Production of Gaseous Fuels Pongamia Residue P M V Subbarao Professor Mechanical Engineering Department Indian Institute of Technology Delhi, New Delhi.

Slides:



Advertisements
Similar presentations
Chapter 4 module 3 Treatment of faeces by composting How should urine and faeces be treated for safe handling and reuse in crop cultivation? How can organic.
Advertisements

Anaerobic Digestion PAK RENEWABLE ENERGY
Anaerobic Digestion Overview David Schmidt University of Minnesota Department of Biosystems and Agricultural Engineering.
Gas out Biomas in Biomas out (Digestate) Biogas production.
BioEnergy Production from Food Waste
ANAEROBIC CO-DIGESTION OF ORGANIC FRACTION OF MUNICIPAL SOLID WASTE AND WASTE ACTIVATED SLUDGE AT DIFFERENT RATIOS A. FLOR, L. ARROJA, I. CAPELA Environment.
Biogas production from sugar beet silage
Biological waste water treatment
AD101 – Nutrient Transformations, Nutrient Management, and Benefits Pius Ndegwa Nutrient Management & Air Quality Specialist Biological Systems Engineering.
UNDERGRADUATE PROJECT’S PROPOSAL SEMESTER I 2012/2013 Biohydrogen Production from Palm Oil Mill Effluent (POME) Using Immobilized Mixed Culture (Sludge)
SFGP 2011 Lille 29 nov. – 1er déc – Biohydrogène : Etat de l’Art - S. Hiligsmann La production de biohydrogène à partir de substrats carbohydratés.
Anaerobic Digestion: Biomass to Bioenergy Douglas W. Hamilton, Ph.D., P.E. Associate Professor, Biosystems and Agricultural Engineering Waste Management.
Sludge Treatment and Disposal
FORTH/ICE-HT Work Package 2 Potential to produce Methane from extraction By-products Through Anaerobic Digestion FORTH G. Antonopoulou, K. Stamatelatou.
BIOCHAIN WORKSHOP 2014 JAN27-29 Characterisation of the organic pools in biomass and the related biochemical methane potential (BMP) Ali Heidarzadeh January.
SPECKY GIRLS PRODUCTION AND UTILIZATION OF METHANE SPECKY GIRLS PRODUCTION AND UTILIZATION OF METHANE Apryl Ng Noor Shafika Liao Swee Yun Sharmilla.
Proces imbalance in biogas plants. Henrik Bangsø Nielsen Biogasforum, seminar, 14/ Strategies for preventing breakdown and recovery of the biogas.
Environmetal problems related to manure management Greenhouse gas emission from manure stores.
Unit Food Science. Problem Area Processing Animal Products.
Biodegradation of organic pollutants in a composting environment in Mauritius Vijayalaxmi Jumnoodoo PhD Candidate Department of Chemical and Environmental.
Production of Gaseous Fuels Pongamia Residue - 2
Developing A Bio-gas based Carbon Neutral Engine Systems A Shift from Exploitation to Harvesting …. P M V Subbarao Professor Mechanical Engineering Department.
The use of structural nano and micro- filtration membrane as a confine bioreactor for microbial growth and extracellular digestive enzymes secretion By.
Hema Rughoonundun Research Week Outline of Presentation The MixAlco Process Introduction Sludge Materials and Methods Results Fermentation of sludge.
Decentralized Power Production in Rural Communities Andrea French Nicole Munguia November 21, 2006.
Increasing biogas production by thermal (70◦C) sludge pre- treatment prior to thermophilic anaerobic digestion Presented by Reem Satti.
Combustion AND Emissions Performance of syngas fuels derived from palm shell and POLYETHYLENE (PE) WASTE VIA CATALYTIC STEAM GASIFICATION Chaouki Ghenai.
Potential for Anaerobic Digestion of Crop Residues Ron Fleming & Malcolm MacAlpine (Ridgetown Campus of University of Guelph), Jim Todd (OMAFRA) CSBE
Production of Bio-Diesel Using Vegetable Oils P M V Subbarao Professor Mechanical Engineering Department Indian Institute of Technology Delhi, New Delhi.
The Anaerobic Digestion Process Andrew Gabriel and Tidasate Success.
Composting Process. The composting process results in the generation of heat, carbon dioxide and water. It results in the production of a stable compost.
ERT Biofuel BIO ETHANOL What, Why, How, How much, ….
Biological and Chemical Conversion Technologies
High Rate Thermophilic Anaerobic Membrane Bioreactor for Wastewater Treatment by Kaushalya C. Wijekoon Master Student (st107821) EEM/SERD Wastewater Ξ.
Anaerobic Digestion and Biogas Terminology and designs.
*Compost is a mixture of decayed organic materials decomposed by microorganisms in a warm, moist, and aerobic environment, releasing nutrients.
Anaerobic Co-digestion of Biomass for Methane Production : Recent Research Achievements Wei Wu CE 521 Today I am going to review recently published papers.
1 Fundamentals of On-Farm Composting Dr. Tom Glanville Agricultural & Biosystems Engineering Iowa State University.
Discussion Increase in algal proportion in all the treatments with different inoculums recorded increase in biogas production. However the methane concentration.
By Dr. Estee Yong Siek Ting
Reuse and Recycle Aerobic and Anaerobic Treatment Composting
Anaerobic Treatment Anaerobik Arıtma Biyoteknolojisi
1 Impact of Fluoride on Microorganisms in Wastewater Treatment Chandra Khatri, Valeria Ochoa and Reyes Sierra-Alvarez Department of Chemical and Environmental.
Opportunities of biogas production from dairy wastewater 2014 Kristóf Szabó.
Ethanol production from oil seed cakes and subsequent biological treatment of the remaining biomass for methane production by Chutima Swangkotchakorn (DTU)
Thermophilic anaerobic digestion of cattle manure and improving the hydrolysis yield Christel Kampman a, Tisse Jarlsvik b, Ulf Martinsson b, Susanna Petersson.
Macroscopic Description of Thermodynamic Systems P M V Subbarao Professor Mechanical Engineering Department I I T Delhi Virtual, Practicable, Economic.
Introduction to Environmental Engineering Dr. Kagan ERYURUK.
Adel Sharif University of Surrey
Nutrient recovery from anaerobic co-digestion of Chlorella vulgaris and waste activated sludge Michael Gordon 1, Tyler Radniecki PhD 2, Curtis Lajoie PhD.
BIOGAS REVIEW >>.
GRASS TO GAS – A BIO CNG PLANT PROPOSAL. Goal To start a company which can commercialize compressed biomethane as a substitute for fossil fuel derived.
Why are microbes important? Ecological Importance of Microbes (Applied and Environmental Microbiology Chapter 25)
Biogas Generation and its Utililities GUIDE :- Prof.A.M.Andhare Suyash Shukla Roll no:- 77 R.C.E.M.
Dr. Mohab Kamal. Sludge is produced from the treatment of wastewater in on-site (e.g. septic tank) and off-site (e.g. activated sludge) systems. This.
METHANOGENS AND BIOGAS. Methanogen An anaerobic microorganism that grows in the presence of carbon dioxide and produces methane gas. Methanogens are found.
Prepared by: Pn. Hairul Nazirah Abdul Halim
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.)
TYPES OF FERMENTATION.
Ioannis Markidis WISE CDT PhD Student, University of Bath
PB389 Integrated Solid Waste Management
Characteristics of inoculum and feedstock
Biogas Technology.
Biogas Jeff Hoover.
Design and Analysis of Biogas Register
Soil Organic Matter and Decomposition.
Centre for Rural Development and Technology IITD
Hinrich Uellendahl Section for Sustainable Biotechnology
Thermo chemistry of combustion
ANAEROBIC DIGESTION OF FISH SLUDGE FOR BIOGAS PRODUCTION
Presentation transcript:

Production of Gaseous Fuels Pongamia Residue P M V Subbarao Professor Mechanical Engineering Department Indian Institute of Technology Delhi, New Delhi Enhance the value of Fuel Energy ….

Pongamia Residue De-oiled cake – Rich Proteins Shells – Rich Cellulose

The Mind of Inventor Robert Boyle 17th-century natural philosopher, chemist, physicist, and inventor, also noted for his writings in theology. Scientific interest in the manufacturing of gas produced by the natural decomposition of organic matter, was first reported in the seventeenth century by Robert Boyle

Major Biological Events in Anaerobic Digestion hydrolytic bacteria

Fitness De-oiled Cakes for Hydrolysis Dry Pongamia Seed Cake Dry Jatropha Seed Cake Seed Cakes soaked in water

Ultimate Methane Potential of A Feed Material C a H b O c N d + X H 2 O  Y CH 4 + Z CO 2 + d NH 3 X = (4a – b + 2c + 3d)/4 Y = (4a + b – 2c – 3d)/8 Z = (4a – b + 2c + 3d)/8 Buswells equation Number of moles per mole of ’organic matter’

8 Ultimate Methane Potential B ult = 22.4 Nl/mol * (4a + b – 2c – 3d) mol 1000 l/m 3 8 * (12a + b + 16c + 14d)g [Nm 3 /g] B ult = * (1/2a + 1/8b – 1/4c – 3/8d) (12a + b + 16c + 14d) [Nm 3 /ton] [Nm 3 ] = one cubic meter of gas at standard state: 1 atm and 0 o C

Proximate analysis of feed materials (As Received Basis) Feed material Moisture content % Oil content % Total solids % Volatile solids % Non- volatile solids % Cattle dung 81.6Nil Jatropha oil seed cake Pongamia oil seed cake

Ultimate Analysis and carbon-nitrogen ratio : VM of feed materials Sr. No. Feed materialC (%)H (%)N (%)C/N ratio 1 Cattle Dung Jatropha oil seed cake Pongamia oil seed cake

1.Entire VS in feed material cannot be degraded. 2.The degradable material can only be completely converted to gas if a longer Hydraulic Retention Time (HRT) is used. 3.Part of the input material is inorganic (even though it may contain H). 4.The digestion process may not be optimal (inhibition). Practical Methane Production

The Inoculum Living element(s) of the parasite are able to contaminate a host feed material. It is the "primary inoculum" that enters the host and induces the degradation. The "secondary inoculum", resulting from the fructification of part of the contaminated host population, causes the spread in the host population

Preparation of Substrates and Determination of Their Properties  Mixing of de-oiled cake with Inoculum.  Dilution ratio and solids concentration.  To keep TS in between % and to maintain flow ability of substrates.  More surface for Bacterial hydrolysis.  An inoculation ratio of 1:10 used in laboratory experimentation.  With and with out cow dung.  A dilution ratio of 3:1 and 4:1 for jatropha cake  and, 3:1 and 3.5:1 for pongamia cake.

Preliminary Batch Biomethanation Study Experimental setup for batch biomethanation study Range of ambient temperature variation 24.5 to 35.1 °C Range of substrate temperature variation 24 to 34.5 °C Period of Experimental Study:15 th March 2006 to 12 th June 2006

Composition of prepared substrates and their C/N ratio, TS, VS and their dilution ratio [as received (live dilution ratio) and absolute dilution ratio (dry basis)] Sl. No. Treatment designation Substrate constituents Dilution ratio, Water : Cake C/N ratio Substrate concentration Cake, g Water, ml Dung, g Inoculum, g LiveAbsolute% TS% VS 11.0 DR [CD] :111.6: Jatropha Oil Cake Substrates 23.0 DR [5JC:0CD] :13.4: DR [5JC:1CD] :13.5: DR [5JC:2CD] :13.5: DR [5JC:3CD] :13.6: DR [5JC:4CD] :13.6: DR [5JC:5CD] :13.7: DR [5JC:0CD] :14.5: DR [5JC:1CD] :14.5: DR [5JC:2CD] :14.5: DR [5JC:3CD] :14.6: DR [5JC:4CD] :14.6: DR [5JC:5CD] :14.6:

16 Sl. No. Treatment designation Substrate constituents Dilution ratio, water : cake C/N ratio Substrate concentration Cake, g Water, ml Dung, g Inoculum, g LiveAbsolute% TS% VS Pongamia Oil Cake Substrates DR [5PC:0CD] :13.7: DR [5PC:1CD] :13.7: DR [5PC:2CD] :13.8: DR [5PC:3CD] :13.9: DR [5PC:4CD] :13.9: DR [5PC:5CD] :13.9: DR [5PC:0CD] :14.3: DR [5PC:1CD] :14.3: DR [5PC:2CD] :14.3: DR [5PC:3CD] :14.4: DR [5PC:4CD] :14.4: DR [5PC:5CD] :14.4: Continued… 16

17 Experimental Setup used for Preliminary Batch Study 17

Conclusions from Characterization of Feed Materials and Preliminary Batch Biomethanation Study  Low yield and very poor quality of biogas was observed during the preliminary batch biomethanation study.  A major challenge in biomethanation of these deoiled cakes is lacking of inherent bacteria like cattle dung.  Lack of these inherent bacteria demands a special attention for operation of digester with cake.  Other major deficiency of cake is the presence of long chain free fatty acids, which are prone to destroy the population of bacteria.  Thus the microbes present in cattle dung inoculum could not survive in new environment.  There may be a continuous drop in population of bacteria in the inoculum.

Need for Development of New Inoculums  The microbes present in cattle dung inoculums could not survive in deoiled cake-water environment.  The substrates of jatropha and pongamia oil cakes might have created a sudden and drastic change in environment for the bacterial activity resulting in their inhibition.  There was a continuous drop in population of bacteria in the inoculums.  This is due to effect of bacterial inhibition since the substrates were new for the bacteria present in the cattle dung inoculum.  This proves that production of effective (special) inoculum in a small aspirator bottles with little amount of initial inoculum (taken from a cattle dung digester) is not feasible.

Biogas plant (20 m 3 /d) capacity available at IIT Delhi 20

Development of Special Inoculum 20 m 3 /d BGPAbout 12 m 3 CD inoculum Feeding of pongamia oil cake in 3:1 DR for 15 days No feeding of CD before last 3 months Schedule I 2 kg pongamia oil cake with 6 kg water for 5 days Start of gas production Continued 5 kg pongamia oil cake with 15 kg water for 10 days Schedule II Drop in gas yield Increase in gas yield Constant gas yield (10-15 day) at 30 cm height 10 cm height 21 Biogas Plant before Feeding Started

Biogas Plant After Feeding of Oil Cake Slurry

Evolution of Microbes  This shows the adaptation of bacteria to the environment offered by new substrates possibly by developing into a suitable strain.  This acclimatization is due to fact that,  when the concentrations of inhibitory or toxic materials were slowly increased within the environment,  many microorganisms could rearrange their metabolic resources, thus overcoming the metabolic blockage produced by the normally inhibitory or toxic material.  However, sufficient time should be made available for this rearrangement to take place where there is drastic change in environment (feed material).  The slurry of the biogas plant stabilized with pongamia oil seed cake was used as inoculum for further studies.