THERMOPHILIC ANAEROBIC CO-DIGESTION OF AGRO-WASTE AND WASTE ACTIVATED SLUDGE: INFLUENCE OF THE ORGANIC LOADING RATE. Pavan P. 1, Bolzonella D. 2, Mata-Alvarez.

Slides:



Advertisements
Similar presentations
EO TP3 SAMPLING WASTE DISPOSAL SYSTEMS.
Advertisements

Anaerobic Treatment of HTC Waste Water B. Wirth a,b, J. Mumme a, B. Erlach b a ) Leibniz Institute for Agricultural Engineering, APECS Junior Research.
TAPE Technology Assessment Protocol – Ecology Guidance for Evaluating Emerging Stormwater Treatment Technologies.
“Water Resources Management:
Assessing the Commercial Feasibility of Manure to Energy Systems
ANAEROBIC CO-DIGESTION OF ORGANIC FRACTION OF MUNICIPAL SOLID WASTE AND WASTE ACTIVATED SLUDGE AT DIFFERENT RATIOS A. FLOR, L. ARROJA, I. CAPELA Environment.
ABSTRACT The EU FP6 NEPTUNE project is related to the EU Water Framework Directive and the main goal is to develop new and optimize existing waste water.
AD101 – Nutrient Transformations, Nutrient Management, and Benefits Pius Ndegwa Nutrient Management & Air Quality Specialist Biological Systems Engineering.
Effect of post digestion temperature on serial CSTR biogas reactors Kanokwan Boe, Dimitar Karakashev, Eric Trably and Irini Angelidaki Institute of Environment.
Co-digestion of manure with straw and perennial grasses Henrik Bjarne Møller, Department of Engineering, Aarhus University, Denmark.
Part III Solid Waste Engineering
Anaerobic Digestion: Biomass to Bioenergy Douglas W. Hamilton, Ph.D., P.E. Associate Professor, Biosystems and Agricultural Engineering Waste Management.
BIOCHAIN WORKSHOP 2014 JAN27-29 Characterisation of the organic pools in biomass and the related biochemical methane potential (BMP) Ali Heidarzadeh January.
Humberto Carlos Ruggeri Frederico de Almeida Lage Filho Mônica Medeiros Roque Passos Piveli Utilization of Shallow Ponds for Ammonia Nitrogen Removal from.
Sludge Happens. Louise Heffernan Metropolitan Council Environmental Services Empire Wastewater Treatment Plant Anaerobic Digester Pilot Project.
Reducing the Amount of Waste Activated Sludge Sara Schmidt CE 479 December 6, 2006.
Aare Kuusik, E. Loigu, O. Sokk, Argo Kuusik Estonia
Concept and Experiences of wastewater treatment In Cakung Slaughterhouse PD Dharma Jaya PUSAT PENGKAJIAN DAN PENERAPAN TEKNOLOGI LINGKUNGAN Badan Pengkajian.
The Swedish Water Experience We offer Swedish water purification knowhow, management and treatment plant construction 1.Background 2.How we work 3.What.
Biogas Production for Energy in Germany -Residues from Food Industry- Prof. Dr. Bernd Stephan University of Applied Science Bremerhaven, Germany.
EPROBIO Foggia 10 July 2010 Environmental Aspects of AD of Sewage Sludge.
Solid Recovered Fuel (SRF) production today and a Projection into the Future Presentation to the FEAD International Conference Bruges, 18 October 2002.
Anaerobic digestion of crop residues at low temperatures Irene Bohn LUND UNIVERSITY Department of Biotechnology.
Aquatic Plants and the Environment (SWES, ECOL, WFSc 474/574)
Selection of variables using FDA for the state identification of an Anaerobic UASB-UAF hybrid Pilot Plant, fed with winery effluents. M. Castellano 1,
– Opportunities Fuel From Food Waste Diane Nelsen, Jiaru Wu, Dave Stensel, John Ferguson, Heidi Gough, and Sally Brown University of Washington Anaerobic.
Increasing biogas production by thermal (70◦C) sludge pre- treatment prior to thermophilic anaerobic digestion Presented by Reem Satti.
A COST EFFECTIVE SOLUTION FOR SMALL – SCALE BIOMETHANE GENERATION Jaroslav KÁRA,Zdeněk PASTOREK,Oldřich MUŽÍK Research Institute of Agricultural Engineering,p.r.i.,
Making Waste Productive. Creating Energy from Waste.
食品生産における排水および廃棄物からのエネルギー回収プロセスのLCA —豆腐生産のケーススタディー
TREATMENT OF A DAIRY FARM WASTEWATER USING A PILOT SCALE UPFLOW ANAEROBIC SLUDGE BLANKET (UASB) PROCESS By Ashveen Deerpaul & Arvinda Kumar RAGEN.
High Rate Thermophilic Anaerobic Membrane Bioreactor for Wastewater Treatment by Kaushalya C. Wijekoon Master Student (st107821) EEM/SERD Wastewater Ξ.
As regards the VFA production, the trend was similar for both the mini-reactors with crops. During the first part of the study, VFA levels were high. This.
July 2013 TECHNICAL DIRECTOR ENVIRONMENTAL APPLICATIONS OF ACCELERATORS INDUSTRY CHALLENGES – SLUDGE TREATMENT MARTIN JOLLY.
Adjusting N:P ratios in liquid dairy manure through nitrification and chemical phosphorus removal to match crop fertilizer requirements Background Nutrient.
 Definition ◦ Scale up studies refers to the act of using results obtained from laboratory studies for designing a prototype and a pilot plant process;
Anaerobic Digestion and Biogas Terminology and designs.
Key stage 3 Group 4 project (KS3-G4P) KCCIS Science Department.
1 CE 548 II Fundamentals of Biological Treatment.
Anaerobic Co-digestion of Biomass for Methane Production : Recent Research Achievements Wei Wu CE 521 Today I am going to review recently published papers.
Discussion Increase in algal proportion in all the treatments with different inoculums recorded increase in biogas production. However the methane concentration.
WASTE WATER STATISTICS IN TURKEY Tülay AKICI Environmental Statistics Division State Institute of Statistics, TURKEY April,
Co-digestion of Hog Manure with Glycerol to Boost Biogas Production Oswald Wohlgemut (MSc) July 14, 2008.
Reuse and Recycle Aerobic and Anaerobic Treatment Composting
Anaerobic Treatment Anaerobik Arıtma Biyoteknolojisi
1 CEQAP CENTRE D’ENGINYERIA QUÍMICA AMBIENTAL I DEL PRODUCTE CEQAP’s main expertise is in the treatment of waste waters and solid wastes improvement of.
Anaerobic Digesters Key Considerations in Feasibility.
‹#› of [total number of slides] This project has received funding from the European Union’s Horizon 2020 research and innovation programme.
Nutrient recovery from anaerobic co-digestion of Chlorella vulgaris and waste activated sludge Michael Gordon 1, Tyler Radniecki PhD 2, Curtis Lajoie PhD.
Intensification of Agro and Food Industry Waste Biodegradation Process
Study of the U.S. Institute for the Environment Introduction to Water and Wastewater and Treatment Tuesday July 14, 2009.
Microbial O 2 Uptake During Sludge Biodegradation as Influenced by Material Physical Characteristics A. Mohajer 1, A. Tremier 2, S. Barrington 1, J. Martinez.
ERT 417 Waste Treatment In Bioprocess Industry Semester /2012 Huzairy Hassan School of Bioprocess Engineering UniMAP.
Prepared by: Pn. Hairul Nazirah Abdul Halim
INFILCO DEGREMONT, INC HIGH SOLID ANAEROBIC DIGESTION (HISAD)
BMP mesophilic trials were performed to Salix samples pre-treated by steam explosion at different temperatures (170 to 230 °C) and time (5, 10 and 15 mins.)
ERT 319 Industrial Waste Treatment Semester /2013 Huzairy Hassan School of Bioprocess Engineering UniMAP.
Nudging for Nature – Does it work? Contact: Dr. Christina Gravert University of Gothenburg, Department of Economics Tel:
Biomass energy, bioetanol, biodiesel and USW.. Obtaining electricity from MSW The current trend in the correct treatment of municipal solid waste generated.
Operational Conditions for Anaerobic Digesters
Removal efficiency of nitrate.
BUSINESS OPPORTUNITIES IN BIOENERGY
Ioannis Markidis WISE CDT PhD Student, University of Bath
Aare Kuusik, E. Loigu, O. Sokk, Argo Kuusik Estonia
Co-Digestion of Biodegradable Municipal Waste with Agricultural Residues - a Developing Concept and Market Tahir Mahmood a*, Zaki-ul-Zaman Asam b, Abdul-Sattar.
Potential activity of methanogens
Performance Analysis of Textile Industry Wastewater Treatment Plant with Physicochemical Characterizations Tadele Assefa Aragaw Faculty of Chemical and.
Characteristics of inoculum and feedstock
Centre for Rural Development and Technology IITD
ANAEROBIC DIGESTION OF FISH SLUDGE FOR BIOGAS PRODUCTION
Presentation transcript:

THERMOPHILIC ANAEROBIC CO-DIGESTION OF AGRO-WASTE AND WASTE ACTIVATED SLUDGE: INFLUENCE OF THE ORGANIC LOADING RATE. Pavan P. 1, Bolzonella D. 2, Mata-Alvarez J. 3, Cecchi F. 2 1 Department of Environmental Sciences, University of Venice. Calle Larga S. Marta 2137, Venice, Italy. 2 Department of Science and Technology, University of Verona. Strada Le Grazie, Verona, Italy. 3 Department of Chemical Engineering. University of Barcelona. Martí i Franquès 1, plta.6; Barcelona This poster deals with the thermophilic anaerobic co-digestion of solid agro-waste (mainly fruit and vegetable residuals from markets) and waste activated sludge originated from the biological treatment of municipal wastewater. A pilot scale digestor of 200 l working volume was used. Treating only wasted sludge, the initial Organic Loading Rate (OLR) was 0,7 kgTVS/m 3 d; then it was increased up to 4 and then to 6 kgTVS/m 3. Increasing the amount of OFMSW in the feeding, the gas production rate (GPR) raised from 0.12 to 3,12 m 3 /m 3 d and the Specific Gas Production (SGP) from 0.16 to 0.51 m 3 /kgTVS. Regarding the process behaviour, its stability was showed also in critical operatif conditions. Considering the option of retrofitting the anaerobic digesters of the existing sludge line in WWTPs, the obtained data clearly show the process feasibility. The main aim of the project is to firmly establish biogas technology as an economically attractive energy production process for both on and off-site use. In particular this work investigates the thermophilic co-digestion of WAS and market waste, also in order to evaluate its feasibilty on existing WWPT so to exploit the already avaiable structures existing in wastewater treatment plants operating within the UE. Abstract The aim of the research project The work carried out is part of a research considered in the VI framework program financially supported by the European Union, the “Cropgen” project (contract n. SES6-CT ). Experimental The used digester was a CSTR type, fed semicontinuously once a day and maintained at 55 ± 1 °C. The substrates were acquired daily from the wastewater treatment plant of Treviso (sludge) and from the municipal collection from fruit and vegetables markets Table 2 Substrates characteristics. Table 3. Main results of the research. Results While GPR shows a linear trends increasing OLR, SGP reached a plateau when OLR approached to 6 kgTVS/m 3 d. This was supposed to be the process limit for these conditions Table 1. Operational conditions used in the research. Biogas production (GPR) increase linearly with OLR, while the specific production reached a plateau when OLR approached to 6 kgTVS/m 3 d. This could be the process limit for these conditions; The OLR range from 2 to 6 kgTVS/m 3 d was investigated, observing a completely stable situation in all the conditions studied. pH and alkalinity values were always in typical ranges. The addition of increasing amount of waste in the feed lead to an improvement in buffer capacity of the digester (from 2700 to 7000 mg CaCO 3 /l); The comparison with mesophilic process shows that, at very low OLR (<1 kgTVS/m 3 d), there are no big difference between the two processes. However, things may be different when higher loading rate are applied. Other experimental work has to be done to investigate this aspect. Only during the last experimental run, the higher OLR caused a slight decrease of pH. Anyway the process seems to be not inhibited. Conclusion The alkalinity and VFA trends showed not problematical values for the process behaviour. The main results of this work are: