Abstract:
Leather is one of the most prospective industries in Bangladesh .Out of the total 206
tanneries in Bangladesh 192 of them are located in Hazaribagh of Dhaka city. A
large amount of solid waste (even in lean season 69.1 ton/day according to 2006
survey of UNIDO) is generated daily by leather manufacturing process in this area
and crude disposal of this waste are creating serious hazard to the environment. An
attempt has been made to analyze the present status of Hazaribagh in terms of solid
waste management. Now it is prerequisite to develop an appropriate waste
management system of the tannery waste and for this it is obvious to manage each
fraction of the waste in a cost effective and environment friendly way. With rapid
depletion of conventional energy sources, the need to find an alternative, preferably
renewable, source of energy from waste is becoming increasingly important for the
sustainable development. A major portion of the solid wastes from leather industry is
fleshing, originates from animal tissue, which contains mainly fat and protein, and
residual chemicals such as lime and sulphide used in the unhairing process of beam
house operation.
Experimental results showed that fleshing contains a significant quantity of volatile
solids (including non-biodegradable fraction of volatile matter such as lignin,
82.57%VS) amenable for biodegradation. Further the characterization of fleshing
showed that it contains low C/N ratio (2.64) and high pH (10.99), these
characteristics were not suitable for using fleshing alone as substrate for anaerobic
digestion,for this reason different proportion of cowdung and domestic sewage were
used as co-substrate for optimum results. The study was carried out by using
different proportions of waste fleshing, cowdung and domestic sewage in four
different laboratory scale reactors carrying 6% total solid concentration. In all the
reactors fleshing and domestic sewage were mixed in 1:1ratio. Anaerobicdigestion
was carried out for 60 days of digestion period at room temperature 30°c ±3 and the
pH of the slurry was maintained by the process itself. The inoculums were
synthesized by the cowdung and water in the laboratory in the same environmental
condition taken for the study and sufficient active biomass was present there.For
thatthe start-up of the reactor was achieved easily.
The reactors were subjected to anaerobic digestion with an aim of developing an
appropriate technology for recovery of bioenergy from the tannery solid waste
fleshing. From the study it was observed thatamended fleshing with domestic sewage
when mixed with cowdung, the significant increase of gas production was
remarkable. The performances of the reactors were analyzed on the basis of volatile
solids destruction efficiency, specific gas yield, COD reduction rate and on methane
yield. Within four reactors the percentages of volatile solid destruction were between
42% to 52%, specific gas production were 0.401, 0.476, 0.239 and 0.288 l/g
respectively according to volatile solids fed and methane yieldwere achieved72%,
73%, 70% and 72% by volume respectively.COD reduction achieved in the test
reactors 48.02% 50.67%, 44.80% and 44.61% respectively. Further, the kinetic
analysis of the data revealed that first order kinetic model is adequate to describe the
co-digestion of animal tissue with cowdung and domestic sewage. On the basis of analysis of the performance of the reactors, it was evident that
amended fleshing is highly potential substrate for biogas generation and it was also
found that R2 reactor, where on the total solids (6%TS) of the slurry 75% of fleshing
with domestic sewage and 25% of cowdung were used, showed the optimum results
in terms of VS reduction (52%), specific gas yield (0.476 l/g) and methane yield
(73% by volume). For this reason, the standards of the reactor R2 were chosen as
optimum condition for gas generation from fleshing. The criteria of the reactor R2
can be used for further study or design purposes. Based on the principles of R2
reactor, the economic feasibility of a fleshing based pilot scale biogas plant was also
studied. The economic return was found to be 3.5 years for that type of plant.