Varieties PK-1284,<br />

1251, 1259, 1043, 1225, 1303, 1314, 1343, 1347, PS-1042 PS-564, 1364 were identified as<br />

resistant to Soybean yellow Mosaic virus.<br />

EXTENSION<br />

The scientists also participate in <strong>the</strong> farmers contact programme as well as practical<br />

trainings at different levels including those <strong>of</strong> IAS and PCS <strong>of</strong>ficers, Extension workers, Agricultural<br />

<strong>of</strong>ficers, Farmers, Defense Personnels etc. The Scientists <strong>of</strong> <strong>the</strong> department also actively<br />

participate in <strong>the</strong> trainings organized under <strong>the</strong> T&V programme <strong>for</strong> <strong>the</strong> benefit <strong>of</strong> farmers/State<br />

level Agricultural Officers. Two Pr<strong>of</strong>essors (Extension Pathology) and crop disease specialists are<br />

deputed to “Help Line Service” started recently by <strong>the</strong> University under Agriculture Technology<br />

- 17 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

In<strong>for</strong>mation Centre (ATIC). The telephone number <strong>of</strong> help line services is 05944-234810 and 1551.<br />

Technology developed by <strong>the</strong> centre is regularly communicated to <strong>the</strong> farmers <strong>of</strong> <strong>the</strong> 13 districts <strong>of</strong><br />

Uttarakhand State through <strong>the</strong> extension staff (<strong>Plant</strong> Protection) <strong>of</strong> both university and state<br />

agriculture and horticulture departments posted in all districts <strong>of</strong> <strong>the</strong> state. The radio talks and TV<br />

programme are delivered. Popular articles and disease circulars are published regularly <strong>for</strong> <strong>the</strong><br />

benefit <strong>of</strong> <strong>the</strong> farmers.<br />

UPGRADATION TO CENTRE OF ADVANCED STUDIES<br />

In view <strong>of</strong> <strong>the</strong> outstanding quality <strong>of</strong> teaching, research and extension work being carried out in<br />

<strong>the</strong> Department, ICAR in 1995 upgraded <strong>the</strong> department to <strong>the</strong> status <strong>of</strong> <strong>the</strong> Centre <strong>of</strong> Advanced<br />

Studies in <strong>Plant</strong> Pathology (CAS) and now has been upgraded to Centre <strong>of</strong> Advanced Faculty<br />

Training (CAFT). Major mandate <strong>of</strong> <strong>the</strong> CAFT is to train scientific faculty from all over <strong>the</strong> country in<br />

important and innovative areas <strong>of</strong> <strong>Plant</strong> Pathology. So far 27 trainings, with 559 participants from 25<br />

states, have been held The CAS was awarded by <strong>the</strong> education division, ICAR on August 14, 1998 a<br />

certificate <strong>of</strong> appreciation in commemoration <strong>of</strong> Golden Jubilee year <strong>of</strong> independence (1998) <strong>for</strong><br />

organizing <strong>the</strong> programmes <strong>for</strong> human resource development and developing excellent instructional<br />

material. The progress report <strong>of</strong> CAS/CAFT in <strong>Plant</strong> Pathology is as follows:<br />

- 18 -


Trainings Held<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

1. Recent advances in biology, epidemiology and management <strong>of</strong> diseases <strong>of</strong> major kharif<br />

crops (Sept. 19- Oct. 12, 1996)<br />

2. Recent advances in biology, epidemiology and management <strong>of</strong> diseases <strong>of</strong> major rabi crops<br />

(Feb. 25 –March 17, 1997)<br />

3. Ecology and ec<strong>of</strong>riendly management <strong>of</strong> soil-borne plant pathogens (Jan 12 – Feb. 02, 1998)<br />

4. Advanced techniques in plant pathology (Oct. 12 – Nov. 02, 1998)<br />

5. Recent advances in detection and management <strong>of</strong> seed-borne pathogens (March 10-30,<br />

1999)<br />

6. Recent advances etiology and management <strong>of</strong> root-rot and wilt complexes (Nov. 26 – Dec.<br />

16, 1998)<br />

7. Integrated pest management with particular reference to plant diseases: concept, potential<br />

and application (Nov. 23 –Dec. 13, 2000)<br />

8. Recent advances in research on major diseases <strong>of</strong> horticultural crops (March 01-30, 2001)<br />

9. Recent advances in plant protection technology <strong>for</strong> sustainable agriculture (Nov. 19 –Dec.<br />

09, 2001)<br />

10. <strong>Plant</strong> diseases diagnosis: past, present and future (Feb. 13, - March 05, 2002)<br />

11. Chemicals in plant protection: past, present and future (Jan. 28 – Feb. 17, 2003)<br />

12. Eco-friendly management <strong>of</strong> plant diseases <strong>of</strong> national importance: present status and<br />

research and extension needs (Nov. 10-30, 2003)<br />

13. Ecologically sustainable management <strong>of</strong> plant diseases: status and strategies (March 22-<br />

April 11, 2004)<br />

14. Disease resistance in field and horticulture crops: key to sustainable agriculture (Dec. 10-30,<br />

2004)<br />

15. Regulatory and cultural practices in plant disease management (Dec. 03-21, 2005)<br />

16. Crop disease management: needs and outlook <strong>for</strong> transgenics, microbial antagonists and<br />

botanicals (March 21 – April 10, 2006)<br />

17. <strong>Soil</strong> Health and Crop Disease <strong>Management</strong> (December 02-22, 2007)<br />

18. Role <strong>of</strong> Mineral Nutrients and Innovative Eco-friendly Measures in Crop Disease<br />

<strong>Management</strong> (March 22- April 11, 2007)<br />

19. <strong>Plant</strong> Disease <strong>Management</strong> on Small Farms (January 03-23, 2008)<br />

20. Seed Health <strong>Management</strong> <strong>for</strong> Better Productivity (March 28 to April 17, 2008)<br />

21. Recent Advances in <strong>Plant</strong> Disease <strong>Management</strong> (Dec. 13, 08 to Jan. 02, 09)<br />

22. Recent Advances in Biological Control <strong>of</strong> <strong>Plant</strong> Diseases (March 20 - April 09, 2009)<br />

23. <strong>Plant</strong> Pathology in Practice (March 22 to April 11, 2010)<br />

24. Climate change, precision agriculture and innovative disease control strategies (March 23 to<br />

April 12, 2011)<br />

25. Quality <strong>Management</strong> and <strong>Plant</strong> Protection Practices <strong>for</strong> enhanced competitiveness in<br />

- 19 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

agricultural export (November 12 to December 02, 2011)<br />

26. Diseases and <strong>Management</strong> <strong>of</strong> Crops under Protected Cultivation (September 04-24, 2012).<br />

27. <strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens<br />

(January 22 to February 11, 2013)<br />

Participations<br />

Sl. No. State Total Sl. No. State Total<br />

1. Andhra Pradesh 15 14. Maharashtra 40<br />

2. Arunachal Pradesh 02 15. Manipur 01<br />

3. Assam 13 16. Meghalaya 01<br />

4. Bihar 25 17. Nagaland 01<br />

5. Chattishgarh 08 18. Orissa 13<br />

6. Gujarat 45 19. Punjab 06<br />

7. Haryana 04 20. Rajasthan 45<br />

8. Himanchal Pradesh 39 21. Sikkim 01<br />

9. Jammu & Kashmir 34 22. Tamil Nadu 17<br />

10. Jharkhand 05 23. Uttar Pradesh 73<br />

11. Karnataka 28 24. Uttarakhand 91<br />

12. Kerla 05 25. West Bengal 18<br />

13. Madhya Pradesh 29 26. -- --<br />

Total = 559<br />

INFRASTRUCTURE<br />

• Wheat Pathology Lab. – General Path, Epidemiology, Toxin, Tissue Culture<br />

• Maize Pathology Lab. – General <strong>Plant</strong> Pathology, Bacteriology<br />

• Rice Pathology Lab. – General <strong>Plant</strong> Pathology<br />

• Ecology and Vegetable Pathology Lab. – Ecology, Histopathology, Biocontrol, Nematodes<br />

• Soybean Path. Lab.– General <strong>Plant</strong> Pathology, Fungicides<br />

• Oil Seed Path. Lab.– General Pl. Path., Tissue, Culture, Histopathology, Toxins<br />

• Pulse Path. Lab. – General Pl. Path., Phytovirology<br />

• Seed Path. Lab. – General Path, Seed Borne diseases<br />

• Biocontrol Lab. – Biocontrol & IPM<br />

• Molecular Pl. Path Lab. – Population biology & host- pathogen interaction<br />

• Mushroom Research & Training Centre – Research & training<br />

• Glass houses – 3<br />

- 20 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Polyhouses – 3<br />

• UG Practical Lab – 1<br />

• PG Lab – 1<br />

• Training Hall – 1<br />

• Conference Hall – 1<br />

• Office – 1<br />

Huts <strong>for</strong> Mushroom Production<br />

- 21 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Research Project (on going)<br />

‣ Programme Mode Support in Agrobiotechnology Phase-II (DBT)<br />

‣ Translational Research Centre on Biopesticides (DBT)<br />

‣ All India Coordinated Research Project on Biological Control (ICAR)<br />

‣ All India Coordinated Wheat and Barley Improvement Project (ICAR)<br />

‣ All India Coordinated Rice Improvement Project (ICAR)<br />

‣ Cereal Systems Initiative <strong>for</strong> South ASIA (CSISA) Objective 3 (IRRI)<br />

‣ Chitosan/Copper-Nanoparticles and Biopesticides <strong>for</strong> Knowledge-Based <strong>Plant</strong> Protection<br />

(DBT)<br />

‣ Large Scale Demonstration <strong>of</strong> IPM Technology through KVKs in Network Mode (HTMM-I)<br />

‣ All India Coordinated Chickpea Improvement Project (ICAR)<br />

‣ All India Coordinated Pigeonpea Improvement Project (ICAR)<br />

‣ All India Coordinated MullaRP Improvement Project (ICAR)<br />

‣ All India Coordinated Soybean Improvement Project (ICAR)<br />

‣ All India Coordinator Research Project on Rapeseed & Mustard (ICAR)<br />

‣ All India Coordinated Research Project on Seed Technology Research (NSP) (ICAR)<br />

‣ DUS Test Centre <strong>for</strong> Implementation <strong>of</strong> PVP-LEGISLATION <strong>for</strong> Forage Sorghum at<br />

Pantnagar (ICAR)<br />

‣ All India Coordinated Potato Improvement Project (ICAR)<br />

‣ Pest risk assessment <strong>of</strong> potato crop in Kumaon Region <strong>of</strong> Uttarakhand (HTMM-I)<br />

- 22 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

‣ All India Coordinated Maize Improvement Project (ICAR)<br />

‣ Demonstration <strong>of</strong> Bio-intensive Integrated Pest Module in Tomato (NHB)<br />

‣ All India Coordinated Sugarcane Improvement Project (ICAR)<br />

‣ All India Coordinated Sorghum Improvement Project (ICAR)<br />

‣ All India Coordinated Mushroom Improvement Project (ICAR)<br />

‣ Demonstration <strong>of</strong> Existing Mushroom Production Technologies (HTMM-I)<br />

Total Budget Outlay – > 1000 lakhs<br />

Research Areas – Biological Control, IPM, Shisham wilt, <strong>Soil</strong> solarization, Population Biology,<br />

Seed pathology, Mushroom etc.<br />

Publication<br />

1. Books - 60<br />

2. Research Bulletins - 20<br />

3. Research Papers - >1200<br />

4. Conceptual / Review articles - >130<br />

5. Chapters contributed to book - >150<br />

6. Extension literature - over (200)<br />

(Hindi – English)<br />

Annual Review <strong>of</strong> Phytopathology - 02<br />

Recognition and Awards:<br />

• UNO (Rome) – Dr. Y. L. Nene<br />

• Pr<strong>of</strong>. M. J. Narisimhan Academic Award (IPS) 5<br />

• Jawahar Lal Nehru Award (ICAR) 2<br />

• Pesticide India Award (ISMPP) 7<br />

• P. R. Verma Award <strong>for</strong> best Ph. D. Thesis (ISMPP) 2<br />

• O<strong>the</strong>r (Hexamar, MS Pavgi, Rajendra Prasad etc.) >21<br />

• Uttaranchal Ratana 2<br />

• Education Award 2004-05” <strong>for</strong> his book “Qyksa ds jksx” 01<br />

by <strong>the</strong> Ministry <strong>of</strong> Human Resource Development, GOI<br />

Pr<strong>of</strong>essional Societies and our Share:<br />

Indian Phytopathological Societies<br />

Presidents – 3<br />

Zonal Presidents – 3<br />

Indian Society <strong>of</strong> Mycology & <strong>Plant</strong> Pathology –<br />

Presidents – 3<br />

Vice Presidents – 1<br />

Indian Soc. Seed Technology<br />

Vice Presidents - 3<br />

- 23 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Science Congress<br />

President (Agriculture Chapter) - 1<br />

National Academy <strong>of</strong> Agricultural Sciences<br />

Fellows - 3<br />

Future Strategies<br />

Teaching: Introduction <strong>of</strong> new courses<br />

Methods in Biological Control<br />

<strong>Plant</strong> disease <strong>of</strong> national importance<br />

Integrated plant disease management<br />

Molecular plant pathology<br />

Advances in mushroom production<br />

Research thrust:<br />

• Biological control & ICM (IPM + INM) in different crops/cropping systems<br />

• Disease management under organic farming<br />

• Microbial ecology<br />

• Green chemicals<br />

• Population biology <strong>of</strong> pathogens (including use <strong>of</strong> molecular tools)<br />

• Induced resistance<br />

• Exploitation <strong>of</strong> indigenous edible and medicinal mushrooms<br />

Human Resource Development<br />

Degree awarded<br />

M.Sc. 335<br />

PhD 198<br />

Trainings organized No. Persons trained<br />

Summer schools (ICAR) 5 136<br />

Summer training (DBT) 1 24<br />

International training (IRRI) 1 11 (8 countries)<br />

Under CAS/CAFT 27 559<br />

Mushroom Production Training 13 315<br />

Under SGSY on Mushroom Production 60 1785<br />

Under HTM on Mushroom 21 574<br />

Under RKVY on IPM 76 4130<br />

Under HTM on IPM 90 2292<br />

Under Seed Technology Research 05 150<br />

Future Goal<br />

Ecologically sustainable management <strong>of</strong> plant diseases to ensure both food security &<br />

safety through education, research & extension<br />

- 24 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Management</strong> <strong>of</strong> Pests in Protected Cultivation-Problems & Perspectives<br />

H.S. Tripathi and Santosh Kumar<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A .& T., Pantnagar-263 145 (UK)<br />

Protected Cultivation and <strong>the</strong> Role <strong>of</strong> Crop Protection<br />

The purpose <strong>of</strong> growing crops under greenhouse conditions is to extend <strong>the</strong>ir cropping<br />

season and to protect <strong>the</strong>m from adverse environmental conditions, such as extreme temperatures<br />

and precipitation, and from diseases and pests (Hanan et al., 1978). Greenhouse structures are<br />

essentially light scaffolding covered by sheet glass, fibreglass or plastic. Such materials have a<br />

range <strong>of</strong> energy-capturing characteristics, all designed to maximize light transmission and heat<br />

retention.Modern technology has given <strong>the</strong> grower some powerful management tools <strong>for</strong><br />

production. Generally, added-value crops are grown under protection. Most <strong>of</strong> <strong>the</strong>m are labourintensive<br />

and energy-demanding during cold wea<strong>the</strong>r. Greenhouse production <strong>the</strong>re<strong>for</strong>e, normally<br />

requires a high level <strong>of</strong> technology to obtain adequate economic returns on investments. Quality is<br />

a high priority <strong>for</strong> greenhouse crops, requiring much care in pest and disease management, not<br />

only to secure yields but also to obtain a high cosmetic standard. Although technological changes<br />

are ultimately intended to reduce production costs and maximize pr<strong>of</strong>its, precise environmental<br />

and nutritional control push plants to new limits <strong>of</strong> growth and productivity. This can generate<br />

chronic stress conditions, which are difficult to measure, but apparently conducive to some pests<br />

and diseases. Historically, not enough attention has been paid to exploiting and amending<br />

production technology <strong>for</strong> <strong>the</strong> control <strong>of</strong> pests and diseases. This makes <strong>the</strong> control <strong>of</strong> pests and<br />

diseases in protected crops even more challenging, with many important problems being<br />

unresolved and new ones arising as <strong>the</strong> industry undergoes more changes in production systems.<br />

Importance <strong>of</strong> Protected Crops <strong>for</strong> <strong>Plant</strong> Production<br />

Greenhouses were initially built in areas with long, cold seasons to produce out-<strong>of</strong> season<br />

vegetables, flowers and ornamental plants. Nor<strong>the</strong>rn Europe is <strong>the</strong> paradigm <strong>of</strong> pioneering areas<br />

<strong>of</strong> greenhouse cultivation. Greenhouses protect crops against cold, rain, hail and wind, providing<br />

plants with improved environmental conditions compared to <strong>the</strong> open field. In greenhouses, crops<br />

can be produced out-<strong>of</strong>-season year-round with yields and qualities higher than those produced in<br />

<strong>the</strong> open field. Greenhouses have also allowed <strong>the</strong> introduction <strong>of</strong> new crops, normally <strong>for</strong>eign to<br />

- 25 -


<strong>the</strong> region (Germing, 1985).<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

There are two basic types <strong>of</strong> greenhouse. The first type seeks maximum control in an<br />

environment to optimize productivity. In Europe, optimal conditions <strong>for</strong> year-round production are<br />

provided in <strong>the</strong> glasshouses <strong>of</strong> The Ne<strong>the</strong>rlands, Belgium, <strong>the</strong> UK and Scandinavia. The o<strong>the</strong>r type<br />

<strong>of</strong> greenhouse, which is very common throughout <strong>the</strong> Mediterranean area, provides minimal<br />

climatic control, enabling <strong>the</strong> plants grown inside to adapt to suboptimal conditions, survive and<br />

produce an economic yield (Enoch, 1986; Tognoni and Serra, 1989; Castilla, 1994).<br />

Reuveni et al,, (2008) observed a reduction in <strong>the</strong> number <strong>of</strong> infection sites <strong>of</strong> B. cinerea<br />

on tomato and cucumber when a UV-absorbing material was added to polyethylene film to<br />

increase <strong>the</strong> ratio <strong>of</strong> blue light to transmitted UV light. Blue photo selective polyethylene sheets<br />

have been suggested <strong>for</strong> <strong>the</strong>ir ability to reduce grey mould on tomato (Reuveni and Raviv, 1992)<br />

and downy mildew on cucumber (Reuveni and Raviv, 1997). Green-pigmented polyethylene<br />

reduced <strong>the</strong> conidial load and grey mould in commercial tomato and cucumber greenhouses by<br />

35–75%. Sclerotinia sclerotiorum on cucumber, Fulvia fulva (Cooke) Cif. (= Cladosporium fulvum<br />

Cooke) on tomato and cucumber powdery mildew were also reduced (Elad, 1997).<br />

The influence <strong>of</strong> greenhouse structures and covers on greenhouse climatic regimes may<br />

have strong consequences <strong>for</strong> pests and <strong>the</strong>ir natural enemies, as <strong>the</strong>y have <strong>for</strong> diseases. In hightech<br />

greenhouses, regulation <strong>of</strong> temperature and water pressure deficit enables <strong>the</strong> creation <strong>of</strong><br />

conditions less favorable to pathogens and, in some cases, more favorable to bio control agents.<br />

The use <strong>of</strong> heating to limit development <strong>of</strong> a number <strong>of</strong> pathogens is well known (Jarvis, 1992).<br />

The use <strong>of</strong> high root temperatures in winter grown tomatoes in rock wool <strong>of</strong>fers a non-chemical<br />

method <strong>of</strong> controlling root rot caused by Phytophthora cryptogea Pethybr. & Lafferty. The high<br />

temperature was shown to enhance root growth while simultaneously suppressing inoculum<br />

potential and infection, and, consequently, reducing or preventing aerial symptoms (Kennedy and<br />

Pegg, 1990). Careful control <strong>of</strong> <strong>the</strong> temperature also proved important in <strong>the</strong> case <strong>of</strong><br />

hydroponically grown spinach and lettuce, in which it prevented or reduced attack by both Pythium<br />

dissotocum Drechs. and Pythium aphanidermatum (Edson) Fitzp. (Bates and Stanghellini, 1984).<br />

Recently, attacks <strong>of</strong> P. aphanidermatum on nutrient film technique (NFT) grown lettuce in Italy<br />

were related to <strong>the</strong> high temperature (>29°C) <strong>of</strong> <strong>the</strong> nutrient solution. Root rot was inhibited by<br />

reducing <strong>the</strong> temperature below 24°C (Carrai, 1993).Productivity is manifold in greenhouses in<br />

comparison to growing <strong>the</strong> vegetables in open field as shown in <strong>the</strong> table below:<br />

Table: Per<strong>for</strong>mance <strong>of</strong> tomato varieties under polyhouse and open field conditions in NEH region<br />

(Barapani)<br />

Varieties Polyhouse Open field Varieties Polyhouse Open field<br />

yield (q/ha) yield (q/ha)<br />

yield (q/ha) yield (q/ha)<br />

BT-117-5-3-1 342.00 115.00 selection-2 233.00 73.83<br />

KT-10 283.60 117.40 selection-1 2000.98 84.03<br />

BT-10 294.00 111.65 KT-15 211.60 51.65<br />

Arka Alok 260.00 57.90 H-24 143.17 58.75<br />

BT-12 302.40 101.00 Arka Abha 193.50 70.33<br />

- 26 -


Status<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Commercial greenhouses with climate-controlled devices are very few in <strong>the</strong> country. Solar<br />

Green houses comprising <strong>of</strong> glass and polyethylene houses are becoming increasingly popular<br />

both in temperate and tropical regions. In comparison to o<strong>the</strong>r countries, India has very little area<br />

under greenhouses as is evident from Table below:<br />

Table: Approximate area (ha) under greenhouses<br />

Country Area Country Area<br />

Japan 54000 Turkey 10000<br />

China 48000 Holland 9600<br />

Spain 25000 USA 4000<br />

South Korea 21000 Israel 1500<br />

Italy 18500 India 3500<br />

Purpose <strong>of</strong> Glasshouse<br />

1. The purpose <strong>of</strong> growing crops under greenhouse conditions is to extend <strong>the</strong>ir cropping<br />

season and to protect <strong>the</strong>m from adverse environmental conditions, such as extreme<br />

temperatures and precipitation, and from diseases and pests<br />

2. Greenhouse production normally requires a high level <strong>of</strong> technology to obtain adequate<br />

economic returns on investments<br />

Problems in glasshouses<br />

1. Normally value added crops are grown under protection most <strong>of</strong> <strong>the</strong>m are laboure<br />

intensive and energy demanding during cold wea<strong>the</strong>r<br />

2. Normally high level <strong>of</strong> technology to obtain adequate economic returns<br />

3. Quality is a high priority <strong>for</strong> greenhouse crops, requiring much care in pest and disease<br />

management, not only to secure yields but cosmetic standard<br />

4. Continues cropping is practiced ,without a fallow--- it leads to <strong>the</strong> build-up <strong>of</strong> soil- borne<br />

and foliar pathogens<br />

5. This can generate chronic stress conditions ,which are conducive to some pests and<br />

diseases<br />

Factors Favorable to Pest and Disease Development: Well-grown and productive crops are<br />

generally less susceptible to diseases, but in many cases compromises have to be made between<br />

optimum conditions <strong>for</strong> economic productivity and conditions <strong>for</strong> disease and pest prevention.<br />

Well-fertilized and irrigated crops are, however, <strong>of</strong>ten more sensitive to pests, like aphids,<br />

whiteflies and leafminers. High host plant densities and <strong>the</strong> resulting microclimate are favorable to<br />

disease spread. Air exchange with <strong>the</strong> outside is restricted, so water vapour transpired by <strong>the</strong><br />

plants and evaporated from warm soil tends to accumulate, creating a low vapour pressure deficit<br />

(high humidity). There<strong>for</strong>e, <strong>the</strong> environment is generally warm, humid and wind-free inside <strong>the</strong><br />

greenhouse. Such an environment promotes <strong>the</strong> fast growth <strong>of</strong> most crops, but it is also ideal <strong>for</strong><br />

<strong>the</strong> development <strong>of</strong> bacterial and fungal diseases (Baker and Linderman, 1979; Fletcher, 1984;<br />

- 27 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Jarvis, 1992), <strong>of</strong> insects vectoring viruses and <strong>of</strong> herbivorous insects. For bacteria and many fungi<br />

(causal agents <strong>of</strong> rusts, downy mildews, anthracnose, grey mould, etc.) Greenhouses are<br />

designed to protect crops from many adverse conditions, but most pathogens and several pests<br />

are impossible to exclude. Windblown spores and aerosols containing bacteria enter doorways<br />

and ventilators; soilborne pathogens enter in windblown dust, and adhere to footwear and<br />

machinery. Aquatic fungi can be present in irrigation water; insects that enter <strong>the</strong> greenhouse can<br />

transmit viruses and can carry bacteria and fungi as well. Once inside a greenhouse, pathogens<br />

and pests are difficult to eradicate.<br />

Problems in protected cultivation<br />

Greenhouses are designed to protect crops from many adverse conditions, but most<br />

pathogens and several pests are impossible to exclude as:<br />

1. Windblown spores and aerosols containing bacteria enter doorways and ventilators<br />

2. <strong>Soil</strong>-borne pathogens enter in windblown dust, and adhere to footwear and machinery<br />

3. Aquatic fungi can be present in irrigation water<br />

4. Insects that enter <strong>the</strong> greenhouse can transmit viruses and can carry bacteria and fungi as<br />

well<br />

5. Once inside a greenhouse, pathogens and pests are difficult to eradicate eg. leach<br />

Factors Stimulating Sustainable Forms <strong>of</strong> Crop Protection in Protected Cultivation:<br />

Protected cultivation is an extremely high-input procedure to obtain food and o<strong>the</strong>r agricultural<br />

products per unit <strong>of</strong> land, although inputs are <strong>the</strong> lowest when related to <strong>the</strong> yield per area.<br />

Among <strong>the</strong> factors stimulating sustainable <strong>for</strong>ms <strong>of</strong> crop protection are <strong>the</strong> following:<br />

1. Consumer concern about chemical residues.<br />

2. Pesticide-resistance in pests and pathogens.<br />

3. Side-effects <strong>of</strong> chemical application are increasingly observed in old and new growing<br />

areas.<br />

4. Efficacy: Some pests and diseases are difficult – sometimes impossible – to control if an<br />

integrated approach is not adopted.<br />

Sometimes this can be achieved cheaply – in both economic and energetic terms – By<br />

means <strong>of</strong> correct crop and management practices. As mentioned be<strong>for</strong>e, <strong>the</strong> most damaging pests<br />

and many pathogens in greenhouses are polyphagous; although <strong>the</strong>y are able to develop on many<br />

host plants, <strong>the</strong>ir negative effect on yield varies with host plant species and cultivar. The<br />

development <strong>of</strong> cultivars which are less susceptible to pests and diseases or that favour <strong>the</strong><br />

activity <strong>of</strong> pest natural enemies is undoubtedly one <strong>of</strong> <strong>the</strong> most sustainable ways to control<br />

diseases in greenhouses and its potential <strong>for</strong> pests has been shown in a few but significant cases.<br />

REFERENCE<br />

• Baker, K.F. and Linderman, R.G. (1979) Unique features <strong>of</strong> <strong>the</strong> pathology <strong>of</strong> ornamental plants,<br />

Annual Review Phytopathology 17, 253–277.<br />

• Bates, M.L. and Stanghellini, M.E. (1984) Root rot <strong>of</strong> hydroponically grown spinach caused by<br />

- 28 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Pythium aphanidermatum and P. dissotocum, <strong>Plant</strong> Disease 68, 989–991.<br />

• Carrai, C. (1993) Marciume radicale su lattuga allevata in impianti NFT, Colture Protette 22(6),<br />

77–81.<br />

• Castilla, N. (1994) Greenhouses in <strong>the</strong> Mediterranean area: Technological level and strategic<br />

management, Acta Horticulturae 361, 44–56.<br />

• Enoch, H.Z. (1986) Climate and protected cultivation, Acta Horticulturae 176, 11–20.<br />

• Fletcher, J.T. (1984) Diseases <strong>of</strong> Greenhouse <strong>Plant</strong>s, Longman, London.<br />

• Germing, G.H. (1985) Greenhouse design and cladding materials: A summarizing review, Acta<br />

• Hanan, J.J., Holley, W.D. and Goldsberry, K.L. (1978) Greenhouse <strong>Management</strong>, Springer-Verlag,<br />

Berlin Horticulturae 170, 253–257.<br />

• Jarvis, W.R. (1992) <strong>Managing</strong> Diseases in Greenhouse Crops, American Phytopathological<br />

Society Press, St Paul, Minn.<br />

• Kennedy, R. and Pegg, G.F. (1990) Phytophthora cryptogea root rot <strong>of</strong> tomato in rock wool<br />

nutrient culture. III. Effect <strong>of</strong> root zone temperature on infection, sporulation and<br />

symptom development, Annals <strong>of</strong> Applied Biology 117, 537–551.<br />

• Reuveni, R. and Raviv, M. (1992) The effect <strong>of</strong> spectrally-modified polyethylene films on <strong>the</strong><br />

development <strong>of</strong> Botrytis cinerea in greenhouse grown tomato plants, Biological<br />

Agriculture & Horticulture 9, 77–86.<br />

• Reuveni, R. and Raviv, M. (1997) Control <strong>of</strong> downy mildew in greenhouse-grown cucumbers using<br />

blue photoselective polyethylene sheets, <strong>Plant</strong> Disease 81, 999–1004.<br />

• Reuveni, R., Raviv, M. and Bar, R. (2008) Sporulation <strong>of</strong> Botrytis cinerea as affected by<br />

photoselective sheets and filters, Annals <strong>of</strong> Applied Biology 134, 417–424.<br />

• Tognoni, F. and Serra, G. (1989) The greenhouse in horticulture: The contribution <strong>of</strong> biological<br />

research, Acta Horticulturae 245, 46–52.<br />

• Wittwer, S.H. and Castilla, N. (1995) Protected cultivation <strong>of</strong> horticultural crops worldwide<br />

- 29 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Soil</strong> Solarization <strong>for</strong> Biocontrol <strong>of</strong> <strong>Plant</strong> Pathogens<br />

Yogendra Singh<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar-263145 (Uttarakhand)<br />

Several methods have been developed <strong>for</strong> <strong>the</strong> management <strong>of</strong> diseases incited by various<br />

plant pathogens, which include application <strong>of</strong> chemicals, breeding <strong>for</strong> disease resistance,<br />

sanitation, crop rotation, biological control and soil disinfestations. The need <strong>for</strong> different methods<br />

<strong>of</strong> plant disease management stems from <strong>the</strong> fact that usually none <strong>of</strong> <strong>the</strong>m is perfect nor can<br />

anyone be used under all circumstances. Moreover, <strong>the</strong> life cycles <strong>of</strong> pathogens may vary in<br />

different crop systems, thus requiring different management strategies. There<strong>for</strong>e, any new<br />

method <strong>of</strong> disease management is <strong>of</strong> value since it adds to our ra<strong>the</strong>r limited arsenal <strong>of</strong> control<br />

methods. This is particularly true with innovative non chemical approaches which are needed to<br />

replace hazardous chemicals.<br />

The concept <strong>of</strong> managing soil borne pathogens has now changed. In past, control <strong>of</strong> <strong>the</strong>se<br />

pathogens concentrated on eradication. Later it has been realized that effective control could be<br />

achieved by interrupting <strong>the</strong> disease cycle, plant resistance or <strong>the</strong> microbial balance leading to<br />

disease reduction below <strong>the</strong> economic injury level, ra<strong>the</strong>r than absolute control. The integrated<br />

pest management concept encompasses many elements. In this context, soil solarization can play<br />

a significant role. <strong>Soil</strong> solarization is a non-chemical soil disinfestation method applied worldwide<br />

<strong>for</strong> <strong>the</strong> control <strong>of</strong> soil borne plant pathogens, weeds and nematodes.<br />

In Israel, extension workers and growers suggested that <strong>the</strong> intensive heating that occurs<br />

in mulched soil might be used <strong>for</strong> disease control. By mulching <strong>the</strong> soil with transparent<br />

polyethylene sheets in <strong>the</strong> hot season prior to planting, a team <strong>of</strong> Israeli workers developed a solar<br />

heating approach <strong>for</strong> soil disinfestation. <strong>Soil</strong> solarization is a method <strong>of</strong> controlling soil borne pests<br />

and pathogens by raising <strong>the</strong> temperature <strong>of</strong> <strong>the</strong> soil through application <strong>of</strong> transparent<br />

polyethylene sheet to a moist soil surface. With solarization vast possibilities <strong>for</strong> disease control<br />

are possible. <strong>Soil</strong> solarization as a disinfestations method, has potential advantages. It is a non<br />

chemical method which is not hazardous to <strong>the</strong> user and does not involve substances toxic to <strong>the</strong><br />

consumer, to <strong>the</strong> host plant or to o<strong>the</strong>r organisms. In <strong>the</strong> right perspective it is less expensive than<br />

o<strong>the</strong>r methods. This technology can easily be transmitted to <strong>the</strong> farmers and can be applied in large<br />

areas manually and mechanically. It may have a long term effect, since effective disease control lasts<br />

<strong>for</strong> more than one season. This method has <strong>the</strong> characteristics <strong>of</strong> an integrated control, since physical,<br />

chemical and biological mechanisms are involved and because <strong>the</strong> control <strong>of</strong> a wide variety <strong>of</strong> pests is<br />

achieved.<br />

Use <strong>of</strong> this method has been reported to reduce <strong>the</strong> population <strong>of</strong> many soil borne pathogens<br />

including fungi bacteria and nematodes as well as weeds (Pullman et al.,1981; Katan et al., 1983;<br />

Barbercheck et al; 1986; Verma et al; 2005). <strong>Soil</strong> solarization applied singly or in combination with<br />

biocontrol agents or reduced doses <strong>of</strong> soil fumigants/fungicides has shown a remarkable<br />

- 30 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

destructive effect on most soil borne plant pathogens.<br />

Various terms like solar heating, plastic or polyethylene tarping, polyethylene or plastic<br />

mulching <strong>of</strong> soil have been used to describe this method. Since this method involves repeated<br />

daily heating at relatively mild temperatures, <strong>the</strong> term solar pasteurization has also been<br />

suggested.<br />

Principles<br />

Heat is used as a lethal agent <strong>for</strong> <strong>the</strong> control <strong>of</strong> plant pathogenic organisms through <strong>the</strong><br />

use <strong>of</strong> transparent polyethylene soil mulches (tarps) <strong>for</strong> capturing solar energy. Polyethylene<br />

covering <strong>of</strong> soil induces green house effect and raises soil temperature. The following<br />

recommendations are made to bring about effective solar heating <strong>of</strong> soil:<br />

Transparent not black polyethylene should be used since it transmits most <strong>of</strong> <strong>the</strong> solar<br />

radiation that heats <strong>the</strong> soil. Black polyethylene, though it is greatly heated by itself, is less<br />

efficient in heating <strong>the</strong> soil than transparent sheet.<br />

<strong>Soil</strong> mulching should be carried out during <strong>the</strong> period <strong>of</strong> high temperatures and intense<br />

solar irradiation.<br />

<strong>Soil</strong> should be kept wet during mulching to increase <strong>the</strong>rmal sensitivity <strong>of</strong> resting structures<br />

such as sclerotia, chlamydospores, etc. and to improve heat conduction.<br />

The thinnest possible polyethylene tarp (25-30 µm) is recommended, since it is both<br />

cheaper and more effective in heating, due to better radiation transmittance, than <strong>the</strong><br />

thicker one. Polyethylene reduces heat convection and water evaporation from <strong>the</strong> soil to<br />

<strong>the</strong> atmosphere. As a result <strong>of</strong> <strong>the</strong> <strong>for</strong>mation <strong>of</strong> water droplets on <strong>the</strong> inner surface <strong>of</strong> <strong>the</strong><br />

poly<strong>the</strong>ne film, its transmissivity to long wave radiation is highly reduced, resulting in better<br />

heating due to an increase in its greenhouse effect. An ideal plastic mulch is that which is<br />

100% transparent to solar radiation and completely opaque to long wave radiation. This<br />

ideal mulch can increase soil temp. by 6-8 0 c over ordinary polyethylene.<br />

Since temperatures at <strong>the</strong> deeper soil layers are lower than at <strong>the</strong> upper ones, <strong>the</strong><br />

mulching period should be sufficiently extended, usually 4 weeks or longer, in order to<br />

achieve pathogen control at all desired depths.<br />

The solar heating method <strong>for</strong> disease control is similar, in principle, to that <strong>of</strong> artificial soil<br />

heating by steam or o<strong>the</strong>r means. There are, however, important biological and technological<br />

differences: (i) With soil solarization <strong>the</strong>re is no need to transport <strong>the</strong> heat from its source to <strong>the</strong><br />

field. (ii) Solar heating is carried out at relatively low temperatures as compared to artificial heating;<br />

thus its effects on living and nonliving components are likely to be less drastic. Negative side<br />

effects observed with soil steaming such as phytotoxicity due to release <strong>of</strong> toxic products and a<br />

rapid soil reinfestation due to <strong>the</strong> creation <strong>of</strong> a biological vacuum have not been reported so far<br />

with solar heating.<br />

Absorption <strong>of</strong> solar radiation in different soils varies according to <strong>the</strong> colour, moisture, and<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

texture <strong>of</strong> <strong>the</strong> soil. In general, <strong>the</strong> soil has high <strong>the</strong>rmal capacity and is a poor heat conductor thus<br />

resulting in a very slow heat penetration in soil. The energy is lost from <strong>the</strong> soil in <strong>the</strong> <strong>for</strong>m <strong>of</strong> long<br />

wave radiation through conduction, convection, and water evaporation. The principles <strong>of</strong> solar<br />

heating in polyethylene mulched soil were demonstrated by Waggoner et al., 1960. If <strong>the</strong>rmal<br />

processes occurring in mulched soil are considered, <strong>the</strong>n soil temperatures at <strong>the</strong> desired depth<br />

can be predicted. Mahrer, 1979 developed a one dimensional numerical model <strong>for</strong> such<br />

predictions. As per this model in wet, polyethylene mulched soil, increased temperatures are due<br />

primarily to <strong>the</strong> elimination <strong>of</strong> heat loss by evaporation and heat convection during <strong>the</strong> day time<br />

and partially to <strong>the</strong> green house effect (preventing part <strong>of</strong> <strong>the</strong> long wave radiation from leaving <strong>the</strong><br />

ground). By predicting <strong>the</strong> temperatures at any depth <strong>of</strong> <strong>the</strong> mulched soil, <strong>the</strong> model enables us to<br />

select <strong>the</strong> suitable climatic regions and <strong>the</strong> time <strong>of</strong> year most adequate <strong>for</strong> solarization <strong>of</strong> soil,<br />

providing data on <strong>the</strong> heat sensitivity <strong>of</strong> <strong>the</strong> pathogens and <strong>the</strong>ir population density at various<br />

depths are available. Relative importance <strong>of</strong> type <strong>of</strong> mulching material, soil type, moisture and<br />

climatic factors can also be evaluated. Analysis <strong>of</strong> <strong>the</strong> spatial soil temperature regimes in mulched<br />

soil showed that heating at <strong>the</strong> edges <strong>of</strong> <strong>the</strong> mulch is lower than at <strong>the</strong> center, and that a narrow<br />

mulch strip is less efficient in heating than a wider one ( Mahrer and Katan, 1981).<br />

Mechanisms<br />

Reduction in disease incidence occurring in solarized soils, results from <strong>the</strong> effects exerted<br />

on each <strong>of</strong> <strong>the</strong> three living components involved in disease ie. host, pathogen, and soil microbiota<br />

as well as <strong>the</strong> physical and chemical environment which, in turn affects <strong>the</strong> activity and<br />

interrelationships <strong>of</strong> <strong>the</strong> organisms. Although <strong>the</strong>se processes occur primarily during solarization,<br />

<strong>the</strong>y may continue to various extents and in different ways, after <strong>the</strong> removal <strong>of</strong> <strong>the</strong> polyethylene<br />

sheets and planting. The most pronounced effect <strong>of</strong> soil mulching with polyethylene is a physical<br />

one, i.e. an increase in soil temperatures, <strong>for</strong> several hours <strong>of</strong> <strong>the</strong> day. However, o<strong>the</strong>r processes<br />

such as shifts in microbial populations, changes in chemical composition and physical structure <strong>of</strong><br />

<strong>the</strong> soil, high moisture levels maintained by <strong>the</strong> mulch, and changes in gas composition <strong>of</strong> <strong>the</strong> soil,<br />

should also be considered while analyzing mechanisms <strong>of</strong> disease control. The following equation<br />

proposed by Baker (1968), <strong>for</strong> relating <strong>the</strong> various factors involved in biological control, should be<br />

adopted <strong>for</strong> this analysis:<br />

Disease severity =inoculum potential x disease potential, where inoculum potential is <strong>the</strong> energy<br />

available <strong>for</strong> colonization <strong>of</strong> a substrate (infection court) at <strong>the</strong> surface and disease potential is <strong>the</strong> ability<br />

<strong>of</strong> <strong>the</strong> host to contract disease. More specifically <strong>the</strong> equation becomes:<br />

Disease severity = (inoculum density x capacity) x (proneness x susceptibility), where<br />

capacity is <strong>the</strong> effect <strong>of</strong> <strong>the</strong> environment on energy <strong>for</strong> colonization, and proneness is <strong>the</strong> effect <strong>of</strong><br />

<strong>the</strong> environment on <strong>the</strong> host. Of <strong>the</strong>se four components, inoculum density (ID) is <strong>the</strong> one most<br />

affected by solarization ei<strong>the</strong>r through <strong>the</strong> direct physical effect <strong>of</strong> <strong>the</strong> heat or by microbial<br />

processes induced in <strong>the</strong> soil. The o<strong>the</strong>r components, however (except <strong>for</strong> susceptibility which is<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

genetically determined) might also be affected.<br />

Whenever microorganisms are subjected to moist heat, at temperatures exceeding <strong>the</strong><br />

maximum <strong>for</strong> growth, <strong>the</strong>ir viability is reduced. The <strong>the</strong>rmal death rate <strong>of</strong> a population <strong>of</strong> an<br />

organism depends on both <strong>the</strong> temperature level and exposure time, which are inversely related.<br />

At a given temperature and time <strong>of</strong> exposure, mortality rate is related to <strong>the</strong> inherent heat<br />

sensitivity <strong>of</strong> <strong>the</strong> organisms and to <strong>the</strong> prevailing environmental conditions. In general, populations<br />

<strong>of</strong> soil borne fungal pathogens are drastically reduced at temperatures <strong>of</strong> 40-50 0 C, exposure time<br />

ranging from minutes to hours <strong>for</strong> <strong>the</strong> higher temperatures, and up to days <strong>for</strong> <strong>the</strong> lower<br />

temperatures. The response <strong>of</strong> <strong>the</strong> population to elevated temperatures depends on propagule<br />

type, age and on environmental factors like pH, presence <strong>of</strong> ions etc. Presence <strong>of</strong> moisture is a<br />

crucial factor since microorganisms are much more resistant to heat under dry conditions. The<br />

effect <strong>of</strong> water can be explained by <strong>the</strong> dependence <strong>of</strong> <strong>the</strong> heat stability <strong>of</strong> proteins on hydration. In<br />

<strong>the</strong> presence <strong>of</strong> water less energy is required to unfold <strong>the</strong> peptide chain <strong>of</strong> proteins, resulting in a<br />

decreased heat resistance. Heating dry soils is <strong>the</strong>re<strong>for</strong>e not effective in pathogen control (Katan<br />

et al., 1976).<br />

Microbial processes, induced in <strong>the</strong> soil by solarization, may contribute to disease control,<br />

since <strong>the</strong> impact <strong>of</strong> any lethal agent in <strong>the</strong> soil extends beyond <strong>the</strong> target organisms. If induced by<br />

solarization, biological control may affect <strong>the</strong> pathogen by increasing its vulnerability to soil<br />

microorganisms or increasing <strong>the</strong> activity <strong>of</strong> soil microorganisms toward pathogen or plant, which<br />

will finally lead to a reduction in disease incidence, pathogen survivability, or both. Thus both short<br />

and long term effects might be expected. Biological control may operate at any stage <strong>of</strong> pathogen<br />

survival or disease development during or after solarization, through antibiosis, lysis, parasitism, or<br />

competition.<br />

Disease <strong>Management</strong><br />

<strong>Soil</strong> solarization has been demonstrated to control diseases caused by many fungal<br />

pathogens such as Rhizoctonia solani, Fusarium spp., Pythium spp., Phytophthora spp.,<br />

Verticillium spp., Sclerotium rolfsii etc., bacterial pathogens such as Agrobacteria and<br />

Pseudomonas and many species <strong>of</strong> nematodes in many crops both under field conditions and<br />

plastic houses (Katan et al., 1983; Abdul et al., 1995; Rao<strong>of</strong> and Rao,1997; Chellemi et al., 1994).<br />

The method has also been used to control many species <strong>of</strong> nematodes. Diseases caused by<br />

Meloidogyne spp., Heterodera spp. etc.have been successfully controlled by soil solarization (Rao<br />

and Krishnappa, 1995; Grinstein et al., 1995).<br />

Weed Control<br />

Solarization results in an effective weed control lasting in some cases <strong>for</strong> more than two or<br />

three seasons (Abdel Rahim et al., 1988; Verma et al., 2005). In general most <strong>of</strong> <strong>the</strong> annual and<br />

many perennial weeds have been found to be effectively controlled. Weed control may be effected<br />

by direct killing <strong>of</strong> weed seeds by heat, indirect microbial killing <strong>of</strong> seeds weakened by sublethal<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

heating, killing <strong>of</strong> seeds stimulated to germinate in <strong>the</strong> moistened solarized soil, and killing <strong>of</strong><br />

germinating seeds whose dormancy is broken in <strong>the</strong> heated soil. Volatiles may also play a role in<br />

weed control (Horowitz, 1980; Rubin and Benzamin, 1981).<br />

Increased growth response<br />

<strong>Plant</strong> growth in solarized infested soil is enhanced as compared to untreated, infested soil<br />

as a result <strong>of</strong> pathogen control but solarization <strong>of</strong> soil which is apparently free <strong>of</strong> known pathogens<br />

<strong>of</strong>ten results in improved plant growth. This could be attributed to increased micro and macro<br />

nutrients in soil solution, elimination <strong>of</strong> minor or unknown pathogens, destruction <strong>of</strong> phytotoxic<br />

substances in <strong>the</strong> soil, release <strong>of</strong> growth regulator like substances, and stimulation <strong>of</strong> mycorrhiza,<br />

PGPR, and o<strong>the</strong>r beneficial microorganisms. The effect <strong>of</strong> soil solarization on earthworms<br />

population has not received much attention but it is thought that <strong>the</strong>y retreat to lower depths to<br />

escape <strong>the</strong> effect <strong>of</strong> soil heating. The increased growth response <strong>of</strong> plants in solarized soil is a well<br />

documented phenomenon and has been verified both in green house experiments and under field<br />

conditions (Broadbent et al, 1977; Katan, 1987; Chen et al., 1991; Singh, 2008).<br />

Combining solarization with o<strong>the</strong>r methods<br />

Despite <strong>the</strong> successes achieved with solarization when used singly this method may be<br />

usefully aided by combination with o<strong>the</strong>r methods <strong>of</strong> disinfestation. As soil solarization is<br />

dependent upon local climatic conditions, sometimes even during conducive periods <strong>of</strong> <strong>the</strong> year,<br />

local wea<strong>the</strong>r conditions will not permit an effective solarization treatment. There<strong>for</strong>e, we must<br />

come up with integrated uses <strong>of</strong> solarization in order to increase <strong>the</strong> predictability <strong>of</strong> <strong>the</strong> treatment<br />

and thus make it more acceptable to growers. Combining solarization with pesticides, organic<br />

amendments, or biocontrol agents improves disease control. Whenever a pathogen is weakened<br />

by heating, even reduced dosages might suffice <strong>for</strong> improved control combining with biocontrol<br />

agents, organic amendments, etc.<br />

Low application rates <strong>of</strong> fungicides, fumigants or herbicides have been successfully<br />

combined with soil solarization to achieve better pest control (Hartz et al, 1993).Simultaneous<br />

application <strong>of</strong> chemicals and tarping <strong>the</strong> soil <strong>for</strong> solarization has been shown to increase <strong>the</strong><br />

effectiveness <strong>of</strong> both <strong>the</strong> methods because <strong>of</strong> synergism (Ben –Yephet et al. 1988; Tjamos, 1984).<br />

Reduced doses <strong>of</strong> metham-sodium (12.5 or 25 ml/m 2 ) applied singly or in combination with soil<br />

solarization synergistically destroyed V. dahliae and F. oxysporum f.sp. vasinfectum in a naturally<br />

infected cotton field. The synergism was attributed to <strong>the</strong> weakening effect induced by increased<br />

soil temperatures along with <strong>the</strong> toxicity <strong>of</strong> <strong>the</strong> chemical. The combination also reduced to one<br />

week <strong>the</strong> time needed to kill sclerotia <strong>of</strong> Sclerotinia sclerotiorum in <strong>the</strong> top 10 cm <strong>of</strong> soil in a lettuce<br />

field and reduced apo<strong>the</strong>cia production. Carbendazim has shown slower degradation rates after<br />

solarization, possibly because <strong>of</strong> changes in <strong>the</strong> populations <strong>of</strong> soil microorganisms after<br />

solarization.<br />

Solarization may also be combined with application <strong>of</strong> crop residues, green and farm yard<br />

manures. There is increasing evidence that <strong>the</strong>se materials release volatile compounds in <strong>the</strong> soil<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

that kill pests and help stimulate <strong>the</strong> growth <strong>of</strong> beneficial soil organisms (Deadman et al, 2006;<br />

Gamliel and Stapleton, 1993).<br />

<strong>Soil</strong> solarization has also been successfully combined with biological control. The use <strong>of</strong><br />

Trichoderma harzianum with solarization in fields infested with Rhizoctonia solani has been shown<br />

to improve disease control while delaying <strong>the</strong> buildup <strong>of</strong> inoculum (Chet et al, 1982). Greenberger<br />

et al, 1987 concluded that solarized soils are frequently more suppressive and less conducive to<br />

certain soil borne pathogens than non-solarized soils. An increase in population <strong>of</strong> green<br />

fluorescent pseudomonads along with an increase <strong>of</strong> Penicillium and Aspergillus spp. following<br />

solarization has been demonstrated (Stapleton and DeVay, 1982).<br />

Limitations<br />

Solarization involves limitations, difficulties and possible negative effects.<br />

It is wea<strong>the</strong>r dependent and can only be used in regions where <strong>the</strong> climate is suitable (hot) and<br />

<strong>the</strong> soil is free <strong>of</strong> crops <strong>for</strong> about one month or more at a time <strong>of</strong> tarping with PE sheets. The<br />

soil heating effect may be limited on cloudy days. Wind or air movement across <strong>the</strong> plastic<br />

sheet rapidly dissipates <strong>the</strong> trapped heat. Strong winds may also lift or tear <strong>the</strong> sheets.<br />

It is too expensive <strong>for</strong> some crops and ineffective in <strong>the</strong> control <strong>of</strong> certain diseases<br />

Heat tolerant pathogens might develop after repeated application, though selection <strong>for</strong><br />

tolerance to lethal agents is not likely to develop with disinfestation methods which are not<br />

target specific<br />

Ano<strong>the</strong>r possibility would be an increase in pathogen population due to a harmful effect on its<br />

antagonists<br />

Future Thrust<br />

The economic pr<strong>of</strong>itability <strong>of</strong> disease control depends on <strong>the</strong> additional income obtained<br />

and <strong>the</strong> cost <strong>of</strong> application. The additional income obtained through solarization far<br />

exceeds with high-value crops but with o<strong>the</strong>r crops situation may not be <strong>the</strong> same. There<br />

are several possibilities <strong>for</strong> reducing <strong>the</strong> cost <strong>of</strong> mulching: (a) Used polyethylene may be as<br />

effective as <strong>the</strong> new, thus reducing <strong>the</strong> cost to nearly zero (b) Reusing <strong>the</strong> polyethylene,<br />

providing it is durable (c) If required during <strong>the</strong> growing season, durable sheets may be<br />

used <strong>for</strong> both solarization and mulch (d) The production <strong>of</strong> thinner poly<strong>the</strong>ne sheets (<strong>of</strong> an<br />

adequate strength) will reduce <strong>the</strong> amount needed per hectare.<br />

<br />

Development in plastic technology may provide improved and economical mulching<br />

materials with greater heating efficiency and increased durability. This may include 1)<br />

Biodegradable plastic that decomposes in <strong>the</strong> natural environment 2) Fur<strong>the</strong>r development<br />

<strong>of</strong> polyethylene recycling processes 3) Developing economic, novel plastic or o<strong>the</strong>r<br />

materials more efficient than poly<strong>the</strong>ne in trapping solar energy, thus reducing our<br />

dependence on climate and making this available to cooler regions 4) Possibility <strong>of</strong> plastic<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

material that can be sprayed on <strong>the</strong> soil, instead <strong>of</strong> polyethylene mulching, should be<br />

explored. At present, biodegradable plastic products available in <strong>the</strong> market are more<br />

expensive than traditional plastics. Their cost needs to be reduced to make <strong>the</strong>m<br />

economical.<br />

REFERENCES<br />

• Abdel Rahim, M. F., Satour, M. M., Mickail, K.Y. and El Eraki, S. A. (1988). Effectiveness <strong>of</strong> soil<br />

solarization in furrow irrigated Egyptian soils. <strong>Plant</strong> Dis.. 72: 143-146.<br />

• Barbercheck, M.E.and von Broembsen, S.L (1986). Effect <strong>of</strong> soil solarization on plant parasitic<br />

nematodes and Phytophthora cinnamomi in South Africa.<strong>Plant</strong> Dis. 70:945-950.<br />

• Broadbent, P, Baker, KF, Franks, N and Holland, J. 1977. Effect <strong>of</strong> Bacillus spp. on increased<br />

growth <strong>of</strong> seedlings in steamed and in non treated soil. Phytopathology. 67: 1027-1034.<br />

• Chellemi, D.O.., Olson, S.M. and Mitchell, D. J. (1994). Effect <strong>of</strong> soil solarization and fumigation on<br />

survival <strong>of</strong> soil borne pathogens <strong>of</strong> tomato in Nor<strong>the</strong>rn Florida. <strong>Plant</strong> Dis. 78: 1167-1172.<br />

• Chen, Y., Gamliel, A., Stapleton, J. J. and Aviad, T. (1991). Chemical, physical and microbial<br />

changes related to plant growth in disinfested soils. In: <strong>Soil</strong> Solarization. Katan, J. and<br />

De Vay, J. E. (eds.) CRC Press, Inc., Boca Raton, FL. pp. 103-129.<br />

• Chet, I, Elad, Y, Kalfon, A, Hadar, Y and Katan, J. 1982. Integrated control <strong>of</strong> soilborne and<br />

bulbborne pathogens in iris. Phytoparasitica. 10:229.<br />

• Deadman, M, Al Nasani, H and Al Sa’di, A. 2006. Solarization and Bi<strong>of</strong>umigation reduce Pythium<br />

aphanidermatum induced damping <strong>of</strong>f and enhance vegetative growth <strong>of</strong> green house<br />

cucumber in OMAN. Journal <strong>of</strong> <strong>Plant</strong> Pathology. 88: 335-337.<br />

• Gamliel, A and Stapleton, J. 1993. Effect <strong>of</strong> chicken compost or ammonium phosphate and<br />

solarization on pathogen control, rhizosphere organisms, and lettuce growth. <strong>Plant</strong><br />

Disease. 77:886-891.<br />

• Grinstein, A., Kritzman, G., Hetzroni, A., Gamliel, A. Mor, M. and Katan, J. (1995). The border<br />

effect <strong>of</strong> soil solarization. Crop Protect. 14: 315-320.<br />

• Hartz, T, DeVay, J and Elmore, C. 1993. Solarization is an effective soil disinfestations technique<br />

<strong>for</strong> strawberry production. Hort. Sci. 28(2): 104-106.<br />

• Horowitz, M. 1980. Weed research in Israel. Weed Sci. 28: 457-460.<br />

• Katan, J, G Katan, J, Greenberger, A, Alon, H and Grinstein, A. 1976. Solar heating by<br />

polyethylene mulching <strong>for</strong> <strong>the</strong> control <strong>of</strong> diseases caused by soil-borne pathogens.<br />

Phytopathology. 66: 683-688.<br />

• Katan, J. (1987). <strong>Soil</strong> solarization. In: Innovative approaches to plant diseases control. Chet, I.<br />

(ed.). John Wiley & Sons New York. pp 77-105.<br />

• Katan, J., Fishler, G. and Grinstein, A. (1983). Short and long term effects <strong>of</strong> soil solarization and<br />

crop sequence on Fusarium wilt and yield <strong>of</strong> cotton in Israel. Phytopathology. 73:1215-<br />

1219.<br />

• Mahrer, Y. 1979. Prediction <strong>of</strong> soil temperature <strong>of</strong> a soil mulched with transparent polyethylene. J.<br />

Appl. Meteorol. 18:263-267.<br />

• Mahrer, Y. and Katan, J. 1981. Spatial soil temperatures regime under transparent polyethylene<br />

mulch-numerical and experimental studies. <strong>Soil</strong> Sci. 131: 82-87.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Pullman, G.S., Devay, J.E., Garber, R.H. and Weinhold, A.R. (1981) <strong>Soil</strong> solarization on<br />

Verticillium wilt <strong>of</strong> cotton and soil borne population <strong>of</strong> Verticillium dahliae, Pythium spp.,<br />

Rhizoctonia solani and Thielaviopsis basicola. Phytopathology. 71:954-959.<br />

• Rao, V. K. and Krishnappa, K. (1995). <strong>Soil</strong> solarization <strong>for</strong> <strong>the</strong> control <strong>of</strong> soil borne pathogen<br />

complexes with special reference to M. incognita and F. oxysporum f.sp. ciceri. Indian<br />

Phytopath. 48: 300-303.<br />

• Rao<strong>of</strong>, M. A. and Nageshwar Rao, T. G. (1997). Effect <strong>of</strong> soil solarization on castor wilt. Indian J.<br />

<strong>Plant</strong> Protect. 25: 154-159.<br />

• Rubin, B and Benjamin, A. 1981. Solar sterilization as a tool <strong>for</strong> weed control. Abstr. Weed Sci.<br />

Soc. Am. p.133.<br />

• Singh, Y. (2008). Effect <strong>of</strong> soil solarization and biocontrol agents on plant growth and<br />

management <strong>of</strong> anthracnose <strong>of</strong> sorghum. Internat. J. Agric. Sci. 4: 188-191.<br />

• Tjamos, EC. 1984. Control <strong>of</strong> Pyrenochaeta lycopersici by combined soil solarization and low dose<br />

<strong>of</strong> methyl bromide in Greece. Acta Hortic. (The Hauge). 152: 253.<br />

• Verma, R. K. Singh, Y., Soni, K. K. and Jamalluddin (2005). Solarization <strong>of</strong> <strong>for</strong>est nursery soil <strong>for</strong><br />

elimination <strong>of</strong> root pathogens and weeds. Indian J. Trop. Biodiv. 13: 81-86.<br />

• Wagonner, PE, Miller, PM and DeRoo, HC. 1960. Plastic mulching principles and benefits. Conn.<br />

Agric. Exp. Stn. Bull. 623, 44 pp.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Microbial <strong>Interactions</strong> in Phyllosphere and Rhizosphere<br />

P.C. Srivastava<br />

Department <strong>of</strong> <strong>Soil</strong> Science, G.B.P.U.A.&T., Pantnagar-263145 (Uttarakhand)<br />

Both positive and negative interactions take place between microbes and also between<br />

microbes and plants. The rhizosphere is a zone <strong>of</strong> predominantly commensal and mutualistic<br />

interactions between plants and microbes. The aerial surfaces <strong>of</strong> plants provide habitats <strong>for</strong> largely<br />

commensal microbes. On <strong>the</strong> negative side, certain viruses, bacteria, and fungi cause plant<br />

diseases that can result in great economic losses and even severe food shortages.<br />

Some <strong>of</strong> <strong>the</strong> positive interactions among plants and microbes are:<br />

<br />

<br />

<br />

Synergistic interactions which include rhizosphere, rhizoplane, phyllosphere and<br />

spermosphere.<br />

Mutualistic interactions which include root nodule interactions, leaf nodule interactions and<br />

mycorrhizal interactions.<br />

Parasitism is <strong>the</strong> only negative interaction among <strong>the</strong> plant and <strong>the</strong> microbes.<br />

Spermosphere<br />

It is <strong>the</strong> volume <strong>of</strong> soil that surrounds a seed with increased microbial activity around a<br />

germinating seed because <strong>of</strong> <strong>the</strong> nutrients leaked into <strong>the</strong> soil by <strong>the</strong> germinating seeds. While<br />

most <strong>of</strong> <strong>the</strong> microbes are harmless, some may be positively beneficial and some <strong>of</strong> <strong>the</strong>m may be<br />

pathogenic. Spermosphere organisms <strong>for</strong>ming <strong>the</strong> normal flora around a germinating seed have<br />

some beneficial effects through biological products like growth hormones. Germinating seeds<br />

excrete certain chemicals which may influence both <strong>the</strong> quality and quantity <strong>of</strong> microbes in <strong>the</strong><br />

vicinity <strong>of</strong> <strong>the</strong> seed.<br />

When a seed is sown in soil, certain interactions take place between <strong>the</strong> seed-borne<br />

micr<strong>of</strong>lora and <strong>the</strong> soil-borne micr<strong>of</strong>lora which influence <strong>the</strong> quality <strong>of</strong> <strong>the</strong> spermosphere at that<br />

condition. When <strong>the</strong> seed is pre-treated with a fungicide or with any o<strong>the</strong>r biological agent, this<br />

influences such interactions to a great extent. For example, <strong>the</strong> fungicide may totally alter <strong>the</strong><br />

seed micr<strong>of</strong>lora by inhibiting some fungal flora and increasing some o<strong>the</strong>r bacterial flora. This<br />

could also influence <strong>the</strong> nature <strong>of</strong> micr<strong>of</strong>lora that is about to colonise <strong>the</strong> rhizosphere. Thus, by<br />

manipulating <strong>the</strong> spermosphere, one changes <strong>the</strong> rhizosphere also. When a seed carrying a<br />

natural or altered load <strong>of</strong> microbes is sown, certain microbes are activated and o<strong>the</strong>rs are<br />

suppressed. Usually, <strong>the</strong> microbes that are artificially loaded onto <strong>the</strong> seed are more dominant<br />

flora <strong>of</strong> <strong>the</strong> seed and this enables <strong>the</strong> scientists to beneficially alter <strong>the</strong> spermosphere <strong>of</strong><br />

a particular seed, as in Rhizobium, Azotobacter and Azospirillum coated seeds. These organisms<br />

get established on <strong>the</strong> root surface <strong>of</strong> <strong>the</strong> germinating seed and benefit <strong>the</strong> plant.<br />

Along with spermosphere micr<strong>of</strong>lora, <strong>the</strong> soil-borne flora may also get activated and<br />

compete with <strong>the</strong> <strong>for</strong>mer (<strong>for</strong> nutrition and space). The chemicals excreted by <strong>the</strong> germinating seed<br />

decide <strong>the</strong> final quality and quantity <strong>of</strong> <strong>the</strong> micr<strong>of</strong>lora around <strong>the</strong> seed. Usually microbes move<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

from <strong>the</strong> spermosphere to <strong>the</strong> rhizosphere within three days. Various chemical treatments <strong>of</strong> <strong>the</strong><br />

seed definitely change <strong>the</strong> rhizosphere micro flora <strong>of</strong> <strong>the</strong> seedling thus indicating <strong>the</strong> plant-rootmicrobes<br />

interactions in <strong>the</strong> soil through <strong>the</strong> seed. When <strong>the</strong> seed is internally or externally<br />

infected by certain pathogenic microorganisms (smut spores), this definitely alters <strong>the</strong> quality and<br />

quantity <strong>of</strong> <strong>the</strong> spermosphere and rhizosphere micr<strong>of</strong>lora (again through competition). When such<br />

a suspected seed is pre-treated with plant protection chemicals, <strong>the</strong> competition is eliminated as<br />

<strong>the</strong> pathogen gets killed and hence <strong>the</strong> seed gets <strong>the</strong> harmless microbes. When <strong>the</strong> seed is pretreated<br />

with organic manure (cow dung) having usual saprophytes present in <strong>the</strong> manure <strong>the</strong>re is<br />

competition between pathogens and non-pathogens saprophytes from <strong>the</strong> organic manure and<br />

depending on <strong>the</strong> efficiency <strong>of</strong> one group, one is suppressed and gets eliminated. For example, a<br />

seed-borne pathogen <strong>of</strong> cotton (Xanthomonas campestris pv malvacearum ) is controlled when<br />

<strong>the</strong> seed is pretreated with cow dung slurry. Fur<strong>the</strong>r, when a pathogen infected seed is sown in<br />

unsterile and sterile soil, <strong>the</strong>re is intense spermospheric effect (enough to suppress <strong>the</strong> pathogen)<br />

in <strong>the</strong> <strong>for</strong>mer whereas in <strong>the</strong> latter case, pathogen becomes highly virulent in <strong>the</strong> absence <strong>of</strong> o<strong>the</strong>r<br />

organisms.<br />

Rhizosphere<br />

Rhizosphere is <strong>the</strong> region where soil and roots <strong>of</strong> <strong>the</strong> plants make contact. Rhizosheath is<br />

a modification <strong>of</strong> rhizosphere, characterized by a relatively thick soil cylinder that adheres to <strong>the</strong><br />

plant roots. When <strong>the</strong> roots are cleaned <strong>of</strong> all <strong>the</strong> soil particles adhering to it and <strong>the</strong>n plated,<br />

microorganisms can be seen developing indicating that <strong>the</strong>re are certain microbes intimately<br />

associated with <strong>the</strong> root surface. Some fungi inhabit <strong>the</strong> root surface in a mycelial state,<br />

e.g.Cephalosporium, Trichoderma and Penicillium. Specific bacteria also get embedded on <strong>the</strong><br />

surface <strong>of</strong> <strong>the</strong> root with <strong>the</strong> help <strong>of</strong> mucilaginous external layer normally present in <strong>the</strong> actively<br />

growing root system.<br />

Effect <strong>of</strong> <strong>Plant</strong> Root on Microbial Populations<br />

The structure <strong>of</strong> <strong>the</strong> plant root system contributes to <strong>the</strong> establishment <strong>of</strong> <strong>the</strong> rhizosphere<br />

microbial population. The interactions <strong>of</strong> plant roots and rhizosphere microorganisms are based<br />

largely on interactive modification <strong>of</strong> <strong>the</strong> soil environment by processes such as water uptake by<br />

<strong>the</strong> plant and release <strong>of</strong> organic chemicals by <strong>the</strong> roots. The influence <strong>of</strong> <strong>the</strong> plant root on <strong>the</strong><br />

micr<strong>of</strong>lora is governed by root exudates, physical and chemical factors in <strong>the</strong> soil.<br />

Effect <strong>of</strong> root exudates<br />

This is <strong>the</strong> major factor that governs <strong>the</strong> micr<strong>of</strong>lora <strong>of</strong> <strong>the</strong> rhizosphere. The root exudates<br />

include: Simple sugars such as glucose and fructose Di, tri and oligo saccharides . All common<br />

amino acids - alanine, serine, leucine, valine, glutamic and asparitic acids. Of <strong>the</strong>se, glutamine and<br />

asparagine are produced in large amounts. O<strong>the</strong>r compound are vitamin like thiamine and biotin,<br />

nucleotides, flavones and auxins. All <strong>the</strong>se root exudates have an effect on <strong>the</strong> rhizosphere<br />

micr<strong>of</strong>lora. Some <strong>of</strong> <strong>the</strong> root exudates like <strong>the</strong> amino acids promote <strong>the</strong> growth <strong>of</strong> micr<strong>of</strong>lora in <strong>the</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

rhizosphere. Some nitrogen fixers such as Azospirillum, Azotobacter paspali use <strong>the</strong> root exudates<br />

as <strong>the</strong> energy source <strong>for</strong> significant nitrogen fixation. Root exudates containing toxic substances<br />

such as glycosides and hydrocyanic acid may inhibit <strong>the</strong> growth <strong>of</strong> pathogens. One <strong>of</strong> <strong>the</strong><br />

attributes <strong>of</strong> root exudates is <strong>the</strong> possible role <strong>the</strong>y play in neutralising <strong>the</strong> soil pH and altering <strong>the</strong><br />

microclimate <strong>of</strong> <strong>the</strong> rhizosphere through liberation <strong>of</strong> water and CO 2 , such changes may influence<br />

infections <strong>of</strong> roots by pathogenic fungi.<br />

Effect <strong>of</strong> plant growth on rhizosphere micr<strong>of</strong>lora<br />

The rhizosphere micr<strong>of</strong>lora may undergo successional changes as <strong>the</strong> plant grows from<br />

germination to maturity. During plant development, a distinct rhizosphere succession results in<br />

rapidly growing, growth factor-requiring, opportunistic microbial population. These successional<br />

changes correspond to changes in <strong>the</strong> materials released by <strong>the</strong> plant root to <strong>the</strong> rhizosphere<br />

during plant maturation. Initially, carbohydrate and mucilaginous exudates from plant roots<br />

stimulate <strong>the</strong> growth <strong>of</strong> microorganisms rapidly within <strong>the</strong> grooves on <strong>the</strong> root surface and within<br />

<strong>the</strong> mucilaginous sheath (rhizoplane). After <strong>the</strong> plant matures, autolysis <strong>of</strong> some <strong>of</strong> <strong>the</strong> root<br />

materials takes place and simple sugars and amino acids are released into <strong>the</strong> soil. This fur<strong>the</strong>r<br />

stimulates <strong>the</strong> growth <strong>of</strong> bacteria with high intrinsic growth rates, e.g. Pseudomonas. As a result <strong>of</strong><br />

<strong>the</strong>se effects, <strong>the</strong> rhizosphere micr<strong>of</strong>lora consists <strong>of</strong> higher proportion <strong>of</strong> gram negative rods and a<br />

lower proportion <strong>of</strong> gram positive rods, cocci and pleomorphic <strong>for</strong>ms. A relatively higher proportion<br />

<strong>of</strong> motile, rapidly growing bacteria are also seen.<br />

Alteration <strong>of</strong> rhizosphere micr<strong>of</strong>lora<br />

<strong>Soil</strong> amendments<br />

This refers to <strong>the</strong> artificial addition <strong>of</strong> amendments and chemical fertilisers supplying N, P<br />

and K. This depends on <strong>the</strong> rhizosphere: soil (R:S) ratio and also on <strong>the</strong> nutritional content <strong>of</strong> <strong>the</strong><br />

chemicals in <strong>the</strong> soil.<br />

Foliar application <strong>of</strong> nutrients<br />

Normal translocation <strong>of</strong> photosynthates from leaves to roots does not affect <strong>the</strong> micr<strong>of</strong>lora.<br />

However, when foliar application <strong>of</strong> antibiotics, growth regulators, pesticides and inorganic<br />

nutrients is carried out, a small amount is being released as root exudates and this can ei<strong>the</strong>r<br />

promote <strong>the</strong> growth <strong>of</strong> <strong>the</strong> present micr<strong>of</strong>lora or change <strong>the</strong> micr<strong>of</strong>lora to some extent.<br />

Artificial inoculation<br />

This is done on seed or soil with preparation containing live microorganisms especially<br />

bacteria (bacterisation). This provides an easier way <strong>for</strong> <strong>the</strong> establishment <strong>of</strong> <strong>the</strong> desired microbes<br />

to <strong>the</strong> rhizosphere. This is because as <strong>the</strong> seed is coated with <strong>the</strong> live microorganisms, as soon as<br />

<strong>the</strong> root evolves, <strong>the</strong> colonising <strong>of</strong> <strong>the</strong> root takes place and establishment <strong>of</strong> <strong>the</strong> o<strong>the</strong>r microbes is<br />

also made possible. Microbial seed inoculants generally used are Azotobacter, Beijerinckia,<br />

Rhizobium or P solubilising microorganisms.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Effect <strong>of</strong> Rhizosphere Microbial Population on <strong>Plant</strong>s<br />

The microorganisms have a marked influence on <strong>the</strong> growth <strong>of</strong> plants. <strong>Plant</strong> growth may be<br />

impaired due to <strong>the</strong> absence <strong>of</strong> appropriate rhizosphere micr<strong>of</strong>lora. The microbial population affect<br />

<strong>the</strong> plant growth in various ways:<br />

Promotion <strong>of</strong> growth<br />

This is brought about by <strong>the</strong> release <strong>of</strong> growth factors like auxins and gibberellins that<br />

promote plant growth. The organisms which release <strong>the</strong>se growth factor include Arthrobacter,<br />

Pseudomonas and Agrobacterium. The production <strong>of</strong> indole acetic acid (IAA), a plant growth<br />

hormone by <strong>the</strong> certain group <strong>of</strong> microorganisms increases <strong>the</strong> rate <strong>of</strong> seed germination and<br />

development <strong>of</strong> root hairs.<br />

Neutralisation <strong>of</strong> toxic substances<br />

This is seen in <strong>the</strong> case <strong>of</strong> plants that grow in flooded sediments e.g. rice. In this case,<br />

<strong>the</strong>re is production <strong>of</strong> hydrogen sulphide generated by <strong>the</strong> sulphate reduction pathway. This<br />

hydrogen sulphide is toxic to <strong>the</strong> plant roots, and this is neutralised by <strong>the</strong> bacteria Beggiatoa. This<br />

is a microaerophilic, catalase negative, sulphide oxidizing filamentous bacterium. This acquires <strong>the</strong><br />

oxygen and catalase enzyme from <strong>the</strong> rice plant and aids in <strong>the</strong> oxidation <strong>of</strong> toxic H 2 S to harmless<br />

S or SO -2 4 , thus protecting <strong>the</strong> rice roots.<br />

Allelopathic effect<br />

Some substances by <strong>the</strong> microbes can have an antagonistic effect too. Some<br />

extracellular products <strong>of</strong> certain microorganisms lead to <strong>the</strong> growth <strong>of</strong> o<strong>the</strong>r kinds <strong>of</strong><br />

microorganisms that can provide a better rhizosphere micr<strong>of</strong>lora. These extracellular products can<br />

also inhibit <strong>the</strong> growth <strong>of</strong> pathogens, thus protecting <strong>the</strong> plant roots from getting damaged.<br />

Nutrient recycling<br />

The nutrients in <strong>the</strong> soil are made available to <strong>the</strong> plants by mobilisation <strong>of</strong> <strong>the</strong> nutrients, by<br />

fixing it in soil. Sometimes, <strong>the</strong> nutrients are made unavailable by immobilisation. For example,<br />

microorganisms produce extracellular amino acids, vitamins, etc. using <strong>the</strong> nutrients and N fixation<br />

process. They make N available to plants as nitrates or o<strong>the</strong>r inorganic <strong>for</strong>ms, e.g. Rhizobium and<br />

Azotobacter. Similarly, sulphur oxidisers make sulphur available as sulphates, e.g. Desulfovibrio.<br />

Phosphorous is made available as phosphates by <strong>the</strong> production <strong>of</strong> acids by <strong>the</strong> micr<strong>of</strong>lora.<br />

Siderophore production is ano<strong>the</strong>r important characteristic feature <strong>of</strong> rhizosphere micr<strong>of</strong>lora. Many<br />

microorganisms respond to a fall in <strong>the</strong> availability <strong>of</strong> iron in soil by producing extracellular low<br />

molecular weight iron transporting agents known as siderophores. These siderophores selectively<br />

complex with iron and supply Fe to <strong>the</strong> living cell. They also act as growth factors or antibiotics.<br />

For example, Pseudomonas fluorescence (one strain produced a siderophore compound<br />

‘pseudobactin’ inhibits <strong>the</strong> growth <strong>of</strong> a pathogen Eewinia carotovora by chelating iron in <strong>the</strong> vicinity<br />

<strong>of</strong> <strong>the</strong> pathogen to reduce <strong>the</strong> disease severity. Thus, microorganisms increase <strong>the</strong> recycling and<br />

solubilisation <strong>of</strong> mineral nutrients and making it available to plants. The abundant growth <strong>of</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

microbial population in <strong>the</strong> rhizosphere can sometimes create a deficiency <strong>of</strong> required minerals <strong>for</strong><br />

<strong>the</strong> plants, e.g. bacterial immobilisation <strong>of</strong> Zn and oxidation <strong>of</strong> Mn cause <strong>the</strong> plant diseases 'little<br />

leaf' <strong>of</strong> fruit trees and ' gray speck' <strong>of</strong> oats. Nitrogen is immobilised in <strong>the</strong> <strong>for</strong>m <strong>of</strong> microbial protein<br />

and some may be lost to <strong>the</strong> atmosphere by denitrification.<br />

Phyllosphere<br />

Phyllosphere refers to <strong>the</strong> quality and quantity <strong>of</strong> microorganisms found on <strong>the</strong> surface <strong>of</strong><br />

<strong>the</strong> leaves and differs with <strong>the</strong> age <strong>of</strong> .<strong>the</strong> plant, leaf area, morphology, atmospheric factors<br />

(temperature, humidity,etc.). Growing seasons may also influence <strong>the</strong> phyllosphere micr<strong>of</strong>lora. It<br />

increases and reaches <strong>the</strong> maximum in autumn when <strong>the</strong> leaves severe.<br />

The position <strong>of</strong> <strong>the</strong> leaves also plays a role in determining <strong>the</strong> micr<strong>of</strong>lora. Leaves at <strong>the</strong><br />

lower levels harbour more microorganisms since <strong>the</strong>y are sheltered and get more nutrients from<br />

<strong>the</strong> raindrops from upper levels. <strong>Plant</strong> leaves are exposed to dust and air currents resulting in <strong>the</strong><br />

establishment <strong>of</strong> a typical flora on <strong>the</strong>ir surface aided by cuticle, waxes and appendages (thorns,<br />

spikes) which help in <strong>the</strong> anchorage <strong>of</strong> microbes. The leaf diffusates/ exudates promote/ deter <strong>the</strong><br />

growth <strong>of</strong> microbes on <strong>the</strong>ir surface. The principal nutritive factor in <strong>the</strong> leaf are amino acids,<br />

glucose, fructose and sucrose. The dominant microorganisms in a <strong>for</strong>est vegetation are <strong>the</strong><br />

nitrogen fixing bacteria such as Beijerinckia and Azotobacter. O<strong>the</strong>r genera like Pseudomonas,<br />

Enwinia, Sarcina have been encountered in <strong>the</strong> phyllosphere. Under damp conditions, some<br />

leaves may harbour cyanobacteria like Anabaena, Calothrix, Nostoc and Tolypothrix on <strong>the</strong>ir<br />

surfaces. Some <strong>of</strong> <strong>the</strong> fungi and actinomycetes encountered are Cladosporium, Alternaria,<br />

Cercospora, Helminthosporium, Mucor and Streptomyces species.<br />

Characteristic Features <strong>of</strong> Phyllosphere Micr<strong>of</strong>lora<br />

Leaf surface microbes may per<strong>for</strong>m an effective function in controlling <strong>the</strong> spread <strong>of</strong> air<br />

borne microbes inciting plant diseases. Presence <strong>of</strong> a fungal spore on <strong>the</strong> surface <strong>of</strong> leaves incite<br />

<strong>the</strong> <strong>for</strong>mation <strong>of</strong> a chemical substance referred to as phytoalexin which are active in host- defence<br />

mechanisms. Resistance to disease causing microbes has also been attributed to fungistatic<br />

compounds secreted by leaves such as malic acid from leaves <strong>of</strong> Cicer arietinum. The name<br />

‘elicitor’ has been commonly used to denote <strong>the</strong> compounds which induce <strong>the</strong> syn<strong>the</strong>sis<br />

<strong>of</strong> phytoalexins. These are biotic elicitors such as polysaccharides from fungal cell walls, lipids,<br />

microbial enzymes and polypeptides. Abiotic elicitors are heavy metal salts, detergents, UV light,<br />

etc. Epiphytic microbes are known to syn<strong>the</strong>sise indole acetic acid. PhylIosphere bacteria are<br />

<strong>of</strong>ten pigmented due to direct solar radiation. Pink-pigmented facultative methylotrophs are<br />

common in <strong>the</strong> phyllosphere. Bacteria can serve as ice nucleators, promoting frost damage to<br />

plants. Genetically modified Pseudomonas syringaea lacks a membrane protein that promotes<br />

nucleation. Inoculating crops with this organism can lower <strong>the</strong> temperature at which frost damage<br />

occurs. Azolla-Anabaena symbiosis is a N fixing association where cyanobacteria live on leaf<br />

surface. Any change in phyllosphere affects plant growth which in turn affects <strong>the</strong> physiological<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

activity <strong>of</strong> root system. Such changes in <strong>the</strong> root result in an altered pH and spectrum <strong>of</strong> chemical<br />

exudation causing a change in rhizosphere micr<strong>of</strong>lora. Thus , <strong>the</strong>re is a link between phyllosphere<br />

micr<strong>of</strong>lora and rhizosphere micr<strong>of</strong>lora. There is a continuous diffusion <strong>of</strong> plant metabolites from <strong>the</strong><br />

leaves which support <strong>the</strong> microbial growth and in turn <strong>the</strong>se microbes protect <strong>the</strong> plant from<br />

pathogens.<br />

Positive <strong>Interactions</strong> <strong>of</strong> <strong>Plant</strong>s and <strong>Microbe</strong>s<br />

Fungal mutualistic interactions are pronounced in plants.<br />

Leaf Nodule<br />

Symbiotic association <strong>of</strong> certain bacterial endophytes with leaves <strong>of</strong> certain plants (usually<br />

belonging to <strong>the</strong> families Rubiaceae and Myrsinaceae) leads to <strong>the</strong> <strong>for</strong>mation <strong>of</strong> nodule like<br />

structures on <strong>the</strong> leaves. The plants Psychotria, Pavetta, Chomelia have received considerable<br />

importance as leaf nodule producing plants. Isolates <strong>of</strong> bacteria that have gained importance in<br />

<strong>for</strong>mation <strong>of</strong> leaf nodules are Mycobacterium rubiacearum, Mycoplana rubra, Flavobacterium<br />

species, Bacterium rubiacearum, Phyllobacterium rubiacearum and Klebsiella rubiacearum. There<br />

are not many advantages (<strong>for</strong> <strong>the</strong> plants) resulting from this sort <strong>of</strong> mutualistic interactions apart<br />

from <strong>the</strong> fact that <strong>the</strong> bacterial partners secrete phytohormones (cytokines) <strong>for</strong> <strong>the</strong> growth <strong>of</strong> <strong>the</strong><br />

plants. The plants definitely provide shelter and photosynthates <strong>for</strong> <strong>the</strong> survival <strong>of</strong> <strong>the</strong>ir bacterial<br />

partners. Since <strong>the</strong>y <strong>for</strong>m a stable phyllospheric micr<strong>of</strong>lora with <strong>the</strong> plants, <strong>the</strong>se bacterial<br />

partners may also prevent <strong>the</strong> entry <strong>of</strong> pathogenic spores from entering through <strong>the</strong> leaves and<br />

establishing <strong>the</strong>mselves.<br />

Mycorrhiza<br />

They occur on almost all terrestrial plants though not as specific as N fixing symbiosis.<br />

Thus a plant may have several mycorrhizae that can <strong>for</strong>m symbiosis with its roots. Extent <strong>of</strong><br />

symbiosis depends on soil fertility. High soil fertility leads to low mycorrhizal infection and poor<br />

symbiosis and vice versa. Roots supply carbohydrates to <strong>the</strong> fungi which absorb nutrients <strong>for</strong>m <strong>the</strong><br />

soil and supply <strong>the</strong>m to <strong>the</strong> crop.<br />

Ectomycorrhiza<br />

Ectomycorrhizal symbiosis is a mutually beneficial union between roots <strong>of</strong> higher plants<br />

and <strong>the</strong> typical ectomycorrhizal fungi are basidiomycetes (Agaricus), ascomycetes or<br />

phycomycetes members. Ectomycorrhizae have poor competitive saprophytic ability hence <strong>the</strong>y<br />

have a tough time competing with o<strong>the</strong>r microbes in <strong>the</strong> soil. The fungal hyphae on <strong>the</strong> exterior <strong>of</strong><br />

<strong>the</strong> roots usually serve as an extension <strong>of</strong> roots and store large amounts carbohydrates<br />

Endomycorrhiza<br />

In this case, <strong>the</strong> fungal hyphae penetrate <strong>the</strong> host root cells. They are quite common<br />

among <strong>the</strong> Ericaceae and Orchidaceae members <strong>of</strong> higher plants as well as fruit trees like citrus,<br />

c<strong>of</strong>fee, rubber, etc.<br />

Vesicular-arbuscular mycorrhiza (VAM) fungi: These are geographically ubiquitous and are<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

commonly found in association with agricultural crops, shrubs, tropical tree species and some<br />

temperate trees. Their nutritional requirements are not specific. VAM associations are <strong>for</strong>med by<br />

non-septate Zygomycetes and Phycomycetes fungi. Some examples are Glomus, Gigaspora,<br />

Acaulospora, Entrophospora and Scutellospora. Glomus is <strong>the</strong> most common fungus. The fungi<br />

are obligate biotrophs and do not grow on syn<strong>the</strong>tic media. Phosphate transfer possibly occurs<br />

across living membranes <strong>of</strong> <strong>the</strong> host and <strong>the</strong> fungus via arbuscles. VAM fungi interact with o<strong>the</strong>r<br />

soil microbes like <strong>the</strong> free-living and symbiotic N fixers and P solubilisers to improve <strong>the</strong>ir<br />

efficiency <strong>for</strong> <strong>the</strong> biochemical cycling <strong>of</strong> nutrients to <strong>the</strong> host plants.<br />

Negative Interaction between <strong>Plant</strong>s And <strong>Microbe</strong>s<br />

Parasitism is <strong>the</strong> only negative interaction between <strong>the</strong> plants and microbes. As parasites,<br />

<strong>the</strong> microbes, like bacteria, fungi, viruses and algae, cause infections in <strong>the</strong> host plant leading <strong>the</strong><br />

development <strong>of</strong> disease and loss <strong>of</strong> commercial value in case <strong>the</strong> host plant is an agricultural crop.<br />

To cause <strong>the</strong> disease, <strong>the</strong> parasite must accomplish two important things:<br />

1. It must enter <strong>the</strong> host plant.<br />

2. It must establish itself at <strong>the</strong> specific target site within <strong>the</strong> plant.<br />

3. The parasite must overcome <strong>the</strong> plant defence mechanisms and causes <strong>the</strong> disease.<br />

These interactions are ei<strong>the</strong>r biotrophic to obtain nutrition from <strong>the</strong> plant <strong>for</strong> a long time<br />

without instantaneous killing <strong>of</strong> <strong>the</strong> plant or necrotrophic wherein <strong>the</strong> pathogen kills <strong>the</strong> host and<br />

obtains <strong>the</strong> nutrition from <strong>the</strong> dead tissues.<br />

REFERENCES<br />

• Fokkema, N. J., and B. Schippers. 1986. Phyllosphere vs rhizosphere as environments <strong>for</strong><br />

saprophytic colonization. p. 137-159. In N. J. Fokkema and J. Van den Heuvel (ed.),<br />

Microbiology <strong>of</strong> <strong>the</strong> phyllosphere. Cambridge University Press, London, UK.<br />

• Mercier, J., and S. E. Lindow. 2001. Field per<strong>for</strong>mance <strong>of</strong> antagonistic bacteria identified in a<br />

novel laboratory assay <strong>for</strong> biological control <strong>of</strong> fire blight <strong>of</strong> pear. Biol. Control 22:66-<br />

71.<br />

• Morris, C. E., and L. L. Kinkel. 2002. Fifty years <strong>of</strong> phylosphere microbiology: significant<br />

contributions to research in related fields, p. 365-375. InIn S. E. Lindow, E. I. Hecht-<br />

Poinar, and V. Elliott (ed.), Phyllosphere microbiology. APS Press, St. Paul, Minn.<br />

• Andrews, J. H., and R. F. Harris. 2000. The ecology and biogeography <strong>of</strong> microorganisms on plant<br />

surfaces. Annu. Rev. Phytopathol. 38:145-180.<br />

• Beattie, G. A., and S. E. Lindow. 1999. Bacterial colonization <strong>of</strong> leaves: a spectrum <strong>of</strong> strategies.<br />

Phytopathology 89:353-359.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Exploiting Nematophagus Fungi <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> Root-Knot<br />

Nematodes<br />

Rakesh Pandey<br />

Microbial Technology & Nematology, CSIR-Central Institute <strong>of</strong> Medicinal and Aromatic <strong>Plant</strong>s, P.O.CIMAP,<br />

Lucknow - 226 015 (UP)<br />

An unseen, underground and hidden, enemy pest, which silently spread from nursery to<br />

nursery, and field-to-field, attacking most <strong>of</strong> <strong>the</strong> agricultural crops including medicinal and aromatic<br />

crops throughout <strong>the</strong> world is plant parasitic nematode. <strong>Plant</strong> parasitic nematodes are microscopic<br />

roundworms that live in diverse habitats viz. soil and plant tissues. Due to obligate nature <strong>of</strong> <strong>the</strong>se<br />

parasites, nematodes attack <strong>the</strong> root or o<strong>the</strong>r plant parts in soil like bulb and tubers, and interrupt<br />

<strong>the</strong> uptake <strong>of</strong> water and nutrients by plants. The annual global loss in agriculture due to damage<br />

by variety <strong>of</strong> phytonematodes can be estimated as more than US$125 billion worldwide. Besides<br />

direct damage some plant parasitic nematodes transmit plant viruses and also interact with fungi<br />

and bacteria to enhance damage several folds. Organic soil amendments have been reported by a<br />

large number <strong>of</strong> researchers to manage nematode problem but <strong>the</strong> large quantities required per<br />

unit area renders <strong>the</strong> strategy largely inapplicable in large scale farming enterprises. The assault<br />

on <strong>the</strong> environment through <strong>the</strong> use <strong>of</strong> chemical nematicides as well as unreliable results from<br />

cultural methods <strong>of</strong> nematode management has necessitated <strong>the</strong> search <strong>for</strong> sustainable, effective<br />

and environmentally acceptable nematode management options. Rhizosphere is <strong>the</strong> site <strong>of</strong><br />

intensive interaction between plant and o<strong>the</strong>r rhizospheric microbes. Rhizospheric flora has<br />

reportedly immense potential <strong>for</strong> soil and plant health. But this all depend on <strong>the</strong> density and types<br />

<strong>of</strong> microbes. Useful microbes like PGPR, mutualistic fungi, and o<strong>the</strong>r nematode antagonists<br />

disfavor <strong>the</strong> multiplication and development <strong>of</strong> phytonematode population in soil, enhancing <strong>the</strong><br />

growth/yield <strong>of</strong> <strong>the</strong> crop. For example when nematode population density reaches a certain level,<br />

host crop yields suffer greatly as few host plant support faster multiplication <strong>of</strong> nematodes and<br />

o<strong>the</strong>rs do not. For sustainable cultivation <strong>of</strong> medicinal and aromatic plants, effective management<br />

<strong>of</strong> plant parasitic nematodes is essential. As my group begins to develop a better understanding <strong>of</strong><br />

<strong>the</strong> complex ecologies <strong>of</strong> soils and agricultural ecosystems, more strategies <strong>for</strong> exploitation <strong>of</strong><br />

microbes <strong>for</strong> <strong>the</strong> management <strong>of</strong> plant parasitic nematodes will be developed. The suggested<br />

characteristics <strong>of</strong> microbes <strong>for</strong> nematode management and better crop health include host<br />

specificity, easy in vitro/in vivo manipulation, mass production and easy dissemination with<br />

standard equipments. Besides it should also have potential <strong>for</strong> establishment and recycling, longer<br />

shelf life providing control <strong>for</strong> extended periods and should not be harmful to <strong>the</strong> environment.<br />

Following types <strong>of</strong> Nematophagus fungi are utilized to manage <strong>the</strong> population <strong>of</strong> plant parasitic<br />

nematodes.<br />

‣ Nematode Trapping Fungi<br />

o<br />

Adhesive Networks<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

o Adhesive Knobs<br />

o Nonconstricting Rings<br />

o Constricting Rings<br />

o Adhesive Conidia<br />

‣ Zoosporic Fungi<br />

‣ Parasites <strong>of</strong> Nematode Eggs<br />

Each group <strong>of</strong> Nematophagus fungi utilizes a different type <strong>of</strong> structure to adhere or attack<br />

<strong>the</strong> nematodes. For nematode trapping fungi, this is thought to be mainly a passive activity with<br />

<strong>the</strong> fungus waiting <strong>for</strong> <strong>the</strong> nematode to pass by and become stuck to knobs, networks, or conidia.<br />

The fungi which <strong>for</strong>m rings have been shown to <strong>for</strong>m more rings in <strong>the</strong> presence <strong>of</strong> nematodes<br />

than in <strong>the</strong>ir absence. Fungal hyphae <strong>the</strong>n penetrate <strong>the</strong> nematode body and utilize it <strong>for</strong> <strong>the</strong>ir<br />

nutrition.<br />

Major fungi which are involved to manage nematode population are Trichoderma<br />

harzianum, Hirsutella rhossiliensis, Hirsutella minnesotensis, Verticillium chlamydosporum,<br />

Arthrobotrys dactyloides, Paceilomyces lilacinus, Myro<strong>the</strong>cium verrucaria etc. Few bacteria are<br />

also reported against phytonematodes are: Pasteuria penetrans (<strong>for</strong>merly known as Bacillus<br />

penetrans), Bacillus thuringiensis (available in insecticidal <strong>for</strong>mulations) and Burkholderia cepacia,<br />

Pseudomonas fluorescens, Bacillus subtilis, Bacillus chitinosporus etc.<br />

It is clear that <strong>the</strong>re is a wide range <strong>of</strong> organisms that feed on, kill, or repel nematodes.<br />

These organisms are most effective, and are found most commonly, in healthy, well-managed soil.<br />

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Introduction<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Soil</strong> Fertility in Organic Farming System<br />

D.K. Singh and Manisha Rani<br />

Department <strong>of</strong> Agronomy, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Organic farming has expanded rapidly in recent years and is seen as a sustainable<br />

alternative to chemical-based agricultural systems (Stockdale et al., 2001; Biao et al., 2003; Avery,<br />

2007). Its annual growth rate has been about 20% <strong>for</strong> <strong>the</strong> last decade (Lotter, 2003), accounting<br />

<strong>for</strong> over 31 million hectares (ha) and generating over 26 billion US dollars in annual trade<br />

worldwide (Yussefi, 2006). Nutrient management in organic farming systems is <strong>of</strong>ten based on soil<br />

fertility building via nitrogen (N) fixation and nutrient recycling <strong>of</strong> organic materials, such as<br />

farmyard manure and crop residues, with limited inputs from permitted fertilizers (Gosling and<br />

Shepherd, 2005). Although organic farming has been criticized <strong>for</strong> relying on <strong>the</strong> build-up <strong>of</strong> soil<br />

phosphorus (P) and potassium (K) by past fertilization be<strong>for</strong>e converting to its acceptance and<br />

popularity are growing due mostly to environmental and health related concerns (Biao et al., 2003;<br />

Galantini and Rosell, 2006). A recent polling <strong>of</strong> residents <strong>of</strong> Ontario, Canada reveals that more<br />

than half think organic food is more nutritious; two-thirds believe organic food is safer than<br />

conventionally grown food; and 9 out <strong>of</strong> 10 believe organic fruits and vegetables are grown without<br />

pesticides <strong>of</strong> any kind (Avery, 2007).<br />

“Organic agriculture is a holistic production management system which promotes and enhances<br />

agro-ecosystem health, including biodiversity, biological cycles and soil biological activity. It<br />

emphasizes <strong>the</strong> use <strong>of</strong> management practices in reference to <strong>the</strong> use <strong>of</strong> <strong>of</strong>f –farm inputs, taking<br />

into account that conditions required locally adopted systems. This is accomplished by using,<br />

where possible, agronomic, biological and mechanical methods as opposed to using syn<strong>the</strong>tic<br />

materials to fulfill any specific function within <strong>the</strong> system” (FAO/WHO Codex Alimentarius<br />

Guidelines, 1999)”<br />

Components <strong>of</strong> <strong>Soil</strong> Fertility<br />

The use <strong>of</strong> <strong>the</strong> term ‘soil fertility’ is <strong>of</strong> little value unless <strong>the</strong> physical, chemical and<br />

biological properties <strong>of</strong> soil that contribute to its fertility are all considered (Abbott and Murphy,<br />

2003).<br />

<strong>Soil</strong> Physical Fertility<br />

<strong>Soil</strong> physical fertility contributes to <strong>the</strong> sustainability <strong>of</strong> organic farming systems by creating<br />

<strong>the</strong> framework in which biological and chemical processes supply nutrients to plants protect soil<br />

from erosion. <strong>Soil</strong> fertility in organically managed systems is generally improved compared to<br />

conventional practices (Glover et al., 2000, Shepherd et al., 2002) due to <strong>the</strong> beneficial effects <strong>of</strong><br />

increased organic matter inputs on soil organisms and soil structure. Organic matter does little to<br />

improve soil aggregation, without <strong>the</strong> activity <strong>of</strong> soil organisms. Improved soil structure and root<br />

growth may be critical in organic farming systems <strong>for</strong> effectively using soil reserves <strong>of</strong> nutrients<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

and poorly soluble fertilizers and <strong>for</strong> preventing nitrogen (N) leaching from mineralizing legume<br />

residues (Thorup-Kristensen, 2001). In some situation, soil physical characteristics are more<br />

dependent on soil type than on management (Drinkwater et al., 1995).<br />

<strong>Soil</strong> Chemical Fertility<br />

Chemical fertility <strong>of</strong> <strong>the</strong> soil depends to a large degree on low management practices<br />

facilitate beneficial biological processes. The chemical fertility <strong>of</strong> soil reflects its capacity to provide<br />

a suitable chemical and nutritional environment to plants (Stockdate et al., 2002) and to support<br />

biological and physical processes (Abbott and Murphy, 2003). Traditional methods <strong>for</strong> prediction<br />

fertilizer applications <strong>for</strong> building and maintaining soil chemical fertility may not be appropriate in<br />

organic farming systems (Oberson et al., 1993, Condron et al., 2000, Watson et al., 2002 a).<br />

<strong>Soil</strong> Biological Fertility<br />

<strong>Soil</strong> biological fertility refers to soil processes involving organisms that improve plant<br />

growth both directly (e.g. symbiosis with root nodule bacteria and mycorrhizal fungi) and indirectly,<br />

through <strong>the</strong>ir depicts on soil chemical fertility (e.g. organic matter mineralization and mineral<br />

dissolution) and physical fertility (e.g. soil aggregation) (lee and Pankhurst 1992, Degens 1997).<br />

<strong>Soil</strong> biological fertility can be quantified by measuring <strong>the</strong> size, activity, diversity and function <strong>of</strong><br />

communities. A soil’s capacity to support biological fertility is determined by inherent physical and<br />

chemical characteristics as well as management practices. Organic farming may alter <strong>the</strong> function<br />

<strong>of</strong> <strong>the</strong> soil microbial community, increasing its ability to release nutrients <strong>for</strong>m organic and poorly<br />

soluble sources, <strong>the</strong>reby compensation <strong>for</strong> <strong>the</strong> absence <strong>of</strong> soluble nutrient inputs (Oberson et al.,<br />

1993; Penfold et al., 1995; AQIS, 1998; Ryan, 1999). Practices that enhance function <strong>of</strong><br />

arbuscular mycorrhizal (AM) fungi and root nodule bacteria have potential to improve some<br />

aspects <strong>of</strong> soil biological and chemical fertility.<br />

The four principles <strong>of</strong> organic agriculture are as follows:<br />

Principle <strong>of</strong> health<br />

Organic Agriculture should sustain and enhance <strong>the</strong> health <strong>of</strong> soil, plant, animal, human<br />

and planet as on and indivisible. This principle points out that <strong>the</strong> health <strong>of</strong> individuals and<br />

communities cannot be separated from <strong>the</strong> health <strong>of</strong> ecosystem - healthy soils produce healthy<br />

crops that foster <strong>the</strong> health <strong>of</strong> animals and people. The role <strong>of</strong> organic agriculture, whe<strong>the</strong>r in<br />

farming, processing, distribution, or consumption, is to sustain and enhance <strong>the</strong> health <strong>of</strong><br />

ecosystems and organisms from <strong>the</strong> smallest in <strong>the</strong> soil to human beings. In particular, organic<br />

agriculture is intended to produce high quality, nutritious food that contributes to preventive health<br />

care and well-being. In view <strong>of</strong> this it should avoid <strong>the</strong> use <strong>of</strong> fertilizers, pesticides, animal drugs<br />

and food additives that may have adverse health effects.<br />

Principle <strong>of</strong> ecology<br />

Organic Agriculture should be based on living ecological systems and cycles, work with<br />

<strong>the</strong>m, emulate <strong>the</strong>m and help sustain <strong>the</strong>m. This principle roots organic agriculture within living<br />

ecological systems. It states that production is to be based on ecological processes, and recycling.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Nourishment and will-being are achieved through <strong>the</strong> ecology <strong>of</strong> <strong>the</strong> specific production<br />

environment. For example, in <strong>the</strong> case <strong>of</strong> crops this is <strong>the</strong> living soil; <strong>for</strong> animals it is <strong>the</strong> farm<br />

ecosystem; <strong>for</strong> fish and marine organisms, <strong>the</strong> aquatic environment.<br />

Principle <strong>of</strong> fairness<br />

Organic Agriculture should build on relationships that ensure fairness with regard to <strong>the</strong><br />

common environment and life opportunities. Fairness is characterized by equity, respect, justice<br />

and stewardship <strong>of</strong> <strong>the</strong> shared world, both among people and in <strong>the</strong>ir relations to o<strong>the</strong>r living<br />

beings. This principle emphasizes that those involved in organic agriculture should conduct human<br />

relationships in a manner that ensures fairness at all levels and to all parties- farmers, workers,<br />

processors, distributors, traders and consumers.<br />

Principle <strong>of</strong> care<br />

Organic Agriculture should be managed in a precautionary and responsible manner to<br />

protect <strong>the</strong> health and well being <strong>of</strong> current and future generations and <strong>the</strong> environment. Organic<br />

agriculture is a living and dynamic system that responds to internal and external demands and<br />

conditions. Practitioners <strong>of</strong> organic agriculture can enhance efficiency and increase productivity,<br />

but this should not be at <strong>the</strong> risk <strong>of</strong> jeopardizing health and well-being.<br />

World <strong>of</strong> Organic Agriculture<br />

According to <strong>the</strong> latest FiBL-IFOAM survey on certified organic agriculture worldwide (as<br />

on end <strong>of</strong> 2010) data on organic agriculture are available from 160 countries. There are 37<br />

million hectares <strong>of</strong> organic agricultural land (including in-conversion areas). The regions with <strong>the</strong><br />

largest areas <strong>of</strong> organic agricultural land are Oceania (12.1 million hectares), Europe (10 million<br />

hectares), and Latin America (8.4 million hectares). The countries with <strong>the</strong> most organic<br />

agricultural land are Australia, Argentina, and <strong>the</strong> United States. Currently 0.9 percent <strong>of</strong> <strong>the</strong><br />

agricultural land is organic. By region, <strong>the</strong> highest shares are in Oceania (2.9 percent) and in<br />

Europe (2.1 percent). In <strong>the</strong> European Union, 5.1 percent <strong>of</strong> <strong>the</strong> farmland is organic.<br />

Global sales <strong>of</strong> organic food & drink reached 59 billion US dollars in 2010 according to<br />

Organic Monitor. The market has expanded over three-fold in ten years (2000:17.9 billion US<br />

dollars). Although growth has slowed since <strong>the</strong> financial crisis started in 2008 sales have<br />

continued to increase at a healthy pace. Demand <strong>for</strong> organic products is concentrated in two<br />

regions; North America and Europe comprise 96 percent <strong>of</strong> global revenues. The high degree <strong>of</strong><br />

sales concentration highlights <strong>the</strong> disparity between production and consumption indeed most<br />

organic food production in regions such as Africa and Latin America is export-geared. In 2010, <strong>the</strong><br />

countries with <strong>the</strong> largest markets were <strong>the</strong> United States, Germany, and France, and <strong>the</strong> highest<br />

per capita consumption was in Switzerland, Denmark, and Luxemburg.<br />

Indian Scenario in brief<br />

Growth in area<br />

Emerging from 42,000 ha under certified organic farming during 2003-04, <strong>the</strong> organic<br />

agriculture grew 29 fold during <strong>the</strong> period up to 2008-09. By March 2011 India had brought more<br />

than 4.43 million ha area under organic certification process. Out <strong>of</strong> this cultivated area accounts<br />

<strong>for</strong> 0.77 million ha while remaining 3.65 million ha was wild <strong>for</strong>est harvest collection area (Table 1).<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Export <strong>of</strong> organic commodities- in spite <strong>of</strong> dwindling area and threat <strong>of</strong> BT cotton to organic<br />

cotton <strong>the</strong> export <strong>of</strong> organic commodities continued to grow in double digit. The growth in export, in<br />

terms <strong>of</strong> total quantity, in terms <strong>of</strong> total value in INR and in terms <strong>of</strong> total value in US$ was 22, 33<br />

and 41% respectively.<br />

Table – 1 Growth <strong>of</strong> area under organic management<br />

S. Years Area in ha under organic certification process<br />

No.<br />

Cultivated (organic + in-conversion) Wild harvest<br />

1 2003-04 42,000 NA<br />

2 2004-05 76,000 NA<br />

3 2005-06 1,73,000 NA<br />

4 2006-07 5,38,000 24,32,500<br />

5 2007-08 8,65,000 24,32,500<br />

6 2008-09 12,07,000 30,55,000<br />

7 2009-10 10,85,648 33,96,000<br />

8 2010-11 7,77,517 36,50,000<br />

Organic farming systems are guided by an overriding philosophy <strong>of</strong> “feed <strong>the</strong> soil to feed<br />

<strong>the</strong> plant.” This basic precept is implemented through a series <strong>of</strong> approved practices designed to<br />

increase soil organic matter, biological activity, and nutrient availability. Over time, adding organic<br />

materials such as green manure, crop residues, and composts to cultivated soils builds levels <strong>of</strong><br />

soil organic matter. As soil organic matter increases, <strong>the</strong> ability <strong>of</strong> <strong>the</strong> soil to supply nutrients to<br />

crops also increases. The ultimate goal is a healthy, fertile, biologically active soil with improved<br />

structure and enhanced nutrient availability. Many soil amendments and organic fertilizers<br />

commonly approved <strong>for</strong> organic production systems have appreciable amounts <strong>of</strong> nutrients, but<br />

only a portion <strong>of</strong> <strong>the</strong>se nutrients are available to <strong>the</strong> current crop.<br />

Role <strong>of</strong> organic matter and humus<br />

The increase <strong>of</strong> soil organic matter to optimum levels is a key aspect <strong>of</strong> any organic<br />

production system. Native organic matter levels are relatively low in Indian soils, generally ranging<br />

from less than 1 percent to 2 percent. Studies have shown that it is unreasonable <strong>for</strong> a grower to<br />

expect to increase soil organic matter by more than about 1 percent, but a relatively small increase<br />

can dramatically improve <strong>the</strong> soil fertility environment in a given field. <strong>Soil</strong> organic matter improves<br />

cation exchange capacity and serves as a reservoir <strong>of</strong> nutrients <strong>for</strong> <strong>the</strong> growing crop. Incorporation<br />

<strong>of</strong> organic matter, also improves soil aeration, drainage, and water-holding capacity. Green<br />

manure crops are an economical means <strong>for</strong> elevating soil organic matter temporarily and providing<br />

nitrogen <strong>for</strong> <strong>the</strong> succeeding crop. They also reduce soil erosion and may <strong>of</strong>fer benefits related to<br />

pest and disease suppression. When green manure is not practical, composts and o<strong>the</strong>r approved<br />

amendments are useful. Compost is a relatively economical organic source <strong>of</strong> nutrients, but<br />

different composts can be quite variable depending upon <strong>the</strong> source. Growers need to understand<br />

<strong>the</strong> factors that contribute to compost quality. Incorporation <strong>of</strong> crop residues, if not used as cattle<br />

feed or <strong>for</strong> composting, can also add organic matter to <strong>the</strong> soil and help recycling <strong>the</strong> nutrients<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

particularly potassium.<br />

The decomposition <strong>of</strong> organic matter in soils can provide much <strong>of</strong> <strong>the</strong> nitrogen (N),<br />

phosphorus (P), and sulfur (S) needed <strong>for</strong> crop nutrition. A portion <strong>of</strong> <strong>the</strong> N from many organic<br />

amendments is converted readily into available mineral <strong>for</strong>ms. Phosphorus from organic<br />

amendments reacts quickly, is bound to soil minerals, and moves very little from where it is placed.<br />

Potassium (K), calcium (Ca), and magnesium (Mg) are relatively soluble from plant residues or soil<br />

organic matter fractions and also contribute to <strong>the</strong> soil pool <strong>of</strong> <strong>the</strong>se nutrients. Organic matter is<br />

also a valuable balanced source <strong>of</strong> many minor elements. Organic matter releases nutrients as it<br />

decomposes and provides slow, constant availability. <strong>Soil</strong> organic matter contains a number <strong>of</strong><br />

fractions that vary in composition and activity. Humus is <strong>the</strong> most resistant and mature fraction <strong>of</strong><br />

soil organic matter. It is very slow to decompose and may last <strong>for</strong> hundreds <strong>of</strong> years. Residues that<br />

are slow to decompose (such as hay or corn stalks) are more efficient producers <strong>of</strong> humus than<br />

are more readily decomposed materials. However, relatively little is understood about <strong>the</strong> benefits<br />

<strong>of</strong> humus or o<strong>the</strong>r specific organic matter fractions <strong>for</strong> crop growth, and an organic grower’s crop<br />

management ef<strong>for</strong>ts should be directed toward increasing total soil organic matter.<br />

Nutrient sources<br />

Green manure-Growing a green manure crop that includes a N-fixing legume is <strong>the</strong> most<br />

economical way to provide N to a succeeding crop. The amount <strong>of</strong> N contributed depends upon<br />

<strong>the</strong> species and vigor <strong>of</strong> <strong>the</strong> green manure, and ultimately on <strong>the</strong> duration <strong>of</strong> its growth cycle.<br />

Typically, a green manure crop will require approximately 50 to 60 days <strong>of</strong> growth to fix between<br />

60 and 90 kg N per ha. Recent research suggests that <strong>the</strong> available N from a green manure<br />

increases over a four- to six-week period following incorporation, and <strong>the</strong>n returns to preincorporation<br />

levels. There<strong>for</strong>e, crops following a green manure rotation may require additional<br />

applications <strong>of</strong> N later in <strong>the</strong> season. The green manure crops may also harvest N, P and K from<br />

deep in <strong>the</strong> soil pr<strong>of</strong>ile and make <strong>the</strong>m more available to <strong>the</strong> succeeding crop.<br />

Compost-Compost is a relatively cost-effective commercial organic source <strong>of</strong> N. Compost<br />

also provides P, K, Ca, Mg, S, and o<strong>the</strong>r minor nutrients in fairly well-balanced amounts. Although<br />

actual concentrations <strong>of</strong> P and K in compost are low, <strong>the</strong> total additions may be quite high due to<br />

<strong>the</strong> high volume <strong>of</strong> material applied. When applying compost, <strong>the</strong> challenges are to know and<br />

understand its composition and to determine how to use it most efficiently. The grower should<br />

understand <strong>the</strong> composting process used by <strong>the</strong> supplier and know <strong>the</strong> sources <strong>of</strong> raw material<br />

used. If <strong>the</strong> materials that are being composted are low in nutrients, <strong>the</strong> compost will have a low<br />

nutrient analysis. Poor-quality or immature compost may actually tie up nitrogen in <strong>the</strong> soil and<br />

decrease <strong>the</strong> availability <strong>of</strong> N to <strong>the</strong> growing crop. The carbon-to-nitrogen ratio (C: N) <strong>of</strong> a compost<br />

is one indication <strong>of</strong> <strong>the</strong> maturity and N availability. As <strong>the</strong> C: N ratio rises above 20:1, <strong>the</strong> tendency<br />

<strong>for</strong> N from <strong>the</strong> soil to be tied up increases. A compost with a C: N ratio <strong>of</strong> less than 20:1 will<br />

generally release N to <strong>the</strong> succeeding crop.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Three types <strong>of</strong> composts are available to organic farmer’s viz. normal compost (NADEP),<br />

vermi-compost and biodynamic compost. The composition <strong>of</strong> <strong>the</strong>se composts varies and should<br />

be considered be<strong>for</strong>e deciding <strong>the</strong> rate <strong>of</strong> application. Use <strong>of</strong> suitable microbial cultures may<br />

accelerate <strong>the</strong> process <strong>of</strong> composting and addition <strong>of</strong> Azotobacter can increase N content <strong>of</strong> <strong>the</strong><br />

compost. Similarly, addition <strong>of</strong> natural P sources such as rock phosphate can enrich <strong>the</strong> compost.<br />

Animal Manure- Decomposed animal manure (FYM) can also be a balanced source <strong>of</strong> N<br />

and o<strong>the</strong>r major and minor nutrients. Fresh manure may be <strong>of</strong> limited use because <strong>of</strong> relatively<br />

high transport costs, <strong>the</strong> potential <strong>for</strong> pollution problems, and <strong>the</strong> potential <strong>for</strong> crop injury. Ano<strong>the</strong>r<br />

potential limitation with manure is <strong>the</strong> availability <strong>of</strong> a consistent supply <strong>of</strong> a material that is uni<strong>for</strong>m<br />

enough to be confidently incorporated into a production programme. Organic certifying agencies<br />

may limit <strong>the</strong> type or timing <strong>of</strong> applications <strong>of</strong> manure on organic production fields. A public<br />

perception <strong>of</strong> increased food-safety–related problems relating to manure fertilization might fur<strong>the</strong>r<br />

limit <strong>the</strong> use <strong>of</strong> manure.<br />

O<strong>the</strong>r commercial organic fertilizers- A number <strong>of</strong> approved organic fertilizers or natural<br />

materials are available commercially (Table 1). Many <strong>of</strong> <strong>the</strong>se materials are by-products <strong>of</strong> fish,<br />

meat, and soybean processing industries. The commercial <strong>for</strong>mulations and nutrient analyses <strong>of</strong><br />

<strong>the</strong>se materials vary considerably. In general, <strong>the</strong>y range from 1 to 12 percent N and provide P, K,<br />

or both along with N. O<strong>the</strong>r simple fertilizer materials that <strong>of</strong>fer only one macronutrient include:<br />

o<br />

o<br />

o<br />

o<br />

blood meal (N)<br />

rock phosphate (P)<br />

potassium sulfate (mined) (K)<br />

green sand (K)<br />

Certain by-products <strong>of</strong> <strong>the</strong> meat processing industry, such as blood and bone meal, have<br />

recently come under scrutiny because <strong>of</strong> food safety concerns and <strong>the</strong> potential <strong>for</strong> disease<br />

transmission.<br />

Table 1: Common organic fertilizer materials and <strong>the</strong>ir approximate analysis (%, dry<br />

weight basis)<br />

_______________________________________________________________________<br />

Nitrogen (N) Phosphorus (P 2 O 5 ) Potassium (K)<br />

_______________________________________________________________________<br />

Fish meal or powder 10–11 6 2<br />

Poultry manure 2–3 1.5 1.5<br />

Seabird and bat guano 9–12 3–8 1–2<br />

Alfalfa meal 4 1 1<br />

Cottonseed meal 6 0.4 1.5<br />

Soybean meal 7 2 1<br />

Bone meal 2 5 0<br />

Kelp


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

circumstances <strong>for</strong> correction <strong>of</strong> minor element deficiencies such as zinc or copper deficiency.<br />

Application <strong>of</strong> approved source materials will raise soil levels to a range where <strong>the</strong>y are not<br />

deficient.<br />

Special-purpose fertilizers-Specific approved nutrient sources <strong>of</strong> K, Ca, and Mg may be<br />

useful to an organic grower when a deficiency or imbalance is indicated by a soil test. Materials<br />

such as gypsum, lime, and potassium-magnesium sulfate have been in use in agriculture <strong>for</strong> many<br />

years and <strong>the</strong>ir value is thoroughly tested. These materials may be used to correct deficiencies or<br />

imbalances <strong>of</strong> potassium, calcium, or magnesium, and lime may be used to raise soil pH. Gypsum<br />

also is <strong>of</strong>ten applied to replace exchangeable sodium prior to leaching a high-sodium soil (usar<br />

land) or to improve water infiltration on clay soils with poor structure. Pyrites may also be used as<br />

amendment <strong>for</strong> sodic soils. Materials derived from kelp and o<strong>the</strong>r processed seaweed contains<br />

nutrients and <strong>of</strong>ten plant hormones and growth regulators. Some claim that microbial soil<br />

stimulants enhance growth or reduce soil pests.<br />

Bi<strong>of</strong>ertilizers- Three types <strong>of</strong> bi<strong>of</strong>ertilizers are used viz. i) Symbiotic N 2 fixers such as<br />

Rhizobium culture <strong>for</strong> legumes, ii) free living N 2 fixers (non-symbiotic bacteria) such as<br />

Azotobacter and Azospirillum sp. <strong>for</strong> cereals, blue green algae and Azolla <strong>for</strong> rice and iii) P<br />

solubilizers such as Pseudomonas sp. While symbiotic N2 fixers inoculated in legumes can fix<br />

substantial amount <strong>of</strong> atmospheric N2 to feed <strong>the</strong> host plant, free-living N2 fixers contribute much<br />

less, usually 10-30 kg/ha. P solubilizers enhance <strong>the</strong> availability <strong>of</strong> native inorganic P. Bi<strong>of</strong>ertilizers<br />

are live materials, hence should be handled carefully and favorable environment in <strong>the</strong> field should<br />

be assured <strong>for</strong> desired results.<br />

<strong>Managing</strong> soil fertility in organic farming systems<br />

The practices used to manage soil fertility in organic farming systems should be<br />

understood in terms <strong>of</strong> <strong>the</strong> aims and underlying principles on which <strong>the</strong>y are based. There<strong>for</strong>e,<br />

practices that facilitate <strong>the</strong> efficient re-use <strong>of</strong> nutrients and organic matter within <strong>the</strong> farm are<br />

stressed. Also, organic production standards only permit non-syn<strong>the</strong>tic fertilizers that are poorly<br />

soluble in <strong>the</strong> soil solution. Nutrients management in organic farming systems is not simply<br />

replacement <strong>of</strong> soluble fertilizers with insoluble fertilizers. To build and maintain adequate soil<br />

fertility, organic farming systems must integrate management practices such as those discussed<br />

below. Mixed livestock – arable systems, crop rotations, legumes, organic matter inputs and <strong>the</strong><br />

use <strong>of</strong> fertilizers that are not readily soluble in soil; similar practices also characterize conventional<br />

farming systems that address sustainability issues, including <strong>the</strong> use <strong>of</strong> legumes to manage plant<br />

and animal nutrition in broad acre livestock-crop production and crop and <strong>for</strong>age rotations to<br />

manage pests and soil fertility.<br />

Livestock<br />

Livestock can directly improve soil chemical and biological fertility by introducing organic<br />

matter and nutrients in manure and manuring. Rotation that includes livestock can be a key<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

component <strong>of</strong> sustainable farming systems. The retention <strong>of</strong> mixed farming in organic farming<br />

systems and <strong>the</strong> associated increases in spatial and temporal habitat heterogeneity was partly<br />

responsible <strong>for</strong> increased diversity <strong>of</strong> organisms observed on organic farms, from soil microbes to<br />

mammals and birds.<br />

Crop rotation<br />

Rotations facilitate processes that alleviated some <strong>of</strong> <strong>the</strong> fertility constraints ot production<br />

that are addressed in conventional farming system by use <strong>of</strong> syn<strong>the</strong>tic inputs. Organic rotation<br />

may include greater use <strong>of</strong> greater use <strong>of</strong> green manures and cover crops, emphasize different<br />

regional crops, and have longer pasture phases than on conventional farms, leading to higher<br />

plant diversity in space and time. Rotations are also used to manage soil physical fertility by<br />

emphasizing inputs <strong>of</strong> organic matter from pasture phase, green manures <strong>of</strong> cover crops.<br />

Legumes in rotations<br />

Legumes are a fundamental component <strong>of</strong> organic farming system (in pastures, green<br />

manures, cover crops or food crops) because <strong>the</strong>y reduce or eliminate <strong>the</strong> need <strong>for</strong> external N<br />

fertilizers providing <strong>the</strong>y are effectively nodulated. The sustainability <strong>of</strong> legume use to supply crops<br />

with N in ei<strong>the</strong>r organic <strong>of</strong> conventional farming systems depends on <strong>the</strong>:<br />

1- Fixation <strong>of</strong> sufficient N in <strong>the</strong> legume biomass:<br />

2- Ability <strong>of</strong> <strong>the</strong> soil community to increase mineralization <strong>of</strong> organic N; and<br />

3- Capacity <strong>of</strong> farming practices to maximize <strong>the</strong> beneficial soil fertility and environmental<br />

effects <strong>of</strong> legumes and minimize <strong>the</strong>ir negative effects.<br />

The sustainability <strong>of</strong> using legumes to supply crop requirements <strong>for</strong> N also depends on <strong>the</strong><br />

capacity <strong>of</strong> organic management practices to maximize beneficial effects <strong>of</strong> legumes while<br />

minimizing <strong>the</strong> potential <strong>for</strong> N leaching. Intercropping with legumes can increase <strong>the</strong> efficiency with<br />

which soil nutrients are used. Steen Jensen and Hauggaard-Nielsen (2003) advocated increased<br />

use <strong>of</strong> legumes in farming systems because <strong>of</strong> beneficial environmental effects including improved<br />

soil structure, erosion protection, increased biological diversity, stimulation <strong>of</strong> rhizosphere<br />

organisms, acidification <strong>of</strong> alkaline soil and reduced energy use and carbon dioxide (CO2)<br />

production on and <strong>of</strong>f <strong>the</strong> farm.<br />

Fertilizers<br />

The fertilizers permitted in certified organic farming systems, and in some cases <strong>the</strong><br />

amount that may be applied, are restricted by organic certification standards. They are loosely<br />

divided into two categories: (i) naturally occurring geological resources (minerals) and (ii) organic<br />

materials. Minerals permitted as fertilizers in organic farming systems include lime, gypsum, rock<br />

phosphate, guano, elemental sulfur (S), dolomite and various ground silicate minerals. Organic<br />

materials include those produced on farms such as green manure, animals manure and compost<br />

as well as <strong>of</strong>f-farm sources such as fish, blood and bone meal, seaweed extracts and microbial<br />

products. Complete lists <strong>of</strong> fertilizers permitted in organic farming systems can be found in <strong>the</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

various organic certification standards.<br />

Conclusion<br />

Organic farming intensifies farm-internal processes like biological activities <strong>of</strong> soils,<br />

recycling <strong>of</strong> livestock and crop waste, enhanced biodiversity as well as nitrogen fixation and<br />

improved phosphorous availability by symbiosis. Organic farming builds up soil fertility and<br />

increases or conserves soil organic matter. Thus, supply and demand <strong>of</strong> nutrients get<br />

synchronized, water and soils get conserved and CO2 sequestered into <strong>the</strong> soil.<br />

REFERENCES<br />

• Abbott, L.K. and Murphy, D.V. 2003. What is biological fertility? In: Abbott L.K. and Murphy, D.V.<br />

(eds) soil Biological Fertility- A Key to Sustainable Land Use in Agriculture. Kluwer<br />

Academic Publishers, <strong>the</strong> Ne<strong>the</strong>rlands. pp. 1-15.<br />

• AQIS 1998. National Standards <strong>for</strong> Organic and Bio-dynamic Produce. Australian Quarantine and<br />

Inspection Service (AQIS), Canberra.<br />

• Avery, A. 2007. Going organic. Crops & <strong>Soil</strong>s. Vol. 40(1):8-12. Amer. Soc. Agron. Madison, WI.<br />

USA.<br />

• Avery, A. 2007. Going organic. Crops & <strong>Soil</strong>s. Vol. 40(1):8-12. Amer. Soc. Agron. Madison, WI. USA.<br />

• Biao, X, X. Wang, Z. Ding, and Y. Yang. 2003. Critical impact assessment <strong>of</strong> organic agriculture.<br />

J. Agric. Environ. Ethics. 16:297-311<br />

• Drinkwater, L.E.,Letourneau,D.K., Workneh, F., van Bruggen, A.H.C. and Shennan, C. 1995.<br />

Fundamental differences between conventional and organic tomato agroecosystems<br />

in Cali<strong>for</strong>nia. Ecological Application 5:1098-1112.<br />

• FAO 1999. Organic Agriculture. Food and agriculture Organization o <strong>the</strong> United Nations, Rome.<br />

http://www.fao.org/unfao/bodies/COAG/COAG15/X0075E.htm. Accessed 26/2/99.<br />

• Galantini, J., R. Rosell, 2006. Long-term fertilization effects on soil organic matter quality and<br />

dynamics under different production systems in semiarid Pampean soils. <strong>Soil</strong> & tillage<br />

research, 87: 72-79.<br />

• Glover, J.D., Reganold, J.P. and Andrews, P.K. 2000. Systematic method <strong>for</strong> rating soil quality <strong>of</strong><br />

conventional, organic and integ4rted apple orchards in Washington State. Agriculture,<br />

Ecosystem and Environment 80:29-45.<br />

• Gosling, P., M. Shepherd. 2005. Long-term changes in soil fertility in organic arable farming<br />

systems in England, with particular reference to phosphorus and potassium. Short<br />

communication. Agriculture, ecosystems and environment, 105: 425-432.<br />

• Lee, K. E. and Pankhurst, C. E. 1992. <strong>Soil</strong> organisms and sustainable productivity. Australian<br />

Journal <strong>of</strong> <strong>Soil</strong> Research 30:855-892.<br />

• Lotter, D.W. 2003. Organic agriculture. Journal <strong>of</strong> Sustainable Agriculture, 21: 59–128.<br />

• Oberson, A., Fardeau, J.C., Besson, J. M. and Sticher, H. 1993. <strong>Soil</strong> phosphorus dynamics in<br />

cropping systems managed according to conventional and biological agricultural<br />

methods. Biology and fertility <strong>of</strong> <strong>Soil</strong>s 16:111-117.<br />

• Olesen, J.E., Schelde, K., Weiske, A., Weisbjerg, M.R., Asman, W.A.H., Djurhuus, J., (2006):<br />

Modelling greenhouse gas emissions from European conventional and organic dairy<br />

farms. Agriculture, Ecosystems and Environment 112, pp.207-22.<br />

• Penfold, C.M., Miyan, M.S., Reeves, T. G. and Grierson, I. T. 1995. biological farming <strong>for</strong><br />

sustainable agricultural production. Australian Journal o f Experimental Agriculture<br />

35:849-856.<br />

• Ryan, M. 1999. Is and enhanced soil biological community, relative to conventional neighbours, a<br />

consistent feature <strong>of</strong> alternative (organic and biodynamic) agricultural systems?<br />

Biological Agriculture and Horticulture 17:131-144.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Shepherd, M.A., Harrison, R. and Webb, J. 2002. <strong>Managing</strong> soil organic matter- implication <strong>for</strong> soil<br />

structure on oranic farms. <strong>Soil</strong> Use and <strong>Management</strong> 18:284-292.<br />

• Smith, K.A., Conen, and F. (2004): Impacts <strong>of</strong> land management on fluxes <strong>of</strong> trace greenhouse<br />

gases. <strong>Soil</strong> Use and <strong>Management</strong> 20, 255-263.<br />

• Stockdale, E.A. and Cookson, W.R.2003. Sustainable farming systems and <strong>the</strong>ir impact on soil<br />

biological fertility-some case studies. In: Abbott L.K. and Murphy, D.V. (eds) <strong>Soil</strong><br />

Biological Fertility- A Key to Sustainable Land Use in Agriculture. Kluwer Academic<br />

Publishers, The Ne<strong>the</strong>rlands. pp 225-239.<br />

• Stockdale, E.A., N.H. Lampkin, M. Hovi, R. Keatinge, E.K.M. Lennartsson, D.W. Macdonald, S.<br />

Padel, F.H. Tattersall, M.S. Wolfe, C.A. Watson. 2001. Agronomic and environmental<br />

implications <strong>of</strong> organic farming systems. Adv. Agron., 70: 261–325.<br />

• Thorup- Kristensen, K. 2001. Are differences in root growth <strong>of</strong> nitrogen catch crops important <strong>for</strong><br />

<strong>the</strong>ir ability to reduce soil nitrate-N content, and how can this be measured? <strong>Plant</strong> and<br />

<strong>Soil</strong> 230:185-195.<br />

• Yussefi, M., H. Willer. 2007. Organic farming worldwide 2007: Overview & main statistics. In: The<br />

world <strong>of</strong> organic agriculture. Statistics and emerging trends.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

The Role <strong>of</strong> <strong>Soil</strong> Micr<strong>of</strong>auna in Maintaining <strong>Soil</strong> Health<br />

Navneet Pareek<br />

Department <strong>of</strong> <strong>Soil</strong> Science, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

<strong>Soil</strong> organisms (biota) carry out a wide range <strong>of</strong> processes that are important <strong>for</strong> soil health<br />

and fertility in both natural and managed agricultural soils. The total number <strong>of</strong> organisms, <strong>the</strong><br />

diversity <strong>of</strong> species and <strong>the</strong> activity <strong>of</strong> <strong>the</strong> soil biota will fluctuate as <strong>the</strong> soil environment changes.<br />

These changes may be caused by natural or imposed systems. The micr<strong>of</strong>auna are a diverse<br />

group which includes <strong>the</strong> protozoa, nematodes, and some arthropods, primarily mites and<br />

springtails (collembola). Micr<strong>of</strong>auna are usually defined as being smaller than 0.2 mm, although<br />

some soil nematodes can reach lengths <strong>of</strong> 5.0 mm.<br />

Protozoa are single-celled animals that feed primarily on bacteria, but also eat o<strong>the</strong>r<br />

protozoa, soluble organic matter, and sometimes fungi. They are several times larger than<br />

bacteria, ranging from 1/5000 to 1/50 <strong>of</strong> an inch (5 to 500 μm) in diameter. Both protozoa and<br />

nematodes are aquatic and live and move in soil water films and water-filled pores <strong>of</strong> soil<br />

aggregates. Protozoa are classified into three groups based on <strong>the</strong>ir shape. Species <strong>of</strong><br />

Mastigophora or flagellates are <strong>the</strong> smallest (5 to 20 μm) and use one to four whip-like flagella to<br />

move. Flagellates feed primarily on bacteria and are <strong>the</strong> most numerous <strong>of</strong> soil protozoa.<br />

Ciliophora or ciliates are <strong>the</strong> largest (10 to 80 μm) protozoa and <strong>the</strong> least numerous and move by<br />

means <strong>of</strong> hair-like cilia. The cilia use vibrating hairs to move. Ciliates use <strong>the</strong> fine cilia along <strong>the</strong>ir<br />

bodies like oars to move rapidly through <strong>the</strong> soil. They eat <strong>the</strong> o<strong>the</strong>r two types <strong>of</strong> protozoa, as well<br />

as bacteria. Cilates may consume as many as ten thousand bacteria per day. Sarcodina or<br />

amoebae also can be quite large and move by means <strong>of</strong> a temporary foot or “pseudopod.”<br />

Amoebas reside in <strong>the</strong> rhizosphere and at <strong>the</strong> root surface where <strong>the</strong>y graze on bacteria<br />

populations. There are two types <strong>of</strong> amoebas: testate and naked. Testate amoebas are encased in<br />

a rigid chitin shell or testa, while naked amoebas lack a rigid shell. Naked amoebas can change<br />

shape and explore tiny pore spaces making <strong>the</strong>m valuable <strong>for</strong> soil nutrient recycling.<br />

Nematodes or roundworms are non-segmented worms with tapered ends typically 1/500 <strong>of</strong><br />

an inch (50 μm) in diameter and 1/20 <strong>of</strong> an inch (1 mm) in length. They have a head, and a tail<br />

with a well developed central nervous and fertility system with a complete digestive system, so<br />

<strong>the</strong>y are considered <strong>the</strong> most primitive animal. They are small enough to fit in most soil pores and<br />

soil aggregates. They are classified in <strong>the</strong> animal phylum Nemata and are best known <strong>for</strong> causing<br />

infectious disease in plants and animals, but <strong>the</strong>y also play an important role in soil and crop<br />

ecology. Nematodes are aquatic organisms so <strong>the</strong>y require adequate soil moisture to move in <strong>the</strong><br />

soil. Nematodes can be divided into five broad groups based on <strong>the</strong>ir diet with <strong>the</strong> first four groups<br />

being free living. Bacterial-feeders consume bacteria through a stoma, a large open channel.<br />

Fungal-feeders feed by puncturing <strong>the</strong> cell wall <strong>of</strong> fungi using a small slender stylet to suck out <strong>the</strong><br />

internal contents. Predatory nematodes eat all types <strong>of</strong> nematodes and protozoa using a stylet.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

They eat smaller microorganisms whole or attach <strong>the</strong>mselves to <strong>the</strong> cuticle <strong>of</strong> larger nematodes,<br />

scraping away until <strong>the</strong> prey’s internal body parts can be extracted. Omnivores eat a variety <strong>of</strong><br />

organisms including bacteria, fungus, protozoa, o<strong>the</strong>r nematodes and roots and may have a<br />

different diet at each life stage. Root-feeders are plant parasites feeding on roots, and thus are not<br />

free-living in <strong>the</strong> soil because <strong>the</strong>y live ei<strong>the</strong>r inside or outside <strong>the</strong> plant root, depending on <strong>the</strong><br />

plant root <strong>for</strong> a food source.<br />

The role soil micr<strong>of</strong>auna play in <strong>the</strong> cycling <strong>of</strong> nutrients in ecosystems has been recognized<br />

<strong>for</strong> many years (Verhoef and Brussaard, 1990). They have significant impact on plant diseases,<br />

and soil health. <strong>Soil</strong> micr<strong>of</strong>auna play a major role in <strong>the</strong> decomposition and turnover <strong>of</strong> organic<br />

matter, regulation <strong>of</strong> population densities <strong>of</strong> micr<strong>of</strong>lora and o<strong>the</strong>r biochemical processes. Protozoa<br />

are unicellular organisms and are <strong>the</strong> main consumers <strong>of</strong> microbial biomass. Nematodes are <strong>the</strong><br />

most numerous multicellular animals on earth, exploiting virtually all <strong>of</strong> <strong>the</strong> planet's terrestrial,<br />

aquatic and marine habitats (except open water). Many nematodes are parasites <strong>of</strong> insects, plants<br />

or animals; o<strong>the</strong>rs feed on fungi, bacteria and o<strong>the</strong>r nematodes. Between 500,000 and<br />

100,000,000 nematode species are believed to live on this planet, but less than 25,000 described<br />

species are yet classified in <strong>the</strong> phylum Nemata. Microorganisms are ubiquitous inhabitants <strong>of</strong> all<br />

soils. A handful <strong>of</strong> soil will contain thousands <strong>of</strong> micr<strong>of</strong>aunal organisms.<br />

Micr<strong>of</strong>aunal species feeding on o<strong>the</strong>r microorganisms help, by <strong>the</strong>ir grazing pressure, keep<br />

<strong>the</strong> microorganism populations young and active, thus stimulating microbial soil processes.<br />

Absence <strong>of</strong> micr<strong>of</strong>auna can result in incomplete cycling <strong>of</strong> elements.<br />

The concept <strong>of</strong> suppressive soils was described by Baker and Cook (1974) in <strong>the</strong>ir first<br />

book on <strong>the</strong> biological control <strong>of</strong> plant pathogens. The suppressiveness is <strong>the</strong> ability <strong>of</strong> a soil to<br />

prevent, truncate or delay <strong>the</strong> development <strong>of</strong> a disease even though favorable environmental<br />

conditions exist. The actual mechanisms <strong>of</strong> disease suppression involve <strong>the</strong> influences <strong>of</strong> various<br />

microbial antagonists, soil fungistasis (inhibition <strong>of</strong> fungal growth), and physical and chemical<br />

properties <strong>of</strong> soils. The role <strong>of</strong> soil fauna in this process has recently been reported.<br />

Organic Matter Decomposition<br />

As nematodes and protozoans feed upon microbial populations, <strong>the</strong>y consequently will<br />

affect organic matter decomposition. It is likely that such feeding ultimately liberates nutrients<br />

immobilized in microbial cells or reduces competition between microorganisms so that<br />

mineralization is actually accelerated. "These activities not only influence <strong>the</strong> general nutrition,<br />

health, and vigour <strong>of</strong> higher plants (which relates to disease susceptibility), but also determine <strong>the</strong><br />

competitive behavior <strong>of</strong> root-infecting fungi and <strong>the</strong>ir microbial antagonists." These indirect and<br />

direct impacts are important ones <strong>for</strong> fur<strong>the</strong>r study.<br />

The role <strong>of</strong> microarthropods in mineralization is also recognized. Mites and collembola are<br />

known to fragment organic matter as <strong>the</strong>y feed on soil micr<strong>of</strong>lora. This fragmentation to finer<br />

particles creates new surface areas <strong>for</strong> microbial colonization and consequently speeds <strong>the</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

decomposition and mineralization processes.<br />

There are several o<strong>the</strong>r interesting features <strong>of</strong> <strong>the</strong> microbiotic community, including<br />

increased nitrogen fixation by nitrogen-fixing bacteria (Azotobacter spp.) where protozoa are<br />

present, and <strong>the</strong> behavior <strong>of</strong> bacterial and fungal-feeding nematodes.<br />

Rhizosphere Effects<br />

The rhizosphere is <strong>the</strong> soil zone surrounding and influenced by plant roots. The primary<br />

influences in this zone are root exudates and <strong>the</strong> chemical and physical features <strong>of</strong> <strong>the</strong> root-soil<br />

interface. Root exudates and sloughed root cells in <strong>the</strong> rhizosphere provide a rich carbon source<br />

<strong>for</strong> microbes. As <strong>the</strong> microbial population increases, so does <strong>the</strong> activity <strong>of</strong> microbe-grazing fauna,<br />

leading eventually to <strong>the</strong> release <strong>of</strong> inorganic nitrogen and phosphorus.<br />

Root exudates can also have a strong influence on soil pathogens. "The nutrients in<br />

exudates release dormant spores and sclerotia from <strong>the</strong> grip <strong>of</strong> soil fungistasis, a natural<br />

phenomenon imposed by chemical inhibitors and microbial competition <strong>for</strong> nutrients. Propagules<br />

freed from fungistasis germinate and establish infection if <strong>the</strong>y are not first consumed by<br />

mycophagous [fungus-eating] animals. Root exudates are also important in <strong>the</strong> activation <strong>of</strong><br />

quiescent nematode stages and in <strong>the</strong> movement <strong>of</strong> plant parasitic <strong>for</strong>ms to infection sites."<br />

Specific <strong>Soil</strong> Fauna-<strong>Plant</strong> Disease Relationships<br />

The fauna have in <strong>the</strong> rhizosphere are sufficient to indicate that soil fauna do regulate<br />

pathogen populations to some degree. Some interesting relationships are summarized in table 1.<br />

Table 1. Summary <strong>of</strong> biological control activities <strong>of</strong> soil micro-and meso- fauna.<br />

Biocontrol Agent<br />

Amoebae<br />

(At least 5 different species)<br />

Nematodes<br />

(Numerous species from 7 genera)<br />

Microarthropods<br />

Mites<br />

Collembola<br />

Action<br />

Conidiall per<strong>for</strong>ations and/or hyphal feeding on<br />

numerous species <strong>of</strong> fungi including Cochliobolus<br />

sativus, Thielaviopsis basicola, Fusarium oxysporum<br />

F. sp. melonis, F. roseum, F. solani, Verticillium<br />

dahliae, Gaeumannomyces graminis, and<br />

Phytophthora cinnamomi.<br />

Also may feed on bacteria, flagellates, blue green<br />

algae, diatoms, and nematodes.<br />

Feed on various species <strong>of</strong> Rhizoctonia, Aternaria,<br />

Pyrenochaeta, Botrytis, Fusarium, and Agaricus.<br />

Fungal feeders, but probably play a minor role in<br />

disease suppression.<br />

Two species found to feed extensively on several<br />

plant pathogenic fungi including Rhizoctonia solani,<br />

and Fusarium oxysporum. Show marked preference<br />

<strong>for</strong> particular types <strong>of</strong> fungi.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Soil</strong> micr<strong>of</strong>auna as bioindicators <strong>of</strong> soil health<br />

In view <strong>of</strong> <strong>the</strong>ir important role in various soil processes, soil micr<strong>of</strong>auna have been<br />

suggested as bioindicators <strong>of</strong> soil health (Gupta and Yeates, 1997). The composition <strong>of</strong> nematode<br />

communities (plant-parasitic and free-living) may be used as bioindicators <strong>of</strong> soil health or<br />

condition because composition correlates well with nitrogen cycling and decomposition, two critical<br />

ecological processes in soil. Maturity and trophic diversity indices withstand statistical rigor better<br />

than do abundances, proportions, or ratios <strong>of</strong> trophic groups (Neher, 2001). Maturity indices<br />

respond to a variety <strong>of</strong> land-management practices, based largely on inferred life history<br />

characteristics <strong>of</strong> families. Similarity indices may be more useful than diversity indices because<br />

<strong>the</strong>y reflect taxon composition. Improving existing indices or developing alternative indices refined<br />

by a greater understanding <strong>of</strong> <strong>the</strong> biology <strong>of</strong> key taxa may enhance <strong>the</strong> utility <strong>of</strong> nematodes as<br />

bioindicators.<br />

Conclusions<br />

Protozoa consume primarily bacteria and o<strong>the</strong>r protozoa and help to regulate bacteria<br />

densities, composition, and populations. In this manner soil micr<strong>of</strong>auna play an important role in<br />

suppression <strong>of</strong> plant pathogens and represent a significant biological control potential. However,<br />

<strong>the</strong>re has not been adequate field testing to verify if this biocontrol potential can be exploited in<br />

cropping systems. In addition, any evaluation <strong>of</strong> a candidate organism must include <strong>the</strong> possibility<br />

<strong>of</strong> adverse effects upon plants, animals, or <strong>the</strong> environment.<br />

Micr<strong>of</strong>auna also help in maintaining soil health <strong>the</strong>y consume o<strong>the</strong>r microbes in <strong>the</strong> soil and<br />

release <strong>the</strong> N as ammonia, which becomes available to plants. Protozoa and bacteria tend to be<br />

more numerous than nematodes in cultivated or tilled soils. Nematodes feed on bacteria, fungus,<br />

protozoa, and o<strong>the</strong>r nematodes, but some are root feeders. A problem with <strong>the</strong> fungal-feeding<br />

amoebae, <strong>for</strong> example, maybe <strong>the</strong>ir effect on o<strong>the</strong>r beneficial organisms such as <strong>the</strong> mycorrhizal<br />

fungi. There<strong>for</strong>e, ef<strong>for</strong>ts to manipulate and exploit <strong>the</strong> friendly fauna populations <strong>for</strong> crop benefit<br />

must be compatible with microbial symbionts, and o<strong>the</strong>r plant-growth promoting rhizosphere<br />

organisms, and with fungi and bacteria that are being promoted <strong>for</strong> biological control <strong>of</strong> diseases.<br />

This is clearly an area with great opportunities <strong>for</strong> fur<strong>the</strong>r research.<br />

REFERENCES<br />

• Baker. E. F and R.J. Cook, 1974. Biological control <strong>of</strong> plant pathogens. W.H. Freeman & Co.<br />

Sanfransisco, 433pp.<br />

• Gupta, V.V.S.R; Yeates, G.W. 1997. <strong>Soil</strong> Micr<strong>of</strong>auna as Bioindicators <strong>of</strong> <strong>Soil</strong> Health. In C.E.<br />

Pankhurst, B.M. Doube, V.V.S.R. Gupta, eds. Biological Indicators <strong>of</strong> <strong>Soil</strong> Health.<br />

Oxon, United Kingdom, CAB International.<br />

• Neher, D.A. 2001. Role <strong>of</strong> nematodes in soil health and <strong>the</strong>ir use as indicators. Journal <strong>of</strong><br />

Nematology, 33(4):161–168. 2001.<br />

• Verhoef, H.A. and Brussaard, L. (1990). Decomposition and nitrogen mineralization in natural and<br />

agro-ecosystems: The contribution <strong>of</strong> soil animals. Biogeochemistry 11: 175-211.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Soil</strong> Degradation- A Threat to Sustainable Agriculture<br />

Ramesh Chandra<br />

Department <strong>of</strong> <strong>Soil</strong> Science, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

<strong>Soil</strong> is one <strong>of</strong> <strong>the</strong> most precious natural resources, which provides a medium <strong>for</strong> plant<br />

growth to meet our food and fibre need. <strong>Soil</strong> filters water, decomposes waste, stores heat, and<br />

exchanges gases and thus have great bearing on environmental quality. <strong>Soil</strong> is a limited and non–<br />

renewable resource. Experience has shown that with continuous utilization even with best<br />

technologies and skills, soil has reached a stage <strong>of</strong> fatigue resulting in decline or stagnation in <strong>the</strong><br />

productivity in almost all crop production systems. Degradation <strong>of</strong> agricultural land has become a<br />

great cause <strong>of</strong> concern during <strong>the</strong> 21 st century and will remain high in <strong>the</strong> next century because <strong>of</strong><br />

its direct impact on agricultural sustainability and food security. <strong>Soil</strong> degradation is <strong>the</strong> temporary<br />

or permanent lowering <strong>of</strong> <strong>the</strong> productive capacity <strong>of</strong> soil caused by over-grazing, de<strong>for</strong>estation,<br />

inappropriate agricultural practices, over exploitation and o<strong>the</strong>r man induced activities. In India, an<br />

ever increasing population places enormous demands on soil resources, which has only 2.4 per<br />

cent <strong>of</strong> <strong>the</strong> world's geographical area but supports over 16 per cent <strong>of</strong> <strong>the</strong> world's population. It has<br />

0.5 per cent <strong>of</strong> <strong>the</strong> world's grazing area, but has over 18 per cent <strong>of</strong> world's cattle population.<br />

These pressures have drastically degraded and caused significant shrinkage in <strong>the</strong> soil resources<br />

due to urbanization and industrial needs.<br />

The soil resources <strong>of</strong> India are enormous as 9, out <strong>of</strong> 12 <strong>Soil</strong> Orders which describe <strong>the</strong><br />

soils <strong>of</strong> <strong>the</strong> planet earth, occur in India. However, some <strong>of</strong> <strong>the</strong> soils have severe constraints<br />

towards meeting <strong>the</strong> challenges <strong>of</strong> <strong>the</strong> next centuries. Land degradation is causing a heavy toll <strong>of</strong><br />

soil resources every year in India. The latest estimates by NBSS and LUP, Nagpur using Global<br />

Assessment <strong>of</strong> <strong>Soil</strong> Degradation (GLASOD) guidelines indicate 187.8 M ha <strong>of</strong> land degraded to<br />

various degrees through different degrading processes. <strong>Soil</strong> degradation problem is especially<br />

severe in arid, semiarid and hilly regions. Important constraints are low soil fertility and nutrient<br />

depletion, multinutrient deficiency, physical degradation and accelerated soil erosion. Apart from<br />

inherent constraints, <strong>the</strong>re are severe human induced constraints particularly in intensively<br />

cropped areas.<br />

Mechanisms that initiate soil degradation include physical, chemical, and biological<br />

processes (Lal, 1994) (Fig. 1). Important among physical processes are a decline in soil structure<br />

leading to crusting, compaction, erosion, desertification, and water logging and environmental<br />

pollution. Chemical processes include acidification, leaching, salinization, nutrient imbalance and<br />

toxicity, decrease in cation retention capacity and fertility depletion. <strong>Soil</strong> biological degradation<br />

processes include reduction in total and biomass carbon, and decline in land biodiversity. Climate<br />

change influences chemical, physical and biological processes and thus contributes to soil<br />

degradation to a great extant. The degraded lands eventually jeopardize human well-being. <strong>Soil</strong><br />

structure is <strong>the</strong> important property that affects all three degradative processes.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Soil</strong> physical degradation<br />

About 95.65 M ha <strong>of</strong> <strong>the</strong> cultivated land in India suffer from soil physical degradation, out <strong>of</strong><br />

which shallow soil cover 25.02 M ha, hardening soils 20.35 M ha, highly permeable soils 10.77 M<br />

ha, soils with high mechanical impedance at shallow depth 10.63 M ha, slowly permeable soils<br />

9.43 M ha and o<strong>the</strong>r physical constraints 9.45 M ha (Yadav, 1996). Physical degradation through<br />

water logging, soil compaction, crusting etc. is serious problem affecting crop productivity. Erosion<br />

by water is <strong>the</strong> most serious degradation problem <strong>of</strong> <strong>the</strong> Indian soils. The analysis <strong>of</strong> <strong>the</strong> existing<br />

soil loss data indicate that soil erosion takes place at an average rate <strong>of</strong> 16.35 tonnes ha -1 year -1<br />

totalling 5,334 m tones year -1 . Nearly 29% <strong>of</strong> <strong>the</strong> total eroded soil permanently lost to <strong>the</strong> sea, and<br />

nearly 10% deposited in reservoirs, resulting in <strong>the</strong> reduction <strong>of</strong> <strong>the</strong>ir storage capacity by 1 to 2%<br />

annually. The remaining 61% <strong>of</strong> <strong>the</strong> eroded soil transported from one place to o<strong>the</strong>r. (Singh, 2000).<br />

Problems <strong>of</strong> physical deterioration <strong>of</strong> soils generally related to reduction in soil organic matter<br />

content, making <strong>the</strong>m more prone to crusting and increased run<strong>of</strong>f. Ano<strong>the</strong>r most serious soil<br />

degradation problem is <strong>of</strong> excessive wetness due to water logging. The estimates show that <strong>the</strong><br />

soil area prone to water-logging is 11.6 M ha. Wind erosion is a serious problem in <strong>the</strong> arid and<br />

semi-arid regions <strong>of</strong> Rajasthan, Haryana, Gujarat, Punjab and coastal areas. Removals <strong>of</strong> natural<br />

vegetative cover resulting from excessive grazing and expansion <strong>of</strong> agriculture to marginal areas<br />

are <strong>the</strong> major human-induced factors leading to accelerated wind erosion. Wind erosion is also<br />

prevalent in <strong>the</strong> coastal areas where sandy soils predominate, and in <strong>the</strong> cold desert regions <strong>of</strong><br />

Leh. Wind erosion is moderate to severe in arid and semi-arid regions <strong>of</strong> <strong>the</strong> northwest, covering<br />

an area <strong>of</strong> 28,600 km 2 , <strong>of</strong> which 68 per cent is covered by sand dunes and sandy plains. However,<br />

active wind erosion is observed in <strong>the</strong> extreme western sectors <strong>of</strong> <strong>the</strong> country.<br />

<strong>Soil</strong> chemical degradation<br />

Chemical degradation <strong>of</strong> soils can occur through a number <strong>of</strong> processes viz. <strong>the</strong> loss <strong>of</strong><br />

nutrients and/or organic matter and accumulation <strong>of</strong> salts and/or pollutants. Amongst <strong>the</strong> soil<br />

groups, Alfisols and Ultisols, are prone to chemical deterioration due to nutrient depletion. It is<br />

estimated that about 70% area in <strong>the</strong> country is deficient in soil organic carbon; having less than<br />

1% Organic C. Deficiency <strong>of</strong> phosphorus is widespread in Indian soils with 49.3, 48.8 and 1.9% <strong>of</strong><br />

soils having low, medium and high P status, respectively. There is also growing intensity <strong>of</strong> o<strong>the</strong>r<br />

plant nutrients deficiency including micronutrients in intensively cultivated areas. Analysis <strong>of</strong> 2.52<br />

lakhs surface soil samples collected from different parts <strong>of</strong> <strong>the</strong> India under AICRP on Micro- and<br />

Secondary Nutrients and Pollutants in <strong>Soil</strong>s and <strong>Plant</strong>s revealed that 49% soils in <strong>the</strong> country are<br />

deficient in Zn, 41% in S, 32% in B, 12% in Fe, 4% in Mn and 3% in Cu <strong>for</strong> crop production point <strong>of</strong><br />

view. These deficiencies have not only adversely affected <strong>the</strong> growth <strong>of</strong> agricultural production,<br />

deteriorated <strong>the</strong> physical, chemical and biological environment <strong>of</strong> soils, but also caused imbalance<br />

<strong>of</strong> <strong>the</strong>se essential nutrients in humans and animals (Singh, 1998).<br />

The o<strong>the</strong>r most important chemical process <strong>of</strong> soil degradation is soil salinization and soil<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

sodicity. It is estimated that a total <strong>of</strong> 10.1 M ha area is suffering from salinity and/or alkalinity<br />

problems. While saline soils have excess <strong>of</strong> neutral soluble salts, that is, chlorides and sulphates<br />

<strong>of</strong> sodium, calcium and magnesium, alkali soils contain appreciable quantities <strong>of</strong> salts, such as<br />

sodium bicarbonate and/or carbonate and high amount <strong>of</strong> exchangeable sodium in <strong>the</strong> clay<br />

fraction. The salt-affected soils are <strong>of</strong> widespread occurrence in <strong>the</strong> arid, semi-arid and sub-humid<br />

(dry) zones <strong>of</strong> <strong>the</strong> Indo-Gangetic plains and coastal regions. Alkali (sodic) soils dominate in areas<br />

having mean annual rainfall <strong>of</strong> more than 600 mm.<br />

<strong>Soil</strong> biological degradation<br />

<strong>Soil</strong> biological processes and soil biodiversity are central to <strong>the</strong> soil fertility and soil physical<br />

properties. Unscientific and indiscriminate use <strong>of</strong> farm inputs such as fertilizers, insecticides,<br />

fungicides, weedicides and growth promoters etc. as a result <strong>of</strong> green revolution technologies<br />

resulted in biological degradation <strong>of</strong> soils. Conventional tillage is known to significantly reduce <strong>the</strong><br />

diversity <strong>of</strong> soil bacteria by reducing both substrate richness and evenness. <strong>Plant</strong> species<br />

influences microbial community composition <strong>of</strong> soil via rhizo-deposition <strong>of</strong> organic substrates,<br />

which serves <strong>the</strong> source <strong>of</strong> energy <strong>for</strong> <strong>the</strong> microorganisms. Studies based on 16S rRNA gene and<br />

phospholipid fatty acid analysis have revealed shifts in <strong>the</strong> total microbial community in response<br />

to <strong>the</strong> different soil and crop management practices, indicating that deliberate management <strong>of</strong> soils<br />

can have a considerable impact on microbial community structure and functions in soil.<br />

Applications <strong>of</strong> chemical fertilizers and agrochemicals lower <strong>the</strong> soil microbial diversity. <strong>Soil</strong><br />

bacteria were observed more sensitive to chemical N fertilizer application during <strong>the</strong> plant growth<br />

cycle (Seneviratne, 2009).<br />

Amelioration <strong>of</strong> Degraded <strong>Soil</strong>s<br />

A degraded soil can be improved and made suitable <strong>for</strong> pr<strong>of</strong>itable crop production using<br />

proper management technology and inputs. However, <strong>the</strong> time and cost involved in reclaiming a<br />

degraded soil are <strong>the</strong> serious limitations. Bad management can turn good soil into deserts and<br />

vice-versa. Followings are some important advisable measures <strong>for</strong> amelioration <strong>of</strong> degraded soils<br />

to put <strong>the</strong>m under pr<strong>of</strong>itable crop production systems.<br />

Enhancing soil organic matter<br />

Organic matter influences almost all <strong>the</strong> components <strong>of</strong> soils linked with crop production.<br />

Organic matter incorporated in to <strong>the</strong> soil can affect its structure, as indicated by porosity,<br />

aggregation and bulk density, as well as causing an impact in terms <strong>of</strong> content and transmission <strong>of</strong><br />

water, air and heat and <strong>of</strong> soil strength. Maintenance <strong>of</strong> soil organic matter (SOM) vis-a-vis carbon<br />

sequestration is <strong>the</strong>re<strong>for</strong>e, essential not only <strong>for</strong> restoration <strong>of</strong> <strong>the</strong> productivity <strong>of</strong> soils, but also<br />

improvement in overall soil health. Several organic materials such as FYM, green manures, city<br />

refuse, composts, <strong>for</strong>est litter, sewage and sludge, domestic and industrial wastes are available <strong>for</strong><br />

use in crop production. Although, increasing soil organic matter in tropical climate is not easy.<br />

However, continuous application <strong>of</strong> lignocellulotic crop residue helps in building SOM temporarily.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Besides, crop production practices <strong>of</strong> conservation tillage may help in building <strong>the</strong> SOM by<br />

avoiding its losses from soil through oxidation.<br />

Integrated nutrient <strong>Management</strong><br />

Integrated nutrient management (INM) is an approach <strong>of</strong> effective and efficient utilization <strong>of</strong><br />

all available nutrient resources i.e. soil reserve, organics, bi<strong>of</strong>ertlizers and chemical fertilizers,<br />

which are locally available, economically viable, socially acceptable and eco-friendly <strong>for</strong> sustaining<br />

and increasing crop production. India will require about 300 m tonnes <strong>of</strong> food grains by 2025 to<br />

feed around 1.4 billion populations. This would necessitate <strong>the</strong> use <strong>of</strong> about 45 m tonnes <strong>of</strong><br />

nutrients. This much need <strong>of</strong> plants nutrients can not be met out by <strong>the</strong> chemical fertilizers alone<br />

with current growth rate in fertilizer consumption. The organic resources available presently, could<br />

meet nearly one-third <strong>of</strong> total nutrients requirement to achieve <strong>the</strong> targeted level <strong>of</strong> food grain<br />

production. INM practice also prevents <strong>the</strong> depletion <strong>of</strong> SOM and improves soil physical, chemical<br />

and biological health.<br />

Water management<br />

Water is a prime natural resource and is considered as a precious national asset. Over<br />

exploitation <strong>of</strong> ground water in several parts <strong>of</strong> <strong>the</strong> country resulted in declined ground water levels<br />

in pockets in 370 districts; reduced supply <strong>of</strong> water and subsided land in some places and is<br />

threatening <strong>the</strong> agriculture sustainability and food security (Samara and Sharma, 2010). Improper<br />

use <strong>of</strong> water and its poor management creates problems <strong>of</strong> salinity, sodicity and waterlogging. The<br />

modern irrigation techniques such as drip irrigation, sprinkler irrigation can become remunerative,<br />

if used <strong>for</strong> high values crops with good agriculture practices and optimum inputs.<br />

<strong>Soil</strong> conservation measures<br />

Various mechanical, agronomic and agro-<strong>for</strong>estry measures can be adopted <strong>for</strong> controlling<br />

soil and water erosion. Under mechanical measures like contour and graded bunds, bench, half<br />

moon and conservation bench terraces etc. and in agronomic measures like cropping systems,<br />

cover crops, mulching, contour cultivation tillage etc. are some <strong>of</strong> <strong>the</strong> promising techniques <strong>for</strong><br />

controlling <strong>the</strong> loss <strong>of</strong> <strong>the</strong> top soil. Agro-<strong>for</strong>estry is becoming popular and a useful way to arrest <strong>the</strong><br />

soil erosion on slopy lands. Moisture conservation in arid regions and plantations <strong>of</strong> multipurpose<br />

trees and shrubs are helpful in controlling soil loss through wind erosion.<br />

Conservation tillage<br />

Conservation tillage in a broad sense is any tillage system that is less intensive than<br />

conventional tillage. In this tillage both land preparation and sowing operations is combined in one<br />

operation or tillage operations <strong>for</strong> land preparation are eliminated altoge<strong>the</strong>r. The most important<br />

component <strong>of</strong> conservation tillage is <strong>the</strong> retention <strong>of</strong> crop residues on soil surface. The success or<br />

failure <strong>of</strong> conservation tillage depends on <strong>the</strong> use <strong>of</strong> herbicides, crop residue management and<br />

efficiency <strong>of</strong> planting equipments to place seed in soil below <strong>the</strong> residues. Conservation tillage<br />

practices minimize <strong>the</strong> soil disturbance, conserve moisture, control soil erosion, and increase SOM<br />

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by reducing its losses via oxidation and addition through crop residue retention.<br />

Amendments in saline and sodic soils<br />

In <strong>the</strong> saline and sodic soils, plant growth is restricted due to increased level <strong>of</strong> salts. To<br />

get good production, <strong>the</strong> process <strong>of</strong> accumulation <strong>of</strong> salts and build up <strong>of</strong> soil electrical conductivity<br />

have to be reversed. To achieve <strong>the</strong>se objectives provision <strong>of</strong> adequate drainage, replacement <strong>of</strong><br />

high concentration <strong>of</strong> Ca ++ , Mg ++ and Na + ions from <strong>the</strong> soil exchange complex and leaching out <strong>of</strong><br />

<strong>the</strong> soluble salts have to ensure. Deep ploughing, sub-soiling, pr<strong>of</strong>ile inversion and scraping are<br />

few o<strong>the</strong>r options <strong>for</strong> managing <strong>the</strong> salt affected soils. These are only temporary measures <strong>for</strong><br />

improving <strong>the</strong> plant growth and generally suitable only <strong>for</strong> saline soils. Alkali/sodic soil require<br />

neutralization <strong>of</strong> alkalinity and replacement <strong>of</strong> Na + ions from <strong>the</strong> soil exchange complex by <strong>the</strong><br />

more favourable salt <strong>of</strong> Ca ++ ions using chemical amendments. The type <strong>of</strong> chemical compounds<br />

and <strong>the</strong>ir quantities required <strong>for</strong> reclamation depend upon physico-chemical properties <strong>of</strong> <strong>the</strong> soil,<br />

desired rate <strong>of</strong> replacement <strong>of</strong> Na + ions and economic consideration. Gypsum is <strong>the</strong> most<br />

economical and commonly used chemical amendment. Besides pyrite, presumed, rice husk,<br />

elemental sulphur, some agro based industrial effluents may also be used judiciously <strong>for</strong> improving<br />

<strong>the</strong> physico-chemical and biological properties <strong>of</strong> salt affected soils depending on <strong>the</strong>ir availability<br />

and economics.<br />

Liming in acid soils<br />

Acid soils in India cover about 30 percent <strong>of</strong> <strong>the</strong> total area <strong>of</strong> <strong>the</strong> country. Low pH <strong>of</strong> acid<br />

soils is not only harmful to plants, but also causes imbalance <strong>of</strong> plant nutrients restricting <strong>the</strong>ir<br />

availability to plants. Acids soils are generality deficient in calcium and magnesium, low in<br />

phosphorus and usually have toxicity <strong>of</strong> iron and aluminum. Micronutrients content <strong>of</strong> acids soils<br />

differs with locations depending upon <strong>the</strong> process <strong>of</strong> <strong>the</strong>ir development and parent materials. Lime<br />

application to <strong>the</strong> crops is <strong>the</strong> most suitable and easy way to increase crop production in <strong>the</strong>ses<br />

soils. Since <strong>the</strong> crops have greater degree <strong>of</strong> tolerance <strong>for</strong> soil acidity especially in <strong>the</strong> pH range <strong>of</strong><br />

5-6, <strong>the</strong> response <strong>of</strong> lime application vary with crops. Crops such as cotton, arhar, lentil, peas,<br />

maize show considerable response to lime application in terms <strong>of</strong> increase in <strong>the</strong> productivity,<br />

whereas upland rice, millets and mustard crops give little or no response to lime application in acid<br />

soils.<br />

Issues and Challenges<br />

The perception that enough is already known about soils is incorrect. Despite, significant<br />

and inevitable role <strong>of</strong> soils in maintaining food security, required emphasis has not been given to<br />

soil management by now. There is need to understand <strong>the</strong> role <strong>of</strong> society in sustaining agriculture<br />

and conversely, <strong>the</strong> role <strong>of</strong> soil in sustaining <strong>the</strong> society. The policies and practices that have<br />

contributed to soil degradation and decline in productivity have to be reversed. Appropriate<br />

national policies should be <strong>for</strong>mulated and implemented to ensure no or minimum land<br />

degradation. Availability <strong>of</strong> sufficient research and development funds to match <strong>the</strong>ir significance in<br />

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terms <strong>of</strong> <strong>the</strong> cost to society, if soils become degraded, must be ensured. The requirement <strong>of</strong> water<br />

(quality and quantity) <strong>for</strong> crop production must be assessed on long-term basis. An understanding<br />

and utilization <strong>of</strong> indigenous knowledge on land degradation, cropping and farming systems, and<br />

soil and water management is necessary <strong>for</strong> obtaining pr<strong>of</strong>itable crop production to ensure food<br />

security in degraded soils.<br />

REFERENCES<br />

• Lal, R. 1994. Sustainable Land Use Systems and <strong>Soil</strong> Resilience, dans Greenland, D.J. et<br />

Szabolcs, I. (édit), <strong>Soil</strong> Resilience and Sustainable Land Use, pp. 41-67. CAB -<br />

International, Walling<strong>for</strong>d, RU.<br />

• Samra, J. S. and Sharma, K. D. 2010. Ground water management <strong>for</strong> national food security. One<br />

day 2 nd National Ground Water Congress, Organized by Central Ground Water<br />

Board on March 22, 2010, Ministry <strong>of</strong> Water Resources, GOI, New Delhi.<br />

• Seneviratne, G. 2009. Collapse <strong>of</strong> beneficial microbial communities and deterioration <strong>of</strong> soil<br />

health: a cause <strong>for</strong> reduced crop productivity. Current Science 96:633.<br />

• Singh, G. B. 2000. VISION 2020: Natural resource management research. Division <strong>of</strong> Natural<br />

resource management, ICAR, Krishi Bhawan, New Delhi.<br />

• Singh, M.V. 1998. 28 th Progress report <strong>of</strong> 1996-98 <strong>for</strong> <strong>the</strong> AICRP <strong>of</strong> Micro- and Secondary<br />

Nutrients and Pollutants in <strong>Soil</strong>s and <strong>Plant</strong>s. IISS, Bhopal. Pp. 1-137.<br />

• Yadav, J.S.P. 1996. Land degradation and its effect on soil productivity, sustainability and<br />

environment. Journal <strong>of</strong> <strong>Soil</strong> and Water Conservation 40: 660-674.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Role <strong>of</strong> <strong>Plant</strong> Growth Promoting Rhizobacteria in Crop Improvement<br />

Anita Sharma, Shubhi Sharma and Geeta Negi<br />

Department <strong>of</strong> Microbiology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Rhizosphere is a narrow region <strong>of</strong> soil that is directly influenced by root secretions and<br />

associated soil microorganisms that feed on sloughed-<strong>of</strong>f plant cells, rhizodepositions (amino<br />

acids, hormones, vitamins) and numerous proteins and sugars released by <strong>the</strong> roots. These<br />

rhizodepositions promote extensive growth <strong>of</strong> bacteria and fungi which make micro colonies on<br />

root surface and show beneficial effect on plants growth. Beneficial effects <strong>of</strong> <strong>Plant</strong> growthpromoting<br />

rhizobacteria (PGPR) on different crops have been reported by Kloepper and Schroth,<br />

(1978). Rhizospheric bacteria help tolerate abiotic stress (Yang,et al. (2009). plant growthpromoting<br />

bacteria directly facilitate <strong>the</strong> proliferation <strong>of</strong> plants by fixing atmospheric nitrogen;<br />

producing siderophores (iron sequester), syn<strong>the</strong>sizing phytohormones, enzymes and solubilizing<br />

minerals such as phosphorus and Zn. Moreover, many plant growth promoting bacteria possess<br />

several o<strong>the</strong>r activities that enable <strong>the</strong>m to facilitate plant growth and, <strong>of</strong> <strong>the</strong>se, may utilize different<br />

ones at various times during <strong>the</strong> life cycle <strong>of</strong> plant. PGP activity has been reported in strains<br />

belonging to several genera such as Azoarcus, Azospirillum, Azotobacter, Arthrobacter, Bacillus,<br />

Clostridium, Enterobacter, Gluconacetobacter, Pseudomonas, and Serratia (Somers and<br />

Vanderleyden, 2004).<br />

Applications <strong>of</strong> PGPR <strong>for</strong> crop improvement<br />

Biological nitrogen fixation<br />

A number <strong>of</strong> bacterial species belonging to genera Azospirillum, Alcaligenes, Arthrobacter,<br />

Acinetobacter, Bacillus, Burkholderia, Enterobacter, Erwinia, Flavobacterium, Pseudomonas,<br />

Rhizobium and Serratia are associated with <strong>the</strong> plant rhizosphere and are able to exert a<br />

beneficial effect on plant growth. Biological nitrogen fixation contributes 180 X 106 metric tons/year<br />

globally, out <strong>of</strong> which symbiotic associations’ produces 80% and <strong>the</strong> rest comes from free-living or<br />

associative systems. The ability to reduce and derive such appreciable amounts <strong>of</strong> nitrogen from<br />

<strong>the</strong> atmospheric reservoir and enrich <strong>the</strong> soil is confined to bacteria and Archaea.<br />

HCN production<br />

Although cyanide acts as a general metabolic inhibitor, it is syn<strong>the</strong>sized, excreted and<br />

metabolized by hundreds <strong>of</strong> organisms, including bacteria, algae, fungi, plants, and insects, as a<br />

mean to avoid predation or competition. The host plants are generally not negatively affected by<br />

inoculation with cyanide-producing bacterial strains and host-specific rhizobacteria can act as<br />

biological weed-control agents. A secondary metabolite produced commonly by rhizosphere<br />

pseudomonads is Hydrogen Cyanide (HCN), a gas known to negatively affect root metabolism and<br />

root growth and is a potential and environmentally compatible mechanism <strong>for</strong> biological control <strong>of</strong><br />

weeds. The HCN production is found to be a common trait <strong>of</strong> Pseudomonas (88.89%) and Bacillus<br />

(50%) in <strong>the</strong> rhizospheric soil and plant root nodules and is a serious environmental pollutant and<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

a biocontrol metabolite in Pseudomonas species.<br />

Biosurfactant<br />

Biosurfactants are structurally diverse group <strong>of</strong> surface active molecules syn<strong>the</strong>sized by<br />

<strong>the</strong> microorganisms. They are amphipathic molecules with hydrophilic and hydrophobic moieties<br />

that partition preferentially at <strong>the</strong> interface between fluid phases. The biocontrol potential <strong>of</strong><br />

biosurfactant has been recently discovered. Rhamnolipids (type <strong>of</strong> biosurfactant containing<br />

rhamnose sugar produced by Pseudomonas) are highly effective against Pythium<br />

aphanidermatum, Plasmapara lactucae and Phytophthora capsici. Biosurfactants with both<br />

hydrophilic and lipophilic structural moieties facilitate <strong>the</strong> uptake <strong>of</strong> hydrocarbons into <strong>the</strong> cells.<br />

Microbial compounds like lipopeptide, glycolipids, fatty acids and polymeric biosurfactants have<br />

been found to have surface activity and able to reduce surface tension and interfacial tension<br />

between water and hydrocarbon phases. Environmental stimuli i.e. carbon substrate, limitation by<br />

C, N or P, Fe limitation and growth phase condition may affect biosurfactant production.<br />

Role <strong>of</strong> PGPR in nitrate mobilization<br />

<strong>Plant</strong> growth-promoting bacteria and NO 3 availability both affect NO 3 uptake and root<br />

architecture in plants. The presence <strong>of</strong> external NO 3 induces <strong>the</strong> expression <strong>of</strong> NO 3 transporter<br />

genes and elicits lateral root elongation in <strong>the</strong> part <strong>of</strong> <strong>the</strong> root system exposed to <strong>the</strong> NO 3 supply.<br />

By contrast, an increase in NO 3 supply leads to a higher plant N status (low N demand), which<br />

represses NO 3 transporters and lateral root development. The effects <strong>of</strong> PGPB on NO 3 uptake and<br />

root development are similar to those <strong>of</strong> low NO 3 availability (concomitant stimulation <strong>of</strong> NO 3<br />

uptake rate and lateral root development).<br />

Phosphate solubilizing microorganisms (PSM)<br />

Phosphorus is one <strong>of</strong> <strong>the</strong> - major plant nutrients required <strong>for</strong> proper plant growth but 90%<br />

Indian soils have inadequate supply <strong>of</strong> available phosphorus. Most <strong>of</strong> <strong>the</strong> essential plant nutrients<br />

including phosphorus remain in insoluble <strong>for</strong>m in soil. <strong>Plant</strong>s absorb P from <strong>the</strong> soil in <strong>the</strong> ionic<br />

<strong>for</strong>m (H 2 PO -) 4 and (HPO 4 ) - 2. Low levels <strong>of</strong> soluble phosphate can limit <strong>the</strong> growth <strong>of</strong> plants. The<br />

phenomena <strong>of</strong> fixation and precipitation <strong>of</strong> P in soils depends upon pH. It has been established<br />

that <strong>the</strong>re are specific groups <strong>of</strong> soil microorganisms which increase <strong>the</strong> availability <strong>of</strong> phosphates<br />

to plants, not only by mineralizing organic phosphorous compounds but also by rendering<br />

inorganic phosphorous compounds more available to <strong>the</strong>m. Most efficient P solubilizers belong to<br />

genera Bacillus and Pseudomonas. Such bacteria and fungi can grow in media where Ca 3 (PO 4 ) 2 ,<br />

FePO 4 , AlPO 4 , Apatite, Bone meal, Rock phosphate are <strong>the</strong> sole source <strong>of</strong> phosphate. The<br />

potential <strong>of</strong> phosphate solubilizing microorganisms has been assessed in Bacillus polymyxa, P<br />

striata, mycorrhizal fungi and B. firmis. These organisms are used as bioinoculants to enhance <strong>the</strong><br />

availability <strong>of</strong> unavailable P to <strong>the</strong> plants.<br />

Zn solubilizing bacteria: Extensive use <strong>of</strong> chemical fertilizers in agriculture has exploited<br />

agricultural land drastically and has led to an increased soil pH which has ultimately disturbed <strong>the</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

availability <strong>of</strong> essential micronutrients to <strong>the</strong> plants. Zn, a common and essential micronutrient <strong>of</strong><br />

various crops becomes unavailable particularly at higher pH. Availability <strong>of</strong> Zn depends upon soil<br />

type, moisture, minerals, organic matter and soil biota. More than 90% <strong>of</strong> Zn remains unavailable<br />

to <strong>the</strong> plants. Rice, sorghum and maize are classified as most sensitive crops and show deficiency<br />

symptoms <strong>of</strong> Zn where as barley and wheat are less sensitive. It acts as an essential component<br />

<strong>of</strong> different enzymes. Zn is also required as a precursor <strong>of</strong> IAA <strong>for</strong> tryptophan syn<strong>the</strong>sis.<br />

Pseudomonas and Bacillus are reported to solubilize Zn compounds (Saravanan, et al. 2003).<br />

Different authors have observed <strong>the</strong> role <strong>of</strong> organic acids (gluconic acid), root exudates,<br />

siderophores , cations and H + ions released by <strong>the</strong> plants/ bacteria in solubilization <strong>of</strong> insoluble Zn<br />

compounds (Simine et al.1998;Saravanan et al. 2007).<br />

Production <strong>of</strong> plant growth regulators<br />

<strong>Plant</strong> hormones are chemical messengers that affect a plant's ability to respond to its<br />

environment. Hormones are organic compounds that are effective at very low concentration; <strong>the</strong>y<br />

are usually syn<strong>the</strong>sized in one part <strong>of</strong> <strong>the</strong> plant and are transported to ano<strong>the</strong>r location. They<br />

interact with specific target tissues to cause physiological responses, such as growth or fruit<br />

ripening. Each response is <strong>of</strong>ten <strong>the</strong> result <strong>of</strong> two or more hormones acting toge<strong>the</strong>r. Because<br />

hormones stimulate or inhibit plant growth, many botanists also refer to <strong>the</strong>m as plant growth<br />

regulators. Botanists recognize five major groups <strong>of</strong> hormones: auxins, gibberellins, ethylene,<br />

cytokinins, and abscisic acid. IAA (indole-3-acetic acid) is <strong>the</strong> member <strong>of</strong> <strong>the</strong> group <strong>of</strong><br />

phytohormones and is generally considered <strong>the</strong> most important native Auxin. It functions as an<br />

important signal molecule in <strong>the</strong> regulation <strong>of</strong> plant development including organogenesis, tropic<br />

responses, cellular responses such as cell expansion, division, and differentiation, and gene<br />

regulation. Diverse bacterial species possess <strong>the</strong> ability to produce <strong>the</strong> auxin phytohormone IAA.<br />

The potential <strong>for</strong> auxin biosyn<strong>the</strong>sis by rhizobacteria can be used as a tool <strong>for</strong> <strong>the</strong> screening <strong>of</strong><br />

effective PGPR strains. The highest concentration <strong>of</strong> IAA is produced by bacterial strain P.<br />

fluorescens and Kocuria varians.<br />

Siderophore production<br />

Iron is an essential growth element <strong>for</strong> all living organisms. The scarcity <strong>of</strong> bioavailable iron<br />

in soil habitats and on plant surfaces foments a furious competition. Under iron-limiting conditions<br />

PGPB produce low molecular-weight compounds called siderophores to competitively acquire<br />

ferric ion. Siderophores (Greek: "iron carrier") are small, high-affinity iron chelating compounds<br />

secreted by microorganisms such as bacteria, fungi and grasses. <strong>Microbe</strong>s release siderophores<br />

to scavenge iron from <strong>the</strong>se mineral phases by <strong>for</strong>mation <strong>of</strong> soluble Fe3+ complexes that can be<br />

taken up by active transport mechanisms. Many siderophores are non-ribosomal peptides,<br />

although several are biosyn<strong>the</strong>sised independently. Siderophores are also important <strong>for</strong> some<br />

pathogenic bacteria <strong>for</strong> <strong>the</strong>ir acquisition <strong>of</strong> iron. Siderophores are amongst <strong>the</strong> strongest binders to<br />

Fe3+ known, with enterobactin being one <strong>of</strong> <strong>the</strong> strongest <strong>of</strong> <strong>the</strong>se.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

PGPR as endophytes<br />

In addition to rhizosphere and rhizoplane colonization, certain PGPR are reported to be<br />

endophytes, localized in <strong>the</strong> intercellular spaces <strong>of</strong> <strong>the</strong> root epidermal cells and vascular tissue<br />

(Chen et al., 1995; Benhamou et al., 1996; Hallmann et al., 1997; M'Piga et al., 1997).Endophytic<br />

bacteria reside within <strong>the</strong> living plant tissues without doing substantive harm or gaining benefit<br />

o<strong>the</strong>r than residency (Kado, 1992). Several factors favour endophytic bacteria as potential agents<br />

<strong>of</strong> ISR. Endophytes have a natural and intimate association with plants. The internal tissues <strong>of</strong><br />

plants provide a relatively uni<strong>for</strong>m and protected environment in comparison to rhizosphere or<br />

rhizoplane where ectophytic bacteria must compete <strong>for</strong> nutrients with o<strong>the</strong>r microbes and endure<br />

fluctuations <strong>of</strong> temperature and moisture, as well as exposure to ultraviolet radiation on above<br />

ground surfaces. In spite <strong>of</strong> <strong>the</strong>se advantages, <strong>the</strong> potential <strong>of</strong> bacterial endophytes has only been<br />

explored to a limited extent. Application <strong>of</strong> endophytic bacteria by stem injection in cotton plants<br />

reduced root rot caused by Rhizoctonia solani and vascular wilt caused by F. oxysporum f. sp.<br />

vasinfectum (Chen et al., 1995). These bacteria move upward and downward from <strong>the</strong> point <strong>of</strong><br />

application and by colonizing <strong>the</strong> internal tissues, can exclude <strong>the</strong> entry <strong>of</strong> a pathogen in <strong>the</strong><br />

vascular stele.<br />

PGPR as biocontrol agent<br />

<strong>Plant</strong> diseases are responsible <strong>for</strong> annual crop losses at a total value <strong>of</strong> more than 200<br />

billion (Agrios, 2005). Resistant plants and chemicals are <strong>of</strong>ten used to control plant diseases.<br />

Resistance does not exist against all <strong>the</strong> diseases and <strong>the</strong> breeding <strong>of</strong> resistant plants takes many<br />

years. Moreover, acceptance <strong>of</strong> genetically engineered resistance is still a sensitive issue in <strong>the</strong><br />

European Union. The use <strong>of</strong> agrochemicals is negatively perceived by <strong>the</strong> consumers and<br />

supermarket chains. It is being increasingly banned by governmental policies. Spontaneous<br />

control <strong>of</strong> plant diseases by bacteria in some fields was discovered at several places around <strong>the</strong><br />

world. The use <strong>of</strong> microbes to control diseases, which is a <strong>for</strong>m <strong>of</strong> biological control, is an<br />

environment-friendly approach. The microbe is a natural enemy <strong>of</strong> <strong>the</strong> pathogen, and if it produces<br />

secondary metabolites, it does so only locally, on or near <strong>the</strong> plant surface, i.e., <strong>the</strong> site where it<br />

should act. In contrast, <strong>the</strong> majority <strong>of</strong> molecules <strong>of</strong> agrochemicals do not reach <strong>the</strong> plant at all.<br />

Moreover, <strong>the</strong> molecules <strong>of</strong> biological origin are biodegradable compared with many<br />

agrochemicals that are designed to resist degradation by <strong>the</strong> microbes. The term biocontrol is<br />

used not only to control diseases in living plants but also to control diseases occurring during <strong>the</strong><br />

storage <strong>of</strong> fruits (also called post harvest control). Studies on <strong>the</strong> control <strong>of</strong> pathogens by<br />

rhizobacteria usually focus on pathogenic microorganisms. Some rhizobacteria are found active<br />

against weeds (Floresfargas and O , Hara, 2006) and insects (Siddiqui et al., 2005, Pechy et al.,<br />

2008).Application <strong>of</strong> PGPR in control <strong>of</strong> plant diseases ,mechanisms involved and <strong>the</strong>ir future<br />

prospects have been described by Compant et al. (2005).<br />

<strong>Soil</strong>s in which pathogens cause disease symptoms are called conducive soils. Some soils,<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

called suppressive soils, contain bacteria that protect plants against fungal diseases despite <strong>the</strong><br />

presence <strong>of</strong> disease-causing pathogens in soil. Mixing small amount <strong>of</strong> suppressive soil with a<br />

large amount <strong>of</strong> conducive soil makes <strong>the</strong> latter soil suppressive. Influence <strong>of</strong> soil factors and<br />

culture practices affect antagonistic efficiency <strong>of</strong> inoculated bacteria on sheath blight <strong>of</strong> rice<br />

(Gnanamanickan et al. (1992). Microbial control <strong>of</strong> plant diseases is a complex process involving<br />

not only <strong>the</strong> biocontrol microbe, <strong>the</strong> pathogen, and <strong>the</strong> plant, but also <strong>the</strong> indigenous micr<strong>of</strong>lora,<br />

macrobiota such as nematodes and protozoa, and soil, stonewool, or vermiculite (Thomashow and<br />

Weller, 1996, Chin-A-Woeng et al., 2003, Compant et al., 2005, Haas and Defago, 2005). To act<br />

efficiently, microbial control agent should remain active under a large range <strong>of</strong> conditions, such as<br />

varying pH, temperature, and concentrations <strong>of</strong> different ions. These requirements are not easy to<br />

fulfill. There<strong>for</strong>e, it is not surprising that <strong>the</strong> efficacy <strong>of</strong> several first-generation commercial<br />

biocontrol products is not always sufficient (Copping, 2004).<br />

Mixed Bacterial Inoculants: Concept and Potential <strong>for</strong> <strong>the</strong> Future<br />

Increased use <strong>of</strong> chemical fertilizer is responsible <strong>for</strong> progressive deterioration <strong>of</strong> soil<br />

health. Reports from various parts <strong>of</strong> <strong>the</strong> country such as Punjab and Uttar Pradesh suggest that<br />

inspite <strong>of</strong> all ef<strong>for</strong>ts, production has come down, which may be correlated with decline in microbial<br />

biomass and <strong>the</strong> accumulation <strong>of</strong> nitrates, nitrites, phosphates and o<strong>the</strong>r essential nutrients in <strong>the</strong><br />

soil. In this changed scenario, it is being realized seriously to accept biological means <strong>for</strong> <strong>the</strong><br />

improvement <strong>of</strong> not only legumes but <strong>for</strong> o<strong>the</strong>r crops as well. Application <strong>of</strong> microbial inoculants is<br />

a low cost eco- friendly technology to enhance crop productivity. Mixed inoculants (combinations<br />

<strong>of</strong> microorganisms) that interact synergistically are currently being devised. Microbial studies<br />

per<strong>for</strong>med without plants indicate that some mixtures allow <strong>the</strong> bacteria to interact with each o<strong>the</strong>r<br />

synergistically, providing nutrients, removing inhibitory products, and stimulating each o<strong>the</strong>r<br />

through physical or biochemical activities that may enhance some beneficial aspects <strong>of</strong> <strong>the</strong>ir<br />

physiology. It still has to be demonstrated that <strong>the</strong>se bacterial synergistic effects also benefit plant<br />

growth. An example <strong>of</strong> this is Azospirillum, one <strong>of</strong> <strong>the</strong> most studied bacteria that associate with<br />

plants (Bashan and Holguin, 1997a). It may associate with sugar- or polysaccharide-degrading<br />

bacteria (PDB), establishing a metabolic association where <strong>the</strong> sugar-degrading bacteria produce<br />

degradation and fermentation products used by Azospirillum as a carbon source, which in turn<br />

provides PDB with nitrogen. O<strong>the</strong>r examples are <strong>the</strong> association between Azospirillum and<br />

Bacillus that degrades pectin, Azospirillum and Cellulomonas that degrades cellulose, and<br />

Azospirillum and Emerobacter cloacae that ferments glucose .<strong>Plant</strong> studies have shown that <strong>the</strong><br />

beneficial effects <strong>of</strong> Azospirillum on plants can be enhanced by co-inoculation with o<strong>the</strong>r<br />

microorganisms. Co-inoculation, frequently, increases growth and yield, compared to single<br />

inoculation and provide <strong>the</strong> plants with more balanced nutrition, and improved absorption <strong>of</strong><br />

nitrogen, phosphorus, and mineral nutrients. Thus, plant growth can be increased by dual<br />

inoculation with Azospirillum and phosphate-solubilizing bacteria. Azospirillum is also considered<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

to be a Rhizobium-"helper" stimulating nodulation, nodule activity, and plant metabolism.<br />

Challenges with PGPR: One <strong>of</strong> <strong>the</strong> challenges <strong>of</strong> using PGPR is natural variation. It is difficult to<br />

predict how an organism may respond when placed in <strong>the</strong> field (compared to <strong>the</strong> controlled<br />

environment <strong>of</strong> a laboratory). PGPR are living organisms and should be able to propagate<br />

artificially to optimize <strong>the</strong>ir viability and biological activity until field application. Like rhizobia, PGPR<br />

do not live <strong>for</strong>ever in a soil and over time growers will need to re-inoculate seeds to bring back<br />

<strong>the</strong>ir populations.<br />

Conclusion<br />

PGPRs are <strong>the</strong> potential tools <strong>for</strong> sustainable agriculture and trend <strong>for</strong> <strong>the</strong> future. For this<br />

reason, <strong>the</strong>re is an urgent need <strong>for</strong> research to clear definition <strong>of</strong> what bacterial traits are useful<br />

and necessary <strong>for</strong> different environmental conditions and plants, so that optimal bacterial strains<br />

can ei<strong>the</strong>r be selected and/or improved. Combinations <strong>of</strong> beneficial bacterial strains that interact<br />

synergistically are currently being devised and numerous recent studies show a promising trend in<br />

<strong>the</strong> field <strong>of</strong> inoculation technology.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Implication <strong>of</strong> PGPR <strong>for</strong> Rhizospheric Colonization and <strong>Plant</strong> Growth<br />

Promotion<br />

Introduction<br />

Reeta Goel<br />

Department <strong>of</strong> Microbiology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Chemical fertilizers have played a significant role in <strong>the</strong> green revolution, but <strong>the</strong>ir<br />

unbalanced use has led to reduction in soil fertility and environmental degradation .However, a<br />

large portion <strong>of</strong> soluble inorganic phosphate applied to soil as chemical fertilizer is immobilized<br />

rapidly and becomes unavailable to plants, which is not an environment friendly approach.<br />

Optimization <strong>of</strong> a biological phosphate solubilizer in <strong>the</strong> <strong>for</strong>m <strong>of</strong> rhizospheric microorganisms<br />

seems to be a suitable tool to release some <strong>of</strong> <strong>the</strong> soil-bound phosphates and reduce <strong>the</strong> use <strong>of</strong><br />

chemical fertilizers.<br />

<strong>Plant</strong> Growth Promoting Rhizobacteria (PGPR)<br />

The group <strong>of</strong> bacteria that colonize roots or rhizosphere soil and beneficial to crops are<br />

referred to as plant growth promoting rhizobacteria (PGPR). <strong>Plant</strong> growth-promoting rhizobacteria<br />

(PGPR) are free-living, soil-borne bacteria, which enhance <strong>the</strong> growth <strong>of</strong> <strong>the</strong> plant or reduce <strong>the</strong><br />

damage from soil-borne plant pathogens. PGPR are <strong>the</strong> rhizospheric bacteria that can enhance<br />

plant growth by a wide variety <strong>of</strong> mechanisms like phosphate solubilization, siderophore<br />

production, biological nitrogen fixation, rhizosphere engineering, production <strong>of</strong> 1-<br />

Aminocyclopropane-1- carboxylate deaminase (ACC), quorum sensing (QS) signal interference<br />

and inhibition <strong>of</strong> bi<strong>of</strong>ilm <strong>for</strong>mation, phytohormone production, exhibiting antifungal activity,<br />

production <strong>of</strong> volatile organic compounds (VOCs), induction <strong>of</strong> systemic resistance, promoting<br />

beneficial plant-microbe symbioses, interference with pathogen toxin production etc.<br />

P Solubilization<br />

Phosphorus (P) is <strong>the</strong> second most essential nutrient after nitrogen (N) and limits plant<br />

growth and development. <strong>Soil</strong> microorganisms are effective in releasing phosphate from total soil<br />

phosphorus through solubilization and mineralization. Microorganisms solubilized inorganic<br />

phosphates in soil and making <strong>the</strong>m available to plants is well known. These microorganisms are<br />

called Phosphate Solubilizing Bacteria (PSB) and <strong>the</strong>y convert insoluble phosphates to soluble<br />

phosphates by acidification.<br />

PSB<br />

PSB bring about <strong>the</strong> mobilization <strong>of</strong> insoluble phosphates in <strong>the</strong> soil and increase plant<br />

growth under conditions <strong>of</strong> poor phosphorus availability. These microorganisms also have <strong>the</strong><br />

potential <strong>for</strong> ecological amelioration <strong>of</strong> P and <strong>the</strong>reby improve growth and <strong>the</strong> establishment <strong>of</strong><br />

plants under low phosphorus availability. These beneficial bacteria enhance plant growth by<br />

improving soil nutrient status, secreting plant growth regulators and suppressing soil-borne<br />

pathogens. The use <strong>of</strong> phosphate solubilizing bacteria as inoculants simultaneously increases P<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

uptake by <strong>the</strong> plant and crop yield. Strains from <strong>the</strong> genera Pseudomonas, Bacillus and Rhizobium<br />

are among <strong>the</strong> most powerful phosphate solubilizers<br />

Our Contribution<br />

Experiments<br />

35 bacterial isolates were originally isolated from Ranichauri and Pithoragarh (Uttarakhand,<br />

India) rhizospheric soils <strong>of</strong> legume crops and were screened <strong>for</strong> qualitative phosphate<br />

solubilization assay on Pikovskaya agar medium plate. Eight <strong>of</strong> those isolates were evident by a<br />

clear halo around <strong>the</strong> bacterial colony on Pikovskaya agar plates. Fur<strong>the</strong>r, two potential PSB,<br />

Chryseobacterium sp. PSR10 and Escherichia coli RGR13 were selected <strong>for</strong> fur<strong>the</strong>r studies. On<br />

<strong>the</strong> basis <strong>of</strong> <strong>the</strong> pot trial study, Chryseobacterium sp. PSR10 strain was selected <strong>for</strong> field study.<br />

Results<br />

<strong>Plant</strong> growth-promoting activities were found to be stimulated in <strong>the</strong> presence <strong>of</strong> microbial<br />

inoculant Chryseobacterium sp. PSR10.<br />

A green house study was conducted to evaluate <strong>the</strong> bioremediation potential and plant<br />

growth promoting activities <strong>of</strong> <strong>the</strong> two potential bacterial strains, Pseudomonas putida 710A and<br />

Commamonas aquatica 710B. Both were originally isolated from soil samples from <strong>the</strong> Semra<br />

mines in Palamau, Jharkhand and were resistant up to 1 mM CdCl 2 and 0.5 mM CdCl 2 ,<br />

respectively. They were screened <strong>for</strong> P solublization followed by heavy metal analysis.<br />

Results<br />

Pseudomonas putida 710A showed better P solubilizing activity, when grown in liquid broth<br />

supplemented with cadmium at 10 °C. Moreover, <strong>the</strong> strain was able to reduce Cd accumulation in<br />

roots and shoots.<br />

Future Prospects<br />

‣ Chryseobacterium sp. PSR10 might be used as a convenient, cost-effective and<br />

ec<strong>of</strong>riendly PSB.<br />

‣ Pseudomonas putida 710A strain could be explored <strong>for</strong> sequestering and as a<br />

growthpromoting bioinoculant in Cd polluted soil.<br />

Publications<br />

‣ Singh AV, Chandra R, Goel, R (2012) Phosphate solubilization by Chryseobacterium sp.<br />

and <strong>the</strong>ir combined effect with N and P fertilizers on plant growth promotion. Archives <strong>of</strong><br />

Agronomy and <strong>Soil</strong> Science. DOI:10.1080/03650340.2012.664767.<br />

‣ Rani A, Souche Y, Goel R (2012) Comparative in situ remediation potential <strong>of</strong><br />

Pseudomonas putida 710A and Commamonas aquatica 710B using plant (Vigna radiata<br />

(L.) wilczek) assay. Ann Microbiol. DOI 10.1007/s13213-012-0545-1.<br />

Funding Agencies<br />

‣ DBT<br />

‣ NBAIM/ICAR<br />

Collaborators<br />

‣ Dr. Yogesh Souche : NCCS, Pune<br />

‣ Dr. Ramesh Chandra : Deptt. <strong>of</strong> <strong>Soil</strong> Science, GBPUAT, Pantnagar<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Microbe</strong>s and Intellectual Property Rights<br />

H.S. Chawla<br />

Department <strong>of</strong> Genetics & <strong>Plant</strong> Breeding, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

The WTO was established on 1 st<br />

January 1995 and is responsible <strong>for</strong> making and<br />

en<strong>for</strong>cing rules <strong>for</strong> trade between nations. WTO marks a major change in global trade rules. As an<br />

organization, it replaces <strong>the</strong> General Agreement on Tariffs and Trades (GATT), which had been in<br />

existence since 1947. All <strong>the</strong> agreements annexed to <strong>the</strong> Agreement establishing <strong>the</strong> WTO were<br />

signed as part <strong>of</strong> a package deal. Member countries did not have <strong>the</strong> option <strong>of</strong> choosing some and<br />

rejecting o<strong>the</strong>rs. Ano<strong>the</strong>r important difference with <strong>the</strong> erstwhile GATT is that WTO has a stronger<br />

compliance mechanism than <strong>the</strong> GATT. A member’s failure to meet <strong>the</strong> obligations can invoke<br />

retaliation across agreements and sectors (Chawla, 2007). As one <strong>of</strong> <strong>the</strong> WTO agreements,<br />

TRIPS is binding on all member countries <strong>of</strong> WTO. TRIPS aim at establishing strong minimum<br />

standards <strong>for</strong> intellectual property rights (IPRs).<br />

Intellectual property rights (IPRs) protection plays a key role in getting an advantageous<br />

position in <strong>the</strong> competitive world <strong>for</strong> achieving economic growth. This has become more<br />

pronounced in <strong>the</strong> globalized economy with <strong>the</strong> obligations in <strong>the</strong> field <strong>of</strong> IPR in <strong>the</strong> WTO regime.<br />

With <strong>the</strong> globalization <strong>of</strong> trade and commerce, it has become important to enrich our knowledge<br />

about IPRs. IPRs are important not only because India as a member is required to accede to <strong>the</strong><br />

conditions <strong>of</strong> an international agreement but also because <strong>the</strong>y <strong>of</strong>fer possible mechanisms <strong>for</strong><br />

stimulating research, enabling access to technology and promoting enterprise growth with an<br />

ultimate aim to benefit human population. The importance <strong>of</strong> IPRs can be gauged from <strong>the</strong> fact<br />

that most globally competitive corporations strategically protect <strong>the</strong>ir intellectual properties in all<br />

potential markets/countries by filing patents and o<strong>the</strong>r IP arrangements. Although each country<br />

implements intellectual property laws at <strong>the</strong> national level, <strong>the</strong> TRIPS (Trade Related Aspects <strong>of</strong><br />

Intellectual Property Rights) agreement imposes minimum standards on patents and o<strong>the</strong>r IPs. As<br />

a result <strong>of</strong> <strong>the</strong> commitments made under <strong>the</strong> TRIPS Agreement, India has enacted and amended<br />

<strong>the</strong>ir existing norms <strong>of</strong> IP protection to be TRIPS compliant, <strong>for</strong> which <strong>the</strong> deadline was December,<br />

2004.<br />

IPRs can be defined as <strong>the</strong> rights given to people over <strong>the</strong> creation <strong>of</strong> <strong>the</strong>ir minds. They<br />

usually give <strong>the</strong> creator an exclusive right over <strong>the</strong> use <strong>of</strong> his/her creation <strong>for</strong> a certain period <strong>of</strong><br />

time. Intellectual property includes patents, copyrights, trademarks, geographical indications,<br />

industrial designs, integrated circuits and trade secrets. The protection <strong>of</strong> IPRs is binding and<br />

legally en<strong>for</strong>ceable.<br />

IPRs have been created to ensure protection against unfair trade practice. Owners <strong>of</strong> IP<br />

are granted protection by a state and/or country under varying conditions and periods <strong>of</strong> time. This<br />

protection includes <strong>the</strong> right to: (i) defend <strong>the</strong>ir rights to <strong>the</strong> property <strong>the</strong>y have created; (ii) prevent<br />

o<strong>the</strong>rs from taking advantage <strong>of</strong> <strong>the</strong>ir ingenuity; (iii) encourage <strong>the</strong>ir continuing innovativeness and<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

creativity; and (iv) assure <strong>the</strong> world a flow <strong>of</strong> useful, in<strong>for</strong>mative and intellectual works.<br />

Patents<br />

A patent is a government granted exclusive right to an inventor <strong>for</strong> <strong>the</strong> development <strong>of</strong> a<br />

new product or process involving an inventive step which is capable <strong>of</strong> industrial application. This<br />

will prevent o<strong>the</strong>rs from practicing i.e. making, using or selling <strong>the</strong> invention. A patent is a personal<br />

property, which can be licensed or sold like any o<strong>the</strong>r property. The purpose <strong>of</strong> a patent is to<br />

encourage and develop new innovations. The Patent Law recognizes <strong>the</strong> exclusive right <strong>of</strong> a<br />

patentee to gain commercial advantage out <strong>of</strong> his invention. There are three criteria <strong>of</strong> novelty,<br />

inventiveness and usefulness to issue a patent <strong>for</strong> <strong>the</strong> innovation. In <strong>the</strong> patent adequate<br />

disclosure should be made so that o<strong>the</strong>rs can also work on it. It should have <strong>the</strong> features: i) be a<br />

written description; ii) enables o<strong>the</strong>r persons to follow; iii) adequate and iv) deposit mechanism.<br />

The present law, Patents Act 1970, amendment 2005 is effective from January 1, 2005. Process<br />

and product patents on all items including food, agro-chemical and pharmaceuticals have been<br />

allowed making The Patents Act fully TRIPS compliant.<br />

The patent system was developed as a means to reward inventions which would be useful<br />

to <strong>the</strong> society. However, in order to ensure <strong>the</strong> interests <strong>of</strong> society, as per <strong>the</strong> Indian Patents Act,<br />

certain things have been excluded from <strong>the</strong> purview <strong>of</strong> patentability (Anonymous (2011). The<br />

sections relevant to <strong>the</strong> title under consideration which are excluded from patentability are:<br />

Section 3(d): <strong>the</strong> mere discovery <strong>of</strong> any new property or mere new use <strong>for</strong> a known substance<br />

or <strong>the</strong> mere use <strong>of</strong> a known process, machine or apparatus unless such known process results<br />

in a new product or employ at least one new reactant;<br />

Section 3(e): a substance obtained by merely admixture resulting only in <strong>the</strong> aggregation <strong>of</strong><br />

<strong>the</strong> properties <strong>of</strong> <strong>the</strong> components <strong>the</strong>re<strong>of</strong> or a process <strong>for</strong> producing such substance:<br />

Section 3(i): any process <strong>for</strong> medicinal, surgical, curative, prophylactic (diagnostic <strong>the</strong>rapeutic)<br />

or o<strong>the</strong>r treatment <strong>of</strong> human beings or any process <strong>for</strong> a similar treatment <strong>of</strong> animals to render<br />

<strong>the</strong>m free <strong>of</strong> disease or to increase <strong>the</strong>ir economic value or that <strong>of</strong> <strong>the</strong>ir products:<br />

Section 3(j): plants and animals in whole or any part <strong>the</strong>re<strong>of</strong> o<strong>the</strong>r than microorganisms but<br />

including seeds, varieties and species and essentially biological processes <strong>for</strong> production or<br />

propagation <strong>of</strong> plants and animals:<br />

Section 3(p): an invention which in effect, is traditional knowledge or which is an aggregation<br />

or duplication <strong>of</strong> known properties <strong>of</strong> traditionally known component or components:<br />

The first patent on living organism was granted to Dr Chakrabarty in 1980 <strong>for</strong> a new microorganism<br />

Pseudomonas which had four plasmids and <strong>the</strong>re<strong>for</strong>e more useful in dispersing oil slicks<br />

than <strong>the</strong> natural organism containing only one such plasmid. US Supreme Court decided that<br />

microorganism should not be precluded from patentability <strong>for</strong> <strong>the</strong> objection raised by USPTO on<br />

<strong>the</strong> basis <strong>of</strong> “product <strong>of</strong> nature”. This precedent is being followed even today to define <strong>the</strong><br />

patentability <strong>of</strong> microorganisms.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Microorganisms per se can be claimed <strong>for</strong> protection provided <strong>the</strong>y are not mere discovery<br />

<strong>of</strong> organisms. It is mandatory to deposit <strong>the</strong> biological material in International Depositary Authority<br />

(IDA). In India, Institute <strong>of</strong> Microbial Technology (IMTECH), Chandigarh is a recognized IDA <strong>for</strong><br />

some category <strong>of</strong> micro-organisms. If an applicant mentions a biological material in <strong>the</strong> patent<br />

specification <strong>the</strong>n disclosure requirements prescribed <strong>for</strong> biological materials have been notified in<br />

<strong>the</strong> list <strong>of</strong> <strong>the</strong> Central Government or <strong>for</strong> indicating its source and geographical origin [Section:<br />

10,4(d)].<br />

The purpose <strong>of</strong> a patent is to promote <strong>the</strong> progress <strong>of</strong> science and useful arts. The patent<br />

law promotes this progress by giving <strong>the</strong> inventor <strong>the</strong> right <strong>of</strong> exclusion. In exchange <strong>for</strong> this right<br />

to exclude o<strong>the</strong>rs, <strong>the</strong> inventor must disclose all details describing <strong>the</strong> invention, so that when <strong>the</strong><br />

patent period expires, <strong>the</strong> public may have <strong>the</strong> opportunity to develop and pr<strong>of</strong>it from <strong>the</strong> use <strong>of</strong><br />

invention. A patent is en<strong>for</strong>ced in <strong>the</strong> country which issues it, meaning <strong>the</strong>reby territorial in nature.<br />

For each country a separate application is to be filed in that country where protection is sought.<br />

<strong>Plant</strong> patents<br />

<strong>Plant</strong> patents are obtainable in US and Japan. The US <strong>Plant</strong> Patent Act <strong>of</strong> 1930 (PPA)<br />

granted property rights <strong>for</strong> privately developed plant varieties <strong>of</strong> asexually reproducing plants.<br />

These rights were extended to new and distinct asexual varieties <strong>for</strong> a period <strong>of</strong> seventeen years.<br />

Advances in breeding technology provided <strong>the</strong> momentum <strong>for</strong> <strong>the</strong> 1970 <strong>Plant</strong> Variety Protection<br />

Act (PVPA). The PVPA provided protection <strong>for</strong> sexually reproducing plants, including seed<br />

germination. In 1980 Diamond vs. Chakrabarty case set in motion <strong>the</strong> trend towards <strong>the</strong> legal<br />

acceptance <strong>of</strong> <strong>the</strong> commodification <strong>of</strong> germplasm. Commodification is <strong>the</strong> process whereby an<br />

object, whe<strong>the</strong>r tangible, such as seed, or intangible, such as knowledge about <strong>the</strong> seed, is turned<br />

into a commodity, i.e. something that acquires an economic worth and can be bought and sold.<br />

US Supreme Court in Diamond vs. Chakrabarty case decided that microorganism should not be<br />

precluded from patentability <strong>for</strong> <strong>the</strong> objection raised by USPTO on <strong>the</strong> basis <strong>of</strong> “product <strong>of</strong> nature”.<br />

The court held that a live, man made bacterium was patentable under <strong>the</strong> PPA and <strong>the</strong> ‘product <strong>of</strong><br />

nature’ objection <strong>the</strong>re<strong>for</strong>e failed and <strong>the</strong> modified organisms were held patentable. In <strong>the</strong> Hibberd<br />

case (1985), involving a tryptophan-overproducing mutant, <strong>the</strong> patent <strong>of</strong>fice ruled that plants could<br />

be patented and <strong>the</strong>re is no distinction between asexually and sexually propagated plants.<br />

Following <strong>the</strong> principle established in <strong>the</strong> Chakrabarty case, it was decided that normal US utility<br />

patents could be granted <strong>for</strong> o<strong>the</strong>r types <strong>of</strong> plant e.g. genetically modified plants. <strong>Plant</strong> patents<br />

have been granted by European Patent Office (EPO) from 1989. But in 1995, EPO severely<br />

restricted <strong>the</strong> scope <strong>of</strong> <strong>Plant</strong> Genetic Systems (Belgium) patent on herbicide resistant plants and<br />

allowed claims only on <strong>the</strong> herbicide resistant gene and <strong>the</strong> process used in <strong>the</strong> generation <strong>of</strong><br />

plants. In Japan, plant patents are allowed, but <strong>the</strong>re are some disputes over territorial rights. Life<br />

<strong>for</strong>ms <strong>of</strong> plants and animals except microorganisms are not patentable in India. In pursuance to<br />

<strong>the</strong> TRIPS agreement, India has enacted “Protection <strong>of</strong> <strong>Plant</strong> Varieties and Farmers’ Rights”<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

(PPV&FR) Act, 2001, a sui generis system <strong>of</strong> plant variety protection which has been described in<br />

detail separately (Chawla, 2005).<br />

<strong>Plant</strong> Variety Protection in India<br />

India and so many o<strong>the</strong>r countries do not protect plants by strict patenting system. But<br />

<strong>the</strong>re is a mandate in <strong>the</strong> TRIPS agreement that plant varieties must be protected. In pursuance to<br />

<strong>the</strong> TRIPS agreement, India has enacted “Protection <strong>of</strong> <strong>Plant</strong> Varieties and Farmers’ Rights”<br />

(PPV&FR) Act, 2001, a sui generis system <strong>of</strong> plant variety protection. The PPV&FR Act 2001<br />

provides protection to Newly bred varieties; Extant varieties – The varieties which were released<br />

under Indian Seeds Act, 1966 and have not completed 15 years as on <strong>the</strong> date <strong>of</strong> application <strong>for</strong><br />

<strong>the</strong>ir protection; Farmers’ varieties – The varieties which have been traditionally cultivated, including<br />

landraces and <strong>the</strong>ir wild relatives which are in common knowledge, as well as those evolved by<br />

farmers; Essentially derived varieties; and Transgenic varieties. To qualify <strong>for</strong> registration under <strong>the</strong><br />

act, a new variety has to con<strong>for</strong>m to <strong>the</strong> criteria <strong>of</strong> novelty (N), distinctiveness (D), uni<strong>for</strong>mity (U) and<br />

stability (S). Besides, a denomination has to be given <strong>for</strong> <strong>the</strong> registration <strong>of</strong> variety (Anonymous,<br />

2010).<br />

The Act had laid down <strong>the</strong> norms <strong>for</strong> registration <strong>of</strong> plant varieties, fee structure, provisions<br />

<strong>of</strong> opposition, DUS testing <strong>of</strong> material, etc. Intellectual Property <strong>Management</strong> Centre <strong>of</strong> G.B. Pant<br />

University <strong>of</strong> Agric. & Tech., Pantnagar has taken <strong>the</strong> lead by registering three farmers’ varieties <strong>of</strong><br />

rice namely Tilakchandan, Hansraj and Indrasan on behalf <strong>of</strong> <strong>the</strong> farmers and <strong>for</strong> <strong>the</strong> benefit <strong>of</strong><br />

farmers.<br />

Once <strong>the</strong> variety has been tested <strong>for</strong> its features <strong>the</strong>n <strong>the</strong> Registrar <strong>of</strong> <strong>the</strong> Authority will<br />

issue <strong>the</strong> certificate <strong>of</strong> registration. It shall have <strong>the</strong> validity <strong>of</strong> nine years initially in case <strong>of</strong> trees<br />

and vines with renewal up to a period <strong>of</strong> 18 years. For o<strong>the</strong>r crops certificate <strong>of</strong> registration will be<br />

issued <strong>for</strong> six years initially with renewal up to 15 years. In case <strong>of</strong> extant varieties <strong>the</strong> validity<br />

period is 15 years from <strong>the</strong> date <strong>of</strong> notification <strong>of</strong> that variety by <strong>the</strong> Central Government under<br />

section 5 <strong>of</strong> <strong>the</strong> Seeds Act 1966.<br />

Copyright<br />

Copyright protects only <strong>the</strong> <strong>for</strong>m <strong>of</strong> expression <strong>of</strong> ideas, not <strong>the</strong> ideas <strong>the</strong>mselves. The<br />

creativity protected by copyright law is creativity in <strong>the</strong> choice and arrangement <strong>of</strong> words, musical<br />

notes, colors, shapes and so on. Copyright was created to provide protection to composers,<br />

writers, authors and artists to protect <strong>the</strong>ir original works against those who copy; those who take<br />

and use <strong>the</strong> <strong>for</strong>m in which <strong>the</strong> original work was expressed by <strong>the</strong> author. Computer<br />

s<strong>of</strong>tware/program is ano<strong>the</strong>r mode <strong>of</strong> expression. A computer program is produced by one or<br />

more human authors but, in its final mode or <strong>for</strong>m <strong>of</strong> expression it can be understood directly only<br />

by a machine (<strong>the</strong> computer) not by human readers. In India, The Copyright Act 1957 as amended<br />

in 1994 is in <strong>for</strong>ce. The Copyright protection <strong>of</strong> computer s<strong>of</strong>tware is under <strong>the</strong> In<strong>for</strong>mation<br />

Technology Act, 2000 (Chawla and Singh, 2005).<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Trademark<br />

A trademark is a symbol that helps to distinguish one product or company from ano<strong>the</strong>r.<br />

Symbols help <strong>the</strong> consumer identify products and/or a company and include designs, shapes,<br />

numbers, slogan, smell, sound or anything that helps <strong>the</strong> consumer to identify <strong>the</strong> products and/or<br />

companies. In research, laboratory equipments bear trademarks that are well known to workers in<br />

<strong>the</strong>ir field. Trademark law, unlike patent or copyright law, confers a perpetual right. So long as <strong>the</strong><br />

trademark continues to identify a single source, anyone who uses a very similar mark may be<br />

liable <strong>for</strong> trademark infringement. The perpetual right <strong>of</strong> trademarks depends on <strong>the</strong> use. The<br />

basic idea <strong>of</strong> ‘use it or lose it’ is essential to preserving trademark rights. A company cannot<br />

register a trademark and <strong>the</strong>n not use it. The product <strong>for</strong> which <strong>the</strong> trademark was registered must<br />

be used commercially.<br />

Trademark rights are so important that multinational companies spend large amount <strong>of</strong><br />

money to maintain <strong>the</strong>ir respective trademarks around <strong>the</strong> world. Every country has different<br />

trademark laws. However, <strong>the</strong>re are agreements to ensure that a company’s trademark in one<br />

country is protected in ano<strong>the</strong>r country. India has a Trade Marks Act, 1999. In this category <strong>the</strong>re<br />

are certification marks like AGMARK, FPO, ISO etc.; service marks viz. LIC, SBI, PNB, etc. and<br />

collective marks viz. INTUC, AA, etc.<br />

O<strong>the</strong>r <strong>for</strong>ms<br />

There are o<strong>the</strong>r <strong>for</strong>ms <strong>of</strong> IPR protection viz. Geographical Indications <strong>of</strong> Goods, Industrial<br />

design, Trade secret and Layout designs <strong>of</strong> integrated circuits.<br />

REFERENCES<br />

• Anonymous, 2010. The Protection <strong>of</strong> <strong>Plant</strong> Varieties and Farmers’ Rights Act, 2001 and Rules,<br />

Universal Law Publishing Co., Delhi, 2010.<br />

• Chawla, H.S., 2007. Intellectual Property Rights. J. Eco-friendly Agriculture, 2(2): 103-112<br />

• Chawla, H.S. and Singh, A.K., 2005. Intellectual Property Rights. Vol II: Copyrights, Trade Marks,<br />

Trade Secrets and Geographical Indications. Pantnagar University Press, pp-75<br />

• Anonymous (2011). The Patents Act, 1970 along with The Patent rules, 2003 as amended by The<br />

Patents (Amendment) Rules, 2005, Universal Law Publishing Co., Delhi<br />

• Chawla, H.S. (2005). Patenting <strong>of</strong> biological material and biotechnology. J Intellectual Property<br />

Rights, 10: 44 – 51<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Induced Resistance: A Novel Strategy <strong>for</strong> <strong>Plant</strong> Protection against<br />

Diseases<br />

Introduction<br />

P.K. Shrotria<br />

Department <strong>of</strong> Genetics & <strong>Plant</strong> Breeding, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

The resistance in plants induced by pathogens was first recognized by Ray (1901) and<br />

Beauverie (1901). Convincing evidences however were obtained only in <strong>the</strong> 1960s, when<br />

reproducible models using tobacco plant were developed (Cruickshank and Mandryk, 1960). The<br />

induced resistance may diminish <strong>the</strong> use <strong>of</strong> toxic chemicals <strong>for</strong> disease control, and thus could be<br />

proposed as an alternative, non-conventional, non-biocidal and ecologically-friendly approach <strong>for</strong><br />

plant protection and hence <strong>for</strong> sustainable agriculture.<br />

Induced resistance<br />

When a plant is inoculated with a pathogen (“primary inoculation”), and after a time interval<br />

is subjected to a secondary (“challenge”) inoculation, reduced disease symptoms develop, i.e. <strong>the</strong><br />

induced plant becomes more resistant than <strong>the</strong> normal, non-induced plant. The term<br />

“immunization” has been used to denote treatments that enhance <strong>the</strong> defensive capacity <strong>of</strong> plants.<br />

Systemic acquired resistance (SAR) and Localized acquired resistance (LAR)<br />

In <strong>the</strong> early 1960s Ross, as a result <strong>of</strong> his carefully controlled laboratory experiments with<br />

tobacco-TMV system, coined <strong>the</strong> terms <strong>for</strong> hypersensitive reaction to TMV i.e. <strong>for</strong>ming <strong>of</strong> small<br />

necrotic lesions following TMV inoculation. Inoculation <strong>of</strong> <strong>the</strong> same leaf after a few days resulted in<br />

development <strong>of</strong> smaller-sized and less numerous lesions, i.e. <strong>the</strong> disease severity was reduced.<br />

These phenomena were referred to as LAR (Ross, 1961a). Ross succeeded also in inducing<br />

resistance to TMV in distant upper leaves <strong>of</strong> tobacco by primary inoculation <strong>of</strong> lower leaves with<br />

<strong>the</strong> virus, a phenomenon referred to as SAR (Ross, 1961b).<br />

Induced systemic resistance (ISR)<br />

Recently, <strong>the</strong> term “induced systemic resistance (ISR) has been introduced to designate<br />

<strong>the</strong> resistance induced in leaves <strong>of</strong> plants by inoculation <strong>of</strong> roots with non-pathogenic<br />

rhizobacteria. First described in Arabidopsis plants, inoculated with <strong>the</strong> root-colonizing<br />

nonpathogenic bacteria Pseudomonas fluorescens; leaves <strong>of</strong> <strong>the</strong>se plants exhibited resistance<br />

against <strong>the</strong> bacterial leaf pathogen Pseudomonas syringae pv. Tomato (Pieterse et al., 1998).<br />

Rhizobacteria-mediated ISR has also been demonstrated against fungi, bacteria and viruses in<br />

Arabidopsis, bean, carnation, cucumber, radish, tobacco and tomato (Van Loon et al., 1998).<br />

Inducers <strong>of</strong> resistance<br />

A multitude <strong>of</strong> factors are reported to induce resistance in plants: pathogens (fungi,<br />

bacteria, viruses) causing hypersensitive necrotic reaction (HR); elicitors <strong>of</strong> biotic origin; abiotic<br />

elicitors, i.e. chemical products, such as benzothiadiazole (BTH), beta-aminobutyric acid (BABA),<br />

2,6-dichloroisonicotinic acid (INA), salicylic acid, inorganic salts, etc. The use <strong>of</strong> chemicals as<br />

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inducers <strong>of</strong> resistance is an area <strong>of</strong> extensive work. Safe application in greenhouse and fields<br />

conditions viz. no direct toxicity to pathogens; no toxicity to plants and animals; no negative effects<br />

on plant growth, broad spectrum <strong>of</strong> defense, long lasting protection; low economical cost are <strong>the</strong><br />

features required in chemical inducers. The application <strong>of</strong> chemical inducers <strong>of</strong> resistance is<br />

means <strong>of</strong> disease control by providing both effective and ecologically-friendly plant protection. A<br />

large array <strong>of</strong> chemical products are shown to induce SAR in tobacco viz. salicylic acid,<br />

isonicotinic acid (INA), benzothiadiazole (BTH) and beta-aminobutyric acid (BABA). Chemicallyinduced<br />

SAR was found to be effective against fungi, bacteria and viruses. The practical<br />

application <strong>of</strong> chemicals as resistance inducers is mainly based on <strong>the</strong>ir systemic effect, i.e. on<br />

SAR expression in plants. The non-protein amino acid β-aminobutyric acid (BABA) induces<br />

resistance without <strong>the</strong> expression <strong>of</strong> PR-genes. BABA can induce resistance to H. parasitica in<br />

Arabidopsis independent <strong>of</strong> SA, JA or ET, through a signaling pathway that requires abscisic adid<br />

(ABA) and involves priming <strong>for</strong> callose deposition,<br />

Mechanisms <strong>of</strong> SAR<br />

A cascade <strong>of</strong> molecular and biochemical events underlies <strong>the</strong> expression <strong>of</strong> SAR. It is<br />

initiated by perception <strong>of</strong> inducers (pathogens, chemicals) resulting in generation <strong>of</strong> signal<br />

molecules translocated at long distance, and switching on <strong>the</strong> diverse processes contributing to<br />

<strong>the</strong> development <strong>of</strong> <strong>the</strong> defense potential <strong>of</strong> plants realized upon secondary inoculation.<br />

Perception <strong>of</strong> inducers is effectuated through binding <strong>of</strong> pathogen-derived molecules (elicitors) or<br />

chemical products with receptor sites on plant membranes or cell walls. Salicylic acid is commonly<br />

recognized as a signal molecule or a prerequisite <strong>for</strong> signal production in SAR. The term “SARgenes”<br />

is used to collectively designate this family <strong>of</strong> nine genes whose expression is correlated<br />

with <strong>the</strong> onset <strong>of</strong> SAR. For TMV-infected tobacco <strong>the</strong> SAR-genes code <strong>for</strong> PR-1 proteins, betaglucanase<br />

(PR-2), chitinase (PR-3), hevein-like protein (PR-4), thaumatin-like and osmotin-like<br />

proteins (PR-5), PR-1 (basic), basic class III chitinase, acidic class III chitinase, and PR-Q’ (Ward<br />

et al., 1991).<br />

Terminology<br />

Because <strong>of</strong> <strong>the</strong> enhanced protection af<strong>for</strong>ded by induction <strong>of</strong> resistance through exposure<br />

to a pathogen, <strong>the</strong> term ‘induced resistance’ has been used synonymously with ‘acquired<br />

resistance’, ‘acquired immunity’ and ‘immunization’. Induced disease resistance has been adopted<br />

as a general term and defined as ‘<strong>the</strong> process <strong>of</strong> active resistance dependent on <strong>the</strong> host plant’s<br />

physical or chemical barriers, activated by biotic or abiotic agents (inducing agents)’ (Kloepper et<br />

al., 1992). Resistance to primary infection can result from <strong>the</strong> presence <strong>of</strong> pre<strong>for</strong>med defensive<br />

barriers, but in inducible resistance mechanisms, <strong>the</strong> infecting pathogen triggering defense<br />

responses through <strong>the</strong> release <strong>of</strong> elicitors which, in turn, lead to <strong>the</strong> expression <strong>of</strong> novel antipathogenic<br />

activities . The resistance is expressed only as a result <strong>of</strong> <strong>the</strong> specific recognition<br />

between plant and pathogen. The term ‘acquired resistance’, advocated by Ross, points to a<br />

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change in <strong>the</strong> physiology <strong>of</strong> <strong>the</strong> plant resulting from an added property. Acquired resistance<br />

obviously is not <strong>the</strong> phenomenon that resistance was not present, but acquired only as a result <strong>of</strong><br />

primary infection.<br />

Association <strong>of</strong> pathogenesis-related proteins with induced resistance<br />

Whereas induction <strong>of</strong> phytoalexins and cell wall rigidification are local reactions,<br />

accumulation <strong>of</strong> pathogenesis-related proteins (PRs) extends into non inoculated plant parts that,<br />

upon challenge, exhibit acquired resistance. PRs have been found to be invariably linked to<br />

necrotizing infections giving rise to SAR, and has been taken as a marker <strong>of</strong> <strong>the</strong> induced state.<br />

Toge<strong>the</strong>r <strong>the</strong> PRs <strong>for</strong>m a set <strong>of</strong> pathogen-induced proteins that may be considered as stress<br />

proteins. PRs may be considered as stress proteins produced in response to, particularly<br />

necrotizing, infections by viruses, viroids, fungi and bacteria, and thought to function in <strong>the</strong><br />

acquired resistance against fur<strong>the</strong>r infection. They accumulate in plant tissues to levels that are<br />

easily detectable on gels by general protein stains. The inducible PRs are mostly acidic proteins<br />

that are secreted into <strong>the</strong> intercellular space <strong>of</strong> <strong>the</strong> leaf. In induced plants <strong>the</strong> accumulated<br />

intercellular proteins <strong>for</strong>m <strong>the</strong> first line <strong>of</strong> defense to a challenging pathogen and, if this fails and<br />

<strong>the</strong> tissue is disrupted, <strong>the</strong> release <strong>of</strong> <strong>the</strong> vacuolar PRs functions as a second line, engulfing <strong>the</strong><br />

pathogen with lytic enzymes (Mauch and Staehelin, 1989).<br />

Systemic signaling by SA<br />

For expressing a HR and developing SAR, SA acts as a signal in <strong>the</strong> induction <strong>of</strong> acquired<br />

resistance. SA is required <strong>for</strong> <strong>the</strong> expression <strong>of</strong> resistance, as well as <strong>for</strong> <strong>the</strong> enhanced defensive<br />

capacity <strong>of</strong> tissues with acquired resistance. Induction <strong>of</strong> acquired resistance and PRs is <strong>of</strong>ten<br />

accomplished by spraying plants with SA solution and assaying <strong>of</strong> <strong>the</strong> sprayed leaves. When SA<br />

was watered on <strong>the</strong> soil, acquired resistance was apparent in upper leaves, indicating that SA was<br />

absorbed by <strong>the</strong> roots and transported throughout <strong>the</strong> plant.<br />

Induction <strong>of</strong> systemic resistance by non-pathogenic micro-organisms<br />

Well-studied biologically-induced disease resistance occurs after root colonization by<br />

selected strains <strong>of</strong> non-pathogenic Pseudomonas spp. This type <strong>of</strong> resistance is generally called<br />

rhizobacteria-induced systemic resistance (Pieterse et al. 1996). The expression <strong>of</strong> rhizobacteriamediated<br />

ISR was shown to be independent <strong>of</strong> <strong>the</strong> presence <strong>of</strong> SA or enhanced PR-gene<br />

expression. Although <strong>the</strong> terms SAR and ISR are synonymous <strong>for</strong> convenience we distinguish<br />

between pathogen- and rhizobacteria-induced resistance by using <strong>the</strong> term SAR <strong>for</strong> <strong>the</strong> pathogeninduced<br />

type and ISR <strong>for</strong> <strong>the</strong> rhizobacteria-induced type <strong>of</strong> resistance.<br />

<strong>Plant</strong>s produce exudates and lysates at <strong>the</strong>ir root surface, where rhizobacteria are<br />

attracted in large numbers. Selected strains <strong>of</strong> non-pathogenic rhizobacteria are named plant<br />

growth-promoting rhizobacteria (PGPR), because <strong>the</strong>y possess <strong>the</strong> capability to stimulate plant<br />

growth. Pseudomonas spp. are among <strong>the</strong> most effective PGPR. They have been shown to be<br />

responsible <strong>for</strong> <strong>the</strong> reduced activity <strong>of</strong> soil-borne pathogens. Apart from such direct antagonistic<br />

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effects on soil-borne pathogens, some PGPR strains are also capable <strong>of</strong> reducing disease<br />

incidence in above-ground plant parts through plant-mediated mechanisms. The enhanced<br />

defensive capacity elicited by Pseudomonas fluorescens CHA0 in tobacco might be fully explained<br />

by <strong>the</strong> bacterial production <strong>of</strong> SA, which could elicit a SAR response.<br />

Combining ISR and SAR to improve biocontrol <strong>of</strong> plant diseases<br />

Detailed knowledge <strong>of</strong> <strong>the</strong> molecular mechanisms underlying induced disease resistance<br />

will be instrumental in developing biologically-based, environmentally-friendly, and durable crop<br />

protection. Simultaneous activation <strong>of</strong> ISR and SAR may confer differential protection against<br />

different types <strong>of</strong> pathogens (Ton et al. 2002). Thus, combining both types <strong>of</strong> induced resistance<br />

can protect <strong>the</strong> plant against a complementary spectrum <strong>of</strong> pathogens, and can even result in an<br />

additive level <strong>of</strong> induced protection against pathogens that are resisted through both <strong>the</strong> JA/ETand<br />

<strong>the</strong> SA- dependent pathways.<br />

Fig. 1. (a) Systemic acquired resistance, induced by <strong>the</strong> exposure <strong>of</strong> root or foliar tissues to abiotic or biotic<br />

elicitors, is dependent <strong>of</strong> <strong>the</strong> phytohormone salicylate (salicylic acid), and associated with <strong>the</strong><br />

accumulation <strong>of</strong> pathogenesis-related (PR) proteins.<br />

(b)Induced systemic resistance, induced by <strong>the</strong> exposure <strong>of</strong> roots to specific strains <strong>of</strong> plant growthpromoting<br />

rhizobacteria, is dependent <strong>of</strong> <strong>the</strong> phytohormones ethylene and jasmonate (jasmonic<br />

acid), independent <strong>of</strong> salicylate, and is not associated with <strong>the</strong> accumulation <strong>of</strong> PR proteins (or<br />

transcripts).<br />

Molecular basis <strong>of</strong> resistance<br />

The advent <strong>of</strong> molecular biology has enabled <strong>the</strong> genes that confer disease resistance to<br />

be analyzed at a molecular level. The majority <strong>of</strong> isolated cereal R genes encode proteins<br />

containing a central domain with a nucleotide binding site (NBS), which binds ei<strong>the</strong>r ATP or GTP,<br />

and a carboxyterminal domain consisting <strong>of</strong> a series <strong>of</strong> degenerate leucine-rich repeat residues<br />

(LRR). These so-called NBS-LRR genes are a super family <strong>of</strong> R genes present in both<br />

monocotyledonous and dicotyledonous species. NBS-LRR proteins have been shown to provide<br />

plant recognition <strong>of</strong> fungal and bacterial pathogens in cereals, but <strong>the</strong>y also recognize viral,<br />

nematode and insect species that parasitize dicotyledonous plants. How R genes recognize<br />

pathogen avirulence products at a molecular level? This recognition process can be envisaged as<br />

a specific receptor– ligand interaction that subsequently leads to activation <strong>of</strong> a defence response.<br />

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Lack <strong>of</strong> interaction suggests ei<strong>the</strong>r indirect recognition <strong>of</strong> <strong>the</strong>se avirulence products by R proteins,<br />

or alternatively <strong>the</strong>se R proteins recognize avirulence product/host protein complexes, a concept<br />

termed ‘<strong>the</strong> guard hypo<strong>the</strong>sis’ (Bogdanove, 2002). Research has focused on <strong>the</strong> elicitor molecules<br />

released during <strong>the</strong> early stages <strong>of</strong> <strong>the</strong> plant–pathogen interaction, and on <strong>the</strong> signaling pathways<br />

used to trigger defenses locally and systemically. The elicitors examined include carbohydrate<br />

polymers, lipids, and glycoproteins, and are ei<strong>the</strong>r secreted by microorganisms or derived from <strong>the</strong><br />

cell walls <strong>of</strong> fungi, bacteria, or plants.<br />

Signal transduction in SAR<br />

Systemic acquired resistance (SAR) refers to a distinct signal transduction pathway that<br />

plays an important role in <strong>the</strong> ability <strong>of</strong> plants to defend <strong>the</strong>mselves against pathogens. After <strong>the</strong><br />

<strong>for</strong>mation <strong>of</strong> a necrotic lesion, ei<strong>the</strong>r as a part <strong>of</strong> <strong>the</strong> hypersensitive response (HR) or as a<br />

symptom <strong>of</strong> disease, <strong>the</strong> SAR pathway is activated. SAR activation results in <strong>the</strong> development <strong>of</strong> a<br />

broad-spectrum, systemic resistance. SAR can be distinguished from o<strong>the</strong>r disease resistance<br />

responses by both <strong>the</strong> spectrum <strong>of</strong> pathogen protection and <strong>the</strong> associated changes in gene<br />

expression. Associated with SAR is <strong>the</strong> expression <strong>of</strong> a set <strong>of</strong> genes called SAR genes. When<br />

SAR is activated, a normally compatible plant-pathogen interaction (i.e., one in which disease is<br />

<strong>the</strong> normal outcome) can be converted into an incompatible one. Conversely, when <strong>the</strong> SAR<br />

pathway is incapacitated, a normally incompatible interaction becomes compatible. A number <strong>of</strong><br />

biochemical and physiological changes have been associated with pathogen infection. These<br />

include cell death and <strong>the</strong> oxidative burst, deposition <strong>of</strong> callose and lignin, syn<strong>the</strong>sis <strong>of</strong><br />

phytoalexins and novel proteins. A protein is classified as a SAR protein when its presence or<br />

activity correlates tightly with maintenance <strong>of</strong> <strong>the</strong> resistance state. Analysis <strong>of</strong> SAR proteins<br />

showed that many belong to <strong>the</strong> class <strong>of</strong> pathogenesis-related (PR) proteins, which originally were<br />

identified as novel proteins accumulating after TMV infection <strong>of</strong> tobacco leaves.<br />

SA plays a key role in both SAR signaling and disease resistance. The leve1 <strong>of</strong> SA was<br />

found to increase by severa1 hundred-fold in tobacco or cucumber after pathogen infection, and<br />

this increase was shown to correlate with SAR. The increased in concentration <strong>of</strong> SA and <strong>the</strong><br />

establishment <strong>of</strong> enhanced disease resistance has been observed not only in tobacco and<br />

cucumber but in o<strong>the</strong>r plants as well.<br />

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Signal transduction occurs when an extracellular signaling molecule activates a cell surface<br />

receptor. In turn, this receptor alters intracellular molecules creating a response. There are two<br />

stages in this process. A signaling molecule activates a specific receptor protein on <strong>the</strong> cell<br />

membrane. A second messenger transmits <strong>the</strong> signal into <strong>the</strong> cell, eliciting a physiological<br />

response. Signal transduction involves <strong>the</strong> binding <strong>of</strong> extracellular signalling<br />

molecules and ligands to cell-surface receptors that trigger events inside <strong>the</strong> cell. The combination<br />

<strong>of</strong> messenger with receptor causes a change in <strong>the</strong> con<strong>for</strong>mation <strong>of</strong> <strong>the</strong> receptor, known<br />

as receptor activation. Intracellular signaling cascades can be started through cell-substratum<br />

interactions; examples are <strong>the</strong> integrin that binds ligands in <strong>the</strong> extracellular matrix and steroids.<br />

Most steroid hormones have receptors within <strong>the</strong> cytoplasm and act by stimulating <strong>the</strong> binding <strong>of</strong><br />

<strong>the</strong>ir receptors to <strong>the</strong> promoter region <strong>of</strong> steroid-responsive genes.<br />

Role <strong>of</strong> SA as translocated signal<br />

Pathogen infection results in significant amounts <strong>of</strong> SA in <strong>the</strong> phloem sap <strong>of</strong> both cucumber<br />

and tobacco. Additionally, in-vivo SA-labeling studies provide evidence that SA produced in <strong>the</strong><br />

leaves <strong>of</strong> TMV-infected tobacco or TNV-infected cucumber is transported throughout <strong>the</strong> plant and<br />

accumulates in uninfected tissues. In fact, as much as 70% (tobacco) and 50% (cucumber) <strong>of</strong> <strong>the</strong><br />

increase in SA in uninfected tissue <strong>of</strong> pathogen-inoculated plants results from SA translocation from<br />

infected leaves to uninfected leaves. Two lines <strong>of</strong> evidence however suggest that SA is not <strong>the</strong> long<br />

distance signal. First, in cucumber, primary leaves infected with P. syringae can be removed 6 hrs<br />

after inoculation, which is be<strong>for</strong>e SA accumulates in <strong>the</strong> phloem, without affecting <strong>the</strong> systemic<br />

increase <strong>of</strong> SA or SAR gene expression (Rasmussen et al., 1991). In grafted tobacco plants, TMV<br />

inoculation <strong>of</strong> NahG rootstocks resulted in very little SA accumulation in infected tissue, compared<br />

with a 185-fold increase <strong>for</strong> wild-type (Xanthi) plant. These results suggest that ei<strong>the</strong>r SA is not <strong>the</strong><br />

long distance signal or very small amounts <strong>of</strong> SA in infected leaves are sufficient <strong>for</strong> full SAR<br />

induction. Even though SA is not likely to be <strong>the</strong> translocated signal that triggers SAR in dista1 plant<br />

organs, it is essential <strong>for</strong> SAR signal transduction. These findings indicate that SA is an essential<br />

signal in SAR and that it is required downstream <strong>of</strong> <strong>the</strong> long distance signal.<br />

Modes <strong>of</strong> action <strong>of</strong> SA<br />

It has been proposed that H 2 0 2 acts as a second messenger <strong>of</strong> SA in SAR signaling. A SA<br />

binding protein was identified as catalase; SA was found to inhibit <strong>the</strong> catalase activity <strong>of</strong> this<br />

protein, leading to elevated levels <strong>of</strong> H 2 0 2 . Fur<strong>the</strong>rmore, H 2 0 2 was found to cause induction <strong>of</strong> PR-<br />

1 gene expression and was postulated to induce SAR (Chen et al., 1993, 1995).<br />

Recent reports, however, indicate that <strong>for</strong> H 2 0 2 to function as a signaling agent <strong>of</strong> SA, H 2 0 2<br />

levels should increase in uninfected leaves <strong>of</strong> tobacco plants during SAR activation. In <strong>the</strong><br />

uninfected leaves <strong>of</strong> inoculated plants, SAR gene expression and <strong>the</strong> establishment <strong>of</strong> SAR did<br />

not correlate with an increase in H 2 0 2 levels. More recent reports fur<strong>the</strong>r suggest that very high<br />

levels <strong>of</strong> SA (1 mM) inhibit <strong>the</strong> in-vitro activity <strong>of</strong> a variety <strong>of</strong> heme-iron-containing enzymes,<br />

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including catalase. In infected leaves, high concentrations <strong>of</strong> SA around <strong>the</strong> site <strong>of</strong> infection may<br />

inhibit catalase and o<strong>the</strong>r oxidoreductases. lnhibition <strong>of</strong> catalase activity could prolong <strong>the</strong> half-life<br />

<strong>of</strong> H 2 0 2 and lead to an amplification <strong>of</strong> <strong>the</strong> oxidative burst. The oxidative burst may trigger a variety<br />

<strong>of</strong> local defense responses including programmed cell death during <strong>the</strong> HR as well as defense<br />

gene expression and syn<strong>the</strong>sis <strong>of</strong> SA in adjacent cells. This would create a runaway cycle leading<br />

to high levels <strong>of</strong> both SA and H 2 0 2 at <strong>the</strong> site <strong>of</strong> pathogen attack.<br />

Chemical activators <strong>of</strong> SAR<br />

SAR was first described as a response to pathogen infection. Subsequently, it has been<br />

found that treatment <strong>of</strong> plants with low molecular weight molecules can also induce SAR. The use<br />

<strong>of</strong> chemicals to activate SAR provides nove1 alternatives <strong>for</strong> disease control in agronomic systems<br />

as well as tools <strong>for</strong> <strong>the</strong> elucidation <strong>of</strong> <strong>the</strong> SAR signal transduction cascade. To be considered an<br />

activator <strong>of</strong> SAR, a chemical should exhibit three characteristics first, <strong>the</strong> compound or its<br />

significant metabolites should not exhibit direct antimicrobial activity; second, it should induce<br />

resistance against <strong>the</strong> same spectrum <strong>of</strong> pathogens as in biologically activated SAR; and third, it<br />

should induce <strong>the</strong> expression <strong>of</strong> <strong>the</strong> same marker genes as evident in pathogen-activated SAR.<br />

Severa1 chemicals or extracts, including silicon, phosphate, 2-thiouracil, polyacrylic acid, nucleic<br />

acids, and fosethyl Al, have been reported as potential activators <strong>of</strong> resistance but have failed to<br />

fulfill <strong>the</strong> above criteria (Kessmann et al., 1994). O<strong>the</strong>r compounds, such as DL-8 aminobutanoic<br />

acid or probenazole, have been shown to slightly induce ei<strong>the</strong>r PR-1 gene expression or<br />

resistance against one or two pathogens, but activation <strong>of</strong> bona fide SAR has not been<br />

demonstrated. To date, SA is <strong>the</strong> only plant-derived substance that has been demonstrated to be<br />

an inducer <strong>of</strong> SAR. The chemicals 2, 6- dichloroisonicotinic acid and its methyl ester (both referred<br />

to as INA) were <strong>the</strong> first syn<strong>the</strong>tic compounds shown to activate SAR, thus, providing broadspectrum<br />

disease resistance. Recently, <strong>the</strong> syn<strong>the</strong>tic chemical benzo (l,2,3) thiadiazole-7-<br />

carbothioic acid S-methyl ester (BTH) was demonstrated to be a potent SAR activator.<br />

Mechanisms <strong>of</strong> mycorrhiza-induced resistance<br />

<strong>Plant</strong>s have established a mutualistic association known as arbuscular mycorrhizas (AM)<br />

with certain soil fungi. Arbuscular mycorrhiza <strong>for</strong>ming fungi (AMF) are obligate biotrophs because<br />

<strong>the</strong>y rely on <strong>the</strong>ir host plant to proliferate and survive. AM deal with <strong>the</strong> reduction <strong>of</strong> incidence<br />

and/or severity <strong>of</strong> soil-borne diseases mainly root rot or wilting caused by fungi such as<br />

Rhizoctonia, Fusarium, or Verticillium, and root rot caused by oomycetes including Phytophthora,<br />

Pythium, and Aphanomyces. A reduction in <strong>the</strong> deleterious effects by parasitic nematodes such as<br />

Pratylenchus and Meloidogyne has also been reported<br />

Different mechanisms operative simultaneously, have been shown to play a role in plant<br />

protection by AMF, namely, improved plant nutrition, damage compensation, competition <strong>for</strong><br />

colonization sites photosynthates, changes in <strong>the</strong> root system, changes in rhizosphere microbial<br />

populations and activation <strong>of</strong> plant defense mechanisms. There is evidence <strong>for</strong> <strong>the</strong> accumulation<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>of</strong> defensive plant compounds related to mycorrhization, although to a much lower extent than in<br />

plant–pathogen interactions.<br />

The identification <strong>of</strong> strigolactones, known to stimulate seed germination <strong>of</strong> parasitic plants,<br />

as host recognition compounds <strong>for</strong> AMF has uncovered a possible mechanism mediating <strong>the</strong><br />

protector effect <strong>of</strong> AM against parasitic plants. Mycorrhizal plants by exudating lower amounts <strong>of</strong><br />

strigolactones are unfavorable to parasitic plant seed germination. Salicylic acid (SA) co-ordinates<br />

defense mechanisms that are generally effective against biotrophic pathogens, whereas<br />

jasmonates (JA) regulate wounding responses and resistance against necrotrophs. As obligate<br />

biotrophs, AMF share similarities with biotrophic pathogens. Thus, <strong>the</strong>ir sensitivity to SA-regulated<br />

defenses is likely. Indeed, exogenous SA application delays mycorrhizal colonization.<br />

Fig 3. (a)Upon attacker recognition, <strong>the</strong> plant produces <strong>the</strong> defense-related signals JA, ET, and<br />

SA in different proportions.(b) Mycorrhiza <strong>for</strong>mation primes <strong>the</strong> tissues <strong>for</strong> a quicker and<br />

more effective activation <strong>of</strong> JA-dependent defense responses upon attack,<br />

Factors influencing <strong>the</strong> expression <strong>of</strong> induced resistance<br />

Effects <strong>of</strong> genotype<br />

In monocots, resistance activated is very long lasting, whereas <strong>the</strong> lasting effect is less<br />

pronounced in dicots. Reduction in powdery mildew on barley following treatment with culture<br />

filtrate <strong>of</strong> B. subtilis was cultivar specific and was most marked in partially resistant cultivars.<br />

Extent <strong>of</strong> induced resistance was most effective in lines with <strong>the</strong> Mla7 gene and least effective in<br />

lines with <strong>the</strong> Mla13 gene.<br />

Environmental effects<br />

Exposure to abiotic stress can influence plant resistance to pathogens. Ayres (1984),<br />

proposed two possible reasons <strong>for</strong> this phenomenon. The first is <strong>the</strong> possibility that <strong>the</strong> negative<br />

effects <strong>of</strong> pathogens and abiotic stress might be additive and second possibility is that abiotic<br />

stress might alter plant resistance to pathogen infection, leading to enhanced resistance. Water<br />

stress has been reported to increase susceptibility to foliar pathogens also has been shown to<br />

enhance resistance to powdery mildew in older leaves <strong>of</strong> barley, grown in dry soil. Appropriate<br />

timing and frequency <strong>of</strong> application, use in conjunction with appropriate-dose <strong>of</strong> fungicides,<br />

combinations <strong>of</strong> agents that induce resistance with fungicides or biological control agents, has<br />

been shown to provide effective disease control.<br />

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REFERENCES<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Ayres, PG (1984). The interaction between environmental stress injury and abiotic disease<br />

physiology. Annu. Rev. Phytopathol. 22:53-75.<br />

• Beauverie J (1901). Essais d’immunisation des végétaux contre les maladies cryptogamiques. CR<br />

Acad Sci Paris. 133: 107-110, 1901.<br />

• Bogdanove AJ. (2002). Protein-protein interactions in pathogen recognition by plants. <strong>Plant</strong><br />

Molecular Biology 50: 981–989.<br />

• Chen, Z, Silva, H, and Klessig, DF (1993). lnvolvement <strong>of</strong> reactive oxygen species in <strong>the</strong><br />

induction <strong>of</strong> systemic acquired resistance by salicylic acid in plants. Science 242:<br />

883-886.<br />

• Chen, ZX, Malamy, J, Henning, J, Conrath, U, Sanchezcasas, P, Silva, H, Ricigllano, J, and<br />

Klessig, DF (1995). Induction, modification, and transduction <strong>of</strong> <strong>the</strong> salicylic acid<br />

signal in plant defense responses. Proc. Natl. Acad. Sci. USA 92: 4134-4137.<br />

• Kessmann, H, Staub, T, H<strong>of</strong>mann, C, Maetzke, T, Herzog, J, Ward, E., Uknes, S., and Ryals, J<br />

(1994). lnduction <strong>of</strong> systemic acquired resistance in plants by chemicals. Annu.<br />

Rev. Phytopathol 32:439-459.<br />

• Kloepper JW, Tuzun S and Kuc JA(1992) Proposed definitions related to induced disease<br />

resistance. Biocontrol Science and Technology 2: 349–351<br />

• Mauch F and Staehelin LA (1989) Functional implications <strong>of</strong> <strong>the</strong> subcellular localization <strong>of</strong><br />

ethylene-induced chitinase and β 1,3-glucanase in bean leaves. The <strong>Plant</strong> Cell 1:<br />

447–457<br />

• Pieterse CMJ, Van Wees SCM, H<strong>of</strong>fland E, Van Pelt JA and Van Loon LC (1996) Systemic<br />

resistance in Arabidopsis induced by biocontrol bacteria is independent <strong>of</strong> salicylic<br />

acid accumulation and pathogenesis-related gene expression. The <strong>Plant</strong> Cell 8:<br />

1225–1237<br />

• Pieterse CMJ, Van Wees SCM, Van Pelt JA, Knoester M, Laan R, Gerrits H, Weisbeek PJ, Van<br />

Loon LC (1998) A novel signaling pathway controlling induced systemic resistance<br />

in Arabidopsis. The <strong>Plant</strong> Cell 10, 1571-1580<br />

• Ray J (1901). Les maladies cryptogamiques des végétaux. Rev Gen Bot. 13: 145-151.<br />

• Ross AF (1961a) Localized acquired resistance to plant virus infection in hypersensitive hosts.<br />

Virology. 14: 329-339<br />

• Ross AF (1961b). Systemic acquired resistance induced by localized virus infection in plants.<br />

Virology. 14: 340-358<br />

• Rasmussen JB, Hammerschmidt R and Zook MN (1991) Systemic induction <strong>of</strong> salicylic acid<br />

accumulation in cucumber after inoculation with Pseudomonas syringae pv.<br />

syringae. <strong>Plant</strong> Physiology 97: 1342–1347<br />

• Ton J, Van Pelt JA, Van Loon LC, Pieterse CMJ (2002). Differential effectiveness <strong>of</strong> salicylatedependent<br />

and jasmonate/ethylene-dependent induced resistance in Arabidopsis.<br />

Molecular <strong>Plant</strong>-<strong>Microbe</strong> <strong>Interactions</strong> 15, 27-34<br />

• Van Loon LC, Bakker PAHM, Pieterse CM. (1998) Systemic resistance induced by rhizosphere<br />

bacteria. Ann Rev Phytopathol. 36: 453-458<br />

• Ward ER, Uknes SJ, Williams SC, Dincher SS, Wiederhold DL, Alexander DC, Ahl-Goy P,<br />

Métraux J-P, Ryals JA (1991) Coordinate gene activity in response to agents that<br />

induce systemic acquired resistance. The <strong>Plant</strong> Cell 3: 1085-1094<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Characterization <strong>of</strong> Macro- and Meteorological Variables <strong>for</strong> Disease<br />

<strong>Management</strong><br />

Introduction<br />

H.S. Kushwaha<br />

Department <strong>of</strong> <strong>Soil</strong> Science, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Initiation and progress <strong>of</strong> plant diseases is <strong>the</strong> outcome <strong>of</strong> interaction <strong>of</strong><br />

four vital<br />

elements viz. Host (susceptibility), Pathogen (Virulence), Environment (Favourable) and time<br />

(Duration <strong>of</strong> interaction). These four elements <strong>for</strong>m <strong>the</strong> " Disease Pyramid " and if <strong>the</strong>se arms<br />

representing four elements can be measured / quantified, <strong>the</strong> volume <strong>of</strong> Pyramid will be a<br />

measure <strong>of</strong> disease produced. All <strong>the</strong>se four elements are vital, but <strong>the</strong> role <strong>of</strong> environment<br />

become more important as it influences both host as well as <strong>the</strong> Pathogen. The severity and<br />

<strong>the</strong> extent <strong>of</strong> this interaction is markedly affected by <strong>the</strong> environment and <strong>the</strong> element <strong>of</strong> time. Not<br />

only <strong>the</strong> growth <strong>of</strong> <strong>the</strong> host is affected by environmental factors like air temperature, leaf<br />

temperature,<br />

relative humidity, wind, precipitation, duration <strong>of</strong> leaf wetness, intensity and<br />

duration <strong>of</strong> radiation, but also <strong>the</strong>y have pr<strong>of</strong>ound influence on Pathogen and disease<br />

development. The amount <strong>of</strong> primary inoculums present is important <strong>for</strong> subsequent disease<br />

development. The climatic conditions significantly influence dormancy <strong>of</strong> plant pathogens and<br />

<strong>the</strong>re<strong>for</strong>e, <strong>the</strong> plant inoculums, when growth commences. Apart from <strong>the</strong> biological factors, <strong>the</strong><br />

micro-meteorological factors such as duration <strong>of</strong> leaf wetness, duration and intensity <strong>of</strong> rain,<br />

wind speed and its direction within and above <strong>the</strong> crop canopy play a very important role in<br />

release and dispersal <strong>of</strong> <strong>the</strong> pathogens.<br />

The plant surface is linked to <strong>the</strong> environment through <strong>the</strong> flow <strong>of</strong> energy between <strong>the</strong>m.<br />

Humidity conditions and specially dew affects <strong>the</strong> growth and development <strong>of</strong> many phytopathogens,<br />

especially <strong>the</strong> fungal organisms. The temperature <strong>of</strong> <strong>the</strong> surface is <strong>the</strong> equilibrium<br />

temperature at which <strong>the</strong> sensible and latent heat fluxes from <strong>the</strong> surface equal <strong>the</strong> net gain by<br />

radiation. Leaf temperature is, <strong>the</strong>re<strong>for</strong>e, sensitive to any changes or differnces in <strong>the</strong> levels <strong>of</strong><br />

exchange. Each leaf or part <strong>of</strong> a leaf has its own equlibrium level and in this way has a unique<br />

microclimate responsible <strong>for</strong> disease outbreaks.<br />

Environment is a complex phenomenon having both biotic as well as abiotic<br />

components. We study <strong>the</strong> physical parameters as wea<strong>the</strong>r. Wea<strong>the</strong>r can be defined as physical<br />

state <strong>of</strong> atmosphere at a particular location at a given time and it is highly dynamic phenomenon.<br />

On <strong>the</strong> o<strong>the</strong>r hand <strong>the</strong> climate is defined as average / aggregate wea<strong>the</strong>r conditions <strong>of</strong> a locality.<br />

The process <strong>of</strong> disease development is greatly influenced by <strong>the</strong> wea<strong>the</strong>r changes in <strong>the</strong> close<br />

vicinity <strong>of</strong> Host-Pathogen interaction. Thus a measurement <strong>of</strong> microclimatic parameters gives real<br />

insight in <strong>the</strong> Host - Pathogen interaction and it is <strong>the</strong> outcome (i.e. The <strong>Plant</strong> Disease).<br />

2. Macro- and Micro-meteorological variables and brief description <strong>of</strong> <strong>the</strong>ir measurement<br />

The major macro and micrometeorological variables which are important from <strong>the</strong> point <strong>of</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

view <strong>of</strong> disease development are maximum and minimum air temperatures; relative humidity; wind<br />

speed and its direction; precipitation; intensity and duration <strong>of</strong> solar radiation; duration <strong>of</strong> leaf<br />

wetness. It is also important to distinguish between macroclimate (meteorological screen) and<br />

microclimate (climate at or very near to <strong>the</strong> host surface, canopy). Microclimate affects growth and<br />

development <strong>of</strong> diseases to <strong>the</strong> extent to which it causes changes in <strong>the</strong> microclimate. Rain is a<br />

macroclimatic factor and <strong>the</strong> continuous drizzle or occurrence <strong>of</strong> dry and wet spells influence some<br />

diseases. Dew is a microclimatic factor and when <strong>the</strong> relative humidity increases above 70 %<br />

condensation begins on plants. Microclimatic factors influence plant diseases more than<br />

macroclimatic factors.<br />

Keeping in view <strong>the</strong> importance <strong>of</strong> meteorological variables, it is essential to measure <strong>the</strong>m<br />

accurately by correct meteorological instruments. In <strong>the</strong> present lecture ef<strong>for</strong>ts have been made to<br />

explain in brief <strong>the</strong> ways and means <strong>of</strong> measurement <strong>of</strong> important meteorological wea<strong>the</strong>r<br />

variables especially in <strong>the</strong> meteorological observatory which are situated almost in all <strong>the</strong> State<br />

Agricultural Universities / ICAR Agricultural Research Institutes all over <strong>the</strong> country. However, <strong>the</strong><br />

micrometeorological wea<strong>the</strong>r variables are monitored by Automatic Wea<strong>the</strong>r Stations which are<br />

being installed in <strong>the</strong> cropped fields <strong>for</strong> specific research purpose.<br />

A) Measurement <strong>of</strong> Macro- meteorological variables<br />

A brief account <strong>of</strong> method <strong>of</strong> measurement <strong>of</strong> major macrometeorological variables along with <strong>the</strong><br />

instruments used in <strong>the</strong> meteorological observatory <strong>for</strong> this purpose is given below:<br />

A plain area <strong>of</strong> 55 m (N-W) x 36 m (E-W) size with short cut grasses provides a good<br />

exposure <strong>for</strong> all <strong>the</strong> meteorological instruments in <strong>the</strong> observatory. If a person stands at <strong>the</strong> gate<br />

facing <strong>the</strong> observatory plot, he will find <strong>the</strong> tall instruments in <strong>the</strong> back row and shorter instruments<br />

in <strong>the</strong> front rows. In general <strong>the</strong> instruments are separated at a distance <strong>of</strong> 9 m from each within<br />

rows <strong>of</strong> 12 m apart. The method <strong>of</strong> measurement <strong>of</strong> <strong>the</strong> important meteorological variables is<br />

described under <strong>the</strong> following sub-heads:-<br />

1. Maximum and Minimum Temperatures<br />

The maximum and minimum air temperatures ( o C) are measured by maximum and<br />

minimum <strong>the</strong>rmometers, respectively. They are housed in a single stevension in approximate<br />

horizontal position at about 4 feet height from <strong>the</strong> ground. The screen is errected on 4 wooden<br />

posts supplied with <strong>the</strong> screen with its door opening to <strong>the</strong> north and <strong>the</strong> bottom at 4 feet<br />

approximately above <strong>the</strong> ground level.<br />

2. Relative Humidity<br />

The relative humidity (%) is measured indirecely by <strong>the</strong> readings <strong>of</strong> dry and wet bulb<br />

temperatures. The dry and wet bulb temperatures are measured by dry and wet bulb<br />

<strong>the</strong>rmometers wich are placed in <strong>the</strong> above Stevenson screen perfectly in <strong>the</strong> vertical positions.<br />

The height <strong>of</strong> <strong>the</strong> bulbs <strong>of</strong> dry and wet <strong>the</strong>rmometers should be from 4' 3" to 4' 6" above <strong>the</strong><br />

ground, respectively <strong>for</strong> correct measurements. From <strong>the</strong> readings <strong>of</strong> dry and wet bulb<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

temperatures <strong>the</strong> relative humidity is computed using Hygrometric Tables prepared by India<br />

Meteorological Department (IMD), Pune, based on <strong>the</strong> values <strong>of</strong> Atmospheric Pressure <strong>of</strong> <strong>the</strong><br />

observatory locations throught <strong>the</strong> Country. At Pantnagar <strong>the</strong> Hygrometric Table <strong>of</strong> 1000 mb is<br />

used.<br />

3. <strong>Soil</strong> Temperature:<br />

The soil temperatures ( o C) in <strong>the</strong> observatory are measured by specially designed <strong>Soil</strong><br />

Thermometers at 5, 10 and 15 cm soil depths. The plot where <strong>the</strong>se <strong>the</strong>rmometers are exposed<br />

should not receive any shadow from <strong>the</strong> neighboring instruments or objects. The bulbs should be<br />

at a vertical depth <strong>of</strong> 5 cm, 10 cm and 20 cm below <strong>the</strong> soil surface and <strong>the</strong> slant <strong>of</strong> <strong>the</strong> stem <strong>of</strong> <strong>the</strong><br />

<strong>the</strong>rmometer should be towards north, i.e. <strong>the</strong> observer should be able to read <strong>the</strong> instruments by<br />

sitting to <strong>the</strong> south <strong>of</strong> <strong>the</strong> instruments.<br />

4. Rainfall<br />

The rainfall is measured by Raingauge. The ordinary raingauge is errected on a masonry<br />

or concrete foundation <strong>of</strong> 3'x 3'x 3' size and sunk into <strong>the</strong> ground. Into this foundation <strong>the</strong> base <strong>of</strong><br />

<strong>the</strong> gauge is cemented so that <strong>the</strong> rim <strong>of</strong> <strong>the</strong> raingauge is exactly one foot above <strong>the</strong> ground level<br />

and 10" above <strong>the</strong> concrete structure, i.e. <strong>the</strong> concret structure will project 2" above <strong>the</strong> ground<br />

surface. While getting <strong>the</strong> gauge, great care is taken to ensure that <strong>the</strong> rim is perfectly level.<br />

5. Bright Sunshine Hours<br />

The recording <strong>of</strong> <strong>the</strong> number <strong>of</strong> bright sunshine hours (hrs) is done by Campbell Stoke's<br />

type Sunshine Recorder. This instrument is exposed on <strong>the</strong> terrace <strong>of</strong> <strong>the</strong> ro<strong>of</strong> or on a pillar in <strong>the</strong><br />

'open' where <strong>the</strong> horizon is clearly visible between North - East and South - East on <strong>the</strong> Eastern<br />

side and between North - West and South - West on <strong>the</strong> Western side. The instrument is placed<br />

on a solid masonry pillar <strong>of</strong> any suitable height <strong>of</strong> 5' or 10' above ground depending upon <strong>the</strong><br />

exposure on eastern and western sides and rigidly fixed to it after proper adjustment is made. The<br />

number <strong>of</strong> burns on <strong>the</strong> sunshine cards are counted to compute <strong>the</strong> duration <strong>of</strong> bright sunshine<br />

hours (hrs) in a day on daily basis. However, no burning on cards takes place on cloudy days.<br />

6. Solar Radiation<br />

The quantity and intensity <strong>of</strong> solar radiation is measured by Pyranometer. This instrument is<br />

placed in <strong>the</strong> same way as <strong>the</strong> sunshine recorder. The output in terms <strong>of</strong> solar radiation is<br />

expressed in W/m2 or Cal./cm2/day units.<br />

7. Wind Speed and Wind Direction:<br />

Wind speed (km/hr) is measured by Anemometer while its direction (in terms <strong>of</strong> Compass<br />

points) is measured by Wind vane. These wind instruments are errected at a height <strong>of</strong> 10 feet from<br />

<strong>the</strong> ground on wooden posts. The site <strong>for</strong> <strong>the</strong>se instruments must be as open as possible and<br />

<strong>the</strong>re must not be any object l<strong>of</strong>tier than <strong>the</strong> instrument <strong>for</strong> a long distance (as far as possible)<br />

around. Long trees and building in <strong>the</strong> neighborhood are always objectionable. Even if <strong>the</strong>re are<br />

not l<strong>of</strong>ty enough to screen <strong>the</strong> instruments, <strong>the</strong>y serve to cause eddies or swirls which act on <strong>the</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

windvane from a direction different from that <strong>of</strong> a general air current in <strong>the</strong> neighborhood.<br />

Such obstructions do not also allow winds from all directions to strike <strong>the</strong> anemometer cups with<br />

equal <strong>for</strong>ce. The standard exposure <strong>of</strong> wind instruments over open level ground in <strong>the</strong> observatory<br />

plot should be 10 ft. above <strong>the</strong> ground. The distance between <strong>the</strong> wind instruments and any<br />

obstruction should be at least 10 times <strong>the</strong> height <strong>of</strong> <strong>the</strong> obstruction.<br />

8. Dew<br />

Dew (mm) is measured by Dew Gauges which are exposed at four heights on a stand and<br />

<strong>the</strong> appearence <strong>of</strong> dew drops is compared with <strong>the</strong> standard photographs to quantify <strong>the</strong> dew in<br />

terms <strong>of</strong> mm <strong>of</strong> dew fall on daily basis.<br />

9. Continuous Recording <strong>of</strong> wea<strong>the</strong>r variables:<br />

i). Air Temperature:<br />

The continuous recording <strong>of</strong> air temperature ( o C) is done by <strong>the</strong> Thermograph or<br />

Thermohygrograph. The recording is done on a daily or week chart depending upon <strong>the</strong> clock<br />

drum. They are placed in <strong>the</strong> observatory area inside <strong>the</strong> double Stevenson screen. In <strong>the</strong> same<br />

screen, a standard <strong>the</strong>rmometer is also placed <strong>for</strong> comparison with its bulb at <strong>the</strong> level <strong>of</strong> <strong>the</strong><br />

<strong>the</strong>rmal element and at a horizontal distance <strong>of</strong> about 5" from it. They are also installed in <strong>the</strong><br />

laboratory <strong>for</strong> recording <strong>of</strong> room temperature.<br />

ii). Relative Humidity:<br />

The continuous recording <strong>of</strong> <strong>the</strong> relative humidity (%) <strong>of</strong> free air in <strong>the</strong> observatory is done<br />

by Hair Hygrograph or Thermohygrograph. The recording is done on a daily or week chart<br />

depending upon <strong>the</strong> clock drum. They are exposed in <strong>the</strong> observatory in <strong>the</strong> same above double<br />

Stevenson screen. The Stevenson screen should be located in a place where <strong>the</strong> surrounding air<br />

is not polluted by excessive smoke or dust particles or is surcharged with brine or oil vapour, since<br />

<strong>the</strong>se instruments have a deleterious effect upon <strong>the</strong> hygroscopic properties <strong>of</strong> <strong>the</strong> hair. They are<br />

also installed in <strong>the</strong> laboratory <strong>for</strong> recording <strong>of</strong> room temperature.<br />

iii). Rainfall<br />

Continuous recording <strong>of</strong> rainfall in <strong>the</strong> observatory is done by Self Recording Rain Gauge<br />

on Chart attached with a clock drum. The recording is done on a daily or week chart depending<br />

upon <strong>the</strong> clock drum.<br />

The standard meteorological week average distribution <strong>of</strong> major wea<strong>the</strong>r variables<br />

recorded during 2012 at Meteorological Observatory situated at Pantnagar is given in Fig.1.<br />

B. Measurement <strong>of</strong> Micro-meteorological variables<br />

The measurement <strong>of</strong> micrometeorological wea<strong>the</strong>r variables in <strong>the</strong> country or <strong>the</strong> World is<br />

done through Automatic Wea<strong>the</strong>r Stations (AWS). These AWS are installed in <strong>the</strong> open fields or<br />

within cropped fields to monitor <strong>the</strong> micro-meteorological conditions <strong>of</strong> crops. The automatic<br />

wea<strong>the</strong>r station is composed with various micro-meteorological instruments <strong>for</strong> monitoring <strong>of</strong><br />

micrometeorological wea<strong>the</strong>r variables such as Air temperature ( o C), Relative humidity (%), Wind<br />

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speed (m/s), Wind direction (degrees from North), Leaf temperature ( o C), Leaf wetness (% <strong>of</strong><br />

total wet), Solar radiation (W m- 2 ), Net radiation (W m- 2 ), Rainfall (mm) and <strong>Soil</strong> temperature ( o C)<br />

etc. A sketch <strong>of</strong> AWS is given in Fig.2. The main and important features <strong>of</strong> <strong>the</strong> system are<br />

described as below:<br />

1. Wide range <strong>of</strong> sensors: A maximum <strong>of</strong> 20 sensors can be a attached to this at a time.<br />

2. Flexible data storage: It has Internal memory to store 19, 200 data points i.e. hourly data<br />

<strong>for</strong> continuous 40 days at a time can be stored.<br />

3. Versatile data transfer: S<strong>of</strong>tware package is available <strong>for</strong> automatic routine collection <strong>of</strong><br />

data at pre determined time interval which can be modified as per <strong>the</strong> need and<br />

requirement.<br />

4. Fully protected: It has a wea<strong>the</strong>r pro<strong>of</strong> enclosure to protect data logger and peripheral<br />

against dust and moisture. The logger can operate over <strong>the</strong> range from - 25 o C to + 50 o C<br />

without any error.<br />

5. Integral data processing: The processing includes <strong>the</strong> averages <strong>of</strong> maximum and minimum<br />

averages <strong>of</strong> all wea<strong>the</strong>r variables, standard deviations, wind vector integration etc.<br />

6. Robust construction: Tripod and mast are build from thick walled, galvanized steel tubing<br />

with nickel-plated fittings. The mast is 3 metre in height with adjustable cross-arm supports<br />

<strong>for</strong> sensors. The mast can be positioned precisely by independently adjusting tripod legs.<br />

Each leg is provided with a flat foot with 12 mm hole which allows anchorage to <strong>the</strong> ground<br />

by stake or to concrete. A lightning conductor and earth spike are also included to save <strong>the</strong><br />

sensors and data logger from destructive effects <strong>of</strong> Thunderstorm and Lightning as and<br />

when experienced in <strong>the</strong> area. For measurement <strong>of</strong> wea<strong>the</strong>r parameters in and over <strong>the</strong><br />

Horticultural crops, a mast <strong>of</strong> 30 meter height (existing in <strong>the</strong> nearby site in <strong>the</strong> same field)<br />

can be used <strong>for</strong> sitting <strong>the</strong> sensors at desired heights depending upon <strong>the</strong> height <strong>of</strong><br />

horticultural crops as per <strong>the</strong> need and requirement.<br />

7. Minimum maintenance: Once erected, <strong>the</strong> AWS requires very little routine attention.<br />

8. Recording device: It has a 21 X Micrologger as recording device. It is a rugged fieldproven<br />

datalogger suitable <strong>for</strong> any application requiring data acquisition, on line data<br />

processing or electronic control. It is compact and power full battery-powered device which<br />

effectively combines <strong>the</strong> functions <strong>of</strong> micro-computer, clock, calibrator, scanner, frequency<br />

counter and controller with one smaller enclosure. The 12 volt Nickel-Cadmium battery is<br />

chargeable by solar panel. The micrologger is programmed to handle almost any task<br />

including signal averaging, excite and delay, totaling, maximum and minimum, standard<br />

deviation, scaling, 5th order polynomial processing, low-pass filtering and wind vector<br />

calculation which are fully supported by simple program statements, toge<strong>the</strong>r with a<br />

histogram command <strong>for</strong> direct calculation <strong>of</strong> frequency distributions. S<strong>of</strong>tware support is<br />

available to simplify more complex programming tasks and to avoid inspection and<br />

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processing <strong>of</strong> stored data.<br />

3. Importance <strong>of</strong> wea<strong>the</strong>r variables in disease management<br />

No doubt, that <strong>the</strong>re is a close relationship between plant diseases and <strong>the</strong> wea<strong>the</strong>r<br />

variables. The viral and bacterial diseases are more wea<strong>the</strong>r-depended due to <strong>the</strong> fact that viral<br />

and bacterial pathogens remain at fixed locations, consistently exposed to a particular type <strong>of</strong><br />

wea<strong>the</strong>r <strong>for</strong> a sufficiently long period. Some <strong>of</strong> <strong>the</strong> examples <strong>of</strong> disease-wea<strong>the</strong>r relationships are<br />

given below:<br />

1. High air temperatures may set limits to <strong>the</strong> development <strong>of</strong> plant disease. A high temperature <strong>of</strong><br />

> 35 ( o C) is fungicidal to <strong>the</strong> organism causing blister blight in tea. A temperature <strong>of</strong> > 25 o C<br />

prevents spore <strong>for</strong>mation in "phytophthora infestanis", <strong>the</strong> late blight fungus. Relatively high<br />

temperatures are important <strong>for</strong> <strong>the</strong> rate <strong>of</strong> inoculums build up <strong>of</strong> downy mildews. In potato blight,<br />

temperatures near <strong>the</strong> optimum <strong>for</strong> vegetative mycelial growth (19 -22 o C) stimulate <strong>the</strong><br />

development <strong>of</strong> blight within <strong>the</strong> potato leaves, thus favouring spread by conidia produced by<br />

<strong>the</strong> leaves.<br />

2. <strong>Soil</strong> temperature play an important role in management <strong>of</strong> various diseases specially <strong>the</strong> soil as<br />

well as <strong>the</strong> seed born diseases. Heating <strong>of</strong> soil by solar radiation can be managed by using <strong>the</strong><br />

mulches. Killing <strong>of</strong> fungal spores may be higher under high soil temperature conditions compared<br />

to low temperatures. Generally <strong>the</strong> soil temperature data is recorded during 0700 and 1400 hours<br />

<strong>of</strong> <strong>the</strong> day and an average value is calculated. But it did not give <strong>the</strong> clear picture <strong>of</strong> periodic soil<br />

temperature variations under mulch and non mulch conditions. For example <strong>the</strong> effect <strong>of</strong> soil<br />

solarization on soil temperature regimes showed that degree day accumulation varied from 919<br />

(38.3 o C) to 787 (32.8 o C) degrees under plastic mulch and non-mulch, respectively, in a single<br />

day at Pantnagar.<br />

3. Microclimatic humidity is <strong>of</strong> importance <strong>for</strong> fungal plant diseases, and not <strong>the</strong> macroclimatic<br />

humidity as registered in meteorological screens. Fur<strong>the</strong>r, disease is more affected by<br />

microclimatic conditions in <strong>the</strong> plant canopy than by <strong>the</strong> macroclimatic ones as measured at <strong>the</strong><br />

standard meteorological stations / observatory located at more distance from <strong>the</strong> crop field.<br />

4. The duration <strong>of</strong> leaf wetness (LWP) is important in <strong>the</strong> development <strong>of</strong> plant diseases. The<br />

germination and substantial crop infection by "phyphthora infestanis" requires a minimum LWP <strong>of</strong><br />

13 hours. The LWP <strong>for</strong> infection by several pathogens varies from 0.5 hours to more than 100<br />

hours. The accomplishment <strong>of</strong> substantial infection by "Venturia inaequalis ", <strong>the</strong> fungus causing<br />

scab on apples and pears, require a period <strong>of</strong> wet leaves <strong>the</strong> minimum duration <strong>of</strong> which is linked<br />

to <strong>the</strong> temperature error. Duration <strong>of</strong> precipitation and <strong>the</strong> persistence <strong>of</strong> fog are <strong>of</strong> prime<br />

significance in LWP. Typically <strong>the</strong> infection process on wet leaves proceeds more quickly at high<br />

temperatures, so that temperature during <strong>the</strong> wetting period as well as <strong>the</strong> LWP must be<br />

considered. Different combinations <strong>of</strong> LWP and temperatures are important <strong>for</strong> development <strong>of</strong><br />

different diseases. Often <strong>the</strong> two factors are combined to construct an index <strong>for</strong> <strong>the</strong> occurrence <strong>of</strong><br />

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a plant disease <strong>of</strong> interest.<br />

5. Ma<strong>the</strong>r (1974), reported that in United States, <strong>the</strong> bacterial wilt and leaf blight in corn is related<br />

to <strong>the</strong> previous inter conditions. When <strong>the</strong> sum <strong>of</strong> <strong>the</strong> average temperatures <strong>of</strong> December, January<br />

and February remains below 38 o C, <strong>the</strong>re is no chance <strong>of</strong> wilt on corn. If <strong>the</strong> sum <strong>of</strong> <strong>the</strong> average<br />

temperatures is above 29.5 o C, corn blight is likely to occur. This follows that if <strong>the</strong> winters are<br />

mild, <strong>the</strong> bacterial wilt and leaf blight are likely to spread in an epidemic <strong>for</strong>m in <strong>the</strong> coming crop<br />

while severe winters reduce <strong>the</strong> chances <strong>of</strong> blight.<br />

6. Also, in United States, <strong>the</strong> severity <strong>of</strong> blue mold <strong>of</strong> tobacco is directly correlated with climatic<br />

conditions viz. temperature and relative humidity during early spring. The mean temperature <strong>for</strong><br />

<strong>the</strong> month <strong>of</strong> January in all <strong>the</strong> tobacco growing areas <strong>of</strong> <strong>the</strong> USA directly affects <strong>the</strong> time <strong>of</strong><br />

sowing, and <strong>the</strong> severity <strong>of</strong> blue mold. If <strong>the</strong> mean temperature <strong>of</strong> January is above normal, blue<br />

mold will appear earlier and <strong>the</strong> disease will be severe. If temperatures are below normal, blue<br />

mold will appear later and <strong>the</strong> disease will be less severe.<br />

7. Air temperature influences <strong>the</strong> epidemic development <strong>of</strong> diseases. There is an optimum<br />

temperature <strong>for</strong> growth <strong>of</strong> any organism and <strong>the</strong>re are limits <strong>of</strong> maximum and minimum<br />

temperautres (cardinal temperatures) outside which it survives but can not grow. Paria and Raj<br />

(1987), reported that <strong>the</strong> groundnut rust disease was favourable by Warm and Humid wea<strong>the</strong>r and<br />

spread from <strong>the</strong> lower most to <strong>the</strong> 5th leaf.<br />

8. Butler and Wadia (1992), reported that 70 % infection in groundnut leaves occurs within a 12<br />

hour wetness period at optimum temperatures (20-25 o C). The period <strong>of</strong> wetness after inoculation<br />

with spore suspension must be continuous. Spread <strong>of</strong> disease within crop is facilitated by wind<br />

movement, rain splash and insects as well. It is now well established fact that at 35 o C, <strong>the</strong><br />

incubation period <strong>of</strong> groundnut rust enhanced beyond 19 days and during summer months <strong>of</strong> April<br />

and May when ambient temperatures range from 40-45 0 C, rust remain confined to host tissues<br />

without expression. They also reported that <strong>for</strong> late leaf spot disease infection is greatest if leaf<br />

wetness is intermittent. Fur<strong>the</strong>r <strong>the</strong> leaf spots were most prevalent in wet areas with annual rainfall<br />

exceeding 500-600 mm. Also fungal infection is highly influenced by wet periods which create<br />

surface wetness <strong>of</strong> plants.<br />

9. Jensen and Boyle (1966) reported that <strong>the</strong> leaf wetness by rainfall, also causes germination <strong>of</strong><br />

conidia and produces green tube <strong>for</strong> proper infection to <strong>the</strong> host. They fur<strong>the</strong>r observed that rain<br />

helps spore dispersal also.<br />

10. Rao et. al. (1994) reported that besides rain, cool temperatures <strong>of</strong> less than 20 o C also play a<br />

role in <strong>the</strong> mechanisms <strong>of</strong> spore releases. Low rainfall (11 mm) with 89 % relative humidity (RH)<br />

could increase disease scale and RH <strong>of</strong> 86 % may aid <strong>the</strong> entry <strong>of</strong> germ tube through open<br />

stomata.<br />

So, in terms <strong>of</strong> prevailing wea<strong>the</strong>r conditions, <strong>the</strong> incidence <strong>of</strong> several diseases can be<br />

even <strong>for</strong>ecast if <strong>the</strong> relationship between <strong>the</strong> wea<strong>the</strong>r <strong>of</strong> an area and <strong>the</strong> diseases in it can be<br />

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visualised. A very simple example is given below to understand <strong>the</strong> disease - wea<strong>the</strong>r<br />

relationships:<br />

Let <strong>the</strong> range <strong>of</strong> climatic conditions <strong>for</strong> <strong>the</strong> development <strong>of</strong> <strong>the</strong> disease be represented by<br />

D, and let C 1 , C 2 and C 3 represent <strong>the</strong> climatic conditions in region 1, 2 and 3. Following three<br />

relationships can be established between disease and wea<strong>the</strong>r:<br />

i. In first case <strong>the</strong> range <strong>of</strong> wea<strong>the</strong>r conditions favouring a disease (D) is entirely <strong>the</strong> outside<br />

<strong>the</strong> range <strong>of</strong> wea<strong>the</strong>r (C 1 ) encountered in <strong>the</strong> area. There<strong>for</strong>e, <strong>the</strong> disease can not flourish<br />

in that region.<br />

ii. In <strong>the</strong> second case <strong>the</strong> wea<strong>the</strong>r (C 2 ) irrespective <strong>of</strong> <strong>the</strong> prevailing wea<strong>the</strong>r conditions, is<br />

always favourable and lies within <strong>the</strong> limits (D) <strong>for</strong> <strong>the</strong> appearence <strong>of</strong> disease. In such<br />

cases, <strong>the</strong> wea<strong>the</strong>r factors are not very important <strong>for</strong> disease <strong>for</strong>ecast.<br />

iii. In third case, which is most frequent and important one, if during <strong>the</strong> year <strong>the</strong> wea<strong>the</strong>r<br />

shifts and is no longer favourable <strong>for</strong> <strong>the</strong> disease, <strong>the</strong>n <strong>the</strong> disease may not occur or<br />

spread at all that year. However, when wea<strong>the</strong>r conditions are close to or favourable <strong>for</strong><br />

disease, <strong>the</strong> chances <strong>of</strong> attack from <strong>the</strong> disease will be comparatively greater.<br />

4. Conclusion<br />

If <strong>the</strong>se quantification studies are continued <strong>for</strong> large period <strong>of</strong> time and data is subjected<br />

to modeling and a better disease <strong>for</strong>ecasting system can be development <strong>for</strong> sustanable<br />

management <strong>of</strong> plant diseases under field conditions.<br />

REFERENCES<br />

• Butler, D.R. and Wadia, K.D.R. (1992). Groundnut foliar disease, infection and leaf wetness in<br />

groundnut: A global perspective. Proceedings <strong>of</strong> an International Workshop, ICRISAT,<br />

Hyderabad, A.P., India., Nov. 25-29, 1997, pp.475.<br />

• Jensen, R.F. and Boyle, L.W. (1966). The effect <strong>of</strong> temperature, relative humidity and precipitation<br />

on peanut leaf spot. <strong>Plant</strong> Dis. Rep., 49 : 975-978.<br />

• Ma<strong>the</strong>r, J.R. (1974). Climatology, Fundamentals and Applications. McGraw Hill Company : 181-<br />

214.<br />

• Paria, T.K. and Raj, S.K. (1987). Epidemiology <strong>of</strong> groundnut rust. Current Research, 16 : 100-<br />

102.<br />

• Rao, P.A.; Ramesh Babu; G. Sarda; Jayalakshmi Devi, R. and H. Naidu. (1994). Prediction and<br />

prevention <strong>of</strong> late leaf spot on kharif groundnut. Pages 386-397, In Sustainability <strong>of</strong><br />

Oilseeds, edited by Prasad M.V.R., Indian Soc. Oilseeds Research, Hyderabad.<br />

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Role <strong>of</strong> Organic Amendments in <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong> Borne <strong>Plant</strong><br />

Pathogens<br />

R.P. Singh & Bijendra Kumar<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

<strong>Soil</strong> borne plant pathogens survive in <strong>the</strong> soil and cause extensive damage to many crops,<br />

and are <strong>of</strong>ten difficult to control with conventional strategies such as <strong>the</strong> use <strong>of</strong> resistant host<br />

cultivars and syn<strong>the</strong>tic fungicides. The lack <strong>of</strong> reliable chemical controls, <strong>the</strong> occurrence <strong>of</strong><br />

fungicide resistance in pathogens, and <strong>the</strong> breakdown or circumvention <strong>of</strong> host resistance by<br />

pathogen populations (McDonald and Linde, 2002) are some <strong>of</strong> <strong>the</strong> reasons underlying ef<strong>for</strong>ts to<br />

develop new disease control measures. The ban <strong>of</strong> methyl bromide, <strong>the</strong> most effective fumigant<br />

used worldwide <strong>for</strong> soil disinfestation, has fur<strong>the</strong>r increased <strong>the</strong> need <strong>for</strong> alternative control<br />

methods. In this context, <strong>the</strong> search <strong>for</strong> an alternative with high efficiency, low cost and limited<br />

environmental impact is <strong>the</strong> immediate need <strong>for</strong> eco-sustainable modern agriculture. In <strong>the</strong> past<br />

century, <strong>the</strong> introduction <strong>of</strong> syn<strong>the</strong>tic inorganic fertilizers, disease-resistant varieties and fungicides<br />

has allowed farmers to break <strong>the</strong> link between organic amendments and soil fertility. As a result,<br />

organic materials such as crop residues and manure from essential resources became solid<br />

wastes. After <strong>the</strong> reduction <strong>of</strong> <strong>the</strong> organic input, soil organic matter decreased over time, soil<br />

fertility declined, and a large number <strong>of</strong> diseases caused by soil borne plant pathogens spread in<br />

agro-ecosystems. However, a renewed interest in application <strong>of</strong> organic matter (OM) to soil, <strong>for</strong><br />

control <strong>of</strong> soil borne pathogens, has been stimulated by public concern about <strong>the</strong> adverse effects<br />

<strong>of</strong> soil fumigants and fungicides on <strong>the</strong> environment, and <strong>the</strong> need <strong>for</strong> healthier agricultural<br />

products. Several studies have shown that organic amendments such as animal manure, green<br />

manure, incorporation <strong>of</strong> crop residues into <strong>the</strong> soil, composts and peats can be very effective to<br />

improve soil structure, fertility and in controlling soil borne plant pathogens such as Fusarium spp.,<br />

Phytophthora spp., Pythium spp., Rhizoctonia solani, Sclerotinia spp., Sclerotium spp.,<br />

Thielaviopsis basicola, Verticillium dahliae, Meloidogyne spp. Ralstonia solanacearum etc.<br />

Different complementary mechanisms have been proposed to explain <strong>the</strong> suppressive<br />

capacity <strong>of</strong> organic amendments:<br />

<br />

<br />

<br />

<br />

<br />

<br />

Enhanced activities <strong>of</strong> antagonistic microbes<br />

Increased competition against pathogens <strong>for</strong> resources that cause fungistasis<br />

Release <strong>of</strong> fungitoxic compounds during organic matter decomposition<br />

Induction <strong>of</strong> systemic resistance in <strong>the</strong> host plants<br />

Changes in soil physio-chemical properties that are unsuitable <strong>for</strong> pathogens<br />

Combinations <strong>of</strong> <strong>the</strong>se mechanisms<br />

However, despite <strong>the</strong> potential value <strong>of</strong> organic soil amendment, <strong>the</strong>re are several<br />

concerns about its efficacy and potential side-effects that limit practical applications. For instance,<br />

some reports indicate that <strong>the</strong> effectiveness <strong>of</strong> OM amendment is variable and, in some cases,<br />

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can enhance disease severity. These negative effects <strong>of</strong> OM amendment were <strong>of</strong>ten associated<br />

ei<strong>the</strong>r with increased inoculum <strong>of</strong> pathogenic fungi because OM provides <strong>the</strong> substrate <strong>for</strong> <strong>the</strong>ir<br />

saprophytic growth or with release <strong>of</strong> phytotoxic compounds that may damage plant roots and<br />

predispose <strong>the</strong>m to pathogen attack. The inconsistent disease control results obtained with OM<br />

amendments, with both suppressive (disease reduction) and conducive (disease increase) effects,<br />

produced skepticism in farmers about <strong>the</strong> use <strong>of</strong> <strong>the</strong>se materials. In addition, despite extensive<br />

research, no reliable methods are currently available to predict <strong>the</strong> effect <strong>of</strong> different OM<br />

amendments on soil borne pathogens (Bananomi et al., 2007).<br />

Effect <strong>of</strong> Different Types <strong>of</strong> Organic Amendment:<br />

The ability <strong>of</strong> different OM types to reduce pathogen populations is highest <strong>for</strong> organic<br />

waste, intermediate <strong>for</strong> crop residues and lowest <strong>for</strong> composts. However, it is interesting to notice<br />

that crop residues increased pathogen populations in some cases. For crop residues, a key factor<br />

that affects <strong>the</strong> fate <strong>of</strong> pathogen populations is oxygen availability in amended soil. In aerobic<br />

conditions <strong>the</strong> effect <strong>of</strong> amendment on fungal populations is very variable. In fact, this includes N<br />

rich tissue with a low C/N ratio, cruciferous species rich in glucosinolates that are known <strong>for</strong> <strong>the</strong>ir<br />

antifungal activity after hydrolysis to isothiocyanates, and N-poor residues with high C/N ratio<br />

(grasses, straw, wood chips, etc.).<br />

Effect <strong>of</strong> Organic Amendments on Disease Suppression<br />

Suppressive capacity varied dramatically among different OM types. Composts and<br />

organic wastes are <strong>the</strong> most suppressive and only in a few cases did <strong>the</strong>se materials increase<br />

disease incidence. The effect <strong>of</strong> amendment with crop residues is more variable, and although<br />

<strong>the</strong>y are <strong>of</strong>ten suppressive, <strong>the</strong>y could also be conducive. The suppressive capacity <strong>of</strong> <strong>the</strong><br />

amendment varied largely towards different pathogens.<br />

OM amendments have multiple direct and indirect effects on <strong>the</strong> plant pathogen- beneficial<br />

microbe system. Understanding <strong>the</strong> relative importance <strong>of</strong> <strong>the</strong>se effects is important <strong>for</strong><br />

management <strong>of</strong> crop residues and organic wastes. For <strong>the</strong>se materials, <strong>the</strong> balance between<br />

negative effects (i.e. phytotoxicity and food base <strong>for</strong> pathogens) and positive effects (i.e. fungitoxic<br />

and fungistatic effects and resistance induction) is pivotal to avoid disease increase. Promising<br />

results have been obtained with T. basicola and V. dahliae. Strong evidence indicates that <strong>the</strong><br />

temporary accumulation <strong>of</strong> ammonia or nitrous acid (in acidic soils), following <strong>the</strong> application <strong>of</strong><br />

crop residues or wastes with high N contents (C/N ratio below 10), are responsible <strong>for</strong> <strong>the</strong><br />

eradication <strong>of</strong> Verticillium microsclerotia. Un<strong>for</strong>tunately, <strong>the</strong>se effects are very variable among<br />

different soil types, being more effective in sandy, OM-poor soils. Detailed and quantitative<br />

knowledge <strong>of</strong> <strong>the</strong> pathways <strong>of</strong> <strong>the</strong> N cycle (ammonification, nitrification, denitrification, etc.) in<br />

different soils is necessary, <strong>for</strong> effective disease control and to avoid environmental pollution if<br />

large quantities are applied. Positive results have also been achieved by using OM with high C/N<br />

ratios. These materials can stimulate microbial activity, which can in turn deplete N availability,<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

and, consequently, impair <strong>the</strong> pathogen infection process. However, N starvation immediately after<br />

OM application can also impair plant growth. To avoid OM phytotoxic effects, correct management<br />

<strong>of</strong> crop residues and wastes is a basic step. This can be achieved by optimizing application rate<br />

and <strong>the</strong> timing between OM applications and planting <strong>the</strong> crop. Un<strong>for</strong>tunately, it is impossible to<br />

generalize about how long planting should be delayed. If decomposition occurs anaerobically, OM<br />

generates adverse conditions <strong>for</strong> many phytopathogenic fungi, but un<strong>for</strong>tunately, also <strong>for</strong> plant<br />

growth. This emphasize <strong>the</strong> importance <strong>of</strong> studying both plant and pathogen responses to OM<br />

during decomposition. Special attention should be paid to choosing <strong>the</strong> application rate. Finally,<br />

application <strong>of</strong> crop residues, and to a lesser extent <strong>of</strong> undecomposed organic wastes, should be<br />

avoided if <strong>the</strong> phytopathological problems are due to Pythium spp. or R. solani. These pathogens<br />

<strong>of</strong>ten respond positively to OMs and colonize <strong>the</strong>m as nutrient substrates. Sclerotium spp. is<br />

ano<strong>the</strong>r good example <strong>of</strong> such a pathogen, favoured by <strong>the</strong> presence <strong>of</strong> crop residues. Volatile<br />

compounds emanating from such residues can stimulate germination <strong>of</strong> sclerotia with a<br />

consequent overall increase <strong>of</strong> disease incidence and severity (Punja and Grogan, 1981).<br />

Organic Matter and Phytotoxicity<br />

OM phytotoxicity has <strong>of</strong>ten been considered an idiosyncratic phenomenon and<br />

consequently, an unpredictable side-effect <strong>of</strong> OM amendments. The occurrence and intensity <strong>of</strong><br />

phytotoxicity are measurable and predictable depending on <strong>the</strong> environmental conditions where<br />

decomposition occurs. Phytotoxicity largely varied among different OM types, according to <strong>the</strong><br />

following rank: crop residues >organic wastes > composts > peats. As decomposition proceeds,<br />

phytotoxicity consistently declines. Many ecological studies report <strong>the</strong> phytotoxic effects <strong>of</strong><br />

decaying plant materials. However, during decomposition, both <strong>the</strong> abundance and <strong>the</strong> activity <strong>of</strong><br />

phytotoxic compounds continuously change over time because <strong>of</strong> <strong>the</strong>ir sorption and polymerisation<br />

on soil organic matter and clay minerals, and because <strong>of</strong> chemical trans<strong>for</strong>mation by<br />

microorganisms. Bonanomi et al. (2006) showed not only a widespread presence <strong>of</strong> phytotoxicity<br />

in decaying plant litter, but also predictable dynamics in relation to both decomposition duration<br />

and environmental conditions.<br />

Conclusion<br />

There is an urgent requirement to find sustainable strategies <strong>for</strong> <strong>the</strong> control <strong>of</strong> soil borne<br />

diseases, <strong>for</strong> both conventional and low-input farming systems. In <strong>the</strong> last 70 years a massive<br />

number <strong>of</strong> studies have been carried out on <strong>the</strong> subject <strong>of</strong> OM amendments <strong>for</strong> <strong>the</strong> control <strong>of</strong> plant<br />

diseases, and this technique appears to be one <strong>of</strong> <strong>the</strong> most promising <strong>for</strong> its low cost and <strong>the</strong><br />

limited environmental impact compared to fungicides and fumigants. OM amendments have great<br />

potential but give inconsistent control and sometimes increased disease severity and phytotoxicity,<br />

which still limit <strong>the</strong>ir use. There is no doubt that <strong>the</strong> benefits <strong>of</strong> OM amendments far outweigh <strong>the</strong>ir<br />

drawbacks but while <strong>the</strong> impact <strong>of</strong> this technique on pathogen populations and disease<br />

suppression remains unpredictable. Significant progress has been made towards understanding<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>the</strong> biology <strong>of</strong> disease suppression by OM amendments in specific plant-pathogen systems, such<br />

as peat-Pythium, leaf compost-Pythium, N-rich waste-V. dahliae, compost-F. oxysporum f.sp.<br />

lycopersici (Borrero et al., 2004) etc. However, still lacking are reliable guidelines to predict <strong>the</strong><br />

impact <strong>of</strong> any type <strong>of</strong> OM amendment on specific soil borne diseases. Researches on <strong>the</strong> following<br />

areas may be valuable <strong>for</strong> better understanding <strong>of</strong> <strong>the</strong> subject:<br />

How different OM types modulate plant-pathogen-antagonist relationships;<br />

Developing OM amendments able to enhance <strong>the</strong> activity <strong>of</strong> beneficial microbes, without<br />

stimulating pathogen populations;<br />

Improving <strong>the</strong> effectiveness <strong>of</strong> combined applications <strong>of</strong> OM amendments and biological<br />

control agents;<br />

Identifying parameters that consistently predict <strong>the</strong> suppressive ability <strong>of</strong> different OMs.<br />

REFERENCE<br />

• Borrero C., Trillas M.I., Ordovás J., Tello J.C., Avilés M.,2004. Predictive factors <strong>for</strong> <strong>the</strong><br />

suppression <strong>of</strong> Fusarium wilt <strong>of</strong> tomato in plant growth media. Phytopathology 94:<br />

1094-1101.<br />

• Bonanomi G., Sicurezza M.G., Caporaso S., Assunta E., Mazzoleni S., 2006. Phytotoxicity<br />

dynamics <strong>of</strong> decaying plant materials. New Phytologist 169: 571-578.<br />

• Bonanomi, G., Antignani, V., Pane , C. and Scala F., 2007, Suppression <strong>of</strong> soilborne fungal<br />

diseases With organic amendments J. <strong>of</strong> Pl. Pathol., 89(33):11-324<br />

• McDonald B.A., Linde C., 2002. Pathogen population genetics, evolutionary potential, and durable<br />

resistance. Annual Review <strong>of</strong> Phytopathology 40: 349-379.<br />

• Punja Z.K., Grogan R.G., 1981. Mycelial growth and infection without a food base by eruptively<br />

germinating sclerotia <strong>of</strong> Sclerotium rolfsii. Phytopathology 71: 1099-1003<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Evaluation and Selection <strong>of</strong> Promising Trichoderma Isolates <strong>for</strong> <strong>the</strong><br />

<strong>Management</strong> <strong>of</strong> <strong>Soil</strong> Borne Fungal <strong>Plant</strong> Pathogens<br />

A.K. Tewari<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, GBPUA&T, Pantnagar- 263 145 (Uttarakhand)<br />

Dual culture Method: This method is used <strong>for</strong> testing mycoparasitic activity <strong>of</strong> antagonist. Pour<br />

15-20ml sterile PDA in sterile plates amended with Chloromphenicol (100 mg/lit.) or streptomycin<br />

(100mg/lit). Place <strong>the</strong> bits (5mm) <strong>of</strong> <strong>the</strong> test pathogen as well as antagonist on <strong>the</strong> PDA plates<br />

opposite to each o<strong>the</strong>r from 1.0 cm from <strong>the</strong> periphery <strong>of</strong> plates (if both are fast growing) or place it<br />

2-3cm apart (if both are slow growing). Incubate <strong>the</strong> plates at 25+1 0 C <strong>for</strong> desired duration.<br />

Observe <strong>the</strong> plates regularly.<br />

I. In-vitro evaluation and selection<br />

(A). Mycoparasitism:<br />

In mycoparasitism <strong>the</strong> pathogen stops growing upon contact with <strong>the</strong> antagonist and its<br />

mycelium begin to lyse backwards and <strong>the</strong> antagonist continue to grow over <strong>the</strong> test fungal<br />

pathogen.<br />

Observations<br />

<br />

First observation should be taken just after contact and measure <strong>the</strong> growth <strong>of</strong> <strong>the</strong><br />

pathogen in dual culture.<br />

After contact, observations should be taken regularly at 3 day interval until <strong>the</strong> antagonist<br />

completely parasitizes <strong>the</strong> test pathogen or antagonist stops growing over <strong>the</strong> test pathogen.<br />

Calculate <strong>the</strong> percent inhibition (parasitized growth) <strong>of</strong> <strong>the</strong> test pathogen by comparing <strong>the</strong> growth<br />

<strong>of</strong> <strong>the</strong> pathogen (after parasitization) with its initial growth (just after contact). To see <strong>the</strong> hyphal<br />

interaction small bits <strong>of</strong> mycelium can be taken from interaction zone and observe under<br />

microscope.<br />

Mycoparasitism <strong>of</strong> Sclerotial plant pathogens<br />

Collect freshly non-dried sclerotia , surface disinfested and wash in sterile distilled water.<br />

Immerse <strong>the</strong>se sclerotia in an aqueous spore or mycelial suspension <strong>of</strong> <strong>the</strong> antagonist <strong>for</strong> 1-5 min.<br />

Place <strong>the</strong>se sclerotia in culture plates containing sterile moist sand. Incubate it <strong>for</strong> 1-4 week at 25-<br />

28 0 C. After desired period <strong>of</strong> time observe colonization <strong>of</strong> antagonist on decayed sclerotia<br />

B). Antibiosis:<br />

The antagonists that has antibiosis effect (<strong>for</strong>mation <strong>of</strong> zone <strong>of</strong> inhibition) in dual culture<br />

must be fur<strong>the</strong>r tested using cellophane membrane and cell free culture filtrates<br />

Non Volatile compounds:<br />

1. Cellophane membrane method<br />

Place sterilized disk (90mm) <strong>of</strong> a cellophane membrane on culture medium. An agar disk <strong>of</strong><br />

antagonistic fungus is placed at <strong>the</strong> centre <strong>of</strong> <strong>the</strong> cellophane membrane. 3-4 days after incubation,<br />

remove <strong>the</strong> cellophane membrane along with <strong>the</strong> growth <strong>of</strong> antagonist. An agar disk from culture<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>of</strong> actively growing test pathogen is transfer to <strong>the</strong> position previously occupied by <strong>the</strong> antagonist.<br />

Test pathogen grown on PDA plates serves as check. The radial growth <strong>of</strong> <strong>the</strong> test pathogen is<br />

recorded 3-4 days after incubation and compare with check. The reduction in radial growth <strong>of</strong> <strong>the</strong><br />

test pathogen shows production <strong>of</strong> non-volatile compounds by <strong>the</strong> antagonist.<br />

2. Cell free culture filtrate<br />

The antagonist is grown on potato broth medium ei<strong>the</strong>r in stationary or in shake culture.<br />

After sufficient mycelium growth <strong>the</strong> mycelium and o<strong>the</strong>r cells are removed by filtration through<br />

filter paper and <strong>the</strong>n sterilized by passing through G 1 ,G 3 and G 5 sintered glass filter. The cell free<br />

sterile culture filtrate is tested <strong>for</strong> efficacy <strong>of</strong> antagonist against <strong>the</strong> fungal pathogens by following<br />

ways.<br />

a. Assay in solid medium<br />

i. Food Poison technique<br />

ii. Filter paper disc method<br />

iii. Agar well method<br />

b. Assay in liquid medium<br />

c. Spore germination test<br />

a. Assay in solid medium<br />

i. Food Poison technique<br />

Mix sterile cell free culture filtrate in sterilized PDA flasks (various concentrations)<br />

and pour in Petri dishes. Inoculate <strong>the</strong> test pathogen at <strong>the</strong> centre <strong>of</strong> <strong>the</strong> PDA plates. Pathogen<br />

on PDA plates without culture filtrate serves as control. Incubate at 25+1 0 C <strong>for</strong> desired<br />

duration. Per cent inhibition was calculated by measuring <strong>the</strong> radial growth <strong>of</strong> <strong>the</strong> test fungus in<br />

amended medium and compare with check.<br />

ii. Filter paper disc method<br />

Pour 15ml <strong>of</strong> a PDA in sterile Petri plates. After solidification uni<strong>for</strong>mly spread 4ml <strong>of</strong> 1.5%<br />

water agar, seeded with 10 4 spores/ml <strong>of</strong> <strong>the</strong> test pathogen. 4-6 filter paper dics (1-2 cm dia,<br />

autoclaved and dried) soaked in culture filtrate and dried, are place on <strong>the</strong> seeded agar medium<br />

from 1-1.5cm periphery <strong>of</strong> <strong>the</strong> plates. After incubation measure <strong>the</strong> zones <strong>of</strong> inhibition around <strong>the</strong><br />

filter paper .<br />

iii. Agar-well Method<br />

Prepare PDA plates as above. Remove Agar plugs at a distance <strong>of</strong> 1-2 cm from <strong>the</strong><br />

periphery <strong>of</strong> <strong>the</strong> PDA plate with <strong>the</strong> help <strong>of</strong> cork borer <strong>of</strong> 1-2 cm dia. Fill <strong>the</strong> wells with a known<br />

concentration and standard quantity <strong>of</strong> <strong>the</strong> cell free culture filtrate. After incubation, measure <strong>the</strong><br />

zones <strong>of</strong> inhibition around <strong>the</strong> wells.<br />

b. Assay in liquid medium<br />

Add sterile culture filtrate at desired concentration in a known volume <strong>of</strong> potato broth and<br />

mix well. The flasks containing medium is inoculated with a 5 mm discs (2 no.) <strong>of</strong> <strong>the</strong> test<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

pathogen. Incubate until sufficient growth has occurred in check (medium without culture filtrate)<br />

flask. Measure fresh and dry weight <strong>of</strong> <strong>the</strong> test pathogen growth and calculate per cent inhibition<br />

c. Spore germination test<br />

Place 0.2-0.5ml <strong>of</strong> <strong>the</strong> desired concentration <strong>of</strong> <strong>the</strong> cell free culture filtrate in <strong>the</strong> wells <strong>of</strong> a<br />

cavity slide and dry at room temp. The same amount (0.2-0.5ml) <strong>of</strong> spore suspension <strong>of</strong> <strong>the</strong> test<br />

pathogen (5X10 3 spores/ml) is added over <strong>the</strong> dried culture filtrate and mix well with help <strong>of</strong> a<br />

glass rod. Incubate it in a humid chamber at 25-28 0 C. Spore germination and characteristics <strong>of</strong> <strong>the</strong><br />

germ tube is recorded at 12 hr interval and compare with check (cavity slides without culture<br />

filtrate) and calculate per cent inhibition.<br />

Volatile compounds:<br />

Grow antagonist on PDA plates. 3-4 days after incubation, inoculate <strong>the</strong> test pathogen in<br />

separate PDA plates. Place inoculated test pathogen (upper) on <strong>the</strong> 3-4 days old antagonistic<br />

plates (lower) by removing lids <strong>of</strong> both <strong>the</strong> plates. Make pair by binding both <strong>the</strong> plates opposite to<br />

each o<strong>the</strong>r with parafilm. Incubate <strong>the</strong> paired plates until full growth has occurred in check plates<br />

(inoculated with test pathogen alone). Calculate <strong>the</strong> per cent growth inhibition by measuring <strong>the</strong><br />

growth <strong>of</strong> <strong>the</strong> test pathogen and comparing it with check plates. The reduction in radial growth <strong>of</strong><br />

<strong>the</strong> test pathogen shows production <strong>of</strong> volatile compounds.<br />

C. Compatibility <strong>of</strong> fungal antagonist with commonly used chemicals:<br />

‘Food Poison Technique’ is used to test <strong>the</strong> compatibility <strong>of</strong> fungal antagonist fungicides,<br />

insecticides, herbicides and o<strong>the</strong>r chemicals to be commonly used <strong>for</strong> plant health.<br />

II. Evaluation and selection <strong>of</strong> promising Trichoderma isolates in glasshouse<br />

1. Disease <strong>Management</strong><br />

A. Seed treatment<br />

B. Seedling dip treatment<br />

C. <strong>Soil</strong> application<br />

D. <strong>Soil</strong> drenching<br />

Observations<br />

i. Disease incidence / Disease severity<br />

ii. Population dynamics (CFU /g soil at 7 days interval)<br />

2. Systemic induced resistance<br />

A. Seed treatment<br />

B. Seedling dip treatment<br />

C. pre-spraying<br />

Observations:<br />

a. Peroxidase,<br />

b. Phenyl alanine ammmonia lyase<br />

c. Polyphenol oxidase<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

d. H 2 O 2 content<br />

e. Phenol content<br />

f. Superoxide dismutase<br />

g. Lypoxygenase<br />

h. Chlorophyll content<br />

i. Membrane stability index<br />

3. <strong>Plant</strong> growth promoter<br />

Observations:<br />

a. Biomass <strong>of</strong> plant<br />

b. Root length & weight<br />

c. Shoot length & weigh<br />

III. Qualitative parameters <strong>for</strong> <strong>for</strong>mulation<br />

a. Spore concentration<br />

b. Shelf life (Viability)<br />

c. Food <strong>for</strong> initial establishment<br />

IV. Field Testing<br />

V. Maintenance <strong>of</strong> culture<br />

Selection <strong>of</strong> promising Trichoderma isolates <strong>for</strong> commercialization<br />

i. Select broad spectrum isolate.<br />

ii. Evaluate per<strong>for</strong>mance under <strong>the</strong> range <strong>of</strong> environmental conditions.<br />

iii. Evaluate <strong>for</strong>mulations.<br />

iv. Evaluate application methods.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Biodeterioration <strong>of</strong> Seed in Storage and its Control by Microbial<br />

Antagonists<br />

K.Vishunavat<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand<br />

As a result <strong>of</strong> public concerns about <strong>the</strong> safety <strong>of</strong> our environment and food supply, it has<br />

become a national research priority to develop new pest management technologies that reduce<br />

our use <strong>of</strong> chemical pesticides. Microorganisms naturally present in agricultural ecosystems are<br />

being studied as environmentally compatible alternatives to traditional chemical methods <strong>for</strong><br />

controlling plant diseases. A serious impediment to bringing many such microorganisms<br />

discovered by ARS scientists to <strong>the</strong> marketplace is <strong>the</strong> lack <strong>of</strong> knowledge <strong>of</strong> cultivation and<br />

<strong>for</strong>mulation technologies needed to produce cells that are tolerant to <strong>the</strong> stresses <strong>of</strong> large-scale<br />

cultivation, separation, processing (drying or dewatering biomass), and storage. There is need to<br />

focus upon <strong>the</strong> studies to discover <strong>the</strong> genetic and metabolic mechanisms that enhance microbial<br />

stress tolerance such that high yields <strong>of</strong> viable effective cells with long shelf lives can be produced.<br />

Post harvest and storage diseases in seed crops<br />

Worldwide, diseases <strong>of</strong> crop plants cause losses estimated to be 12%, and post harvest<br />

losses due to food spoilage have been estimated to be between 10% to 50%. In <strong>the</strong> United<br />

States, <strong>the</strong>se figures are estimated to be 12% and 9%, respectively. Finding ways to prevent<br />

microorganisms from causing <strong>the</strong>se losses would help ensure a stable food supply <strong>for</strong> <strong>the</strong> world's<br />

ever expanding population.<br />

Post Harvest Storage <strong>of</strong> Grain<br />

a. An international Association, he group <strong>for</strong> Assistance on systems relating to grain after<br />

harvest (GASGA) , is a voluntary association linked with donor operations that promote <strong>the</strong><br />

preservation <strong>of</strong> grain in storage .<br />

b. GASGA has following objectives<br />

c. To stimulate technical cooperation in all aspects <strong>of</strong> grain post harvest research and<br />

development in both developing and developed countries<br />

d. To identify and seek ways <strong>of</strong> meeting research and development training ,and in<strong>for</strong>mation<br />

needs in <strong>the</strong> post harvest subsector<br />

e. To serve an advisory role and provide a <strong>for</strong>um <strong>for</strong> exchange <strong>of</strong> technical in<strong>for</strong>mation<br />

,experience and ideas <strong>for</strong> a global collaborative approach to fungal and mycotoxin<br />

problems<br />

Storage fungi<br />

Storage fungi (also called storage molds) are usually not present to any serious extent<br />

be<strong>for</strong>e harvest and invade grains or seeds during storage. Small quantities <strong>of</strong> spores <strong>of</strong> storage<br />

fungi may be present on grain going into storage or may be present on spoiled grain present in<br />

harvest, handling and storage equipment or structures. Under improper storage conditions this<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

small amount <strong>of</strong> inoculum can increase rapidly leading to significant problems.The most common<br />

storage fungi are species <strong>of</strong> Aspergillus and Penicillium. These fungi are widely distributed and<br />

almost always present. O<strong>the</strong>r than certain fungi <strong>of</strong> Cladosporium herbarum and Botryodiplodia<br />

sp.also cause deterioration during storage. Storage fungi may cause damages to <strong>the</strong> seeds during<br />

harvesting processing, cleaning and drying <strong>of</strong> <strong>the</strong> grains be<strong>for</strong>e storage and during storage<br />

Invasion by storage fungi<br />

The storage fungi get access to <strong>the</strong> seed/grain tissues via micropyle, peduncle,<br />

microscopic creaks on seed surface superficially over <strong>the</strong> surface <strong>of</strong> various seed tissues such as<br />

rachis, ,spikelets, pericarp,caryopsis.Invasion <strong>of</strong> storage fungi may follow <strong>the</strong> path into <strong>the</strong> various<br />

seed tissues. The fungus A.flavus colonizes <strong>the</strong> ear tip to <strong>the</strong> base <strong>of</strong> silks <strong>the</strong>n glumes by <strong>the</strong> milk<br />

stage . However, <strong>the</strong> fungus only colonizes <strong>the</strong> seed surface and rarely penetrate cob pith. A<br />

flavus penetrate <strong>the</strong> maize seeds through <strong>the</strong> pericarp. There <strong>the</strong> seeds (embryo and cotyledons)<br />

serve as food source <strong>of</strong> <strong>the</strong> fungus. A.flavus in maize gets a way into seed through rachilla <strong>of</strong><br />

adjuscent spikelet from <strong>the</strong> rachis and tracts <strong>the</strong>n reaches to <strong>the</strong> floral axis through <strong>the</strong><br />

parenchyma <strong>of</strong> <strong>the</strong> rachilla and reaches to <strong>the</strong> innermost layer <strong>of</strong> <strong>the</strong> pericarp.The hyphae in that<br />

case may be inter or intracellular in floral axis or and inside <strong>the</strong> seed orInvasion <strong>of</strong> maize seed by<br />

Aspergillus flavus may also takes place via <strong>the</strong> silks.<br />

Factors affecting storage fungi to develop in storage<br />

• The development <strong>of</strong> storage fungi in stored grain is influenced by<br />

• The moisture content <strong>of</strong> <strong>the</strong> stored grain,<br />

• The temperature <strong>of</strong> <strong>the</strong> stored grain,<br />

• The condition <strong>of</strong> <strong>the</strong> grain going into storage,<br />

• The length <strong>of</strong> time <strong>the</strong> grain is stored and<br />

• The amount <strong>of</strong> insect and mite activity in <strong>the</strong> grain<br />

Table 1: Correlation <strong>of</strong> Fungal Species and Storage Insects<br />

Insect screened<br />

Fungi isolated<br />

Sitophilus oryzae L. A flavus, A. candidus, A. ochroaceus, A.<br />

fumigatus,A. terreus, A. parasiticus, A.<br />

restrictus, A. terricola,A. ustus, A. versicolor, A.<br />

sydowi, A. ruber, A. chevalier),A niger, P.<br />

rugulosum, Amblyosporium sp., Cladosporium<br />

sp.,<br />

Tribolium castaneum Herbst A. flavus, A. candidus, P. islandicum, A.<br />

versicolor, A. niger,A. ruber, A. chevalier<br />

Trogoderma granaria Everts A. flavus, A. candidus, P. islandicum, A. ruber,<br />

A. glaucis gr.,A. niger, A. sydowi, A. versicolor,<br />

P. restrictum<br />

Bruchus chinensis Linn A. flavus, A. candidus, A. sydowi, A. ruber, A.<br />

glaucus gr.<br />

Oryzaephilus surinamensis Linn A. flavus, A. ochroaceus, A. restrictus, A.<br />

glaucus gr.,A. terreus, P. decumbens,<br />

Cladosporium sp.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Stegoblum peneceum Linn<br />

Rhizoperth dominica Fab<br />

Araecerus fasciculatus<br />

Corcyra cephalonica Staint<br />

Esphestia cautella Walker<br />

A. candidus, A. glaucus gr.<br />

A. candidus, A. ochraceus, A. niger. A. glaucus<br />

gr.<br />

A. flavus, A. candidus, A. niger, A. glaucus gr.<br />

A. flavus, A. candidus, A. ochraceus, A. sydowi,<br />

A. ruber,A. niger, A. restrictus, A. versicolor, P.<br />

spinullosum,P. corylophilum, Nigrospora sp.<br />

A.flavus, A. candidus, A. niger, A. glaucus gr.,A.<br />

terreus, A. ruber, A. versicolor<br />

Factors affecting damages in storage<br />

• Moisture content<br />

• Temperature<br />

• Cracked and broken kernels and <strong>for</strong>eign material<br />

• The extent to which grain in already invaded by storage fungi<br />

• Length <strong>of</strong> time <strong>the</strong> grain is to be stored.<br />

• Amount <strong>of</strong> insect and mite activity in grain<br />

Losses due to storage fungi in storage<br />

• Seed discolouration<br />

• Hot spots and Heating in storage<br />

• Respiration<br />

• Biochemical changes.<br />

• Loss in dry weight<br />

• mycotoxin production<br />

1. Seed discolouration<br />

Appearance is an important factor in grain grading, i.e. <strong>the</strong> grain's commercial<br />

quality.Seeds become distinctly discoloured during storage as a result <strong>of</strong> heating caused by<br />

internal fermentation. The most common storage fungi are species <strong>of</strong> Aspergillus and<br />

Penicillium.some <strong>of</strong> <strong>the</strong> seeds discolouration. Moulds growing on stored grain affect its<br />

appearance: dulling <strong>the</strong> kernel's normally bright appearance, discolouring <strong>the</strong> kernels, and<br />

producing white threadlike-mycelia on <strong>the</strong> kernels.For example, in corn ,Penicillium rot caused by<br />

Penicillium species is evident as discrete tufts or clumps or a blue-green or gray-green mold<br />

erupting through <strong>the</strong> pericarp <strong>of</strong> individual kernels or on broken kernels .Aspergillus flavus is<br />

evident as a greenish-yellow to mustard yellow, felt-like mold growth on or between kernels,<br />

especially adjacent to or in insect damaged kernels.<br />

2. Hot spots and heating in storage<br />

Stored grain insects and fungi commonly act toge<strong>the</strong>r to destroy grains and feeds. Mould<br />

can cause kernels to clump toge<strong>the</strong>r and obstruct <strong>the</strong> free flow <strong>of</strong> <strong>the</strong> grain during handling. The<br />

moisture and heat from <strong>the</strong>ir metabolic activity (respiration) will increase grain moisture and<br />

temperature which may lead to self-ignition.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

The moisture and warm temperatures <strong>of</strong> spoiling grain pockets will attract stored product<br />

pests such as rusty grain beetles and mites. If <strong>the</strong> hot spot develops in <strong>the</strong> fall, it may stay warm<br />

enough <strong>for</strong> <strong>the</strong> insects to over winter.<br />

Hot spots may occur when a pocket <strong>of</strong> grain is wetter than <strong>the</strong> rest <strong>of</strong> <strong>the</strong> stored grain due<br />

to improper storage. Mould can begin to grow in a pocket <strong>of</strong> moist grain or oilseeds and produce<br />

more heat and moisture. The resulting increase in temperature and moisture contents causes an<br />

increase in <strong>the</strong> growth and respiration <strong>of</strong> <strong>the</strong> moulds.<br />

3. Respiration<br />

During respiration <strong>the</strong> carbohydrates, C6 H12 O6, which make up most <strong>of</strong> <strong>the</strong> dry matter in<br />

<strong>the</strong> seed, are dissolved by enzymes and are consumed by moulds. This loss in dry matter causes<br />

a reduction in <strong>the</strong> marketable mass <strong>of</strong> grain. Respiration is <strong>of</strong> two types:<br />

Anaerobic<br />

For aerobic respiration to continue, oxygen must continue to diffuse into <strong>the</strong> bulk. If <strong>the</strong><br />

storage container is air tight and oxygen is flushed out or not replenished as it is consumed <strong>the</strong>n<br />

anaerobic processes may take over.<br />

Anaerobic<br />

Anaerobic processes can be desirable, such as in <strong>the</strong> fermentation <strong>of</strong> silage, but <strong>for</strong> most<br />

stored products anaerobic activity causes unacceptable odours, tastes, and o<strong>the</strong>r changes in <strong>the</strong><br />

product.<br />

The actual rate <strong>of</strong> heat production can vary considerably. If lipids are oxidized <strong>the</strong> amount<br />

<strong>of</strong> heat released is 3946 kJ/g as compared with 15.7 kJ/g <strong>for</strong> glucose (Multon 1988). If oxygen is<br />

absent and fermentation <strong>of</strong> glucose occurs, <strong>the</strong> heat released is about one-tenth <strong>of</strong> that released<br />

under aerobic conditions.<br />

4. Biochemical changes<br />

Invasion <strong>of</strong> fungi on grain or seeds bring about physical and biochemical changes. For<br />

example, in raddish seeds infected with Aspergillus flavus changes in amount <strong>of</strong> fatty acids,<br />

glycerol ,sugar and amino-acids were observed. Seed borne fungi in vegetables (Brassicaceae)<br />

brought about <strong>the</strong> reduction in chlorophyll, starch, total sugars and amino acids besides affecting<br />

enzymes. Wheat grains infected with fungi also have poor flour quality. The wheat grains infected<br />

with (Alternaria tenuis) black point have higher protein content and reduced potassium, calcium ,<br />

zinc and manganese in such grains. In food grains, during improper storage, are subject to mould<br />

attack and this is accelerated by insects under high moisture and temperature. Breakdown <strong>of</strong> fats<br />

causes an increase in free fatty acids, and oxidation brings on rancid flavours.In stored rice<br />

Aspergillus flavus and A. versicolour caused maximum reduction in carbohydrate contents.A. niger<br />

cause maximum reduction in oleic and linoleic acid in peanut seeds. (Vaidya and Dharma vir<br />

1989). The oil, from infected kernels, acrid smelling. Aspergillus flavus, Cladosporium herbarum<br />

and Botryodiplodia sp.caused loss in oil content in groundnut seeds<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

5. Loss in dry weight<br />

This respiration results in some loss <strong>of</strong> dry weight and produces <strong>the</strong> phenomenon called<br />

"spontaneous heating". In cereal grains loss in quality and quantity during storage is caused by<br />

fungi, insects, rodents and mites. Respiration may, in certain cases, contribute to a loss <strong>of</strong> dry<br />

matter during grain storage. However, <strong>the</strong> losses due to respiration are minor compared to those<br />

caused by living organisms.<br />

The weight loss generally adopted as a criterion <strong>of</strong> grain damage does not give a picture <strong>of</strong> actual<br />

loss, as <strong>the</strong> grains containing internal infestations are not detected in such analyses. Basic<br />

research is needed to find <strong>the</strong> relationship between weight loss and true loss in quality brought<br />

about by mould or by internal infestations with <strong>the</strong> insects.<br />

6. Catastrophic losses due to mycotoxin production in stored grains and feed<br />

Mould fungi when grow on stored grain in silos or in storage bins may lead to catastrophic<br />

losses as <strong>the</strong>y produce <strong>the</strong>ir secondary metabolites on stored grains which on consumption are<br />

health hazardous to man and animal. In <strong>the</strong> Midwest, in 1934 more than 5,000 horses died<br />

because <strong>of</strong> "moldy corn disease” on consumption <strong>of</strong> moldy grain.<br />

An outbreak <strong>of</strong> "Turkey X disease" in Great Britain in 1960 was traced to contaminated<br />

peanut meal from Brazil. Aflatoxin was indicated as <strong>the</strong> cause <strong>of</strong> <strong>the</strong> death <strong>for</strong> more than 100,000<br />

young turkeys and some 20,000 ducklings, pheasants, and partridge poults.<br />

In 1972, Gibberella ear rot caused extensive feed-refusal problems in swine in <strong>the</strong> Corn<br />

Belt. Aflatoxin has caused problems in several animal species in <strong>the</strong> sou<strong>the</strong>astern United States<br />

<strong>for</strong> many years, and fescue toxicosis due to a fungus, Acremonium coenophialum has been a<br />

common problem with fescue pastures in <strong>the</strong> South <strong>for</strong> many years.<br />

Human suffering from mycotoxicoses includes ergot poisoning associated with ingestion <strong>of</strong><br />

rye flour contaminated with ergot (holy fire, St. Anthony's fire); cardiac beriberi associated with<br />

Penicillium molds in rice (yellow rice toxins); and alimentary toxic aleukia (ATA,) associated with<br />

Fusarium molds on overwintered wheat, millet, and barley. Several mycotoxins have been linked<br />

to increased incidence <strong>of</strong> cancer in human beings. These include aflatoxin, sterigmatocystin<br />

zearalenone, patulin, ochratoxin, and fumonisin. Although <strong>the</strong> adverse effects <strong>of</strong> feeding moldy<br />

feeds was long known by livestock and poultry producers, a specific mycotoxin was not<br />

implicated.An outbreak <strong>of</strong> aflatoxicosis in India was linked to moldy corn containing aflatoxin, killing<br />

more than 100 persons and affecting more than 400 dogs.<br />

Mycotoxins have been found in four samples <strong>of</strong> seeds from 12 samples studied. In two <strong>of</strong> <strong>the</strong>m,<br />

<strong>the</strong> toxin level exceeded <strong>the</strong> allowable concentration: Aflatoxin B-I - 15 mg/kg, and Zearalenon -<br />

2,000 mkg/kg. Similarly, in three <strong>of</strong> five Soya samples imported from Spain, Aflatoxin B-1 20, 30<br />

mkg/kg was found, respectively, while in one, sterigmatosistin 150 mkg/kg was discovered ( 2004<br />

Seed trade Pakistan) .<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

7. Production <strong>of</strong> Mycotoxins<br />

Groundnut is one <strong>of</strong> <strong>the</strong> crops, which is vulnerable to attack <strong>of</strong> Aflatoxin. Aflatoxin may<br />

grow on Groundnut kernels, if <strong>the</strong> moisture content is above 8 to 9 percent. Aflatoxin <strong>of</strong>ten grows<br />

in ships cargo during transit <strong>of</strong> more than 4 to 6 weeks. Aflatoxin contamination <strong>of</strong> Groundnut is a<br />

major health hazard to human and animals and it is one <strong>of</strong> <strong>the</strong> most important constraints in<br />

Groundnut trade. The main reason <strong>for</strong> <strong>the</strong> contamination in Groundnut is due to poor pre-harvest<br />

and post-harvest practices like moisture stressed crop, stacking <strong>the</strong> pods/kernels in high humid<br />

conditions, which leads to growth <strong>of</strong> <strong>the</strong> fungus. In <strong>the</strong> international Groundnut trade, tolerance<br />

levels are specific <strong>for</strong> this quality parameter, with strict condition posed <strong>for</strong> Groundnut meant <strong>for</strong><br />

human consumption (4 ppb in Europe).<br />

<strong>Management</strong> <strong>of</strong> microorganisms during post harvest operations<br />

• Better crop husbandry practices<br />

• Preharvest control <strong>of</strong> diseases and pests in field<br />

• Appropriate harvest procedures<br />

• Drying <strong>the</strong> grains<br />

• Building <strong>of</strong> better storage facilities and control <strong>of</strong> storage atmosphere<br />

• Ensiling<br />

• Use <strong>of</strong> microbial antagonists<br />

• Use <strong>of</strong> Pesticides and fungicides rodenticides<br />

• Sanitation <strong>of</strong> stores be<strong>for</strong>e storage:<br />

• Use <strong>of</strong> grain protectants<br />

• Grain preservatives<br />

• Fumigation<br />

Ensiling a process in which microorganisms in storage are managed through promoting<br />

<strong>the</strong> o<strong>the</strong>r microorganisms in such away that <strong>the</strong>y may kill or stop <strong>the</strong> growth <strong>of</strong> <strong>the</strong> microorganisms<br />

that cause spoilage.To prevent micro-organic growth, grain must be handled like silage,<br />

which means promoting <strong>the</strong> growth <strong>of</strong> acid-producing bacteria in <strong>the</strong> absence <strong>of</strong> oxygen. A state <strong>of</strong><br />

preservation results when <strong>the</strong> acids, produced without oxygen, kill <strong>the</strong> o<strong>the</strong>r microorganisms in<br />

such away that <strong>the</strong>y may kill or stop <strong>the</strong> growth <strong>of</strong> <strong>the</strong> micro-organisms that cause spoilage.<br />

Combined rolling and packing result in <strong>the</strong> rapid exclusion <strong>of</strong> oxygen, which creates a favorable<br />

environment <strong>for</strong> acid <strong>for</strong>ming micro-organisms.<br />

Microbial Antagonists<br />

Microbial Antagonists <strong>for</strong> storage microorganisms are not yet well understood. However,<br />

<strong>the</strong> researches that has been done has yielded exciting and promising results, and <strong>the</strong> study <strong>of</strong><br />

microbial antagonists has become a rapidly expanding field in plant pathology.<br />

As a result <strong>of</strong> public concerns about <strong>the</strong> safety <strong>of</strong> our environment and food supply, it has<br />

become a national research priority to develop new pest management technologies that reduce<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

our use <strong>of</strong> chemical pesticides and microbial antagonists is an alternative.<br />

Microorganisms naturally present in agricultural ecosystems are being studied as<br />

environmentally compatible alternatives to traditional chemical methods <strong>for</strong> controlling plant<br />

diseases. A serious impediment to bringing many such microorganisms discovered by ARS<br />

scientists to <strong>the</strong> marketplace is <strong>the</strong> lack <strong>of</strong> knowledge <strong>of</strong> cultivation and <strong>for</strong>mulation technologies<br />

needed to produce cells that are tolerant to <strong>the</strong> stresses <strong>of</strong> large-scale cultivation, separation,<br />

processing (drying or dewatering biomass), and storage. There is need to focus upon <strong>the</strong> studies<br />

to discover <strong>the</strong> genetic and metabolic mechanisms that enhance microbial stress tolerance such<br />

that high yields <strong>of</strong> viable effective cells with long shelf lives can be produced.To be most effective,<br />

antagonists <strong>of</strong> plant disease and food spoilage should be:<br />

‣ genetically stable<br />

‣ effective at low concentrations<br />

‣ easy to culture and amenable to growth on an inexpensive medium<br />

‣ effective against a wide range <strong>of</strong> pathogens in a variety <strong>of</strong> systems<br />

‣ prepared in an easily distributable <strong>for</strong>m<br />

‣ non-toxic to humans<br />

‣ resistant to pesticides<br />

‣ compatible with o<strong>the</strong>r treatments (physical and chemical)<br />

‣ non-pathogenic against <strong>the</strong> host plant<br />

These antagonists have been applied to <strong>the</strong> above-ground parts <strong>of</strong> plants, to <strong>the</strong> soil (and<br />

roots), and to plant seeds. The above-ground environment is <strong>the</strong> least stable <strong>for</strong> antagonists<br />

because <strong>of</strong> <strong>the</strong> extreme variability in moisture and nutrients. <strong>Soil</strong> is more stable environment <strong>for</strong><br />

microbiota, but soil in most fields is generally nutrient poor, pH may range from 4-8, and<br />

temperatures and moisture may vary widely. In contrast, greenhouse planting mixes can be<br />

managed more effectively to promote antagonist colonization. Finally, it is practical to treat seeds<br />

to favour microbial antagonists.<br />

a. Biological seed treatments<br />

Biological seed treatments control seed pests by parasitizing <strong>the</strong> pest organisms,<br />

competing <strong>for</strong> food on <strong>the</strong> root system, or producing toxic compounds that inhibit pathogen growth.<br />

Control <strong>of</strong> surface pathogens include beneficial microbes in compost teas, herbal sprays,<br />

washes or oils, hot water, heat, and disinfectants.<br />

1. Microbial seed treatment<br />

2. Biodynamic Treatments<br />

3. Herbal Treatments<br />

4. Hot Water Bath<br />

5. Disinfectants<br />

Knowledge <strong>of</strong> <strong>the</strong> interactions among microorganisms and ways to manipulate microbiota<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

is growing as research in this field rapidly expands. Antagonists have been successfully used to<br />

suppress tomato mosaic, foot and butt rot <strong>of</strong> conifers, citrus tristeza disease, and crown gall <strong>of</strong><br />

several crops.<br />

Seeds have been coated with antagonists that reduce infection by pathogens and also<br />

enhance plant growth. The most commonly applied antagonists to <strong>the</strong> seeds are Bacillus subtilis,<br />

Chateomium sp.Penicillium oxalicum and Trichoderma species. Biopriming <strong>of</strong> infected carrot seed<br />

with an Antagonist, Clonostachys rosea, has been selected <strong>for</strong> Control <strong>of</strong> Seedborne Alternaria<br />

spp.<br />

Biological fungicides are a relatively new tool available. Biological fungicides contain beneficial<br />

bacteria or fungi (microbial antagonists) which help suppress pathogens that cause plant disease.<br />

For example, F-Stop, registered as a seed treatment <strong>for</strong> tomatoes, contains a biocontrol agent<br />

called Trichoderma viride sensu. T-22G Biological <strong>Plant</strong> Protectant Granules, registered as an<br />

in-furrow soil treatment on tomatoes and o<strong>the</strong>r vegetables, contains Trichoderma harzianum,<br />

strain KRL-AG2.<br />

Commercial <strong>for</strong>mulations <strong>of</strong> microbial agents <strong>for</strong> treatment<br />

Kodiak concentrate registered <strong>for</strong> seed and pod vegetables, soybeans, wheat and barley,<br />

and corn plus all o<strong>the</strong>r agricultural seeds, contains Bacillus subtilis bacteria which colonize <strong>the</strong><br />

developing root system, suppressing disease organisms such as Fusarium, Rhizoctonia, Alternaria<br />

and Aspergillus that attack root systems.<br />

When used with a chemical seed treatment, <strong>the</strong> combination <strong>of</strong> chemicals and Kodiak<br />

provides protection to <strong>the</strong> root <strong>for</strong> a much longer time than with chemicals alone.<br />

As <strong>the</strong> root system develops, <strong>the</strong> bacteria grow with <strong>the</strong> roots extending <strong>the</strong> protection<br />

throughout <strong>the</strong> growing season. As a result <strong>of</strong> this biological protection, a vigorous root system is<br />

established by <strong>the</strong> plant, which <strong>of</strong>ten results in more uni<strong>for</strong>m stands and greater yields<br />

Bio-Seed-Gard is an OMRI-approved blend <strong>of</strong> micro-organisms <strong>for</strong> use as a seed<br />

treatment <strong>for</strong> Corn, Soybeans, Peas, Legumes, and o<strong>the</strong>r crops. AgriEnergy Resources, <strong>the</strong> Co.<br />

that developed <strong>the</strong> product, has done greenhouse and field trials showing improved: seeding vigor,<br />

stand establishment, root growth, plant growth, and yield. Dry blend <strong>of</strong> Trichoderma & Mycorrhizal<br />

species.<br />

CB-QGG is a liquid biological seed treatment and root growth promoter <strong>for</strong>mulated with<br />

beneficial microbes, macro and micro nutrients, amino acids, organic acids, root growth stimulants,<br />

enzymes, proteins, vitamins and minerals. CB-QGG makes less available <strong>for</strong>ms <strong>of</strong> soil phosphate<br />

available to plants, promotes nitrogen fixation, root development and quick emergence, stimulates<br />

cell division and increases stress tolerance. In addition, CB-QGG it produces substances which<br />

increase <strong>the</strong> vigor <strong>of</strong> treated plants helping <strong>the</strong>m resist damage by pathogenic fungi and damping<br />

<strong>of</strong>f. This results in a more consistent plant stand and increased yields. CB-QGG promotes early<br />

root growth and larger roots. Larger roots provide better access to moisture and nutrients which<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

translates into improved health throughout <strong>the</strong> life cycle <strong>of</strong> <strong>the</strong> crop.<br />

b. Biodynamic (Seed Soaks and Sprays)<br />

Biodynamic preparations are used to enhance <strong>the</strong> biological activity <strong>of</strong> <strong>the</strong> soil. The<br />

preparations consist <strong>of</strong> mineral, plant, or animal manure extracts, usually fermented and applied in<br />

small proportions to compost, manures, <strong>the</strong> soil, or directly onto plants, after dilution and stirring<br />

procedures called dynamizations. The preparations are used a seed soak to encourage<br />

germination and growth <strong>of</strong> seedlings and <strong>for</strong> anti-fungal control. The solutions are lightly sprayed<br />

on seeds and <strong>the</strong>n quick dried on a screen.<br />

Methods <strong>for</strong> Preparations<br />

They are numbered 500 to 508. BD#500 is made from cow manure fermented in a bovine<br />

horn and buried <strong>for</strong> six months through autumn and winter. It is used as a soil spray to stimulate<br />

root growth and <strong>the</strong> production <strong>of</strong> humus.<br />

BD#501 is <strong>the</strong> horn silica preparation made from powdered quartz packed into a cow horn<br />

and buried in <strong>the</strong> soil through spring and summer <strong>for</strong> six months. It is used as a plant spray <strong>for</strong> <strong>the</strong><br />

stimulation and regulation <strong>of</strong> growth.<br />

BD#502 - 507 are compost inoculates and are inserted into <strong>the</strong> compost piles to increase<br />

microbial activity, enhancing <strong>the</strong> decomposition process.<br />

They are made from <strong>the</strong> fermented herbs yarrow (Achillea millefolium), chamomile<br />

(An<strong>the</strong>mis nobilis), stinging nettle(Urtica dioica), oak bark (Quercus alba), dandelion (Taraxacum<br />

<strong>of</strong>ficinale), and valerian (Valariana <strong>of</strong>ficinalis), respectively. Each preparation stimulates processes<br />

essential <strong>for</strong> plant growth and are used to streng<strong>the</strong>n <strong>the</strong> life <strong>for</strong>ces on <strong>the</strong> farm.<br />

Natural Products<br />

Considerable research activity has occurred in <strong>the</strong> Asian-Pacific region on <strong>the</strong> potential <strong>for</strong><br />

plant extracts to control seed-borne fungi. The oils <strong>of</strong> cassia and clove inhibited growth <strong>of</strong><br />

established seed borne infections <strong>of</strong> Aspergillus flavus, Curvularia pallescens and Chaetomium<br />

indicum in maize (Chatterjee 1990).<br />

Aqueous extracts <strong>of</strong> Strychnos nux-vomica, garlic bulbs, ginger rhizomes, basil leaves, and<br />

fruits <strong>of</strong> Azadirachta indiica were used to control Alternaria padwickii in rice seeds (Shetty et al<br />

1989), while extracts from peppermint and garlic reduced rice seed infection by Cochliobolus<br />

miyabeanus (Alice and Rao 1986).<br />

Garlic bulb extract inhibited <strong>the</strong> spore germination and mycelial growth <strong>of</strong> seed-borne<br />

fungal pathogens <strong>of</strong> jute, including Macrophomina phaseolina, Botryodiplodia <strong>the</strong>obromae and<br />

Colletotrichum corchori (Ahmed and Sultana 1984).<br />

Homeopathic drugs, Filixmas and Blatta orientalis, completely suppressed <strong>the</strong> population<br />

<strong>of</strong> Fusarium oxysporum in <strong>the</strong> seed myc<strong>of</strong>lora <strong>of</strong> wheat (Raka et al. 1989).<br />

Aspergillus ruber infection and weevil oviposition <strong>of</strong> Zabrotes subfaciatus were reduced by<br />

mineral oil and soybean oil treatment <strong>of</strong> dry beans stored in Ecuaddor (Hall and Harman 1991).<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Soybean oil, applied at a rate used to suppress grain dust, reduced storage fungi growth in<br />

maize and soybeans during 12 months in field storage bins in Iowa (McGee et al 1989, White and<br />

Toman 1994).<br />

BD 500 The vegetable seeds are treated with BD 500 <strong>for</strong> about 12 an hour and dried in <strong>the</strong><br />

shade <strong>for</strong> about 1 hour. The seeds are <strong>the</strong>n sown in <strong>the</strong> beds. Healthy plants are obtained and <strong>the</strong><br />

germination <strong>of</strong> seeds is very good. Seeds treated with this method include Cowpea, Okra, Radish,<br />

Beans.<br />

It may be concluded that Microorganisms naturally present in agricultural ecosystems are<br />

environmentally compatible alternatives to traditional chemical methods <strong>for</strong> controlling storage pest<br />

and diseases and <strong>for</strong> seed treatment in organic seed production in particular. A serious<br />

impediment to bring many such microorganisms to <strong>the</strong> marketplace is <strong>the</strong> lack <strong>of</strong> knowledge <strong>of</strong><br />

cultivation and <strong>for</strong>mulation technologies needed to produce cells that are tolerant to <strong>the</strong> stresses <strong>of</strong><br />

large-scale cultivation, separation, processing (drying or dewatering biomass), and storage. Ther<br />

is every scope <strong>of</strong> indegineous natural plant extracts to be effective means <strong>for</strong> maenagement <strong>of</strong><br />

storage disease and pests.<br />

- 115 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Reduced Risk Pesticides: The Best Alternative to Ensure Food<br />

Safety without Compromising Environment Quality<br />

S.N. Tiwari<br />

Department <strong>of</strong> Entomology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

What are Conventional Reduced Risk Pesticides<br />

Pesticides that pose less risk to human health and <strong>the</strong> environment than existing<br />

conventional alternatives which are<br />

• neurotoxins,<br />

• carcinogens,<br />

• reproductive and developmental toxicants,<br />

• groundwater contaminants<br />

Advantages <strong>of</strong> Conventional Reduced Risk Pesticides<br />

• Low impact on human health<br />

• Lower toxicity to non-target organisms (birds, fish, plants)<br />

• Low potential <strong>for</strong> groundwater contamination<br />

• Low use rates<br />

• Low pest resistance potential<br />

• Compatibility with IPM<br />

In<strong>for</strong>mation required <strong>for</strong> Reduced Risk Assessment<br />

• Executive summary <strong>of</strong> chemical<br />

• Human health effects<br />

• Environmental fate and effects<br />

• O<strong>the</strong>r hazards<br />

• Pest resistance and management (e.g., IPM)<br />

• Risk comparisons to registered alternatives<br />

• Comparative per<strong>for</strong>mance<br />

Factors considered to grant Reduced Risk Status<br />

Human health effects<br />

• very low mammalian toxicity<br />

• toxicity generally lower than alternatives (10-100X)<br />

• displaces chemicals that pose potential human health concerns e.g., OPs, probable<br />

carcinogens<br />

• reduces exposure to mixers, loaders, applicators and re-entry workers<br />

Classification <strong>of</strong> Pesticides :<br />

Classification <strong>of</strong> <strong>the</strong><br />

insecticides<br />

Medium lethal dose by<br />

<strong>the</strong> oral route (acute<br />

toxicity) LD 50 mg/kg.<br />

Body weight <strong>of</strong> test<br />

animals<br />

Medium lethal dose by<br />

<strong>the</strong> dermal route<br />

(derma toxicity) LD 50<br />

mg/kg. Body weight <strong>of</strong><br />

test animals<br />

1. Extremely Toxic 1-50 1-200 Bright red<br />

Colour <strong>of</strong> identification<br />

band on <strong>the</strong> label<br />

- 116 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

2. Highly toxic 51-500 201-2000 Bright yellow<br />

3. Moderately toxic 501-5000 2001-20000 Bright blue<br />

4. Slightly toxic More than 5000 More than 20000 Bright green<br />

Factors considered granting Reduced Risk Status<br />

Non-target organism effects (birds)<br />

• very low toxicity to birds<br />

• very low toxicity to honeybees<br />

• significantly less toxicity/risk to birds than alternatives<br />

• not harmful to beneficial insects, highly selective pest<br />

impacts<br />

Factors considered granting Reduced Risk Status<br />

Non-target organism effects (fish)<br />

• very low toxicity to fish<br />

• less toxicity/risk to fish than alternatives<br />

• potential toxicity/risk to fish less harsh<br />

• similar toxicity to fish as alternatives but significantly less exposure<br />

Factors considered to grant Reduced Risk Status<br />

Groundwater (GW)<br />

• low potential <strong>for</strong> GW contamination<br />

• low drift, run<strong>of</strong>f potential<br />

• run<strong>of</strong>f mitigatable<br />

Factors considered to grant Reduced Risk Status<br />

General factors<br />

• Lower use rates than alternatives, fewer applications<br />

• Low pest resistance potential<br />

• i.e. new mode <strong>of</strong> action<br />

• Highly compatible with IPM<br />

• Efficacy<br />

• Phytotoxicity<br />

Reduced Risk Insecticides<br />

Active ingredient<br />

Hexaflumuron<br />

Noviflumuron<br />

Tebufenozide<br />

Site <strong>of</strong> application<br />

Below and above ground termite bait stations<br />

Above ground bait station<br />

Cotton, Sugarcane, Mustard, Leafy veg., Brassica leafy veg,<br />

Fruiting veg., Tuberous & Corm vegetable, Turnip, Citrus,<br />

Grape, Walnut, Pome fruit, Berry crop group, Mint, tree nuts,<br />

Pecan, <strong>for</strong>estry, ornamentals,<br />

- 117 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Bupr<strong>of</strong>ezin<br />

Indoxacarb<br />

Novaluron<br />

Acetamiprid<br />

Lambda-cyhalothrin<br />

Clothianidin<br />

Lufenuron<br />

Dinotefuran<br />

Methoxyfenozide<br />

Spiromesifen<br />

Et<strong>of</strong>enprox<br />

Spinosad<br />

Spinetoram<br />

Rice, Cotton, Mango, Grape, Chilies, cucurbit veg., head<br />

lettuce, almond, citrus, grape, tomato, bean (succ.), lychee<br />

fruits, pistachio, avocado, guava, peach, pome fruit, sugar<br />

apple<br />

Cotton, Cabbage, Chilies, Tomato, Pigeon pea, fruiting veg.,<br />

brassica leafy veg., lettuce, sweet corn, pome fruit, alfalfa,<br />

peanut, potato, Soybean, fire ant bait, grape,<br />

Cotton, Cabbage, Tomato, Chilli, Gram, Apple, Pear, Peach,<br />

Plum, Blueberries Ornamentals,<br />

Cotton, Rice, pome fruit, citrus, grapes, brassica leafy veg.,<br />

leafy veg. (excl.brassica), fruiting veg.,Ornamentals, potato,<br />

Cotton, Rice, Brinjal, Tomato, Chilli, Pigeon pea, Chick pea,<br />

Onion, Okra, Groundnut, Mango, legume vegetables, fruiting<br />

vegetables, sugarcane, termite barrier,<br />

Rice, Cotton, Canola, Corn (seed treatments),<br />

Cotton, Pigeon pea, Cabbage, Cauliflower, Termite bait station<br />

Rice, leafy vegetables, cotton, brassica head & stem<br />

subgroup, cucurbit vegetables, fruiting vegetables, grape,<br />

potato, Brassica leafy greens, Turnip (greens)<br />

Cotton, pome fruit, fruiting vegetables, grapes, brassica leafy<br />

vegetables,leafy vegetables, corn, stone fruit, tree nuts,<br />

cucurbits, okra, pea , soybean<br />

Brassica leafy vegetables, corn (field), cotton,cucurbits, fruiting<br />

vegetables, leafy greens, ornamentals, strawberry, tuberous &<br />

corm vegetables, tomato, bean, pea<br />

Rice<br />

Cotton, red gram, cereal grains, corn, oat, barley, millet, grain<br />

amaranth, peanut, Brassica leafy veg., Cabbage, Cauliflower,<br />

fruiting veg., leafy veg., cucurbit veg., Chillies, legume veg,<br />

leaves <strong>of</strong> root and tuber veg., okra, onion, turnip greens,<br />

asparagus, garden beet sugar beet (root), alfalfa, fruit fly bait,<br />

mint, Tropical fruit, almond, pistachio,apple, pome fruit, citrus,<br />

stone fruit, nuts, berry group, fig, grape, Non-grass animal feed<br />

Amaranth, pome fruit, stone fruit, artichoke, asparagus,<br />

avocado, banana, head & stem Brassica; Brassica leafy<br />

greens; bulb vegetables; bushberry; caneberry; cereal grains<br />

(ex. rice, sorghum, millet); cherimoya; citrus; corn (sweet);<br />

cotton; cranberry; cucurbit vegetables; custard apple; fig;<br />

foliage <strong>of</strong> legume vegetables; fruiting vegetables; grape;<br />

guava; juneberry; leafy vegetables; leaves <strong>of</strong> root & tuber<br />

vegetables; legume vegetables, lychee; mango; mint;okra;<br />

papaya; pea & bean, dried, soybean, pea & bean, peanut;<br />

pistachio; root & tuber vegetables; sorghum; lime; star apple;<br />

star fruit; strawberry; sugar apple; tree nuts; watercress,<br />

- 118 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Chlorantraniliprole<br />

Spirotetramat<br />

Tolfenpyrad<br />

Bifenazate<br />

Cotton, Rice, Sugarcane, Cabbage, Grape, Pome Fruit,<br />

Potato, Stone Fruit, Brassica Leafy Vegetables, Cucurbit<br />

Vegetables, Fruiting Vegetables, Leafy Vegetables, Turf,<br />

Ornamentals, Tree Nuts, Pistachio, Artichoke, Asparagus,<br />

Caneberry, Cacao, Citrus,C<strong>of</strong>fee, Corn (field,sweet, pop), Fig;<br />

Forage,Fodder & Straw <strong>of</strong> Cereal Grains; Grass<br />

Forage,Fodder, & Hay; Herbs & Spices; Hops; Legume<br />

Vegetables (ex. soybean); Mint; Non-grass Animal Feeds;<br />

Oilseed Crops; Okra; Olive; Peanut; Pomegranate; Prickly<br />

Pear Cactus; Rice; Small Vine-climbing Fruits; Strawberry;<br />

Sugarcane; Tea; Tobacco; Tropical Fruits; Tuberous & Corm<br />

Vegetables, Termiticide Use<br />

Almond, Brassica Head & Stem Vegetables, Brassica Leafy<br />

Greens, Citrus, Cucurbits, Fruiting Vegetables, Grape, Hops,<br />

Leafy Vegetables, Onion, Pome Fruit, Stone Fruit,Strawberry,<br />

Tree Nuts, Tuberous & Corm Vegetables<br />

Ornamentals<br />

Ornamentals, stone fruit, edible-podded pea, tuberous & corm<br />

vegetables<br />

Acequinocyl Ornamentals, strawberry, almond, citrus, pome fruit, field<br />

ornamentals,<br />

Etoxazole<br />

Fenpyroximate<br />

Cl<strong>of</strong>entezine<br />

Tolfenpyrad<br />

Cotton, pome fruit, strawberry, grape, tree nuts,<br />

Ornamentals, cotton, grape, pome fruit, citrus, hops, mint,<br />

pistachio, tree nuts<br />

Grape<br />

Ornamentals<br />

OP Alternative Insecticides:<br />

Fipronil<br />

Thiamethoxam<br />

Imidacloprid<br />

Emamectin benzoate<br />

Clothianidin<br />

Chlorfenapyr<br />

Cotton, Rice, Sugarcane, Cabbage, Chilli, home lawn, golf<br />

course, commercial and recreational turf and sod farms (fire<br />

ant), potting medium mixtures (fire ant), turf (homeowner,<br />

commercial; fire ant),<br />

Seed treatment (Cotton, Sorghum, Wheat, Okra, Barley,<br />

Canola, Sunflower )<br />

Foliar (Cotton, Rice, Wheat, Mustard, Mango, Potato, Tomato,<br />

Brinjal, Tea, Citrus, cucurbit veg., fruiting veg., pome fruit,<br />

tuberous and corm veg., ornamentals, beans, stone fruit; mint,<br />

Seed treatment : Cotton, Rice, Sugarcane, Okra, Sunflower,<br />

Sorghum, Pearl millet, Chilli, Mustard, Foliar: Cotton, Rice,<br />

Sugarcane, Sunflower, Okra, Chilli, Mango, Citrus, Groundnut<br />

Cotton, Red gram, Chick pea, Brinjal, Okra, Cabbage, Chilli<br />

Rice, Cotton, Turf, Ornamentals, Pome fruit, Tobacco,<br />

Cabbage, Chili , Post construction control <strong>of</strong> termites<br />

- 119 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Zeta-Cypermethrin<br />

Flonicamid<br />

Gamma-cyhalothrin<br />

Novaluron<br />

Deltamethrin<br />

Pymetrozine<br />

Etoxazole<br />

Alfalfa, corn (field, pop, sweet), head and stem brassica veg.,<br />

leafy brassica greens, leafy veg., onion (green), sugar beet,<br />

sugarcane, rice<br />

Ornamentals, cotton, cucurbit vegetables, fruiting vegetables,<br />

pome fruit, potato, stone fruit, nursery & landscape ornamentals,<br />

head & stem Brassica,<br />

Wheat, alfalfa, Brassica head & stem subgroup, canola, corn<br />

(field, sweet), cotton, fruiting vegetables, garlic, legume<br />

vegetables (ediblepodded) subgroup, lettuce (head, leaf), tree<br />

nuts, onion (dry bulb), pea and bean dry shelled (except<br />

soybean) subgroup, pea and bean succulent shelled subgroup,<br />

peanut, pome fruit, rice, sorghum, soybean, stone<br />

fruit,sugarcane, sunflower,<br />

Cotton, Cabbage, Tomato, Chili, Bengal gram, pome fruit<br />

Corn, cucurbit vegetables, fruiting vegetables, onion , pome<br />

fruit, root & tuber vegetables, sorghum, tree nuts<br />

Asparagus<br />

Grape, tree nuts<br />

Reduced Risk Bird Repellent :<br />

Methyl Anthranilate<br />

Cherry, blue berry, grape, <strong>for</strong>estry<br />

Reduced Risk Fungicides<br />

Hymexazol<br />

Fludioxonil<br />

Mefenoxam (Metalaxyl-M)<br />

Azoxystrobin<br />

Sugar beet (seed treatment)<br />

Corn , strawberry, bulb vegetables, turf, caneberry, pistachio,<br />

stone fruit<br />

Maize, Millet, Sorghum, Sunflower, Mustard, Citrus, Cotton,<br />

Leafy vegetables, Nonbearing deciduous fruits and nuts and<br />

peanuts<br />

Wheat, barley, rice, oat, pea, onion, carrot, beans, potato,<br />

oilseed, grape, banana, peach, tomato, pecan, peanut ,almond,<br />

cucurbit veg, canola, potato, stone fruit, citrus, corn, cotton,<br />

leafy veg, root and tuber veg., soybean, leafy brassica greens,<br />

bushberry, eggplant, grass (grown <strong>for</strong> seed), jackfruit,<br />

juneberry, lingonberry, loquat, mint (spearmint, peppermint),<br />

okra, pawpaw, pepper, persimmon, salal, strawberry, tamarind,<br />

tropical fruit, turnip(greens), watercress, waxjambu, white<br />

sapote, legume vegetables, artichoke (globe), asparagus, head<br />

& stem Brassica subgroup, herbs, spices, safflower,<br />

Sunflower, Tomato, Chili, Mango<br />

- 120 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Cyprodinil<br />

Fenhexamid<br />

Trifloxystrobin<br />

Zoxamide<br />

Fludioxonil<br />

Fluazinam<br />

Stone fruit, onion (dry bulb & green),Strawberry, bushberry,<br />

caneberry,<br />

pistachio, watercress, Brassica leafy vegetables,carrot, herbs,<br />

lychee fruits<br />

Grape, strawberry, ornamentals, almond, stone fruit, pear,<br />

pepper, pomegranate<br />

Pome fruit, grape, cucurbit veg., root vegetable, peanut, turf,<br />

banana, ornamentals, almond, fruiting veg., hops, potato, sugar<br />

beet, wheat, ornamentals, citrus, corn (field, pop),pecan, rice,<br />

stone fruit, barley, oats,<br />

Grape, cucurbit veg., tomato,<br />

Potato, Strawberry, bulb vegetables<br />

Seed treatments (brassica leafy veg., bulb veg., cereal grains,<br />

cotton, cucurbit veg., foliage <strong>of</strong> legume veg., fruiting veg., grass,<br />

herbs and spices, leafy veg., leaves and roots <strong>of</strong> tuber veg.,<br />

legume veg., non-grass animal feeds, peanut, rape seed, root<br />

and tuber veg., sunflower)<br />

Groungnut, Potato<br />

Fenamidone Lettuce, cucurbit vegetables, onion, potato, Tomato,<br />

ornamentals, Grape<br />

Boscalid<br />

Fenhexamid<br />

Quinoxyfen<br />

Pyrimethanil<br />

Cyaz<strong>of</strong>amid<br />

Flazasulfuron<br />

Berries, bulb vegetables, canola, fruiting vegetables, grape,<br />

legume vegetables, lettuce (head,leaf), peanut, root vegetables<br />

(except sugar<br />

beet, garden beet, radish, turnip), stone fruit,strawberry, tree<br />

nuts, tuberous & corm vegetables, turf, celery, spinach,<br />

Cucumber (greenhouse), fruiting vegetables, kiwifruit, leafy<br />

green subgroup (except spinach), stone fruit<br />

grape, cherry, lettuce, melons, pepper, strawberry<br />

Almond, grape, onion (dry bulb, green), pome fruit, stone fruit,<br />

strawberry, tomato, tuberous & corm vegetables<br />

Cucurbit vegetables, potato, tomato, Fruiting Vegetables, Grape<br />

(regional tolerance), Okra, Brassica Leafy Vegetables, Hops,<br />

Spinach, Turnip (greens)<br />

Turf<br />

Mandipropamid Brassica leafy vegetables, bulb vegetables, cucurbit<br />

vegetables, fruiting vegetables, grape, tuberous & corm<br />

vegetables, leafy vegetables<br />

Reduced Risk Herbicide<br />

Flumiclorac-pentyl<br />

Imazapic<br />

Metolachlor<br />

Imazamox<br />

Corn, soybean, cotton defoliant use<br />

Peanut<br />

Soybean<br />

Soybean, alfalfa, canola, legume veg., wheat,<br />

- 121 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Carfentrazone-ethyl<br />

Diflufenzopyr<br />

Glyphosate<br />

s-Dime<strong>the</strong>namid<br />

Carfentrazone-ethyl<br />

Flucarbazone sodium<br />

Prohexadione calcium<br />

Butafenacil<br />

Cyhal<strong>of</strong>op-butyl<br />

Imazethapyr<br />

Glufosinate ammonium<br />

Fluroxypyr<br />

Mesosulfuron methyl<br />

Penoxsulam<br />

Wheat, corn, cotton (defoliant use), turf,<br />

Corn, Grass<br />

Glyphosate-tolerant corn, canola, sugar beet, animal feed, nongrass<br />

group (exc. alfalfa); aloe vera; artichoke, globe; bamboo<br />

shoots; betelnut; buffalo gourd; chaya; crambe, seed; custard<br />

apple; flax; foliage <strong>of</strong> legume veg.; galangal root; ginger, white<br />

(flower); plum; grass, <strong>for</strong>age, fodder and hay group; herb and<br />

spices group; leafy veg.; leaves <strong>of</strong> root and tuber veg.; mustard<br />

seed; okra; palm heart; palm oil; papaya, pepper leaf; root and<br />

tuber veg.; sesame seed; Spanish lime; stevia (leaves); cherry;<br />

water spinach<br />

Non-crop area, Tea<br />

Corn, soybean, peanut<br />

Cereal grains, Wheat<br />

Wheat<br />

Apple<br />

Cotton<br />

Rice<br />

Rice, Soybean, Groundnut<br />

Rice, Tea<br />

Corn<br />

Wheat (along with Iodosulfuron Methyl Sodium)<br />

Rice, turf, Grape, Tree Nuts<br />

Bispyribac-sodium<br />

Mesotrione<br />

Pinoxaden<br />

Saflufenacil<br />

Aminopyralid<br />

Fluthiacet-methyl<br />

Alternative)<br />

(OP<br />

Rice, Turf<br />

Sugarcane, Corn, Turf, Berry group, Flax, Asparagus, Grass,<br />

Oat, Okra, Sorghum,<br />

Barley, wheat<br />

Cereal Grains; Citrus; Cotton; Foliage <strong>of</strong> Legume Vegetables;<br />

Forage, Fodder, & Straw <strong>of</strong> Cereal Grains; Grape; Legume<br />

Vegetables; Pome Fruit; Stone Fruit; Sunflower; Tree Nuts<br />

Range & pasture lands, rights <strong>of</strong> way, roadsides, industrial<br />

vegetation management<br />

Cotton<br />

Fur<strong>the</strong>r Risk Reduction<br />

• By Selectivity<br />

Action Required<br />

• Introduction <strong>of</strong> concept<br />

• Subsidy on RR Pesticides<br />

- 122 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Trichoderma as Inducer <strong>of</strong> <strong>Plant</strong> Resistance to Diseases<br />

R.P. Singh & Bhanu Pratap Bhadauria<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Trichoderma spp. is fungi that are present in nearly all agricultural soils and in o<strong>the</strong>r<br />

environments such as decaying wood. The antifungal abilities <strong>of</strong> <strong>the</strong>se beneficial microbes have<br />

been known since <strong>the</strong> 1930s, and <strong>the</strong>re have been extensive ef<strong>for</strong>ts to use <strong>the</strong>m <strong>for</strong> plant disease<br />

control since <strong>the</strong>n. Trichoderma species are among <strong>the</strong> most widely used biological control agents<br />

against soil borne plant pathogens. Biological control mechanisms <strong>of</strong> this fungus are competition,<br />

antibiosis and parasitism. In fact, we do not know whe<strong>the</strong>r most <strong>of</strong> <strong>the</strong> benefits <strong>of</strong> Trichoderma<br />

occur because <strong>the</strong>y directly attack and control disease-causing fungi, as has long been believed,<br />

or because <strong>the</strong>y have direct effects upon plants. Many recent findings suggest that plant<br />

development and biochemistry are strongly affected by Trichoderma strains. The capability <strong>of</strong> T.<br />

harzianum to promote increased growth response has been established. A 30% increase in<br />

seedling emergence and 95% increase in root area have been reported. It is also known to<br />

stimulated nutritional adsorption (Harman et al., 2004). Specific strains <strong>of</strong> fungi in <strong>the</strong> genus<br />

Trichoderma colonize and penetrate plant root tissues and initiate a series <strong>of</strong> morphological and<br />

biochemical changes in <strong>the</strong> plant, considered to be part <strong>of</strong> <strong>the</strong> plant defense response, which in<br />

<strong>the</strong> end leads to induced systemic resistance (ISR) in <strong>the</strong> entire plant. Until recently, research on<br />

Trichoderma-plant interactions focused mostly on mycoparasitic aspects <strong>of</strong> plant protection. Only a<br />

few studies so far have dealt with plant defense responses induced by Trichoderma (Chang et al.<br />

1997; Yedidia et al. 1999; Yedidia et al. 2000; Martinez et al. 2001). Considering that Trichoderma<br />

acts in rhizosphere, <strong>the</strong> effect <strong>of</strong> native <strong>for</strong>mulations <strong>of</strong> <strong>the</strong> mycoparasite on defense responses in<br />

plant leaves has been a neglected aspect in plant resistance studies.<br />

<strong>Plant</strong>s possess various inducible defense mechanisms <strong>for</strong> protection against pathogen<br />

attack. An example <strong>of</strong> this is systemic acquired resistance (SAR), which is activated by a wide<br />

range <strong>of</strong> pathogens, especially (but not only) those that cause tissue necrosis. Similarly,<br />

colonization <strong>of</strong> plant roots by certain non pathogenic rhizobacteria can induce systemic resistance<br />

(ISR) in <strong>the</strong> host plant. Both pathogen-induced SAR and rhizobacteria-mediated ISR are effective<br />

against different types <strong>of</strong> pathogens, and are typically characterized by a restriction <strong>of</strong> pathogen<br />

growth and a suppression <strong>of</strong> disease development compared with primary infected, non-induced<br />

plants. However, <strong>the</strong> signaling pathways controlling pathogen-induced SAR and rhizobacteriamediated<br />

ISR differ. Whereas SAR requires endogenous accumulation <strong>of</strong> salicylic acid (SA), <strong>the</strong><br />

signalling pathway controlling ISR functions independently <strong>of</strong> SA and requires intact<br />

responsiveness to <strong>the</strong> plant hormones jasmonic acid (JA) and ethylene. Additionally, it has been<br />

established that accumulation <strong>of</strong> phytoalexins and o<strong>the</strong>r low molecular weight antimicrobial<br />

metabolites is integral to plant protection. The chemical structures <strong>of</strong> phytoalexins vary among<br />

different plant families and include flavonoids, terpenoids and indoles (Darvill and Albersheim ,<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

1984).<br />

Processes Involved in Induced Systemic Resistance<br />

Perception by plant cells <strong>of</strong> elicitors produced by <strong>the</strong> inducing agent that initiate<br />

phenomenon<br />

Signal transduction that is needed to propagate <strong>the</strong> induced state systemically through<br />

<strong>the</strong> plant<br />

Expression <strong>of</strong> defense mechanisms that limit or inhibit fur<strong>the</strong>r pathogen penetration in<br />

to host tissues.<br />

Resistance-inducing traits <strong>of</strong> beneficial microbes<br />

Microbial determinants that contribute to induced resistance as triggered by beneficial<br />

microbes are best studied <strong>for</strong> fluorescent Pseudomonas spp. In analogy to <strong>the</strong> microbe-associated<br />

molecular patterns (MAMPs) flagellin and lipopolysaccharides (LPS) <strong>of</strong> pathogenic Pseudomonas<br />

spp., it was found that <strong>the</strong>se cell surface components <strong>of</strong> beneficial Pseudomonas spp. are potent<br />

inducers <strong>of</strong> <strong>the</strong> host immune response. Antibiotics, which are produced by some beneficial<br />

microorganisms, can also function as MAMPs in triggering <strong>the</strong> immune response.<br />

MAMPs involved in systemic resistance triggered by beneficial fungi are not well studied.<br />

Trichoderma-derived xylanase and cellulase are well known inducers <strong>of</strong> ethylene biosyn<strong>the</strong>sis. It<br />

was shown that cellulase treatment leads to activation <strong>of</strong> defense mechanisms in melon<br />

cotyledons (Martinez et al. 2001). Djonovic et al. (2006) demonstrated that <strong>the</strong> hydrophobin-like<br />

elicitor Sm1 <strong>of</strong> <strong>the</strong> beneficial soil-borne fungus Trichoderma virens induces systemic resistance in<br />

maize. Maize plants grown with SM1-deletion strains or SM1-overexpressing strains displayed<br />

decreased or enhanced levels <strong>of</strong> systemic disease protection, respectively, demonstrating its role<br />

in triggering host defense. Peptaibols are linear peptide antibiotics produced by Trichoderma and<br />

o<strong>the</strong>r fungal genera. In <strong>the</strong> biocontrol agent and inducer <strong>of</strong> plant defense responses Trichoderma<br />

virens, enzymes <strong>for</strong>ming peptaibols are encoded by tex1 and disruption <strong>of</strong> <strong>the</strong>se genes led to a<br />

significantly reduced systemic resistance response in cucumber plants against <strong>the</strong> leaf pathogen<br />

Pseudomonas syringae pv. lachrymans as compared with plants grown in presence <strong>of</strong> <strong>the</strong> wildtype.<br />

Two syn<strong>the</strong>tic 18-amino-acid peptaibol iso<strong>for</strong>ms induce systemic protection when applied to<br />

cucumber seedlings suggesting that <strong>the</strong>se peptides are critical in <strong>the</strong> chemical communication<br />

between Trichoderma and plants as triggers <strong>of</strong> defense responses. However, <strong>the</strong> peptaibol<br />

alamethicin induced a <strong>for</strong>m <strong>of</strong> active cell death in Arabidopsis thaliana cell cultures and caused<br />

lesions in leaves <strong>of</strong> plants after a few days showing that <strong>the</strong>se molecules may also retain some<br />

phytotoxicity on certain plant species. It has also recently been demonstrated that some o<strong>the</strong>r<br />

secondary metabolites <strong>of</strong> plant beneficial Trichoderma spp. such as harzianolide and pentylpyranone<br />

may have a role in activation <strong>of</strong> plant defense responses.<br />

Peroxidase and polyphenol oxidase are oxidative enzymes contributing to defense against<br />

pathogens. The peroxidase activity increases in plants during pathogen infection and has been<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

correlated with resistance. High activity <strong>of</strong> peroxidase increased <strong>the</strong> ability <strong>of</strong> transgenic tobacco<br />

plants to suppress growth <strong>of</strong> <strong>the</strong> pathogenic bacterium Erwinia carotovara.. Several previous<br />

experiments have demonstrated <strong>the</strong> importance <strong>of</strong> polyphenol oxidase-mediated phenolic<br />

oxidation in restricting plant disease development. For example polyphenol oxidase-over<br />

expressing tomato plants were shown to exhibit a great increase in resistance to P. syringae.<br />

Compared with control plants, <strong>the</strong>se transgenic lines showed less severity <strong>of</strong> disease symptoms,<br />

with over 15-fold fewer lesions, and strong inhibition <strong>of</strong> bacterial growth, causing more than 100-<br />

fold reduction <strong>of</strong> bacterial population in <strong>the</strong> infected leaves. Consequently, high activities <strong>of</strong><br />

peroxidise and polyphenol oxidase can be components <strong>of</strong> resistance against pathogens, including<br />

bacteria.<br />

Ethylene is an important factor in <strong>the</strong> regulation <strong>of</strong> plant reaction to pathogens. An increase<br />

<strong>of</strong> ethylene <strong>for</strong>mation in pathogen-challenged plants has been related both to defense responses<br />

leading to resistance as well as to symptom development during pathogenesis. The role <strong>of</strong><br />

ethylene in incompatible interactions is mostly contradictory and depends on <strong>the</strong> pathogen used.<br />

Similarly, regarding to susceptible responses, ethylene insensitivity may lead to both increases<br />

and decreases <strong>of</strong> symptom development. In addition, recent findings indicate <strong>the</strong> role <strong>of</strong> ethylene<br />

in induced systemic resistance. The fact that ethylene is a known inducer <strong>of</strong> several pathogen<br />

defense-related enzymes, e.g. peroxidase, glucanase, and chitinase, lends support to <strong>the</strong><br />

regulative role <strong>of</strong> ethylene in resistance responses. Examples <strong>of</strong> <strong>Plant</strong> –Pathogen system where<br />

induced resistance by Trichoderma spp. have been reported is given in table-1.<br />

Table-1: Induced Resistance in <strong>Plant</strong> by Trichoderma species<br />

Species and<br />

strain<br />

T. virens<br />

G-6,G-6-5 and<br />

G-11<br />

T. harzianum<br />

T-39<br />

T. harzianum<br />

T-39<br />

T. asperellum<br />

T-203<br />

<strong>Plant</strong> Pathogens Evidences or effect Time<br />

after<br />

Appli.<br />

Cotton<br />

Bean<br />

Tomato<br />

Pepper<br />

Tobacco<br />

Lettuce<br />

Bean<br />

Rhizoctonia<br />

solani<br />

Colletotrichum<br />

lindemuthianum<br />

Botrytis cinerea<br />

Protection <strong>of</strong> plants,<br />

induction <strong>of</strong> fungitoxic<br />

terpenoid phytolexins<br />

Protection <strong>of</strong> leaves<br />

when T-39 was present<br />

only on roots<br />

B. cinerea Protection <strong>of</strong> leaves<br />

when T-39 was present<br />

only on roots<br />

Cucumber Pseudomonas<br />

syringae<br />

pv,lachrymans<br />

Protection <strong>of</strong> leaves<br />

when T-203 was present<br />

only on roots, production<br />

<strong>of</strong> antifungal compounds<br />

in leaves<br />

4<br />

days<br />

10<br />

days<br />

7<br />

days<br />

5<br />

days<br />

Efficacy<br />

78%<br />

reduction in<br />

disease<br />

48%<br />

reduction in<br />

lesion area<br />

25-100%<br />

reduction<br />

Up to 80%<br />

reduction in<br />

disease on<br />

leaves &<br />

100% on<br />

stem<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

T. harzianum<br />

T-22,<br />

T. atroviride<br />

P1<br />

T. harzianum<br />

T-1 & T-22, T.<br />

virens T3<br />

T. harzianum<br />

T-22<br />

T. harzianum<br />

T-22<br />

Trichoderma<br />

GT3-2<br />

Bean<br />

B. cinerea,<br />

X. campestris<br />

pv. phaseoli<br />

Cucumber Green mottle<br />

mosaic virus<br />

Protection <strong>of</strong> leaves<br />

when T-22 or P1 was<br />

present only on roots,<br />

production <strong>of</strong> antifungal<br />

compounds in leaves<br />

Protection <strong>of</strong> leaves<br />

when Trichoderma strain<br />

were present only on<br />

roots<br />

Tomato A. solani Protection <strong>of</strong> leaves<br />

when Trichoderma strain<br />

were present only on<br />

roots<br />

Maize C. graminicola Protection <strong>of</strong> leaves<br />

when Trichoderma strain<br />

were present only on<br />

roots<br />

Cucumber C. orbiculare,<br />

P. syringae pv.<br />

lachrymans<br />

T. harzianum Pepper Phytophthora<br />

capsici<br />

T. harzianum<br />

NF-9<br />

Rice<br />

Magnapor<strong>the</strong><br />

grisea,<br />

X. oryzae pv.<br />

oryzae<br />

Protection <strong>of</strong> leaves<br />

when Trichoderma strain<br />

were present only on<br />

roots, Induction <strong>of</strong><br />

lignification & superoxide<br />

generation<br />

Protection <strong>of</strong> stem when<br />

Trichoderma strain were<br />

present only on roots,<br />

inhanced production <strong>of</strong><br />

<strong>the</strong> phytolexin capsidol<br />

Protection <strong>of</strong> leaves<br />

when NF-9 was present<br />

only on roots<br />

7-10<br />

days<br />

7<br />

days<br />

3<br />

month<br />

14<br />

day<br />

69% & 54%<br />

respectively<br />

Reduction<br />

in growth<br />

eliminated<br />

Up to 80%<br />

reduction in<br />

disease<br />

44%<br />

reduction in<br />

lesion size<br />

1 day 59%<br />

52%<br />

protection<br />

respectively<br />

9<br />

days<br />

14<br />

days<br />

40%<br />

reduction in<br />

lesion<br />

length<br />

34-50%<br />

reduction in<br />

disease<br />

Induced defense signalling pathways<br />

It is probable that MAMPs <strong>of</strong> beneficial microbes and pathogens are recognized in a largely<br />

similar manner, ultimately resulting in an enhanced defensive capacity <strong>of</strong> <strong>the</strong> plant. However, in<br />

plant–beneficial microbe interactions, MAMP-triggered immunity does not ward <strong>of</strong>f <strong>the</strong> interacting<br />

beneficial as it remains accommodated by <strong>the</strong> plant. This suggests a high degree <strong>of</strong> coordination<br />

and a continuous molecular dialog between <strong>the</strong> plant and <strong>the</strong> beneficial organism. The local and<br />

systemic defense responses that are triggered by beneficial and parasitic microorganisms are<br />

controlled by a signalling network in which <strong>the</strong> plant hormones salicylic acid (SA), jasmonic acid<br />

(JA), and ethylene (ET) play important roles. There is ample evidence that SA, JA, and ET<br />

pathways cross communicate, allowing <strong>the</strong> plant to finely tune its defense response depending on<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>the</strong> invader encountered (Koornneef and Pieterse, 2008). ISR, which is triggered by beneficial<br />

microorganisms like Trichoderma spp. requires components <strong>of</strong> <strong>the</strong> JA and ET signalling pathway<br />

(Pieterse, 1998). Both pathogen-induced SAR and Trichoderma spp. - triggered ISR are controlled<br />

by <strong>the</strong> transcriptional regulator NPR1 (Pieterse and Loon, 2004). List <strong>of</strong> MAMPs identified in<br />

different Trichoderma spp. is given in table-2.<br />

Table-2: Tricoderma MAMPs Identified in Different Species<br />

MAMP/ Effector Tricoderma<br />

Activity<br />

species<br />

PROTEINS<br />

Xylanase Xyn2/Eix T. viride A xylanase that elicits ET biosyn<strong>the</strong>sis and<br />

hypersensitive response in tobacco leaf tissues<br />

Cellulases T. longibrachiatum Activated and heat-denatured cellulases elicit<br />

melon defences through <strong>the</strong> activation <strong>of</strong> <strong>the</strong><br />

Cerato-platanins<br />

Sm1/Epl1<br />

T. virens/<br />

T. atroviride<br />

SA and ET signalling pathways, respectively<br />

Hydrophobin-like SSCP orthologues that can<br />

induce expression <strong>of</strong> defence response in<br />

cotton and maize<br />

Swollenin TasSwo T. asperelloides Expansin-like protein with a cellulose-binding<br />

domain capable <strong>of</strong> stimulating local defence<br />

responses in cucumber roots & Leaves &<br />

af<strong>for</strong>ding local protection against B. cinerea &<br />

P. syringae<br />

Endopolygalacturonase<br />

ThPG1<br />

T. harzianum Involved in active colonization <strong>of</strong> tomato root &<br />

ISR-like defense in Aradiopsis<br />

SECONDARY METABOLITES<br />

Alamethicin<br />

(20mer peptaibol)<br />

T. viride Elicitation <strong>of</strong> JA & SA biosyn<strong>the</strong>sis in Lima<br />

bean<br />

Trichokonin<br />

(20mer peptaibol)<br />

T. pseudokoningii Induces <strong>the</strong> production <strong>of</strong> ROS, <strong>the</strong><br />

accumulation <strong>of</strong> phenolic compounds at <strong>the</strong><br />

application site & virus resistance in tobacco<br />

plants through multiple defense signallling<br />

pathways<br />

18mer Peptaibols T. virens Elicitation <strong>of</strong> cucumber systemic defenses<br />

6-Pentyl-α-pyrone,<br />

horzianolid<br />

harzianopyridone<br />

&<br />

against P. syringae<br />

Various Low- conc. metabolites activating plant<br />

defense mechanisms & regulating plant growth<br />

in pea, tomato & canola<br />

Limitations <strong>of</strong> Induced Systemic Resistance<br />

Dependence on environmental condition<br />

Only partial protection<br />

Problem <strong>of</strong> mass multiplication, storage and application<br />

Phytotoxicity<br />

Resurgence<br />

Effect on quality<br />

Safety<br />

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REFERENCES<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

• Chang, P.F.L., Xu Y., Narasimhan, M.L., Cheah, K.T., D’Urzo, M.P., Damsz B., Kononowicz, A.K.,<br />

Abad, L., Hasegawa, P.M., Bressan, R.A. 1997. Induction <strong>of</strong> pathogen resistance<br />

and pathogenesis-relatedgenes in tobacco by a heat-stable Trichoderma mycelial<br />

extract and plant signal messengers. Physiol. <strong>Plant</strong>. 100: 341–352.<br />

• Darvill, AG, Albersheim, P. 1984. Phytoalexins and <strong>the</strong>ir elicitors a defense against microbial<br />

infection in plants. Annu Rev <strong>Plant</strong> Physiol. 35:243–275.<br />

• Djonović, S.; Vargas, W.A.; Kolomiets, M.V.; Horndeski, M.; Wiest, A.; Kenerley, C.M. 2007. A<br />

proteinaceous elicitor Sm1 from <strong>the</strong> beneficial fungus Trichoderma virens is<br />

required <strong>for</strong> induced systemic resistance in maize, <strong>Plant</strong> Physiol, 145 : 875–889.<br />

• Harman, G.E., Howell, C.R., Viterbo, A., Chet, I. and Lorito, M. 2004. Trichoderma species<br />

• opportunistic, avirulent plant symbionts. Microbiology, 2: 43-56.<br />

• Koornneef, A. and Pieterse, C. M. J. 2008. An in<strong>for</strong>mative overview <strong>of</strong> molecular mechanisms<br />

involved in crosstalk between defense signaling pathways, <strong>Plant</strong> Physiol, 146: 839–<br />

844.<br />

• Martinez, C., Blanc, F., Le Claire, E., Besnard, O., Nicole, M., Baccou, J.C. 2001. Salicylic acid<br />

and ethylene pathways are differentially activated in melon cotyledons by active or<br />

heat-denatured cellulase from Trichoderma longibrachiatum. <strong>Plant</strong> Physiol. 127:<br />

334–344.<br />

• Pieterse, C.M.J.; Van Wees, S.C.M.; Pelt, J.A. Van; Knoester, M.; Laan, R.; Gerrits, H.; Weisbeek,<br />

P.J. and Loon, L.C. Van. 1998. A novel signaling pathway controlling induced<br />

systemic resistance in Arabidopsis, <strong>Plant</strong> Cell, 10: 1571–1580.<br />

• Pieterse, C.M.J. and Loon, L.C. Van. 2004. NPR1: <strong>the</strong> spider in <strong>the</strong> web <strong>of</strong> induced resistance<br />

signaling pathways. Curr Opin <strong>Plant</strong> Biol, 7: 456–464.<br />

• Yedidia, I., Benhamou, N., Chet, I. 1999. Induction <strong>of</strong> defense responses in cucumber plants<br />

(Cucumis sativus L.) by <strong>the</strong> biocontrol agent Trichoderma harzianum. Appl. Env.<br />

Microbiol. 65: 1061–1070.<br />

• Yedidia, I., Benhamou, N., Kapulnik, Y., Chet, I. 2000. Induction and accumulation <strong>of</strong> PR proteins<br />

activity during early stages <strong>of</strong> root colonization by <strong>the</strong> mycoparasite Trichoderma<br />

harzianum strain T-203. <strong>Plant</strong> Physiol. Biochem. 38: 863–873<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Influence <strong>of</strong> Environmental Parameters on Trichoderma Strains with<br />

Biocontrol Potentials<br />

A.K. Tewari<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B. Pant Univ. <strong>of</strong> Agric. & Tech., Pantnagar- 263 145 (UK)<br />

Trichoderma genus is one <strong>of</strong> <strong>the</strong> most common soil fungi, isolated from various habitats,<br />

This is also known <strong>for</strong> secreting secondary metabolites in <strong>the</strong> environment which affects on wide<br />

spectrum <strong>of</strong> various fungal groups, especially pathogenic fungi. Reports by various workers show<br />

that Trichoderma spp. is a powerful antagonists <strong>of</strong> parasitic soil fungi <strong>of</strong> Pythium,Phytophthora,<br />

Sclerotinia, Sclerotium, Rhizoctonia, Fusarium, Verticillium and Gaeumannomyces,<br />

In recent times Biological control is an important component <strong>of</strong> IPM system instead <strong>of</strong> its<br />

independent use. In most <strong>of</strong> <strong>the</strong> cases <strong>the</strong> bioagents are effective in laboratory or greenhouse<br />

conditions only, and not all that successful under field conditions. The investigations on<br />

epidemiological aspects <strong>of</strong> <strong>the</strong> disease as well as developments <strong>of</strong> <strong>the</strong> bioagents are, <strong>the</strong>re<strong>for</strong>e,<br />

crucial to keep <strong>the</strong> biocontrol recommendations under varying environmental conditions. Among<br />

fungal bioagents, Trichoderma is very promising candidates <strong>for</strong> <strong>the</strong> biological control <strong>of</strong> plant<br />

pathogenic fungi. When planning <strong>the</strong> application <strong>of</strong> antagonistic Trichoderma strains <strong>for</strong> <strong>the</strong><br />

purposes <strong>of</strong> biological control, it is very important to consider <strong>the</strong> environmental parameters<br />

affecting <strong>the</strong> biocontrol agents in <strong>the</strong> soil. The environment (<strong>the</strong> effects <strong>of</strong> temperature, water<br />

potential and pH) effectiveness <strong>of</strong> antagonist and its ability to survive in an ecosystem , host<br />

exudates presence <strong>of</strong> chemicals , metal ions, and <strong>the</strong> antagonistic bacteria in <strong>the</strong> soil are<br />

important factors to decide <strong>the</strong> fate <strong>of</strong> biological control <strong>of</strong> plant pathogens. In spite <strong>of</strong> various<br />

abiotic factors biotic factors <strong>of</strong> antagonists like; ability to colonize <strong>the</strong> substrate and competent with<br />

o<strong>the</strong>r microorganism in <strong>the</strong> niche, production. <strong>of</strong> chlamydospores which can sustain <strong>for</strong> a longer<br />

period <strong>of</strong> time even in adverse climatic conditions, germination and recovery time <strong>of</strong> <strong>the</strong> spore,<br />

release from <strong>for</strong>mulation ,doubling time/linear growth rate and movement to <strong>the</strong> site <strong>of</strong> action <strong>of</strong> <strong>the</strong><br />

antagonist also plays a major role <strong>for</strong> <strong>the</strong> antagonistic potential <strong>of</strong> <strong>the</strong> Trichoderma<br />

Most <strong>of</strong> <strong>the</strong> Trichoderma strains are mesophilic and grow well in a wide range <strong>of</strong><br />

temperature from 15-35 0 C. Low temperatures in winter may cause a problem during biological<br />

control by influencing <strong>the</strong> activity <strong>of</strong> <strong>the</strong> Trichoderma. Trichoderma cannot tolerate dry conditions;<br />

however, we may need <strong>the</strong>se agents against plant pathogenic fungi which are able to grow and<br />

cause disease even in dry soils. The pH characteristics <strong>of</strong> <strong>the</strong> soil is also considered to <strong>the</strong> most<br />

important parameters affecting <strong>the</strong> activities <strong>of</strong> mycoparasitic Trichoderma strains. Trichoderma<br />

strains were able to grow in a wide range <strong>of</strong> pH from 2.0 – 6.0 with an optimum at 4.0.<br />

Mycoparasitic Trichoderma strains were found to be able to display various enzyme activities<br />

under a wider range <strong>of</strong> pH values 3.0- 6.0.Trichoderma are more effective in acidic soil , however<br />

Pseudomonas fluorescence are more effective in slightly alkaline soil ( above pH 6.5) .<br />

In <strong>the</strong> IPM strategy, we may have to combine Trichoderma strains with chemical<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

pesticides or metal compounds, <strong>the</strong>re<strong>for</strong>e it is important to collect in<strong>for</strong>mation about <strong>the</strong> effects <strong>of</strong><br />

pesticides and metal ions on <strong>the</strong> biocontrol strains. Antagonistic soil bacteria may also have<br />

negative effects on <strong>the</strong> biocontrol abilities <strong>of</strong> Trichoderma strains, <strong>the</strong>re<strong>for</strong>e it may be<br />

advantageous if a biocontrol strain possesses bacterium- degrading abilities as well.<br />

The number <strong>of</strong> studies about <strong>the</strong> effects <strong>of</strong> different environmental factors on mycoparasitic<br />

Trichoderma strains is increasing from year to year, indicating, that in order to reach effective<br />

biological control, it is necessary to broaden our knowledge about <strong>the</strong> epidemiology and<br />

ecophysiology <strong>of</strong> <strong>the</strong> Trichoderma. The application <strong>of</strong> mycoparasitic Trichoderma strains with<br />

improved tolerance <strong>of</strong> unfavorable environmental conditions could increase <strong>the</strong> efficacy <strong>of</strong><br />

biological control. The breeding <strong>of</strong> Trichoderma <strong>for</strong> cold-tolerance, osmotolerance, bacteriumtolerance,<br />

pesticide- or metal-resistance may result in effective mycoparasitic strains <strong>for</strong> biocontrol<br />

application against fungal plant pathogens under a wider range <strong>of</strong> environmental conditions.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Smut Fungi: Potential Pathogens and Biocontrol Agents<br />

K. Vishunavat<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Smuts and bunts referto a particle <strong>of</strong> dirt or a smudge made by soot, smoke, or dirt.The<br />

smuts are fungi, mostly Ustilaginomycetes (<strong>of</strong> <strong>the</strong> class Teliomycetae, subphylum Basidiomycota),<br />

that cause plant disease. Several important genera include Ustilago, Sphacelo<strong>the</strong>ca,<br />

Tolyposporium, Tilletia, Entyloma, and Urocystis. The disease is initiated when soil-borne, or in<br />

particular seed-borne, teliospores germinate and eventually produce hyphae that infect<br />

germinating seeds by penetrating <strong>the</strong> coleoptile be<strong>for</strong>e plants emerge or through spores<br />

dissiminated to infect <strong>the</strong> reproductive organs.<br />

1. Nuclear Cycle <strong>of</strong> smut fungi<br />

The life cycle <strong>of</strong> smut fungi is partly dictated by <strong>the</strong> heterothallic nature <strong>of</strong> <strong>the</strong> fungus. When<br />

primary and secondary sporidia (basidiospores) ,each having a single haploid nucleus germinate,<br />

<strong>the</strong>y produce monokaryotic (1N) hyphae. At some unknown point in <strong>the</strong> life cycle <strong>of</strong> <strong>the</strong> pathogen,<br />

monokaryotic hyphae <strong>of</strong> different, compatible mating types fuse to produce dikaryotic (1N + 1N)<br />

hyphae. This dikaryotization most likely occurs on <strong>the</strong> plant surface just prior to penetration or<br />

within <strong>the</strong> plant tissue after penetration by <strong>the</strong> hyphae. At some later time, fusion (karyogamy) <strong>of</strong><br />

compatible nuclei occurs within <strong>the</strong> dikaryotic hyphae, and teliospores develop.<br />

2. Infection by Smut fungi<br />

Types <strong>of</strong> infection in smut fungi<br />

Seedling infection<br />

The smut spores are usually smooth walled, externally seed borne, germinate with <strong>the</strong><br />

seed germination. The infection <strong>of</strong> <strong>the</strong> seedling takes place be<strong>for</strong>e its emergence out <strong>of</strong> <strong>the</strong> soil.<br />

Change <strong>of</strong> haplophase to diplophase takes place be<strong>for</strong>e infection.<br />

Floral or blossom infection or intraseminal infection<br />

Rough walled wind blown spores fall onto <strong>the</strong> fresh flowers where <strong>the</strong>y germinate to cause<br />

infection <strong>of</strong> <strong>the</strong> ovary after diplodization. The binucleate hyphae reach <strong>the</strong> embryo, remify, and<br />

become dormant with maturity <strong>of</strong> <strong>the</strong> seed. The infection thus carried internally with <strong>the</strong> seed and<br />

when <strong>the</strong> later germinates, <strong>the</strong> fungus also grows up and finally appears as black powdwery mass<br />

in <strong>the</strong> inflorescence.<br />

Shoot infection<br />

This is usually local infection. Spores are carried through wind currents and fall on to <strong>the</strong><br />

young buds, young flowers , developing seeds , or may fall on <strong>the</strong> ground , perennate <strong>the</strong>re<br />

ultimately germinate next year causing infection <strong>of</strong> <strong>the</strong> host parts through wind blown sporidia.<br />

According to effect on host <strong>the</strong> smut may be:<br />

Ovariculous<br />

The inflorescence develop normally and <strong>the</strong> ovary also functions in <strong>the</strong> normal way but <strong>the</strong><br />

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content <strong>of</strong> <strong>the</strong> ovary are ultimately destroyed and replaced by <strong>the</strong> smut spore masses.Loose smut<br />

in which <strong>the</strong> wall <strong>of</strong> <strong>the</strong> ovary is eaten away and <strong>the</strong> smut spores are easily blown <strong>of</strong>f. Ano<strong>the</strong>r<br />

example is covered smut in which ovary wall remain intact thus keeping <strong>the</strong> spores toge<strong>the</strong>r<br />

unless <strong>the</strong> wall is mechanically broken.<br />

Culmiculous: The full development <strong>of</strong> <strong>the</strong> inflorescence is suppressed.<br />

Role <strong>of</strong> environmental conditions and soil borne inoculum in causing smut diseases <strong>of</strong><br />

cereals<br />

(i) Loose smut <strong>of</strong> wheat<br />

The level <strong>of</strong> loose smut infection in wheat varies according to wea<strong>the</strong>r conditions during <strong>the</strong><br />

flowering period <strong>of</strong> <strong>the</strong> crop . Cool, moist conditions extend <strong>the</strong> flowering period, giving loose smut<br />

spores more chance to infect <strong>the</strong> open flowers. Seed produced in cool wet seasons is likely to<br />

carry increased infection levels, whereas hot dry conditions at flowering time may reduce <strong>the</strong><br />

infection level.<br />

(ii) Covered smuts / common bunt/ stinking smut/ hill smut <strong>of</strong> wheat<br />

Pathogen is soil borne or may be carried through seed.Spores are so hardy that <strong>the</strong>y may infect<br />

wheat crop even after 10 year in soil and after passage through <strong>the</strong> digestive tracts <strong>of</strong> cattle and<br />

sheep may infect wheat crop. <strong>Soil</strong> temperature, moisture, type <strong>of</strong> soil fertility, host variety<br />

,physiological races, spore load, depth and rate <strong>of</strong> sowing and day length have marked influence<br />

on spore germination and subsequent infection.<br />

(iii) Covered smut <strong>of</strong> barley Ustilago hordei<br />

The black spore mass <strong>of</strong> this smut remains covered by more or less firmly adhering<br />

membranes <strong>of</strong> <strong>the</strong> grain and <strong>the</strong> basal parts <strong>of</strong> <strong>the</strong> glumes. Fungus is externally seed borne. The<br />

spores adhere on seed surface while threshing.The seedling infection is influenced by soil<br />

moisture and soil temperature. Optimum temperature <strong>for</strong> spore germination is 20 o C and <strong>the</strong><br />

maximum 35 o C. The period <strong>of</strong> infection is limited to <strong>the</strong> period between germination and<br />

emergence <strong>of</strong> <strong>the</strong> seedling. Deep sowing leng<strong>the</strong>ns <strong>the</strong> period <strong>of</strong> susceptibility. Shallow sowing<br />

reduces disease incidence<br />

Cool soil temperature, high moisture helps to reduces infection.<br />

(iv) Loose Smut <strong>of</strong> Oat (Ustilago avenae)<br />

The infection is seed borne (dormant mycelium in <strong>the</strong> pericarp) or seed contamination<br />

(spore adhere on seed surface during threshing).The soil environment is essential factor in<br />

determining <strong>the</strong> severity <strong>of</strong> infection.Optimum temperature <strong>for</strong> spore germination is 15-28 0 C while<br />

maximum is 31-34 0 C and minimum is 4-5 0 C.High soil temperature and low soil moisture favours<br />

<strong>the</strong> disease.<br />

(v) Smut <strong>of</strong> maize Ustilago maydis<br />

The fungus survives on mature heaps and crop refuses and <strong>the</strong>se serve as main source <strong>of</strong><br />

harboring inoculum. The fungus produce Gall on <strong>the</strong> infected cob, stem, leaves, axillary buds and<br />

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parts <strong>of</strong> <strong>the</strong> male flower tissues. The saprophytic phase may be as prolonged as <strong>the</strong> fungus go on<br />

growing indefinitely on fresh nutrient solutions.Not much work has been done in India due to<br />

obscure nature <strong>of</strong> <strong>the</strong> disease.<br />

(vi) Loose smut <strong>of</strong> sorghum (Sphacelo<strong>the</strong>ca cruenta)<br />

In <strong>the</strong> ear head, spiketets are affected and grains get converted into <strong>the</strong> sori .The spores<br />

are <strong>for</strong>med in ovary and floral bracts.The fungus is both soil borne and externally seed borne.<br />

Spores remain viable <strong>for</strong> four years in dry conditions. Spores germinate best at 18-20 0 C .Low<br />

temperature, low soil moisture, and deep sowing favours infection.<br />

(vii) Head smut sorghum (Sphacelo<strong>the</strong>ca reilianum)<br />

Entire inflorescence gets converted into a big sorus.The soil borne inoculum is major<br />

source <strong>of</strong> infection although pathogen may be externally seed borne. <strong>Soil</strong> temperature and<br />

moisture are main factors responsible <strong>for</strong> survival <strong>of</strong> spores.Dry cool soil favours survival while<br />

moist and warm soil reduces survival. Application <strong>of</strong> low C: N organic amendments reduce<br />

inoculum density.The disease is more in crop grown in clay loam soil (high moisture) than in sandy<br />

loam soil. Frequent irrigation after sowing reduces disease incidence. Deep sowing show high<br />

disease incidence. Application <strong>of</strong> urea, ammonium sulphate, and triple-super-phosphate reduces<br />

disease incidence.<br />

(ix) Long smut <strong>of</strong> sorghum Tolyposporium ehrenbergii)<br />

Few grains in an ear are trans<strong>for</strong>med into smut sori.The primary inoculum may be<br />

introduced by some alternative host. The disease is air borne in nature and wind blown spores fall<br />

on to bud and initiate a mycelium which is expressed in heads. Spores germinate at 15-36 0 C<br />

optimum by 28 0 0 C. Seed treatment is <strong>the</strong>re<strong>for</strong>e <strong>of</strong> no use.Crop rotation, field sanitation helps to<br />

reduce <strong>the</strong> disease. The varieties with covered glumes may escape infection.<br />

(x) Smut <strong>of</strong> pearl millet (Tolyposporium penicillariae)<br />

The pathogen is soil borne. Sori are on scatterd grain in <strong>the</strong> ear. Spores are held in balls.<br />

On germination <strong>the</strong>y give rise to sporidia which are carried by air current towards <strong>the</strong> floral axis<br />

and settle down on <strong>the</strong> florets immediately cause infection .Similar to <strong>the</strong> long smut disease ,crop<br />

rotation, field sanitation help to reduce <strong>the</strong> infection and <strong>the</strong> varieties with covered glumes may<br />

escape infection .<br />

(xi) Covered smuts / common bunt/ stinking smut/ hill smut <strong>of</strong> wheat (Tilletia caries or T.<br />

foietidia)<br />

Pathogen is soil borne or may be carried through seed as externally seed borne infection .<br />

Spores are so hardy that <strong>the</strong>y may infect wheat crop after 10 year <strong>of</strong> storage in soil and after<br />

passage through <strong>the</strong> digestive tracts <strong>of</strong> cattle and sheep may infect wheat crop.<strong>Soil</strong> temperature,<br />

moisture, type <strong>of</strong> soil fertility, host variety, physiological races, spore load, depth and rate <strong>of</strong><br />

sowing and day length have marked influence on spore germination and subsequent infection.<br />

(xii) Covered smuts / common bunt/ stinking smut/ hill smut <strong>of</strong> wheat (Tilletia laevis)<br />

The temperature <strong>for</strong> spores to germinate are, 0-4 0 C minimum, 18-20 0 C optimum and 36 0 C<br />

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<strong>the</strong> maximum. Different races behave differently as regard to <strong>the</strong>ir temperature requirement. Low<br />

soil temperature and high soil moisture are conducive <strong>for</strong> disease development.Optimum soil<br />

temperature favouring disease is 9-12 0 C .The planting during high temperature effectively reduce<br />

disease incidence. Shallow sowing reduces disease incidence while deep sowing increases <strong>the</strong><br />

disease.<br />

(xiii) Karnal bunt Neovossia indica ( Tilletia indica)<br />

The Pathogen is soil borne or may be carried through seed on seed surface. Spore may<br />

remain viable in soil <strong>for</strong> 4-5 years.The survival <strong>of</strong> spores depends upon <strong>the</strong> depth in soil. The<br />

viability <strong>of</strong> spore decreases with <strong>the</strong> increase in depth <strong>of</strong> soil. The environmental conditions in<br />

Nor<strong>the</strong>rn India in <strong>the</strong> month <strong>of</strong> Mid February or early march favors spore germination. Good<br />

teliospore germination in soil is at 15% or above soil moisture. Irrigation, cloudy or foggy wea<strong>the</strong>r<br />

<strong>for</strong> 7-10 days in December to March, and at minimum average temperature <strong>of</strong> 3.7 0 C and<br />

maximum 27.5 0 C, is good <strong>for</strong> teliospore germination. However, <strong>for</strong> disease to develop high<br />

humidity frequent light rains, cloudy wea<strong>the</strong>r, and low temperature at <strong>the</strong> time <strong>of</strong> flowering are<br />

required. Excessive irrigation and nitrogen fertilizers show heavy incidence <strong>of</strong> bunt. High microbial<br />

population by green manuring and fertilizer in soil show low bunt incidence.<br />

(ivx)Bunt <strong>of</strong> rice ( Tilletia horrida)<br />

Few grains in <strong>the</strong> ear get converted into black powder mass in <strong>the</strong> husk.Spores survive in<br />

soil, or go with seed awns and partially infected grains.Spores remain viable <strong>for</strong> 2-more years in<br />

soil. Disease is more common in light than in heavy soil. Heavy nitrogen fertilizers make plant<br />

susceptible to disease.However, temperature <strong>of</strong> 25-30 0 C and high humidity ( 85% or more ) with<br />

intermittent showers at <strong>the</strong> time <strong>of</strong> ear emergence favours infection.<br />

(vx) Leaf smut <strong>of</strong> rice ( Entyloma oryzae )<br />

Black spots covered by <strong>the</strong> epidemis and having black smut spore underneath in<br />

leaves.The fungus survive on diseased leaf trash in soil. High nitrogen application in soil enhances<br />

disease.<br />

(vix) Flag smut <strong>of</strong> wheat (Urocystis tritici)<br />

The pathogen is soil and seed borne. The fungus persists in soil <strong>for</strong> many years.Sowing in<br />

moist soil enhances disease. Seed when sown through broadcasting in dry land, harrowed and<br />

<strong>the</strong>n irrigated show low disease incidence.The minimum, optimum and maximum temperature <strong>for</strong><br />

spore to germinate is 5, 20 and 28 0 C .<strong>Soil</strong> with excessive Ca macronutrient favors disease.Deep<br />

sowing enhances disease.<br />

Classical examples <strong>of</strong> smut fungi as bioagents<br />

Ustilago maydis is unique amongst biological weapons in that it is not only edible, but<br />

considered highly desirable. In Mexico, galls on sweet corn are known as huitlacoche and <strong>the</strong>y can<br />

be more valuable than <strong>the</strong> plant itself. Farmers may <strong>the</strong>re<strong>for</strong>e try to spread <strong>the</strong> disease when<br />

plants are seen to be infected.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Tilletia ehrhartae: A seed infecting fungus (Tilletia ehrhartae) could provide a biological control <strong>for</strong><br />

an invasive Veldt grass (Ehrharta calycina) in South Africa and Australia.<br />

Similarly , white smut fungus (Entyloma ageratinae) a native <strong>of</strong> Jamica and Maxico may<br />

be used as biocontrol agent <strong>for</strong> successful biocontrol programme against mist flower (Ageratina<br />

riparia ) in Hawaii .The fungus was released to some worst mist flower infested areas in north<br />

Island and New Zealand in 1998 establishing readily and quickly becoming common.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Biocontrol <strong>of</strong> Fungal Phytopathogens by Trichoderma spp.<br />

Lakshmi Tewari, Disha Sharma and Rajkumar Pandey<br />

Department <strong>of</strong> Microbiology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Biological control <strong>of</strong> phytopathogens by antagonistic organisms is a potential, non chemical<br />

and more eco friendly tool <strong>for</strong> crop protection. Trichoderma species are considered as one <strong>of</strong> <strong>the</strong><br />

most important biocontrol fungi <strong>for</strong> improving plant growth and protecting crops from several fungal<br />

plant pathogens (Harman 2000). Most <strong>of</strong> <strong>the</strong> chemical pesticides used to control plant diseases<br />

and phyto-pathogens are highly toxic and harmful <strong>for</strong> <strong>the</strong> human beings causing environmental<br />

hazards also. An effective alternative or supplement to <strong>the</strong>se chemical pesticides is biological<br />

control (cook and baker, 1983). Biological control strategy is highly compatible with sustainable<br />

agriculture and has a major role to play as a component <strong>of</strong> integrated pest management (IPM)<br />

programme.<br />

Figure1: Morphological features <strong>of</strong> Trichoderma harzianum<br />

Trichoderma sp. are free living soil fungi that are highly interactive with o<strong>the</strong>r rhizosphere<br />

micro flora in root, soil and foliar environments. Mycoparasitic activity and antibiotic production<br />

potential were first demonstrated in Trichoderma lignorum by Weindling (1932). One <strong>of</strong> <strong>the</strong> most<br />

interesting aspects <strong>of</strong> studies on Trichoderma is its potential to employ varied mechanisms <strong>for</strong><br />

disease control. In general <strong>the</strong> fungus exhibits a preference <strong>for</strong> wet soil. The iron content <strong>of</strong> <strong>the</strong><br />

-<br />

soil, HCO 3 , salt and organic matter content, presence or absence <strong>of</strong> o<strong>the</strong>r microbes in soil are<br />

also important determinants <strong>of</strong> micro site preference by Trichoderma sp. The genus Trichoderma<br />

was introduced by Persoon almost two hundred years ago and was isolated from soil<br />

decomposing matter. Trichoderma <strong>for</strong> <strong>the</strong> most part classified as imperfect fungi in that <strong>the</strong>y<br />

produced only asexual spores; <strong>the</strong> sexual stage when found is within <strong>the</strong> Ascomycetes in <strong>the</strong><br />

genus Hypocrea (Harman, 2002), Rifai (1969) outlined <strong>the</strong> speciation concept within <strong>the</strong> genus<br />

Trichoderma and described nine species aggregates. With <strong>the</strong> use <strong>of</strong> molecular approaches<br />

particularly sequence polymorphism with internal transcribed spacer (ITS) regions <strong>of</strong> nuclear<br />

ribosomal DNA (rDNA), <strong>the</strong> texa recently have gone from nine to at least 35 species ( Hayes et al,<br />

1994). The conidiophores are highly ramified and phailides are flask shaped or ovoidal (Hermosa<br />

et al, 2000).<br />

Biocontrol Potential <strong>of</strong> Trichoderma species<br />

Since <strong>the</strong> pioneer work <strong>of</strong> Weindling, several reports on successful biocontrol <strong>of</strong> fungal<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

phytopathogens by Trichoderma sp. have accumulated. Among Trichoderm. most widely reported<br />

and commonly used biocontrol species are T.harzianum, T. viride and T. virens. They have been<br />

reported to inhibit many soil borne pathogenic fungi such as Fusarium, Pythuim, Sclerotium,<br />

Rhizoctonia, Sclerotinia, Macrophomia sp. etc., which are <strong>the</strong> major wilt causing fungal pathogens<br />

<strong>of</strong> various crops.<br />

T. harzianum has potential <strong>for</strong> biological control <strong>of</strong> sheath blight <strong>of</strong> rice by antagonizing <strong>the</strong><br />

pathogen Rhizoctonia solani (Tewari and Singh, 2005). Today Trichoderma strains are used <strong>for</strong><br />

biological control, ei<strong>the</strong>r alone or in combination with o<strong>the</strong>r microbes or chemical adjuvants. They<br />

are known to produce a wide range <strong>of</strong> antibiotic substances and parasitize o<strong>the</strong>r fungal phytopathogens.<br />

They also compete with o<strong>the</strong>r soil microorganisms <strong>for</strong> key exudates from seeds and<br />

roots that stimulate germination <strong>of</strong> propagules <strong>of</strong> plant pathogenic fungi in soil, nutrients and<br />

space. They are also known to produce certain lytic enzymes that degrade <strong>the</strong> cell wall <strong>of</strong> <strong>the</strong><br />

pathogen. Besides <strong>the</strong>se direct inhibitory effects on pathogens, Trichoderma sp. exerts beneficial<br />

effects on plant growth and development. These versatile fungi are highly efficient producers <strong>of</strong><br />

many extra-cellular enzymes like cellulases, chitinases, glucanases, proteases etc. Growth<br />

enhancement by Trichoderma sp. has been observed even in <strong>the</strong> absence <strong>of</strong> any detectable<br />

disease and in sterile soil and is not considered to be a side effect <strong>of</strong> suppression <strong>of</strong> disease or<br />

minor plant pathogens.<br />

Mechanisms Involved in Biocontrol <strong>of</strong> Fungal Phytopathogens by Trichoderma sp.<br />

Trichoderma sp. uses a variety <strong>of</strong> mechanisms to provide protection against several plant<br />

pathogens and/or plant diseases and enhance plant growth, such as it may (i) directly kill <strong>the</strong><br />

pathogens by mycoparasitism and/or antibiosis, (ii) adversely affect <strong>the</strong> growth and development<br />

<strong>of</strong> <strong>the</strong> pathogen by competing <strong>for</strong> <strong>the</strong> nutrients, oxygen or space (iii) alter fitness <strong>of</strong> <strong>the</strong> pathogen,<br />

(iv) induce systemic plant resistance, (v) enhance plant growth and its tolerance to stress, (vi)<br />

metabolize plant exudates supporting pathogen, and /or (vii) inactivate enzymes produced by <strong>the</strong><br />

pathogens and (viii) syn<strong>the</strong>size cell wall degrading enzymes (lytic enzymes) that degrade <strong>the</strong> cell<br />

wall <strong>of</strong> pathogen (Altomare et al., 1999).<br />

As an antagonist, Trichoderma may directly kill <strong>the</strong> pathogen ei<strong>the</strong>r by antibiosis or by<br />

mycoparasitism. The simplest technique to test <strong>the</strong> antagonism between a biocontrol agent and<br />

fungal plant pathogen is dual culture technique. Attachment <strong>of</strong> Trichoderma on to <strong>the</strong> host<br />

pathogen is followed by a series <strong>of</strong> degenerative events that promote osmotic imbalances<br />

triggering cell disruption. Host cell disruption may involve one or more cell wall degrading<br />

(hydrolytic) enzymes (CWDE) such as cellulases, chitinases, glucanases, proteases and/or<br />

xylanases and probably also peptaibol antibiotics ( Schirmbock et al, 1994). The combined<br />

activities <strong>of</strong> <strong>the</strong>se compounds result in parasitism <strong>of</strong> <strong>the</strong> target fungus and dissolution <strong>of</strong> <strong>the</strong> cell<br />

walls. T-harzianum exhibits excellent mycoparasitic activity against Rhizoctonia solani where as T.<br />

virens relies more on antibiosis against hyphae <strong>of</strong> this pathogen.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Antibiosis is <strong>the</strong> second major mechanism <strong>for</strong> biocontrol strategy employed by Trichoderma<br />

in <strong>the</strong> biocontrol <strong>of</strong> several fungal phytopathogens. Most Trichoderma strains produce volatile and<br />

nonvolatile toxic metabolites. Weindeling characterized <strong>the</strong> lethal principal excreated by strains <strong>of</strong><br />

T. lignorum into <strong>the</strong> medium as gliotoxin and demonstrated that it was toxic to both Rhizoctonia<br />

solani and Sclerotinia Americana. At present, Trichoderma is known to produce more than 43<br />

different types substances having antiobiotic activity such as gliotoxin, gliovirin, glioviridin, viridian,<br />

alkyl pyrons, isonitrils, polyketides, peptaibols, diketopiperazines, sesquiterpenes and some<br />

steroids. The production <strong>of</strong> secondary metabolites by Trichoderma sp. is strain dependent and<br />

includes anti fungal substances that have been classified into three categories: (i) volatile<br />

antibiotics, i.e. 6-pentyl-α-pyrone (6 PP) and most <strong>of</strong> <strong>the</strong> isocyanide derivatives, (ii) water soluble<br />

compounds such as heptelidic acid or koningic acid, (iii) peptaibols, that are linear oligopeptides <strong>of</strong><br />

12 to 22 amino acids rich in α – amino isobutyric acid, N-acetylated at <strong>the</strong> N-terminus and<br />

containing an amino alcohol at <strong>the</strong> C-terminus. The production <strong>of</strong> low molecular weight non polar<br />

volatile compounds (i.e. 6 PP) results in a high concentration antibiotic in <strong>the</strong> soil environment that<br />

has a relatively long distance range <strong>of</strong> influence on <strong>the</strong> microbial community (Fig 2).<br />

Figure 2: Phase 1: <strong>the</strong> mycoparasite produces high molecular weight compounds that reach <strong>the</strong><br />

host. Phase 2: low molecular weight-degradation products that are released from <strong>the</strong><br />

host cell walls reach <strong>the</strong> mycoparasite and activate <strong>the</strong> mycoparasitic gene expression<br />

cascade.(Schirmbock et al., 1994)<br />

A unique class <strong>of</strong> linear hydrophobic polypeptides called peptaibols, is produced by most<br />

species <strong>of</strong> Trichoderma. Many peptaibols such as Trichorzianin, trichokindins, harzianins,<br />

trikoninginus, tichokonins, trichogins etc. exhibit a broad range <strong>of</strong> bioactivities related to cell<br />

membrane perturbations (Wiest et al, 2002). They are thought to act on <strong>the</strong> membrane <strong>of</strong> <strong>the</strong><br />

target fungus to inhibit membrane associated enzymes involved in cell wall syn<strong>the</strong>sis. The<br />

apoptosis <strong>of</strong> <strong>the</strong> pathogen is associated with <strong>the</strong> alteration <strong>of</strong> membrane permeability, loss <strong>of</strong><br />

mitochondrial transmembrane potential, degeneration <strong>of</strong> cellular organelles, and degeradation <strong>of</strong><br />

DNA along with accumulation <strong>of</strong> vacuoles in <strong>the</strong> cytoplasm resulting in <strong>the</strong> programmed cell death.<br />

Recently, <strong>the</strong> antimicrobial peptaibols from Trichoderma pseudokoningii have been reported to<br />

induce programmed cell death in plant fungal pathogens, Fusarium (Mei Shiet et al, 2012).<br />

Trichokonins (TK VI), a type <strong>of</strong> peptaibol from Trichoderma pseudokoningii SMF2, exhibited<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

antibiotic activities against plant fungal pathogens (Fusarium oxysporum).<br />

Fig3: Mrphological changes in TK VI- treated cells <strong>of</strong> F. oxysporum<br />

Competition is considered as a classical mechanism <strong>of</strong> biocontrol that involves competition<br />

between antagonist and plant pathogens <strong>for</strong> space air and nutrients. The omni presence <strong>of</strong><br />

Trichoderma in agricultural and natural soils through out <strong>the</strong> world proves that it is an excellent<br />

competitor <strong>for</strong> space and nutritional resources. Nei<strong>the</strong>r antibiotic nor mycoparatism is mainly<br />

involved in biocontrol <strong>of</strong> seedling disease in cotton but competition is <strong>the</strong> main mechanism in that<br />

case. Trichoderma sp. also have <strong>the</strong> ability to induce systemic and localized resistance in many<br />

plants and this acts as an indirect biocontrol mechanism. Various plants mono- and dicotyledonous<br />

species showed increased resistance to pathogen attack when pre-treated with<br />

Trichoderma (Harman et al, 2004). The pathogenesis related (PR) proteins include anti fungal<br />

chitinases, glucanases and proteinases and oxidative enzymes such as peroxidases,<br />

polyphenoloxidases and lipoxygenases. Recently <strong>the</strong> molecular mechanism <strong>of</strong> resistance<br />

induction at gene level in plant by Trichoderma hamatum 382 was studied using high density<br />

oligonucleotide microarray approach. During interaction <strong>of</strong> Trichoderma with <strong>the</strong> plant, different<br />

classes <strong>of</strong> metabolites may act as elicitors or resistance introducers ( Lorito, 2007). Trichoderma<br />

strains produce 3 main classes <strong>of</strong> compounds that induce resistance in plants: proteins with<br />

enzymatic activities, avirulence like gene products able to induce defense reaction in plants and<br />

low molecular weight compounds released from fungal or plant cell walls by <strong>the</strong> activity <strong>of</strong><br />

Trichoderma enzymes.<br />

Some pathogens depend upon production <strong>of</strong> plant cell wall degrading enzymes to infect<br />

living plants; Botrytis cinerea produces pectinolytic, cutinolytic and cellulolytic enzymes to infect<br />

living plants. Secondary metabolites or proteolytic enzymes produced by Trichoderma may<br />

inactivate <strong>the</strong>se pathogens’ enzymes resulting in reduced ability <strong>of</strong> <strong>the</strong> pathogen to infect host<br />

plant. Proteolytic activity <strong>of</strong> T. viride was claimed to be involved in biocontrol <strong>of</strong> Sclerotium rolfsii in<br />

autoclaved soil. Attachment <strong>of</strong> Trichoderma to <strong>the</strong> host pathogen is followed by a series <strong>of</strong><br />

degenerating events and degeradation <strong>of</strong> cell wall <strong>of</strong> <strong>the</strong> pathogens by syn<strong>the</strong>sizing various cell<br />

wall degrading enzymes viz. chitinases, glucanases and proteinases.<br />

Biological control is <strong>of</strong> particular interest as a component <strong>of</strong> integrated pest management<br />

(IPM) and can best be exploited within <strong>the</strong> frame work <strong>of</strong> this management system. Combination <strong>of</strong><br />

<strong>the</strong> seed/root application <strong>of</strong> T-harzianum with soil solarization was very effective in management <strong>of</strong><br />

seed and seedling disease <strong>of</strong> tobacco, brinjal and capsicum in nursery at farmers’ fields. Wilt and<br />

root rot complex <strong>of</strong> chickpea, lentil and pigeon pea were successfully managed by integration <strong>of</strong> T.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

harzianum or T.virens with carboxin. Although, it is fact that use <strong>of</strong> biocontrol <strong>for</strong> disease<br />

management may not totally replace chemicals in near future, but, Judicious use <strong>of</strong> biocontrol<br />

agents such as Trichoderma sp. can significantly reduce our dependence on chemical pesticides<br />

and <strong>the</strong>re by contribute to sustainable agriculture. Not only this <strong>the</strong> biocontrol agents by replacing<br />

noxious chemical pesticides and also being more eco friendly in nature, help in clean up<br />

environment.<br />

REFERENCES<br />

• Harman, G.E. 2000. Myths and dogmas <strong>of</strong> Biocontrol: Changes in <strong>the</strong> perceptions derived from<br />

research on Trichoderma harzianum T-22. <strong>Plant</strong> Dis. 84: 377-393.<br />

• Cook, R.J. and Baker, K.F. 1983. The nature and practices <strong>of</strong> biological control <strong>of</strong> plant<br />

pathogens. APS Books, St. Paul. MN, U.S.A., pp 599<br />

• Weindling, R. 1932. Trichoderma lignorum as a parasite <strong>of</strong> o<strong>the</strong>r soil fungi. Phytopathology 22:<br />

834-845.<br />

• Harman, G.E. 2002. Trichoderma sp. including, T. harzianum, T.viride, T.koningii, T. hamatum and<br />

o<strong>the</strong>r spp. Deurteromycetes, Moniliales (asexual classification system). Biological<br />

Control. Cornell University, Geneva, NY. 144-56.<br />

• 5 . Rifai,M.A. 1969 .A revision <strong>of</strong> genus Trichoderma. Mycological Papers 116:1-56. .<br />

• Hayes, C.K., Klemsdal, S., Lorito, M., Di Pietro, A., Peterbauer, C., Nakasa, J.P., Tronsmo, A. and<br />

Harman, G.E. 1994. Isolation and sequence <strong>of</strong> an endochitinase –encoding gene<br />

from a cDNA library <strong>of</strong> Trichoderma harzianum. Gene 138: 143-148.<br />

• Hermosa,M.R., Grondona,I.,Iturriaga,E.A., Diaz-Minguez,J.M., Castro,C., Monte,E. and Garcia-<br />

Acha,I. 2000. Applied and Environmental Microbiology. 66 : 1890-1898.<br />

• Tewari,L. and Singh,R. 2005. Biological control <strong>of</strong> sheath blight <strong>of</strong> rice by Trichoderma harzianum<br />

using different delivery systems. Indian Phytopath. 58 (1): 35-40.<br />

• Altomare, C., Norvell, W.A., Bjorkman, T. and Harman, G.E. 1999. Solubilization <strong>of</strong> phosphates<br />

and micronutrients by <strong>the</strong> plant growth promoting biocontrol fungus Trichoderma<br />

harzianum Rifai 1295-22. Appl. Environ. Microbiol. 65: 2926-2933.<br />

• Schirmbock, M., Lorito, M., Wang, Y.L., Hayes, C.K., Artisan-Atac, I., Scala, F., Harman, G.E., and<br />

Kubicek, C.P. 1994. Parallel <strong>for</strong>mation and synergism <strong>of</strong> hydrolic enzymes and<br />

peptaibol antibiotics, molecular mechanisms involved in <strong>the</strong> antagonistic action <strong>of</strong><br />

Trichoderma harzianum against phytopathogenic fungi. Appl. Environ. Microbiol.<br />

60:4364-4370.<br />

• Wiest, A., Grezagorski, D., Xu, B., Goulard, C., Rebuffat, S., Ebbole, D. J., Bodo, B., and Kenerly,<br />

C. 2002. Identification <strong>of</strong> peptibols from Gliocladium virens and cloning <strong>of</strong> a peptibol<br />

syn<strong>the</strong>tase. J. Biol. Chem. 277 (23): 2086-2088.<br />

• Mei Shi,3 Lei Chen,3 Xiao-Wei Wang, Tian Zhang, Pei-Bao Zhao, Xiao-Yan Song, Cai-Yun Sun,<br />

Xiu-Lan Chen, Bai-Cheng Zhou and Yu-Zhong Zhang. 2012. Antimicrobial<br />

peptaibols from Trichoderma pseudokoningii induce programmed cell death in plant<br />

fungal pathogens. Microbiology (2012), 158, 166–175.<br />

• Harman,G.E., Howell, C.R., Viterbo,A., Cget,I. and Lorito, M. 2004.Trichoderma sp.- opportunistic,<br />

avirulent plant symbionts. Nature Reviews Microbiology. 2 (1) : 43-56.<br />

• Lorito M, Harman GE, Hayes CK, Broadway RM, Tronsmo A, Woo SL, Di Pietro A. 1993.<br />

Chitinolytic enzymes produced by Trichoderma harzianum: Antifungal activity <strong>of</strong><br />

purified endochitinase and chitobiosidase. Phytopathology 83:302-307.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Biological Control <strong>of</strong> <strong>Plant</strong> Diseases under Different Environments<br />

Introduction<br />

V. S. Pundhir and Bhupendra Singh Kharayat<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Traditional methods used to protect crops from diseases have been largely based on <strong>the</strong><br />

use <strong>of</strong> chemical pesticides. Applications <strong>of</strong> fungicides and fumigants can have drastic effects on<br />

<strong>the</strong> environment and consumer, and are <strong>of</strong>ten applied in greater quantities than herbicides and<br />

insecticides in agricultural production. Chemical methods are not economical in <strong>the</strong> long run<br />

because <strong>the</strong>y pollute <strong>the</strong> atmosphere, damage <strong>the</strong> environment, leave harmful residues, and can<br />

lead to <strong>the</strong> development <strong>of</strong> resistant strains among <strong>the</strong> target organisms with repeated use.<br />

Biological control involves <strong>the</strong> use <strong>of</strong> beneficial organisms, <strong>the</strong>ir genes, and/or products,<br />

such as metabolites, that reduce <strong>the</strong> negative effects <strong>of</strong> plant pathogens and promote positive<br />

responses by <strong>the</strong> plant. To date, a number <strong>of</strong> BCAs have been registered and are available as<br />

commercial products, including strains belonging to bacterial genera such as Agrobacterium,<br />

Pseudomonas, Streptomyces and Bacillus, and fungal genera such as Gliocladium, Trichoderma,<br />

Ampelomyces, Candida and Coniothyrium. Trichoderma spp. are among <strong>the</strong> most frequently<br />

isolated soil fungi and present in plant root ecosystems (Harman et al., 2004). These fungi are<br />

opportunistic, avirulent plant symbionts, and function as parasites and antagonists <strong>of</strong> many<br />

phytopathogenic fungi, thus protecting plants from disease. So far, Trichoderma spp. are among<br />

<strong>the</strong> most studied fungal BCAs and commercially marketed as biopesticides, bi<strong>of</strong>ertilizers and soil<br />

amendments (Harman et al., 2004). Depending upon <strong>the</strong> strain, <strong>the</strong> use <strong>of</strong> Trichoderma in<br />

agriculture can provide numerous advantages: (i) colonization <strong>of</strong> <strong>the</strong> rhizosphere by <strong>the</strong> BCA<br />

(‘‘rhizosphere competence’’) allowing rapid establishment within <strong>the</strong> stable microbial communities<br />

in <strong>the</strong> rhizosphere; (ii) control <strong>of</strong> pathogenic and competitive/deleterious micr<strong>of</strong>lora by using a<br />

variety <strong>of</strong> mechanisms; (iii) improvement <strong>of</strong> <strong>the</strong> plant health and (iv) stimulation <strong>of</strong> root growth<br />

(Harman et al., 2004).<br />

The ecological processes determining <strong>the</strong> successor o<strong>the</strong>r wise <strong>of</strong> biological control are<br />

complex, with <strong>the</strong> development <strong>of</strong> a general <strong>the</strong>ory made difficult by <strong>the</strong> diversity <strong>of</strong> target pests<br />

and biological control organisms. Sustainable biological control <strong>of</strong> plant pathogens depends on<br />

efficient exploitation <strong>of</strong> naturally-occurring micro-organisms. In an ideal crop ecosystem,<br />

interactions between plant pathogens and <strong>the</strong>ir antagonists in <strong>the</strong> infection court would suppress<br />

<strong>the</strong> initiation <strong>of</strong> infection <strong>of</strong> <strong>the</strong> host plant. The complex nature <strong>of</strong> phyllosphere ecology has, so far,<br />

militated against <strong>the</strong> development <strong>of</strong> successful biocontrol agents (BCA) <strong>for</strong> foliar plant pathogens.<br />

Their commercial exploitation in integrated pest or crop management (IPM/ICM) has been<br />

constrained by <strong>the</strong> costs <strong>of</strong> development, governmental policy and supra national directives.<br />

However, <strong>the</strong>re is optimism concerning future prospects and some demonstrated successes in<br />

greenhouse cultivation (. The need to predict <strong>the</strong> outcome <strong>of</strong> <strong>the</strong> interactions between a BCA, <strong>the</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

pathogen, <strong>the</strong> crop, <strong>the</strong> resident micr<strong>of</strong>lora and <strong>the</strong> environment has repeatedly been cited as <strong>the</strong><br />

way <strong>for</strong>ward to achieve reproducible biological control. The key to investigating dynamics <strong>of</strong> a<br />

biocontrol system is to understand <strong>the</strong> mechanisms involved in biocontrol, how <strong>the</strong>y interact and<br />

how <strong>the</strong>y are manifested at different hierarchical levels, from <strong>the</strong> infection court to <strong>the</strong> ecosystem<br />

scale. The principal mechanisms involved include mycoparasitism, antibiosis, competition and<br />

induced resistance. Additional mechanisms are through hypovirulence mediated through fungal<br />

viruses, now reported <strong>for</strong> <strong>the</strong> first time in Botrytis cinerea and enzymatic interference with<br />

pathogen pathogenicity enzymes. The characteristics <strong>of</strong> BCA are such that slight changes in<br />

external environment could result in drastic changes in <strong>the</strong> system dynamics and hence biocontrol<br />

efficacies. This may explain <strong>of</strong>ten observed inconsistencies in biocontrol efficacy in practice since<br />

spatiotemporal environmental heterogeneity is a rule ra<strong>the</strong>r than an exception. Implementation <strong>of</strong><br />

biological control is fraught with constraints, and successful application depends on a thorough<br />

knowledge <strong>of</strong> <strong>the</strong> ecology and biology <strong>of</strong> both <strong>the</strong> target pest and <strong>the</strong> biological control agent.<br />

Although biocontrol has been effective in controlling a range <strong>of</strong> plant diseases, <strong>the</strong>re are various<br />

reports in <strong>the</strong> literature that question its general effectiveness (Cook, 1993). Vasudevan et al.<br />

(2002) observed that this inconsistency in per<strong>for</strong>mance has plagued researchers and <strong>the</strong>ir ef<strong>for</strong>ts<br />

to exploit biocontrol agents <strong>for</strong> commercial use. It generally is acknowledged that disease<br />

suppression by biological control is <strong>the</strong> result <strong>of</strong> complex interactions among <strong>the</strong> antagonist, <strong>the</strong><br />

pathogen, <strong>the</strong> host plant and its associated microbial community, and <strong>the</strong> physical environment<br />

(Handelsman and Stabb, 1996; Andrews and Harris 2000; Kinkel, 1997; Whipps, 2001). However,<br />

we are unaware <strong>of</strong> quantitative studies to syn<strong>the</strong>size data on <strong>the</strong> relative efficacy <strong>of</strong> a range <strong>of</strong><br />

biocontrol agents in suppressing plant disease in relation to biological and application-oriented<br />

factors. As such, several fundamental questions regarding <strong>the</strong> level <strong>of</strong> disease suppression by<br />

biocontrol agents still remain unanswered. For example, is biological control generally more<br />

successful <strong>for</strong> soilborne or <strong>for</strong> aerial diseases? To what extent is its effectiveness determined by<br />

overall disease pressure? Is biocontrol really more effective in <strong>the</strong> greenhouse than in <strong>the</strong> field, as<br />

is assumed generally (Paulitz and Bélanger, 2001) ? Are <strong>the</strong>re certain factors related to <strong>the</strong><br />

biology <strong>of</strong> <strong>the</strong> pathogen or <strong>the</strong> biocontrol agent (e.g., fungus versus bacterium, r- versus K-<br />

selected life history) that help predict success or failure <strong>of</strong> biological control? And how significant<br />

and consistent are <strong>the</strong>se effects across a wide range <strong>of</strong> antagonist–disease combinations?<br />

Disease suppression, as mediated by biocontrol agents, is <strong>the</strong> consequence <strong>of</strong> <strong>the</strong> interactions<br />

between <strong>the</strong> plant, pathogens, and <strong>the</strong> microbial community. Basic environmental conditions, such<br />

as temperature, moisture, sunlight, and soil physical and chemical characteristics, can greatly<br />

affect <strong>the</strong> physiology <strong>of</strong> <strong>the</strong> host plant and subsequent disease development, as well as alter <strong>the</strong><br />

interactions among plant, pathogen, and biocontrol agent in various ways. This is in addition to<br />

potential direct effects on <strong>the</strong> pathogen and biocontrol organisms and o<strong>the</strong>r soil microbes, and all<br />

<strong>of</strong> <strong>the</strong>se effects may influence efficacy <strong>of</strong> biological control. O<strong>the</strong>r conditions related to <strong>the</strong> specific<br />

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pathosystem involved, such as <strong>the</strong> occurrence <strong>of</strong> different pathogenic races and variability in<br />

disease resistance and susceptibility among host cultivars, also affect <strong>the</strong> disease response and<br />

may influence biological control.<br />

Biological control under different environments:<br />

As <strong>the</strong> plant and plant pathogens adapted to different ecological environments viz.<br />

phylosphere to rhizosphere, aquatic system (rice-pathosystem) to terrestrial ecosystem, annual to<br />

perennial tree ecosystem and tropical to subtropical environments. Being biological <strong>the</strong>se<br />

microorganism have to be applied in accordance with <strong>the</strong>ir ecological requirements.<br />

Biological control in phylosphere<br />

Kiss (2003) reviewed <strong>the</strong> ecology, modes <strong>of</strong> action and biocontrol efficacy <strong>of</strong> <strong>the</strong><br />

approximately 40 fungal species that have been reported as natural antagonists <strong>of</strong> powdery<br />

mildews or have been tested as potential biocontrol agents. Of <strong>the</strong>se, pycnidial fungi belonging to<br />

<strong>the</strong> genus Ampelomyces Ces. are <strong>the</strong> oldest known and <strong>the</strong> commonest natural antagonists <strong>of</strong><br />

powdery mildews that have been intensively studied in crop protection practice. In addition, <strong>the</strong><br />

interactions between host plants, powdery mildew fungi and Ampelomyces mycoparasites are one<br />

<strong>of</strong> <strong>the</strong> most evident cases <strong>of</strong> tritrophic relationships in nature, because this relationship is common<br />

world-wide and takes place exclusively on aerial plant surfaces, thus facilitating its direct<br />

observation (Kiss, 1998). However, it has received little attention in fungal and plant ecology,<br />

although it could be used as a model to study <strong>the</strong> significance <strong>of</strong> mycoparasitism in <strong>the</strong> natural<br />

dynamics <strong>of</strong> plant parasitic fungi. Some biocontrol fungi have more than one mechanism to<br />

antagonize <strong>the</strong>ir hosts. Trichoderma spp., <strong>for</strong> example, produces antifungal compounds, act as<br />

mycoparasites, induce plant defence mechanisms and can stimulate plant growth (Howell, 2003).<br />

In contrast, Ampelomyces acts directly by invasion and destruction <strong>of</strong> host cytoplasm.<br />

Ampelomyces kills <strong>the</strong> parasitized powdery mildew cells by causing a rapid degeneration <strong>of</strong> <strong>the</strong><br />

cytoplasm (Hashioka and Nakai, 1980). These mycoparasites suppress both asexual and sexual<br />

sporulation <strong>of</strong> <strong>the</strong> attacked powdery mildew mycelia by colonizing and destroying <strong>the</strong><br />

conidiophores, and <strong>the</strong> immature ascocarps, respectively. The early stage <strong>of</strong> Mycoparasitism is<br />

apparently biotrophic, but <strong>the</strong> invaded cytoplasm <strong>the</strong>n begins to die and a necrotrophic interaction<br />

results (Hashioka and Nakai, 1980; Sundheim and Krekling, 1982).<br />

Biological control in perennial tree ecosystem<br />

Root rot caused by Heterobasidion annosum sensu lato (Fr.) Bref. is one <strong>of</strong> <strong>the</strong> most<br />

destructive diseases <strong>of</strong> coniferous trees in <strong>the</strong> Nor<strong>the</strong>rn Hemisphere. The annual economic losses<br />

caused by this fungus in Europe are estimated to at least 790 million €. The main route <strong>of</strong> infection<br />

<strong>for</strong> H. annosum s.l. is by basidiospores germinating on <strong>the</strong> stump surface after tree felling during<br />

summer periods. Thereafter <strong>the</strong> fungus invades neighboring healthy trees via root contact<br />

(Redfern and Stenlid, 1998). Currently, Phlebiopsis gigantea (Fr.) Jül., a common saprotrophic<br />

wood-decay basidiomycete and a highly competitive primary colonizer on conifer wood, is used as<br />

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an effective biological control agent against Heterobasidion in many European countries<br />

(Korhonen et al., 1993). One <strong>of</strong> <strong>the</strong> most commonly used <strong>for</strong>mulas <strong>of</strong> P. gigantea is registered as<br />

Rotstop. A biocontrol method to reduce H. annosum s.l. infection is to apply <strong>the</strong> wood degrading<br />

fungus Phlebiopsis gigantea in a spore solution (Rotstop) directly on <strong>the</strong> freshly cut stumps<br />

immediately after cutting.<br />

Biological control in rhizospheric disease<br />

Wilt<br />

The use <strong>of</strong> biocontrol agents to control Fusarium wilt has been reported <strong>for</strong> many crops<br />

including tomato, cucumber, melon, strawberry, banana and carnation. Several reports have<br />

previously demonstrated <strong>the</strong> successful use different species <strong>of</strong> Trichoderma, Pseudomonas,<br />

Streptomyces, non pathogenic Fusarium (npFo) <strong>of</strong> both rhizospheric and endophytic in nature<br />

against Fusarium wilt disease under both glass house and field conditions (Alabouvette et al.<br />

1993; Getha et al. 2005). Several reports indicate that Trichoderma species can effectively<br />

suppress Fusarium wilt pathogens (Sivan and Chet, 1986). Georgios et al. (2007) have been used<br />

two known Pseudomonas biocontrol strains separately and in combination to assess <strong>the</strong>ir<br />

antagonistic effectiveness against F. oxysporum f. sp. niveum in pot experiments. P. chlororaphis<br />

PCL1391 significantly reduced disease severity. P. fl uorescens WCS365 was less effective in<br />

disease suppression, while a combination <strong>of</strong> <strong>the</strong> two bacteria had intermediate effects. He also<br />

noted that biological control <strong>of</strong> Fusarium wilt with P. chlororaphis <strong>of</strong>fers a potentially useful tool in<br />

an integrated pest management program to control Fusarium wilt <strong>of</strong> watermelon.<br />

Root rot and Dampig-<strong>of</strong>f<br />

Damping-<strong>of</strong>f and root rot on greenhouse cucumbers, mainly caused by a number <strong>of</strong><br />

Pythium spp., including P. aphanidermatum, P. ultimum and P. irregular, are recurring problems<br />

<strong>for</strong> growers. Biological control <strong>of</strong> damping-<strong>of</strong>f and root rot <strong>of</strong> cucumber caused by various Pythium<br />

spp. have identified nonpathogenic (mycoparasitic) Pythium spp. and a number <strong>of</strong> bacterial<br />

antagonists, primarily Pseudomonas spp. (Paulitz and Bélanger 2001) and Bacillus subtilis<br />

(Ehrenberg) Cohn as potential biocontrol agents, which were shown to significantly reduce disease<br />

severity. In addition, <strong>the</strong> biocontrol agents S. griseoviridis and T. harzianum in Mycostop and<br />

Rootshield, respectively, are reported to be effective against damping-<strong>of</strong>f and root rot diseases<br />

caused by Pythium spp. (Paulitz and Bélanger 2001).<br />

Biological control <strong>of</strong> plant parasitic nematodes<br />

Biological control <strong>of</strong> nematodes is <strong>the</strong> use <strong>of</strong> microbial agents such as bacteria and fungi<br />

that reduce nematode population by <strong>the</strong>ir antagonistic behaviour. Fungi continuously destroy<br />

nematodes in virtually all soils because <strong>of</strong> <strong>the</strong>ir constant association with nematodes in <strong>the</strong><br />

rhizosphere. Pasteuria penetrans has been <strong>the</strong> subject <strong>of</strong> intensive study as a promising biological<br />

control agent <strong>of</strong> nematodes. A large number <strong>of</strong> nematophagous fungi are known to trap or prey on<br />

nematodes, but <strong>the</strong> most imporant genera include Arthrobotrys, Monacrosporium, Nematophthora,<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Hirsutella, Verticillium and Paecilomyces. Application <strong>of</strong> some <strong>of</strong> <strong>the</strong>se fungi in vegetable crops<br />

has given interesting results. Integrated nematode management can be realized by variety <strong>of</strong><br />

techniques including predators and parasites, genetic resistance <strong>of</strong> host, soil amendment with<br />

organic matter and o<strong>the</strong>r cultural practices. Few commercial preparations <strong>of</strong> <strong>the</strong>se fungi are also<br />

available in <strong>the</strong> market.<br />

Non-target effects <strong>of</strong> fungi used to biologically control plant diseases<br />

While effective in <strong>the</strong> control <strong>of</strong> plant diseases, <strong>the</strong>se mechanisms may pose risks to nontarget<br />

species including mycorrhizal and saprophytic fungi, soil bacteria, plants, insects, aquatic<br />

and terrestrial animals, and humans. Non-target effects including mycoparasitism <strong>of</strong> mycorrhizae,<br />

reduction in plant root colonisation by mycorrhizal fungi, disorders in commercial mushrooms and<br />

nodulation by Rhizobium spp., and changes in plant growth have been associated with fungal<br />

biological control agents, such as Trichoderma spp. Also, <strong>the</strong> genera Trichoderma and<br />

Gliocladium have been linked to respiratory disorders and shellfish toxicity in humans,<br />

respectively. Biological control agents, such as Pythium oligandrum, Talaromyces flavus,<br />

Coniothyrium minitans and Ampelomyces quisqualis have modes <strong>of</strong> action which may pose risks<br />

to non-target fungi, bacteria, plants and animals. There is need <strong>for</strong> future research into ecological<br />

impacts associated with <strong>the</strong> release <strong>of</strong> any biological agent and methods <strong>of</strong> determining possible<br />

non-target effects. Adequate monitoring and <strong>the</strong> use <strong>of</strong> molecular techniques to identify and follow<br />

<strong>the</strong> movement <strong>of</strong> biological control agents are needed to examine and mitigate negative biological<br />

impacts (Theresa and Boland, 2003).<br />

Future Prospects<br />

One <strong>of</strong> <strong>the</strong> biggest ecological challenges facing microbiologists and plant pathologists in<br />

<strong>the</strong> near future is <strong>the</strong> development <strong>of</strong> environmentally friendly alternatives to <strong>the</strong> extensive use <strong>of</strong><br />

chemical pesticides <strong>for</strong> combating crop diseases. The use <strong>of</strong> beneficial microorganisms<br />

(biopesticides) is considered one <strong>of</strong> <strong>the</strong> most promising methods <strong>for</strong> more rational and safe cropmanagement<br />

practices. In <strong>the</strong> short term, <strong>the</strong> technology already exists to directly identify<br />

biocontrol agents active against target pathogens, to select strains with an affinity <strong>for</strong> particular<br />

crops or cultivars, to engineer strains <strong>for</strong> greater efficacy and reliability, and to develop and exploit<br />

soils naturally suppressive to particular pathogens. For specific pathosystems, how does <strong>the</strong><br />

environment influence <strong>the</strong> asymptotic limit to biological control? Can asymptotic limits to biocontrol<br />

be shifted by new, mixed, or altered technologies?<br />

REFERENCES<br />

• Alabouvette, C.; Lemanceau, P. and Steinberg, C.1993. Recent advances in <strong>the</strong> biological control<br />

<strong>of</strong> Fusarium wilts. Pesticides Science. 37:365–373.<br />

• Andrews, J. H. and Harris, R. F. 2000. The ecology and biogeography <strong>of</strong> microorganisms on plant<br />

surfaces. Annu. Rev. Phytopathol. 38:145-180.<br />

• Cook, R. J. 1993. Making greater use <strong>of</strong> introduced microorganisms <strong>for</strong> biological control <strong>of</strong> plant<br />

pathogens. Annu. Rev. Phytopathol. 31:53-80.<br />

• Georgios T.T.; Anastasia, L. and Katina T.K. 2007. Reduction <strong>of</strong> Fusarium wilt in watermelon by<br />

- 145 -


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Pseudomonas chlororaphis PCL1391 and P. fl uorescens WCS365. Phytopathol.<br />

Mediterr. 46: 320–323<br />

• Getha K.; Vikineswary, S.; Wong, W.; Seki, T.; Ward, A. and Goodfellow, M. 2005. Evaluation <strong>of</strong><br />

Streptomyces sp. strain G10 <strong>for</strong> suppression <strong>of</strong> Fusarium wilt and rhizosphere<br />

colonization in pot grown banana plantlets. Journal <strong>of</strong> Industrial Microbiology and<br />

Biotechnology. 32: 24-32.<br />

• Handelsman, J. and Stabb, E. V. 1996. Biocontrol <strong>of</strong> soilborne plant pathogens. <strong>Plant</strong> Cell<br />

8:1855-1869.<br />

• Hashioka, Y. and Nakai, Y. 1980. Ultrastructure <strong>of</strong> pycnidial development and mycoparasitism <strong>of</strong><br />

Ampelomyces quisqualis parasitic on Erysiphales. Transactions <strong>of</strong> <strong>the</strong> Mycological<br />

Society <strong>of</strong> Japan 21, 329-338.<br />

• Howell, C.R. 2003. Mechanisms employed by Trichoderma species in <strong>the</strong> biological control <strong>of</strong><br />

plant diseases: <strong>the</strong> history and evolution <strong>of</strong> current concepts. <strong>Plant</strong> Disease. 87: 4-<br />

10.<br />

• Kinkel, L. L. 1997. Microbial population dynamics on leaves. Annu. Rev. Phytopathol. 35:327-347.<br />

• Kiss, L. 2003. A review <strong>of</strong> fungal antagonists <strong>of</strong> powdery mildews and <strong>the</strong>ir potential as biocontrol<br />

agents. Pest <strong>Management</strong> Science. 59: 475-483.<br />

• Loliam, B.; Morinaga, T. and Chaiyanan S. 2012. Biocontrol <strong>of</strong> Phytophthora infestans, fungal<br />

pathogen <strong>of</strong> seedling damping <strong>of</strong>f disease in economic plant nursery. Hindawi<br />

Publishing Corporation Psyche. Volume 2012, Article ID 324317, 6 pp.<br />

doi:10.1155/2012/324317<br />

• Paulitz, T. C. and Bélanger, R. R. 2001. Biological control in greenhouse systems. Annu. Rev.<br />

Phytopathol. 39:103-133.<br />

• Sikora, R.A. 1992. <strong>Management</strong> <strong>of</strong> <strong>the</strong> antagonistic potential in agricultural ecosystems <strong>for</strong> <strong>the</strong><br />

biological control <strong>of</strong> plant-parasitic nematodes. Ann. Rev. Phytopathol. 30: 245-270.<br />

• Sivan, A. and Chet, I.1986. Biological control <strong>of</strong> Fusarium spp. in cotton, wheat and muskmelon by<br />

Trichoderma harzianum. J.Phytopathol. 116: 39–47.<br />

• Stirling, G.R. 1991. Biological control <strong>of</strong> plant-parasitic nematodes. Walling<strong>for</strong>d, UK, CAB<br />

International. 282 pp.<br />

• Sundheim, L. and Krekling, T. 1982. Host-parasite relationships <strong>of</strong> <strong>the</strong> hyperparasite<br />

Ampelomyces quisqualis and its powdery mildew host Sphaero<strong>the</strong>ca fuliginea .<br />

Journal <strong>of</strong> Phytopathology.104:202-210.<br />

• Theresa, A.B. and Boland, G.J. 2003. A review <strong>of</strong> <strong>the</strong> non-target effects <strong>of</strong> fungi used to<br />

biologically control plant diseases. Agriculture, Ecosystems and Environment.100:3-<br />

16.<br />

• Vasudevan, P.; Kavitha, S.; Priyadarisini, V. B.; Babujee, L. and Gnanamanickam, S. S. 2002.<br />

Biological control <strong>of</strong> rice diseases. in: Biological Control <strong>of</strong> Crop Diseases. S. S.<br />

Gnanamanickam, ed. Marcel Dekker, New York. p387-420.<br />

• Whipps, J. M. 2001. Microbial interactions and biocontrol in <strong>the</strong> rhizosphere. J. Exp. Bot. 52:487-<br />

511.<br />

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Introduction<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

<strong>Microbe</strong>s and <strong>Soil</strong> Quality<br />

Kiran P. Raverkar<br />

Department <strong>of</strong> <strong>Soil</strong> Science, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

<strong>Soil</strong> is a very valuable natural resource and wonderful gift <strong>of</strong> nature to <strong>the</strong> human being<br />

which per<strong>for</strong>ms infinite functions. The agriculture related main ecological functions fulfilled through<br />

soil include i) production <strong>of</strong> biomass ii) various filtering, buffering and trans<strong>for</strong>ming actions, and iii)<br />

a niche <strong>for</strong> biological habitat and gene reserve. It is critical <strong>for</strong> <strong>the</strong> maintenance <strong>of</strong> any ecosystem;<br />

<strong>the</strong>re<strong>for</strong>e, <strong>the</strong> well being <strong>of</strong> soil is pivotal <strong>for</strong> <strong>the</strong> sustenance and survival <strong>of</strong> <strong>the</strong> life on <strong>the</strong> earth. As<br />

per <strong>the</strong> <strong>Soil</strong> Science Society <strong>of</strong> America “soil quality is <strong>the</strong> capacity <strong>of</strong> a specific kind <strong>of</strong> soil to<br />

function within natural or managed ecosystem boundaries to sustain plant and animal productivity,<br />

maintain or enhance water and air quality, and support human health and habitation”. The soil<br />

quality dictates <strong>the</strong> four main horizons <strong>of</strong> <strong>the</strong> life which are interrelated (Fig. 1).<br />

<strong>Soil</strong> Productivity<br />

Human/Animal<br />

Health<br />

<strong>Soil</strong> Quality<br />

Food quality/<br />

safety<br />

Environmental<br />

quality<br />

Fig.1: Horizons <strong>of</strong> <strong>the</strong> life influenced by soil quality<br />

The physical, chemical and biological are <strong>the</strong> main components <strong>of</strong> soil quality. The physical<br />

as well as chemical properties are governed by <strong>the</strong> microbial world <strong>of</strong> soil. The biological<br />

properties which can be measured as indices <strong>of</strong> <strong>the</strong> soil quality mainly include potentially<br />

mineralizable N, microbial biomass, soil respiration, different enzymatic activities etc. <strong>Soil</strong> microbial<br />

biomass indicates <strong>the</strong> soil microbial population whereas <strong>the</strong> soil respiration tells about to <strong>the</strong><br />

metabolic activity. <strong>Soil</strong> is a reservoir <strong>of</strong> most <strong>of</strong> <strong>the</strong> enzymes <strong>of</strong> microbial as well as plant origin.<br />

Some enzymes such as dehydrogenases are <strong>of</strong> general importance whereas phosphatases<br />

indicate <strong>the</strong> specific activity <strong>of</strong> microorganisms. H<strong>of</strong>fmann and Seegerer (1950) was <strong>the</strong> first to<br />

propose <strong>the</strong> use <strong>of</strong> enzymes as an index <strong>of</strong> <strong>the</strong> fertility status <strong>of</strong> soil. The integrative activity <strong>of</strong><br />

number <strong>of</strong> soil enzymes has been proposed to predict soil fertility vis-à-vis soil quality. This<br />

approach reflects <strong>the</strong> release <strong>of</strong> nutrients during organic matter turnover as well as relative<br />

availability <strong>of</strong> inorganic nutrients over <strong>the</strong> estimation <strong>of</strong> activity <strong>of</strong> single enzyme. By employing <strong>the</strong><br />

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cluster analysis Zhou and Co-workers (1983) grouped Chinese soils into four fertility classes. Qui<br />

et al (1981) also reported a positive correlation between enzyme activities and fertility levels.<br />

During organic matter decomposition <strong>the</strong> activities <strong>of</strong> various enzymes releases <strong>the</strong> specific plant<br />

nutrients and thus <strong>the</strong>ir activity correlates with <strong>the</strong> soil fertility status.<br />

<strong>Microbe</strong>s and <strong>the</strong>ir role<br />

The microorganisms present underneath and on <strong>the</strong> surface layers <strong>of</strong> soil plays a pivotal<br />

role in sustaining <strong>the</strong> soil fertility and plant health <strong>for</strong> crop production due to <strong>the</strong>ir intrinsic/ acquired<br />

abilities to per<strong>for</strong>m an array <strong>of</strong> roles such as soil humus <strong>for</strong>mation, biological control <strong>of</strong> pests,<br />

growth promotions, soil tilth and structure (Lynch and Bragg, 1985). Belowground diversity<br />

encompasses a spectrum <strong>of</strong> microbes including bacteria, fungi, actinomycetes, algae and<br />

protozoa. The plants secrete various carbon rich compounds in <strong>the</strong> rhizosphere which are used as<br />

source <strong>of</strong> carbon by <strong>the</strong> microbial community <strong>for</strong> its maintenance and to function. The plants are<br />

dependent <strong>for</strong> <strong>the</strong>ir nutrition on <strong>the</strong> abilities <strong>of</strong> <strong>the</strong> microorganisms to make <strong>the</strong> various nutrients<br />

available e.g. nitrogen, phosphorus, iron etc. Out <strong>of</strong> <strong>the</strong> myriad population some microorganism<br />

<strong>for</strong>ms <strong>the</strong> close association with plants that could be beneficial, neutral or detrimental to <strong>the</strong> plant.<br />

Ecosystems in nature are generally in equilibrium state which supports <strong>the</strong> sustainable<br />

biomass production <strong>for</strong> human use maintaining <strong>the</strong> quality <strong>of</strong> natural base. However, <strong>the</strong><br />

interventions introduced <strong>for</strong> enhanced agricultural production results in disturbed ecosystem vis-àvis<br />

deteriorated quality <strong>of</strong> natural base. The “green revolution” in India was fuelled through <strong>the</strong> use<br />

<strong>of</strong> plant genotypes highly responsive to chemical sources <strong>of</strong> nutrients, especially nitrogen. The<br />

long term sustainability <strong>of</strong> agricultural ecosystems, which are dependent on <strong>the</strong> use <strong>of</strong> chemical<br />

fertilizers and modern intensive practices <strong>of</strong> cultivation, maintaining <strong>the</strong> surrounding environment<br />

intact is under question since recent past.<br />

Human population in <strong>the</strong> world is flattening over <strong>the</strong> years and would reach to 9 billion mark<br />

by <strong>the</strong> year 2020. The challenge <strong>of</strong> meeting <strong>the</strong> need <strong>for</strong> food <strong>of</strong> exploding population over <strong>the</strong><br />

time could only be achieved through intensification <strong>of</strong> <strong>the</strong> agriculture using modern technologies<br />

(Borlogue and Dowswell, 1994), considering <strong>the</strong> sustainability aspects. The sustainable agriculture<br />

addresses <strong>the</strong> judicious management <strong>of</strong> varying natural resources satisfying <strong>the</strong> changing human<br />

needs while maintaining/ improving <strong>the</strong> quality <strong>of</strong> natural resource base and environment. Among<br />

<strong>the</strong> various natural resources soil is <strong>the</strong> prime and thus it becomes imperative to maintain/improve<br />

<strong>the</strong> health <strong>of</strong> it. If <strong>the</strong> soil is sick it reflects immediately on <strong>the</strong> tiny creatures <strong>of</strong> <strong>the</strong> soil i.e. microbes<br />

and thus soil biological properties would indicate <strong>the</strong> wellbeing <strong>of</strong> <strong>the</strong> soil. Estimation <strong>of</strong> group <strong>of</strong><br />

soil properties, thus, to understand <strong>the</strong> impact <strong>of</strong> various management practices on soil health is a<br />

good and sound proposal. The various physical, chemical and biological soil quality indicators are<br />

listed in Table 1.<br />

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Table 1. Physical, chemical and biological soil quality indicators<br />

Chemical indicators Physical indicators Biological indicators<br />

Cation exchange Aggregate stability Microbial biomass<br />

capacity<br />

Bulk density<br />

Biomass C/N<br />

pH<br />

Aeration<br />

Potentially mineralizable<br />

Electrical conductivity<br />

Contaminants presence,<br />

Hydraulic<br />

conductivity<br />

nitrogen<br />

<strong>Soil</strong> respiration<br />

concentration, mobility Consistence<br />

<strong>Soil</strong> enzymes (Phosphatase,<br />

etc.<br />

Total N & P etc.<br />

WHC<br />

dehydrogenase,<br />

arylsulphatase)<br />

Organic matter<br />

<strong>Soil</strong> Quality components<br />

<strong>Soil</strong> quality comprises inherent as well as dynamic soil quality parameters. Inherent soil<br />

quality defines <strong>the</strong> inherent capacity <strong>of</strong> a soil <strong>for</strong> crop growth. It depends on <strong>the</strong> properties which<br />

are static, changing little over short time frame (years to decade) as developed as <strong>the</strong> product <strong>of</strong><br />

soil <strong>for</strong>mation. While dynamic soil quality is based on <strong>the</strong> properties that change over short time<br />

frame (years to decade) and influenced by land use management and agronomic practices.<br />

Major services provided by soil<br />

<strong>Soil</strong> function in many ways and provides various services <strong>for</strong> keeping <strong>the</strong> environment<br />

sustainable <strong>for</strong> <strong>the</strong> life on earth. The major services provided by soil are:<br />

• Trans<strong>for</strong>mation <strong>of</strong> carbon through decomposition <strong>of</strong> plant residues including SOM<br />

◦ Essential ecosystem function<br />

◦ Driver <strong>of</strong> nutrient cycling<br />

◦ Also supports detoxification and<br />

◦ Waste disposal service<br />

◦ C-sequestration: role in regulating emission <strong>of</strong> GHG e.g. CO 2 and CH 4<br />

• Cycling <strong>of</strong> nutrients: N, P, K including N2O emissions<br />

• Maintenance <strong>of</strong> structure and fabric <strong>of</strong> <strong>the</strong> soil<br />

◦ <strong>Soil</strong> aggregation<br />

◦ Particle transport<br />

◦ Formation <strong>of</strong> biostructures<br />

◦ Pore networks<br />

• Biological regulation <strong>of</strong> soil population<br />

<strong>Soil</strong> is composed <strong>of</strong> solid, liquid and gaseous phases and is dominated by solid phase.<br />

However <strong>for</strong> <strong>the</strong> sustenance <strong>of</strong> soil health <strong>the</strong> balance between <strong>the</strong>se three phase is very<br />

important.<br />

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Microorganisms: key functions in soil<br />

In top soil biological components occupy


(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

compared (Karlen et al, 2000). For monitoring <strong>the</strong> soil health policy relevant end points are very<br />

important. The end points should be pragmatic which can provide logical categories fro regulatory<br />

decisions and should be integrated <strong>for</strong> indicators that are ecologically related. An end point matrix<br />

has been suggested (Fig. 2), which provides a comprehensive and effective assessment <strong>of</strong> soil<br />

health when integrated toge<strong>the</strong>r (Nielsen and Winding, 2002).<br />

Pressure on soil health<br />

Climate, natural events, urbanisation,<br />

agriculture, <strong>for</strong>estry, waste disposal<br />

etc.<br />

Atmospheric<br />

balance<br />

<strong>Soil</strong> health<br />

<strong>Plant</strong> health<br />

Animal<br />

health<br />

Human<br />

health<br />

<strong>Soil</strong> microbial<br />

community<br />

health<br />

Fig. 2: Policyrelevant<br />

end points <strong>of</strong> soil health<br />

Leaching to gr.<br />

Water<br />

Surface run-<strong>of</strong>f<br />

monitoring<br />

Driving <strong>for</strong>ce-Pressure-State-Impact-Response (DPSIR) assessment<br />

<strong>Soil</strong><br />

ecosystem<br />

health<br />

Relevant indicators <strong>of</strong> specific end points have been identified based on DPSIR<br />

assessment framework, that has been developed primarily <strong>for</strong> environmental issues. The DPSIR<br />

framework can be employed <strong>for</strong> assessment <strong>of</strong> soil health provided <strong>the</strong> indicators <strong>for</strong> each <strong>of</strong> <strong>the</strong><br />

PSI-elements developed (Huber et ai, 2001). The DPSIR assessment framework applied to soil is<br />

depicted in Fig.3.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Re<strong>for</strong>m <strong>of</strong> environmental policy<br />

Changing mgnt. practices<br />

Responses<br />

Changes in soil functions<br />

Changes in crop yields<br />

Loss <strong>of</strong> biodiversity<br />

Impacts<br />

Agriculture<br />

Driving <strong>for</strong>ce<br />

Over grazing<br />

Over fertilization<br />

Intensive cropping<br />

Wastes recycled to land<br />

Pressures<br />

State<br />

Contamination<br />

Nutrient leaching to<br />

ground water<br />

Fig.3. The DPSIR assessment framework <strong>for</strong> soil<br />

Criteria specific to soil health indicators<br />

Doran and Safley (1997) have listed certain criteria <strong>for</strong> soil health indicators. The soil health<br />

indicators should be:<br />

linked and/or correlated with ecosystem processes<br />

• integrated with soil physical, chemical, and biological properties<br />

• selected relative to ease <strong>of</strong> per<strong>for</strong>mance and cost effectiveness<br />

• responsive to variations in management and climate at an appropriate time scale<br />

• compatible with existing soil data bases when possible<br />

Since <strong>the</strong> soil fulfills <strong>the</strong> diversified functions through various services to <strong>the</strong> planet earth it<br />

is difficult to identify and rely on one single property <strong>for</strong> assessment <strong>of</strong> soil health. Instead <strong>of</strong><br />

evaluating <strong>the</strong> psoil health based on single parameter(s) independently it is wise to employ <strong>the</strong><br />

DPSIR concept characterizing <strong>the</strong> end points through several soil ecosystem parameters (Table<br />

3).<br />

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Table 3. End points <strong>for</strong> monitoring soil health through soil ecosystem parameters<br />

End point<br />

Atmospheric balance<br />

<strong>Soil</strong> ecosystem health<br />

<strong>Soil</strong> microbial community health<br />

Leaching to groundwater or<br />

surface run-<strong>of</strong>f<br />

<strong>Plant</strong> health<br />

Animal health<br />

Human health<br />

<strong>Soil</strong> ecosystem parameter<br />

C-cycling<br />

Biodiversity<br />

C-cycling<br />

N-cycling<br />

Microbial biomass<br />

Microbial activity<br />

Key species<br />

Biodiversity<br />

C- cycling<br />

Microbial biomass<br />

Microbial activity<br />

Bioavailability<br />

N-cycling<br />

Bioavailability<br />

N-cycling<br />

Key species<br />

Microbial biomass<br />

Bioavailability<br />

Key species<br />

Bioavailability<br />

Microbial indicators <strong>of</strong> soil health<br />

Microbial indicators cover a diverse set <strong>of</strong> microbial measurements due to multifunctional<br />

properties <strong>of</strong> microbial communities in soil ecosystem. Various microbial indicators which can be<br />

monitored in respect <strong>of</strong> <strong>the</strong> soil ecosystem parameters along with <strong>the</strong> methods available are given<br />

in Table 4.<br />

Table 4. List <strong>of</strong> microbial indicators <strong>for</strong> soil health monitoring<br />

<strong>Soil</strong> ecosystem Microbial indicator<br />

parameter<br />

Biodiversity Genetic diversity Functional<br />

diversity Marker lipids<br />

Ready-to-use<br />

methods<br />

PCR-DGGE BIOLOGTM<br />

PLFA<br />

C-cycling<br />

<strong>Soil</strong> respiration<br />

Metabolic quotient (qCO2)<br />

Decomposition <strong>of</strong> organic matter<br />

<strong>Soil</strong> enzyme activity Methane<br />

oxidation<br />

Methanotrophs<br />

CO 2 -production or O 2 -consumption<br />

C resp /C biomass<br />

Litterbags<br />

Enzyme assays Methane<br />

measurements<br />

MPN<br />

PLFA<br />

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N-cycling<br />

N-mineralisation Nitrification<br />

Denitrification<br />

N-fixation: Rhizobium<br />

N-fixation: Cyanobacteria<br />

Microbial biomass Microbial biomass: Direct<br />

methods<br />

Microbial biomass: Indirect<br />

methods<br />

Microbial quotient<br />

Fungi<br />

Microbial activity<br />

Fungal-bacterial ratio Protozoa<br />

Bacterial DNA syn<strong>the</strong>sis<br />

Bacterial protein syn<strong>the</strong>sis<br />

RNA measurements<br />

Community growth physiology<br />

Bacteriophages<br />

NH 4 + -accumulation<br />

NH 4 + -oxidation assay<br />

Acetylene inhibition<br />

assay<br />

Pot test<br />

MPN<br />

Nitrogenase activity<br />

Microscopy<br />

PLFA<br />

CFI,CFE<br />

SIR<br />

C micro / C org<br />

PLFA<br />

Ergosterol<br />

PLFA<br />

MPN<br />

Thymidine incorporation<br />

Leucine incorporation<br />

CO 2 -production or<br />

O 2 -consumption<br />

Key species<br />

Mycorrhiza<br />

Human pathogens<br />

Microscopy<br />

Pot test<br />

Selective plating<br />

Bioavailability<br />

Suppressive soil<br />

Biosensor bacteria<br />

Plasmid-containing bacteria<br />

Antibiotic-resistant bacteria<br />

Incidence and expression <strong>of</strong><br />

catabolic<br />

genes<br />

Pot test<br />

Remedios TM , Microtox R<br />

Gel electrophoresis<br />

Selective growth<br />

Selective growth<br />

Epilogue<br />

<strong>Microbe</strong>s and <strong>the</strong>ir activities are undisposable component <strong>for</strong> <strong>the</strong> quality maintenance/<br />

improvement <strong>of</strong> soil. The multifaceted functions played by <strong>the</strong> microorganisms contributes directly<br />

as well as indirectly to <strong>the</strong> soil quality. <strong>Microbe</strong>s helps in growing <strong>the</strong> plants healthy i.e. free <strong>of</strong><br />

diseases as well as nourishing it with <strong>the</strong> essential nutrients through various activities. This is<br />

achieved through managing organic matter and enhancing soil life including microorganisms, and<br />

optimizing nutrient availability by green manure, composts and o<strong>the</strong>r bi<strong>of</strong>ertilizers, including <strong>the</strong><br />

use <strong>of</strong> nitrogen fixing crops. To monitor <strong>the</strong> changes occurring as an impact <strong>of</strong> various<br />

management practices in agriculture, microbial indicators provide a very effective tool <strong>for</strong><br />

discriminating <strong>the</strong> positive/ negative impact on soil health. However <strong>for</strong> monitoring <strong>the</strong> soil health in<br />

a real sense it is pertinent to consider <strong>the</strong> end point processes dictated by <strong>the</strong> soil ecosystem<br />

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parameters. The DPSIR framework would be more realistic <strong>for</strong> evaluating and monitoring <strong>the</strong> soil<br />

health <strong>for</strong> <strong>for</strong>mation <strong>of</strong> <strong>the</strong> effective policies <strong>for</strong> <strong>the</strong> maintenance <strong>of</strong> soil health <strong>for</strong> sustaining <strong>the</strong> life<br />

on <strong>the</strong> earth.<br />

REFERENCES<br />

• Borlogue, N. E. and Dowswell, C. R. (1994). Key note lecture. Suppl. Trans. Of 15th World<br />

Congress <strong>of</strong> <strong>Soil</strong>s Science. p. 15.<br />

• Doran, J.W. and Safley, M. (1997). Defining and assessing soil health and sustainable<br />

productivity. In : Biological Indicators <strong>of</strong> <strong>Soil</strong> Health. Pankhurst, C.E., Doube, B.M.,<br />

and Gupta, V.V.S.R. (eds.). CAB International, pp. 1-28.<br />

• H<strong>of</strong>fman, E. and Seegerer, A. (1950). Biochem. Z. 321 :97.<br />

• Huber, S., Syed, B., Freudenschuss, A., Ernstsen, V., and Loveland, P. (2001). Proposal <strong>for</strong> a<br />

European soil monitoring and assessment framework. Technical report no. 61,<br />

European Environment Agency, Copenhagen, Denmark<br />

• Karlen, D. L. and Andrews, S. S. (2000). The soil quality concept: A tool <strong>for</strong> evaluating<br />

sustainability. In: <strong>Soil</strong> Stresses, Quality and Care; DIAS Report <strong>Plant</strong> Production<br />

no.38, Elmholt, S., Stenberg, B., Grønlund, A. and Nuutinen, V. (eds.), Danish<br />

Institute <strong>of</strong> Agricultural Sciences, Tjele, Denmark, p.15-26.<br />

• Lynch, J. M. and Bragg, E. (1985). Microorganisms and soil aggregate stability. Adv. <strong>Soil</strong> Sci. 2 :<br />

133.<br />

• Nielsen, M.N. and Winding ,A. (2002). Microorganisms as indicators <strong>of</strong> soil health. Ministry <strong>of</strong> <strong>the</strong><br />

Environment, national Envirojnmental Research Institute. Pp. 84.<br />

• Qui, F. Q., Zhou, L. K., Chen, E. F.,Ding, Q. T., Zhang, A. M. and Dang, L.C. (1981). Acta Pedol.<br />

Sin. 18 : 244.<br />

• Zhou, L. K., Zhang, Z. M. and Cao, C. M. (1983). Acta Pedol. Sin. 20 : 413.<br />

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Suppressive <strong>Soil</strong>s in <strong>Plant</strong> Disease <strong>Management</strong><br />

Krishna Pratap Singh<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

<strong>Soil</strong> is a complex mix <strong>of</strong> organic and inorganic matter that includes thousands <strong>of</strong> different<br />

species, <strong>the</strong> vast majority <strong>of</strong> which are still undescribed. Some <strong>of</strong> <strong>the</strong> organisms are pests which<br />

cause significant crop losses while o<strong>the</strong>rs per<strong>for</strong>m ‘environmental services’ such as biological<br />

control <strong>of</strong> pests, aeration, drainage, nutrient and water cycle. Disease suppressive soils have been<br />

recognized <strong>for</strong> over 100 years and <strong>the</strong> mechanisms by which disease suppression is brought<br />

about has been <strong>the</strong> subject <strong>of</strong> study <strong>for</strong> nearly four decades. Disease suppressive soils are defined<br />

by Cook and Baker (1983) as soils in which <strong>the</strong> pathogen does not establish or persist, <strong>the</strong><br />

pathogen establishes but causes no damage or <strong>the</strong> pathogen causes some disease damage, but<br />

<strong>the</strong> disease becomes progressively less severe even though <strong>the</strong> pathogen persists in soil. The<br />

mechanism <strong>of</strong> suppression <strong>of</strong> soil includes antibiosis, competition, parasitism and predation.<br />

Chemical and physical attributes <strong>of</strong> soil, including pH, organic matter and clay content, can<br />

operate in <strong>the</strong> suppression <strong>of</strong> plant diseases directly or indirectly through <strong>the</strong>ir impact on soil<br />

microbial activity.<br />

Disease Suppressive <strong>Soil</strong>s<br />

A disease suppressive soil is one in which <strong>the</strong> level <strong>of</strong> disease that develops on plants<br />

grown in that soil is less than that which develops on plants grown in o<strong>the</strong>r soils under similar<br />

conditions. However, almost all soils have some disease suppressive properties, so <strong>the</strong><br />

phenomenon <strong>of</strong> disease suppressive soil should be thought <strong>of</strong> on a continuum <strong>of</strong> low to high levels<br />

<strong>of</strong> suppression, ra<strong>the</strong>r than thinking <strong>of</strong> soils as being ei<strong>the</strong>r disease suppressive or conducive. In<br />

many cases <strong>the</strong> disease suppressive nature <strong>of</strong> a soil is <strong>the</strong> result <strong>of</strong> <strong>the</strong> presence and activity <strong>of</strong><br />

<strong>the</strong> microorganisms in <strong>the</strong> soil. Bacteria, fungi, and soilborne fauna can all act to change <strong>the</strong><br />

suppressiveness <strong>of</strong> a soil.<br />

<strong>Soil</strong> is considered suppressive when, in spite <strong>of</strong> favorable conditions <strong>for</strong> disease to occur, a<br />

pathogen ei<strong>the</strong>r cannot become established, establishes but produces no disease, or establishes<br />

and produces disease <strong>for</strong> a short time and <strong>the</strong>n declines. Suppressiveness is linked to <strong>the</strong> types<br />

and numbers <strong>of</strong> soil organisms, fertility level, and nature <strong>of</strong> <strong>the</strong> soil itself (drainage and texture).<br />

The mechanisms by which disease organisms are suppressed in <strong>the</strong>se soils include induced<br />

resistance, direct parasitism (one organism consuming ano<strong>the</strong>r), nutrient competition, and direct<br />

inhibition through antibiotics secreted by beneficial organisms. Additionally, <strong>the</strong> response <strong>of</strong> plants<br />

growing in <strong>the</strong> soil contributes to suppressiveness. This is known as “induced resistance” and<br />

occurs when <strong>the</strong> rhizosphere (soil around plant roots) is inoculated with a weakly virulent<br />

pathogen. After being challenged by <strong>the</strong> weak pathogen, <strong>the</strong> plant develops <strong>the</strong> capacity <strong>for</strong> future<br />

effective response to a more virulent pathogen (Sullivan, 2004). There are numerous terms (Table<br />

1) that have been used to describe <strong>the</strong> apparent properties <strong>of</strong> such soils.<br />

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Table 1. Favourable/ Unfavourable terms used to describe <strong>for</strong> disease development<br />

Favourable <strong>for</strong> disease development<br />

Conducive<br />

Non-competitive<br />

Non-decline<br />

Non-immune<br />

Non-impeditive<br />

Non-inhibitory<br />

Non-resistant (Susceptible)<br />

Receptive<br />

Short life<br />

Sterile<br />

Unfavourable <strong>for</strong> disease development<br />

Suppressive<br />

Competitive<br />

Decline<br />

Immune<br />

Impeditive<br />

Inhibitory<br />

Resistant<br />

Antagonistic<br />

Long life<br />

Biologically buffered, Fungistatic, Disease<br />

suppressive, Pathogen suppressive<br />

Specific and General Suppression<br />

Historically, suppressiveness to soilborne diseases in field soils has been divided into two<br />

major categories: general and specific. Specific suppression results from one organism directly<br />

suppressing a known pathogen. These are cases where a biological control agent is introduced<br />

into <strong>the</strong> soil <strong>for</strong> <strong>the</strong> specific purpose <strong>of</strong> reducing disease incidence. General suppression is <strong>the</strong><br />

result <strong>of</strong> a high biodiversity <strong>of</strong> microbial populations that creates conditions unfavorable <strong>for</strong> plant<br />

diseases to develop. A good example <strong>of</strong> specific suppression is provided by a strategy used to<br />

control one <strong>of</strong> <strong>the</strong> organisms that cause damping <strong>of</strong>f—Rhizoctonia solani. Where present under<br />

cool temperatures and wet soil conditions, Rhizoctonia kills young seedlings. The beneficial fungus<br />

Trichoderma locates Rhizoctonia through a chemical released by <strong>the</strong> pathogen, <strong>the</strong>n attacks it.<br />

Beneficial fungal strands (hyphae) entangle <strong>the</strong> pathogen and release enzymes that dehydrate<br />

Rhizoctonia cells, eventually killing <strong>the</strong>m.<br />

In one case soil organic matter case, management had an unexpected effect on take all<br />

suppression. Organically managed soils had lower levels <strong>of</strong> antibiotic producing Pseudomonas<br />

fluorescens, but still had low levels <strong>of</strong> disease even with <strong>the</strong> presence <strong>of</strong> <strong>the</strong> pathogen.<br />

Conventionally managed soils had high levels <strong>of</strong> antibiotic producing P. fluorescens, but also had<br />

high disease. The reality <strong>of</strong> suppressive soils is much more complex than it is usually presented<br />

when you take into account soil organic matter characteristics and <strong>the</strong> overall activity <strong>of</strong> <strong>the</strong> soil<br />

microbiota. So even in cases with well studied and extensively documented biocontrol organisms,<br />

<strong>the</strong>re are aspects <strong>of</strong> <strong>the</strong> system that we are just beginning to understand.<br />

According to Cook and Baker (1983): General suppression is related to <strong>the</strong> total amount <strong>of</strong><br />

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microbiological activity at a time critical to <strong>the</strong> pathogen. A particularly critical time is during<br />

propagule germination and pre-penetration growth in <strong>the</strong> host rhizosphere. The kind <strong>of</strong> active soil<br />

microorganisms during this period are probably less important than <strong>the</strong> total active microbial<br />

biomass, which competes <strong>for</strong> <strong>the</strong> pathogen <strong>for</strong> carbon and energy in some cases and <strong>for</strong> nitrogen<br />

in o<strong>the</strong>r cases, and possibly causes inhibition through more direct <strong>for</strong>ms <strong>of</strong> antagonism. In a<br />

sense, general suppression is <strong>the</strong> equivalent <strong>of</strong> a high degree <strong>of</strong> soil fungistasis. No one<br />

microorganism or specific group <strong>of</strong> microorganisms is responsible by itself <strong>for</strong> general<br />

suppression.<br />

Specific suppression operates against a background <strong>of</strong> general suppression but is more<br />

qualitative, owing to more specific effects <strong>of</strong> individual or select groups <strong>of</strong> microorganisms<br />

antagonistic to <strong>the</strong> pathogen during some stage in its life cycle<br />

Suppression: “it depends”: Variability <strong>of</strong> suppression with composted materials is extremely<br />

high. Scientists don’t understand enough at this point to predict if a batch <strong>of</strong> compost will suppress<br />

a certain disease on a certain crop which is a major obstacle to using <strong>the</strong>se materials effectively in<br />

farming. Many <strong>of</strong> <strong>the</strong> studies that test multiple batches <strong>of</strong> compost in a variety <strong>of</strong> pathosystems<br />

come up with <strong>the</strong> somewhat unsatisfying conclusion that “sometimes it works, sometimes it<br />

doesn’t and we’re not totally sure why”.<br />

Variability <strong>of</strong> suppression: Compiling <strong>the</strong> results <strong>of</strong> over 400 scientific papers shows that <strong>the</strong><br />

variability <strong>of</strong> suppression increases with <strong>the</strong> number <strong>of</strong> pathogens tested in <strong>the</strong> study. So that even<br />

if a particular batch <strong>of</strong> compost is consistently suppressive towards one plant pathogen, it is likely<br />

to have a range <strong>of</strong> effects on o<strong>the</strong>r pathogens. This variability is <strong>of</strong> great relevance to growers<br />

because very rarely is <strong>the</strong>re only one pathogen causing a problem in a specific production system.<br />

Real world complications: Testing compost‐ based materials in <strong>the</strong> field can be complicated by<br />

<strong>the</strong> fact that multiple pathogens are naturally present. In this on‐ farm trial <strong>of</strong> aerated liquid<br />

compost extracts conducted by <strong>the</strong> Rodale Institute, <strong>the</strong> authors found that treatment with <strong>the</strong><br />

extracts significantly controlled some <strong>of</strong> <strong>the</strong> pathogens while actually exacerbating <strong>the</strong> symptoms<br />

caused by o<strong>the</strong>r pathogens.<br />

Dangerous Assumption: All composts and cover crops that suppress disease do so by reducing<br />

<strong>the</strong> amount <strong>of</strong> pathogen present in <strong>the</strong> soil. One reason <strong>for</strong> <strong>the</strong> variability <strong>of</strong> suppression seen with<br />

composts among a range <strong>of</strong> pathogens is that different mechanisms are involved in <strong>the</strong><br />

suppression <strong>of</strong> different types <strong>of</strong> pathogens.<br />

Suppression index: Specific measurements are <strong>of</strong>ten associated with suppression as seen in this<br />

“suppression index”. Positive numbers on <strong>the</strong> index indicate that a high value <strong>of</strong> a measurement<br />

like microbial activity or total bacterial cell counts positively correlates with suppression and vice<br />

versa. When all available scientific data on all pathosystems is combined several indicators stand<br />

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out as being consistently associated with suppression.<br />

However, when you look at <strong>the</strong> suppression index <strong>for</strong> different types <strong>of</strong> pathogens <strong>the</strong><br />

variability becomes more apparent. For example high levels <strong>of</strong> FDA hydrolysis (a measure <strong>of</strong><br />

microbial activity) is positively correlated with suppression <strong>of</strong> Pythium spp., but negatively<br />

correlated with suppression <strong>of</strong> Rhizoctonia spp. This variability <strong>of</strong> reliable indicators depending on<br />

<strong>the</strong> type <strong>of</strong> is one <strong>of</strong> <strong>the</strong> reasons suppression is so difficult to predict.<br />

History <strong>of</strong> disease suppression research:<br />

The existence <strong>of</strong> soils which are unfit <strong>for</strong> <strong>the</strong> development <strong>of</strong> certain diseases has been<br />

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known <strong>for</strong> a long time without attempts to understand <strong>the</strong> reasons such as <strong>the</strong> physical or chemical<br />

properties <strong>of</strong> <strong>the</strong> soil, cultural practices or genuine suppression due to natural biological control.<br />

Mac Millan (1919) describe earlier on disease suppression in <strong>the</strong> presence <strong>of</strong> <strong>the</strong> pathogen. He<br />

observed that Fusarium blight <strong>of</strong> potatoes was severe in San Luis Valley and Greeley District but<br />

that <strong>the</strong> disease had subsided in <strong>the</strong> latter area. It was generally assumed that <strong>the</strong> populations <strong>of</strong><br />

<strong>the</strong> pathogen declined under alfafa, however, Mac Millan observed that in some locations<br />

Fusarium blight was severe after 9 years <strong>of</strong> alfalfa, while in o<strong>the</strong>rs only one years was sufficient to<br />

get good control. Thus, he concluded that suppression had occurred in <strong>the</strong> presence <strong>of</strong> <strong>the</strong><br />

pathogen. By 1934, certain soil types in Wisconsin were recognized as those in which <strong>the</strong> pea wilt<br />

organism established itself quickly and o<strong>the</strong>rs in which <strong>the</strong> organism developed slowly and wilt<br />

occurred seldom or not at all. Menzies introduced <strong>the</strong> concept <strong>of</strong> “suppressive soils” with his work<br />

on <strong>the</strong> relationship <strong>of</strong> soil type to Streptomyces scab <strong>of</strong> potato, in Cali<strong>for</strong>nia. Since <strong>the</strong>n many<br />

research paper/ articles have appeared describing <strong>the</strong> complex nature <strong>of</strong> disease suppression in<br />

soil. However, <strong>the</strong> subject <strong>of</strong> “Suppressive soil” received considerable fillip from <strong>the</strong> publication <strong>of</strong><br />

a book “Biological control <strong>of</strong> plant pathogens” by Baker and Cook, in 1974. The history has been<br />

known <strong>for</strong> a long time to suppressed in certain soils are,<br />

o Late 1800s: suppressive soils documented [Huber & Schneider, 1982]<br />

o 1930s-1940s: Link made between composts and soil health [Howard, 1943]<br />

o 1956: Biological nature <strong>of</strong> suppression documented [Menzics 1959]<br />

o 1970s-1980s: Extensive work done on suppressive composts [Hoitink & Kuter, 1986,<br />

Weltzein, 1989]<br />

There is a vast literature on <strong>the</strong> biological control <strong>of</strong> soil-borne pathogens, but <strong>for</strong> this<br />

article <strong>the</strong> goal is to examine examples <strong>of</strong> biological suppression <strong>of</strong> soil-borne plant pathogens.<br />

The pathogens reported to have been suppressed in certain soils are listed in Table 2.<br />

Table 2. Examples <strong>of</strong> Disease- Suppressive <strong>Soil</strong>s<br />

Pathogens Disease(s) caused Pathogens Disease(s) caused<br />

Armillaria mellea Root rot <strong>of</strong> conifers Gaeumannomyces Take-all <strong>of</strong> wheat<br />

graminis<br />

Cephalosporium Stripe <strong>of</strong> wheat Olpidium brassicae Lettuce<br />

graminearum<br />

Didymella lycopersici Stem rot <strong>of</strong> tomato Phomopsis scleroides Rot <strong>of</strong> cucurbits<br />

Fusarium avenaceum Root rot <strong>of</strong> lentils Phytophthora<br />

cinnamomi<br />

Root rots <strong>of</strong> various<br />

crops<br />

F. oxysporum f.sp. Wilt <strong>of</strong> sweet potatoes Poria weirii Root rot <strong>of</strong> conifers<br />

batatas<br />

F. oxysporum f.sp. Wilt <strong>of</strong> banana Pseudocercosporella Root rot <strong>of</strong> cereals<br />

cubense<br />

herpotrichoides<br />

F. oxysporum f.sp. Wilt <strong>of</strong> cucurbits Pseudomonas S<strong>of</strong>t rots<br />

cucumerinum<br />

solanacearum<br />

F. oxysporum f.sp. Wilt <strong>of</strong> cyclamen Pythium<br />

Root rot <strong>of</strong> radish<br />

cyclaminis<br />

aphanidermatum<br />

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F. oxysporum f.sp. Wilt <strong>of</strong> carnation Pythium ultimum Root rots<br />

dianthi<br />

F. oxysporum f.sp. lini Wilt <strong>of</strong> flax Pythium spp. Root rots<br />

F. oxysporum f.sp. Wilt <strong>of</strong> tomato Rhizoctonia solani Root rots <strong>of</strong> many<br />

lycopersici<br />

crops<br />

F. oxysporum f.sp. Wilt <strong>of</strong> melon Sclerotium rolfsii Root rot <strong>of</strong> tomato<br />

melonis<br />

F. oxysporum f.sp. Wilt <strong>of</strong> pea S. cepivorum Wilt <strong>of</strong> onion<br />

pisi<br />

F. oxysporum f.sp. Wilt <strong>of</strong> beans Streptomyces scabies Scab <strong>of</strong> potatoes<br />

phaseoli<br />

F. oxysporum f.sp. Wilt <strong>of</strong> radish<br />

Verticillium albo-atrum Wilt <strong>of</strong> potatoes<br />

raphani<br />

F. udum Wilt <strong>of</strong> pigeonpea Heterodera avenae Cereal cyst nematode<br />

F. solani Root rot <strong>of</strong> beans<br />

Physical and chemical characteristics <strong>of</strong> suppressive soil:<br />

<strong>Soil</strong>s are composed <strong>of</strong> varying proportions <strong>of</strong> solids, liquids and gases. The relative<br />

amounts <strong>of</strong> liquids and gases depend upon how tightly <strong>the</strong> solid particles are packed toge<strong>the</strong>r.<br />

Depth, texture, structure, porosity, and consistency are important physical properties. They<br />

influence rooting depth, aeration, water movement and chemical and biological activities. Physical<br />

factors that influence microorganisms include moisture, temperature, aeration, and <strong>the</strong> mechanical<br />

strength <strong>of</strong> <strong>the</strong> soil. Texture refers to <strong>the</strong> particle sizes <strong>of</strong> <strong>the</strong> soil, such as, sand, silt and clay. It<br />

affects aeration, water retention and root movement. The arrangement <strong>of</strong> <strong>the</strong> individual particles<br />

into larger units determines soil structure. Clay and humus adhere to <strong>for</strong>m units <strong>of</strong> soil called peds.<br />

<strong>Soil</strong> porosity refers to that part <strong>of</strong> <strong>the</strong> soil that contains air and water and <strong>the</strong> relative proportion <strong>of</strong><br />

each varies with <strong>the</strong> wetness or dryness <strong>of</strong> <strong>the</strong> soil. <strong>Soil</strong> chemical properties refer <strong>the</strong> inorganic<br />

and organic constituents. <strong>Soil</strong> organic matter, cation exchange capacity, pH and minerals, soluble<br />

or insoluble, all constitute <strong>the</strong> chemical properties <strong>of</strong> <strong>the</strong> soil. The biological activity is strongly<br />

affected by <strong>the</strong> chemistry <strong>of</strong> <strong>the</strong> microhabitat (Chaube, 1989)<br />

Burke (1965) was not able “to transfer <strong>the</strong> rot suppressive properties <strong>of</strong> <strong>the</strong> resistant soil to<br />

o<strong>the</strong>rs by transfer <strong>of</strong> microorganisms” even with <strong>the</strong> addition <strong>of</strong> nutritive substances or by<br />

autoclaving <strong>the</strong> receptor soil. This “suggests that rot suppression depends upon <strong>the</strong> predominance<br />

<strong>of</strong> both physical and microbiological components <strong>of</strong> <strong>the</strong> resistant soil and that nei<strong>the</strong>r<br />

component alone is sufficient to produce <strong>the</strong> effect”. Examples <strong>of</strong> suppressive and or conducive<br />

soils influenced by physical and chemical properties <strong>of</strong> soil are summarized in <strong>the</strong> Table 3. The<br />

carpogenic germination <strong>of</strong> sclerotia <strong>of</strong> Sclerotinia sclerotiorum in soil samples collected from<br />

different places <strong>of</strong> Uttar Predesh, India has been studied by Singh et.al. 1991 and 1995. The<br />

percentage germination increased with increasing amounts <strong>of</strong> sand in <strong>the</strong> soil samples but was<br />

reduced in <strong>the</strong> soil that contained high concentrations <strong>of</strong> Na + , Ca 2+ , Cl - and So 2- 4 . Similar<br />

carpogenic germination was observed in <strong>the</strong> soil that had very low amounts <strong>of</strong> Mg 2+ and HCO - 3 .<br />

There was a reduction in carpogenic germination in those soils which had more organic carbon.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

There was no uni<strong>for</strong>m effect on pH on sclerotial germination but <strong>the</strong> pH <strong>of</strong> all <strong>the</strong> soil samples was<br />

above 7. Physico-chemical properties, ion-exchange capacity and soil nutrient status influenced<br />

apo<strong>the</strong>cial germination <strong>of</strong> sclerotia <strong>of</strong> S. sclerotiorum. The cation exchange capacity <strong>of</strong> different<br />

soil samples indicates that <strong>the</strong> soil sample (Rajapur Muksudan) showing maximum cation<br />

exchange capacity also shows minimum carpogenic germination. This is because <strong>of</strong> <strong>the</strong> fact that<br />

<strong>the</strong> soils having more cation exchange capacity release more nutrients <strong>for</strong> <strong>the</strong> growth <strong>of</strong> plants, but<br />

carpogenic germination <strong>of</strong> sclerotia is known to be favoured on <strong>the</strong> medium that contains least<br />

nutrients and that is why in <strong>the</strong> present case also <strong>the</strong>re is more carpogenic germination in those<br />

soil samples which exhibit less cation exchange capacity. Maximum positive correlation was found<br />

in Ca 2+ , HCO 3 - , Cl - and SO 4 2- with o<strong>the</strong>r characters.<br />

Table 3. Suppressive and conducive soils influenced by soil Physical and Chemical<br />

properties<br />

Disease(s)<br />

<strong>Soil</strong> properties<br />

A. Where <strong>the</strong> pathogen does not establish<br />

Fusarium wilt <strong>of</strong> Banana<br />

Sandy soil (C), Clay soil (S)<br />

Fusarium wilt <strong>of</strong> cotton<br />

Fusarium root rot <strong>of</strong> wheat<br />

Fusarium wilt <strong>of</strong> peas<br />

Fusarium root rot <strong>of</strong> bean<br />

Aphanomyces root rot <strong>of</strong> peas<br />

Phymatotrichum root rot <strong>of</strong> cotton<br />

Pine root rot<br />

Verticillium wilt <strong>of</strong> sunflower<br />

Acidic soil (C)<br />

Sandy soil, low organic matter and low rainfall (C)<br />

Fine textured, high organic matter and high rainfall (S)<br />

Heavy clay soil (S)<br />

Loessial (C) Lacustrine (S)<br />

Aluminum ions (S)<br />

Alkaline soils (C)<br />

Light soil (C) Heavy soil (S)<br />

Aluminum ions (S)<br />

B. Pathogen establishes but fails to cause disease<br />

Aphanomyces root rot <strong>of</strong> peas<br />

Fusarium root rot <strong>of</strong> beans<br />

Phytophthora root rot <strong>of</strong> avocado<br />

Phytophthora root rot <strong>of</strong> avocado<br />

Verticillium wilt <strong>of</strong> cotton<br />

Compact soil (C)<br />

Compact soil (C)<br />

Abiotic fungistatic factors (S)<br />

High organic matter (S),<br />

High exchangeable calcium (S)<br />

Copper induced fungistasis (S)<br />

C. Pathogen establishes, produces disease <strong>for</strong> a while but <strong>the</strong>n declines<br />

Fusarium root rot <strong>of</strong> bean<br />

Phymatotrichum root rot <strong>of</strong> cotton<br />

Scab <strong>of</strong> potato<br />

Rhizoctonia damping <strong>of</strong>f <strong>of</strong> radish<br />

Take-all <strong>of</strong> wheat<br />

Continuous crop (S)<br />

High exchangeable sodium (S)<br />

Continuous potatoes (S)<br />

In rotation with sugar beet, oats and maize (C)<br />

Continuous crop (S)<br />

Continuous crop (S)<br />

Mechanisms <strong>of</strong> biocontrol:<br />

A. Single organism: The following are examples <strong>of</strong> each <strong>of</strong> <strong>the</strong> documented mechanisms <strong>of</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

biocontrol with a single organism.<br />

1. Antibiosis: Antibiosis refers to <strong>the</strong> production <strong>of</strong> antibiotics. Pythium zoospores attack<br />

plant roots. However, when roots are treated with a biocontrol bacterium, Bacillus cereus,<br />

disease is prevented. The bacteria produce an antibiotic zwittermicin A that prevents <strong>the</strong><br />

germination <strong>of</strong> zoospore cysts which contributes to <strong>the</strong> protection from disease.<br />

2. Competition <strong>for</strong> nutrients: Some biocontrol agents consume chemicals that <strong>the</strong> pathogen<br />

needs as a cue to germinate or a vital nutrient <strong>for</strong> growth. Sporangia <strong>of</strong> Pythium ultimum lie<br />

dormant in <strong>the</strong> soil until <strong>the</strong>y are exposed to linoleic acid, a fatty acid released by<br />

germinating seeds. Linoleic acid acts as a germination cue which initiates infection. The<br />

bacterium Enterobacter cloacae metabolizes linoleic acid thus removing <strong>the</strong> cue to<br />

germinate. Although <strong>the</strong> Pythium sporangium is still viable, it does not germinate and no<br />

infection occurs.<br />

3. Parasitism: Some biocontrol agents carry out direct parasitism <strong>of</strong> <strong>the</strong> pathogen. For<br />

example, fungi <strong>of</strong> <strong>the</strong> genus Trichoderma encircle Pythium hyphae, puncture <strong>the</strong> cell wall<br />

and drain cellular contents. Several commercially available biocontrol <strong>for</strong>mulations include<br />

Trichoderma species.<br />

4. Induced systemic resistance: <strong>Plant</strong>s have a system <strong>of</strong> protection against pathogens that<br />

is somewhat analogous to mammalian immune systems. One component <strong>of</strong> this is Induced<br />

Systemic Resistance or ISR. In split pot experiments with cucumber plants, one part <strong>of</strong> <strong>the</strong><br />

root system was exposed to <strong>the</strong> bacterium Pseudomonas corrugata. A separate part <strong>of</strong> <strong>the</strong><br />

root system was exposed to Pythium aphanidermatum zoospores, but in plants treated with<br />

<strong>the</strong> bacteria no disease occurred. In this case <strong>the</strong> biocontrol bacterium had no direct<br />

contact with <strong>the</strong> plant pathogen. Instead, <strong>the</strong> bacterium initiated <strong>the</strong> plant’s defense<br />

response and a phloem mobile signal carried this in<strong>for</strong>mation to <strong>the</strong> o<strong>the</strong>r parts <strong>of</strong> <strong>the</strong> plant.<br />

With <strong>the</strong> arrival <strong>of</strong> this chemical signal, <strong>the</strong> plant starts to make protective compounds like<br />

antioxidants, nitrous oxide, and hydrogen peroxide that can lessen <strong>the</strong> tissue damage<br />

caused by pathogens.<br />

B. Multiple organism biocontrol: While scientists have learned a substantial amount about how<br />

individual species <strong>of</strong> microbes can prevent plant disease, understanding how <strong>the</strong> complex<br />

communities <strong>of</strong> microorganisms present in soil, compost and decomposing cover crops suppress<br />

disease has proven much more difficult. Although some commercial compost testing facilities<br />

claim to be able to predict which compost will be suppressive with certain biological<br />

measurements, <strong>the</strong>re is no scientific basis <strong>for</strong> this claim. The reality <strong>of</strong> <strong>the</strong> situation is much more<br />

complicated.<br />

Conclusion<br />

Because <strong>of</strong> <strong>the</strong> high variability in compost‐ mediated suppression <strong>of</strong> different pathogens,<br />

finding measurements that can predict overall suppressiveness may be unrealistic. In <strong>the</strong> future,<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

predictive factors may be pathosystem specific. Opportunities <strong>for</strong> collaboration exist among<br />

growers, compost producers and researchers to continue to improve <strong>the</strong> efficacy <strong>of</strong> compost use<br />

<strong>for</strong> plant disease suppression.<br />

REFERENCES<br />

• Bonanomi, G., Antignani, V., Capodilupo, M., and Scala, F. 2010. Identifying <strong>the</strong> characteristics <strong>of</strong><br />

organic soil amendments that suppress soilborne plant diseases. <strong>Soil</strong> Biology and<br />

Biochemistry 42: 136‐ 144.<br />

• Burke, D.W. 1965. Fusarium root rot <strong>of</strong> beans and behavior <strong>of</strong> <strong>the</strong> pathogen in different soils.<br />

Phytopathology 55: 1122<br />

• Chaube, H.S. 1989. Pathogen suppressive soil, In: Perspectives <strong>of</strong> Phytopathology, V.P. Agnitre,<br />

et al. (Eds), Today and Tomorrow Printer, New Delhi<br />

• Singh, U.P., Singh, K.P., and Shahi, D.K. 1991. Carpogenic germination <strong>of</strong> sclerotia <strong>of</strong> Sclerotinia<br />

sclerotiorum in some soil samples differing in H, organic carbon, silt, clay, sand<br />

and ion exchange capability. Phytophylloctica 23: 241 - 243.<br />

• Singh, K.P., Shahi, D.K., and Singh, U.P. 1995. Carpogenic germination <strong>of</strong> sclerotia <strong>of</strong><br />

Sclerotinia sclerotiorum in some soil samples differing in ion exchange and soil<br />

nutrients properties. Tropical Science 35: 354 - 358.<br />

• Sullivan, P. 2004. Sustainable management <strong>of</strong> soil-borne plant diseases. <strong>Soil</strong> System Guide,<br />

National Sustainable Agriculture In<strong>for</strong>mation Service, ATTRA.<br />

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Introduction<br />

(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Pesticides: Past, Present and Future<br />

R.P. Srivastava<br />

Department <strong>of</strong> Entomology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Agriculture is an important sector <strong>of</strong> <strong>the</strong> Indian economy and vital <strong>for</strong> <strong>the</strong> food and<br />

nutritional security <strong>of</strong> <strong>the</strong> nation. Ensuring food security <strong>for</strong> more than 1 billion Indians with<br />

diminishing cultivable land resources is a herculean task. This necessitates use <strong>of</strong> high yielding<br />

variety <strong>of</strong> seeds, balanced use <strong>of</strong> fertilizers, judicious use <strong>of</strong> quality pesticides along with education<br />

<strong>of</strong> farmers and use <strong>of</strong> modern farming techniques. In order to meet <strong>the</strong> needs <strong>of</strong> a growing<br />

population, agricultural production and protection technology have to play a crucial role.<br />

Substantial food production is lost due to insect pests, plant pathogens, weeds, rodents, birds,<br />

nematodes and during storage.<br />

Pesticides industry has developed substantially and has contributed significantly towards<br />

India’s agriculture and public health. In value terms <strong>the</strong> size <strong>of</strong> <strong>the</strong> Indian pesticide industry was<br />

$3.8 billion in <strong>the</strong> year 2011. India is a predominant exporter <strong>of</strong> pesticides to USA, Europe and<br />

African countries. Recently, <strong>the</strong> domestic industry is characterized by over-capacity, low capacity<br />

utilization and unsustainable levels <strong>of</strong> production from many units and low investments in R&D.<br />

Besides, <strong>the</strong> <strong>for</strong>mulation market is highly fragmented with large number <strong>of</strong> small <strong>for</strong>mulators.<br />

Globally, <strong>the</strong>re is a growing trend towards low dosage, high potency molecules and as such,<br />

market <strong>for</strong> usage <strong>of</strong> high volume pesticides is declining. With <strong>the</strong> advent <strong>of</strong> <strong>the</strong> integrated pest<br />

management (IPM) technique, <strong>the</strong> use <strong>of</strong> bio pesticides and genetically modified (GM) seeds has<br />

increased globally.<br />

Pest Species, Crop Loss and Benefits <strong>of</strong> Pesticides Application<br />

Worldwide, approximately 10,000 species <strong>of</strong> insects and mites, 50,000 species <strong>of</strong> plant<br />

pathogens, and 8,000 species <strong>of</strong> weeds damage crops.The losses caused by insect pests<br />

estimated at 14%, plant pathogens 13%,and weeds 13% .Pesticides are <strong>the</strong>re<strong>for</strong>e indispensable in<br />

agricultural production. About one-third <strong>of</strong> <strong>the</strong> agricultural products are produced by using<br />

pesticides. Without pesticide application <strong>the</strong> loss <strong>of</strong> fruits, vegetables and cereals from pest injury<br />

would reach 78%, 54% and 32% respectively. Crop loss from pests declines to 35- 42% when<br />

pesticides are used.<br />

Worldwide Pesticides Use and Reach to Non-Target<br />

Globally 4.6 million tons <strong>of</strong> chemical pesticides are annually sprayed into <strong>the</strong> environment.<br />

There are currently about 500 pesticides with mass applications, <strong>of</strong> which organochlorine<br />

pesticides, some herbicides and <strong>the</strong> pesticides containing Hg, As, and Pb are highly poisonous to<br />

<strong>the</strong> environment. Only 1% <strong>of</strong> <strong>the</strong> sprayed pesticides are effective (reach to <strong>the</strong> target), 99% <strong>of</strong><br />

pesticides applied are released to non-target soils, water bodies and atmosphere, and finally<br />

absorbed by almost every organism.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Pesticides, Non-target Organisms and our environment<br />

Regarding effect on non target organisms, <strong>the</strong> most important publication was Rachel<br />

Carson’s best-selling book “Silent Spring,” published in 1962. She (a scientist) issued grave<br />

warnings about pesticides, and predicted massive destruction <strong>of</strong> <strong>the</strong> planet’s fragile ecosystems<br />

unless more was done to halt what she called <strong>the</strong> “rain <strong>of</strong> chemicals.” In retrospect, this book really<br />

launched <strong>the</strong> environmental movement.<br />

She was focusing on <strong>the</strong> chlorinated hydrocarbons, such as DDT, and pointed to evidence<br />

linking <strong>the</strong>m to death <strong>of</strong> non target creatures (organisms o<strong>the</strong>r than those that <strong>the</strong> pesticide is<br />

intended to kill), such as birds. She argued that <strong>the</strong> death <strong>of</strong> non targets occurred via two basic<br />

ways:<br />

1) Direct toxicity - It was discovered that DDT was toxic to fish (especially juveniles) and crabs,<br />

not only to insects.<br />

2) Indirect toxicity - related to its persistence. (Its persistence came in part from its insolubility;<br />

from <strong>the</strong> fact that it was a syn<strong>the</strong>tic, recently introduced compound that micro-consumers, such as<br />

bacteria, lacked enzymes capable <strong>of</strong> degrading - basically <strong>the</strong>y hadn’t evolved to use it as an<br />

energy source, as well as from o<strong>the</strong>r features <strong>of</strong> its chemistry.)<br />

The indirect toxicity related to two principles:<br />

i. Bioconcentration - <strong>the</strong> tendency <strong>for</strong> a compound to accumulate in an organism’s tissues<br />

(especially in fatty tissues <strong>for</strong> fat soluble organochlorines such as DDT)<br />

ii. Biomagnification - an increase in concentration up <strong>the</strong> food chain (These terms are<br />

sloppily used; sometimes “bioaccumulation” is also used to mean <strong>for</strong> both <strong>the</strong> terms)<br />

(Source: http://oregonstate.edu/~muirp/ pesthist.htm)<br />

Pesticide: Global Scenario<br />

Global generic market <strong>of</strong> pesticides was $45 billion. Export opportunities <strong>for</strong> Indian<br />

companies are immense with key markets being USA, France, Ne<strong>the</strong>rlands, South Africa, and<br />

Bangladesh.<br />

Indian Scenario: Production Trends<br />

India is <strong>the</strong> 4th largest producer <strong>of</strong> pesticides after USA, Japan and China. India is <strong>the</strong><br />

second largest producer <strong>of</strong> pesticides in Asia. According to <strong>the</strong> Centre <strong>for</strong> Monitoring Indian<br />

Economy (CMIE), pesticide production in India <strong>for</strong> FY10 stood at 6.2 lakh tonnes. CMIE has taken<br />

production details from <strong>the</strong> annual reports <strong>of</strong> <strong>the</strong> pesticide companies. It could be much higher as<br />

<strong>the</strong>re are lot <strong>of</strong> small unauthorised individuals and companies manufacturing pesticides without<br />

product registration. There is no data available on that. The presence <strong>of</strong> <strong>the</strong>se small players has<br />

resulted in driving down <strong>the</strong> prices due to fierce competition.<br />

The total market size in India, including exports, <strong>for</strong> 2009 was approximately Rs.70 bn.<br />

According to a latest report released by Research on India, a leading provider <strong>of</strong> market<br />

intelligence reports on leading industries, <strong>the</strong> market is expected to grow at CAGR <strong>of</strong> 2.38% <strong>for</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

next 3 years. The Indian pesticides industry has been growing at 8-9% p.a. over <strong>the</strong> past five<br />

years (FY07-FY11). Industry size is estimated to be $3.8 billion in FY11 with exports accounting<br />

<strong>for</strong> 50% <strong>of</strong> <strong>the</strong> market. Over <strong>the</strong> XIIth plan period, <strong>the</strong> segment is expected to grow at 12-13%<br />

p.a. with domestic demand growing at 8-9% p.a. and export demand at 15-16% p.a. Three broad<br />

categories <strong>of</strong> companies are present in <strong>the</strong> industry - Multi-National, Indian including <strong>the</strong> public<br />

sector companies and small sector units. There are about 125 technical grade pesticides<br />

manufacturers in <strong>the</strong> country <strong>of</strong> which about 60 are in <strong>the</strong> organized sector, and 10 are,<br />

multinationals. There are about 800 pesticides <strong>for</strong>mulators in <strong>the</strong> country. Most Indian technical<br />

manufacturers are focused on <strong>of</strong>f-patent pesticides.<br />

Pesticide Consumption<br />

Pesticides are among <strong>the</strong> crucial inputs required to sustain and improve <strong>the</strong> agricultural<br />

production in country. Substantial amount <strong>of</strong> crop is lost due to attack from pests. What is<br />

surprising is that, despite <strong>the</strong> country’s huge agricultural base, pesticide consumption in India is<br />

one <strong>of</strong> <strong>the</strong> lowest in <strong>the</strong> world with per hectare consumption <strong>of</strong> less than one kg compared to US<br />

(4.5 kg/ha) and Japan (11 kg/ha). Consumption could be low <strong>for</strong> <strong>the</strong> following reasons:<br />

‣ Lack <strong>of</strong> awareness among <strong>the</strong> farmers about different types <strong>of</strong> pesticides available and <strong>the</strong>ir<br />

impact on environment.<br />

‣ Pesticide is <strong>the</strong> last input in agricultural cropping operation; hence, farmers generally have no<br />

surplus money left and start using <strong>the</strong>m only after <strong>the</strong> pest attack.<br />

Consumption is mainly driven by cotton and paddy crops.<br />

In India pesticide use is<br />

extended to approximately 16.7 mn hectares, which is just 9% <strong>of</strong> <strong>the</strong> total cultivable land.<br />

Insecticide accounts <strong>for</strong> largest share in consumption in India followed by herbicide and fungicide,<br />

unlike high herbicide and fungicide usage globally. This is probably because India‘s tropical<br />

climate is conducive <strong>for</strong> <strong>the</strong> multiplication <strong>of</strong> insects.<br />

List <strong>of</strong> pesticides which are banned, refused registration and restricted in use (As on 31 th<br />

Dec, 2012)<br />

I. PESTICIDES / FORMULATIONS BANNED IN INDIA<br />

A. Pesticides Banned <strong>for</strong> manufacture, import and use<br />

1. Aldicarb 15. Heptachlor<br />

2. Aldrin 16. Lindane (Gamma-HCH)*<br />

3. Benzene Hexachloride 17. Maleic Hydrazide<br />

4. Calcium Cyanide 18. Menazon<br />

5. Chlorbenzilate 19. Metoxuron<br />

6. Chlordane 20. Nitr<strong>of</strong>en<br />

7. Chlor<strong>of</strong>envinphos 21. Paraquat Dimethyl Sulphate<br />

8. Copper Acetoarsenite 22. Pentachloro Nitrobenzene<br />

9. Dibromochloropropane 23. Pentachlorophenol<br />

10. Dieldrin 24. Phenyl Mercury Acetate<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

11. Endrin 25. Sodium Methane Arsonate<br />

12. Ethyl Mercury Chloride 26. TCA (Trichloro acetic acid)<br />

13. Ethyl Parathion 27. Tetradifon<br />

14. Ethylene Dibromide 28. Toxaphene(Camphechlor)<br />

*(Banned vide Gazette Notification No S.O. 637(E) Dated 25/03/2011)-Banned <strong>for</strong><br />

Manufacture,Import or Formulate w.e.f. 25th March,2011 and banned <strong>for</strong> use w.e.f. 25th<br />

March,2013.<br />

B. Pesticide <strong>for</strong>mulations banned <strong>for</strong> import, manufacture and use<br />

1. Carb<strong>of</strong>uron 50% SP 3. Methomyl 24% <strong>for</strong>mulation<br />

2. Methomyl 12.5% L 4. Phosphamidon 85% SL<br />

C. Pesticide / Pesticide <strong>for</strong>mulations banned <strong>for</strong> use but continued to<br />

manufacture <strong>for</strong> export<br />

1. Captafol 80% Powder 2. Nicotin Sulfate<br />

D. Pesticides Withdrawn<br />

1. Dalapon 5. Paradichlorobenzene (PDCB)<br />

2. Ferbam 6. Simazine<br />

3. Formothion 7. Warfarin<br />

4. Nickel Chloride<br />

II.<br />

PESTICIDES REFUSED REGISTRATION<br />

S.No. Name <strong>of</strong> Pesticides<br />

S.No. Name <strong>of</strong> Pesticides<br />

1. Ammonium Sulphamate 10. Fentin Acetate<br />

2. Azinphos Ethyl 11. Fentin Hydroxide<br />

3. Azinphos Methyl 12. Lead Arsenate<br />

4. Binapacryl 13. Leptophos (Phosvel)<br />

5. Calcium Arsenate 14. Mephosfolan<br />

6. Carbophenothion 15. Mevinphos (Phosdrin)<br />

7. Chinomethionate (Morestan) 16. 2,4, 5-T<br />

8. Dicrotophos 17. Thiodemeton / Disulfoton<br />

9. EPN 18. Vamidothion<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

III. PESTICIDES RESTRICTED FOR USE IN THE COUNTRY<br />

S.N<br />

o<br />

Name<br />

Pesticides<br />

1. Aluminium<br />

Phosphide<br />

<strong>of</strong><br />

Details <strong>of</strong> Restrictions<br />

The Pest Control Operations with Aluminium Phosphide may be<br />

undertaken only by Govt./Govt. undertakings / Govt. Organizations /<br />

pest control operators under <strong>the</strong> strict supervision <strong>of</strong> Govt. Experts or<br />

experts whose expertise is approved by <strong>the</strong> <strong>Plant</strong> Protection Advisor to<br />

Govt. <strong>of</strong> India except 1 Aluminium Phosphide 15 % 12 g tablet and<br />

2 Aluminum Phosphide 6 % tablet.<br />

[RC decision circular F No. 14-11(2)-CIR-II (Vol. II) dated 21-09-1984<br />

and G.S.R. 371(E) dated 20 th may 1999]. 1 Decision <strong>of</strong> 282 nd RC held on<br />

02-11-2007 and, 2 Decision <strong>of</strong> 326 th RC held on 15-02-2012.<br />

The production, marketing and use <strong>of</strong> Aluminium Phosphide tube packs<br />

with a capacity <strong>of</strong> 10 and 20 tablets <strong>of</strong> 3 g each <strong>of</strong> Aluminium<br />

Phosphide are banned completely. (S.O.677 (E) dated 17 th July, 2001)<br />

2. Captafol<br />

3. Cypermethrin<br />

4. Dazomet<br />

5. Diazinon<br />

6.<br />

Dichloro<br />

Diphenyl<br />

Trichloroethane<br />

(DDT)<br />

7. Fenitrothion<br />

8. Fenthion<br />

The use <strong>of</strong> Captafol as foliar spray is banned. Captafol shall be used<br />

only as seed dresser. (S.O.569 (E) dated 25 th July, 1989)<br />

The manufacture <strong>of</strong> Captafol 80 % powder <strong>for</strong> dry seed treatment (DS)<br />

is banned <strong>for</strong> use in <strong>the</strong> country except manufacture <strong>for</strong> export.<br />

(S.O.679 (E) dated 17 th July, 2001)<br />

Cypermethrin 3 % Smoke Generator, is to be used only through Pest<br />

Control Operators and not allowed to be used by <strong>the</strong> General Public.<br />

[Order <strong>of</strong> Hon,ble High Court <strong>of</strong> Delhi in WP(C) 10052 <strong>of</strong> 2009 dated<br />

14-07-2009 and LPA-429/2009 dated 08-09-2009]<br />

The use <strong>of</strong> Dazomet is not permitted on Tea.<br />

(S.O.3006 (E) dated 31 st Dec, 2008)<br />

Diazinon is banned <strong>for</strong> use in agriculture except <strong>for</strong> household use.<br />

(S.O.45 (E) dated 08 th Jan, 2008)<br />

The use <strong>of</strong> DDT <strong>for</strong> <strong>the</strong> domestic Public Health Programme is restricted<br />

up to 10,000 Metric Tonnes per annum, except in case <strong>of</strong> any major<br />

outbreak <strong>of</strong> epidemic. M/s Hindustan Insecticides Ltd., <strong>the</strong> sole<br />

manufacturer <strong>of</strong> DDT in <strong>the</strong> country may manufacture DDT <strong>for</strong> export to<br />

o<strong>the</strong>r countries <strong>for</strong> use in vector control <strong>for</strong> public health purpose. The<br />

export <strong>of</strong> DDT to Parties and State non-Parties shall be strictly in<br />

accordance with <strong>the</strong> paragraph 2(b) article 3 <strong>of</strong> <strong>the</strong> Stockholm<br />

Convention on Persistent Organic Pollutants (POPs).<br />

(S.O.295 (E) dated 8 th March, 2006)<br />

Use <strong>of</strong> DDT in Agriculture is withdrawn. In very special circumstances<br />

warranting <strong>the</strong> use <strong>of</strong> DDT <strong>for</strong> plant protection work, <strong>the</strong> state or central<br />

Govt. may purchase it directly from M/s Hindustan Insecticides Ltd. to<br />

be used under expert Governmental supervision.<br />

(S.O.378 (E) dated 26 th May, 1989)<br />

The use <strong>of</strong> Fenitrothion is banned in Agriculture except <strong>for</strong> locust control<br />

in scheduled desert area and public health.<br />

(S.O.706 (E) dated 03 rd May, 2007)<br />

The use <strong>of</strong> Fenthion is banned in Agriculture except <strong>for</strong> locust control,<br />

household and public health. (S.O.46 (E) dated 08 th Jan, 2008)<br />

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9. Lindane<br />

(Gamma-HCH)<br />

10.<br />

Methoxy<br />

Mercuric<br />

Chloride<br />

(MEMC)<br />

Ethyl<br />

11. Methyl Bromide<br />

12. Methyl<br />

Parathion<br />

13. Monocrotophos<br />

14. Sodium Cyanide<br />

Lindane is banned <strong>for</strong> manufacture, import or <strong>for</strong>mulate. However it is<br />

allowed <strong>for</strong> use up to 24 th march, 2013 <strong>for</strong> termite control in Building<br />

including wood, and termite control in Agriculture as per approved label<br />

claims by <strong>the</strong> Registration Committee and <strong>for</strong> exports.<br />

[S.O.637 (E) dated 25 th March, 2011 AND S.O.1472 (E) dated 29 th Aug.,<br />

2007]<br />

The use <strong>of</strong> MEMC is banned completely except <strong>for</strong> seed treatment <strong>of</strong><br />

potato and sugarcane. (S.O.681 (E) dated 17 th July, 2001)<br />

Methyl Bromide may be used only by Govt./Govt. undertakings/Govt.<br />

Organizations / Pest control operators under <strong>the</strong> strict supervision <strong>of</strong><br />

Govt. Experts or Experts whose expertise is approved by <strong>the</strong> <strong>Plant</strong><br />

Protection Advisor to Govt. <strong>of</strong> India.<br />

[G.S.R.371 (E) dated 20 th May, 1999 and earlier RC decision]<br />

Methyl Parathion 50 % EC and 2% DP <strong>for</strong>mulations are banned <strong>for</strong> use<br />

on fruits and vegetables.<br />

(S.O.680 (E) dated 17 th July, 2001)<br />

The use <strong>of</strong> Methyl Parathion is permitted only on those crops approved<br />

by <strong>the</strong> Registration Committee where honeybees are not acting as a<br />

pollinators. (S.O.658 (E) dated 04 th Sep., 1992.)<br />

Monocrotophos is banned <strong>for</strong> use on vegetables.<br />

(S.O.1482 (E) dated 10 th Oct, 2005)<br />

The use <strong>of</strong> Sodium Cyanide shall be restricted <strong>for</strong> Fumigation <strong>of</strong> Cotton<br />

bales under expert supervision approved by <strong>the</strong> <strong>Plant</strong> Protection<br />

Advisor to Govt. <strong>of</strong> India. (S.O.569(E) dated 25 th July, 1989)<br />

Employment<br />

Pesticides manufacturing sector provides direct and indirect employment to approximately<br />

60,000 people, nearly 10,000 <strong>of</strong> <strong>the</strong>se working in pesticides manufacturing units. In <strong>the</strong> XIIth five<br />

year plan, <strong>the</strong> industry envisages employment increase to <strong>the</strong> extent <strong>of</strong> 7%.<br />

Pesticide: Export<br />

India is a net exporter <strong>of</strong> pesticides. Exports account <strong>for</strong> ~50% <strong>of</strong> <strong>the</strong> pesticides market.<br />

Indian exports <strong>of</strong> pesticides grew at ~ 15% p.a. during <strong>the</strong> XIth plan period and will continue to<br />

grow at <strong>the</strong> same rate during <strong>the</strong> XIIth 5 year plan period. The key export destination markets are<br />

USA, France, Ne<strong>the</strong>rlands, Belgium, Spain, South Africa, Bangladesh, Malaysia and Singapore.<br />

Some <strong>of</strong> <strong>the</strong> agro-chemicals exported over <strong>the</strong> years include Isoproturon, Endosulphan, Aluminium<br />

Phosphide, Mancozeb, Cypermethrin, Thiamethoxam, Imidacloprid etc.<br />

Exports in value terms have almost doubled from Rs.27.9 bn in 2006 to Rs.52.2 bn in<br />

2010. Exports have grown at CAGR <strong>of</strong> 13.48% over <strong>the</strong> past five years. Manufacturers have<br />

shifted <strong>the</strong>ir focus more towards exports due to domestic seasonal demand, better price realisation<br />

in <strong>the</strong> global market, domestic overcapacity and low credit periods. India also has an advantage <strong>of</strong><br />

low manufacturing cost due to availability <strong>of</strong> cheap and high quality scientific pool.<br />

Strengths & opportunities<br />

1) Cost competitiveness: But <strong>for</strong> taxes and levies, Indian producers can make available <strong>the</strong><br />

product at <strong>the</strong> cheapest price available in <strong>the</strong> world. Low cost manufacturing base leads to<br />

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competitive cost <strong>of</strong> production <strong>of</strong> pesticides especially Pyrethroids, Organo Phosphorous<br />

(OP) Ester etc.<br />

2) Huge export potential: The excess production capacity is a perfect opportunity to<br />

increase exports by utilizing India’s low cost producer status.<br />

3) Growth in demand <strong>for</strong> food grains: India has 16% <strong>of</strong> <strong>the</strong> world’s population and less than<br />

2% <strong>of</strong> <strong>the</strong> total landmass. Increasing population and high emphasis on achieving food grain<br />

self sufficiency is expected to increase growth <strong>of</strong> pesticides industry.<br />

4) Limited farmland availability: India has more than 190 million hectares <strong>of</strong> gross<br />

cultivated area and scope <strong>of</strong> bringing new areas under cultivation is severely limited.<br />

Available agriculture land per capita has been reducing globally and is expected to reduce<br />

fur<strong>the</strong>r. The pressure is <strong>the</strong>re<strong>for</strong>e to increase yield per hectare which can be achieved<br />

through increased usage <strong>of</strong> pesticides.<br />

5) Growth <strong>of</strong> horticulture & floriculture: Growing horticulture and floriculture industries will<br />

result in increasing demand <strong>for</strong> pesticides especially fungicides.<br />

6) Increasing awareness: There is loss <strong>of</strong> crops due to non-use <strong>of</strong> pesticides. Companies<br />

are increasingly training farmers regarding right use <strong>of</strong> pesticides in terms <strong>of</strong> quantity to be<br />

used, <strong>the</strong> right application methodology and appropriate chemicals to be used <strong>for</strong> identified<br />

pest problems. With increasing awareness, <strong>the</strong> use <strong>of</strong> pesticides is expected to increase.<br />

7) Patent expiry: In <strong>the</strong> year 2014, many molecules are likely to go <strong>of</strong>f patent throwing <strong>the</strong><br />

market open <strong>for</strong> generic players. Pesticides industry in India can exploit this opportunity.<br />

8) Product portfolio expansion: Threats like genetically modified seeds, integrated pest<br />

management (IPM), organic farming etc can be turned into opportunities if <strong>the</strong> industry reorients<br />

itself to better address <strong>the</strong> needs <strong>of</strong> its consumers and broadens its product <strong>of</strong>fering<br />

to include a range <strong>of</strong> agri-inputs instead <strong>of</strong> only pesticides.<br />

9) Environment friendly pesticides: The issue <strong>of</strong> monitoring <strong>of</strong> pesticide residues in food<br />

and agricultural commodities will occupy an important position both in domestic sale and<br />

export <strong>of</strong> agrobased products. There will be a gradual shift towards pesticides that are user<br />

and environmental friendly.<br />

10) R&D in pesticides: Prior to 2005, i.e. in <strong>the</strong> process patent regime, Indian companies<br />

concentrated on marketing generic and <strong>of</strong>f patent products. Due to this, <strong>the</strong> R&D<br />

expenditure by Indian companies was lower at approximately 1% <strong>of</strong> turnover. Global<br />

companies focused on high end specialty products and dominated <strong>the</strong> market <strong>for</strong> patent<br />

new molecules and globally, pesticides companies spend 8-10% <strong>of</strong> <strong>the</strong>ir turn over on R&D.<br />

However, with <strong>the</strong> onset <strong>of</strong> <strong>the</strong> product patent regime in India, <strong>the</strong> Indian companies will<br />

need to increase R&D expenditure to meet competition from global market. Alternatively<br />

Indian companies can also be competitive in <strong>the</strong> area <strong>of</strong> Contract Research and<br />

Manufacturing Services (CRAMS).<br />

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Challenges & weaknesses<br />

1) High cost <strong>of</strong> power & finance: Very high cost <strong>of</strong> power, unreliability <strong>of</strong> supply and<br />

frequent interruption with high transmission and distribution losses. Chemical industry is<br />

highly capital-intensive and high cost <strong>of</strong> finance in India is a challenge (interest rate 14%-<br />

15% p.a. as compared to 2% to 6% prevailing in developed countries).<br />

2) Infrastructure: Poor transport and communication infrastructure, resulting in delays and<br />

slow movement <strong>of</strong> goods.<br />

3) Scale <strong>of</strong> production: The plant sizes are not comparable to world-scale operations<br />

effecting to cost <strong>of</strong> production.<br />

4) Labour laws: Labour laws at present do not allow flexibility in deployment <strong>of</strong> labour. This<br />

discourages modernization and investment in technological changes and eventually leads<br />

to industrial sickness, thus adversely affecting workers as well. Cumbersome and<br />

complicated product development process from inception to registration to manufacture,<br />

<strong>for</strong>mulation and sale.Luke warm response <strong>of</strong> Centre and State Governments in<br />

streng<strong>the</strong>ning quality control en<strong>for</strong>cement, in comparison to o<strong>the</strong>r agriculture inputs like<br />

fertilizers (50% subsidy) and seeds (no excise duty and taxes), pesticides are excisable<br />

and multipoint taxable.<br />

5) R&D costs: R&D to develop a new agrochemical molecule takes an average <strong>of</strong> 9 years<br />

and high cost on research. Indian companies have to focus on developing newer<br />

molecules and will face challenges in building <strong>the</strong>se capabilities.<br />

6) Threat from Genetically Modified (GM) seeds: Genetically modified seeds possess self<br />

immunity towards natural adversaries which have <strong>the</strong> impact on <strong>the</strong> business <strong>of</strong> pesticides<br />

7) Need <strong>for</strong> efficient distribution systems: Since <strong>the</strong> number <strong>of</strong> end users is large and<br />

widespread, effective distribution via retailers is essential to ensure product availability.<br />

Lately companies have been directly dealing with retailers by cutting <strong>the</strong> distributor from<br />

<strong>the</strong> value chain <strong>the</strong>reby reducing distribution costs, educating retailers on product usage<br />

and <strong>of</strong>fering competitive price to farmers<br />

8) Support <strong>for</strong> Integrated Pest <strong>Management</strong> (IPM) & rising demand <strong>for</strong> Organic farming:<br />

Promotion <strong>of</strong> IPM and usage <strong>of</strong> bio-pesticides is gaining momentum. With increasing<br />

demand <strong>for</strong> organic food, farmers have reduced chemical usage and have adopted organic<br />

farming. Agrochemical companies will have to tackle <strong>the</strong> rising environment awareness and<br />

address concerns on negative impact <strong>of</strong> pesticide usage.<br />

9) Counterfeit products: The spurious pesticides market has a negative impact on <strong>the</strong><br />

organized sector revenues and farmers.<br />

Action plan 2012-2017<br />

Based on <strong>the</strong> export potential and potential <strong>for</strong> increased penetration in <strong>the</strong> domestic<br />

market, <strong>the</strong> Indian agrochemical industry can target a size <strong>of</strong> $7.7 billion by FY17 (up from existing<br />

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$3.8 billion). However, achieving this target will require governmental support and <strong>the</strong> industry<br />

initiative with regard to <strong>the</strong> following aspects:<br />

1) Registration <strong>of</strong> pesticides: Delay in getting product registrations leads to delay in exports,<br />

hampering India’s exports. The procedure should be simplified and time bound registration and<br />

issue <strong>of</strong> registration certificate <strong>for</strong> export within 30 days from receipt <strong>of</strong> request from exporter/<br />

manufacturer should be ensured. Efficiency <strong>of</strong> Central Insecticides Board & Registration<br />

Committee (CIB & RC) should be increased by bringing more transparency, implementing robust<br />

and secured online data submission<br />

2) Multiple governing authorities <strong>for</strong> crop protection: Pesticides come under Dept. <strong>of</strong><br />

Chemicals and Petrochemicals, Ministry <strong>of</strong> Agriculture and Ministry <strong>of</strong> Health & Family Welfare.<br />

These activities falling under different ministries should be merged. Government could explore<br />

setting up a separate division under Dept. <strong>of</strong> Chemicals & Petrochemicals which could deal with all<br />

<strong>the</strong> issues such as pesticide registration, its use, fixation <strong>of</strong> standards <strong>for</strong> residue in food chain etc.<br />

3) Environmental clearance should be speed up through single window clearance <strong>for</strong> setting up<br />

pesticides manufacturing plants. Once a factory is cleared from <strong>the</strong> environment point <strong>of</strong> view, any<br />

product changes (within selected parameters) could be allowed without seeking additional<br />

clearances.<br />

4) Ambivalence prevails about <strong>the</strong> use <strong>of</strong> pesticides: There is need to pro-actively educate<br />

farmers <strong>for</strong> <strong>the</strong> safe, appropriate and judicious use <strong>of</strong> pesticides. A clear national policy directive is<br />

needed to increase pesticide usage, as at present <strong>the</strong> coverage is only about 20% <strong>of</strong> cultivated<br />

areas resulting 10 to 30% crop loss due to pests and weeds<br />

5) Spurious pesticides: The presence <strong>of</strong> spurious pesticides in <strong>the</strong> market is a major problem.<br />

The problem can be tackled by adopting <strong>the</strong> following approach:<br />

i) Improve <strong>the</strong> method <strong>of</strong> sampling, and make <strong>the</strong> inspectors accountable<br />

ii) Pesticide testing labs need to be upgraded and should be mandated to seek accreditation from<br />

NABL (National Accreditation Board <strong>for</strong> Laboratories) i.e. ISO 17025 certification<br />

iii) Industry members or independent quasi-government agencies should be allowed to undertake<br />

surprise visits to <strong>the</strong>se labs<br />

iv)A joint analysis <strong>of</strong> samples through an independent laboratory which is accredited by NABL<br />

should be considered<br />

V) Insecticides Act, 1968 should be reviewed and amended <strong>for</strong> any loopholes that can be<br />

exploited to support spurious pesticide manufacturers<br />

6) Recognize pesticides as a knowledge based industry: The pesticides industry is to be<br />

provided <strong>the</strong> same support as pharmaceuticals. This would support investment in R&D<br />

7) Budgetary support to pesticides industry: Considering crop losses due to pests, weeds and<br />

diseases, <strong>the</strong>re is urgent need <strong>for</strong> <strong>the</strong> following budgetary support:<br />

i) The pesticide industry is to be treated equal to fertilizer industry and <strong>the</strong> government to reduce<br />

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central excise duty from <strong>the</strong> present 10% to 4%. This will reduce costs, resulting in increased<br />

usage <strong>of</strong> plant protection chemicals to reduce crop losses<br />

ii) Section 35(2AB) <strong>of</strong> <strong>the</strong> Income Tax Act should be amended to provide weighted deduction <strong>of</strong><br />

expenses <strong>for</strong> <strong>the</strong> following:<br />

a) Agriculture extension work such as undertaking demonstration and training to farmer and all<br />

expenses connected <strong>the</strong>reto<br />

b) Development, upkeep and use <strong>of</strong> agricultural web sites<br />

c) Undertaking <strong>of</strong> R&D work in-house or through agricultural universities or reputed research<br />

organizations<br />

d) Farmer meetings <strong>for</strong> sharing best practices and <strong>the</strong>ir familiarization tours <strong>for</strong> education and<br />

training<br />

e) Fees & expenses paid to experts <strong>for</strong> dissemination <strong>of</strong> in<strong>for</strong>mation and best practices to farmers/<br />

users<br />

f) Knowledge dissemination through media or o<strong>the</strong>rwise.<br />

iii) All agricultural inputs should be treated as far as taxes, levies and subsidies are concerned, at<br />

par.<br />

iv)Government should consider and allocate funds <strong>for</strong> educating end users/ farmers <strong>for</strong> <strong>the</strong> benefit<br />

<strong>of</strong> pest control and also safe and judicious use <strong>of</strong> pesticides<br />

v) Government should encourage latest technology adoption measures among farmers and create<br />

farmer panels <strong>for</strong> key crops across India<br />

8) To ensure better adherence to Safety, Health & Environment (SHE) and Good Manufacturing<br />

Practices (GMP) norms <strong>for</strong> crop protection, Government should make ef<strong>for</strong>ts to guide SMEs<br />

Target <strong>for</strong> XII TH five year plan<br />

The Indian pesticides industry grew at a rate <strong>of</strong> 8-9% over <strong>the</strong> past five years (FY07-FY11).<br />

Industry size is estimated to be $3.8 billion in FY11 with exports accounting <strong>for</strong> ~50% <strong>of</strong> <strong>the</strong><br />

market. Over <strong>the</strong> XII th plan period, <strong>the</strong> segment is expected to grow at 12-13% p.a. with domestic<br />

demand growing at 8-9% p.a. and export demand growing at 15-16% p.a. Based on <strong>the</strong> export<br />

potential and potential <strong>for</strong> increased penetration in <strong>the</strong> domestic market, <strong>the</strong> Indian agrochemical<br />

industry target a size <strong>of</strong> US $7.7 billion by FY17.<br />

Chemical management in india: policy and legislative framework<br />

Development <strong>of</strong> Chemical <strong>Management</strong> Regime:<br />

India’s environment management ef<strong>for</strong>ts started quite early, after independence in<br />

1947.The Insecticides Act to regulate <strong>the</strong> harmful impacts <strong>of</strong> pesticides was passed in 1968.After<br />

<strong>the</strong> Stockholm Conference in 1972, India enacted two major environmental laws- The Water<br />

(Prevention and Control <strong>of</strong> Pollution) Act in 1974, passed <strong>for</strong> <strong>the</strong> purpose <strong>of</strong> prevention and control<br />

<strong>of</strong> water pollution, followed by <strong>the</strong> Air (Prevention and Control <strong>of</strong> Pollution) Act in 1981.It also led to<br />

<strong>the</strong> institutionalization <strong>of</strong> <strong>the</strong> regulatory infrastructure through <strong>the</strong> establishment <strong>of</strong> <strong>the</strong> Central and<br />

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State Pollution Control Boards (SPCB).<br />

However, it was after <strong>the</strong> Bhopal disaster in 1984 that chemical safety issues became<br />

specifically recognised through <strong>the</strong> passing to umbrella legislation, <strong>the</strong> Environmental Protection<br />

Act (EPA) 1986, under which specific rules on chemical safety have been framed from time to<br />

time. Subsequently, after <strong>the</strong> Rio Summit in 1992, <strong>the</strong> World Summit on Sustainable Development<br />

(WSSD) held in Johannesburg in 2002, which adopted <strong>the</strong> 2020 goal, as well as <strong>the</strong> Strategic<br />

Approach to International Chemical <strong>Management</strong> (SAICM) process, chemicals safety –has slowly<br />

become part <strong>of</strong> an overall development policy agenda.Even <strong>the</strong> Indian Planning Commission, <strong>the</strong><br />

highest national planning body has recognised this in its ongoing Eleventh 5-Year plan. Serious<br />

environmental health problems affect millions <strong>of</strong> people who suffer from respiratory and o<strong>the</strong>r<br />

diseases caused or exacerbated by biological and chemical agents, both indoors and outdoors.<br />

Millions are exposed to unnecessary chemical and physical hazards in <strong>the</strong>ir home, workplace or<br />

wider environment (Plannning Commission, 2007).<br />

In terms <strong>of</strong> legislation, India is well placed , even <strong>the</strong>re are gaps. Almost in all steps <strong>of</strong><br />

chemical management from cradle to grave, some legislation has been laid down and consists <strong>of</strong><br />

more than 15 Acts and 19 Rules (National Chemical <strong>Management</strong> Pr<strong>of</strong>ile, 2006). Yet areas such<br />

as substitution <strong>of</strong> hazards in products and processes or <strong>the</strong> remediation <strong>of</strong> contaminated sites<br />

need attention.<br />

Constitutional provisions<br />

The Indian Constitution, through its 42 nd amendment, under Article 48 states,”The state<br />

shall endeavour to protect and improve <strong>the</strong> environment and to safeguard <strong>the</strong> <strong>for</strong>ests and wildlife<br />

<strong>of</strong> <strong>the</strong> country”. Through various judgements , <strong>the</strong> Indian Supreme Court has also interpreted <strong>the</strong><br />

provisions <strong>of</strong> Article 21, which enshrines a Right to Life to hold that environmental degradation<br />

violates <strong>the</strong> fundamental right to life.<br />

The Environment (Protection) Act 1986, amended 1991<br />

The EPA is a fundamental act enabling umbrella legislation, under which <strong>the</strong> designated<br />

ministry in <strong>the</strong> Central Government (Ministry <strong>of</strong> Environment and Forests, MOEF) can frame rules<br />

and procedures to deal with chemical safety issues. It provides <strong>for</strong> both criminal as well as civil<br />

penalties and severe fines <strong>for</strong> violations as well as imparts wide ranging powers <strong>for</strong> regulators to<br />

take action in <strong>the</strong> event <strong>of</strong> non-compliance to <strong>the</strong> Act, including ordering <strong>the</strong> closure <strong>of</strong> units.<br />

However, since <strong>the</strong>se penaltiess have been ineffectual, this is now being re-examined to make this<br />

a real deterrent.<br />

Future Challenges<br />

To develop more and more new molecules having<br />

1) Low mammalian toxicity<br />

2) Less soluble in water<br />

3) Leaching potential shall be less or absent<br />

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4) New new chemistry<br />

5) Molecular weight <strong>of</strong> new molecules shall be ranged from 200-450<br />

6) More discoveries in macromolecular pesticides<br />

7) More innovations required <strong>for</strong> new neo-nicotinoids<br />

8) More biotechnological innovations to be directed in<br />

9) Transgenic plants etc.<br />

10) More innovative technology to be developed in application <strong>of</strong> pesticides, a special care<br />

shall be given on <strong>the</strong> nozzles, sprayer or applicator with an intention to minimize <strong>the</strong> loss <strong>of</strong><br />

applied pesticide or target organisms<br />

11) Minimization <strong>of</strong> residue load in ecosystem<br />

12) More emphasis shall be given in bio-control agents.<br />

13) Research emphasis shall be given in innovations <strong>of</strong> more plant derived bio-pesticides<br />

REFERENCE<br />

• Bhattacharyya A., Suhrid R B and Ganguly P. 2009. New pesticide molecules, <strong>for</strong>mulation<br />

technology and uses: Present status and future challenges. The Journal <strong>of</strong> <strong>Plant</strong><br />

Protection Sciences, 1(1): 9-15.<br />

• http://www.cibrc.nic.in/reg_products.htm(2007)<br />

• http://www.epa.gov/opp00001/biopesticides/ Environmental Protection Agency <strong>of</strong> <strong>the</strong> USA 2012.<br />

Regulating Biopesticides. ( Accessed April 2012)<br />

• http://www.epa.gov/pesticides/factsheets/chemical_fs.htm<br />

• http://www.ncipm.org.in/asps/pesticides<br />

• http://oregonstate.edu/~muirp/ pesthist.htm<br />

• Huang K., Xia L., Zhang Y., Ding X, Zahn A.J.(2009).Recent advances in <strong>the</strong> biochemistry <strong>of</strong><br />

spinosyns.Appl Microbiol Biotechnol 82:13–23.<br />

• IRAC 2012. IRAC MoA Classification Scheme. www.irac-online.org or enquiries@irac-online.org<br />

(accessed April 2012)<br />

• Nollet L.M.L and Rathore H.S.2010.Handbook <strong>of</strong> Pesticides Methods <strong>of</strong> Pesticide Residues<br />

Analysis. CRC Press, Taylor and Francis group, Boca Raton.<br />

http://www.tylorandfrancis.com, http://www.crcpress.com.<br />

• Waxler P., Kolk J. V. D., Mohapatra A and Agarwal R. 2012. Chemicals, Environment, Health A<br />

global <strong>Management</strong> Perspective. CRC Press, Taylor and Francis group New York.<br />

• WenJun Zhang., FuBin Jiang and Jian Feng Ou. 2011. Global pesticide consumption and pollution:<br />

with China as a focus. Proceedings <strong>of</strong> <strong>the</strong> International Academy <strong>of</strong> Ecology and<br />

Environmental Sciences, 1(2):125-144<br />

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Isolation, Identification and Quantification <strong>of</strong> Trichoderma<br />

Roopali Sharma, Smita Puri and Erraya<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Isolation <strong>of</strong> Trichoderma species- Select healthy plants from standing crop <strong>of</strong> desired location<br />

and collect <strong>the</strong> rhizospheric soil (soil tightly adhering <strong>the</strong> root) by gently and carefully uprooting <strong>the</strong><br />

plant.<br />

Materials required- Trichoderma selective medium (TSM)- MgSO 4 .7H 2 O (0.2 g), K 2 HPO 4 (0.9 g),<br />

KCl (0.15 g), NH 4 NO 3 (1.0 g), Glucose (3.0 g), Chloramphenicol (0.20 g), Apron 35SD (0.015 g),<br />

Captan (0.2 g), Rose Bengal (0.15 g), Agar-agar (20 g) and 1 L distilled water (Elad et al., 1981),<br />

Potato Dextrose Agar (potato- 200g, dextrose-20g and agar -20g), 4% water agar (40 g agar in 1l<br />

water) Petri plates, sterile water, measuring cylinder, pipette, tips, rose bengal, antibiotics.<br />

Isolation from rhizosphere<br />

Serial dilution technique (Krassilnikov, 1950) is used <strong>for</strong> isolation <strong>of</strong> Trichoderma from<br />

rhizospheric soil.<br />

1. Air dry soil samples <strong>for</strong> 4 h.<br />

2. Suspend 10 g soil in 100 ml <strong>of</strong> sterile distilled water (1:10) and stirred well.<br />

3. Allow <strong>the</strong> soil particles to settle down, transfer 10 ml <strong>of</strong> clear supernatant to ano<strong>the</strong>r flask<br />

containing 90 ml sterile distilled water (1:100).<br />

4. Prepare serial dilutions 10 -2 to 10 -6 by following same procedure.<br />

5. Prepare Trichoderma selective medium (TSM) <strong>for</strong> isolation <strong>of</strong> Trichoderma.<br />

6. Dissolve antibiotics and fungicides in 50 ml <strong>of</strong> 30 per cent ethyl alcohol and add in to <strong>the</strong><br />

medium prior to pouring into Petri plates.<br />

7. Take 1 ml <strong>of</strong> each dilution 10 -4 to 10 -6 with help <strong>of</strong> 5 ml pipette and pour it on <strong>the</strong> Petri plate<br />

seeded with TSM in an inoculation chamber under aseptic conditions.<br />

8. Incubate <strong>the</strong> plates at 28±1 ° C <strong>for</strong> 5 days.<br />

9. Record observations on <strong>the</strong> appearance <strong>of</strong> <strong>the</strong> colonies from 3 rd to 5 th day.<br />

10. Pick individual colony and maintain <strong>the</strong> pure culture.<br />

Isolation from rhizoplane<br />

Take root pieces <strong>of</strong> a plant in 100ml sterile water and shake it well.<br />

1. Give 10-20 Serial washings to <strong>the</strong> above roots with sterilized water until clear root surface<br />

is exposed.<br />

2. Place <strong>the</strong> washed roots on Petri plates having TSM.<br />

3. Incubate <strong>the</strong> plates <strong>for</strong> 5-7 days at 25°C.<br />

Isolation from phylloplane<br />

1. Collect fresh healthy leaves in sterile poly<strong>the</strong>ne bags.<br />

2. Transfer 10g <strong>of</strong> <strong>the</strong>se leaves to 100 ml sterile water and stir <strong>for</strong> 20 min using magnetic<br />

stirrer.<br />

3. Prepare serial dilutions up to 10 -3 .<br />

4. Transfer 1 ml aliquot from all <strong>the</strong> dilutions to sterile Petri plates and pour TSM.<br />

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5. To get <strong>the</strong> colonies <strong>of</strong> antagonistic fungi, incubate <strong>the</strong> plates <strong>for</strong> 5-7 days at 25°C.<br />

Purification <strong>of</strong> Trichoderma culture<br />

1. Purify Trichoderma isolates single spore culture.<br />

2. Inoculate spores <strong>of</strong> isolates onto a Petri dish seeded with 4% Water agar.<br />

3. With <strong>the</strong> help <strong>of</strong> binocular, select and transfer single germinating spore in slants having<br />

PDA with <strong>the</strong> help <strong>of</strong> inoculation needle.<br />

4. Incubate <strong>the</strong> cultures at 25±1 ° C <strong>for</strong> 5 days and store at 4 ° C.<br />

Quantification <strong>of</strong> spores through haemocytometer<br />

In <strong>Plant</strong> pathology, microbiology and cell culture <strong>the</strong>re are many applications that require<br />

use <strong>of</strong> suspensions <strong>of</strong> cells, <strong>for</strong> this purpose it is necessary to determine cell concentration. One<br />

can <strong>of</strong>ten determine cell density <strong>of</strong> a suspension spectrophotometrically, however that <strong>for</strong>m <strong>of</strong><br />

determination does not allow an assessment <strong>of</strong> cell viability, nor can one distinguish cell types.<br />

A device used <strong>for</strong> determining <strong>the</strong> number <strong>of</strong> cells per unit volume <strong>of</strong> a suspension is called<br />

a counting chamber. The most widely used type <strong>of</strong> chamber is called a hemocytometer, since it<br />

was originally designed <strong>for</strong> per<strong>for</strong>ming blood cell counts.<br />

Preparation <strong>of</strong> counting chamber- To prepare <strong>the</strong> counting chamber <strong>the</strong> mirror-like polished<br />

surface is carefully cleaned with lens paper. The coverslip is also cleaned. Coverslips <strong>for</strong> counting<br />

chambers are specially made and are thicker than those <strong>for</strong> conventional microscopy, since <strong>the</strong>y<br />

must be heavy enough to overcome <strong>the</strong> surface tension <strong>of</strong> a drop <strong>of</strong> liquid. The coverslip is placed<br />

over <strong>the</strong> counting surface prior to putting on <strong>the</strong> cell suspension. The suspension is introduced into<br />

one <strong>of</strong> <strong>the</strong> V-shaped wells with a pasteur or o<strong>the</strong>r type <strong>of</strong> pipet. The area under <strong>the</strong> coverslip fills<br />

by capillary action. Enough liquid should be introduced so that <strong>the</strong> mirrored surface is just covered.<br />

The charged counting chamber is <strong>the</strong>n placed on <strong>the</strong> microscope stage and <strong>the</strong> counting grid is<br />

brought into focus at low power.<br />

It is essential to be extremely careful with higher power objectives, since <strong>the</strong> counting<br />

chamber is much thicker than a conventional slide. The chamber or an objective lens may be<br />

damaged if <strong>the</strong> user is not not careful. One entire grid on standard hemacytometers with Neubauer<br />

rulings can be seen at 40x (4x objective). The main divisions separate <strong>the</strong> grid into 9 large squares<br />

(like a tic-tac-toe grid). Each square has a surface area <strong>of</strong> one square mm, and <strong>the</strong> depth <strong>of</strong> <strong>the</strong><br />

chamber is 0.1 mm. Thus <strong>the</strong> entire counting grid lies under a volume <strong>of</strong> 0.9 mm-cubed.<br />

Suspensions should be dilute enough so that <strong>the</strong> cells or o<strong>the</strong>r particles do not overlap<br />

each o<strong>the</strong>r on <strong>the</strong> grid, and should be uni<strong>for</strong>mly distributed. To per<strong>for</strong>m <strong>the</strong> count, determine <strong>the</strong><br />

magnification needed to recognize <strong>the</strong> desired cell type. Now systematically count <strong>the</strong> cells in<br />

selected squares so that <strong>the</strong> total count is 100 cells or so (number <strong>of</strong> cells needed <strong>for</strong> a statistically<br />

significant count). For large cells this may mean counting <strong>the</strong> four large corner squares and <strong>the</strong><br />

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middle one. For a dense suspension <strong>of</strong> small cells you may wish to count <strong>the</strong> cells in <strong>the</strong> four 1/25<br />

sq. mm corners plus <strong>the</strong> middle square in <strong>the</strong> central square. Always decide on a specific counting<br />

patter to avoid bias. For cells that overlap a ruling, count a cell as "in" if it overlaps <strong>the</strong> top or right<br />

ruling, and "out" if it overlaps <strong>the</strong> bottom or left ruling.<br />

Here is a way to determine a particle count using a Neubauer hemocytometer. Suppose<br />

that you conduct a count as described above, and count 187 particles in <strong>the</strong> five small squares<br />

described. Each square has an area <strong>of</strong> 1/25 mm-squared (that is, 0.04 mm-squared) and depth <strong>of</strong><br />

0.1 mm. The total volume in each square is (0.04)x(0.1) = 0.004 mm-cubed. You have five<br />

squares with combined volume <strong>of</strong> 5x(0.004) = 0.02 mm-cubed. Thus you counted 187 particles in<br />

a volume <strong>of</strong> 0.02 mm-cubed, giving you 187/(0.02) = 9350 particles per mm-cubed. There are<br />

1000 cubic millimeters in one cubic centimeter (same as a milliliter), so your particle count is<br />

9,350,000 per ml.<br />

Cells are <strong>of</strong>ten large enough to require counting over a larger surface area. For example,<br />

you might count <strong>the</strong> total number <strong>of</strong> cells in <strong>the</strong> four large corner squares plus <strong>the</strong> middle<br />

combined. Each square has surface area <strong>of</strong> 1 mm-squared and a depth <strong>of</strong> 0.1 mm, giving it a<br />

volume <strong>of</strong> 0.1 mm-cubed. Suppose that you counted 125 cells (total) in <strong>the</strong> five squares. You <strong>the</strong>n<br />

have 125 cells per 0.5 mm-cubed, which is 250 cells/mm-cubed. Again, multiply by 1000 to<br />

determine cell count per ml (250,000).<br />

Sometimes you will need to dilute a cell suspension to get <strong>the</strong> cell density low enough <strong>for</strong><br />

counting. In that case you will need to multiply your final count by <strong>the</strong> dilution factor. For example,<br />

suppose that <strong>for</strong> counting you had to dilute a suspension <strong>of</strong> Chlamydomonas 10 fold. Suppose you<br />

obtained a final count <strong>of</strong> 250,000 cells/ml as described above. Then <strong>the</strong> count in <strong>the</strong> original<br />

(undiluted) suspension is 10 x 250,000 which is 2,500,000 cells/ml.<br />

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Mechanism <strong>of</strong> Mycoparasitism and Antibiosis<br />

Roopali Sharma, Smita Puri and Rashmi Tewari<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

The activities <strong>of</strong> biocontrol agents mainly depends on different physiological environmental<br />

conditions to which <strong>the</strong>y are subjected. For this reason, biocontrol exerted by BCAs is sometimes<br />

unpredictable. Understanding <strong>the</strong>ir mechanisms <strong>of</strong> biocontrol will lead to improved application <strong>of</strong><br />

<strong>the</strong> different strains as biocontrol agents. These mechanisms are complex and what has been<br />

defined as biocontrol is <strong>the</strong> final result <strong>of</strong> different mechanisms acting synergistically to achieve<br />

disease control. Biocontrol results ei<strong>the</strong>r from competition <strong>for</strong> nutrients and space or as a result <strong>of</strong><br />

<strong>the</strong> ability <strong>of</strong> biocontrol agents to produce and/or resist metabolites that ei<strong>the</strong>r impede spore<br />

germination (fungistasis), kill <strong>the</strong> cells (antibiosis) or modify <strong>the</strong> rhizosphere, e.g., by acidifying <strong>the</strong><br />

soil, so that <strong>the</strong> pathogen cannot grow. Biocontrol may also results from a direct interaction<br />

between <strong>the</strong> pathogen itself and <strong>the</strong> biocontrol agent, as in mycoparasitism, which involves<br />

physical contact and syn<strong>the</strong>sis <strong>of</strong> hydrolytic enzymes, toxic compounds and/or antibiotics that act<br />

synergistically with <strong>the</strong> enzymes. Trichoderma sp. can even exert positive effects on plants with an<br />

increase in plant growth (mineralization) and <strong>the</strong> stimulation <strong>of</strong> plant defense mechanisms.<br />

Mechanism <strong>of</strong> disease suppression may be due to competition, antibiosis or mycoparasitism.<br />

Mycoparasitism<br />

When one fungus parasitizes ano<strong>the</strong>r, <strong>the</strong> phenomenon is called mycoparasitism,<br />

hyperparasitism, direct parasitism or interfungus parasitism. Mycoparasitism, <strong>the</strong> direct attack <strong>of</strong><br />

one fungus on ano<strong>the</strong>r, is a very complex process that involves sequential events, including<br />

recognition, attack and subsequent penetration and killing <strong>of</strong> <strong>the</strong> host. Almost all taxonomic groups<br />

<strong>of</strong> fungi are found to be involved in this phenomenon and <strong>of</strong>ten species within <strong>the</strong> same genus<br />

(e.g. Pythium) interact as host and parasite. Some examples <strong>of</strong> mycoparasitism in reference to<br />

biological control <strong>of</strong> diseases are <strong>the</strong> following.<br />

1. Trichoderma sp., mainly T. harzianum, is one <strong>of</strong> <strong>the</strong> most common mycoparasitic fungi.<br />

Trichoderma spp. parasitize a range <strong>of</strong> o<strong>the</strong>r fungi. The events leading to mycoparasitism<br />

are complex, and take place as follows: first, Trichoderma strains detect o<strong>the</strong>r fungi and<br />

grow towards <strong>the</strong>m; remote sensing is at least partially due to <strong>the</strong> sequential expression <strong>of</strong><br />

cell-wall degrading enzymes. Different strains can follow different patterns <strong>of</strong> induction, but<br />

<strong>the</strong> fungi apparently always produce low levels <strong>of</strong> an extracellular exochitinase. Diffusion <strong>of</strong><br />

this enzyme catalyses <strong>the</strong> release <strong>of</strong> cell wall oligomers from target fungi, and this in turn<br />

indicates <strong>the</strong> expression <strong>of</strong> fungitoxic endochitinases, which also diffuse and begin to<br />

attack on <strong>the</strong> target fungus be<strong>for</strong>e contact is actually made. Once <strong>the</strong> fungi come into<br />

contact, Trichoderma spp. attach to <strong>the</strong> host and can coil around it and <strong>for</strong>m appressoria<br />

(=specialized pressing organs from which a minute infection peg can grow and infect a cell)<br />

on <strong>the</strong> host surface. Attachment is mediated by <strong>the</strong> binding <strong>of</strong> carbohydrates in <strong>the</strong><br />

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Trichoderma cell wall to lectins (proteins having high affinity towards <strong>the</strong> carbohydrates)<br />

on <strong>the</strong> target fungus. Once in contact, <strong>the</strong> Trichoderma produce several fungitoxic cell-walldegrading<br />

enzymes, and probably also peptaibol antibiotics. The combined activities <strong>of</strong><br />

<strong>the</strong>se compounds result in parasitism <strong>of</strong> <strong>the</strong> target fungus and dissolution <strong>of</strong> <strong>the</strong> cell walls.<br />

At <strong>the</strong> sites <strong>of</strong> <strong>the</strong> appressoria, holes can be produced in <strong>the</strong> target fungus, and direct entry<br />

<strong>of</strong> Trichoderma hyphae into <strong>the</strong> lumen <strong>of</strong> <strong>the</strong> target fungus occurs. There are at least 20-30<br />

known genes, proteins and o<strong>the</strong>r metabolites that are directly involved in this interaction,<br />

which is typical <strong>of</strong> <strong>the</strong> complex systems that are used by <strong>the</strong>se fungi in <strong>the</strong>ir interactions<br />

with o<strong>the</strong>r organisms.<br />

Scanning electron micrograph <strong>of</strong> <strong>the</strong> surface <strong>of</strong> hyphae <strong>of</strong> <strong>the</strong> plant pathogen Rhizoctonia solani<br />

after mycoparasitic Trichoderma hyphae were removed. Erosion <strong>of</strong> <strong>the</strong> cell wall due to <strong>the</strong> activity<br />

<strong>of</strong> cell wall degrading enzymes from <strong>the</strong> biocontrol fungus is evident, as are holes where <strong>the</strong><br />

mycoparasitic Trichoderma hyphae penetrated <strong>the</strong> R. solani (photo courtesy <strong>of</strong> Ilan Chet, Hebrew<br />

University <strong>of</strong> Jerusalem).<br />

2. Sevearl yeasts, <strong>for</strong> example, Pichia guilliermondii, also parasitize and inhibit <strong>the</strong> growth <strong>of</strong><br />

Botrytis, Penicillium, and o<strong>the</strong>r plant pathogenic fungi.<br />

3. Fungal plant pathogens that develop sclerotia are difficult to control as <strong>the</strong>se propagules<br />

persist <strong>for</strong> long periods in soil. Several fungi which invade sclerotia and act as<br />

mycoparasite have now been identified. One <strong>of</strong> <strong>the</strong> most interesting is Sporidesmium<br />

sclerotiorum, which obligately parasitizes sclerotia <strong>of</strong> five important pathogens, Sclerotinia<br />

sclerotiorum, S. minor, S. trifoliorum, Selerotium cepivorum and Botrytis cinerea. Spores <strong>of</strong><br />

this mycoparasite added in sufficient quantities have been shown to give good control <strong>of</strong><br />

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diseases such as lettuce drop caused by Sclerotinia minor. After infection, glucanose<br />

activity in <strong>the</strong> sclerotia increases, resulting in <strong>the</strong> production <strong>of</strong> glucose, which is readily<br />

assimilated by <strong>the</strong> mycoparasite and allows growth <strong>of</strong> germ tubes out <strong>of</strong> <strong>the</strong> sclerotium and<br />

into <strong>the</strong> soil <strong>for</strong> a distance <strong>of</strong> up to 3 cm. O<strong>the</strong>r sclerotia within this radius are infected.<br />

Exploitation <strong>of</strong> this property by disking in inoculums <strong>of</strong> spores <strong>of</strong> <strong>the</strong> fungus resulted in 53<br />

per cent control <strong>of</strong> lettuce drop caused by S. minor. Ano<strong>the</strong>r sclerotial parasite,<br />

Conyothirium minitans, has also been demonstrated biological control potential, but only<br />

when added to soil at high inoculums rates.<br />

Antibiosis<br />

Antibiosis is that antagonistic condition in which <strong>the</strong>re is suppression <strong>of</strong> pathogenic<br />

microorganisms due to secretion <strong>of</strong> toxic or inhibitory compounds (antibiotics) by o<strong>the</strong>r<br />

microorganisms. Such compounds range from hydrogen cyanide (HCN) to enzymes and <strong>the</strong><br />

microorganisms involved are <strong>of</strong>ten species <strong>of</strong> Trichoderma and Gliocladium among fungi, and<br />

Bacillus and Pseudomonas among bacteria. The pioneer work on <strong>the</strong> isolation and identification <strong>of</strong><br />

antibiotic compounds from BCAs concerned are those syn<strong>the</strong>sized by fungal antagonists. For<br />

instancei.<br />

Ghisalberti et al. (1990) isolated two pyrone antibiotics from <strong>the</strong> isolates <strong>of</strong> Trichoderma<br />

harzianum that suppressed take all disease <strong>of</strong> wheat (Gaeumanomyces graminis f. sp. tritici).<br />

ii. Inhibition in <strong>the</strong> growth <strong>of</strong> plant pathogenic fungi (Rhizoctonia solani, Phoma betae and<br />

Pythium ultimum) by Laetisaric aravilis, a basidiomycete, has been observed in both<br />

laboratory and field trials; <strong>the</strong> inhibitory substance has been a long chain fatty acid called<br />

laetisaric acid.<br />

Many antibiotics have been isolated and characterized from Trichoderma. These include<br />

gliotoxin, gliovirin and glioviridin from T. virens. and viridin, alkyl pyrones, isonitriles, polyketides,<br />

peptaibols, diketopiperazines, sesquiterpenes and some steroids from o<strong>the</strong>r Trichoderma spp.<br />

Bacteria BCAs are known to produce most diverse range <strong>of</strong> antimicrobial compounds. Bacillus<br />

subtilis effectively controls Rhizoctonia solani in many crops by producing bacilysin and<br />

fengymycin. Bacilysin inhibits yeast and bacteria and fengymycin inhibits filamentous fungi. In<br />

1994, however, zwittermicin A antibiotic has been obtained from Bacillus cereus strain UW 85,<br />

ano<strong>the</strong>r successful biological control agent <strong>of</strong> damping <strong>of</strong>f and root rot <strong>of</strong> soybean (Phytophthora<br />

sojae). The first commercial BCA was probably strain K84 <strong>of</strong> Agrobacterium which has been used<br />

successfully to control crown gall disease by Agrobacterium tumefaciens by agrocin 84 antibiotic.<br />

Strains <strong>of</strong> Pseudomonas produce several toxic inhibitory compounds including phenazine-1-<br />

carboxylic acid, phenazine-1-carboxamide, anthranilic acid, diacetyl phloroglucinol, pyoluteorin,<br />

pyrrolnitrin and viscosinamide.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Some antibiotic products <strong>of</strong> BCAs, <strong>the</strong>ir class, source microorganism and target<br />

microorganism.<br />

Class <strong>of</strong><br />

compound<br />

Antibiotic product Source microorganism Target<br />

microorganism<br />

Amino acid Basilycin Bacillus subtilis Yeasts and<br />

derived<br />

Bacteria<br />

Aminopolyol Zwittermicin A Bacillus cereus Fungi<br />

Cyanide HCN Pseudomonas fluorescens Fungi<br />

Enzymes chitinase Serratia marcescens Fungi<br />

Fatty acid Laetisaric acid Laetisaria arvalis Fungi<br />

Furanone<br />

Lipopeptide<br />

3-(1-hexenyl)-5-<br />

methyl-2-<br />

Iturin,<br />

Surfactin,<br />

Viscosin amide<br />

Pseudomonas aure<strong>of</strong>aciens Fusarium spp.<br />

Pythium ultimum,<br />

Rhizoctonia solani,<br />

Thielaviopsis<br />

basicola<br />

Bacillus subtilis, Bacillus subtilis,<br />

Pseudomonas fluorescens DR<br />

54<br />

Nicotinic acid 2-methylheptyl Streptomyces sp.<br />

derived<br />

isonicotinate<br />

Nucleotide Agrocin 84 Agrobacterium strain K 84<br />

Agrobacterium strain K 1026<br />

Peptide Dimerum (a Trichoderma virens,<br />

siderophore) Brevibacillus brevis<br />

Gramicidin S<br />

Phenazine Phenazine-1- Pseudomonas fluorescens,<br />

carboxylic acid, Pseudomonas chlororaphis PCL<br />

Phenazine-1- 1391<br />

Phenol<br />

carboxamide<br />

Anthranilic acid,<br />

Diacetylphloroglucinol,<br />

Flavipin,<br />

Pyoluteorin<br />

Pseudomonas fluorescens,<br />

Pseudomonas fluorescens,<br />

Epicoccum nigrum,<br />

Pseudomonas fluorescens<br />

Fungi and<br />

Bacteria,<br />

Fungi and<br />

Bacteria,<br />

Pythium ultimum<br />

Rhizoctonia solani,<br />

Fusarum spp.<br />

Agrobacterium<br />

tumefaciens<br />

Fungi<br />

Botrytis cinerea<br />

Gaeumannomyces<br />

graminis f.sp. tritici<br />

Gaeumannomyces<br />

graminis f.sp.<br />

tritici,<br />

Monilia laxa,<br />

Pythium ultimum,<br />

Piperazine Gliotoxin Gliocladium virens Fungi<br />

Pyrone 6-pentyl-α-pyrone Trichoderma spp. Gaeumannomyces<br />

graminis f.sp. tritici<br />

Peptaibols<br />

Trichozianins,<br />

trichokindins,<br />

trichorzins,<br />

harzianins,<br />

trichogins etc<br />

Trichoderma spp.<br />

Phenyl-pyrrole Pyrrolnitrin Pseodomonas spp. Fungi<br />

Inhibit a number <strong>of</strong><br />

fungi and gram<br />

positive bacteria<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Mass Production and Formulation Technology <strong>of</strong> Trichoderma<br />

Roopali Sharma and Bhanu Pratap Bhadauria<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Materials required: Barnyard millet (jhangora), 250 ml Erlenmayer flasks, inoculating<br />

needle, Trichoderma culture, Talcum powder, CMC, Sieves, Grinder, Polypropylene bags<br />

Mass multiplication <strong>of</strong> Trichoderma isolates<br />

Barnyard millet (jhangora) grains are used to prepare pure powder <strong>of</strong> Trichoderma.<br />

1. Wash and soak <strong>the</strong> grains in water <strong>for</strong> 12 h and <strong>the</strong>n filled in 250 ml Erlenmeyer flasks (@<br />

100g/ flask) or in half kg polypropylene bags (150 grains/bag).<br />

2. Plug <strong>the</strong> flasks and bags with non absorbent cotton plug (with <strong>the</strong> help <strong>of</strong> neck).<br />

3. Autoclave at 20 lbs psi. <strong>for</strong> 20 min.<br />

4. After cooling to room temperature, inoculate <strong>the</strong> flasks or bags with 4-6 discs <strong>of</strong> actively<br />

growing culture <strong>of</strong> Trichoderma harzianum.<br />

5. Incubate <strong>the</strong> bags at 28 ° C <strong>for</strong> 10-12 days and shake at regular intervals.<br />

6. The colonized grains turn green with sporulation.<br />

7. After 12 days, <strong>the</strong> colonized grains are emptied into plastic trays and dried under shade <strong>for</strong><br />

4-5 days.<br />

8. The dried colonized grains are <strong>the</strong>n ground with <strong>the</strong> help <strong>of</strong> Willey Mill or normal grinder to<br />

get a powder.<br />

9. This powder is <strong>the</strong>n sieved through a normal coarse (50 mesh size) and fine (80 mesh<br />

size) sieves, simultaneously to obtain a very fine pure powder.<br />

10. This pure powder is <strong>the</strong>n mixed with talcum powder in a ratio <strong>of</strong> 10 g pure powder + 1kg<br />

Talcum powder (commercial grade ) get <strong>the</strong> commercial <strong>for</strong>mulation. The shelf life <strong>of</strong> <strong>the</strong><br />

<strong>for</strong>mulation is <strong>for</strong> four months under room temperature and six months under controlled<br />

conditions.<br />

11. 10% Carboxy Methyl Cellulose (CMC) is also added as a sticker.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Identification <strong>of</strong> Pseudomonas and Bacillus isolates using Biolog<br />

System<br />

J.Kumar, Roopali Sharma, Smita Puri and Kahkashan Arzoo<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

In recent years, popular methods <strong>for</strong> studying plant pathogens community structure were<br />

based on <strong>the</strong> analysis <strong>of</strong> phospholipid fatty acids (PLFA) or denaturing/temperature gradient gel<br />

electrophoresis (DGGE/TGGE) etc. The above-mentioned methods are based on molecular<br />

assays. Measurements <strong>of</strong> physiological activity <strong>of</strong> microorganisms represent ano<strong>the</strong>r approach,<br />

allowing <strong>the</strong> study <strong>of</strong> different characteristics <strong>of</strong> microbial communities. The Biolog technique is<br />

one <strong>of</strong> <strong>the</strong> methods which rely on measurements <strong>of</strong> utilizing different carbon substrates by<br />

microorganisms. Measurements <strong>of</strong> substrate use enable qualifying microbial metabolic capabilities<br />

and hence functional diversity <strong>of</strong> a microbial community.<br />

The Principle <strong>of</strong> <strong>the</strong> Biolog Method - The Biolog plate’s method was first used to compare<br />

metabolic activity <strong>of</strong> heterotrophic microbial communities from different habitats such as water, soil<br />

and wheat rhizosphere. The technique is based on a redox system. Various types <strong>of</strong> plates are<br />

used, but Biolog GN plates <strong>for</strong> gram-negative bacteria are <strong>the</strong> most popular ones. Biolog Microbial<br />

Identification System is based on metabolic phenotypes. Biolog plates are plastic microtiter plates<br />

containing 95 different carbon substrates in wells, and no substrate in one well which is used as<br />

control. Among <strong>the</strong> 95 substrates one can distinguish a few groups <strong>of</strong> chemical compounds, <strong>for</strong><br />

example, carbohydrates, amino acids, carboxylic acids, amines, amides and polymers. Biolog is<br />

based on <strong>the</strong> <strong>the</strong>ory that a species <strong>of</strong> bacteria develops a unique metabolic finger-print on a set <strong>of</strong><br />

carbon sources and biochemicals. The cultured bacteria are tested <strong>for</strong> utilization <strong>of</strong> different<br />

carbon sources and biochemicals, which are pre-filled and dried into a 96 well test plate.<br />

Additionally, each well contains a colourless Tetrazolium redox dye, used to colorimetrically<br />

indicate utilization <strong>of</strong> <strong>the</strong> substrates. Cells utilizing nutrient, respire and release energy which<br />

reduces proprietary Tetrazolium dye to <strong>for</strong>m a distinct purple colour. Biolog data collection<br />

s<strong>of</strong>tware is used to record <strong>the</strong> unique metabolic pr<strong>of</strong>ile into <strong>the</strong> computer which can be compared<br />

with thousands <strong>of</strong> pr<strong>of</strong>iles (corresponding to thousands <strong>of</strong> species) stored in <strong>the</strong> Biolog databases.<br />

If <strong>the</strong> pr<strong>of</strong>ile is matched, computer displays <strong>the</strong> identified species.<br />

Biolog has designed proprietary microplates <strong>for</strong> identification <strong>of</strong> a wide range <strong>of</strong> microbes<br />

up to species level, such as Gen III plate (<strong>for</strong> gram negative and gram positive aerobic bacteria),<br />

AN plate (<strong>for</strong> anaerobic bacteria), YT plate (<strong>for</strong> yeast) and FF plate (<strong>for</strong> filamentous fungi). Nearly<br />

2550 species are covered by Biolog <strong>for</strong> identification.<br />

Application- It has been used <strong>for</strong> clean room analysis <strong>of</strong> microbial identification prevalent in<br />

environment, industrial quality control in analysis <strong>of</strong> food and/or agricultural products, plant disease<br />

diagnosis, veterinary, analysis <strong>of</strong> clinical samples including dangerous pathogens <strong>of</strong> human,<br />

animal and plant origin, education and research involving general and applied microbiology.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Different types <strong>of</strong> Biolog plates- The Biolog GNplates have been designed <strong>for</strong> identification <strong>of</strong><br />

gram negative bacteria and contain substrates appropriate <strong>for</strong> this group <strong>of</strong> microorganisms.<br />

Analogically, <strong>the</strong> GP plates are adapted <strong>for</strong> identification <strong>of</strong> gram positive bacteria. Two types <strong>of</strong><br />

Biolog plates are available i.e. GEN II and GEN III. Microbial identification <strong>for</strong> GEN II MicroPlates<br />

involves five basic steps (identification process <strong>for</strong> AN, YT, or FF) while GEN III plates involves in<br />

four basic steps. These steps apply to all identifications. A small number <strong>of</strong> species have<br />

peculiarities that may require an extra step or special handling techniques.<br />

The Microbial Identification Process <strong>for</strong> GEN II MicroPlates<br />

Step 1: Isolation <strong>of</strong> a pure culture - As a first step to accurate microbe identification, streak agar<br />

plates using correct techniques to generate well isolated colonies. Always use Biologrecommended<br />

culture media and growth conditions.<br />

Step 2: Gram staining and determining test protocol- For bacteria, proper Gram stain<br />

technique and interpretation are <strong>the</strong> important second step in <strong>the</strong> ID process identification; use <strong>the</strong><br />

wet prep test as necessary to differentiate yeasts from filamentous fungi.<br />

Step 3: Prepare inoculum at specified cell density- Determine cell density using Colorimeter.<br />

Cell density describes oxygen concentration a key parameter to control when testing<br />

microorganisms in MicroPlates. Additionally, Biolog has carefully optimized <strong>the</strong> required<br />

inoculating fluids and standards.<br />

Step 4: Inoculate and incubate MicroPlate- Pipette <strong>the</strong> specified amount <strong>of</strong> cell suspension into<br />

<strong>the</strong> MicroPlate, put <strong>the</strong> lid on, and incubate under <strong>the</strong> same conditions <strong>of</strong> temperature and<br />

atmosphere used to culture <strong>the</strong> microorganism. Biolog MicroPlates do not need oil overlays or<br />

color-developing chemicals.<br />

Step 5: Read MicroPlate and determine ID- After an appropriate incubation time, read<br />

MicroPlates ei<strong>the</strong>r by eye or using <strong>the</strong> MicroStation Reader. In ei<strong>the</strong>r case, <strong>the</strong> pattern <strong>for</strong>med in<br />

<strong>the</strong> wells is entered into <strong>the</strong> s<strong>of</strong>tware, which searches <strong>the</strong> database and provides identification in<br />

seconds.<br />

Data is fed into a s<strong>of</strong>tware enabled computer which per<strong>for</strong>ms analysis and reports <strong>the</strong><br />

species <strong>of</strong> <strong>the</strong> isolated micro-organism.<br />

‣ A large sized database is comprised <strong>of</strong> ~2550 species <strong>of</strong> which ~700 are <strong>of</strong> clinical<br />

importance.<br />

‣ Gen II Microplate can be used to identify 1350 species <strong>of</strong> aerobic bacteria.<br />

‣ AN Microplate can be used to identify 361 species <strong>of</strong> anaerobic bacteria.<br />

‣ YT Microplate can be used to identify 267 species <strong>of</strong> yeast.<br />

‣ FF Microplate can be used to identify 619 species <strong>of</strong> filamentous fungi (619 species).<br />

‣ GN2 Microplate can be used to identify species <strong>of</strong> gram negative bacteria.<br />

‣ GP2 Microplate can be used to identify species <strong>of</strong> gram positive bacteria.<br />

Technology can be used in manual, semi-automatically or fully automatically as per <strong>the</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

researcher’s variable needs and budget.<br />

Gen III Microstation System (Most preferred system)- GEN III Microstation is a semi-automated<br />

microbial identification system. It is Plate reader which is linked to a computer configured with<br />

s<strong>of</strong>tware related to data collection and microbial identification s<strong>of</strong>tware. It is capable <strong>of</strong> reading all<br />

types <strong>of</strong> Biolog Microplates. A microplate loaded with suspension <strong>of</strong> a test organism is incubated in<br />

a user-provided incubator and read using Microstation. The metabolic finger print is read and sent<br />

to <strong>the</strong> computer <strong>for</strong> recording and eventual comparative studies with pr<strong>of</strong>iles already stored in<br />

Biolog databases. Computer reports <strong>the</strong> species/genus when <strong>the</strong> metabolic finger print is matched<br />

with those present in Biolog Database. The system is capable <strong>of</strong> identifying aerobic bacteria,<br />

anaerobic bacteria, yeast as well as filamentous fungi.<br />

System Benefits- No Gram stain is needed. One test panel IDs <strong>for</strong> both GN and GP bacteria. Setup<br />

time in under a minute, accurate results in as little as 4 hours, Powerful RetroSpect s<strong>of</strong>tware <strong>for</strong><br />

trending and tracking.<br />

Gen III Omnilog Id System (Preferred system <strong>for</strong> handling a large number <strong>of</strong> samples)- Gen III<br />

Omnilog Id System is an automated microbial identification system. It is provided along with Omnilog<br />

which is Plate reader cum Incubator. It is linked to a computer configured with s<strong>of</strong>tware related to<br />

data collection and microbial identification s<strong>of</strong>tware. A microplate loaded with suspension <strong>of</strong> test<br />

organism is incubated and read in Omnilog. The metabolic finger print is read and sent to <strong>the</strong><br />

computer <strong>for</strong> recording and eventual comparative studies with pr<strong>of</strong>iles already stored in Biolog<br />

databases. Computer reports <strong>the</strong> species/genus when <strong>the</strong> metabolic finger print is matched with<br />

those present in Biolog Database. Omnilog can accommodate 50 Microplates simultaneously, with<br />

recording <strong>of</strong> <strong>the</strong> metabolic finger-print at 15 minutes interval in real-time thus making <strong>the</strong> microbial<br />

identification automated and high throughput. The system is capable <strong>of</strong> automated identification <strong>of</strong><br />

aerobic bacteria only. It can be upgraded to undertake Phenotype Microarray.<br />

Gen III Omnilog Plus Id System- The system is capable <strong>of</strong> automated identification <strong>of</strong> aerobic<br />

bacteria, and rapid identification <strong>of</strong> anaerobic bacteria, yeast as well as filamentous fungi.<br />

Gen III Microlog M System (Manual System)- Microlog M is <strong>the</strong> Manual Version <strong>of</strong> Biolog’s<br />

Microbial Identification System. It uses <strong>the</strong> same Gen III plate and Gen III Microbial Identification<br />

s<strong>of</strong>tware, as are used in automated systems. Difference is that Computer and Plate Reader, are<br />

not provided in Manual System. Microbial culture is used to inoculate <strong>the</strong> Gen III plate, which is<br />

<strong>the</strong>n incubated in a lab incubator. Plate is read <strong>for</strong> all <strong>the</strong> 96 tests manually in terms <strong>of</strong> Positive or<br />

Negative reaction (If color appears, it is positive o<strong>the</strong>rwise negative). The plate results (positive or<br />

negative), are fed manually in Gen III s<strong>of</strong>tware which is provided and loaded in a user provided<br />

computer. S<strong>of</strong>tware does <strong>the</strong> analysis, searches Biolog provided database, and <strong>the</strong>n reports <strong>the</strong><br />

species. You can also update <strong>the</strong> database with those genus/species which are not present in<br />

Biolog database (using an optional Retrospect). Manual system can be used <strong>for</strong> only aerobic<br />

bacteria.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Biochemical Tests <strong>for</strong> Identification <strong>of</strong> Bacterial Pathogens<br />

Yogendra Singh and Bhupendra Singh Kharayat<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

The identification and classification <strong>of</strong> bacteria are <strong>of</strong> crucial importance in environmental,<br />

industrial, medical and agricultural microbiology and microbial ecology. A number <strong>of</strong> different<br />

phenotypic and genotypic methods are presently being employed <strong>for</strong> microbial identification and<br />

classification. Each <strong>of</strong> <strong>the</strong>se methods permits a certain level <strong>of</strong> phylogenetic classification, from <strong>the</strong><br />

genus, species, subspecies, biovar to <strong>the</strong> strain specific level. Moreover, each method has its<br />

advantages and disadvantages; with regard to ease <strong>of</strong> application, reproducibility, requirement <strong>for</strong><br />

equipment and level <strong>of</strong> resolution.<br />

Gram Staining<br />

Requirements<br />

<br />

<br />

<br />

Protocol<br />

24 h old culture <strong>of</strong> test bacterium<br />

Slides, light microscope, glass rods, cotton, vim powder, blotting sheets, tap water<br />

Hucker’s crystal violet stain, safranin, 95% alcohol, iodine solution<br />

1. Take a loopful <strong>of</strong> <strong>the</strong> test organism.<br />

2. Spread on a clean slide and allow it to air dry.<br />

3. Gently heat to fix <strong>the</strong> smear.<br />

4. Cover <strong>the</strong> smear with crystal violet <strong>for</strong> 1 minute.<br />

5. Flash wash in running water <strong>for</strong> a few seconds.<br />

6. Rinse <strong>the</strong> smear with iodine and cover <strong>for</strong> 1 minute.<br />

7. Rinse <strong>the</strong> slide in running water.<br />

8. Decolorize with alcohol (95%) drop wise till <strong>the</strong> dye does not run <strong>of</strong>f <strong>the</strong> smear.<br />

9. Rinse with water.<br />

10. Cover <strong>the</strong> smear with counter stain safranin <strong>for</strong> 30 seconds.<br />

11. Rinse with water and blot dry. Observe under oil immersion lens.<br />

Observation<br />

The gram positive cells stain purple and <strong>the</strong> gram negative cells stain red.<br />

KOH Confirmatory Test/ Solubility Test<br />

Requirements<br />

<br />

<br />

<br />

Protocols<br />

<br />

Test bacterial culture <strong>of</strong> 24 h growth.<br />

Potassium hydroxide (3% aq., w/v)<br />

Inoculation loop, glass slides<br />

With <strong>the</strong> help <strong>of</strong> a pipette place a drop <strong>of</strong> KOH on clean slide.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

With sterile loop remove a part <strong>of</strong> a single, well- separated colony from a young actively<br />

growing culture.<br />

Mix <strong>the</strong> culture into <strong>the</strong> KOH until an even suspension is obtained.<br />

Lift <strong>the</strong> loop from <strong>the</strong> slide and observe.<br />

Observation<br />

If a string <strong>of</strong> slime is lifted with <strong>the</strong> loop, <strong>the</strong> bacterium is Gram negative. If a watery<br />

suspension is produced and no string <strong>of</strong> slime observed, <strong>the</strong> culture is Gram positive.<br />

Catalase Production test<br />

Requirements<br />

Test bacterium<br />

Hydrogen peroxide (H 2 O 2 )<br />

Glass slide<br />

Protocols<br />

Smear a loopful <strong>of</strong> 24-48 hr slant growth on a slide<br />

Cover it with a few drop <strong>of</strong> hydrogen peroxide<br />

Observation: Production <strong>of</strong> gas bubbles (O 2 ) indicates a positive reaction.<br />

Test <strong>for</strong> H 2 S production<br />

Requirements<br />

Test bacterium<br />

Strips <strong>of</strong> filter paper (Whatman No. 42)<br />

Lead acetate<br />

Protocols<br />

Take strips <strong>of</strong> filter paper (Whatman No. 42) impregnated with lead acetate solution<br />

Air dry <strong>the</strong> strips and autoclave <strong>the</strong>m<br />

Keep autoclaved strips inside <strong>the</strong> slants inoculated with <strong>the</strong> bacterial isolate, one end <strong>of</strong><br />

<strong>the</strong> strip is held by <strong>the</strong> cotton plug and <strong>the</strong> o<strong>the</strong>r end is free and hanging.<br />

Incubate at 28 0 C <strong>for</strong> 3 days.<br />

Observation<br />

Blackening <strong>of</strong> strip indicates a positive reaction.<br />

Medium <strong>for</strong> production <strong>of</strong> H 2 S<br />

Peptone: 10 g<br />

NaCl: 5 g<br />

Water: 1000 ml<br />

Agar 20g<br />

pH: 7.0<br />

Citrate test<br />

Simmons Citrate Agar is used <strong>for</strong> <strong>the</strong> differentiation <strong>of</strong> gram negative bacteria on <strong>the</strong> basis <strong>of</strong><br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

citrate utilization.<br />

Medium<br />

Ammonium Dihydrogen Phosphate 1.0g<br />

Dipotassium Phosphate 1.0g<br />

Sodium Chloride 5.0g<br />

Sodium Citrate 2.0g<br />

Magnesium Sulfate 0.2g<br />

Agar 15.0g<br />

Bromthymol Blue 0.08g<br />

Distilled water<br />

1000ml<br />

Protocol:<br />

Dispense <strong>the</strong> medium and autoclave at121 0 C <strong>for</strong> 15 minutes<br />

Allow to cool in a slanted position <strong>for</strong> use as slants. Medium may also be used <strong>for</strong> plating<br />

Inoculate slants with growth from a pure culture<br />

Incubate <strong>for</strong> 4 days at 35±2 0 C.<br />

Observation: Growth with blue colour in <strong>the</strong> slants indicates a positive reaction whereas<br />

negative reaction is evidenced by no to trace growth with original dark green medium (no<br />

change in colour).<br />

Oxidase Test<br />

Impregnated disk method<br />

In this method reagent impregnated disks are used.<br />

Wet <strong>the</strong> disks with de-ionized water using inoculating loop<br />

With <strong>the</strong> help <strong>of</strong> loop aseptically transfer a large mass <strong>of</strong> pure bacteria to <strong>the</strong> disk<br />

Observe <strong>the</strong> disk <strong>for</strong> colour change. If <strong>the</strong> area <strong>of</strong> inoculation turns dark blue, <strong>the</strong> result<br />

is positive<br />

Precautions: Per<strong>for</strong>m <strong>the</strong> oxidase test on fresh cultures. Using older cultures may yield<br />

unexpected results. The colour change should occur within <strong>the</strong> first 30 seconds. Disregard any<br />

colour change after this time period. Do not use a nichrome loop as this may lead to a false<br />

positive result.<br />

Logan’s Differential Medium <strong>for</strong> Erwinia<br />

The medium was developed by Logan in 1966 to distinguish E.carotovora pv. atroseptica<br />

from pv. carotovora. E.carotovora pv. carotovora reduces <strong>the</strong> tetrazolium to insoluble red <strong>for</strong>mazan<br />

and colonies (about 1.5 mm dia.) develop a pink to red/purple colour.<br />

Nutrient agar<br />

28.0 g<br />

Yeast extract<br />

5.0 g<br />

Glucose 5.0g<br />

Water<br />

1000 ml<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

After autoclaving, <strong>the</strong> medium is cooled to 60 0 C and 10 ml <strong>of</strong> filtered-sterilized 0.5%<br />

solution <strong>of</strong> 2,3,5-tri phenyl tetrazolium chloride added.<br />

Suggested readings<br />

• Janse, J. D. 2006. Phytobacteriology principles and practice.366p.<br />

• Schaad, N.W.; Jones, J.B. and Chun, W. 2001. Laboratory Guide <strong>for</strong> Identification <strong>of</strong><br />

<strong>Plant</strong> Pathogenic Bacteria. 3rd edn. St Paul, MN, USA: APS Press.158.<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

Visit to Meteorological Observatory and Automatic Wea<strong>the</strong>r Station in<br />

Cropped Field at N.E.B. CRC<br />

Introduction<br />

H. S. Kushwaha<br />

Department <strong>of</strong> <strong>Soil</strong> Science, G.B.P.U.A.&T., Pantnagar- 263 145 (Uttarakhand)<br />

Since <strong>the</strong> meteorological instruments in <strong>the</strong> meteorological observatories are exposed<br />

over <strong>the</strong> short cut grass, apparently <strong>the</strong> values <strong>of</strong> some <strong>of</strong> <strong>the</strong> important wea<strong>the</strong>r variables<br />

especially <strong>the</strong> air temperature, relative humidity, leaf wetness and <strong>the</strong> wind in particular may<br />

differ significantly from those observed in a cropped field. The major meteorological instruments<br />

available at meteorological observatory included Stevension screen to house maximum<br />

<strong>the</strong>rmometer, minimum <strong>the</strong>rmometer, dry bulb <strong>the</strong>rmometer and wet bulb <strong>the</strong>rmometer, three soil<br />

<strong>the</strong>rmometers each at 5, 10 and 20 cm soil depth, USWB Class A open Pan evaporimeter,<br />

Ordinary & self recording rain gauges, Anemometer, Wind vane, Bright Sunshine recorder, dew<br />

gauge etc. The data is recorded daily twice a day at 0712 hrs and at 1412 hrs at Pantnagar by<br />

IMD trained meteorological observers and record is maintained in pocket registers supplied by<br />

IMD. However, <strong>the</strong> validity <strong>of</strong> such wea<strong>the</strong>r data recorded at meteorological observatory at a<br />

location from a field experiment will decrease with<br />

<strong>the</strong> distance from <strong>the</strong> meteorological<br />

observatory. Keeping in view this constraint, <strong>for</strong> disease-wea<strong>the</strong>r relationship it is, recommended<br />

& advised to monitor <strong>the</strong>se important wea<strong>the</strong>r variables over and within <strong>the</strong> crops under natural<br />

field conditions. These fields have variability in terms <strong>of</strong> crops <strong>the</strong>ir type and stage, soil<br />

moisture, ground water table, tillage operations <strong>for</strong> soil manipulation etc. as compared with <strong>the</strong><br />

meteorological observatory field. Also detailed and reliable wea<strong>the</strong>r in<strong>for</strong>mation is also not<br />

available in many locations in <strong>the</strong> country due to non-availabilty <strong>of</strong> meteorological observatories.<br />

For this purpose, a Scientific Automatic Wea<strong>the</strong>r Station (AWS) attached with micrologger and<br />

Computer will be very useful <strong>for</strong> recording <strong>of</strong> wea<strong>the</strong>r parameters within and over <strong>the</strong> crops<br />

accurately and <strong>the</strong>n correlate <strong>the</strong>m with crop observations <strong>for</strong> understanding <strong>the</strong> real crop -<br />

wea<strong>the</strong>r relationships in general and disease - wea<strong>the</strong>r relationships in particular <strong>for</strong> major crops<br />

<strong>of</strong> <strong>the</strong> area. There is a close relationship between crop diseases and wea<strong>the</strong>r variables and,<br />

<strong>the</strong>re<strong>for</strong>e, under prevailing wea<strong>the</strong>r conditions, <strong>the</strong> incidence <strong>of</strong> several diseases may occur in an<br />

area and <strong>the</strong> application <strong>of</strong> chemicals in <strong>the</strong>se crops will depend on <strong>the</strong> intensity and durability <strong>of</strong><br />

<strong>the</strong> wea<strong>the</strong>r conditions prevailing at particular and sensitive crop stage. The details <strong>of</strong> observations<br />

are given below :<br />

A. Meteorological observatory<br />

A plain area <strong>of</strong> 55 m (N-W) x 36 m (E-W) size with short cut grasses free from all<br />

obstacles including highway, high building, big trees, canals, rivers and wild animals provides a<br />

good exposure <strong>for</strong> installing all <strong>the</strong> meteorological instruments in <strong>the</strong> observatory. If a person<br />

stands at <strong>the</strong> gate facing <strong>the</strong> observatory plot, he will find <strong>the</strong> tall instruments in <strong>the</strong> back row and<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

shorter instruments in <strong>the</strong> front rows. In general <strong>the</strong> instruments are separated at a distance <strong>of</strong> 9 m<br />

from each within rows <strong>of</strong> 12 m apart. All observations are taken manually by meteorological<br />

observer daily twice a day.<br />

B. Automatic wea<strong>the</strong>r station (AWS)<br />

A Campbell Scientific Automatic Wea<strong>the</strong>r Station has been designed and developed to a<br />

very high standard <strong>for</strong> reliable measurement and recording <strong>of</strong> wide range <strong>of</strong> important<br />

micrometeorological variables in and above <strong>the</strong> crops The station is soundly engineered and<br />

based Campbell,s proven 21X micrologger whose comprehensive specification enables <strong>the</strong> user<br />

to undertake virtually any monitoring task. The main and important features <strong>of</strong> <strong>the</strong> system are<br />

described as below:<br />

1. Wide range <strong>of</strong> sensors: A maximum <strong>of</strong> 20 sensors can be a attached to this at a time.<br />

2. Flexible data storage: It has Internal memory to store 19, 200 data points i.e. hourly data <strong>for</strong><br />

continuous 40 days at a time can be stored.<br />

3. Versatile data transfer: S<strong>of</strong>tware package is available <strong>for</strong> automatic routine collection <strong>of</strong> data<br />

at pre determined time interval which can be modified as per <strong>the</strong> need and requirement.<br />

4. Fully protected: It has a wea<strong>the</strong>r pro<strong>of</strong> enclosure to protect data logger and peripheral against<br />

dust and moisture. The logger can operate over <strong>the</strong> range from - 25 o C to + 50 o C without any<br />

error.<br />

5. Integral data processing: The processing includes <strong>the</strong> averages <strong>of</strong> maximum and minimum<br />

averages <strong>of</strong> all wea<strong>the</strong>r variables, standard deviations, wind vector integration etc.<br />

6. Robust construction: Tripod and mast are build from thick walled, galvanished steel tubing<br />

with nickle-plated fittings. The mast is 3 metre in height with adjustable cross-arm supports <strong>for</strong><br />

sensors. The mast can be positoned precisely by independently adjusting tripod legs. Each leg is<br />

provided with a flat foot with 12 mm hole which allows anchorage to <strong>the</strong> ground by stake or to<br />

concrete. A lightning conductor and earth spike are also included to save <strong>the</strong> sensors and<br />

datalogger from destructive effects <strong>of</strong> Thunderstorm and Lightning as and when experienced in <strong>the</strong><br />

area. For measurement <strong>of</strong> wea<strong>the</strong>r parameters in and over <strong>the</strong> Horticutural crops, a mast <strong>of</strong> 30<br />

metre height (existing in <strong>the</strong> nearby site in <strong>the</strong> same field) can be used <strong>for</strong> sitting <strong>the</strong> sensors at<br />

desired heights depending upon <strong>the</strong> height <strong>of</strong> horticultural crops as per <strong>the</strong> need and requirement.<br />

7. Minimum maintenance: Once errected, <strong>the</strong> station requires very little routine attension.<br />

8. Recording device<br />

It has a 21 X Micrologger as recording device. It is a rugged field-proven datalogger<br />

suitable <strong>for</strong> any application requiring data acquisition, on line data processing or electronic control.<br />

It is compact and powerfull battery-powered device which effectively combines <strong>the</strong> functions <strong>of</strong><br />

micro-computer, clock, calibrator, scanner, frequency counter and controller with one smaller<br />

enclosure. The 12 volt Nickle-Cadmium battery is chargeable by solar pannel. The micrologger is<br />

programmed to handle almost any task including signal averaging, exite and delay, totaling,<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

maximum and minimum, standard deviation, scaling, 5th order polynomial processing, low-pass<br />

filtering and wind vector calculation which are fully supported by simple program statements,<br />

toge<strong>the</strong>r with a histogram command <strong>for</strong> direct calculation <strong>of</strong> frequency distributions. S<strong>of</strong>tware<br />

support is available to simplify more complex programming tasks and to avoid inspection and<br />

processing <strong>of</strong> stored data.<br />

Structure, Functioning and Sitting <strong>of</strong> Various Micro-meteorological Sensors on Automatic<br />

Wea<strong>the</strong>r Station<br />

This Automatic Wea<strong>the</strong>r Station (AWS) is composed with various micrometeorological<br />

instruments / sensors <strong>for</strong> monitoring <strong>the</strong> micrometeorological wea<strong>the</strong>r variables such as Air<br />

temperature ( o C), Relative humidity (%), Wind speed (m s -1 ), Wind direction (degrees from North),<br />

Leaf temperature ( o C), Leaf wetness ( % <strong>of</strong> total wet), Solar radiation (W m -2 ), Net radiation (W<br />

m -2 ), Rainfall (mm) , <strong>Soil</strong> temperature ( o C) etc. within and above <strong>the</strong> crop canopy. A brief<br />

description <strong>of</strong> sensors measuring <strong>the</strong>se wea<strong>the</strong>r variables is given under <strong>the</strong> following subheads:<br />

1. Air temperature and relative humidity:<br />

The air temperature and relative humidity in and above crop canopy are measured by HMP<br />

35 AC Temperature and Relative Humidity (RH) probes (two sensors). The probe contains a<br />

Vaisala capacitive relative humidity sensor and a precision <strong>the</strong>rmistor. The probe is designed to be<br />

housed in a 41004-5 or URSI radiation shield and is attached with a 3 m long lead wire and<br />

a connector. The length <strong>of</strong> lead wire can be increased as per <strong>the</strong> requirement.<br />

2. Wind speed:<br />

Wind speed in and above crop canopy is measured by A100R Switching Anemometer<br />

(two sensors) in which a magnet rotates with <strong>the</strong> rotor spindle. The varying field <strong>for</strong>ces a mercury<br />

wetted reed switch to make contact once per resolution. This instrument is a precision instrument<br />

which is easily interfaced with Datalogger to give accurate measurements <strong>of</strong> wind run or mean<br />

wind speed in m/s. This instrument is constructed from anodised aluminium alloy, stainless steels<br />

and wea<strong>the</strong>r resisting plastics. A stainless steel shaft runs in two precision, corrosion-resistant ball<br />

races. The bearings are protected from <strong>the</strong> entry <strong>of</strong> moisture droplets and dust, resulting <strong>the</strong><br />

instrument suitable <strong>for</strong> permanent exposure to <strong>the</strong> wea<strong>the</strong>r. Its sensitivity is 0.80 revolutions per<br />

metre with an overall accuracy <strong>of</strong> 2 % + 0.1 m s -1 .<br />

3. Wind Direction<br />

The wind direction at 3 m height is measured by W200P Potentiometer Wind Vane (one<br />

sensor). This instrument is manufactured by Vector Instruments Ltd. and measures <strong>the</strong> wind<br />

direction directly in degrees from North. The windvane incorporates a 358 degree micro - torque<br />

potentiomter (wire wound type). The 2 degree gap is filled to ensure operation and a long service<br />

life. The precision ball - bearing races are corrosion - resistant and are protected against <strong>the</strong> entry<br />

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<strong>of</strong> moisture and dust.<br />

4. Leaf Temperature<br />

The temperature ( o C) <strong>of</strong> leave is measured by K-Type Thermocouples (two sensors).<br />

Copper and constantan <strong>the</strong>rmocouple wires were twisted to <strong>for</strong>m <strong>the</strong> sensors and are connected<br />

to <strong>the</strong> leaves <strong>of</strong> <strong>the</strong> plants. There is provision <strong>of</strong> adding two more leaf temperature sensors.<br />

5. <strong>Soil</strong> Temperature:<br />

The soil temperature ( o C) at 10 and 20 cms soil depths are measured by 107 Thermister<br />

Probes (two sensors). These probes incorporate a precision <strong>the</strong>rmistor in a water resistant probe<br />

with a standard 3 m long cable.<br />

6. Leaf Wetness Period<br />

The duration <strong>of</strong> leaf wetness at crop surface is measured by 237 Wetness Sensing grid.<br />

This grid is suitable <strong>for</strong> a range <strong>of</strong> Scientific and Industrial wetness sensing applications. It<br />

provides a simple measure <strong>of</strong> <strong>the</strong> degree <strong>of</strong> wetness <strong>of</strong> <strong>the</strong> surface to which <strong>the</strong>y are attached /<br />

exposed and <strong>the</strong>y can also be used to measure <strong>the</strong> percentage <strong>of</strong> time <strong>for</strong> which <strong>the</strong> surface is wet<br />

or dry. The sensor consists <strong>of</strong> a rigid epoxy circuit board (75 mm x 60 mm) with interlacing gold -<br />

plated fingers. Condensation or rain on <strong>the</strong> sensor lowers <strong>the</strong> resistance between <strong>the</strong> fingers<br />

which is measured by <strong>the</strong> datalogger.<br />

7. Solar Radiation<br />

The Solar or Global radiation at 3 m height is being measured by SP1110 Pyranometer<br />

sensor (one sensor). This is a compact high - output <strong>the</strong>rmally stable solar radiation sensor. The<br />

cosine- errected head contains a special high grade Silicon Photocell sensitive to short-wave<br />

radiation with wavelength between 350 and 1100 nm. The head is completely sealed and can be<br />

left indefinitely in exposed conditions. A levelling mount is also available which enables <strong>the</strong><br />

pyranometer to be accurately positioned. The output is 10 mv / 1000 W m -2 with excellent linearity.<br />

8. Net Radiation:<br />

The net radiation which is <strong>the</strong> difference between <strong>the</strong> incomming solar radiation and <strong>the</strong><br />

outgoing radiation received on <strong>the</strong> crop surface is being measured by Q -7 Net Radiometer (one<br />

sensor). This instrument is high - output <strong>the</strong>rmopile sensor which measures <strong>the</strong> algebraic sum <strong>of</strong><br />

incoming and outgoing all - wave radiation (i.e. short- and long - wave components). Incoming<br />

radiation consists <strong>of</strong> direct (beam) and diffuse plus long wave irradiance from <strong>the</strong> sky. Outgoing<br />

radiation consists <strong>of</strong> reflected solar radiation plus <strong>the</strong> terrestroal long-wave components. It consists<br />

60 - junction <strong>the</strong>rmopile with low electrical resistance. The top and bottom surfaces are painted<br />

black and are protected from convective cooling by hemispherial heavy duty polye<strong>the</strong>lene<br />

windshileds.<br />

9. Rainfall<br />

The rainfall is measured by ARG 100 Aerodynamic Tipping Bucket Raingauge (one<br />

sensor). It is a well designed tipping bucket raingauge which combines durable construction<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

with very reasonable cost. The gauge <strong>of</strong>fers less resistance to air flow and helps to reduce <strong>the</strong><br />

sampling errors that inevitably occur during wind - driven rain. This instrument is constructed from<br />

UV - resistant, vaccum - moulded plastic and consists <strong>of</strong> a base and an upper collecting funnel.<br />

The base splits into two parts, <strong>the</strong> inner section supporting <strong>the</strong> tipping - bucket mechanism and<br />

<strong>the</strong> outer providing protection and allowing <strong>the</strong> unit to be bolded firmly to a suitable mounting<br />

plinth or concrete slab. The gauge resolution is 0.2 mm / tip. <strong>the</strong> funnel diameter is 25.5 cms.<br />

10. Micrologger enclosure<br />

All <strong>the</strong> sensors and <strong>the</strong> logging equipment are supported on a sturly tripod and mast. A<br />

fiberglass housing with lock and key provides as excellent environmental protection <strong>for</strong> <strong>the</strong><br />

datalogger and ancillary equipment. Glass fitted nylon water pro<strong>of</strong> connectors are fitted to <strong>the</strong> base<br />

<strong>of</strong> <strong>the</strong> enclosure and sensors may be removed or replaced with minimum disturbance to <strong>the</strong><br />

wea<strong>the</strong>r station.<br />

C. Recording & data logger programming in automatic wea<strong>the</strong>r station<br />

All <strong>the</strong>se above sensors have been hooked into <strong>the</strong> 21X Micrologger (Datalogger) which<br />

runs through a chargeable battery charged with Solarex Solar Panels. In order to record <strong>the</strong><br />

output <strong>of</strong> <strong>the</strong>se sensors, a datalogger programme has been prepared in <strong>the</strong> Computer depending<br />

upon <strong>the</strong> number <strong>of</strong> <strong>the</strong> sensors attached with different channels in <strong>the</strong> datalogger and also <strong>the</strong><br />

frequency and time <strong>of</strong> observations. This has been done with <strong>the</strong> help <strong>of</strong> micro -programmes<br />

developed in <strong>the</strong> Computer, and <strong>the</strong> output is converted into <strong>the</strong> desired units <strong>for</strong> each wea<strong>the</strong>r<br />

variable. Each variable is sensed after each minute and an integrated value over a period <strong>of</strong> five<br />

minutes is calculated. Twelves such values <strong>of</strong> each data point is totalled or averaged over a<br />

period <strong>of</strong> say one hour and is stored in <strong>the</strong> memory <strong>of</strong> <strong>the</strong> datalogger at an appropriate<br />

location at each hour <strong>of</strong> <strong>the</strong> day. The data is also averaged or totalled from each day called Julian<br />

day (i.e. <strong>the</strong> day <strong>of</strong> a year from Ist January) from <strong>the</strong> date <strong>of</strong> planting / sowing <strong>of</strong> <strong>the</strong> crop in <strong>the</strong><br />

field. In <strong>the</strong> present study <strong>the</strong> recording <strong>of</strong> micrometeorological wea<strong>the</strong>r variables by AWS were<br />

started one month be<strong>for</strong>e <strong>the</strong> first sowing <strong>of</strong> potato crop and continued till <strong>the</strong> end <strong>of</strong> <strong>the</strong> Potato<br />

crop season. The crop var. Kufri Bahar which is sensitive to Late Blight <strong>of</strong> Potato was planted on<br />

25 - 10 – 2012. The observations on micro-meteorological variables in crop field since October 01,<br />

2012 and will continue till harvesting <strong>of</strong> crop <strong>of</strong> all planting dates depending upon <strong>the</strong> maturity <strong>of</strong><br />

crop in March 2013. The incidence <strong>of</strong> Late Blight <strong>of</strong> Potato is monitored on day by day basis and<br />

will continue till maturity <strong>of</strong> crop in all plots. The recording <strong>of</strong> micro- meteorological data<br />

observations is also continuing till date. The current data <strong>of</strong> this hour can be noted on <strong>the</strong> provided<br />

sheet. At a time, <strong>the</strong> micro-meteorological data <strong>of</strong> last 40 days can stored in this datalogger and it<br />

can be seen on hourly basis on liquid crystal display (LCD) <strong>of</strong> <strong>the</strong> datalogger.<br />

From this data logger each week <strong>the</strong> micro-meteorological data thus stored in its memory<br />

is transferred into <strong>the</strong> SM 192 Storage Module by connecting it to <strong>the</strong> 9 - pin serial I / O port. This<br />

Storage Module is taken to <strong>the</strong> laboratory and connected to <strong>the</strong> Computer. From SM -192 using<br />

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(<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens)<br />

SC – 532, 9 - pin Peripheral to RS - 232 interface, <strong>the</strong> data is <strong>the</strong>n transferred into <strong>the</strong> Computer<br />

in ASCII <strong>for</strong>m using SMCOM programmes developed <strong>for</strong> this purpose in <strong>the</strong> <strong>for</strong>m <strong>of</strong> a Computer<br />

file. From this file <strong>the</strong> data is <strong>the</strong>n splitted into <strong>the</strong> hourly as well as into daily values using splitting<br />

programmes like SPLIT 03. PAR and SPLIT 04. PAR, respectively, which have also been<br />

development on Computer. The data will <strong>the</strong>n be used <strong>for</strong> identification <strong>of</strong> micro-meteorological<br />

wea<strong>the</strong>r conditions conducive <strong>for</strong> <strong>the</strong> occurrence <strong>of</strong> late blight <strong>of</strong> potato during <strong>the</strong> 2009-10<br />

season.<br />

Data sheet <strong>for</strong> recording <strong>of</strong> current observations <strong>of</strong> micro-meteorological variables in <strong>the</strong><br />

potato field AT CRC using automatic wea<strong>the</strong>r station<br />

The current micro-meteorological wea<strong>the</strong>r variables are being recorded by Automatic<br />

Wea<strong>the</strong>r Station (AWS) in <strong>the</strong> field from 01-10-2012 and <strong>the</strong> date <strong>of</strong> planting <strong>of</strong> Potato crop var.<br />

Kufri Bahar in plot is 25-10-2012 during this Rabi season <strong>of</strong> 2012 - 13 at Crop Research Centre <strong>of</strong><br />

<strong>the</strong> University. The current data can be read on Liquid Crystal Display (LCD) <strong>of</strong> <strong>the</strong> Datalogger <strong>of</strong><br />

<strong>the</strong> AWS in <strong>the</strong> table given below in <strong>the</strong> specific sequence <strong>of</strong> attached sensors:<br />

1. Name <strong>of</strong> <strong>the</strong> crop : Potato 2. Date <strong>of</strong> Ist planting <strong>of</strong> crop : 25-10-2012<br />

3. Stage <strong>of</strong> <strong>the</strong> crop : Tuber Formation 4. Julian day : 40<br />

5. Date <strong>of</strong> observation : 09-02-2013 6. Time <strong>of</strong> observation : 1600 hrs<br />

-----------------------------------------------------------------------------------------------------------------------------------<br />

S.No. LOCATION NO. WEATHER VARIABLE HEIGHT UNITS<br />

----------------------------------------------------------------------------------------------------------------------------------<br />

1. 1 Relative Humidity 1 3m %<br />

2. 2 Air Temperature 1 3m<br />

3. 3 Relative Humidity 2 crop %<br />

4. 4 Air Temperature 2 crop<br />

5. 5 Net Radiation crop W m -2<br />

6. 6 Solar Radiation 3m W m -2<br />

7. 7 <strong>Soil</strong> Temperature 1 10 cm depth<br />

8. 8 <strong>Soil</strong> Temperature 2 20 cm depth<br />

9. 9 Leaf Wetness crop %<br />

10. 10 Wind Direction 3m Degrees<br />

11. 11 Wind Speed 1 3m m s -1<br />

12. 12 Wind Speed 2 crop m s -1<br />

13. 13 Rainfall crop mm<br />

14. 14 Leaf Temperature 1 crop<br />

15. 15 Leaf Temperature 2 crop<br />

o C<br />

o C<br />

o C<br />

o C<br />

o C<br />

o C<br />

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ANNEXURE-I<br />

CENTRE OF ADVANCED FACULTY TRAINING IN PLANT PATHOLOGY<br />

College <strong>of</strong> Agriculture, Pantnagar-263 145 (Uttarakhand)<br />

Following committees have been constituted <strong>for</strong> smooth conduct <strong>of</strong> <strong>the</strong> training programme on<br />

“<strong>Managing</strong> <strong>Plant</strong> <strong>Microbe</strong> <strong>Interactions</strong> <strong>for</strong> <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong>-borne <strong>Plant</strong> Pathogens”<br />

scheduled on January 22 to February 11, 2013.<br />

1. Overall Supervision<br />

Dr. K. Vishunavat, Director CAFTPP<br />

Dr. Yogendra Singh, Course Coordinator<br />

Dr. R.P. Singh, Co-course Coordinator<br />

Dr. R.P. Awasthi<br />

Dr. V.S. Pundhir<br />

Dr. K.S. Dubey<br />

3. Inaugural Session, Intersession Tea and<br />

valedictory function Committee<br />

Dr. K.P.S. Kushwaha – Chairman<br />

Dr. Bijendra Kumar<br />

Mr. S. P. Yadav<br />

5. Transport and Reception Committee<br />

Dr. Pradeep Kumar – Chairman<br />

Dr. S.K. Mishra<br />

Mr. B.C. Sharma<br />

7. Registration Committee<br />

Dr. K.P. Singh – Chairman<br />

Dr. (Mrs.) Deepshikha<br />

Dr. (Mrs.) Renu Singh<br />

9. Audiovisual Aid & Publicity Committee<br />

Dr. R.K. Sahu-Chairman<br />

Dr. Geeta Sharma<br />

Mr. Ajit Kumar<br />

2. Invitation, Inaugural and Closing<br />

Function Committee<br />

Dr. H.S. Tripathi– Chairman<br />

Dr. A.K. Tewari<br />

Mr. S.P. Yadav<br />

Mr. Mehboob<br />

4. Budget Committee<br />

Dr. R. P. Awasthi – Chairman<br />

Dr. Vishwanath<br />

Mr. O.P. Varshney (A.O.)<br />

Mr. A. B. Joshi<br />

Mr. Praveen Kumar<br />

Mr. Prakash Joshi<br />

6. Boarding & Lodging Committee<br />

Dr. V.S. Pundhir – Chairman<br />

Dr. R.P. Singh<br />

Dr. Mohan Singh<br />

Mr. Vikram Prasad<br />

8. Field / Excursion Trip Committee<br />

Dr. K.S. Dubey– Chairman<br />

Dr. Vishwanath<br />

Dr. Satya Kumar<br />

10. Committee <strong>for</strong> typing correspondence<br />

work<br />

Dr. A.K. Tewari, Chairman<br />

Smt. Meena Singh<br />

Mr. Gharbharan Prasad<br />

-i-


ANNEXURE-II<br />

LIST OF PARTICIPANTS<br />

Sl.<br />

No.<br />

Name and Address<br />

Phone/E-mail<br />

1. Shri. Y.M. Rojasara<br />

Assistant Research Scientist<br />

Bidi Tobacco Research Station<br />

Anand Agricultural University<br />

Anand- 388 110 (Gujarat)<br />

2. Dr. B. Anjaneya Reddy<br />

Assistant Pr<strong>of</strong>essor, <strong>Plant</strong> Pathology<br />

College <strong>of</strong> Horticulture, NH-4<br />

Tamaka, Kolar- 563 101 (Karnataka)<br />

3. Dr. K.R. Shreenivasa<br />

Asstt. Pr<strong>of</strong>essor-SMS (<strong>Plant</strong> Pathology)<br />

Krishi Vigyan Kendra, Navile<br />

Shimoga-577 225 (Karnataka)<br />

4. Shri. Umashankar Kumar N.<br />

Assistant Pr<strong>of</strong>essor (<strong>Plant</strong> Pathology)<br />

Krishi Vigyan Kendra<br />

Univ. <strong>of</strong> Agricl. Sciences, Bangalore<br />

Mudigere- 577 132 (Karnataka)<br />

5. Shri. Raghavendra Achari<br />

Assistant Pr<strong>of</strong>essor <strong>of</strong> <strong>Plant</strong> Pathology<br />

Horticulture Research Station<br />

Taluk and District Bijapur<br />

Tidagundi-586 119 (Karnataka)<br />

6. Dr. (Mrs.) K. Karuna<br />

Assistant Pr<strong>of</strong>essor (SS) Pathologist<br />

AICRP (Sunflower)<br />

ZARS, UAS GKVK<br />

Bangalore- 560 065 (Karnataka)<br />

7. Dr. Vijay Bahadur Singh<br />

Assistant Pr<strong>of</strong>essor/Jr. Scientist (Pl. Path.)<br />

Rainfed Research Sub-station <strong>for</strong><br />

Sub-tropical Fruits, Raya<br />

S.K.U.A.S.T-Jammu-180 009 (J&K)<br />

8. Dr. Mohammad Ashraf Ahanger<br />

Assistant Pr<strong>of</strong>essor<br />

Mountain Crop Research Station Sagam<br />

SKUAST-Kashmir, Anantnag- 192231 (J&K)<br />

9. Dr. (Mrs.) V. Bhuvaneswari<br />

Scientist (<strong>Plant</strong> Pathology)<br />

Andhra Pradesh Rice Research Institute &<br />

Regional Agricultural Research Station<br />

Maruteru- 534 122 (AP)<br />

(O): 02692-262061<br />

(Mb.): 09429159782<br />

E-mail: yogeshrojasara@gmail.com<br />

(O): 08152-243208<br />

(Mb.): 09844188834<br />

E-mail: arb_agri@yahoo.co.in<br />

(Mb.): 07259345526<br />

E-mail: shreenikr@rediffmail.com<br />

(O): 08263-228198<br />

(Mb.): 09739337172<br />

E-mail: umapathologist@gmail.com<br />

(O): 08352-235000, 235002<br />

(Mb.): 09448876730<br />

E-mail: achari_r@rediffmail.com<br />

raghavendra.achari@uhsbagalkot.edu.cin<br />

ars_tidagundi@rediffmail.com<br />

(O): 080-2330153<br />

(R): 080-23466136<br />

(Mb.): 9901513044<br />

E-mail: kavlikaruna@yahoo.co.in<br />

csl_narayan2003@yahoo.com<br />

(O): 09469211285<br />

(R): 09419274324<br />

(Mb.): 09797559776<br />

E-mail: vbsinghkhb@gmail.com<br />

(O): 01931238246<br />

(Mb.): 07298590079<br />

E-mail: agsamina@yahoo.com<br />

(O): 08819-246283, 214273<br />

(Mb.): 9441915094<br />

E-mail: bhuvanavk2001@gmail.com<br />

-i-


10. Dr. L. Rajendran<br />

Assistant Pr<strong>of</strong>essor (<strong>Plant</strong> Pathology)<br />

Horticulture Research Station<br />

Vijayanagaram, TNAU,Ooty-643001(TN)<br />

11. Dr. V. Sendhilvel<br />

Assistant Pr<strong>of</strong>essor (<strong>Plant</strong> Pathology)<br />

Krishi Vigyan Kendra<br />

Tamil Nadu Agricultural Univerity<br />

Virinjipuram (TN)<br />

12. Dr. R.C. Shakywar<br />

Asstt. Pr<strong>of</strong>. (Pl. Path. & Microbiology)<br />

Department <strong>of</strong> <strong>Plant</strong> Protection<br />

College <strong>of</strong> Horticulture & Forestry<br />

Central Agricultural University<br />

Pasighat- 791 102 (Arunachal Pradesh)<br />

13. Dr. Yogesh Vitthalrao Ingle<br />

Assistant Pr<strong>of</strong>essor <strong>of</strong> <strong>Plant</strong> Pathology<br />

Regional Research Centre, Amravati<br />

(Dr. PDKV, Akola), Amravati- 444 603 (MS)<br />

14. Dr. Shlokeshwar Raj Sharma<br />

I/C Programme Coordinator SMS (Pl Prot.)<br />

Krishi Vigyan Kendra<br />

J.N. Krishi Vishwa Vidyalaya, Jabalpur<br />

Piproud-Katni-483 442 (MP)<br />

15. Dr. Virendra Singh<br />

SMS/Asstt Pr<strong>of</strong>. (<strong>Plant</strong> Protection)<br />

Krishi Vigyan Kendra<br />

SVPUAT Cotton Research Farm<br />

D.M. Road, Bulandshahar (UP)<br />

16. Dr. Ram Suman Mishra<br />

Assistant Pr<strong>of</strong>essor (<strong>Plant</strong> Pathology)<br />

Department <strong>of</strong> Vegetable Science<br />

N.D.U.A&T., Kumarganj<br />

Faizabad- 224 229 (UP)<br />

17. Dr. Phool Chand<br />

Jr. Scientist-cum-Assistant Pr<strong>of</strong>essor<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology<br />

Tirhut College <strong>of</strong> Agriculture<br />

(Rajendra Agricultural University)<br />

Dholi, Muzaffarpur- 843 121 (Bihar)<br />

18. Dr. Amar Singh<br />

Assistant Scientist (<strong>Plant</strong> Pathology)<br />

CSKHP Krishi Vishvavidyalaya<br />

Palampur- 176 062 (HP)<br />

19. Dr. Chandrashekara C.<br />

Scientist (<strong>Plant</strong> Pathology)<br />

VPKAS, (ICAR), Almora-263 601 (UK)<br />

(Mb.): 09865804560<br />

E-mail: rucklingraja@rediffmail.com<br />

(O): 04147-250001<br />

(Mb.): 09786730806<br />

E-mail: veltnau@rediffmail.com<br />

(O): 0368-2224887<br />

(Mb.): 09402477033<br />

E-mail: rcshakywar@gmail.com<br />

(O): 0721-2663076<br />

(Mb.): 09422766437<br />

E-mail: yog_ingle@rediffmail.com<br />

(O): 07622-268515<br />

(R): 07622-268515<br />

(Mb.): 09977244254<br />

E-mail: srsharma_srsgkp@rediffmail.com<br />

(Mb.): 09456841516<br />

9411477003<br />

E-mail: virendrdr@gmail.com<br />

(Mb.): 09450045737<br />

E-mail: drramsumanmishra@gmail.com<br />

(O): 0621-2293227<br />

(Mb.): 9661450698<br />

E-mail: phoolchand1964@gmail.com<br />

(O): 01894-230326<br />

(Mb.): 9418149782<br />

E-mail: singhamar008@gmail.com<br />

(O): 05962-230060<br />

(Mb.): 9557935569<br />

E-mail: chandrupath@gmail.com<br />

-ii-


20. Dr. Rajesh Kumar<br />

Assistant Pr<strong>of</strong>essor<br />

Department <strong>of</strong> Horticulture<br />

G.B.P.U.A.&T., Pantnagar- 263 145 (UK)<br />

21. Dr. Shilpi Rawat<br />

SMS (<strong>Plant</strong> Protection)<br />

Officer In-charge, KVK<br />

VCSG College <strong>of</strong> Horticulture<br />

UUHF, Bharsar-234 123 (UK)<br />

22. Dr. Mukesh Kumar Karnwal<br />

Asstt. Seed Scientist/JRO<br />

Deptt. <strong>of</strong> Genetics and <strong>Plant</strong> Breeding<br />

G.B.P.U.A.&T., Pantnagar- 263 145 (UK)<br />

23. Dr. Shailesh Tripathi<br />

Assistant Pr<strong>of</strong>essor<br />

Department <strong>of</strong> Horticulture<br />

G.B.P.U.A.&T., Pantnagar- 263 145 (UK)<br />

24. Dr. Ashwani Tapwal<br />

Scientist-D, Forest Pathology Division<br />

Forest Research Institute (FRI)<br />

Dehradun- 248 006 (UK)<br />

25. Dr. L.B. Yadav<br />

Assistant Pr<strong>of</strong>essor<br />

Department <strong>of</strong> <strong>Plant</strong> Pathology<br />

G.B.P.U.A.&T., Pantnagar- 263 145 (UK)<br />

(O): 05944-233145<br />

(Mb.): 9415574127<br />

E-mail: rkshukla2006@gmail.com<br />

(O): 01348-226076<br />

(Mb.): 8216360611<br />

E-mail: rawat_shilpi2004@yahoo.com<br />

(Mb.): 9410188039<br />

E-mail: karan.mk23@gmail.com<br />

(O): 05944-233114<br />

(R): 05944-234108<br />

(Mb.): 9412970450<br />

E-mail: shaileshgbpuat@gmail.com<br />

(O): 0135-2224259<br />

(R): 09411141370<br />

(Mb.): 09411141370<br />

E-mail: ashwanitapwal@gmail.com<br />

tapwala@icfre.org<br />

(R): 05944-233211<br />

(Mb.): 9456345392<br />

E-mail: yadav_lalbahadur@yahoo.co.in<br />

S U M M A R Y<br />

Sl. No. State No. <strong>of</strong> participants<br />

1 Andhra Pradesh 01<br />

2 Arunachal Pradesh 01<br />

3 Bihar 01<br />

4 Gujarat 01<br />

5 Himachal Pradesh 01<br />

6 Jammu & Kashmir 02<br />

7 Karnataka 05<br />

8 Madhya Pradesh 01<br />

9 Maharashtra 01<br />

10 Tamil Nadu 02<br />

11 Uttar Pradesh 02<br />

12 Uttarakhand 07<br />

Total Participants 25<br />

-iii-


TRAINING<br />

ON<br />

ANNEXURE-III<br />

“MANAGING PLANT MICROBE INTERACTIONS FOR THE MANAGEMENT OF SOIL-BORNE<br />

PLANT PATHOGENS”<br />

(January 22 to February 11, 2013)<br />

Venue<br />

Sponsored by<br />

CAFT Hall, <strong>Plant</strong> Pathology<br />

Centre <strong>of</strong> Advance Faculty Training in <strong>Plant</strong> Pathology (ICAR, New Delhi)<br />

GUEST SPEAKERS/CONTRIBUTORS<br />

Dr. Serge Savary<br />

Dr. L. Willocquet<br />

Dr. U.S. Singh<br />

Dr. R.K. Khetarpal<br />

Dr. Rakesh Pandey<br />

Dr. Y.P. Singh<br />

Director <strong>of</strong> Research, Phytopathologist, INRA, France<br />

In-charge <strong>of</strong> Research, Phytopathologist, INRA, France<br />

Coordinator, South Asia, Bill & Melinda Gates Foundation<br />

(BMGF) Proj., International Rice Research Institute, New Delhi<br />

Science Director (Asia) and Country Director (India), CABI South<br />

Asia-India, 2nd Floor, CG Block, NASC Complex, DP Shastri<br />

Marg, Opp. Todapur Village,PUSA, New Delhi<br />

Scientist, Central Institute <strong>of</strong> Medicinal &Aromatic <strong>Plant</strong>s,<br />

CIMAP), Near Kukrail Picnic Spot, Lucknow- 226 015 (UP)<br />

Principal Scientist, Forest Pathology Division, Forest Research<br />

Institute, Dehradun<br />

LOCAL SPEAKERS<br />

Dr. J. Kumar<br />

Dr. K. Vishunavat<br />

Dr. H.S. Tripathi<br />

Dr. R.P. Awasthi<br />

Dr. V.S. Pundhir<br />

Dr. Pradeep Kumar<br />

Dr. K.P. Singh<br />

Dr. Vishwanath<br />

Dr. Y. Singh<br />

Dr. R.P. Singh<br />

Dr. K.P.S. Kushwaha<br />

Dr. A.K. Tewari<br />

Dean, College <strong>of</strong> Agriculture<br />

Pr<strong>of</strong>essor and Head-cum-Director CAFT <strong>Plant</strong> Pathology<br />

Ex-Pr<strong>of</strong>essor, <strong>Plant</strong> Pathology<br />

Pr<strong>of</strong>essor, <strong>Plant</strong> Pathology<br />

Pr<strong>of</strong>essor, <strong>Plant</strong> Pathology<br />

Pr<strong>of</strong>essor, <strong>Plant</strong> Pathology<br />

Pr<strong>of</strong>essor, <strong>Plant</strong> Pathology<br />

Assoc. Pr<strong>of</strong>., <strong>Plant</strong> Pathology<br />

SRO, <strong>Plant</strong> Pathology<br />

SRO, <strong>Plant</strong> Pathology<br />

SRO, <strong>Plant</strong> Pathology<br />

SRO, <strong>Plant</strong> Pathology<br />

-i-


Dr. Roopali Sharma<br />

Dr. Geeta Sharma<br />

Dr. S.K. Mishra<br />

Dr. Ramesh Chandra<br />

Dr. K.P. Raverkar<br />

Dr. Navneet Pareek<br />

Dr. P.C. Srivastava<br />

Dr. M.A. Khan<br />

Dr. S.N. Tewari<br />

Dr. R.P. Srivastava<br />

Dr. D.K. Singh<br />

Dr. H.S. Chawla<br />

Dr. P.K. Shrotria<br />

Dr. H.S. Kushwaha<br />

Dr. A.S. Nain<br />

Dr. Reeta Goel<br />

Dr. Anita Sharma<br />

Dr. Laxmi Tewari<br />

Dr. Anil Kumar Gupta<br />

Dr. Anil Sharma<br />

Dr. Balwinder Singh<br />

Dr. R.N. Pateriya<br />

JRO, <strong>Plant</strong> Pathology<br />

JRO, <strong>Plant</strong> Pathology<br />

JRO, <strong>Plant</strong> Pathology<br />

Pr<strong>of</strong>esor & Head, <strong>Soil</strong> Science<br />

Associate Pr<strong>of</strong>essor, <strong>Soil</strong> Science<br />

Associate Pr<strong>of</strong>essor, <strong>Soil</strong> Science<br />

Pr<strong>of</strong>essor, <strong>Soil</strong> Science<br />

Pr<strong>of</strong>essor, Entomology<br />

Pr<strong>of</strong>essor, Entomology<br />

Pr<strong>of</strong>essor, Entomology<br />

Associate Pr<strong>of</strong>essor, Agronomy<br />

Pr<strong>of</strong>. & Head, Genetics and <strong>Plant</strong> Breeding<br />

Pr<strong>of</strong>essor, Genetics and <strong>Plant</strong> Breeding<br />

Pr<strong>of</strong>essor, Agrometerology<br />

Assoc. Pr<strong>of</strong>., Agrometerology<br />

Pr<strong>of</strong>. & Head, Microbiology<br />

Assoc. Pr<strong>of</strong>., Microbiology<br />

Assoc. Pr<strong>of</strong>., Microbiology<br />

Pr<strong>of</strong>. & Head, MBGE<br />

Assoc. Pr<strong>of</strong>., Biological Sciences<br />

Assoc. Pr<strong>of</strong>., Anatomy<br />

Assoc. Pr<strong>of</strong>essor, Farm Machinery<br />

-ii-


ANNEXURE-IV<br />

CENTRE OF ADVANCED FACULTY TRAINING IN PLANT PATHOLOGY<br />

G.B. Pant University <strong>of</strong> Agric. & Tech., Pantnagar-263 145 (UK)<br />

Course Schedule (January 22 to February 11, 2013)<br />

“MANAGING PLANT MICROBE INTERACTIONS FOR THE MANAGEMENT OF SOIL-BORNE<br />

Venue<br />

PLANT PATHOGENS”<br />

: CAFT Hall, Department <strong>of</strong> <strong>Plant</strong> Pathology<br />

Day & Date Time Topic <strong>of</strong> Lecture Name & Designation<br />

<strong>of</strong> Speaker<br />

Tuesday<br />

22.1.13<br />

09:00-09:30 hrs Registration<br />

Venue: CAFT Hall, <strong>Plant</strong> Pathology<br />

Registration<br />

Committee<br />

09:30-10:00 hrs Introduction with <strong>Plant</strong> Pathology Faculty<br />

Venue: CAFT Hall, <strong>Plant</strong> Pathology<br />

Faculty, <strong>Plant</strong><br />

Pathology<br />

10:00-11:00 hrs Inaugural Function<br />

Wednesday<br />

23.1.13<br />

Thursday<br />

24.1.13<br />

Friday<br />

25.1.13<br />

11:00-11:15 hrs Tea break<br />

Venue: Conference Hall, Agriculture College<br />

11:15-12:45 hrs Visit to laboratories <strong>of</strong> Department <strong>of</strong> <strong>Plant</strong><br />

Pathology<br />

12:45-14:30 hrs Lunch<br />

Dr. Y. Singh<br />

14:30-17:00 hrs Visit to University Research Centers Drs. P. Kumar &<br />

Vishwanath<br />

09:30-10:30 hrs College <strong>of</strong> Agriculture at a Glance Dr. J. Kumar, Dean<br />

Ag.<br />

10:30-11:30 hrs IPM is <strong>the</strong> solution. But what is <strong>the</strong> problem? Dr. Serge Savary,<br />

France<br />

11:30-11:45 hrs Tea break<br />

11:45-13:00 hrs A new on-line simulation course on plant disease<br />

epidemiology<br />

13:00-14:30 hrs Lunch<br />

14:30-15:30 hrs Department <strong>of</strong> <strong>Plant</strong> Pathology and CAFT<br />

activities at Pantnagar<br />

15:30-15:45 hrs Tea break<br />

Dr. L. Willocquet,<br />

France<br />

Dr. K. Vishunawat,<br />

Director, CAFT<br />

15:45-17:00 hrs Interactive session with Participants & Students Dr. L. Willocquet,<br />

France<br />

09:30-10:30 hrs <strong>Soil</strong> degradation- a threat to sustainable Dr. Ramesh Chandra<br />

agriculture<br />

10:30-11:30 hrs Role <strong>of</strong> IPM in management <strong>of</strong> soil borne<br />

diseases<br />

11:30-11:45 hrs Tea break<br />

Dr. Serge Savary,<br />

France<br />

11:45-13:00 hrs Discussion with participants Dr. Serge Savary,<br />

France<br />

13:00-14:30 hrs Lunch<br />

14:30-17:00 hrs Isolation, identification and quantification <strong>of</strong><br />

Trichoderma (Practical)<br />

09:30-10:45 hrs Biodeterioration <strong>of</strong> seeds and its control by<br />

microbial antagonists<br />

10:45-11:00 hrs Tea Break<br />

11:00-12:30 hrs Role <strong>of</strong> organic amendments in <strong>the</strong> management<br />

<strong>of</strong> soil borne plant pathogens<br />

Dr. Roopali Sharma<br />

Dr. K. Vishunavat<br />

Dr. R.P. Singh<br />

-i-


Saturday<br />

26.1.13<br />

Sunday<br />

27.1.13<br />

Monday<br />

28.1.13<br />

Tuesday<br />

29.1.13<br />

Wednesday<br />

30.1.13<br />

Thursday<br />

31.1.13<br />

Friday<br />

1.2.13<br />

12:30-14:30 hrs Lunch Break<br />

14:30-17:00 hrs TA settlement Drs. R.P. Awasthi &<br />

Vishwanath<br />

09:30-11:30 hrs Independence day programme at Gandhi Hall<br />

Visit to University library<br />

09:30-10:30 hrs Biological control <strong>of</strong> plant pathogens under<br />

sustainable agriculture: status and prospects<br />

10:30-11:30 hrs Influence <strong>of</strong> environmental parameters on<br />

Trichoderma strains with biocontrol potentials<br />

11:30-11:45 hrs Tea break<br />

Dr. J. Kumar<br />

Dr. A. K.Tewari<br />

11:45-13:00 hrs <strong>Soil</strong> solarization <strong>for</strong> biocontrol <strong>of</strong> plant pathogens Dr. Yogendra Singh<br />

13:00-14:30 hrs Lunch<br />

14:30-17:00 hrs Visit to Biocontrol Lab & Mechanism <strong>of</strong><br />

mycoparasitism and antibiosis (Practical)<br />

Dr. Roopali Sharma<br />

and Smita Puri<br />

09:30-10:30 hrs Suppressive soils in plant disease management Dr. K.P. Singh<br />

10:30-11:30 hrs Protected cultivation: Problems and Perspectives Dr. H.S. Tripathi<br />

11:30-11:45 hrs Tea break<br />

11:45-13:00 hrs Visit to MRTC Drs. S.K.<br />

Mishra/Geeta Sharma<br />

13:00-14:30 hrs Lunch break<br />

14:30-17:00 hrs Visit to KNSCCF Dr. S.K. Mishra<br />

09:30-10:30 hrs Case studies: successes and problems<br />

encountered<br />

Dr. J. Kumar<br />

10:30-11:30 hrs <strong>Soil</strong> fertility in organic farming system Dr. D.K. Singh<br />

11:30-11:45 hrs Tea break<br />

11:45-13:00 hrs <strong>Interactions</strong> <strong>of</strong> microbes in <strong>the</strong> phyllosphere and<br />

rhizosphere<br />

13:00-14:30 hrs Lunch break<br />

14:30-15:45 hrs Mass production and <strong>for</strong>mulation technology <strong>of</strong><br />

Trichoderma (Practical)<br />

15:45-16:00 hrs Tea break<br />

16:00-17:00 hrs Identification <strong>of</strong> Pseudomonas and Bacillus<br />

isolates using Biolog system (Practical)<br />

09:30-10:30 hrs Role <strong>of</strong> entomopathogens in management <strong>of</strong><br />

insect pests<br />

10:30-11:30 hrs Characterization <strong>of</strong> micro-meterological variables<br />

<strong>for</strong> disease management<br />

11:30-11:45 hrs Tea break<br />

Dr. P.C. Srivastava<br />

Drs. A.K. Tewari<br />

/Roopali Sharma<br />

Drs. J. Kumar &<br />

Roopali Sharma<br />

Dr. S.N.Tewari<br />

Dr. H.S. Kushwaha<br />

11:45-13:00 hrs Role <strong>of</strong> soil micro-fauna in maintaining soil health Dr. Navneet Pareek<br />

13:00-14:30 hrs Lunch break<br />

14:30-15:30 hrs Induced resistance in plants <strong>for</strong> managing plant<br />

diseases<br />

15:30-15:45 hrs Tea break<br />

15:45-17:00 hrs Isolation and identification <strong>of</strong> entomophagous<br />

fungi (Practical)<br />

Dr. P.K. Shrotria<br />

Dr. C.P. Singh<br />

09:30-10:30 hrs Biological management <strong>of</strong> seed borne pathogens Dr. K. Vishunavat<br />

10:30-11:30 hrs <strong>Microbe</strong>s and intellectual property right (IPR) Dr H.S. Chawla<br />

11:30-11:45 hrs Tea break<br />

-ii-


Saturday<br />

2.2.13<br />

Sunday<br />

3.2.13<br />

Monday<br />

4.2.13<br />

Tuesday<br />

5.2.13<br />

Wednesday<br />

6.2.13<br />

Thursday<br />

7.2.13<br />

11:45-13:00 hrs Biocontrol and integrated disease management in<br />

different environments<br />

13:00-14:30 hrs Lunch break<br />

14:30-15:30 hrs Role <strong>of</strong> plant growth promoting rhizobacteria in<br />

crop improvement<br />

15:30-15:45 hrs Tea break<br />

Dr. V.S. Pundhir<br />

Dr. Anita Sharma<br />

15:45-17:00 hrs Microbial degradation <strong>of</strong> pesticides Dr. Anita Sharma<br />

09:30-10:30 hrs Development <strong>of</strong> lower cost production storage and<br />

distribution systems <strong>of</strong> beneficial microbes<br />

10:30-11:30 hrs Biocontrol <strong>of</strong> fungal phytopathogens by<br />

Trichoderma spp.<br />

11:30-11:45 hrs Tea break<br />

11:45-13:00 hrs Evaluation and Selection <strong>of</strong> Promising<br />

Trichoderma Isolates For <strong>the</strong> <strong>Management</strong> <strong>of</strong> <strong>Soil</strong><br />

Borne Fungal <strong>Plant</strong> Pathogens<br />

13:00-14:30 hrs Lunch break<br />

Dr. K.P. Singh<br />

Dr. Laxmi Tewari<br />

Dr. A.K. Tewari<br />

14:30-17:00 hrs Identification <strong>of</strong> Bacteria (Practical) Dr. Yogendra Singh<br />

10:00-11:00 hrs Integration <strong>of</strong> microbials and sustainable tools<br />

(compost, organic manures, bi<strong>of</strong>umigation, crop<br />

rotation) <strong>for</strong> ec<strong>of</strong>riendly plant disease<br />

management<br />

11:00-11-15 hrs Tea break<br />

Dr. J. Kumar<br />

11:15-12:30 hrs Writing <strong>of</strong> Research Papers/Scientific reports Dr. J. Kumar<br />

12:30-14:30 hrs Lunch break<br />

14:30-17:00 hrs Visit to university library<br />

09:30-10:30 hrs Exploiting nematophagous fungi <strong>for</strong> <strong>the</strong><br />

management <strong>of</strong> root knot nematodes<br />

10:30-11:30 hrs Role <strong>of</strong> microbes in management <strong>of</strong> <strong>for</strong>est<br />

diseases<br />

11:30-11:45 hrs Tea break<br />

Dr. Rakesh Pandey,<br />

CIMAP<br />

Dr. Y.P.Singh, FRI,<br />

Dehradun<br />

11:45-13:00 hrs <strong>Management</strong> <strong>of</strong> root knot nematodes Dr. Rakesh Pandey,<br />

CIMAP<br />

13:00-14:30 hrs Lunch break<br />

14:30-15:30 hrs Implication <strong>of</strong> PGPR <strong>for</strong> Rhizosphere colonization<br />

and plant growth promotion<br />

15:30-15:45 hrs Tea break<br />

Dr. Reeta Goel<br />

15:45-17:00 hrs <strong>Soil</strong> DNA extraction and its implication (Practical) Dr. Reeta Goel<br />

Visit to Research station, Majhera (Nainital)<br />

09:30-10:30 hrs Trichoderma as inducer <strong>of</strong> plant resistance to<br />

diseases<br />

10:30-11:30 hrs Reduced risk pesticides: safe and powerful tool<br />

<strong>for</strong> effective pest control<br />

11:30-11:45 hrs Tea break<br />

11:45-13:00 hrs Disease resistance in plants through mychorrhizal<br />

fungi induced allelochemicals<br />

13:00-14:30 hrs Lunch break<br />

14:30-17:00 hrs Isolation and identification <strong>of</strong> mychorrhizal fungi<br />

(Practical)<br />

09:30-10:30 hrs Molecular mechanism associated with fungal<br />

pathogenesis and diseases resistance to Karnal<br />

bunt <strong>of</strong> wheat<br />

Drs. Pradeep Kumar &<br />

Vishwanath<br />

Dr. R.P. Singh<br />

Dr. S.N. Tewari<br />

Dr. Anil Sharma<br />

Dr. Anil Sharma<br />

Dr Anil Kumar Gupta<br />

-iii-


Friday<br />

8.2.13<br />

Saturday<br />

9.2.13<br />

Sunday<br />

10.2.13<br />

Monday<br />

11.2.13<br />

10:30-11:30 hrs Remote sensing and GIS <strong>for</strong> stress management<br />

in plants<br />

11:30-11:45 hrs Tea break<br />

11:45-13:00 hrs The role <strong>of</strong> biocontrol methods in integrated crop<br />

protection<br />

13:00-14:30 hrs Lunch<br />

Dr. A.S. Nain<br />

Dr. M.A. Khan<br />

14:30-15:30 hrs <strong>Microbe</strong>s and soil quality Dr. K.P. Raverkar<br />

15:30-15:45 hrs Tea break<br />

15:45-17:00 hrs Production technology <strong>of</strong> bi<strong>of</strong>ertilizers (Practical) Dr. K.P. Raverkar<br />

09:30-10:30 hrs Smut fungi: potential pathogen & biocontrol agent Dr. K. Vishunavat<br />

10:30-11:30 hrs Importance <strong>of</strong> bio-energy <strong>for</strong> sustainable<br />

agriculture<br />

11:30-11:45 hrs Tea break<br />

11:45-13:00 hrs Identification <strong>of</strong> Trichoderma spp. using<br />

molecular tools (Practical)<br />

13:00-14:30 hrs Lunch break<br />

14:30-17:00 hrs Practical demonstration <strong>of</strong> scanning electron<br />

microscopy (Practical)<br />

Dr. R.N. Pateriya<br />

Dr. Anil Kumar Gupta<br />

Dr. Balwinder Singh<br />

09:30-10:30 hrs Pesticides: Past, Present and Future Dr. R.P. Srivastava<br />

10:30-11:30 hrs Presentation by participants<br />

11:30-11:45 hrs Tea break<br />

11:45-12:30 hrs Presentation by participants<br />

12:30-13:00 hrs Evaluation <strong>of</strong> <strong>the</strong> training programme and<br />

feedback from trainees<br />

13:00-14:30 hrs Lunch break<br />

Dr. Yogendra Singh<br />

14:30-15:45 hrs Visit to Meterological observatory at N.E.B. CRC Dr. H.S. Kushwaha<br />

15:45-16:00 hrs Tea break<br />

16:00-17:00 hrs <strong>Management</strong> <strong>of</strong> abiotic stresses in rice Dr. U.S. Singh, IRRI<br />

University Library visit<br />

09:30-10:30 hrs Bio-security and bio-safety issues in relation to<br />

plant pathogenic microbes<br />

10:30-11:30 hrs Presentation by participants<br />

11:30-11:45 hrs Tea break<br />

Dr. R.K. Khetrapal<br />

11:45-13:00 hrs Quarantine <strong>for</strong> <strong>the</strong> management <strong>of</strong> plant diseases Dr. R.K. Khetrapal<br />

13:00-14:30 hrs Lunch break<br />

14:30-15:00 hrs Discussion with <strong>Plant</strong> Pathology Faculty<br />

15:00-16:00 hrs Valedictory Session<br />

-iv-

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