Efgect of Cow Dung Inoculum on Biogas Generation from Anaerobic - - PowerPoint PPT Presentation

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Efgect of Cow Dung Inoculum on Biogas Generation from Anaerobic Digestion of Organic Fraction of Municipal Solid Waste A Case Study of India ATUL KUMAR INDIAN INSTITUTE OF TECHNOLOGY (INDIAN SCHOOL OF MINES) DHANBAD, INDIA 7 th


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Efgect of Cow Dung Inoculum on Biogas Generation from Anaerobic Digestion of Organic Fraction of Municipal Solid Waste – A Case Study of India ATUL KUMAR

INDIAN INSTITUTE OF TECHNOLOGY (INDIAN SCHOOL OF MINES) DHANBAD, INDIA 7th International Conference on Sustainable Solid Waste Management, 2019

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What are we going to learn today?

  • Motivation for this study
  • Objectives
  • Materials and methods
  • Key results
  • Conclusions

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Motivation for this study

  • One-third
  • f

total world food production gets wasted every year.

  • Most of the organic wastes meets with

the traditional disposal techniques.

  • Scarcity of suitable land for landfilling.
  • Stringent regulations.
  • Potent renewable energy source.
  • Reduce the environmental impacts.

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  • Fig. 1: Anaerobic digestion process
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Objectives

  • T
  • identify the optimum combination of OFMSW and CM

for effjcient anaerobic digestion.

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Materials and methods

  • Feedstock materials
  • Leftover food waste and other degradable wet organic waste.
  • The co-digestion substrate was cow dung (CM) collected from a farm.
  • Reactor Set-up
  • Aspirator glass bottles of capacity 1000 mL with bottom sampling port

were used.

  • The experiments were performed in batch.

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  • Fig. 2: Experimental set-up of the anaerobic batch reactor

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Reactor Set-up (Continue..)

  • The reactors were filled with four different substrate to inoculum ratio (0.5,

0.63, 0.75 and 1.0) based on VS contents.

  • The inoculum and substrate were thoroughly mixed in the blender before

being added to the reactor.

  • All the reactors were operated at mesophilic temperature (35 ± 1 °C).
  • Water displacement method was used for biogas production measurement at

a fixed time every day.

  • The other end of silicone tube was inserted in an inverted 50 ml graduated

measuring cylinder filled with water, whereas in duplicate it was 1.5 N NaOH solution.

  • The reactors were terminated at the end of 30th day.

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Analytical methods

  • The Characteristics of the collected samples were analysed in the

laboratory.

Table 1: Characteristics of feedstock materials Parameter OFMSW CM Moisture content (%) 81.2 84.4 pH 5.3 7.4 Total Solid (TS) (%) 18.8 15.6 Volatile Solid (VS) (% d.b.) 90 79.3 COD (mg/L) 79800 19600 Carbon, C (% d.b.) 45.12 37.34 Nitrogen, N (% d.b.) 1.58 3.03 C/N ratio 28.56 12.32

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Reactor Mixing ratio of OFMSW and CM (on VS basis) OFMSW (g VS/L) CM (g VS/L) Organic loading (g VS/L) R1

  • 10

10 R2 0.50 5 10 15 R3 0.63 6.3 10 16.3 R4 0.75 7.5 10 17.5 R5 1.00 10 10 20 Table 2: Combinations of feedstock in batch reactors

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Key results

Variation of pH in the reactors

  • During

hydrolysis, the substrates get converted into amino acids and fatty acids which lead to accumulation of volatile fatty acids (VFA) resulting in a decrease in pH of the reactor.

  • Till 12-15 days the pH in all the reactors

gradually decreases.

  • Due to CM as a co-substrate, the pH of the

reactors again increases which creates favourable environment for the methanogenic bacteria.

5 10 15 20 25 30 4 4,5 5 5,5 6 6,5 7 7,5 8 8,5

R1 R2 R3 R4 R5 Time (days) pH

  • Fig. 3: Variation of pH of the reactors

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Biogas generation

  • The maximum biogas production

was found in reactor R2.

  • The percentage of methane in the

generated biogas was 62%.

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R1 R2 R3 R4 R5 200 400 600 800 1000 1200 1400 1600 1800

Reactors B io g a s g en era tio n (m L )

  • Fig. 4: Biogas generated in the reactors
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12 5 10 15 20 25 30 200 400 600 800 1000 1200 1400 1600 1800 R1 R2 R3 R4 R5

Time (days) Cumulative biogas (mL)

  • Fig. 5: Cumulative biogas generation
  • The biogas production of 1594

mL at S/I ratio of 0.5, followed by 1301 mL at 0.63, 1152 mL at 0.75 and 1037 mL at 1.0.

  • The biogas generation was very

less from mono-digestion of CM (R1).

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Conclusions

  • The biogas yield in the different reactors are not very encouraging.
  • The maximum biogas yield of 106.27 mL/g VS was observed in reactor R2.
  • The order of biogas yield in all the reactors are R2>R3>R4>R5>R1.
  • The reason for lesser biogas production in all the reactors was due to the

drop in pH of the reactors at initial stage of the reaction.

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Acknowledgement: I want to thank Department of Science and Technology,

  • Govt. of India, for providing me funding opportunity for attending this conference.

Thank You & Questions?

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