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Research Journal <strong>of</strong> Chemistry and Environment___________________________________Vol.17 (3) March (2013)<br />

Res. J. Chem. Environ.<br />

<strong>Isolation</strong> <strong>of</strong> <strong>Malathion</strong> <strong>degrading</strong> <strong>Pseudomonas</strong><br />

<strong>xanthomarina</strong> <strong>with</strong> plant growth promoting activity<br />

Goyat Pankaj, Bhatia Divya and Malik Deepak Kumar *<br />

Department <strong>of</strong> Biotechnology Engineering, University Institute <strong>of</strong> Engineering and Technology, Kurukshetra University Kurukshetra-136119, INDIA<br />

*deepmolbio@rediffmail.com<br />

Abstract<br />

<strong>Malathion</strong> is an organophosphorus insecticide used<br />

all over the world to control adult mosquitoes. A total<br />

<strong>of</strong> 10 morphologically different bacterial cultures<br />

DKM1, DKM2, DKM3, DKM4, DKM5, DKM6,<br />

DKM7, DKM8, DKM9 and DKM10 were isolated by<br />

using enrichment method. The growth study <strong>of</strong><br />

isolated strains showed that the bacterial strain<br />

(DKM8) was able to grow in minimal medium<br />

containing 0.5 mM <strong>Malathion</strong> as a sole carbon<br />

source. The isolated bacterial strain DKM8 was found<br />

very close to <strong>Pseudomonas</strong> <strong>xanthomarina</strong> on the basis<br />

<strong>of</strong> morphological, physiological and biochemical<br />

characteristics. The resting cell study showed that<br />

strain (DKM8) can degrade <strong>Malathion</strong> 70.5% <strong>with</strong>in<br />

two days. The isolated bacterial strain DKM8 was<br />

also showing plant growth promoting activities (IAA<br />

production, phosphate solubilization, protease activity<br />

and antifungal activity). These data indicate that the<br />

isolated bacterial strain DKM8 can be used for<br />

degradation <strong>of</strong> <strong>Malathion</strong> along <strong>with</strong> plant growth<br />

promoting activity in agriculture.<br />

Keywords: <strong>Malathion</strong>, Indole acetic acid, PGPR, Resting<br />

cell study, GC.<br />

Introduction<br />

<strong>Malathion</strong> (O, O-dimethyl-S (1, 2 dicarbethoxyethyl) dithiophosphate)<br />

is an organophosphate insecticide used<br />

extensively to control adult mosquitoes. Like most<br />

organophosphates, <strong>Malathion</strong> is degraded in soils 27, 45 , in<br />

aquatic systems 24 and in terrestrial plants and animals 13 .<br />

Due to the environmental concerns associated <strong>with</strong><br />

accumulation <strong>of</strong> this pesticide in food products and water<br />

supplies, efforts are currently underway to develop safe,<br />

convenient and economically feasible methods for<br />

pesticides detoxification. Bioremediation takes place in<br />

order to transform the contaminants into substances that<br />

can be absorbed and used by autotrophic organisms <strong>with</strong> no<br />

toxic effect 43 . The microbial interactions are useful, neutral<br />

or harmful and influence plant growth accordingly 1 .<br />

Plant growth-promoting bacteria (PGPB) are rhizosphere<br />

bacteria that can help plant growth by different<br />

mechanisms 14 . The detrimental environmental impact <strong>of</strong><br />

chemical fertilizers and their rising cost, the use <strong>of</strong> PGPB<br />

as natural fertilizers is beneficial for the development <strong>of</strong><br />

sustainable agriculture. PGPR promote plant growth by<br />

(59)<br />

various mechanisms that include: (i) The ability to produce<br />

or change the concentration <strong>of</strong> the plant hormones like<br />

indole acetic acid 42 , gibberelic acid 26 , cytokines 44 and<br />

ethylene 14 (ii) symbiotic nitrogen fixation 16, 17 (iii) asymbiotic<br />

nitrogen fixation 5 (iv) phosphate solubilization 49 (v)<br />

antagonisms against phytopathogenic microorganisms by<br />

the production <strong>of</strong> siderophores 42 , β-1, 3- glucanase 40 ,<br />

chitinase 12 , antibiotics 29 and cyanide 11 .<br />

Material and Methods<br />

Chemicals: The chemicals, media and reagents used in<br />

present studies were <strong>of</strong> AR grade and taken from Hi Media,<br />

CDH and Rankem etc. <strong>Malathion</strong> was purchased from New<br />

Chemi Industries Ltd, India. Analytical and spectroscopic<br />

grade hexane and acetone were purchased from CDH and<br />

Rankem respectively. All other chemicals were <strong>of</strong> AR<br />

grade commercially available.<br />

<strong>Isolation</strong> <strong>of</strong> <strong>Malathion</strong> Degrading Bacterial Culture<br />

from Pesticide Contaminated Soil: The soil sample was<br />

taken from pesticide contaminated field. The enrichment<br />

technology was used for the isolation <strong>of</strong> <strong>Malathion</strong><br />

<strong>degrading</strong> bacterial strains by using basal salt medium<br />

(BSM) <strong>with</strong> the following composition (in g/L) (NH4)2SO4,<br />

1.0; K2HPO4, 0.1; MgSO4, 0.2; FeSO4.7H2O, 0.001; NaCl,<br />

1.0; Na2MoO4, 0.0033 4 . Approximately 10 g <strong>of</strong> soil sample<br />

was suspended in 250 ml basal salt medium supplemented<br />

<strong>with</strong> 0.30 mM <strong>Malathion</strong> and incubated at 30 ºC. After 7<br />

days <strong>of</strong> incubation, 15-20 ml broth culture was used to<br />

inoculate fresh basal salt medium containing 0.35 mM<br />

<strong>Malathion</strong>.<br />

Subsequently three-four rounds <strong>of</strong> enrichment were carried<br />

out in basal salt medium supplemented <strong>with</strong> increasing<br />

concentration <strong>of</strong> <strong>Malathion</strong> up to 0.5 mM. The enriched<br />

medium was spreaded over nutrient agar plates containing<br />

0.5 mM <strong>Malathion</strong>. After 3 days <strong>of</strong> incubation,<br />

morphologically different types <strong>of</strong> colonies were streaked<br />

for their purification on nutrient agar plates containing 0.5<br />

mM <strong>Malathion</strong>. The isolated bacterial cultures were<br />

transferred to fresh slants at regular intervals for further<br />

study.<br />

Identification and Growth Study <strong>of</strong> Isolated Bacterial<br />

Culture: The growth <strong>of</strong> all isolated bacterial strains was<br />

observed by taking absorbance at 600 nm at interval <strong>of</strong> 0, 6,<br />

12, 24, 48, 96, 120 and 168 hr in basal salt media (BSM)<br />

supplemented <strong>with</strong> 0.5 mM malathion. The bacterial strain<br />

DKM8 was identified on the basis <strong>of</strong> their morphological,<br />

physiological and biochemical characteristics from Institute<br />

<strong>of</strong> Microbial Technology (IMTECH), Chandigarh.


Research Journal <strong>of</strong> Chemistry and Environment___________________________________Vol.17 (3) March (2013)<br />

Res. J. Chem. Environ.<br />

IAA Production <strong>of</strong> Isolated Bacterial Cultures: The<br />

indole acetic acid production <strong>of</strong> isolated bacterial strain<br />

was determined by using Salkowski reagent 15 . The 2%<br />

inoculums <strong>of</strong> all the isolated bacterial culture were<br />

transferred individually into 5 ml LB broth supplemented<br />

<strong>with</strong> 100 µg/ml L-tryptophan and incubated at 28 ºC for 4<br />

days. After 2 and 4 days, 2 ml growth suspension was taken<br />

from culture broth and centrifuged for 5 min at 10,000 rpm.<br />

Then equal amount <strong>of</strong> Salkowski reagent (0.5 M FeCl3 in<br />

35 % Perchloric acid) was added in the supernatant. The<br />

supernatant was mixed by shaking and allowed to stand at<br />

room temperature for 30 min till the development <strong>of</strong> pink<br />

color. For quantitative estimation <strong>of</strong> IAA, optical density <strong>of</strong><br />

culture broth was taken at 500 nm. The effect <strong>of</strong> different<br />

concentration <strong>of</strong> <strong>Malathion</strong> (0.5 mM and 1.0 mM) on IAA<br />

production was also checked by using the same method.<br />

Uninoculated broth served as control.<br />

Phosphate Solubilization and Protease Activity <strong>of</strong><br />

Isolated Bacterial Cultures: The phosphate solubilization<br />

activity <strong>of</strong> all isolated bacterial strains was checked by<br />

using Pikovskaya 32 medium. The bacterial cultures were<br />

spot inoculated on Pikovskaya medium containing<br />

tricalcium phosphate [Ca3 (PO4)2] and incubated at 30 ºC<br />

for 10 days. The development <strong>of</strong> a clear zone was<br />

considered as phosphate solubilizing activity. The<br />

phosphate solubilization was also checked by using same<br />

method at different concentration <strong>of</strong> <strong>Malathion</strong> (0.5 mM<br />

and 1.0 mM). The protease activity was checked by using<br />

skimmed milk agar medium 34 . The bacterial strains were<br />

spot inoculated on skimmed milk agar plates and incubated<br />

at 30 ºC for 48 hr to check the proteolytic activity. The<br />

development <strong>of</strong> a clear zone at the inoculation site on the<br />

culture plates was considered as an index <strong>of</strong> proteolytic<br />

activity.<br />

Anti-fungal Activity against Aspergillus sp. and<br />

Antibiotic Resistance Pattern <strong>of</strong> Isolated Bacterial<br />

Cultures: The antagonistic ability <strong>of</strong> isolated bacterial<br />

cultures was determined <strong>with</strong> slight modifications 3 . The<br />

growth suspension <strong>of</strong> Aspergillus was spread on the surface<br />

<strong>of</strong> nutrient agar plates. After the absorption <strong>of</strong> Aspergillus<br />

suspension, bacterial strains were spot inoculated. The<br />

antifungal activity <strong>of</strong> bacterial strains against the<br />

Aspergillus was assessed on the basis <strong>of</strong> inhibition zone<br />

size after 4 days <strong>of</strong> incubation at 30 ºC. The antibiotic<br />

resistant pattern <strong>of</strong> bacterial strains DKM8 and DKM9 was<br />

determined by disc diffusion method. The overnight growth<br />

suspension <strong>of</strong> strains DKM8 and DKM9 was spread over<br />

nutrient agar plate.<br />

After absorption <strong>of</strong> bacterial suspension antibiotic discs<br />

were placed, plates <strong>with</strong>out antibiotic discs were<br />

considered as control. The following antibiotic discs were<br />

tested, chloromphenicol, oxacillin, ampicillin,<br />

clarithromycin, gentamycin, amoxyclav, vancomycin,<br />

cephalothin, amikacin, novobiocin, erythromycin,<br />

teicoplanin, co-trimoxazole, penicillin, azithromycin,<br />

(60)<br />

<strong>of</strong>loxacin, methicillin, linezolid, clindamycin and<br />

tetracycline. The zone <strong>of</strong> inhibition was obsereved after 48<br />

hr <strong>of</strong> incubation at 30 ºC.<br />

Quantitative Analysis <strong>of</strong> <strong>Malathion</strong> Degradation by<br />

Resting Cell Study: On the basis <strong>of</strong> plant growth<br />

promoting activity and growth in BSM medium containing<br />

0.5 mM malathion, bacterial strain DKM8 was selected for<br />

their ability to degrade <strong>Malathion</strong> by resting cell study 23 .<br />

The isolate DKM8 was grown in 300 ml nutrient broth<br />

supplemented <strong>with</strong> 0.5 mM <strong>Malathion</strong> at 30 ºC up to mid<br />

log phase. Cells were harvested at 4 ºC and washed twice<br />

<strong>with</strong> BSM. These cells were resuspended in 50 ml BSM<br />

supplemented <strong>with</strong> 0.5 mM <strong>Malathion</strong>. Aliquots <strong>of</strong> 10 ml<br />

were taken at different time interval <strong>of</strong> 0, 24 and 48 hrs.<br />

Heat killed cells <strong>of</strong> strain DKM8 were used as control.<br />

<strong>Malathion</strong> was extracted for 30 min from cell free<br />

supernatant by using 50 ml hexane in separating funnel<br />

(neutral extraction). After neutral extraction, the pH <strong>of</strong> the<br />

aqueous phase was adjusted to 2.0 <strong>with</strong> 2 N HCl and again<br />

extracted for 30 min <strong>with</strong> 50 ml hexane: acetone (acidic<br />

extraction). The amount <strong>of</strong> <strong>Malathion</strong> at different time was<br />

analyzed by gas chromatography.<br />

Results<br />

<strong>Isolation</strong> and Identification <strong>of</strong> <strong>Malathion</strong> Degrading<br />

Bacteria: A total <strong>of</strong> 10 morphologically different bacterial<br />

cultures (DKM1, DKM2, DKM3, DKM4, DKM5, DKM6,<br />

DKM7, DKM8, DKM9 and DKM10) were isolated by<br />

using enrichment method as shown in table 1. All the<br />

isolated bacterial cultures were showing growth in BSM<br />

media containing 0.5 mM <strong>Malathion</strong>. All the isolated<br />

bacterial cultures were also checked for their plant growth<br />

promoting activity. Out <strong>of</strong> the ten cultures, only one<br />

bacterial strain DKM8 utilized <strong>Malathion</strong> as a sole carbon<br />

and energy source along <strong>with</strong> plant growth promoting<br />

ability (indole acetic acid, phosphate solubilization,<br />

antifungal and protease activity), was selected for further<br />

study.<br />

The morphological, physiological and biochemical features<br />

<strong>of</strong> bacterial strain DKM8 are shown in table 2 and 3. It is a<br />

motile, gram negative, rod shape and catalse and oxidase<br />

positive. It was not growing on Maconkey agar as lactose<br />

fermenting microorganism. This culture can grow at 30 and<br />

37 o C, but was unable to grow at low temperature (4, 10, 15<br />

and 25 o C) and high temperature (42 and 60 o C). It can<br />

grow at different pH (5.0, 8.0 and 10.0) and different<br />

concentrations <strong>of</strong> NaCl (2%, 4%, 5% and 8%). This culture<br />

can utilize citrate as carbon source. The culture DKM8 was<br />

unable to hydrolyze tween 20, tween 40, starch, gelatin,<br />

esculin and urea. This isolate did not produce acid from<br />

sugar lactose. The culture DKM8 was producing acid from<br />

sugar dextrose. On the basis <strong>of</strong> these results the culture<br />

DKM8 was found very closely related to <strong>Pseudomonas</strong><br />

<strong>xanthomarina</strong>.<br />

Growth <strong>of</strong> Isolated Bacterial Strains: On the basis <strong>of</strong>


Research Journal <strong>of</strong> Chemistry and Environment___________________________________Vol.17 (3) March (2013)<br />

Res. J. Chem. Environ.<br />

growth over BSM agar medium containing 0.5 mM<br />

malathion, ten bacterial strains were selected for their<br />

growth in BSM medium containing 0.5 mM malathion, The<br />

growth <strong>of</strong> DKM1, DKM2, DKM3, DKM4, DKM5, DKM6,<br />

DKM7, DKM8, DKM9 and DKM10 is shown in fig. 1.<br />

The growth <strong>of</strong> bacterial culture DKM8 was rapid after 1<br />

day in the presence <strong>of</strong> 0.5 mM <strong>Malathion</strong>, showing<br />

exponential phase <strong>of</strong> growth. After 4 days, the growth <strong>of</strong><br />

DKM8 declined which may be due to unavailability <strong>of</strong><br />

<strong>Malathion</strong> as sole carbon source or due to the production <strong>of</strong><br />

some other toxic compounds indicating the death phase.<br />

Indole Acetic Acid Production <strong>of</strong> Isolated Bacterial<br />

Strains: The bacterial isolates DKM3, DKM5, DKM8 and<br />

DKM9 were found to produce indole acetic acid. The<br />

intensity <strong>of</strong> colour change varied depending upon the<br />

amount <strong>of</strong> IAA produced by a particular isolate. The<br />

culture DKM8 and DKM9 were produced (3.7 and 2.2<br />

µg/ml IAA) after 2 days and (7.3 and 3.3 µg/ml IAA) after<br />

4 days respectively as shown in table 4. The bacterial<br />

culture DKM8 produced (3.5 and 3.8 µg/ml IAA) after 2<br />

days and (6.8 and 6.3 µg/ml IAA) after 4 days and culture<br />

DKM9 produced (2.4 and 2.1 µg/ml IAA) after 2 days and<br />

(3.4 and 3.1 µg/ml IAA) after 4 days respectively, at 0.5<br />

and 1.0 mM concentration <strong>of</strong> malathion.<br />

Phosphate Solubilization <strong>of</strong> Isolated Bacterial Culture:<br />

All the ten bacterial isolates were screened for their<br />

phosphate solubilization. Out <strong>of</strong> ten, only five bacterial<br />

isolates DKM1, DKM3, DKM5, DKM8 and DKM9<br />

formed clear zone on Pikovaskaya medium, considered as<br />

phosphate solubilizing bacteria as shown in table 1. The<br />

bacterial culture DKM8 was showing more phosphate<br />

solubilization as compared to DKM1, DKM3, DKM5 and<br />

DKM9 on the basis <strong>of</strong> diameter <strong>of</strong> halo zone in cm. The<br />

bacterial culture DKM8 was forming 1.1 and 1.2 cm halo<br />

zone after 7 and 10 days <strong>of</strong> incubation respectively. At 0.5<br />

and 1.0 concentration <strong>of</strong> <strong>Malathion</strong>, DKM8 bacterial<br />

culture was forming 1.1 and 1.1 cm halo zone after 7 days<br />

and 1.3 and 1.1 cm halo zone after 10 days respectively.<br />

Antifungal against Aspergillus sp. and Protease Activity<br />

<strong>of</strong> Isolated Bacterial Cultures: Out <strong>of</strong> ten, only two<br />

bacterial isolates DKM8 and DKM9 were forming halo<br />

zone on the nutrient agar plate containing Aspergillus<br />

growth suspension at 30 ºC, considered as antifungal active<br />

bacterial strain as shown in table 1. The halo zone was not<br />

formed by bacterial isolates DKM1, DKM2, DKM3,<br />

DKM4, DKM5, DKM6, DKM7 and DKM10. Only two<br />

bacterial isolates DKM8 and DKM10 were forming clear<br />

zone on the skimmed milk agar medium at 30 ºC,<br />

considered as protease producing bacteria as shown in table<br />

1. The clear zone on skimmed milk agar medium was not<br />

formed by bacterial isolates DKM1, DKM2, DKM3,<br />

DKM4, DKM5, DKM6, DKM7 and DKM9.<br />

Antibiotic Resistance Pattern <strong>of</strong> Bacterial Strain DKM8<br />

and DKM9: The antibiotic resistant pattern <strong>of</strong> DKM8 and<br />

(61)<br />

DKM9 was determined by using disc diffusion method.<br />

The bacterial culture DKM8 was sensitive towards<br />

antibiotic (cephalothin, teicoplanin, methicillin) and<br />

resistant towards (chloromphenicol, oxacillin, ampicillin,<br />

clarithromycin, gentamycin, amoxyclav, vancomycin,<br />

amikacin, novobiocin, erythromycin, co-trimoxazole,<br />

penicillin, azithromycin, <strong>of</strong>loxacin, linezolid, clindamycin,<br />

tetracycline). The bacterial culture DKM9 was sensitive<br />

toward antibiotic (clarithromycin, amoxyclav,<br />

erythromycin, teicoplanin, <strong>of</strong>loxacin, methicillin, linezolid,<br />

clindamycin) and resistant towards (chloromphenicol,<br />

oxacillin, ampicillin, gentamycin, vancomycin, amikacin,<br />

novobiocin, co-trimoxazole, penicillin, azithromycin,<br />

tetracycline)<br />

Degradation <strong>of</strong> <strong>Malathion</strong> by Bacterial Strain DKM8:<br />

To elucidate that the bacterial strain DKM8 degrades<br />

<strong>Malathion</strong>, resting cell study was performed. From GC<br />

analysis, it was found that the initial concentration <strong>of</strong><br />

<strong>Malathion</strong>, 6.9 ppm, reduced to 4.74 ppm after 24 hr and<br />

further reduced to 2.04 ppm after 48 hr indicating 70.5 %<br />

depletion <strong>of</strong> <strong>Malathion</strong> by bacterial strain DKM8 as shown<br />

in fig. 2. However, in case <strong>of</strong> heat killed resting cell, no<br />

depletion <strong>of</strong> <strong>Malathion</strong> was observed.<br />

Discussion<br />

During enrichment, the natural selection <strong>of</strong> microorganisms<br />

takes place in the presence <strong>of</strong> xenobiotic compound and its<br />

rapid biodegradation is known to take place 7 . In most cases,<br />

the isolated microorganisms are able to utilize the pesticide<br />

as a source <strong>of</strong> a single element (C, N, P or S).<br />

<strong>Pseudomonas</strong> putida strain was able to use ethoprophos as<br />

a carbon source but not as a phosphorus source 21 . In the<br />

present study by using enrichment technique 10 bacterial<br />

strains (DKM1, DKM2, DKM3, DKM4, DKM5, DKM6,<br />

DKM7, DKM8, DKM9 and DKM10) were isolated from<br />

pesticide contaminated soil. All the isolated strains were<br />

able to grow in both minimal salt agar medium as well as in<br />

broth medium containing 0.5 mM <strong>Malathion</strong> as the sole<br />

carbon source. The different bacterial strains were isolated<br />

by using enrichment culture technique capable <strong>of</strong> <strong>degrading</strong><br />

organophosphorus pesticides such as <strong>Malathion</strong>. These<br />

include Agrabacterium radiobacte 18 , <strong>Pseudomonas</strong> and<br />

Micrococcus sp. 37 and Bacillus thuringiensis 50 .<br />

The isolated bacterial strain DKM8 was found very close to<br />

<strong>Pseudomonas</strong> <strong>xanthomarina</strong> on the basis <strong>of</strong> morphological,<br />

physiological and biochemical characteristics. Most species<br />

<strong>of</strong> <strong>Pseudomonas</strong> can grow in minimal medium <strong>with</strong> a<br />

single organic compound as carbon and energy source 31 .<br />

Pseudomonads possess a variety <strong>of</strong> diverse catabolic<br />

pathways that enable them to metabolize an equally diverse<br />

number <strong>of</strong> low molecular weight compounds, including<br />

chlorinated aliphatic hydrocarbons such as<br />

phenoxyalkanoic acid herbicides 25 . It is known for its<br />

capacity to degrade phenolic compounds 19 and other<br />

aromatic substances. Therefore, Pseudomonads are ideal<br />

choice as the bacteria to be used for degradative


Research Journal <strong>of</strong> Chemistry and Environment___________________________________Vol.17 (3) March (2013)<br />

Res. J. Chem. Environ.<br />

biotechnologies 33, 47 .<br />

In the present study, the growth <strong>of</strong> all isolates was observed<br />

in BSM media containing 0.5 mM <strong>Malathion</strong>. The growth<br />

<strong>of</strong> bacterial culture DKM8 was rapid after 1 day in the<br />

presence <strong>of</strong> 0.5 mM <strong>Malathion</strong>, showing exponential phase<br />

<strong>of</strong> growth. After 4 days, the growth <strong>of</strong> DKM8 declined<br />

which may be due to unavailability <strong>of</strong> <strong>Malathion</strong> as sole<br />

carbon source or due to the production <strong>of</strong> some toxic<br />

compound indicating the death phase.<br />

The physiologically most active auxin in plants is indole-3acetic<br />

acid (IAA), which is known to stimulate both rapid<br />

(e.g. increases in cell elongation) and long-term (e.g. cell<br />

division and differentiation) responses in plants. In the<br />

present study, bacterial isolates DKM3, DKM5, DKM8 and<br />

DKM9 were showing IAA production. The isolate DKM8<br />

was showing more IAA production as compared to DKM9.<br />

The IAA production ability <strong>of</strong> bacterial strain DKM8 was<br />

also checked in the presence <strong>of</strong> <strong>Malathion</strong>. It was found<br />

that there was no effect on IAA production in presence <strong>of</strong><br />

different concentration <strong>of</strong> <strong>Malathion</strong> (0.5 mM, 1.0 mM and<br />

1.5 mM). <strong>Pseudomonas</strong> species have shown promising<br />

results in the production <strong>of</strong> IAA as plant growth promotion<br />

activites 42 .<br />

Phosphate solubilizing microorganism (PSM) is present in<br />

almost all soils, although their number varies depending<br />

upon the soil and climatic conditions 22 . First time in 1903,<br />

tricalcium phosphate (TCP) solubilization was<br />

demonstrated by soil bacteria in liquid and in solid<br />

medium 38 . However, the extent <strong>of</strong> phosphate solubilization<br />

varies <strong>with</strong> the source <strong>of</strong> inorganic phosphate and the<br />

micro-organisms involved 2 . PSM helps in utilization <strong>of</strong><br />

indigenous rock phosphates 20 . Thus, PSM causes the<br />

release <strong>of</strong> nutrients into the soil for naturally balanced<br />

proportion 6 and exerts beneficial effects on plant<br />

development 14 . In the present study, all the ten bacterial<br />

isolates were screened for phosphate solubilization activity.<br />

The bacterial isolates DKM1, DKM3, DKM5, DKM8 and<br />

DKM9 were forming clear zone on the Pikovaskaya<br />

medium, considered as phosphate solubilizing bacteria. The<br />

bacterial culture DKM8 was showing more phosphate<br />

solubilization as compared to DKM1, DKM3, DKM5 and<br />

DKM9. The phosphate solubilizing ability <strong>of</strong> DKM8 was<br />

not adversely affected by the presence <strong>of</strong> <strong>Malathion</strong>.<br />

Microbial community composition can also contribute to<br />

the suppression <strong>of</strong> germination and mycelia growth <strong>of</strong> soil<br />

fungi to a certain extent 9 . In the present study, out <strong>of</strong> ten,<br />

only two bacterial strains (DKM8 and DKM9) showed<br />

antifungal activity against Aspergillus sp. The antifungal<br />

potential <strong>of</strong> Bacillus sp., <strong>Pseudomonas</strong> sp. and<br />

Streptomyces sp. has also been reported to inhibit the<br />

mycelial growth <strong>of</strong> many species <strong>of</strong> Aspergillus,<br />

Penicillium and Fusarium 28, 30 .<br />

For agricultural application, protease producing microorg-<br />

(62)<br />

anisms act as biological control agents for eradication <strong>of</strong><br />

some fungal plant pathogens 41 . Regulation <strong>of</strong> soil protease<br />

activities in soil is important to maintain the fertility <strong>of</strong><br />

soil 46 . In the present study, out <strong>of</strong> ten bacterial isolates,<br />

only two bacterial strains (DKM8 and DKM10) were<br />

showing protease activity on skimmed milk agar medium.<br />

The bacterial strain DKM8 showed more protease activity<br />

as compared to DKM10.<br />

The antibiotics produced by PGPR include: butyrolactones,<br />

zwittermycin A, kanosamine, oligomycin A, oomycin A,<br />

phenazine-1-carboxylic acid, pyoluteorin, pyrrolnitrin,<br />

viscosinamide, xanthobaccin and 2, 4-diacetyl<br />

phloroglucinol 48 . The DAPG is one <strong>of</strong> the most efficient<br />

antibiotics in the control <strong>of</strong> plant pathogens 10 and can be<br />

produced by various strains <strong>of</strong> <strong>Pseudomonas</strong> 35 . The isolates<br />

DKM8 and DKM9 were resistant to antibiotic<br />

(chloromphenicol, oxacillin, ampicillin, gentamycin,<br />

vancomycin, amikacin, novobiocin, co-trimoxazole,<br />

penicillin, azithromycin and tetracycline).<br />

The resting cell study was performed to check the<br />

quantitative degradation <strong>of</strong> <strong>Malathion</strong>. Resting cells <strong>of</strong><br />

<strong>Pseudomonas</strong> derived from cultures were grown on<br />

diazinon or <strong>Malathion</strong> for extensive destruction <strong>of</strong> these<br />

two organophosphates 36 . In the present study, from GC<br />

analysis, it was found that the initial concentration <strong>of</strong><br />

<strong>Malathion</strong> (6.9 ppm) reduced to 4.74 ppm after 24 hr and<br />

further reduced to 2.04 ppm after 48 hr indicating 70.5 %<br />

depletion <strong>of</strong> <strong>Malathion</strong> by strain DKM8. It was reported<br />

that a strain <strong>of</strong> <strong>Pseudomonas</strong> isolated from peppermill<br />

effluents was capable <strong>of</strong> <strong>degrading</strong> <strong>Malathion</strong> cometabollically<br />

up to <strong>Malathion</strong> mono carboxylic acid 39 .<br />

Several species <strong>of</strong> <strong>Pseudomonas</strong> have been reported to<br />

degrade organophosphorus pesticide 8,33 .<br />

Conclusion<br />

This research may have practical applications in<br />

bioremediation <strong>of</strong> <strong>Malathion</strong> contaminated soil, waste<br />

dump, industrial effluents and contaminated water<br />

environment. Apart from this, bacterial strain DKM8 can<br />

be used in the field <strong>of</strong> agriculture as a tool for plant growth<br />

promotion. Manipulations <strong>of</strong> such bacterial strains in<br />

relation to bioremediation and plant growth promotion are<br />

promising areas for further development. The bacterial<br />

strain DKM8 can be used as bi<strong>of</strong>ertilizer for sustainable<br />

crop production system along <strong>with</strong> remediation <strong>of</strong><br />

<strong>Malathion</strong> under field conditions. Characterizing the<br />

pathway for degradation, identifying the genes and<br />

enzymes involved in this process represents areas for<br />

further investigation.<br />

References<br />

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Research Journal <strong>of</strong> Chemistry and Environment___________________________________Vol.17 (3) March (2013)<br />

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OD at 600 nm<br />

0.45<br />

0.4<br />

0.35<br />

0.3<br />

0.25<br />

0.2<br />

0.15<br />

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0<br />

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DKM1<br />

DKM2<br />

DKM3<br />

DKM4<br />

DKM5<br />

DKM6<br />

DKM7<br />

Fig. 1: Growth <strong>of</strong> isolated strains in basal salt medium containing 0.5 mM <strong>Malathion</strong><br />

<strong>Malathion</strong><br />

Concentration<br />

(ppm)<br />

8<br />

7<br />

6<br />

5<br />

4<br />

3<br />

2<br />

1<br />

0<br />

6.9<br />

6.9<br />

6.8<br />

4.74<br />

6.8<br />

0 hr 24 hr 48 hr<br />

Time (hr)<br />

<strong>Malathion</strong> degradation by<br />

DKM8<br />

<strong>Malathion</strong> degradation by<br />

heat killed cells<br />

2.04<br />

Fig. 2: Degradation <strong>of</strong> <strong>Malathion</strong> by bacterial strain DKM8


Research Journal <strong>of</strong> Chemistry and Environment___________________________________Vol.17 (3) March (2013)<br />

Res. J. Chem. Environ.<br />

Table 1<br />

Growth promoting characteristics (IAA production, Phosphate solubilization, antifungal activity and protease<br />

activity) <strong>of</strong> isolated bacterial strains<br />

Culture Name IAA production Phosphate solubilization Antifungal activity Protease activity<br />

DKM1 - + - -<br />

DKM2 - - - -<br />

DKM3 + + - -<br />

DKM4 - - - -<br />

DKM5 + + - -<br />

DKM6 - - - -<br />

DKM7 - - - -<br />

DKM8 + + + +<br />

DKM9 + + + -<br />

DKM10 - - - +<br />

Table 2<br />

Identification <strong>of</strong> <strong>Malathion</strong> <strong>degrading</strong> bacterial culture DKM8 by morphological and physiological test<br />

Tests Result<br />

Colony morphology Circular, Cream, Entire, Flat<br />

Gram’s reaction -<br />

Cell shape and size Rod, 0.8x1.5<br />

Spore (s) -<br />

Motility +<br />

Growth at temperatures (°C)<br />

4, 10, 15, 25, 42, 60 -<br />

30, 37 +<br />

Growth at pH<br />

pH 5.0, 8.0, 10.0 +<br />

Growth on NaCl (%)<br />

2.0, 4.0, 5.0 +<br />

8.0 +<br />

+: Positive, -: Negative, (+): Weak positive<br />

Table 3<br />

Identification <strong>of</strong> <strong>Malathion</strong> <strong>degrading</strong> bacterial culture DKM8 by biochemical test<br />

Tests DKM8<br />

Growth on MacConkey -<br />

Indole test -<br />

Methyl red test +<br />

Voges Proskauer test -<br />

Citrate utilization +<br />

H2S production -<br />

Gas production from glucose -<br />

Gelatin, Esculin, Starch and Urea hydrolysis -<br />

Nitrate reduction +<br />

Ornithine and Lysine decarboxylase -<br />

Catalase and oxidase test +<br />

Tween 20 and Tween 40 hydrolysis -<br />

Acid production from Dextrose +<br />

Acid production from Lactose -<br />

+: Positive, -: Negative, (+): Weak positive<br />

(64)


Research Journal <strong>of</strong> Chemistry and Environment___________________________________Vol.17 (3) March (2013)<br />

Res. J. Chem. Environ.<br />

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DKM8 2 3.7 3.5 3.8<br />

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DKM9 2 2.2 2.4 2.1<br />

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(Received 15 th October 2012, accepted 17 th January 2013)

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