Specialist Group on ANAEROBIC DIGESTION Newsletter - IWA
Specialist Group on ANAEROBIC DIGESTION Newsletter - IWA
Specialist Group on ANAEROBIC DIGESTION Newsletter - IWA
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<str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong><br />
<strong>ANAEROBIC</strong> <strong>DIGESTION</strong><br />
<strong>Newsletter</strong><br />
June 2009<br />
CONTENTS<br />
Chairman’s note 2<br />
C<strong>on</strong>tributi<strong>on</strong>s to the <strong>Newsletter</strong> 2<br />
Management committee of the AD <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> 3<br />
How to join the <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong> 3<br />
Update from the Task <str<strong>on</strong>g>Group</str<strong>on</strong>g>s <strong>on</strong> Anaerobic Digesti<strong>on</strong> 4<br />
News from the world <strong>on</strong> Anaerobic Digesti<strong>on</strong> 5<br />
AD people <strong>on</strong> the move 6<br />
Past and coming c<strong>on</strong>ferences and events 8<br />
Books and publicati<strong>on</strong>s 11<br />
PhD theses <strong>on</strong> anaerobic digesti<strong>on</strong> 13<br />
Ongoing anaerobic digesti<strong>on</strong> projects 29<br />
Anaerobic URL sites 33<br />
Disclaimer: This is not a journal, but a <strong>Newsletter</strong> issued by the <strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong>.<br />
Statements made in this <strong>Newsletter</strong> do not necessarily represent the views of the <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> or those of the<br />
<strong>IWA</strong>. The use of informati<strong>on</strong> supplied in the <strong>Newsletter</strong> is at the sole risk of the user, as the <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g><br />
and the <strong>IWA</strong> do not accept any resp<strong>on</strong>sibility or liability.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 1
CHAIRMAN’S NOTE<br />
Welcome to the 2009 Anaerobic Digesti<strong>on</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>Newsletter</strong>, and a<br />
new specialist group management committee. As most of you probably know,<br />
the AD specialist group is <strong>on</strong>e of the largest in <strong>IWA</strong>, with over 1000 members,<br />
and has a massive impact <strong>on</strong> public policy, and the sustainable applicati<strong>on</strong> of<br />
wastewater around the world.<br />
The outgoing committee, headed by Jules van Lier, and Sergey Kalyuzhnyi<br />
were a key part of the success and activity of the specialist group, and we now<br />
have some big shoes to fill. Gladly, Jules has agreed to c<strong>on</strong>tinue his input to the<br />
specialist group as Western Europe representative. Jules is <strong>on</strong>e of four original<br />
management committee members who c<strong>on</strong>tinued, out of 20 members in total. It<br />
is very exciting that we have so many new, and early career specialists in the<br />
management committee, to ensure inspired leadership for anaerobic digesti<strong>on</strong> for<br />
the future.<br />
We also have a lot of exciting events coming up in the near future. AD12, the<br />
major anaerobic c<strong>on</strong>ference will be held in Guadalajara, Mexico in late October 2010. In past c<strong>on</strong>gresses, we<br />
have seen the emergence of major themes, including hydrogen producti<strong>on</strong> in M<strong>on</strong>treal at AD10, and more<br />
recently, bio-electrochemical systems at AD11 in Brisbane. Supporting this, we have AD sp<strong>on</strong>sored specialist<br />
c<strong>on</strong>ferences, including WWTmod2010, in March 2010 in Canada, an area for emerging modelling topics, and<br />
Anaerobic Digesti<strong>on</strong> of Solid Wastes and Energy Crops, to be held in 2011, in Vienna. Al<strong>on</strong>g with these<br />
<str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> c<strong>on</strong>ferences, there will be a number of new initiatives directly from <strong>IWA</strong>, aimed at increasing<br />
collaborati<strong>on</strong> between specialist groups. Together with the rest of the management committee, and <strong>IWA</strong> as a<br />
whole, we thank you, our specialist group members for your support through the electi<strong>on</strong> process. I look<br />
forward to meeting old and new friends in the specialist group very so<strong>on</strong>, but in the meantime, please enjoy our<br />
latest newsletter.<br />
CONTRIBUTIONS TO THE NEWSLETTER<br />
C<strong>on</strong>tributi<strong>on</strong>s to the <strong>Newsletter</strong> should be addressed to the <strong>Newsletter</strong> Editor or alternatively to the <str<strong>on</strong>g>Group</str<strong>on</strong>g><br />
Chairman or to the <str<strong>on</strong>g>Group</str<strong>on</strong>g> Secretary. Please submit your c<strong>on</strong>tributi<strong>on</strong>s by e-mail and in Microsoft Word format.<br />
<str<strong>on</strong>g>Group</str<strong>on</strong>g> Chairman <str<strong>on</strong>g>Group</str<strong>on</strong>g> Secretary <strong>Newsletter</strong> Editor<br />
Dr Damien Batst<strong>on</strong>e<br />
Advanced Water Management Centre<br />
(AWMC)<br />
The University of Queensland<br />
St Lucia, 4072<br />
Australia<br />
fax: +61-7-33654726<br />
e-mail: damienb@awmc.uq.edu.au<br />
Dr Henri Spanjers<br />
Lettinga Associates Foundati<strong>on</strong><br />
(LeAF)<br />
P.O. Box 500<br />
NL-6700 AM Wageningen<br />
The Netherlands<br />
Tel: +31 317483202/+31 317482023<br />
e-mail: henri.spanjers@wur.nl<br />
Dr Jorge Rodríguez-Rodríguez<br />
Sustainable Envir<strong>on</strong>ment Research Centre<br />
(SERC)<br />
University of Glamorgan<br />
P<strong>on</strong>typridd CF37 1DL<br />
United Kingdom<br />
Tel: +44(0)1443 65 4282<br />
email: jrodrigu@glam.ac.uk<br />
Editor’s note: The best care was taken to avoid typing errors during the editing of the c<strong>on</strong>tributi<strong>on</strong>s received<br />
from SG members. However should the reader find any mistake please report it to the editor and it will be<br />
corrected in the next issue.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
2 June 2009 <strong>Newsletter</strong>
MANAGEMENT COMITEE OF THE AD SPECIALIST GROUP<br />
A renovated Management Committee for the <strong>IWA</strong> Anaerobic Digesti<strong>on</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> has been elected early<br />
this year. The compositi<strong>on</strong> of the new committee is as follows:<br />
MANAG. COMMITTEE ROLE PERSON ELECTED E-MAIL<br />
Chair Damien Batst<strong>on</strong>e damienb@awmc.uq.edu.au<br />
Secretary Henri Spanjers henri.spanjers@wur.nl<br />
<strong>Newsletter</strong> Editor Jorge Rodríguez-Rodríguez jrodrigu@glam.ac.uk<br />
REGIONAL REPRESENTATIVES<br />
Northern Europe Irini Angelidaki ria@er.dtu.dk<br />
Western Europe<br />
Jules B. van Lier<br />
Alan Guwy<br />
j.b.vanlier@tudelft.nl<br />
ajguwy@glam.ac.uk<br />
Southern Europe<br />
Joan Mata-Álvarez<br />
Jean-Philippe Steyer<br />
jmata@ub.edu<br />
steyer@ensam.inra.fr<br />
Central & Eastern Europe Pavel Jenicek<br />
Eberhard F. Morgenroth<br />
pavel.jenicek@vscht.cz<br />
eberhard.morgenroth@eawag.ch<br />
North America<br />
David Bagley<br />
Viviane Yargeau<br />
bagley@uwyo.edu<br />
viviane.yargeau@mcgill.ca<br />
Central America Germán Buitrón gbuitr<strong>on</strong>m@ii.unam.mx<br />
South America Carlos Chernicharo calemos@desa.ufmg.br<br />
Middle East Moktar Hamdi moktar.hamdi@insat.rnu.tn<br />
Central Asia Makarand M. Ghangrekar ghangrekar@civil.iitkgp.in<br />
Asia Raman Saravanane rsaravanane@pec.edu<br />
Asian Islands Hiroshi Tsuno hs-tsuno@water.mbox.media.kyoto-u.ac.jp<br />
Australia Jurg Keller j.keller@uq.edu.au<br />
HOW TO JOIN THE SPECIALIST GROUP ON <strong>ANAEROBIC</strong> <strong>DIGESTION</strong><br />
All members of <strong>IWA</strong> are welcome to join the <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g>. With the <strong>IWA</strong> registrati<strong>on</strong>, you can indicate<br />
which <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g>(s) you wish to join.<br />
If you wish to become member of the <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong> and you did not have indicated it<br />
<strong>on</strong> your <strong>IWA</strong> registrati<strong>on</strong> form, please c<strong>on</strong>tact the Chairman or the Secretary.<br />
You may also directly c<strong>on</strong>tact <strong>IWA</strong>:<br />
Keith Roberts<strong>on</strong> (keith.roberts<strong>on</strong>@iwahq.org.uk) or Frances Lucraft (frances.lucraft@iwahq.org.uk)<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 3
UPDATE FROM THE TASK GROUPS ON <strong>ANAEROBIC</strong> <strong>DIGESTION</strong><br />
<strong>IWA</strong> Task <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Mathematical Modelling of Anaerobic Digesti<strong>on</strong><br />
The <strong>IWA</strong> Anaerobic Digesti<strong>on</strong> Modelling Task <str<strong>on</strong>g>Group</str<strong>on</strong>g> is currently not active, but we have observed a number of<br />
developments in the area. A workshop was held at WWTmod 2008 in Quebec, Canada. This was aimed at<br />
identifying some of the key limitati<strong>on</strong>s of the ADM1 for practical use. The two major issues identified were<br />
characterisati<strong>on</strong> of influents, and the physicochemical system. In particular, for the latter, it was identified that<br />
phosphorous still could not be effectively modelled in anaerobic digesters (or in aerobic systems). The <strong>IWA</strong><br />
Benchmarking Model Taskgroup has partly addressed the first issue as Nopens, et al. (2009) "An ASM/ADM<br />
model interface for dynamic plant-wide simulati<strong>on</strong>" Wat. Res. 43(7): 1913-1923. This provides an input model<br />
for relatively straight forward definiti<strong>on</strong> from activated sludge, and can be readily adapted to other substrates.<br />
The main task remaining is providing reference applicati<strong>on</strong>s of this input model to areas other than activated<br />
sludge. The issue of advanced physicochemical models is more involved, and some of the challenges have been<br />
further outlined in Batst<strong>on</strong>e, D.J. (2009) “Towards a generalised physicochemical modelling framework”<br />
Reviews in Envir<strong>on</strong>. Sci. Biotech 8(2):113.<br />
Damien Batst<strong>on</strong>e, Chair of ADM Task <str<strong>on</strong>g>Group</str<strong>on</strong>g><br />
<strong>IWA</strong>-AD Task <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Harm<strong>on</strong>izati<strong>on</strong> of Anaerobic Biodegradati<strong>on</strong>, Activity and Inhibiti<strong>on</strong> Assays<br />
(TG ABAI)<br />
The ABAI TG has the objective to harm<strong>on</strong>ise anaerobic biodegradability, activity and inhibiti<strong>on</strong> assays. The<br />
group met last time for a workshop in Prague, where a report was written summarising the discussi<strong>on</strong>s during<br />
the ABAI TG. Based <strong>on</strong> the work of ABAI TG a paper was presented by at the Solid waste c<strong>on</strong>ference by David<br />
Bolz<strong>on</strong>ella in Hemet, Tunesia. The paper has been recently published:<br />
I. Angelidaki, M. Alves, D. Bolz<strong>on</strong>ella, L. Borzacc<strong>on</strong>i, J. L. Campos, A. J. Guwy, S. Kalyuzhnyi, P.<br />
Jenicek and J. B. van Lier (2009). Defining the biomethane potential (BMP) of solid organic wastes and<br />
energy crops: a proposed protocol for batch assays. Water Sci. Technol. 59(5), pp. 927-934<br />
Irini Angelidaki, Chair of the ABAI-TG<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
4 June 2009 <strong>Newsletter</strong>
NEWS FROM THE WORLD ON <strong>ANAEROBIC</strong> <strong>DIGESTION</strong><br />
Lee Kuan Yew Water prize 2009 awarded to Gatze Lettinga<br />
(from LeAF <strong>Newsletter</strong> March 2009)<br />
We are happy to announce that Gatze Lettinga is awarded the<br />
Lee Kuan Yew Water prize 2009. The Lee Kuan Yew Water<br />
prize is an annual award for “outstanding c<strong>on</strong>tributi<strong>on</strong>s<br />
towards solving global water problems by applying<br />
groundbreaking technologies or implementing innovative<br />
policies and programmes which benefit mankind”. The prize<br />
comprises a gold medalli<strong>on</strong>, an award certificate and a cash<br />
prize of S$300000. The prize is named after former<br />
Singapore Prime Minister and present Minister Mentor Lee<br />
Kuan Yew, who has been excepti<strong>on</strong>ally important for<br />
Singapore in attaining a sustainable water supply.<br />
Gatze Lettinga receives the award for his “breakthrough,<br />
envir<strong>on</strong>mentally sustainable soluti<strong>on</strong> for the treatment of<br />
used water using anaerobic technology”. The jury recognizes the revoluti<strong>on</strong>ary aspects of the treatment c<strong>on</strong>cept<br />
that enables cost-effective (pre-) treatment of wastewater, combined with the producti<strong>on</strong> of renewable energy,<br />
fertilizer and soil c<strong>on</strong>diti<strong>on</strong>er. Furthermore, the jury appreciates the fact that the technology was never patented,<br />
which makes the technology universally available. As a c<strong>on</strong>sequence anaerobic wastewater technology has been<br />
widely applied for both industrial and municipal wastewater.<br />
This is the sec<strong>on</strong>d time that the prize has been awarded. Gatze Lettinga was chosen from a total of 39<br />
nominati<strong>on</strong>s from 19 different countries. He will receive the award <strong>on</strong> June 24 in the official residence and<br />
office of Singapore’s president during the Singapore Internati<strong>on</strong>al Water Week (SIWW) 22-26 June 2009. In<br />
additi<strong>on</strong>, Gatze Lettinga will deliver the Singapore Water Lecture <strong>on</strong> June 23.<br />
The SIWW is a global platform for experts in different fields to discuss <strong>on</strong>going issues in the water world. The<br />
theme in 2009 is “SustainableCities – Infrastructure and technologies for Water”. During this event we will<br />
organise a special sessi<strong>on</strong> dedicated to sustainable technology development with Gatze Lettinga as h<strong>on</strong>oured<br />
guest.<br />
Gatze Lettinga was professor “Anaerobic Treatment Technology and Reuse” at the subdepartment of<br />
Envir<strong>on</strong>mental Technology of Wageningen University from 1988 to 2001. In 1997 and together with professor<br />
Jules van Lier, he founded LeAF, of which he was board member till July 2004. Nowadays, he is still active as<br />
advisor of the board of LeAF (am<strong>on</strong>gst his numerous other activities). Gatze Lettinga’s achievements have been<br />
h<strong>on</strong>oured by several awards. Only two years ago he received the prestigious Tyler prize for Envir<strong>on</strong>mental<br />
Achievements in Los Angeles, USA.<br />
For more informati<strong>on</strong> <strong>on</strong> the Lee Kuan Yew Water prize and the Singapore Internati<strong>on</strong>al Water Week:<br />
http://www.siww.com.sg/<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 5
AD PEOPLE ON THE MOVE<br />
OPEN POSITIONS<br />
21 m<strong>on</strong>th postdoctoral positi<strong>on</strong> at the Laboratoire de Biotechnologie de l’Envir<strong>on</strong>nement (LBE-<br />
INRA), Narb<strong>on</strong>ne – France <strong>on</strong> the topic of “Optimisati<strong>on</strong> of biomass pretreatment and<br />
hydrolysis to maximise biogas producti<strong>on</strong> from agricultural wastes”<br />
The work will be undertaken at the Laboratoire de Biotechnologie de l’Envir<strong>on</strong>nement (LBE). The candidate<br />
will take advantage of working in a multi-disciplinary group with competences in microbial engineering, process<br />
engineering, modeling, automatics and microbial ecology.<br />
This post-doc positi<strong>on</strong> will be included in a research collaborati<strong>on</strong> with Campinas University (Unicamp, INRA<br />
FASESP project).<br />
This project will have three main objectives:<br />
1- To maximise biogas (biomethane) producti<strong>on</strong> from several lignocellulosic residues by the development of<br />
physico-chemical and/or enzymatic pre-treatments,<br />
2- To optimise pre-treatments and find relati<strong>on</strong>ships between optimal pre-treatment c<strong>on</strong>diti<strong>on</strong>s and biomass<br />
characterisati<strong>on</strong><br />
3- To determine bio-physico-chemical indicators of anaerobic biodegradability (or biomethane potential).<br />
Besides, batch anaerobic digesti<strong>on</strong> runs which will allow us to assess biomethane producti<strong>on</strong> from raw and<br />
pretreated biomass. Experiments will also c<strong>on</strong>cern :<br />
- biomass characterisati<strong>on</strong> according to classical methods used within residues treatment domain. Innovating<br />
methods or methods taken from other scientific fields are also forecasted. They may include biochemical,<br />
chemical, physical or spectroscopic methods.<br />
- biomass pretreatments which may include physical, thermo-chemical and enzymatic techniques,<br />
- modeling of pre-treatments and anaerobic digesti<strong>on</strong> to describe relati<strong>on</strong>s between biomass characterisati<strong>on</strong><br />
and optimal pretreatment c<strong>on</strong>diti<strong>on</strong>s and methane producti<strong>on</strong>.<br />
Starting date from September 1st 2009 Durati<strong>on</strong> 21 m<strong>on</strong>ths<br />
Expected competence of the candidate:<br />
- Candidates must hold a PhD in process engineering or bioengineering<br />
- Skills in lignocellulosic biomass treatment will be a plus<br />
- The ability to communicate and publish in English is mandatory<br />
- Candidates should combine aut<strong>on</strong>omy and team working abilities.<br />
Candidature c<strong>on</strong>diti<strong>on</strong>s:<br />
• Doctor at recruitment date (French doctorate, PhD or foreign doctorate of equivalent level) for less than 5<br />
years,<br />
• To fill an applicati<strong>on</strong> <strong>on</strong> INRA Web site ( www.inra.fr ) before July 31 st .<br />
C<strong>on</strong>tact: Dr. Hélène Carrère (carrere@supagro.inra.fr) and Dr. Jean-Phi Steyer (steyer@supagro.inra.fr)<br />
INRA, UR 050, Laboratoire de biotechnologie de l’Envir<strong>on</strong>nement, Avenue des Etangs, 11100 Narb<strong>on</strong>ne,<br />
FRANCE. http://www.m<strong>on</strong>tpellier.inra.fr/narb<strong>on</strong>ne<br />
Open PhD positi<strong>on</strong>s in Hamburg University<br />
Investigati<strong>on</strong> of the microbial diversity in anaerobic digesters for renewable biomass (sugar beet silage) by FISH<br />
technique.<br />
Investigati<strong>on</strong> of the microbial diversity in anaerobic digesters for renewable biomass (sugar beet silage) by the<br />
RFLP technique.<br />
C<strong>on</strong>tact: Prof. Dr. Paul Scherer<br />
Hamburg University of Applied Sciences<br />
Lohbruegger Kirchstr. 65<br />
21033 Hamburg-Bergedorf (Germany)<br />
Tel.: +49/40/42875-6355 or -6351<br />
Fax: +49/40/42875-6359<br />
www.haw-hamburg.de/4357 (profile)<br />
Paul.Scherer@haw-hamburg.de<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
6 June 2009 <strong>Newsletter</strong>
CHANGES OF AFFILIATION<br />
Largus (Lars) T. Angenent has joined the Department of Biological and Envir<strong>on</strong>mental Engineering at Cornell<br />
University at the rank of Associate Professor after 6 years <strong>on</strong> the faculty at Washingt<strong>on</strong> University in St. Louis.<br />
Dr. Angenent holds a Ph.D. in Envir<strong>on</strong>mental Engineering from Iowa State University, an M.S. in<br />
Envir<strong>on</strong>mental Technology/Microbiology from Wageningen University (formerly Wageningen Agricultural<br />
University), Wageningen, The Netherlands, and a B.S. in Envir<strong>on</strong>mental Sciences from Wageningen University.<br />
Dr. Angenent’s research focuses <strong>on</strong> optimizing biological anaerobic fermentati<strong>on</strong> processes to foster undefined<br />
mixed cultures that c<strong>on</strong>vert organic wastes into bioenergy carriers, such as methane, electrical current, hydrogen,<br />
or precursors for the liquid biofuel butanol. In this area, his lab focuses <strong>on</strong> improving the performance and<br />
stability of anaerobic digesters, <strong>on</strong> novel microbial fuel cell c<strong>on</strong>figurati<strong>on</strong>s, and <strong>on</strong> the optimizati<strong>on</strong> of anaerobic<br />
fermentati<strong>on</strong> or respirati<strong>on</strong>. When necessary, molecular biology techniques are used in c<strong>on</strong>juncti<strong>on</strong> with l<strong>on</strong>gterm<br />
bioreactor studies. Dr. Angenent is a member of the Internati<strong>on</strong>al Water Associati<strong>on</strong>, Associati<strong>on</strong> of<br />
Envir<strong>on</strong>mental Engineering and Science Professors, American Society for Microbiology, American Associati<strong>on</strong><br />
for the Advancement of Science, American Institute of BioEngineering.<br />
Samir K. Khanal recently joined the Dept. of Molecular Biosciences and Bioengineering, University of Hawaii<br />
at Manoa as an Assistant Professor. Prior to joining University of Hawaii, Dr. Khanal was a Research Assistant<br />
Professor in the Department of Civil, C<strong>on</strong>structi<strong>on</strong> and Envir<strong>on</strong>mental Engineering at Iowa State University,<br />
Ames, IA. Dr. Khanal’s research focuses <strong>on</strong> producti<strong>on</strong> of biofuels/Bioenergy and valuable bio-based products<br />
from agri/forest-residues and wastes. Dr. Khanal is a co-recipient of R&D 100 Award, 2008 Grand Prize for<br />
University Research presented by the American Academy of Envir<strong>on</strong>mental Engineers and Internati<strong>on</strong>al Water<br />
Associati<strong>on</strong> (<strong>IWA</strong>) Project Innovati<strong>on</strong> Award.. Dr. Khanal also recently published a book " Anaerobic<br />
Biotechnology for Bioenergy Producti<strong>on</strong>: Principles and Applicati<strong>on</strong> (Wiley-Blackwell Publishing). Dr. Khanal<br />
is a registered engineer in the state of Iowa.<br />
Titia de Mes has worked at DHV B.V. as a Process Design Engineer - Wastewater Treatment, Amersfoort,<br />
Netherlands. In August 2008 I took up a positi<strong>on</strong> within Atkins, Dubai, UAE as Senior Wastewater Engineer. In<br />
the Netherlands wastewater effluents are often discharged into streams and not reused. In the Middle East,<br />
potable water is mainly obtained from energy intensive desalinati<strong>on</strong> processes, the reuse of wastewater effluent<br />
is very feasible. One of my roles within Atkins is to advise our clients <strong>on</strong> water reuse schemes, appropriate<br />
treatment and water and energy saving opti<strong>on</strong>s. titia.demes@atkinsglobal.com<br />
Eberhard Morgenroth has served <strong>on</strong> the faculty of the University of Illinois at Urbana-Champaign since 2000.<br />
Starting in August 2009 he will take over a professor positi<strong>on</strong> at ETH (Swiss Federal Institute of Technology<br />
Zürich) and EAWAG (Swiss Federal Institute of Aquatic Science and Technology). His new c<strong>on</strong>tact informati<strong>on</strong><br />
are: eberhard.morgenroth@eawag.ch<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 7
PAST AND COMING CONFERENCES AND EVENTS<br />
An experts' colloquium <strong>on</strong> anaerobic technology:<br />
Sustainable Energy Producti<strong>on</strong> and Wastewater Treatment<br />
Keynote Speaker: Prof. Dr. Gatze Lettinga<br />
The Experts’ Colloquium will be held <strong>on</strong> the morning of Thursday, 25 th June 2009 at the SUNTEC Singapore<br />
Internati<strong>on</strong>al C<strong>on</strong>venti<strong>on</strong> & Exhibiti<strong>on</strong> Centre. Attendance is by invitati<strong>on</strong> <strong>on</strong>ly. Kindly c<strong>on</strong>tact Ms. Tai Xiang<br />
(xtai@wspc.com) for inclusi<strong>on</strong> into the invitati<strong>on</strong> list.<br />
The Nanyang Envir<strong>on</strong>ment and Water Research Institute (NEWRI) and Lettinga Associates Foundati<strong>on</strong><br />
(LeAF), together with World Scientific Publishing, are proud to announce An Experts' Colloquium <strong>on</strong><br />
Anaerobic Technology - Sustainable Energy Producti<strong>on</strong> and Wastewater Treatment. This Colloquium, held in<br />
h<strong>on</strong>or of Prof. Dr. Gatze Lettinga, winner of the 2009 Lee Kuan Yew Water Prize, aims to bring together leaders<br />
in anaerobic technology to discuss the sustainability and future of Anaerobic Technology.<br />
Held in c<strong>on</strong>juncti<strong>on</strong> with the Singapore Internati<strong>on</strong>al Water Week 2009, an internati<strong>on</strong>al panel of leading<br />
academics and industry speakers will be touching <strong>on</strong> various topics in anaerobic technology. The goal of the<br />
workshop is to share with stakeholders a more sustainable approach in envir<strong>on</strong>mental engineering, focusing <strong>on</strong><br />
the state of the art, potentials & challenges of implementing modern high-rate anaerobic treatment systems in<br />
integrated settings for applicati<strong>on</strong>s in Asia and elsewhere. The Colloquium’s Keynote Speaker, Prof. Dr. Gatze<br />
Lettinga will share his insights <strong>on</strong> the topic “The Ever-Improving Digestibility of High Rate Anaerobic<br />
Wastewater Treatment”.<br />
The forthcoming journal, Advances in Envir<strong>on</strong>mental Research and Development (AERD) will also be<br />
launched during the colloquium. AERD aims for rapid disseminati<strong>on</strong> of original and high quality technical<br />
papers which may be in materials, analytical techniques, water and wastewater treatment, water reclamati<strong>on</strong>,<br />
water quality, modeling of quantity and quality, air polluti<strong>on</strong> management and c<strong>on</strong>trol, soil remediati<strong>on</strong>, and<br />
wastes management and resource recovery.<br />
Annual Anaerobic Treatment Short Course in USA<br />
The annual short course titled "Anaerobic Treatment of High-Strength Industrial Waste" will be held September<br />
16-17, 2009 at Marquette University in Milwaukee, Wisc<strong>on</strong>sin, USA. Speakers will include Drs. Willy<br />
Verstraete (Gent University), Daniel Zitomer (Marquette University) and Dennis Totzke (Applied Technologies,<br />
Inc.).<br />
Informati<strong>on</strong> will be presented regarding sustainability and greenhouse gas emissi<strong>on</strong> avoidance, biogas<br />
utilizati<strong>on</strong>, anaerobic treatment fundamentals, operating strategies, design/c<strong>on</strong>structi<strong>on</strong>/start-up guidelines and<br />
case studies of operating anaerobic treatment systems.<br />
For more informati<strong>on</strong>, see http://www.marquette.edu/ANT after July 15 or email Daniel Zitomer<br />
(daniel.zitomer@mu.edu)<br />
III Simposio colombiano sobre Biotecnología Ambiental y III Simposio Colombiano sobre<br />
Digestión Anaerobia<br />
Late October, 2009. Auditorio Mario Laserna, Universidad de los Andes<br />
Organisers: Centro de Investigaci<strong>on</strong>es en Ingeniería Ambiental [CIIA] Universidad de los Andes y Red<br />
Colombiana de Biotecnología Ambiental [RECBAM]<br />
More info: http://IIIsimposiobiotecnologia.uniandes.com<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
8 June 2009 <strong>Newsletter</strong>
The Internati<strong>on</strong>al Workshop <strong>on</strong> Strategy for Anaerobic Biotechnology<br />
24-27 November 2009 Xi'an Nan Yang Hotel, Xi’an, China. Hosted by: Xi’an Jiaot<strong>on</strong>g University, Xi’an, China<br />
Anaerobic treatment has been accepted as an important technology which has been playing a key role in<br />
sustainable development since the past thirty years. A symbol for this is that the very prestigious “Tyler Prize of<br />
Envir<strong>on</strong>mental Achievement” (April, 2007) and the “Lee Kuan Yew Prize”(June, 2009) awarded Professor G.<br />
Lettinga, the main inventor of UASB and the promoter of the other innovative c<strong>on</strong>cepts <strong>on</strong> anaerobic<br />
technology. To push forward the applicati<strong>on</strong> of this sustainable technology, an internati<strong>on</strong>al workshop <strong>on</strong><br />
anaerobic biotechnology will be held <strong>on</strong> November 24-27, 2009 in Xi'an, China. It will also be good for the<br />
people who are engaged in this field to meet each other, exchange their experiences and ideas. On the occasi<strong>on</strong>,<br />
famous experts and scholars will give interesting reports.<br />
Topics:<br />
1. The research and applicati<strong>on</strong> of anaerobic biological in industrial and domestic wastewater treatment.<br />
2. Key technology and equipment <strong>on</strong> anaerobic wastewater treatment<br />
3. The research and applicati<strong>on</strong> of anaerobic digesti<strong>on</strong> of solid wastes<br />
4. Strategy for development of anaerobic technology<br />
5. C<strong>on</strong>versi<strong>on</strong> and utilizati<strong>on</strong> technology of energy from anaerobic biological treatment.<br />
6. Others<br />
Key Dates:<br />
April 20, 2009: First Announcement and call for papers<br />
July 20, 2009: Deadline for submissi<strong>on</strong> of abstracts and the sec<strong>on</strong>d announcement<br />
October 8, 2009: Deadline for submissi<strong>on</strong> of full papers<br />
November 1, 2009: Third announcement<br />
November 23, 2009: Registrati<strong>on</strong> at Xi’an Nanyang Hotel<br />
November 27-28: Departure<br />
Before 23 or after 27 of November, visit to Tsinghua University in Beijing.<br />
Fee: (1) No registrati<strong>on</strong> fee. (2) Free industrial visit<br />
Internati<strong>on</strong>al Workshop <strong>on</strong> Anaerobic Digesti<strong>on</strong>: An old story for today and tomorrow<br />
10-11 th December 2009, Narb<strong>on</strong>ne, France<br />
From A. Volta to R. Moletta, what have we learnt And how could this be useful for tomorrow<br />
Dr. René Moletta, the founder of the “Laboratoire de Biotechnologie de<br />
l’Envir<strong>on</strong>nement” (LBE-INRA - http://www.m<strong>on</strong>tpellier.inra.fr/narb<strong>on</strong>ne) has<br />
been active for more than 30 years in promoting Anaerobic Digesti<strong>on</strong> all over the<br />
world, both at a scientific level and in an industrial perspective. Before he retires,<br />
former colleagues wish to thank him in organising a special 2 day workshop <strong>on</strong><br />
Anaerobic Digesti<strong>on</strong>, An Old Story for Today and Tomorrow. This workshop will<br />
be a unique opportunity to listen to world wide recognised top scientists, to hear<br />
their great expertise in the field, to share their experience and their view of history,<br />
and to discuss with them about future in a friendly atmosphere. This workshop is<br />
also special in the sense that there will be no deadlines for sending an abstract…<br />
just a place to be and not to miss ! Both from an academic and industrial<br />
perspective!<br />
Registrati<strong>on</strong> is limited to 150 pers<strong>on</strong>s and early registrati<strong>on</strong> is<br />
recommended. It will take place in Narb<strong>on</strong>ne, France, <strong>on</strong> the 10th and<br />
11th of December 2009. Narb<strong>on</strong>ne is a lovely and sunny city located<br />
in the south of France and has a great history since the Roman time.<br />
The workshop will be help in the “salle des synodes”, a charming hall<br />
in the old palace of the archbishops, downtown Narb<strong>on</strong>ne.<br />
For more informati<strong>on</strong> and details, please c<strong>on</strong>tact:<br />
Jean-Phi Steyer (steyer@supagro.inra.fr) or Romain Cress<strong>on</strong><br />
(cress<strong>on</strong>@supagro.inra.fr)<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 9
OLIVEBIOTEQ (Seminar <strong>on</strong> biotechnology and olive products quality in the Mediterranean)<br />
The 3rd Editi<strong>on</strong> of OLIVEBIOTEQ, a c<strong>on</strong>gress-workshop dedicated to the olive industry, will take place next<br />
15-19 December 2009 in Sfax, Tunisia. This internati<strong>on</strong>al c<strong>on</strong>gress covers all aspects of this industry from the<br />
agr<strong>on</strong>omy of olive tree culture to the technology of olive transformati<strong>on</strong> (olive canning and olive oil producti<strong>on</strong>)<br />
and the management of the resulting sub-products (three phase olive mill wastewater and husk, two-phase olive<br />
mill waste, wastewater from olive canning, biomass from olive tree pruning). Olivebioteq is <strong>on</strong>e of the most<br />
important events for the actors of this industrial sector in the Mediterranean basin. Beside of being an important<br />
ec<strong>on</strong>omic activity for several Mediterranean countries, olive industry is also <strong>on</strong>e of the most polluting in the<br />
same area. Until now, no satisfactory soluti<strong>on</strong> has been applied by this industry for the protecti<strong>on</strong> of the<br />
envir<strong>on</strong>ment. Direct anaerobic digesti<strong>on</strong> or co-digesti<strong>on</strong> of its sub-products is an alternative that still looks for<br />
recogniti<strong>on</strong> and acceptati<strong>on</strong> by this industry. The 3rd Olivebioteq is then a good opportunity to promote the<br />
activities of those of you who work in this field and enters perfectly in the frame of the topic number 6: “New<br />
uses and valorisati<strong>on</strong> alternatives of olive tree products (nutriti<strong>on</strong>, health, cosmetics, energy, envir<strong>on</strong>ment ...)”.<br />
More informati<strong>on</strong> about the c<strong>on</strong>gress is available at the following link:<br />
http://www.iresa.agrinet.tn/oliveteq/1-en.html<br />
The call for papers is opened until June 30, 2009. A commercial exhibiti<strong>on</strong> will be set up in parallel to the<br />
workshop-c<strong>on</strong>gress.<br />
WWTmod2010, the 2 nd <strong>IWA</strong>/WEF Wastewater Treatment Modelling Seminar<br />
It will be held in M<strong>on</strong>t-Sainte-Anne, Québec, Canada, March 28-30, 2010. This is <strong>on</strong>e of the principal seminars<br />
for model development and soluti<strong>on</strong> policy, and is supported by the <strong>IWA</strong> AD specialist group. Further<br />
informati<strong>on</strong> can be found here:<br />
http://www.wef.org/C<strong>on</strong>ferencesTraining/C<strong>on</strong>ferencesEvents/WWTmod2010/<br />
12 th World C<strong>on</strong>gress <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
As you may know, the next big event of the anaerobic community will be in Guadalajara, Mexico next year. The<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong> selected that city as the venue for the 12 th World C<strong>on</strong>gress <strong>on</strong><br />
Anaerobic Digesti<strong>on</strong>.<br />
The organizing committee for AD 12 has been working <strong>on</strong> site in<br />
order to define the date, hotel, technical and touristic visits, to name a<br />
few of the initial decisi<strong>on</strong>s to be made. We can inform that the local<br />
venue will be Fiesta Americana Hotel, very well located in Guadalajara<br />
and that the c<strong>on</strong>gress will be held from Sunday October 31 st to Thursday<br />
November 4 th 2010. Technical visits will take place <strong>on</strong> Friday 5 th .<br />
The instituti<strong>on</strong>s involved in the organizati<strong>on</strong> are the Institute of<br />
Engineering of the Nati<strong>on</strong>al University of Mexico (UNAM) the<br />
University of Guadalajara, the Scientific and Technology Research Institute of San Luis Potosi (IPICyT) and the<br />
Metropolitan University (UAM).<br />
Guadalajara is the capital city of Jalisco state. It is the sec<strong>on</strong>d / third most important city of Mexico. This<br />
regi<strong>on</strong> is the cradle of Tequila and Mariachi, two symbols of Mexico. Some Tequila factories have installed<br />
anaerobic treatment plants, so the visit to the town of Tequila will be a most attractive technical-tourist visit, just<br />
60 km from Guadalajara.<br />
We are expecting around 600 delegates to AD 12, due to the traditi<strong>on</strong>al high technical level of the c<strong>on</strong>gress,<br />
but also to the tourist attracti<strong>on</strong>s that Jalisco and the whole Mexico offers: variety of cultural expressi<strong>on</strong>s such as<br />
archaeological sites and col<strong>on</strong>ial cities, renowned folk handcrafts, plenty of natural beauties, beaches,<br />
mountains, deserts, jungle, a diversity of cuisine styles, and the warmth of the welcoming characteristic of its<br />
people.<br />
The program and the scientific committee will be defined during this June, as the invitati<strong>on</strong> and c<strong>on</strong>firmati<strong>on</strong><br />
process is under way. The call for papers and the web site of the c<strong>on</strong>gress will be announced in a few weeks. A<br />
small commercial exhibiti<strong>on</strong> will also take place. We count <strong>on</strong> your participati<strong>on</strong>.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
10 June 2009 <strong>Newsletter</strong>
BOOKS AND PUBLICATIONS<br />
Anaerobic Biotechnology and Odor/Corrosi<strong>on</strong> C<strong>on</strong>trol for Municipalities and Industries<br />
Author: R. E. Speece,<br />
Vanderbilt University (616 pages) Price $135. US.<br />
Arehae Press, 5840 Robert E. Lee Drive, Nashville, TN USA 37215<br />
Anaerobic Biotechnology and Odor/Corrosi<strong>on</strong> C<strong>on</strong>trol for<br />
Municipalities and Industries is a unique resource prepared to provide<br />
<strong>on</strong> the job training for water quality specialists seeking up-to-date<br />
answers for optimizing design and operati<strong>on</strong> of municipal sludge<br />
digesters and industrial anaerobic treatment processes preventing odor<br />
and corrosi<strong>on</strong> formati<strong>on</strong> in collecti<strong>on</strong> and treatment systems<br />
This book (2008) is an expanded versi<strong>on</strong> of Anaerobic<br />
Biotechnology for Industrial Wastewaters by R. E. Speece (1996),<br />
c<strong>on</strong>taining 170 new pages.<br />
In Part I as chapters 1-7, and largely focused <strong>on</strong> municipal<br />
applicati<strong>on</strong>s. One chapter explores global issues of CH 4 and H 2 S. There<br />
are 70 pages <strong>on</strong> the anaerobic digesti<strong>on</strong> of municipal sludges and a<br />
chapter <strong>on</strong> biogas utilizati<strong>on</strong> is included. Extensive coverage is included<br />
of odor/corrosi<strong>on</strong> c<strong>on</strong>trol in municipal collecti<strong>on</strong> systems. There are two<br />
general approaches to odor c<strong>on</strong>trol: allowing the hydrogen sulfide to<br />
form and then attempting to treat it or preventing its generati<strong>on</strong> in the<br />
first place. A recent technology, Superoxygenati<strong>on</strong>, using the sec<strong>on</strong>d<br />
approach is included as Chapter 7 because of its proven effectiveness in<br />
odor and corrosi<strong>on</strong> preventi<strong>on</strong> as dem<strong>on</strong>strated in full-scale installati<strong>on</strong>s.<br />
When the generati<strong>on</strong> of hydrogen sulfide is eliminated, so also is the<br />
biogenic formati<strong>on</strong> of sulfuric acid. Updated c<strong>on</strong>tent of the earlier text is included in Part II as chapters 8-19,<br />
pertaining to industrial effluent treatment.<br />
The author's decades of teaching, research and c<strong>on</strong>sulting experience in adapting the remarkable possibilities<br />
of anaerobic biotechnology to both municipal and industrial wastewater reclamati<strong>on</strong>, eminently qualify him to<br />
compile comprehensive research and <strong>on</strong>-site reports currently available, and collate them into this valuable<br />
reference. Anaerobic processes at present are very useful in protecting and enhancing our envir<strong>on</strong>ment. Since<br />
regulatory issues drive technology, newer anaerobic c<strong>on</strong>figurati<strong>on</strong>s and protocols are becoming widely used<br />
successfully amidst present day shifts in financial advantage and heightened public outcry against odor and<br />
corrosi<strong>on</strong> problems.<br />
Key Topics<br />
• Preventing odors and corrosi<strong>on</strong> in municipal collecti<strong>on</strong> systems<br />
• Assessing the proper role of microbial c<strong>on</strong>sortia proximity<br />
• Incorporating recuperative thickening to maximize reactor volume usage<br />
• Optimizing thermophilic digesti<strong>on</strong> to meet EPA standards for Class A biosolids<br />
• Biodegrading toxicants<br />
Special Features<br />
• Text boxes throughout for clarity and factual retenti<strong>on</strong><br />
• In depth study of methane-producers and hydrogen sulfide-producers<br />
• Inclusi<strong>on</strong> of Superoxygenati<strong>on</strong> technology opti<strong>on</strong> for preventi<strong>on</strong> of odors and corrosi<strong>on</strong><br />
To Order:<br />
C<strong>on</strong>tact Archae Press (www.archaepress.com)<br />
Archae Press<br />
5840 R. E. Lee Drive<br />
Nashville, TN 37215<br />
615-665-0847<br />
dick.speece@vanderbilt.edu<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 11
Anaerobic Biotechnology for Bioenergy Producti<strong>on</strong>: Principles and Applicati<strong>on</strong><br />
Author: Samir K. Khanal, Ph.D., P.E. (University of Hawai'i at Manoa)<br />
Publisher: Wiley-Blackwell (www.wiley.com)<br />
Publicati<strong>on</strong> date: October 2008<br />
ISBN: 978-0-8138-2346-1<br />
Anaerobic biotechnology is a cost-effective and sustainable means of<br />
treating waste and wastewaters that couples treatment processes with the<br />
reclamati<strong>on</strong> of useful by-products and renewable biofuels. This means of<br />
treating municipal, agricultural, and industrial wastes allows waste products<br />
to be c<strong>on</strong>verted to value-added products such as biofuels, biofertilizers, and<br />
other chemicals. Anaerobic Biotechnology for Bioenergy Producti<strong>on</strong>:<br />
Principles and Applicati<strong>on</strong>s provides the reader with basic principles of<br />
anaerobic processes al<strong>on</strong>gside practical uses of anaerobic biotechnology<br />
opti<strong>on</strong>s. This book will be a valuable reference to any professi<strong>on</strong>al currently<br />
c<strong>on</strong>sidering or working with anaerobic biotechnology opti<strong>on</strong>s.<br />
• Coverage of basic Anaerobic Biotechnology principles<br />
• Practical applicati<strong>on</strong>s of principles and processes<br />
• Thorough coverage of cost-effective and sustainable means of treating<br />
waste water and resource reclamati<strong>on</strong><br />
The details about book can be found at:<br />
http://www.wiley.com/WileyCDA/WileyTitle/productCd-0813823463.html<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
12 June 2009 <strong>Newsletter</strong>
PhD THESES ON <strong>ANAEROBIC</strong> <strong>DIGESTION</strong><br />
Biomass Granulati<strong>on</strong> and Treatment of Sewage using UASB Reactor<br />
by Puspendu Bhunia<br />
Instituti<strong>on</strong>:<br />
Civil Engineering Department<br />
Indian Institute of Technology<br />
Kharagpur-721 302, WB, India<br />
Supervisor:<br />
Dr M.M. Ghangrekar<br />
Abstract:<br />
Biomass granulati<strong>on</strong> in upflow anaerobic sludge blanket (UASB) reactor still remains a challenging task while<br />
treating many wastewaters. This study enlightens the criteria’s for the determinati<strong>on</strong> of minimum size of<br />
granules, required to gain advantage of granular sludge c<strong>on</strong>figurati<strong>on</strong> and variati<strong>on</strong> of different properties with<br />
size of granules. Based <strong>on</strong> sedimentati<strong>on</strong> theory, this study suggests 0.34 mm as the minimum size of granules<br />
for sludge with specific gravity of 1.035. Likewise, 0.52 mm, 0.41 mm, 0.36 mm, 0.33 mm, and 0.3 mm should<br />
be c<strong>on</strong>sidered as minimum size of granules for specific gravity of 1.01, 1.02, 1.03, 1.04, and 1.05, respectively<br />
for retenti<strong>on</strong> of granules inside the reactor.<br />
For thick inoculum, suspended solids (SS) > 110 g/l and volatile suspended solids (VSS) to SS ratio < 0.3,<br />
cati<strong>on</strong>ic polymer additives were found to have a negative impact <strong>on</strong> biomass granulati<strong>on</strong> and COD removal<br />
efficiency. Based <strong>on</strong> the statistical models it is c<strong>on</strong>cluded that for such thick inoculum, granulati<strong>on</strong> can be<br />
obtained for treating low strength wastewaters by selecting proper combinati<strong>on</strong>s of influent COD and liquid<br />
upflow velocity, making organic loading rate (OLR) greater than 1.0 kg COD/m 3 .d.<br />
A Biomass Granulati<strong>on</strong> Index (BGI) has been framed based <strong>on</strong> mixing in the sludge bed, induced due to<br />
biogas and superficial upflow velocity of wastewater in UASB reactors. Based up<strong>on</strong> the above studies, it is<br />
c<strong>on</strong>cluded that good granular sludge (percentage of granules more than 50%, w/w) can be developed in UASB<br />
reactor if BGI is maintained in the rage of 245 to 480.<br />
Three kinetic models namely, M<strong>on</strong>od, Grau sec<strong>on</strong>d-order, and Haldane model have been studied to predict<br />
the effluent COD c<strong>on</strong>centrati<strong>on</strong> at steady-state. The results indicate that Grau sec<strong>on</strong>d-order multicomp<strong>on</strong>ent<br />
substrate removal model fits well for estimates of kinetic coefficient in UASB reactors. The investigati<strong>on</strong> of<br />
n<strong>on</strong>linear regressi<strong>on</strong> using different error functi<strong>on</strong>s as well as predicti<strong>on</strong> analysis reveals associati<strong>on</strong> of errors<br />
with the linearized forms of M<strong>on</strong>od model used for evaluating the kinetic coefficients. Hence, it is advisable to<br />
undertake n<strong>on</strong>linear regressi<strong>on</strong> technique using different error functi<strong>on</strong>s in the determinati<strong>on</strong> of kinetic<br />
coefficients for M<strong>on</strong>od model.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 13
Microbial community structure in anaerobic degradati<strong>on</strong> of terephthalate and<br />
phenol<br />
by CHEN Chia-Lung (ccl9@np.edu.sg)<br />
Instituti<strong>on</strong>:<br />
Department of Civil Engineering, Nati<strong>on</strong>al University of Singapore<br />
New PhD C<strong>on</strong>tact:<br />
Ngee Ann Polytechnic<br />
Centre of Innovati<strong>on</strong> in Envir<strong>on</strong>mental & Water Technology<br />
Blk 34, #01-01, 535 Clementi Road, Singapore 599489<br />
+65-64607091 (office)<br />
+65-96757041 (mobile)<br />
ccl9@np.edu.sg<br />
chialung.chen@gmail.com<br />
Supervisors:<br />
Assoc. Prof. Wen-Tso LIU<br />
Department of Civil and Envir<strong>on</strong>mental Engineering, University of Illinois at Urbana-Champaign, USA;<br />
Divisi<strong>on</strong> of Envir<strong>on</strong>mental Science and Engineering, Nati<strong>on</strong>al University of Singapore, Singapore<br />
Prof. Ong Say Le<strong>on</strong>g<br />
Divisi<strong>on</strong> of Envir<strong>on</strong>mental Science and Engineering, Nati<strong>on</strong>al University of Singapore, Singapore<br />
Abstract:<br />
Microbial community structures in the anaerobic (methanogenic) biological processes treating terephthalate- and<br />
phenol-c<strong>on</strong>taining wastewaters were characterized using 16S rRNA gene-based molecular techniques. The<br />
overall results showed that the methanogenic microbial communities involved in terephthalate and phenol<br />
degradati<strong>on</strong> were temperature-dependent, and the main microbial populati<strong>on</strong>s were phylogenetically closely<br />
related. In additi<strong>on</strong>, phenol-degrading enrichment cultures can also degrade terephthalate and benzoate,<br />
suggesting that these phenol-degrading c<strong>on</strong>sortia could be used as the seeding sludge for a bioreactor treating<br />
terephthalate, or as a co-substrate to enrich terephthalate-degrading microbial c<strong>on</strong>sortia, shortening the reactor<br />
start-up time. Syntrophorhabdaceae (formerly known as Deltaproteobacteria group TA; oval-shaped),<br />
Pelotomaculum- (fat-rod, some of which may c<strong>on</strong>tain spherical spores at the central of cells), and<br />
Methanosaeta-related cells (filamentous bamboo-shaped or rods with flat-ends) were found as the most<br />
predominant microbial populati<strong>on</strong>s involved in anaerobic terephthalate and phenol degradati<strong>on</strong>.<br />
List of publicati<strong>on</strong>s:<br />
Chia-Lung Chen, Jer-Horng Wu, I-Cheng Tseng, Teh-Ming. Liang and Wen-Tso Liu. Characterizati<strong>on</strong> of active<br />
microbes in a full-scale anaerobic fluidized bed reactor treating phenolic wastewater. Microbes and<br />
Envir<strong>on</strong>ments (Accepted, published <strong>on</strong>line 25-Apr-2009).<br />
Chia-Lung Chen, Jer-Horng Wu and Wen-Tso Liu (2008). Identificati<strong>on</strong> of important microbial populati<strong>on</strong>s in<br />
the mesophilic and thermophilic phenol-degrading methanogenic c<strong>on</strong>sortia. Water Research 42, 1963-1976.<br />
Chia-Lung Chen, Hervé Macarie, Ignacio Ramirez, Alejandro Olmos, Say Le<strong>on</strong>g Ong, Oscar M<strong>on</strong>roy and Wen-<br />
Tso Liu. (2004). Microbial community structure in a thermophilic anaerobic hybrid reactor degrading<br />
terephthalate. Microbiology 150, 3429-3440.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
14 June 2009 <strong>Newsletter</strong>
Optimizati<strong>on</strong> of fermentati<strong>on</strong> c<strong>on</strong>diti<strong>on</strong>s in batch and c<strong>on</strong>tinuous hydrogen<br />
producti<strong>on</strong><br />
by Gustavo Dávila-Vázquez (gdv@ciatej.net.mx)<br />
Instituti<strong>on</strong>:<br />
Instituto Potosino de Investigación Científica y Tecnológica. División de Ciencias<br />
Ambientales. Camino a la Presa San José 2055. Lomas 4ª Sección. San Luis Potosí,<br />
SLP. México. 78216<br />
New PhD C<strong>on</strong>tact:<br />
Centro de Investigación y Asistencia en Tecnología y Diseño del Estado de Jalisco.<br />
Unidad de Tecnología Ambiental.<br />
Av. Normalistas 800.<br />
Colinas de la Normal. Guadalajara, Jal. México. 44270<br />
gdv@ciatej.net.mx<br />
gdv76@prodigy.net.mx<br />
Supervisors:<br />
Dr. Elías Razo-Flores and Dr. Ant<strong>on</strong>io de León-Rodríguez<br />
Abstract:<br />
Hydrogen (H 2 ) is seen as a future energy carrier. Because compared to hydrocarb<strong>on</strong>s, it c<strong>on</strong>tains 2.75-times<br />
more energy by weight, besides the fact that its combusti<strong>on</strong> <strong>on</strong>ly generates steam as by-product. H 2 can be also<br />
used for electricity generati<strong>on</strong> with the aid of fuel cells, without the producti<strong>on</strong> of greenhouse gases. Around the<br />
95% of the H 2 used in industry is now produced from hydrocarb<strong>on</strong>s, which makes this process unsustainable.<br />
On the other hand, biohydrogen (Bio-H 2 ) generated from biomass, is a sustainable energetic alternative which is<br />
also neutral in greenhouse gases emissi<strong>on</strong>. Some microorganisms are capable of produce Bio-H 2 under<br />
anaerobic c<strong>on</strong>diti<strong>on</strong>s, from a wide range of organic substrates. In this thesis, the producti<strong>on</strong> of Bio-H 2 was<br />
studied with glucose, lactose and cheese whey (CW) as substrates, in batch and c<strong>on</strong>tinuous experiments and<br />
heat-treated anaerobic granular sludge as inoculum. The effect of initial pH and initial substrate c<strong>on</strong>centrati<strong>on</strong> <strong>on</strong><br />
both the hydrogen molar yield (HMY) and volumetric Bio-H 2 producti<strong>on</strong> rate (VHPR) was studied for the three<br />
substrates in batch experiments. Both, higher HMY and VHPR obtained in batch experiments were found at<br />
higher initial pH than comm<strong>on</strong>ly reported as optima in the literature. Furthermore, CW was selected to assess<br />
Bio-H 2 producti<strong>on</strong> with two different media (A and B) due to the high HMY and VHPR obtained, and because<br />
CW is an industrial by-product. The microbial community analysis showed differences in the microorganisms<br />
present for the experiments with each medium. Clostridium and Enterobacter species dominated with the use of<br />
medium B, while experiments with medium A <strong>on</strong>ly showed the presence of a proteobacterium. C<strong>on</strong>sequently,<br />
the use of mineral medium B yielded around twice the VHPR than the obtained with medium A, while HMY<br />
had a slight increase with the use of medium B. Finally, a c<strong>on</strong>tinuous stirred tank reactor was operated for 65.6<br />
days using CW as substrate, supplemented with mineral medium B. Three hydraulic retenti<strong>on</strong> times (HRT: 10, 6<br />
and 4h) were tested attaining the highest VHPR at 6h. Moreover, four organic loading rates (OLR) were<br />
evaluated at a fixed HRT of 6h. The highest VHPR, 46.61 mmol H 2 /l/h and HMY of 2.8 mol H 2 /mol lactose<br />
were attained at an OLR of 138.6 g lactose/l/d. The dominant bacterial species at HRT of 10 and 6h bel<strong>on</strong>ged to<br />
the Clostridium genus. The VHPR obtained here in c<strong>on</strong>tinuous experiments is the highest reported for a stirred<br />
tank reactor inoculated with anaerobic granular sludge using LS as substrate. The enhancements of both HMY<br />
and VHPR are critical to assess the full-scale practical applicati<strong>on</strong> of fermentative processes, which are now<br />
c<strong>on</strong>sidered as potential primary generators of sustainable energy in the near future.<br />
List of publicati<strong>on</strong>s:<br />
Davila-Vazquez, G., et al. (2008). Fermentative biohydrogen producti<strong>on</strong>: Trends and perspectives. Rev Envir<strong>on</strong><br />
Sci Biotechnol. 7(1):27-45. http://dx.doi.org/10.1007/s11157-007-9122-7<br />
Davila-Vazquez, G., et al. (2008). Fermentative hydrogen producti<strong>on</strong> in batch experiments using lactose, cheese<br />
whey and glucose: Influence of initial substrate c<strong>on</strong>centrati<strong>on</strong> and pH. Int J Hydrogen Energy. 33(19):4989-<br />
4997. http://dx.doi.org/10.1016/j.ijhydene.2008.06.065<br />
Davila-Vazquez, G., et al. (2009). C<strong>on</strong>tinuous biohydrogen producti<strong>on</strong> using cheese whey: Improving the<br />
hydrogen producti<strong>on</strong> rate. Int J Hydrogen Energy. In press. http://dx.doi.org10.1016/j.ijhydene.2009.02.063<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 15
Operati<strong>on</strong> and modeling of anaerobic sequencing batch reactors (ASBR) in the<br />
treatment of complex effluents<br />
by Andrés D<strong>on</strong>oso-Bravo<br />
Instituti<strong>on</strong>:<br />
School of Biochemical Engineering, P<strong>on</strong>tificia Universidad Católica de Valparaíso<br />
New PhD C<strong>on</strong>tact:<br />
Postdoctoral Researcher<br />
Department of Chemical Engineering and Envir<strong>on</strong>mental Technology<br />
University of Valladolid. Spain<br />
Supervisor:<br />
Dr. Rolando Chamy<br />
Abstract:<br />
Anaerobic digesti<strong>on</strong> has become a c<strong>on</strong>solidated and sustainable technology due to its<br />
ec<strong>on</strong>omical and envir<strong>on</strong>mental benefits. Nowadays, anaerobic digesti<strong>on</strong> is applied in a<br />
wide variety of organic waste and wastewater and presents comparable advantages over c<strong>on</strong>venti<strong>on</strong>al aerobic<br />
processes. Several anaerobic reactors have been developed, mainly UASB, EGSB and CSTR reactors, however,<br />
new c<strong>on</strong>figurati<strong>on</strong>s are being developed and studied to increase the amount of waste treated by anaerobic<br />
digesti<strong>on</strong>. One of the most important features of the Anaerobic Sequencing Batch Reactors (ASBR) is its<br />
operati<strong>on</strong>al flexibility as a result of its operati<strong>on</strong>al variables that may be manipulated such as the reacti<strong>on</strong> time,<br />
the feeding time or the type of feeding.<br />
In this work, an Anaerobic Sequencing Batch Reactor (ASBR) has been operated for 8 m<strong>on</strong>ths to treat low<br />
strength sewage with high suspended organic matter c<strong>on</strong>tent simulating domestic wastewater. Three phases of<br />
operati<strong>on</strong> with increasing Organic Loading Rates (OLR) have been carried out: 0.4 (phase I), 0.8 (phase II) and<br />
1.2 kg COD/m 3·d (phase III). During the whole experimental period, adequate values of the stability parameters<br />
(pH, total alkalinity) were obtained. During phases I and II, the removal efficiencies of organic matter<br />
(expressed as total COD) and total suspended solids ranged between 50 and 60%. However, these values<br />
decreased to 15-25% in phase III, due to the less HRT the methanogenic biomass was washed out of the reactor<br />
Afterward, a two-phase anaerobic system using Anaerobic Sequencing Batch Reactors (ASBR) treating the<br />
same simulated wastewater, to optimize the activity of both populati<strong>on</strong>s was implemented. Two reactors in<br />
series were set, the first <strong>on</strong>e was hydrolytic/acidogenic, while the sec<strong>on</strong>d <strong>on</strong>e was a methanogenic. Instantaneous<br />
feeding was used in both reactors. This c<strong>on</strong>figurati<strong>on</strong> will promote solid removal reaching higher efficiencies.<br />
During the experiment, a 69% and 50% of removal efficiencies of total cod removal were obtained for a OLR of<br />
0.63 and 1.22 kgCOD/m 3·d, respectively. The Solubilized Organic Fracti<strong>on</strong> (SOF) was within a range of 0.3 -<br />
0.6 gCOD solubilized /gpCOD removed and an average <strong>on</strong> the Acidified Organic Fracti<strong>on</strong> (AOF) of 0.6 gCOD vfaproduced/gsCOD<br />
fed , produced in the hydrolytic-acidogenic reactor. These are good results c<strong>on</strong>sidering the low<br />
COD influent and the high fracti<strong>on</strong> level of solids c<strong>on</strong>tent. The methanogenic reactor presented VFA removal<br />
fracti<strong>on</strong> (VFARF) value between 0.4 – 0.6 gCOD vfa-removed /gCOD vfa-fed for the OLR of 0.63 and 1.22. An overall<br />
good behaviour of the system was achieved during the whole experimentati<strong>on</strong>, showing that the two-phase<br />
system was stable, robust and effective for simulated domestic wastewater by anaerobic digesti<strong>on</strong>.<br />
Then 2 anaerobic sequencing reactors were implemented assessing two operati<strong>on</strong> modalities batch and fedbatch,<br />
in the phenolic wastewater treatment using an unacclimated biomass was evaluated. It is important to note<br />
that many industries do not have a c<strong>on</strong>tinuous discharge of phenol in their effluents, though phenol may be<br />
released occasi<strong>on</strong>ally because of a seas<strong>on</strong>al change or abnormality in the upstream process. In these cases, it is<br />
necessary to acquire acclimated biomass or to utilize rapid biomass adaptati<strong>on</strong> in order to treat the effluent. The<br />
batch reactor showed a poor performance at 5 g/l of cod with a 10, 25 and 40% of the phenol cod, despite a<br />
readily co-substrate was used in the treatment. A fast adaptati<strong>on</strong> of the biomass was performed in the fed-batch<br />
reactor using phenol as the <strong>on</strong>ly carb<strong>on</strong> source, reaching a 100% of phenol removal in 10 days. The best results<br />
were obtained with a 400 mg/l (160 mg/l·d) after 40 days of operati<strong>on</strong> reaching over 95% of phenol removal.<br />
The phenol c<strong>on</strong>centrati<strong>on</strong> impaired the biomass settleability in both reactors, causing an important washout of<br />
biomass. A fed-batch modalities can be an alternative for the anaerobic treatment of phenolic wastewater.<br />
Finally, a model with 3 reacti<strong>on</strong>s and 2 populati<strong>on</strong>s was developed, implemented and validated with the<br />
experimental data previously obtained. A good correlati<strong>on</strong> between the simulated variables and the experimental<br />
data was obtained; hence this model might represent a potential tool to c<strong>on</strong>trol and predicti<strong>on</strong> purposes.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
16 June 2009 <strong>Newsletter</strong>
Study of the effect of process parameters <strong>on</strong> the thermophilic anaerobic<br />
digesti<strong>on</strong> of sewage sludge, evaluati<strong>on</strong> of a thermal sludge pre-treatment and<br />
overall energetic assessment<br />
by Ivet Ferrer (ivet.ferrer@upc.edu)<br />
C<strong>on</strong>tact:<br />
Secti<strong>on</strong> of Envir<strong>on</strong>mental and Sanitary Engineering<br />
Department of Hydraulic, Maritime and Envir<strong>on</strong>mental Engineering<br />
Technical University of Catal<strong>on</strong>ia (UPC)<br />
C/ Jordi Gir<strong>on</strong>a 1-3, Builing D1, 08034 Barcel<strong>on</strong>a, Spain<br />
Tel: +34 93 401 6463<br />
ivet.ferrer@upc.edu<br />
Supervisors:<br />
Xavier F<strong>on</strong>t<br />
Felícitas Vázquez<br />
Abstract:<br />
Energy c<strong>on</strong>sumpti<strong>on</strong> accounts for some 30 % of the total operating costs of intensive sewage treatment plants<br />
and, in c<strong>on</strong>venti<strong>on</strong>al <strong>on</strong>es, around 15-20 % of this energy is used in the sludge treatment line. Therefore,<br />
optimisati<strong>on</strong> of sludge management can c<strong>on</strong>tribute in the reducti<strong>on</strong> of wastewater treatment costs. Thermophilic<br />
anaerobic digesti<strong>on</strong> is more efficient than mesophilic digesti<strong>on</strong>, in terms of biogas producti<strong>on</strong>, volatile solids<br />
(VS) removal and pathogens destructi<strong>on</strong>. The process might be further accelerated by sludge pre-treatment. The<br />
aim of this PhD Thesis was to study the impact of process parameters <strong>on</strong> the thermophilic anaerobic digesti<strong>on</strong> of<br />
sludge, to evaluate the effect of implementing a low temperature pre-treatment step, and to assess alternative<br />
processes from an energy perspective.<br />
Two lab-scale reactors were operated for almost two years in order to study the effect of process<br />
temperature, sludge retenti<strong>on</strong> time (SRT), organic loading rate (OLR) and 70 ºC sludge pre-treatment. The<br />
results were assessed from an energy perspective, by means of theoretical energy balances; and compared to<br />
those obtained with other experimental data. A first order kinetic model was also used.<br />
According to the results, methane producti<strong>on</strong> rate increased with the OLR (i.e SRT and VS), although<br />
process unbalance was observed at 6 days SRT (OLR > 5 kg VS m 3 d -1 ). In order to prevent process failure,<br />
limit values may be: VFA (2.5 g L -1 ), acetate (0.5 g L -1 ), acetate/propi<strong>on</strong>ate (0.5), intermediate alkalinity (IA)<br />
(1.8 g CaCO 3 L -1 ), IA/partial alkalinity (0.9), IA/total alkalinity (0.5), CH 4 (55 %).<br />
The 70 ºC sludge pre-treatment promoted a rapid sludge solubilizati<strong>on</strong>, which was followed by a progressive<br />
VFA generati<strong>on</strong> after 24 h. Anaerobic digesti<strong>on</strong> of pre-treated sludge (9-48 h) increased biogas producti<strong>on</strong> by<br />
30-40 % working at 55 ºC with a SRT of 10 days.<br />
Theoretical energy balances suggest that thermophilic sludge digesti<strong>on</strong> would result in net energy producti<strong>on</strong><br />
provided that digesters with wall insulati<strong>on</strong> and with energy recovery from both the biogas produced and the<br />
effluent sludge are used. In this case, the energy efficiency would be similar for thermophilic digesters working<br />
at half the SRT (10-15 days) of mesophilic digesters (20-30 days), meaning that the sludge daily flow rate could<br />
be increased or the reactor volume reduced, with subsequent savings in sludge treatment costs. Furthermore,<br />
two-stage systems (70/55 ºC) may result in higher net energy producti<strong>on</strong> compared to single-stage systems (55<br />
ºC) at 10 days SRT.<br />
Keywords: Anaerobic digesti<strong>on</strong>, energy balance, sludge, thermal pre-treatment, thermophilic.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 17
Sulfate reducing biological processes in biofilms for metal precipitati<strong>on</strong><br />
by Marisol Gallegos García (mgg@ipicyt.edu.mx)<br />
Instituti<strong>on</strong>:<br />
Instituto Potosino de Investigación Científica y Tecnológica.<br />
División de Ciencias Ambientales.<br />
Camino a la Presa San José 2055. Lomas 4ª Sección.<br />
San Luis Potosí, SLP. México. 78216<br />
Supervisors:<br />
Dr. Elías Razo-Flores<br />
Dra. Mª. Lourdes Berenice Celis-García<br />
Abstract:<br />
The envir<strong>on</strong>ment c<strong>on</strong>taminati<strong>on</strong> by heavy metals is an important matter due to its negative impact over the<br />
public health, the envir<strong>on</strong>ment and the ec<strong>on</strong>omy. Sulfate reducti<strong>on</strong> has become and alternative for the treatment<br />
of wastewaters that c<strong>on</strong>tain heavy metals. The general objective of this work was to study the applicati<strong>on</strong> of<br />
biological sulfate reducti<strong>on</strong> processes in biofilm reactors for metal precipitati<strong>on</strong> and recovery of the metal<br />
sulfides in <strong>on</strong>e step. First of all, the competence between methanogens and sulfate reducers was studied in an<br />
UASB reactor that was operated for over 240 days, for the development of sulfate reducing biomass from a<br />
methanogenic granular sludge. The chemical oxygen demand (COD) removed by sulfate reducti<strong>on</strong> was 20% and<br />
the total sulfide c<strong>on</strong>centrati<strong>on</strong> reached in the reactor was 310 mg/L. The specific sulfate reducing and<br />
methanogenic activities of the granular sludge pointed out to the development of sulfate reducing bacteria<br />
(SRB). The presence of SRB that oxidize incompletely the substrate to acetate, allowed the permanence of<br />
methanogens that were not limited by substrate, and in c<strong>on</strong>sequence were not completely displaced by the SRB<br />
at the end of reactor operati<strong>on</strong>. Afterwards, a down-flow fluidized bed reactor (DFFB) was proposed for the<br />
precipitati<strong>on</strong> and recovery of metals. The DFFB reactor was operated c<strong>on</strong>tinuously during 320 days and<br />
precipitati<strong>on</strong> efficiencies over 99.0% of Fe, Zn and Cd were obtained. The recovered metal sulfides amounted to<br />
90% of the theoretical mass expected to be precipitated; pyrite (FeS), sphaleryte (ZnS) and greenockite (CdS)<br />
predominated in the precipitate. The metal loading rate did not affect the reactor performance even at pH values<br />
as low as 5.0. The COD removal efficiency was close to 54%, which suggested an incomplete substrate<br />
oxidati<strong>on</strong> by the immobilized SRB, this was c<strong>on</strong>firmed by the high c<strong>on</strong>centrati<strong>on</strong> of acetate in the effluent and<br />
the absence of alkalinity producti<strong>on</strong>. Finally, the development of a sulfate reducing biofilm able to oxidize<br />
completely the substrate was studied. To achieve this, a selecti<strong>on</strong> pressure by substrate was used; three different<br />
assays were carried out in the DFFB reactor that was fed with a mixture of acetate/lactate with the following<br />
ratios <strong>on</strong> a COD basis: 50/50, 80/20 and 90/10 during 21 days. The best biofilm performance in terms of COD<br />
removal efficiency (71%) and sulfide producti<strong>on</strong> rate (2.9 mg H 2 S/L-h) was obtained with the biofilm developed<br />
in the experiment with the 90/10 acetate/lactate ratio. With this biofilm, the reactor was operated c<strong>on</strong>tinuously<br />
110 days. When the pH in the fed was decreased to 4.0, any inhibitory effect was observed over the SRB, as the<br />
reactor performance showed which achieved COD and sulfate removal efficiencies of 80 and 42%, respectively.<br />
The alkalinity produced by the complete oxidati<strong>on</strong> of the substrate neutralized the influent pH, and maintained a<br />
pH of 7.0 within the reactor. This work is the first to report the precipitati<strong>on</strong> and recovery of metals as metal<br />
sulfides in <strong>on</strong>e step and the development, in a short period of time, of a SRB biofilm able to oxidize completely<br />
the substrate.<br />
Link to Thesis: http://www.ipicyt.edu.mx/storage-sipicyt/materialbiblioteca/GallegosGarc%edaMarisol.pdf<br />
List of publicati<strong>on</strong>s:<br />
Gallegos-García, M., et al. (2009). Precipitati<strong>on</strong> and recovery of metal sulfides from metal c<strong>on</strong>taining acidic<br />
wastewater in a sulfidogenic down-flow fluidized bed reactor. Biotechnol Bioeng. 102, 91-99.<br />
doi.wiley.com/10.1002/bit.22049<br />
Gallegos-García, M., et al. (2008). Competencia por sustrato durante el desarrollo de Biomasa sulfato reductora<br />
a partir de un lodo metanogénico en un reactor UASB. Sometido, a la Revista Internaci<strong>on</strong>al de<br />
C<strong>on</strong>taminación Ambiental.<br />
Gallegos-García, M., et al. (In preparati<strong>on</strong>). Formati<strong>on</strong> of a sulfate-reducing biofilm of complete oxidati<strong>on</strong> of the<br />
substrate for the treatment of a synthetic effluent with sulfate.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
18 June 2009 <strong>Newsletter</strong>
Characterizati<strong>on</strong> and treatment of grey water; opti<strong>on</strong>s for (re)use<br />
Instituti<strong>on</strong>:<br />
Sub-department of Envir<strong>on</strong>mental Technology<br />
Wageningen University<br />
Wageningen, The Netherlands<br />
Supervisors:<br />
Jules van Lier<br />
Grietje Zeeman<br />
by Lina Abu Ghunmi<br />
Abstract:<br />
In addressing the issues of water shortage and appropriate sanitati<strong>on</strong> in Jordan, domestic grey water treatment<br />
receives growing interest. Grey water comprises the domestic wastewater flows excluding waters associated<br />
with the toilet. The topics of c<strong>on</strong>cern for grey water are its characteristics, treatment opti<strong>on</strong>s and potentials for<br />
use after treatment. The overall objective of this thesis is to develop a c<strong>on</strong>cept for <strong>on</strong>-site treating grey water for<br />
agricultural usage, thus sustaining a recycling process of grey wastewater in arid climate countries, like Jordan.<br />
A review was made regarding the currently available grey water treatment technologies. In additi<strong>on</strong>, grey water<br />
was quantitatively and qualitatively characterized, and grey water reuse requirements including treatment, were<br />
analyzed. Biodegradability and biodegradati<strong>on</strong> rates of the grey water were investigated for selecting appropriate<br />
design and operati<strong>on</strong> criteria of the treatment technology to be developed. A low-tech semi-technical scale<br />
treatment system was tested to treat grey water discharges from a dormitory at the Jordan University campus.<br />
The treatment system was evaluated <strong>on</strong> obtained removal efficiencies and c<strong>on</strong>formity of the effluent to the<br />
Jordan guidelines for the use of reclaimed water in irrigati<strong>on</strong> schemes. Finally, the objectives, approaches and<br />
the results of each chapter are summarized and discussed together with the potentials of applying decentralised<br />
sanitati<strong>on</strong> and reuse (DeSaR) c<strong>on</strong>cepts in Jordan.<br />
Results show that storage and treatment are prerequisites for any type of grey water use. Grey water is<br />
aerobically and anaerobically biodegradable but the c<strong>on</strong>versi<strong>on</strong> rates are low. The core of the treatment c<strong>on</strong>cept<br />
c<strong>on</strong>sists of an integrated storage and anaerobic treatment unit, fed with a natural influent flow pattern in a downflow<br />
mode. In the proposed system, up to a <strong>on</strong>e day operati<strong>on</strong>al cycle is applied, i.e. a variable HRT 24 hours.<br />
The sec<strong>on</strong>d step c<strong>on</strong>sists of an aerobic post-treatment, mechanically aerated in a down-flow mode and a <strong>on</strong>e day<br />
operati<strong>on</strong>al cycle, i.e. 24 hours HRT. Both units need insulati<strong>on</strong> in the winter period. The final effluent, stable in<br />
winter and summer, meets the Jordanian standards for usage in restricted irrigati<strong>on</strong>. The achievable treatment<br />
efficiency for the CODtot is 44% in the anaerobic unit and 70% in the combined anaerobic-aerobic, unlike the<br />
high anaerobic and aerobic biodegradability in batch experiments, viz. 70 and 86%, respectively. The highest<br />
removal efficiency achieved was for the CODss fracti<strong>on</strong>, viz. 71% in the anaerobic and 85% in the combined<br />
system. Therefore, it is expected that the CODtot removal efficiency of the system can be improved, by<br />
enhancing the CODcol and CODdis, removal, i.e. applying filtrati<strong>on</strong> and/or adding chemicals such as<br />
adsorbents, coagulants and/or flocculants to the treatment units.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 19
Combined carb<strong>on</strong> and nitrogen removal in integrated anaerobic/anoxic sludge<br />
bed reactors for the treatment of domestic sewage<br />
by Ghada Nassri Kassab<br />
Instituti<strong>on</strong>: Sub-department of Envir<strong>on</strong>mental Technology, Wageningen University, The Netherlands<br />
Supervisors: Jules van Lier and Bram Klapwijk<br />
Abstract: The main objective of this research is to assess the applicability and effectiveness of integrating<br />
anaerobic digesti<strong>on</strong> and denitrificati<strong>on</strong> processes in a single sludge system. The integrated c<strong>on</strong>cept is of<br />
particular interest for the treatment of high-strength domestic wastewater and is accomplished by means of<br />
sequential anaerobic-aerobic systems. The anaerobic pre-treatment can c<strong>on</strong>sist of a single anaerobic stage or two<br />
anaerobic stages, c<strong>on</strong>diti<strong>on</strong>ed mainly by the wastewater characteristics, the prevailing ambient temperatures and<br />
the scale of applicati<strong>on</strong>. Effluent nitrogen level adjustments using treatment systems c<strong>on</strong>sisting of a single<br />
anaerobic stage followed by an aerobic stage, can be incorporated by circulating part of the nitrified aerobic<br />
effluent to the influent of the anaerobic stage, integrating denitrificati<strong>on</strong> and anaerobic digesti<strong>on</strong>. In the<br />
sequential treatment system c<strong>on</strong>sisting of two anaerobic stages followed by an aerobic stage, nitrogen level<br />
adjustments can be incorporated by partially circulating the nitrified aerobic effluent to the sec<strong>on</strong>dary anaerobic<br />
stage (methanogenic stage). The first part of this research is focused <strong>on</strong> studying the potentiality of integrating<br />
denitrificati<strong>on</strong> and methanogenesis processes in single stage UASB reactors operated with flocculent sludge,<br />
simulating the single anaerobic stage receiving circulated nitrified effluent. Operating a lab-scale UASB reactor<br />
<strong>on</strong> synthetic wastewater, simulating high-strength domestic wastewater, under integrated c<strong>on</strong>diti<strong>on</strong>s with a<br />
COD/NO 3 -N ratio of 23 resulted in 92% COD and 97% nitrate removal. Denitrificati<strong>on</strong> was the main nitrate<br />
reducti<strong>on</strong> pathway. Compared to operati<strong>on</strong> under strict anaerobic c<strong>on</strong>diti<strong>on</strong>s, methanogenesis reducti<strong>on</strong> up<strong>on</strong><br />
launching the integrated process coincided with reducti<strong>on</strong> of COD available for methane producti<strong>on</strong>. Thus,<br />
indicating that methane producti<strong>on</strong> in the UASB reactor was not distressed by the denitrificati<strong>on</strong> process<br />
inhibitory effects. This c<strong>on</strong>clusi<strong>on</strong> is compatible with results obtained from the operati<strong>on</strong> of a semi-technical<br />
UASB reactor <strong>on</strong> raw domestic wastewater supplemented with synthetic nitrate. In the latter reactor, integrated<br />
operati<strong>on</strong> at a COD/NO 3 -N ratio ranging between 20 and 38 didn’t result in significant reducti<strong>on</strong> in observed<br />
methanogenesis, if compared with operati<strong>on</strong> under strict anaerobic c<strong>on</strong>diti<strong>on</strong>s. This preservati<strong>on</strong> of<br />
methanogenesis can be attributed to two factors. Firstly, under integrated process c<strong>on</strong>diti<strong>on</strong>s, an increased<br />
degree of hydrolysis prevailed that apparently mitigated the reducti<strong>on</strong> in COD available for methane producti<strong>on</strong><br />
resulting from COD allocati<strong>on</strong> to nitrate reducti<strong>on</strong> processes. Sec<strong>on</strong>dly, the sludge specific methanogenic<br />
activity was preserved under integrated c<strong>on</strong>diti<strong>on</strong>s, most likely due to the fact that a substantial fracti<strong>on</strong> of the<br />
methanogenic biomass was shielded from the oxidized N-compounds in the interiors of the flocculent bio-film.<br />
Regarding nitrogen removal, nitrate was completely removed. However, it wasn’t completely denitrified, as 33%<br />
of applied nitrate was reduced via dissimilatory nitrate reducti<strong>on</strong> to amm<strong>on</strong>ium. This obviously decreases the<br />
efficiency of an integrated system in terms of achieving a high degree of nitrogen removal, at the prevailing<br />
range of COD/NO 3 -N ratio, i.e. 20-38. Most interestingly, integrated operati<strong>on</strong> didn’t lead to deteriorati<strong>on</strong> of the<br />
flocculent sludge settleability or dewaterability features. The sec<strong>on</strong>d part of this research is focused <strong>on</strong> studying<br />
the integrati<strong>on</strong> of methanogenesis and denitrificati<strong>on</strong> processes in EGSB reactors for the treatment of pre-settled<br />
domestic wastewater. The EGSB reactor simulates the sec<strong>on</strong>dary anaerobic stage receiving part of the nitrified<br />
effluent of the succeeding aerobic stage, within a treatment system c<strong>on</strong>sisting of two anaerobic stages followed<br />
by an aerobic stage. Two lab scale EGSB reactors were employed in the study; the first was operated under<br />
integrated denitrificati<strong>on</strong> and methanogenic processes, whereas the sec<strong>on</strong>d was operated under strict<br />
methanogenic c<strong>on</strong>diti<strong>on</strong>s to set a reference for assessing the impacts of integrated process operati<strong>on</strong>. Moreover,<br />
the study was carried in two successive periods, in which the applied upflow velocity in the first and sec<strong>on</strong>d<br />
periods was 4.5 m.h -1 and 8 m.h -1 , respectively. In the integrated reactor that was operated at a COD/NO 3 -N ratio<br />
of 20, during the two experimental periods, nitrate was approximately completely removed by means of the<br />
denitrificati<strong>on</strong> process. In the integrated reactor, the COD c<strong>on</strong>sumed in methane producti<strong>on</strong> was 67% and 69%<br />
of the COD available for its producti<strong>on</strong> during the first and sec<strong>on</strong>d period, respectively. Such low percentages<br />
are attributed to “integrated granules” washout of the reactor. This washout is attributed to the growth of<br />
denitrifiers in form of fluffy biofilm <strong>on</strong> the surface of granules which in turn deteriorated the granules’<br />
settleability. The liquid shear stress induced by the 4.5 m.h -1 and 8 m.h -1 up flow velocities was not enough to<br />
prevent accumulati<strong>on</strong> of the fluffy biofilm. Of practical interest is the preservati<strong>on</strong> of specific methanogenic<br />
activity in the sludge grown under integrated c<strong>on</strong>diti<strong>on</strong>s. Thus, if the encountered sludge detainment problems<br />
with integrated granules are resolved, EGSB reactors under integrated c<strong>on</strong>diti<strong>on</strong>s can be operated at OLRs<br />
comparable to those under strict methanogenic c<strong>on</strong>diti<strong>on</strong>s. Settleability of integrated granules can be<br />
substantially improved by periodic applicati<strong>on</strong> of excessive detachment forces induced either by periodic<br />
increase in upflow velocity or by periodic circulati<strong>on</strong> of the sludge bed from the bottom to the top of the reactor.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
20 June 2009 <strong>Newsletter</strong>
Research and design of small scale bioreactor<br />
by Mindaugas Kvasauskas<br />
Instituti<strong>on</strong>:<br />
Department of Envir<strong>on</strong>ment Protecti<strong>on</strong>, Vilnius Gediminas Technical University, Lithuania<br />
Supervisor:<br />
Pranas Baltrnas<br />
Abstract:<br />
Due to bad odour, organic waste accumulati<strong>on</strong> facilities should be kept apart from residential areas. A c<strong>on</strong>stantly<br />
increasing amount of organic waste makes it necessary to occupy areas of useful land. A possible technological<br />
soluti<strong>on</strong> to preventing odours and reducing organic waste amounts is using biodigesters for producing gas and<br />
for further using of the gas to generate energy. Also, anaerobic treatment of organic waste c<strong>on</strong>tributes to the<br />
fulfilment of the Kyoto Protocol requirements for the reducti<strong>on</strong> of greenhouse gas emissi<strong>on</strong>s and use of mineral<br />
fuel resources.<br />
In order to determine the case when the maximum qualitative and quantitative evolvement of biogas is<br />
possible under psychrophilic c<strong>on</strong>diti<strong>on</strong>s, extintive investigati<strong>on</strong>s of evolved biogas were carried out through the<br />
employment of different biodegradable wastes and their mixtures.<br />
The psychrophilic temperature (22±2ºC) was maintained in the 6 bioreactors of 220 l in volume. Gas-flow<br />
and biogas compositi<strong>on</strong> (CH 4 , H 2 S, O 2 ) were measured.<br />
The research was c<strong>on</strong>ducted in a number of stages. One-type organic waste was used in the first stage:<br />
wastewater treatment sludge (WTS), margarine producti<strong>on</strong> waste (MPW), fruit and vegetable waste (FV), hen<br />
manure (HM), pig manure (PM) and grain (G). The sec<strong>on</strong>d stage employed margarine producti<strong>on</strong> waste (MPW)<br />
mixtures with hen manure (HM) and wastewater treatment sludge (WTS). The third stage used meat waste<br />
(MW) mixtures with graminaceous waste (GW), wastewater treatment sludge (WTS) and pig manure (PM). The<br />
fourth stage used mixtures of hen manure (HM) and fruit and vegetable waste (FV), and pig manure (PM) and<br />
grain (G). The mixtures were made at ratios of 1:3, 1:1 and 3:1 by volume. Prior to the experiment, a substrate<br />
c<strong>on</strong>taining 10% of dry substance of its total mass was prepared.<br />
It was determined experimentally that the highest biogas producti<strong>on</strong> rate under psychrophilic c<strong>on</strong>diti<strong>on</strong>s<br />
when treating biodegradable waste of <strong>on</strong>e type can be obtained using pig manure, 33 l/m 3 d, and the smallest –<br />
treating margarine producti<strong>on</strong> waste, 14 l/m 3 d. The highest c<strong>on</strong>centrati<strong>on</strong> of methane was recorded when using<br />
pig manure (87.8%) and wastewater treatment sludge (86.4%), whereas the lowest – when using margarine<br />
producti<strong>on</strong> waste (4.8%). The highest biogas producti<strong>on</strong> rate under psychrophilic c<strong>on</strong>diti<strong>on</strong>s when treating<br />
biodegradable waste of two types can be obtained using a mixture of meat waste and pig manure 1:3, 34 l/m 3 d,<br />
and the smallest – treating a mixture of margarine producti<strong>on</strong> waste and wastewater treatment sludge 3:1, 8<br />
l/m 3 d. The highest c<strong>on</strong>centrati<strong>on</strong> of methane was recorded when using a mixture of pig manure and grain 3:1, i.<br />
e. 87.8%, whereas the lowest – when using a mixture of margarine producti<strong>on</strong> waste and poultry manure 3:1, i.<br />
e. 4.8%. Also it was established experimentally that the optimum period of keeping biomass in the bioreactor<br />
under psychrophilic c<strong>on</strong>diti<strong>on</strong>s is from 2 to 3 weeks.<br />
Only the data when CH4 c<strong>on</strong>centrati<strong>on</strong> in biogas reached 65% are given. The total energy value in kJ, recorded<br />
during the days of the experiment, when biogas was suitable for burning, as well as the medium energy value.<br />
The greatest amount of energy can be produced during anaerobic treatment of organic waste under<br />
psychrophilic c<strong>on</strong>diti<strong>on</strong>s from PM. The total energy value reaches 4696 kJ from 1 m 3 biomass per experiment<br />
time when CH 4 c<strong>on</strong>centrati<strong>on</strong> reached 65%, and the medium value – 294 kJ/m 3 . Good results were also achieved<br />
when using a PM and GW 3:1 mixture. The total energy value reaches 3278 kJ from 1 m 3 biomass per<br />
experiment time when CH 4 c<strong>on</strong>centrati<strong>on</strong> reached 65%, and the medium value – 234 kJ/m 3 .<br />
The lowest energy value under psychrophilic c<strong>on</strong>diti<strong>on</strong>s was obtained when using MPW and WTS 1:3. The<br />
total energy value reaches 1376 kJ (58% less than in the case of PM) and the medium value – 153 kJ/m 3 (35%<br />
less than in the case of PM).<br />
To intensify biogas producti<strong>on</strong> process, mezophylic or thermophilic temperature should be held in<br />
bioreactors. The improved bioreactors are suitable for efficient processing of different solid and liquid<br />
biodegradable wastes generating in agriculture, food industry and wastewater treatment plants.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 21
Improving stability of anaerobic digesters for animal waste treatment<br />
by Marcelo Loureiro Garcia (mlgarcia@rc.unesp.br)<br />
New PhD C<strong>on</strong>tact:<br />
Assistant Professor<br />
Universidade Estadual Paulista (UNESP)<br />
Instituto de Geociências e Ciências Exatas de Rio Claro<br />
Departamento de Petrologia e Metalogenia<br />
Av. 24/A, 1515. Bela Vista<br />
Rio Claro, SP 13506-900, Brasil<br />
Tel: +55 (19) 3526 2833<br />
mlgarcia@rc.unesp.br<br />
Supervisor:<br />
Largus (Lars) Angenent, PhD<br />
Associate Professor<br />
Biological and Envir<strong>on</strong>mental Engineering<br />
Cornell University<br />
214 Riley-Robb Hall<br />
Ithaca, NY 14853, USA<br />
Tel: +1-607-255-2480 Fax: +1-607-255-4080<br />
la249@cornell.edu<br />
Abstract:<br />
In countries where c<strong>on</strong>centrated animal feeding operati<strong>on</strong>s (CAFOs) are used, implementati<strong>on</strong> of animal waste<br />
treatment is desired for both envir<strong>on</strong>mental protecti<strong>on</strong> and energy recovery. The capability of anaerobic systems<br />
to produce large quantities of biogas from animal wastes has been dem<strong>on</strong>strated, however, a lack of knowledge<br />
<strong>on</strong> the microbial community structure exits. Four 5-liter anaerobic sequencing batch reactors (ASBRs) were<br />
operated over a period of 988 days to treat swine waste. Over the course of three distinct operating periods, the<br />
performance of the bioreactors was assessed with c<strong>on</strong>venti<strong>on</strong>al envir<strong>on</strong>mental engineering techniques, while<br />
archaeal and bacterial microbial communities were unraveled with molecular biology techniques. The bacterial<br />
community analyses did not show a significant difference between low- and high-amm<strong>on</strong>ia reactors for different<br />
temperatures at the phyla level, with Firmicutes and Bacteroidetes as the predominant bacterial phyla. Members<br />
of the family Methanosarcinaceae and of the order Methanomicrobiales predominated as acetoclastic and<br />
hydrogenotrophic methanogens, respectively. The performance of the anaerobic digesters was clearly affected<br />
by varying total amm<strong>on</strong>ium c<strong>on</strong>centrati<strong>on</strong>s and mesophilic temperatures, however, this did not result in a<br />
c<strong>on</strong>siderable microbial community shift. Carb<strong>on</strong> and energy sources outplayed toxicity effects of amm<strong>on</strong>ia and<br />
temperature c<strong>on</strong>straints of kinetics and thermodynamics in determining the microbial bioreactor communities.<br />
However, some changes in the community were found. For instance, a gene sequencing survey from a sample<br />
enriched with 13 C-acetate indicated an enhancement of sequences from the genus Pseudom<strong>on</strong>as (am<strong>on</strong>g other<br />
uncultured phyla), explaining the 25% methane that was generated via an alternative pathway: syntrophic<br />
acetate oxidati<strong>on</strong> (with GC-MS). This pathway <strong>on</strong>ly occurred at very high amm<strong>on</strong>ia c<strong>on</strong>centrati<strong>on</strong>s (5,200 total<br />
amm<strong>on</strong>ium-N (mg/L)), which prevented unstable c<strong>on</strong>diti<strong>on</strong>s in the bioreactors with high amm<strong>on</strong>ia levels. We<br />
showed that powerful molecular biology techniques are needed to m<strong>on</strong>itor incremental changes in the<br />
community structure that can have large effects <strong>on</strong> reactor stability.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
22 June 2009 <strong>Newsletter</strong>
Mesophilic Fermentative Hydrogen Producti<strong>on</strong> from Sewage Biosolids<br />
by Jaime Massanet-Nicolau (jmassane@glam.ac.uk)<br />
Instituti<strong>on</strong>:<br />
Sustainable Envir<strong>on</strong>ment Research Centre (SERC).<br />
Faculty of Health, Sport and Science<br />
University of Glamorgan<br />
P<strong>on</strong>typridd, CF37 1DL, UK<br />
Supervisor:<br />
Prof Richard Dinsdale<br />
Prof Alan Guwy<br />
Prof Andrew Wheatley<br />
Abstract:<br />
The increasing cost of fossil fuels, combined with c<strong>on</strong>cerns about their impact <strong>on</strong> our envir<strong>on</strong>ment has led to a<br />
renewed interest in hydrogen as a clean, sustainable, alternative energy vector. Using sewage biosolids as the<br />
substrate for fermentative hydrogen producti<strong>on</strong> offers several advantages over the use of other biomass sources.<br />
It is available at little or no cost and is abundant, being produced wherever there are human settlements, with 1.3<br />
milli<strong>on</strong> t<strong>on</strong>nes (dry solids) per year currently being produced in the U.K al<strong>on</strong>e.<br />
This research dem<strong>on</strong>strated the feasibility of hydrogen producti<strong>on</strong> from sewage biosolids via anaerobic<br />
fermentati<strong>on</strong>. To do this a number of issues specifically relating to the nature of sewage biosolids had to be<br />
addressed. Firstly, the solids c<strong>on</strong>tent and rheology made automatic feeding difficult. The feedstock also<br />
c<strong>on</strong>tained high levels of indigenous microorganisms and a high ratio of insoluble to soluble carbohydrate.<br />
To address these challenges, a novel reactor design using wide bore tubing and computer c<strong>on</strong>trolled pumping<br />
equipment was successfully used to c<strong>on</strong>struct a working c<strong>on</strong>tinuously fed bio-reactor. A combinati<strong>on</strong> of heat<br />
treatment at 70 o C for <strong>on</strong>e hour and pre-treatment with a commercially available food processing enzyme mixture<br />
was found to be the most efficient method of inactivating competing microorganisms and improving substrate<br />
quality.<br />
Hydrogen was successfully produced via batch fermentati<strong>on</strong> of primary sewage biosolids which had<br />
underg<strong>on</strong>e heat treatment and enzymatic digesti<strong>on</strong>. When fermentati<strong>on</strong> took place at pH 5.5 a peak hydrogen<br />
producti<strong>on</strong> rate of 3.75 cm 3 min -1 was observed. At this pH the hydrogen yield was 0.37 mol H 2 mol -1<br />
carbohydrate, equivalent to 18.14 L H 2 kg -1 dry solids. Fermentative hydrogen producti<strong>on</strong> from sewage biosolids<br />
was also dem<strong>on</strong>strated in a five litre, c<strong>on</strong>tinuously fed bio-reactor for the first time. A comparis<strong>on</strong> of different<br />
hydraulic retenti<strong>on</strong> times showed that hydrogen producti<strong>on</strong> was most stable at a HRT of 24 hours. A hydrogen<br />
producing fermenter was successfully linked to a methanogenic bio-reactor in a two stage digesti<strong>on</strong> process.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 23
Anaerobic digesti<strong>on</strong> in sustainable biomass chains<br />
Instituti<strong>on</strong>:<br />
Sub-department of Envir<strong>on</strong>mental Technology<br />
Wageningen University<br />
Wageningen, The Netherlands<br />
Supervisors:<br />
Jules van Lier<br />
Rudy Rabbinge<br />
by Claudia P. Pab<strong>on</strong> Pereira<br />
Abstract:<br />
This thesis evaluates the potential c<strong>on</strong>tributi<strong>on</strong> of anaerobic digesti<strong>on</strong> (AD) to the sustainability of biomass<br />
chains. Results provide insights in the technological potential to recover energy and valuable by-products from<br />
energy crops and residues, and evaluate biomass cascades involving AD technology for their feasibility and<br />
desirability. Embedding AD in biomass chains addresses current c<strong>on</strong>straints towards increased use of biomass<br />
for energy producti<strong>on</strong> c<strong>on</strong>sidering land competiti<strong>on</strong> and envir<strong>on</strong>mental polluti<strong>on</strong>. Within this panorama so far<br />
major advantages of AD to improve energy efficiency and closing material cycles have received a limited<br />
attenti<strong>on</strong>. As part of the experimental research an Oxitop® protocol was refined for screening plant material<br />
suitable for anaerobic digesti<strong>on</strong> based <strong>on</strong> their energy c<strong>on</strong>tent. Envir<strong>on</strong>mental factors influencing the test<br />
outcome are the use of NaOH pellets for CO 2 scavenging, substrate pretreatment, microbial culture, and type of<br />
buffer. The use of NaOH pellets and substarte pretreatments were most influential <strong>on</strong> the results. By means of<br />
the developed Oxitop® protocol the relati<strong>on</strong>ship between plant ligno-cellulosic compositi<strong>on</strong> and the biomethane<br />
potential (BMP) and hydrolysis rates was researched. The Acid Detergent Fibre (ADF) and the Neutral<br />
Detergent Fibre (NDF) as analyzed by the van Soest method were proposed as suitable plant characterizati<strong>on</strong><br />
techniques for predicting the biodegradability and hydrolysis c<strong>on</strong>stants. The biodegradability model developed<br />
was further used to predict the biodegradability of 114 European plant samples identifying interesting crops and<br />
crop residues suitable for anaerobic digesti<strong>on</strong>. Batch experiments <strong>on</strong> digestate quality showed an increase of 20-<br />
26% and 0-36% in solublised NH 4 + and PO 4 3- , respectively, after 2 m<strong>on</strong>ths of digesti<strong>on</strong>. The largest fracti<strong>on</strong>s of<br />
the inorganic nutrients were found in the liquid fracti<strong>on</strong> of the digestate, i.e. 80-92% NH 4 + and 65-74% PO 4 3- .<br />
Increase in manure c<strong>on</strong>tent in the mixture showed a positive effect in the methane producti<strong>on</strong> rate and the total<br />
amount of nutrients in the digestate.<br />
The added value of AD within different biomass cascades was evaluated using the sustainable development<br />
c<strong>on</strong>cept in a specified system boundary. The sensitivity analysis of the energy balance of an AD facility shows<br />
that heat losses become the most important energy loss when high value substrate such as energy maize are<br />
employed. In c<strong>on</strong>trast, when a low energy substrate such as manure is used, the indirect energy of the<br />
infrastructure facilities, become the most important energy input. A sustainability framework was proposed for<br />
evaluating the potential role of AD in biomass cascades applied for the Colombian situati<strong>on</strong>. Results show that<br />
producti<strong>on</strong> of bio-ethanol from cassava is <strong>on</strong>ly sustainable from an energy and greenhouse gas (GHG)<br />
perspective when energy recovery from the process residues, using AD, is part of the process. The exact<br />
outcome of the evaluati<strong>on</strong> largely depends <strong>on</strong> variables like substrate drying, type of fuel used and type of<br />
applied AD system. During the study of other biomass cascades the c<strong>on</strong>tributi<strong>on</strong> of by-products was shown to be<br />
crucial, c<strong>on</strong>stituting 41-68% of the sum of all energy flows. For oil palm, sugarcane, panelacane and cassava,<br />
the energy c<strong>on</strong>tributi<strong>on</strong> of the byproducts to the different biofuel systems fluctuates between 51-158, 122-290,<br />
71-170, and 36-71 GJ.ha -1 yr -1 , respectively. AD had also a positive impact <strong>on</strong> nutrient recovery and water<br />
savings in the studied chains. The energy, nutrient and water benefits were set in perspective by giving an<br />
indicati<strong>on</strong> <strong>on</strong> the ec<strong>on</strong>omic benefits and land savings potentially attainable under Colombian c<strong>on</strong>diti<strong>on</strong>s.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
24 June 2009 <strong>Newsletter</strong>
Modeling Microbial Diversity in Anaerobic Digesti<strong>on</strong><br />
by Ivan Ramírez (ramirezy@supagro.inra.fr)<br />
New PhD C<strong>on</strong>tact:<br />
Laboratoire de Biotechnologie de l'Envir<strong>on</strong>nement<br />
LBE-INRA Avenue des étangs - 11100 Narb<strong>on</strong>ne, France<br />
Tel: +33 468.425.151 - Fax: +33 468.425.160<br />
ramirezy@supagro.inra.fr<br />
Supervisor:<br />
Dr. Jean-Philippe Steyer<br />
Laboratoire de Biotechnologie de l'Envir<strong>on</strong>nement<br />
LBE-INRA Avenue des étangs - 11100 Narb<strong>on</strong>ne, France<br />
tel: +33 468.425.151 - Fax: +33 468.425.160<br />
steyer@supagro.inra.fr<br />
web: http://www.m<strong>on</strong>tpellier.inra.fr/narb<strong>on</strong>ne<br />
Abstract:<br />
This new century addresses several envir<strong>on</strong>mental challenges am<strong>on</strong>g which distributi<strong>on</strong> of drinking water,<br />
global warming and availability of new in substituti<strong>on</strong> of fossil fuels are of the most importance. Am<strong>on</strong>g other<br />
renewable sources, biogas producti<strong>on</strong> from wastes is particularly interesting. Moreover, a techno-ec<strong>on</strong>omical<br />
comparis<strong>on</strong> dem<strong>on</strong>strated the benefits of a two-step process (H 2 +CH 4 ) compared to the classical <strong>on</strong>e-step<br />
methane producti<strong>on</strong>. Ec<strong>on</strong>omic evaluati<strong>on</strong> of biogas plants has revealed that many plants can <strong>on</strong>ly survive<br />
ec<strong>on</strong>omically if special incentives are applied. Nowadays, it is thus necessary to find ways to optimize the<br />
biogas producti<strong>on</strong> in order to make biogas plants ec<strong>on</strong>omically viable with decreased or no subsidies.<br />
Optimizati<strong>on</strong> of the biogas process by advanced m<strong>on</strong>itoring and c<strong>on</strong>trol can undoubtedly lead to better ec<strong>on</strong>omy.<br />
Such strategies require, in general, the development of appropriate mathematical models, which adequately<br />
represent the main biological processes that take place. Moreover, experimental evidence is available suggesting<br />
that the structure and properties of a microbial community may be influenced by process operati<strong>on</strong> and <strong>on</strong> their<br />
turn also determine the reactor functi<strong>on</strong>ing. In order to adequately describe these phenomena, more detailed<br />
microbial diversity should be taken up in mathematical models. This was dem<strong>on</strong>strated in this work by<br />
extending the ADM1 model to describe microbial diversity between organisms of the same functi<strong>on</strong>al group.<br />
The developed model was further shown useful in assessing the relati<strong>on</strong>ship between reactor performance and<br />
microbial community structure in different c<strong>on</strong>diti<strong>on</strong>s: difference in reactor c<strong>on</strong>figurati<strong>on</strong>s, influents and load<br />
regimes, both in normal and abnormal situati<strong>on</strong>s. As engineered systems are often more manageable than largescale<br />
ecosystems, and because parallels between engineered envir<strong>on</strong>ments and other ecosystems exist, we<br />
showed in this work that the former was used to elucidate some unresolved microbial ecological issues.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 25
Bioaugmentati<strong>on</strong> for recovery of anaerobic digesters subjected to a toxicant<br />
by Anne E. Schauer-Giménez<br />
Instituti<strong>on</strong>:<br />
Marquette University, December 2008<br />
New PhD C<strong>on</strong>tact:<br />
Post-doctoral Fellow<br />
Marquette University<br />
Water Quality Center<br />
Milwaukee, WI (USA)<br />
Supervisor:<br />
Dr. Daniel H. Zitome<br />
Abstract:<br />
Traditi<strong>on</strong>ally, practiti<strong>on</strong>ers have c<strong>on</strong>sidered anaerobic methanogenic cultures as “black boxes” and have not paid<br />
c<strong>on</strong>siderable attenti<strong>on</strong> to the microorganisms. However, the methanogenic community is important because<br />
different populati<strong>on</strong>s may behave differently in terms of methane producti<strong>on</strong> rate or stability during process<br />
upset. The research presented in this dissertati<strong>on</strong> explored the diversity of Bacteria and Archaea communities in<br />
various methanogenic enrichment cultures.<br />
With the help of molecular techniques (PCR, cl<strong>on</strong>ing, restricti<strong>on</strong> digests, and sequencing), Bacteria and<br />
Archaea cl<strong>on</strong>e libraries were c<strong>on</strong>structed for four enrichment cultures herein referred to as C1, C2, C3, C4. The<br />
enrichment c<strong>on</strong>diti<strong>on</strong>s differed based up<strong>on</strong> substrates and oxygen fed, and were as follows: C1 – H 2 :CO 2 , C2 –<br />
H 2 :CO 2 + glucose, C3 – H 2 :CO 2 + air, and C4 – H 2 :CO 2 + glucose and air. It was hypothesized that the varied<br />
c<strong>on</strong>diti<strong>on</strong>s would have an effect <strong>on</strong> microbial community diversity.<br />
When comparing the enrichment cultures that received air versus those that did not, a shift in methanogen<br />
community occurred. In C1 and C2, Methanosaeta was the most dominant genus. On the other hand,<br />
Methanosaeta was not dominant in C4 and not found in any sequences in C3. Methanospirillum was the most<br />
comm<strong>on</strong> methanogen genus in C3. These results indicate that additi<strong>on</strong> of air had an effect <strong>on</strong> the methanogen<br />
community.<br />
Bioaugmentati<strong>on</strong>, the additi<strong>on</strong> of a specific microorganism or mixed culture to enhance a desired activity<br />
(e.g. methane producti<strong>on</strong> or COD reducti<strong>on</strong>), can potentially be used to increase the recovery rate of anaerobic<br />
wastewater treatment facilities after exposure to toxicants. In the work describe herein, cultures C2 and C4 were<br />
used to bioaugment upset anaerobic digesters. The bioaugmentati<strong>on</strong> investigati<strong>on</strong>s successfully dem<strong>on</strong>strated<br />
the ability of the bioaugmentati<strong>on</strong> culture to increase methane producti<strong>on</strong> and recovery rate of a stressed digester<br />
exposed to the toxicant, oxygen. Methane producti<strong>on</strong> increased an average of 47% in the bioaugmentati<strong>on</strong><br />
digesters as compared to the c<strong>on</strong>trols, which were not bioaugmented. Also, SCOD c<strong>on</strong>centrati<strong>on</strong>s in the<br />
bioaugmented digesters decreased below 2,000 mg/L 83 days so<strong>on</strong>er than the c<strong>on</strong>trols. Bioaugmentati<strong>on</strong> is a<br />
promising approach to help decrease the recovery time of anaerobic digesters exposed to a toxicant.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
26 June 2009 <strong>Newsletter</strong>
Effects of Macrolide Antimicrobials <strong>on</strong> Anaerobic Treatment Systems<br />
Instituti<strong>on</strong>:<br />
University of Illinois at Urbana-Champaign (USA)<br />
Supervisors:<br />
Lutgarde Raskin (advisor)<br />
Julie Zilles (co-advisor)<br />
Eberhard Morgenroth (co-advisor)<br />
by Toshio Shimada (TShimada@carollo.com)<br />
Abstract:<br />
Antimicrobials are used comm<strong>on</strong>ly in animal producti<strong>on</strong> facilities for treatment and preventi<strong>on</strong> of disease and as<br />
growth enhancers. An anaerobic sequencing batch reactor (ASBR) was operated with a synthetic, carbohydratebased<br />
wastewater to study the effects of tylosin, a macrolide antimicrobial comm<strong>on</strong>ly used in swine producti<strong>on</strong>,<br />
<strong>on</strong> treatment performance, microbial community structure, and development of antimicrobial resistance. The<br />
experimental period was divided into three c<strong>on</strong>secutive phases with different influent tylosin c<strong>on</strong>centrati<strong>on</strong>s (0,<br />
1.67, and 167 mg/L). The additi<strong>on</strong> of 1.67 mg/L tylosin to the reactor had negligible effects <strong>on</strong> total methane<br />
producti<strong>on</strong> and effluent chemical oxygen demand (COD), yet analyses of individual ASBR cycles revealed a<br />
decrease in the rates of methane producti<strong>on</strong> and propi<strong>on</strong>ate uptake. The additi<strong>on</strong> of 167 mg/L tylosin to the<br />
reactor resulted in a gradual decrease in methane producti<strong>on</strong> and the accumulati<strong>on</strong> of propi<strong>on</strong>ate and acetate.<br />
Batch tests indicated that the specific biogas producti<strong>on</strong> (SBP) with the substrate butyrate was completely<br />
inhibited in the presence of tylosin. Measurements of treatment performance together with phylogenetic and<br />
quantitative fluorescence in situ hybridizati<strong>on</strong> (FISH) analyses suggested that the additi<strong>on</strong> of 1.67 mg/L and 167<br />
mg/l of tylosin inhibited homoacetogenic bacteria, propi<strong>on</strong>ate oxidizing syntrophic bacteria, and aceticlastic<br />
methanogens. Tylosin directly inhibited these two bacterial populati<strong>on</strong>s, while inhibiti<strong>on</strong> of the methanogenic<br />
populati<strong>on</strong> was presumed to be indirect and was attributed to a decrease in the pH of the reactor.<br />
In additi<strong>on</strong> to evaluating the impact of tylosin <strong>on</strong> anaerobic treatment, the accumulati<strong>on</strong> and degradati<strong>on</strong> of<br />
storage compounds was studied in the glucose-fed ASBR. Total carbohydrate analysis showed that 26% of the<br />
glucose added to the reactor transiently accumulated within the biomass. 13C nuclear magnetic res<strong>on</strong>ance<br />
(NMR) analysis identified the main carbohydrate produced as trehalose (alpha-D-glucopyranosyl-(-Dglucopyranoside)).<br />
The Internati<strong>on</strong>al Water Associati<strong>on</strong> Anaerobic Digesti<strong>on</strong> Model No. 1 (ADM1) was<br />
modified to include microbial storage and hydrolysis of reserve carbohydrates, and tylosin liquid-solid mass<br />
transfer and inhibiti<strong>on</strong>. This modified model adequately described accumulati<strong>on</strong> and degradati<strong>on</strong> of storage<br />
compounds as well as the microbial populati<strong>on</strong> dynamic profiles observed in the ASBR. The modeling results<br />
c<strong>on</strong>firmed that tylosin inhibited saturated fatty acid beta-oxidizing syntrophic bacteria and suggested inhibiti<strong>on</strong><br />
of fermentative bacteria resulting in unfavorable effects <strong>on</strong> methanogenesis.<br />
Keywords:: ADM1, anaerobic, macrolide, methanogenesis, storage, SBR, tylosin<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 27
Development of High-Rate Anaerobic Granular Sludge Bed Process for Low<br />
Strength Wastewater Treatment at Low Temperature<br />
by Wilasinee Yoochatchaval (wilasinee.y@nies.go.jp)<br />
New PhD C<strong>on</strong>tact:<br />
Post doctoral researcher, Water and Soil Envir<strong>on</strong>ment divisi<strong>on</strong>,<br />
Nati<strong>on</strong>al Institute for Envir<strong>on</strong>mental Studies, 16-2 Onogawa,<br />
Tsukuba, Ibaraki, Japan 305-8506<br />
Email: wilasinee.y@nies.go.jp, wilasinee_y@hotmail.com<br />
Supervisors:<br />
Dr. Kazuaki Syutsubo, Senior Researcher of Nati<strong>on</strong>al Institute for Envir<strong>on</strong>mental<br />
Studies, Japan<br />
Dr. Takashi Yamaguchi, Associate Professor of Nagaoka University of Technology,<br />
Japan<br />
Dr. Hideki Harada, Professor of Tohoku University, Japan<br />
Abstract:<br />
In this study, the anaerobic granular sludge process and its operati<strong>on</strong> mode were established for efficienttreatment<br />
of the low strength wastewater at low temperature. First of all, the feasibility of an expanded granular<br />
sludge bed (EGSB) reactor for low strength wastewater with 0.6-0.8 g COD/L was tested at 20°C. In this<br />
process, methanogenic granular sludge was used as seed and recirculati<strong>on</strong> of effluent was made to fluidize the<br />
sludge bed. As a result, sludge retenti<strong>on</strong> in this process was very well (over 40 days). C<strong>on</strong>sequently, this process<br />
was possible to achieve high rate treatment of low strength wastewater at hydraulic retenti<strong>on</strong> time of 1.5 h with<br />
COD loading rate of 12.8 kg COD/m 3 /day.<br />
The influence of decreasing in the temperature and the organic c<strong>on</strong>centrati<strong>on</strong> of the wastewater was<br />
evaluated in lab-scale EGSB reactor. The reactor exhibited sufficient COD removal efficiency until 10°C<br />
operati<strong>on</strong> due to the good-microbial adaptati<strong>on</strong> of granular sludge at low temperature. The significant increase<br />
of hydrogen-fed methanogenic activity between test temperatures of 15°C and 20°C was observed. At this time,<br />
proliferati<strong>on</strong> of psychrotolerant methanogen (hydrogen utilizing Methanospirillum spp.) in the retained sludge<br />
was c<strong>on</strong>firmed. On the other hand, decrease of organic c<strong>on</strong>centrati<strong>on</strong> of wastewater (from 0.8 to 0.4 gCOD/L)<br />
has caused the deteriorati<strong>on</strong> of organic removal efficiency and physical property of retained sludge due to the<br />
inactivati<strong>on</strong> of anaerobic bacteria. To solve this problem, new operati<strong>on</strong>al technology was proposed. C<strong>on</strong>trol of<br />
ORP of influent and intermittent the effluent recirculati<strong>on</strong> are possible to active the microbial activity of<br />
methanogens in the retained sludge.<br />
To clarify the effect of sucrose c<strong>on</strong>tent of fed-wastewater <strong>on</strong> the physico-microbial characteristics of<br />
granular sludge, we operated two reactors at 20°C by sucrose based wastewater (sucrose, 90% of COD) and<br />
volatile fatty acid based wastewater (sucrose, 0% of COD). Sucrose founded much negatives effects <strong>on</strong> the<br />
granular sludge physical properties and microbial properties (bulking and wash out of retained sludge due to the<br />
overgrowth of acidogens) at low temperature c<strong>on</strong>diti<strong>on</strong>.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
28 June 2009 <strong>Newsletter</strong>
ONGOING <strong>ANAEROBIC</strong> <strong>DIGESTION</strong> PROJECTS<br />
The Wales Centre of Excellence for Anaerobic Digesti<strong>on</strong> was established in 2008 at the University of<br />
Glamorgan, Wales, UK. The Centre is Directed by Dr Sandra Esteves and was created to assist with the creati<strong>on</strong><br />
of an infrastructure of AD plants in Wales to treat municipal food wastes and other biodegradable commercial<br />
and industrial wastes.<br />
Building <strong>on</strong> the c<strong>on</strong>siderable research experience developed over the past 40 years in the Sustainable<br />
Envir<strong>on</strong>ment Research Centre at the University of Glamorgan, the Centre of Excellence represents an effective<br />
means of using this expertise to support the growth of an AD industry in Wales and the UK.<br />
The Centre of Excellence has a mandate to provide two key roles in Wales. Firstly the Centre is working<br />
towards removing barriers to implementing AD caused by a lack of understanding of the technology. This will<br />
be achieved through a programme of awareness raising and provisi<strong>on</strong> of impartial informati<strong>on</strong> and advice. The<br />
Centre has already engaged with key policy and regulatory stakeholders including local authority planning<br />
authorities, the Envir<strong>on</strong>ment Agency and government procurement teams.<br />
Sec<strong>on</strong>dly, the Centre of Excellence is providing technical assistance and guidance to those directly involved<br />
in establishing AD plants within Wales. This ranges from pre-feasibility discussi<strong>on</strong>s, delivery of feasibility<br />
studies through to substrate and digestate characterisati<strong>on</strong>, biogas potentials and l<strong>on</strong>ger term pilot scale studies<br />
undertaken at the Centre’s laboratory facility.<br />
Centre Director Dr Sandra Esteves says “Anaerobic digesti<strong>on</strong> will, over a<br />
relatively short timescale, become a key waste management and bio-energy<br />
generati<strong>on</strong> technology in Wales and the UK. The Wales Centre of Excellence for<br />
Anaerobic Digesti<strong>on</strong> has been created to help those implementing, regulating<br />
and utilising the technology to maximise the envir<strong>on</strong>mental and ec<strong>on</strong>omic<br />
benefits to Wales. The Centre should ensure that this is achieved through the<br />
development of an integrated and technically robust infrastructure and a l<strong>on</strong>g<br />
term plan to support the management of these facilities <strong>on</strong>ce in place.”<br />
Funding to establish the Centre has been provided by the Welsh Assembly<br />
Government.<br />
For further informati<strong>on</strong> please c<strong>on</strong>tact:<br />
Dr Sandra Esteves (sesteves@glam.ac.uk) Tel. +44(0)1443 624130.<br />
or visit: www.walesadcentre.org.uk<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 29
The PROBIOGAS Project<br />
The objective of the PROBIOGAS project is to develop sustainable systems of producti<strong>on</strong> and use of biogas in<br />
agro-industrial areas, the dem<strong>on</strong>strati<strong>on</strong> of its viability and its promoti<strong>on</strong> in Spain. The project has been<br />
c<strong>on</strong>sidered by the Ministry of Science and Innovati<strong>on</strong> both singular and strategic, having received funds from<br />
the Ministry itself and from the European Regi<strong>on</strong>al Development Fund (ERDF). The project began at the end of<br />
2007 and will finish in 2010. The project has a total eligible budget of 6.7M€ and has received ec<strong>on</strong>omical<br />
support like grants and refund anticipati<strong>on</strong>s loans.<br />
The activities of this project are centered in biogas obtained from wastes of agro-industrial origin (animal<br />
farms, agriculture, agro-industry, food industries, bioenergy industries, etc.); landfill gas and biogas originating<br />
from urban wastewater purificati<strong>on</strong> stati<strong>on</strong>s are not c<strong>on</strong>sidered.<br />
In additi<strong>on</strong>, all the studied techniques of anaerobic digesti<strong>on</strong> in the project always apply the c<strong>on</strong>cept of "codigesti<strong>on</strong>"<br />
(joint treatment of organic wastes of different origin and compositi<strong>on</strong>). In PROBIOGÁS the codigesti<strong>on</strong><br />
of combinati<strong>on</strong>s of the most important agro-industrial wastes in Spain will be studied.<br />
The project c<strong>on</strong>sists of twelve inter-related subprojects, which<br />
have their own specific objectives, although they share the comm<strong>on</strong><br />
objective of PROBIOGAS. Thus, part of these subprojects will<br />
involve an investigati<strong>on</strong> into the improvement of the producti<strong>on</strong><br />
systems of biogas based <strong>on</strong> the anaerobic co-digesti<strong>on</strong> of the more<br />
frequent agro-industrial wastes in Spain. Others will investigate ways<br />
of improving the agr<strong>on</strong>omic use of the digestate in traditi<strong>on</strong>al and<br />
power cultures. Also, a study of the viability of the possible uses of<br />
biogas in vehicles, facilities of co-generati<strong>on</strong>, microturbines and fuel<br />
cells, as well as their introducti<strong>on</strong> in natural gas networks will be carried out. In additi<strong>on</strong>, seven acti<strong>on</strong>s of<br />
technological dem<strong>on</strong>strati<strong>on</strong> including innovating acti<strong>on</strong>s will be made as much in biogas producti<strong>on</strong> techniques<br />
as in the use of the digestate and biogas.<br />
In this project there is ample participati<strong>on</strong> (28 partners), divided in companies (15) and research centers (13)<br />
and which, although they develop their activity in different sectors, share their interest in the advantage of<br />
producti<strong>on</strong> and use systems of biogas.<br />
The relati<strong>on</strong> of partners is as follows: ABANTIA, Energía y Medio Ambiente (AEMA), AINIA Centro<br />
Tecnológico, Purines Almazán S.L., Biogas Fuel Cell (BFC), CSIC-CEBAS, CESPA, Fundación CIDAUT,<br />
Centro de Investigaci<strong>on</strong>es Energéticas Medioambientales y Tecnológicas (CIEMAT), SAC Ganadera del Valle<br />
de los Pedroches (COVAP), Fundación Asturiana de la Energía (FAEN), Fundación Patrim<strong>on</strong>io Natural de<br />
Castilla y León (FNAT), Centro Tecnológico de Gestión Integral de Residuos Orgánicos (GIRO), S.A.T. San<br />
Ramón (GSR), GUASCOR, Instituto para la Diversificación y Ahorro de la Energía (IDAE), Universidad de<br />
León (IRENA UL), Instituto Valenciano de Investigaci<strong>on</strong>es Agrarias (IVIA), NATURGAS ENERGÍA S.A.,<br />
PROTECMA, FUNDACIÓN RURAL CAJA, Sociedade Galega do Medio Ambiente (SOGAMA), Unión<br />
Temporal de Empresas TETMA S.A. -URBASER S.A., Universidad de Barcel<strong>on</strong>a (UB), Universidad de Cádiz<br />
(UCA), Universidad Miguel Hernández (UMH), Universidad de Oviedo (UNIOVI), Universidad Politécnica de<br />
Valencia (UPV) and Universidade de Santiago de Compostela (USC).<br />
The coordinator of the project is AINIA, in the pers<strong>on</strong> of Mr. Andrés Pascual. For more informati<strong>on</strong>, see Web<br />
page: www.probiogas.es<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
30 June 2009 <strong>Newsletter</strong>
ANAMIX – Assessment of rheological behavior and mass transfer properties for the<br />
improvement of dry digesti<strong>on</strong> processes<br />
Methane fermentati<strong>on</strong> is a biological process c<strong>on</strong>verting organic matter into a methane-rich gas (biogas). It is<br />
mostly used for municipal and agricultural organic wastes, which c<strong>on</strong>stitute a valuable resource: the European<br />
producti<strong>on</strong> of biogas was equivalent to 5 milli<strong>on</strong> t<strong>on</strong>s of oil in 2006. Most systems used for municipal wastes<br />
today are called dry digesti<strong>on</strong> processes: they are more efficient and less water-c<strong>on</strong>suming than classical<br />
systems, but the mechanical structure of the digesti<strong>on</strong> medium is still ill-defined and difficult to c<strong>on</strong>trol at the<br />
industrial scale. The essence of the ANAMIX project is to answer to specific questi<strong>on</strong>s associated to dry<br />
digesti<strong>on</strong>, using new techniques and new approaches for the descripti<strong>on</strong> of dense and pasty media. It combines<br />
Process Engineering (rheology, mass transfer, mixing) and Life Science (microbial kinetics and ecosystem<br />
ecology) together to study the complex interacti<strong>on</strong>s occurring in dry digesti<strong>on</strong>, and to propose a model enabling<br />
the simulati<strong>on</strong> of the mechanisms. Our project is guided by a double expectati<strong>on</strong>: first, to improve our<br />
knowledge of basic mechanisms that take place in dry digesti<strong>on</strong> systems; Sec<strong>on</strong>d, to provide the tools for<br />
making the future industrial systems easier to design and to operate.<br />
Partnership:<br />
INSA Ly<strong>on</strong>, Laboratory for Civil and Envir<strong>on</strong>mental Engineering (http://lgcie.insa-ly<strong>on</strong>.fr/index.phpRub=1)<br />
INRA Narb<strong>on</strong>ne, Laboratoire de Biotechnologie de l’Envir<strong>on</strong>nement<br />
VALORGA INTERNATIONAL<br />
Coordinator: Pierre BUFFIERE – INSA de Ly<strong>on</strong> (pierre.buffiere@insa-ly<strong>on</strong>.fr)<br />
Financial support: 528,841 €, funded by the french Nati<strong>on</strong>al Research Agency (ANR), Bioenergy Call 2008.<br />
Dates: From December 2008, 36 m<strong>on</strong>ths<br />
Metal speciati<strong>on</strong> in anaerobic sludge digesters supplemented with trace nutrients to<br />
enhance biogas producti<strong>on</strong><br />
School of Civil Engineering and School of Geography, Earth and Envir<strong>on</strong>mental Sciences,<br />
University of Birmingham, UK<br />
Supervisors: Dr CM Carliell-Marquet; Dr John Bridgeman; Dr Joanna Renshaw<br />
PhD students: Farryad Ishaq; Jimmy Roussel<br />
Project sp<strong>on</strong>sors: Engineering and Physical Sciences Research Council (UK) and Severn Trent Water Ltd.<br />
Anaerobic sludge digesters are metal-rich envir<strong>on</strong>ments. Metals coming into the digesters are rapidly<br />
precipitated as carb<strong>on</strong>ates, sulphides and, to a lesser extent, phosphates. Methanogenic bacteria have specific<br />
requirements for metals such as nickel, cobalt and ir<strong>on</strong>. Research has shown that supplementing anaerobic<br />
digesters with trace amounts of these required metals can increase the methane yield. Other research has<br />
highlighted the fragile balance that exists in these digesters between beneficial cati<strong>on</strong>s and ani<strong>on</strong>s (e.g. ir<strong>on</strong> and<br />
phosphate). For example, ir<strong>on</strong> supplementati<strong>on</strong> can increase methane producti<strong>on</strong> but excess ir<strong>on</strong> can cause<br />
phosphate to be precipitated, rendering it biologically unavailable, which could in turn decrease methane<br />
producti<strong>on</strong>.<br />
This introduces two key themes about which little are understood. Firstly, the issue of bioavailability: In what<br />
form is a metal bioavailable in an anaerobic digester In what form is a metal biologically unavailable<br />
Sec<strong>on</strong>dly, the issue of chemical equilibrium, i.e. that every change made to the inorganic balance of an anaerobic<br />
digester has multiple knock-<strong>on</strong> effects to cati<strong>on</strong>s and ani<strong>on</strong>s within the digester. Hence, the true effect of adding<br />
a metal supplement to increase methane yield is difficult to predict.<br />
This research investigates the effect of trace metal supplementati<strong>on</strong> <strong>on</strong> biochemical reacti<strong>on</strong> rates and metal<br />
speciati<strong>on</strong> in anaerobic sludge digesters. C<strong>on</strong>trolled laboratory digesti<strong>on</strong> experiments, e.g. acetate utilisati<strong>on</strong> rate<br />
or hydrolysis rate tests, are being used to measure the effect of trace nutrient supplements <strong>on</strong> different stages in<br />
the digesti<strong>on</strong> process. Metal fracti<strong>on</strong>ati<strong>on</strong> experiments <strong>on</strong> digesters and digested sludge, combined with<br />
equilibrium speciati<strong>on</strong> models, are being used to improve our understanding of metal speciati<strong>on</strong> and<br />
bioavailability in laboratory digesters supplemented with trace nutrients. An important outcome of this research<br />
is determining solubility products for compounds in a digested sludge matrix, as opposed to pure water, so that<br />
existing equilibrium speciati<strong>on</strong> models (eg. MINTEQA2) can be used to reliably predict speciati<strong>on</strong> scenarios in<br />
anaerobic sludge digesters.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 31
200 WTPD Thermal Dryer Using Landfill Gas as the Primary Fuel Goes Online In<br />
Manatee County Florida<br />
By: Alex L. M<strong>on</strong>roe, PE, Sr. Engineer/Scientist McKim & Creed, PA, 104 Gillespie Street, Fayetteville, NC<br />
28301 USA, (E-mail: am<strong>on</strong>roe@mckimcreed.com)<br />
INTRODUCTION<br />
Manatee County is located <strong>on</strong> the west coast of Florida and, like so many other areas in Florida, is experiencing<br />
rapid growth, which at times taxes the capacity of its wastewater utility infrastructure. The county owns and<br />
operates three water reclamati<strong>on</strong> facilities: the North, the Southeast and the Southwest. All have n<strong>on</strong>-discharge<br />
permits (total current capacity is 40.5 MGD). All the wastewater treated by the county’s WRFs is land-applied<br />
<strong>on</strong> residential sites, farmlands or golf courses. The following lists the dryer’s fuel requirements for the dryer<br />
purchased by the county.<br />
Table 1 Biosolids Fuel Requirements<br />
Dryer Fuel Natural Gas Landfill<br />
Gas<br />
High Heating Value, BTU/SCF 1,038 410<br />
Fuel Volume, CFH 19,269 48,700<br />
Dryer, Therms/hr 200 202<br />
Total Therms/hr (with 10% C<strong>on</strong>tingency) 220 222<br />
Since the landfill has an abundance of methane gas, the<br />
landfill gas was selected as the primary fuel while natural gas<br />
was selected as the backup fuel for the dryer. The county<br />
anticipates that it will save up to $1.7 milli<strong>on</strong> per year by using<br />
landfill gas as the primary fuel for the dryer.<br />
CONCLUSIONS AND LESSONS LEARNED<br />
The project has been <strong>on</strong>line since August of 2008 and is producing Class AA pellets of excepti<strong>on</strong>al quality.<br />
The main problem c<strong>on</strong>cerning the landfill gas was high carb<strong>on</strong> dioxide and nitrogen emissi<strong>on</strong>s from the<br />
dryer that were in violati<strong>on</strong> of the Clean Air Act. To overcome this problem, the county elected to install a<br />
thermal oxidizer to treat the emissi<strong>on</strong>s from the dryer. Natural gas had to be used to power the thermal oxidizer<br />
due to the variability in the quality of the landfill gas since the landfill gas was not scrubbed to remove<br />
c<strong>on</strong>taminants. Another problem that had to be overcome due to the varying quality of the landfill gas resulted in<br />
natural gas having to be used with the landfill gas to provide optimum drying capacity. The ratio of landfill gas<br />
to natural gas turned out to be 70 percent landfill gas and 30 percent natural gas. This reduced the anticipated<br />
savings in the cost for natural gas.<br />
The biosolids generated by the county is meeting the State of Florida’s Class AA biosolids criteria following<br />
the drying process. The county intends to use the pellets from the dryer as a soil amendment for the daily cover<br />
at the landfill, and plans to sell the pellets to local farms and residents as a fertilizer. The savings over natural<br />
gas will also provide the county a payback for the capital cost of the dryer over an eight- to ten-year period.<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
32 June 2009 <strong>Newsletter</strong>
<strong>ANAEROBIC</strong> URL SITES<br />
Teaching, awareness and training sites<br />
www.uasb.org<br />
Anaerobic knowledge centres:<br />
www.ftns.wau.nl/lettinga-associates/<br />
www.walesadcentre.org.uk<br />
www. orstom.fr/loma<br />
www.enzyme.chem.msu.ru/ekbio/eng/index.html<br />
Anaerobic digesti<strong>on</strong> companies<br />
3R Ingeniería Ambiental SL<br />
ADI<br />
Aquatec Maxc<strong>on</strong><br />
Biotec<br />
Biotecs<br />
Biothane Systems Internati<strong>on</strong>al<br />
Biotim<br />
Ecomembrane<br />
Ecovati<strong>on</strong><br />
Entec Biogas GmbH<br />
Global Water Engineering<br />
Gr<strong>on</strong>tmij<br />
IBTech<br />
NewBio, Inc<br />
Ondeo Degrém<strong>on</strong>t<br />
Paques<br />
Proserpol<br />
Purac<br />
Rains<br />
Reva Enviro<br />
http://www.3r-ingenieria.es<br />
http://www.adi.ca<br />
http://www.aquatecmaxc<strong>on</strong>.com.au<br />
http://www.bio-tec.net<br />
http://www.biotecs.com.br<br />
http://www.biothane.com<br />
http://www.biotim.be<br />
http://www.ecomembrane.com<br />
http://www.ecovati<strong>on</strong>.com<br />
http://www.entec-biogas.at<br />
http://www.globalwaterengineering.com<br />
http://www.gr<strong>on</strong>tmij.nl<br />
http://www.ibtech.com.mx<br />
http://www.newbio.com<br />
http://www.degrem<strong>on</strong>t.fr<br />
http://www.paques.nl<br />
http://www.proserpol.com<br />
http://www.lackebywater.se/en<br />
http://www.rainsgroup.com<br />
http://www.revaenviro.com/index.htm<br />
Other sites with AD links:<br />
http://www.ad-nett.org/<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> Anaerobic Digesti<strong>on</strong><br />
June 2009 <strong>Newsletter</strong> 33