ABSTRACT
1. One
of the most important environmental problems faced by the world is management
of wastes. Industrial processes create a variety of waste water pollutants;
which are difficult and costly to treat. Wastewater characteristics and levels
of pollutants vary significantly from industry to industry. Now-a-days emphasis
is laid on waste minimization and revenue generation through byproduct
recovery. Pollution prevention focuses on preventing the generation of wastes,
while waste minimization refers to reducing the volume or toxicity of hazardous
wastes by water recycling and reuse, and process modifications and the
byproduct recovery as a fall out of manufacturing process creates ample scope
for revenue generation thereby offsetting the costs substantially.
2. Production
of ethyl alcohol in distilleries based on cane sugar molasses constitutes a
major industry in Asia and South America . The world’s total production of alcohol from
cane molasses is more than13 million m3/annum. The aqueous distillery effluent stream known
as spent wash is a dark brown highly organic effluent and is approximately
12-15 times by volume of the product alcohol.
It is one of the most complex, troublesome and strongest organic
industrial effluents, having extremely high COD and BOD values. Because of the
high concentration of organic load, distillery spent wash is a potential source
of renewable energy. The paper reviews
the status and appropriate treatment alternatives for disposal of the
distillery wastewater.
KEYWORDS
Distillery
Spentwash, Revenue Generation, Byproduct Recovery.
INTRODUCTION
1. Production of ethyl alcohol in distilleries
based on cane sugar molasses constitutes a major industry in Asia and South America . The
world’s total production of alcohol from cane molasses is more than13 million m3/annum. The aqueous distillery effluent stream known
as spent wash is a dark brown highly organic effluent and is approximately
12-15 times by volume of the product alcohol.
It is one of the most complex, troublesome and strongest organic
industrial effluents, having extremely high COD and BOD values. Because of the
high concentration of organic load, distillery spent wash is a potential source
of renewable energy.
2. The 295 distilleries in India
produce 2.7 billion litres of alcohol and generating 40 billion litres of
wastewater annually. The enormous distillery wastewater has potential to
produce 1100 million cubic meters of biogas. The population equivalent of
distillery wastewater based on BOD has been reported to be as high as 6.2
billion which means that contribution of distillery waste in India to organic pollution is
approximately seven times more than the entire Indian population. The
wastewater from distilleries, major portion of which is spentwash, is nearly 15
times the total alcohol production. This massive quantity, approximately 40
billion litres of effluent, if disposed untreated can cause considerable stress
on the water courses leading to widespread damage to aquatic
ALCOHOL MANUFACTURING PROCESS AND NATURE OF DISTILLERY WASTE WATER
3. In India bulk of the alcohol is being
produced from sugar cane molasses. Molasses is a thick viscous byproduct of
the sugar industry which is acidic in nature, rich in salts, dark
brown in
colour and it also contains
sugar which could not be crystallized. For manufacturing alcohol,
the Molasses is diluted with water into a solution containing 15-16 %
of sugars. This solution is then inoculated with yeast strain and is
allowed to ferment at room temperature. The fermented wash is distilled in a
series of distillation columns to obtain alcohol of adequate/ requisite
strength and quality/specification. This alcohol is used for various purposes
including potable and industrial. For manufacture of alcoholic beverages, the
alcohol is, if required, matured and blended with malt alcohol (for
manufacture of whisky) and diluted to requisite strength to obtain the
desired type of liquor/ Indian Made Foreign Liquor (IMFL). This is bottled in
bottles of various sizes for the convenience of consumers.
S.No.
|
Parameter
|
Range
|
1.
|
pH
|
4.3-5.3
|
2.
|
Total Suspended Solids
|
12,000-14,000
|
3.
|
Total Dissolved Solids
|
45,000-75,000
|
4.
|
B.O.D., 20 0C, 5 days
|
40,000-50,000
|
5.
|
C.O.D.
|
80,000-1,00,000
|
BIO-ENERGY POTENTIAL
FROM DISTILLERY EFFLUENTS
4. In India there are 295 distilleries
producing 3.20 billion litres of alcohol
generating 45 billion litres of
wastewater annually. The enormous distillery wastewater has potential to
produce 1200 million cubic meters of biogas. The post methanation wastewater if used carefully for irrigation of agricultural crops
can produce more than 85000 tonne of biomass
annually. This biogas normally contains 60% methane gas, which is a
well-recognized fuel gas with minimum air pollution potential. If this source
of energy is tapped, it will fetch additional energy units worth 5
trillion-kilo calories annually. Besides, the Post
Methanation Effluent (PME) can provide 245000 tones of potassium, 12500 tones
of nitrogen and 2100 tones of phosphorus annually. Thus the manorial
potential of effluent can be measured by the fact that one year’s effluent can
meet the potassium requirement of 1.55 million hectare land, nitrogen
requirement of 0.13 million hectare land and phosphorus requirement of 0.025
million hectare land if two crops are taken in a year.
Annual Bio energy Potential of Distillery Effluent in Various
States of India
|
|||||||
State
|
Units
|
Capacity (M Ltr/Yr)
|
Effluent
(M Ltr/Yr) |
Biogas (M m3)
|
Total N (tones)
|
Total Ka (tones)
|
Biomass
(tones)
|
A P
|
24
|
123
|
1852
|
50
|
566
|
11115
|
3704
|
|
1
|
2
|
24
|
0.7
|
7
|
144
|
48
|
|
13
|
88
|
1323
|
35.7
|
397
|
7940
|
2646
|
|
6
|
15
|
218
|
6
|
65
|
1304
|
436
|
|
10
|
128
|
1919
|
51.8
|
576
|
11511
|
3838
|
Karnataka
|
28
|
187
|
2799
|
75.6
|
840
|
16794
|
5598
|
M P
|
21
|
469
|
7036
|
190
|
2111
|
42219
|
14072
|
|
65
|
625
|
9367
|
253
|
2810
|
56217
|
18734
|
|
8
|
88
|
1317
|
35.6
|
395
|
7902
|
2634
|
Tamilnadu
|
19
|
212
|
3178
|
86
|
953
|
1971
|
6356
|
U P
|
43
|
617
|
9252
|
250
|
2776
|
55512
|
18504
|
W B
|
6
|
24
|
371
|
10.1
|
111
|
22223
|
742
|
Rajasthan
|
7
|
14
|
202
|
3
|
61
|
1215
|
404
|
Kerala
|
8
|
23
|
343
|
9.3
|
103
|
2064
|
686
|
|
3
|
11
|
165
|
4.5
|
50
|
990
|
330
|
|
1
|
7
|
98
|
5.5
|
29
|
585
|
196
|
Nagaland
|
1
|
2
|
24
|
0.7
|
7
|
144
|
48
|
J & K
|
7
|
24
|
366
|
11
|
110
|
2196
|
732
|
H P
|
2
|
3
|
39
|
1
|
12
|
234
|
78
|
Haryana
|
5
|
41
|
615
|
16.6
|
185
|
3690
|
1230
|
Total
|
285
|
2703
|
40,508
|
1096.1
|
12,154
|
263,070
|
81016
|
PRESENT STATUS OF TREATMENT
AND DISPOSAL
5. Spent
wash treatment is proposed by three different routes currently viz; (a) Concentration followed by incineration,
(b) Anaerobic digestion with biogas
recovery followed by aerobic polishing and
(c) Direct wet oxidation of stillage by air at high temperature with
generation of steam followed by aerobic polishing. All of these processes are
capital intensive. The incineration process involves an investment of the order
of 400% of the distillery cost, whereas the other two processes along with the
secondary treatment require an investment of 200-300% of the distillery cost.
The unfavourable economics make it difficult to implement these treatment
processes on the plant scale. Because anaerobic digestion and wet oxidation are
less expensive, these alternatives are more attractive. However, there is a need for development of a
suitable process with lower investments and higher energy recovery. Many distilleries
in India
are allowing their effluent for application on land as direct irrigation water,
spent wash cake and spent wash-press mud compost. The advances
manifesting the possibilities of energy conservation are also discernible in
the case of distilleries. The methane gas generated in the digesters is used as
a fuel to compensate the energy needs of the industry. A general estimate
suggests that the cost of an anaerobic biological digester is recovered within
2-3 years of installation because of substantial saving of coal and other
fuels.
COST RECOVERY METHODS FROM THE DISTILLERY EFFLUENTS
6. The wastewaters generated during the
distillery and brewery operations contain high organic loads. It has a BOD from
30,000 to 60,000 mg/1. So due to this high organic contents, the wastewaters
can be subjected to treatment for the production of biogas, composting,
aquaculture and potash recovery.
(a) BIOGAS. For the production of biogas
from distillery effluent, anaerobic biomethanation of the effluent is adopted,
generally. High rate anaerobic
technologies are utilized for biogas generation. Fluidised Bed Reactors and Up
flow Anaerobic Sludge Blanket (UASB) Reactors are mostly utilized for the
production of biogas from the effluents. Some of the biogas production
processes being commercial1y established in India at present are:-
·
BIOTHANE PROCESS:
This process uses the UASB reactor for the production of biogas. This is
a stable and automatic process with low operational costs.
·
BIOBED PROCESS: It is similar to Bio thane process. It
uses UFB reactors. It needs less installation area and its construction cost is
lower compared to any other system.
·
BIOPAQ PROCESS: In this process anaerobic bacteria are
used to treat the distillery effluents for the production of biogas. UASB process
is utilized here. The separated sludge in this process makes excellent manure.
The generated biogas is used to produce steam for the distillation of alcohol
and thus it replaces 50-60% of the total required energy in the process of
distillation. For a plant having 40-45,000 kg COD/day 75-80% of COD can be
reduced and nearly Rs. 25.50 lakhs can be saved annually for a distillery
having 300 working days in a year. The generated biogas from UASB reactor of
BioPaq process can be collected and be used as a fuel in gas/dual engine.
Through suitable coupling the engine can be coupled with the A/C generator for
generation of electricity from biogas. For a 45 klpd distillery 11 KV of power
is generated which is then utilized in the distillery thus cutting down the
power consumption.
·
SULZER' S PROCESS: The technology of this type of biogas
plant is provided by Sulzer Brothers Limited, Switzerland . It is specifically
made for Indian conditions. A biogas plant at the distillery of Padmashri Dr.
Vitthalrao Vikhe Patil S.S.K. Ltd., Pravaranagar, Ahmednagar District, Maharashtra is based on Sulzer's technology. The capacity
of this distillery is 6,000 lpd which generates 900 m3 of spent wash per day.
The biogas production is in the range of 16,550 to 21,870 m3 per day. The
savings in the cost of fuel is in the range of Rs. 312 lakhs to Rs. 652 lakhs
per year.
o
ECONOMICS OF THE BIOGAS PLANT OF SULZER’S
DESIGN
These calculations are made for a
distillery producing 30,000 litres of alcohol per day. The effluent
characteristics are for conventional batch type fermentation process.
o
EFFLUENT
CHARACTERISTICS
Before Treatment After Treatment
Flow m3/day 450 450
pH 4.0
to 4.5 7.0
to 7.8
BOD mg/l 45,000
to 50,000 6,000 to 8,000
COD mg/l 80,000
to 1000,000 25,000 to 35,000
o
PERFORMANCE
Reduction of BOD % 80
to 85 %
Reduction of COD % 65
to 70 %
Biogas Production Nm3/day 12,300
Specific Biogas
Production Nm3/kg of COD degraded 0.4
to 0.5
% of methane in biogas 60
to 65 %
o
ECONOMICS
Calorific
value of biogas 6000
Kcal/ Nm3
Calorific
Value of Coal 4000
Kcal/Kg
Coal
equivalent of Biogas per day 18.45
tonnes
Cost of Coal at Rs 1800
per tonne Rs 33,210 pd
Annual fuel savings Rs 99.63 lacs
Capital cost of plant Rs 230 lacs
Interest at 15 % on 75
% of the capital cost** Rs 26,73,750
Maintenance costs Rs 2,00,000
Staff Salary Rs 1,50,000
Power 40 KW at Rs 2/-
per unit Rs 5,76,000
Total Annual Cost Rs 36,00,000
Net Savings per year Rs 99.36 – 36
=
Rs 63.63 lacs
Total Pay back period = 230 / 63.63
= 3
to 4 years.
(b) COMPOSTING In this process, press mud generated
from sugar mill is utilised to produce compost by mixing distillery effluent.
Both anaerobic and aerobic composting systems are practiced. In some plants
composting with treated effluent treated through bio-methanation plant is also
practiced. This system can achieve zero effluent if the press mud quantity
matches with the effluent generated.
·
ECONOMICS OF
BIOEARTH COMPOSTING
Capacity of the Distillery 50
KLPD
Number of working days in a year
In
the Distillery 300
In
the Composting Plant 275
Generated spentwash 350
KLPD (Biostil Plant)
Solid content in spentwash 17
%
Spentwash to Press mud Ratio 2.5
KL : 1 MT
Man Power Required 50
Culture Requirement 31.5
MT/annum
Press mud requirement 43,000
MT/ annum
Cost of Culture Rs 1.75 lakhs per MT
Cost of Press mud Rs 12 per MT
Man Power cost Rs 50 per day
Capital Cost Rs 175 lakhs (excluding land)
Land Requirement 25
acres
Bio Earth Production
38,000 MT per year
Annual Maintenance Costs 1.5
% of equipment costs
% Costs of Funds 20
% per annum
·
OPERATION
COSTS
Cost of Culture 55.13
lakhs
Average Cost of Funds 17.5
lakhs
Cost of Diesel 11.32
lakhs
Cost of Press mud 5.16
lakhs
Cost of Transportation of Press mud 0.00
Annual Man Power Cost 6.88
lakhs
Depreciation (@ 10 %) 15.00
lakhs
Maintenance 2.25
lakhs
Annual Operational Cost of Compost Plant 113.24 lakhs
Cost of One Metric Tonne of Bioearth =Annual Operational
cost of plant
Compost
Produced in MT
= 11324000
38000
38000
= Rs
298.00 per MT
·
NET
COST/BENEFIT FOR DIFFERENT SELLING PRICES OF COMPOST
SP of Bioearth Net
Cost / Benefit
in
Rs
in Rs
0 -11324000.00
100.00 -7524000.00
200.00 -3724000.00
298.00 0.00
350.00 1976000.00
400.00 3876000.00
500.00 7676000.00
Net annual cost/benefit of Compost = Sales value of 38000 MT of compost less annual
operating costs
·
COMPUTATION
OF PAY BACK PERIOD
1. SP
of Bioearth - Rs 250.00
Initial
cash outflow - Rs 17500000.00
Net
annual cash inflow - Rs 1738000.00
Pay
Back Period - 10.06 Years (17500000/1738000.00)
2. SP
of Bioearth - Rs 350.00
Initial
cash outflow - Rs 17500000.00
Net
annual cash inflow - Rs 5226000.00
Pay
Back Period - 3.34 Years
(17500000.00/5226000.00)
3. SP
of Bioearth - Rs 500.00
Initial
cash outflow - Rs 17500000.00
Net
annual cash inflow - Rs 10926000.00
Pay
Back Period - 1.6 Years
(17500000.00/10926000.00)
(c) POTASH
RECOVERY It is done by incinerating the distillery spent wash. In this process, the raw distillery spent
wash is first neutralized with lime and filtered. This is further concentrated
to about 60% solids in multiple-effect forcer circulation evaporators. Now this
thick liquor from the evaporator is burnt in an incinerator and is converted
into ash. The dry solids of the spent wash in the form of coke in the incinerator
has an average calorific value of 2 Kcal/kg, which is sufficient for supporting
self-combustion of the thick liquor in the incinerator. The resulting ash is
found to contain about 37% of potash as potassium oxide on an average. This ash
is further leached with water to dissolve the potassium salts. Then it is
neutralized with sulphuric acid and is evaporated. The potassium salts are
crystallized in a crystal1izer. The crystallized mixed potassium salt contains
73.5% of potassium sulphate (K2SO4) 16.5% potassium
chloride (KCl) and 5% of sodium salts.
It is estimated that a distillery discharging about 300 m3
of spent wash per day could recover 3 tonnes of Potassium as Potassium oxide or
about 5.34 tonnes of Potassium sulphate and 1.2 tonnes of Potassium chloride
per day. This potassium is used as a
fertilizer.
(d) DISTILLERY WASTEWATER
UTILISATION IN AGRICULTURE Being very rich in organic matters, the utilisation
of distillery
effluents in agricultural fields creates organic fertilization in the soil
which raises the pH of the soil, increases availability
of certain nutrients and capability to
retain water and also improves the physical structure of soil. Mostly the distillery
wastewaters are used for pre-sowing irrigation. The post-harvest fields are
filled with distillery effluents. After 15-20 days, when the surface is almost
dried, the fields are tilled and the crops are sown and subsequent irrigation
is given with fresh water. However, the effluent is diluted 2-3 times before
application on crops. Apparently, the irrigation with distillery
wastewater seems to be an attractive agricultural practice which not only
augments crop yield but also provides a plausible solution for the land disposal of the effluents. One cubic metre of methanated effluent contains nearly 5 kg
of potassium, 300 grams of nitrogen and 20 grams of phosphorus. If
one centimetre of post methanation effluent is applied on
one hectare of agricultural land
annually, it will yield nearly
600 kg of potassium, 360 kg of
calcium, 100 kg of sulphates, 28 kg
of nitrogen and 2 kg of phosphates. The distillery effluent contains 0.6 to 21.5 percent potash as KO, 0.1
to 1.0 percent phosphorus as PO and 0.01 to 1.5 percent Nitrogen as N2.
The irrigational and manorial
potential of distillery wastewaters
is given below:
i) Total
Volume available in Million m3
/annum :
6.87
ii) Nutrients
Contribution Potential (tonnes/annum) :N - 69380
KO - 27480
·
ECONOMICAL
ASPECTS
When the distillery effluents are used for irrigation in fallow lands, the microbes present in it transform the lands into fertile ones, giving high yields of paddy and
sugarcane. Farmers could save nitrogenous fertilisers worth Rs 1335 crores
per annum if at least 200 distilleries
of out country recycled their wastes
to the agricultural fields. However, it is predicted that the utilisation of distillery effluent for irrigation of land would
make available nitrogen,
phosphorous and potash valued at about
Rs 500 crores each year. The added advantage of this application would be that these fertilisers would be available to soil in organic
form. As the secondary
and tertiary systems for the treatment of distillery effluent are highly energy intensive and
according to the
estimates of the Union Ministry of Energy a total connected load of 200 M.W. would be
required to energising these systems if 246 distilleries endeavour to reduce the BOD level of effluent to the extent possible.
The generation of the desired energy would need an installed load of 350 M.W. which
would require capital
investment of the order of about Rs 1400 crores. So
it will be an attractive practice to utilise the distillery effluents for ferti-irrigation of land after primary
treatment, as land is available in abundance around the distilleries which are located in the sugarcane belts.
RECOMMENDATIONS
7. Reviewing the magnitude of pollution potential of
distillery wastewaters and the experiences gained over years
on recovery of residues and treatment of wastewater the following
recommendations are made :-
·
In-plant
control measures for conservation and reuse of water and good house-keeping for
prevention of spillage and leakages should be the prerequisite.
·
For
recovery from the treatment of distillery spentwash, depending on the availability
and cost of land in a particular area, simple treatment in anaerobic lagoon to
generate biogas followed by treatment in aerated lagoon or oxidation ditch may
be considered. Where the availability and cost of land are the main
constraints, activated sludge type of aeration treatment in a deep oxidation
ditch would be more economical than the conventional or extended aeration
sludge process.
·
For the
treatment of distillery spent wash, removal and/or recovery of yeast should be
prerequisite to reduce the load and eliminate certain undue problems in the
waste treatment/recovery plants. This recovered yeast can be utilised as a good
cattle feed. Recovery of spent grains and yeast and their utilisation as animal
feed and feed supplement might be encouraged not only for reducing the
pollution load form the wastewaters but also in providing for a reasonable
return on their capital investment of the industry.
·
Where the
availability of land is a severe constraint, evaporation and incineration of
distillery spent wash to recover potash would appear to be the only choice. In
spite of high capital investment required for such type of plants, heat
recovery would defray significantly the organisation and maintenance costs and
contribute towards conservation of energy.
·
In the
countries like ours, where indigenous sources of potash are scarce or not
available, recovery of potash from crude ash by evaporation and incineration of
spent wash would appear to be an economically attractive alternative. If heat
recovery is simultaneously used, the pay back period of the plant can be
substantially reduced.
·
Anaerobic
digestion of spent wash in a closed digester followed by its treatment under an
activated sludge process, especially in an oxidation ditch to reduce costs, might
be adopted as the most cost-effective system for the distilleries which are
located away from sugar factories. Moreover, the treated effluent can be
conveniently used for irrigation of cane fields or other crop lands,
subsequently.
·
Biogas
generated from the distillery effluents, can be effectively utilized in
production plant boilers thus saving about 50 to 60 percent fuel/steam. The
treated effluent having almost all the potash retained in it may be utilised
for irrigation purposes.
·
The
utilisation of the distillery effluent in agricultural fields will not only
enrich these further with essential plant nutrients like nitrogen, phosphorous
and potash but also compensate the expenditure on fertilizers for crop growth.
This practice will result in revenue generation and further lead to offsetting
the costs substantially.
·
Similarly
spentwash utilization in bioearth composting, where adequate land is available,
being a simple process and not involving any heavy machinery is also one of the
cost effective methods of disposal. Moreover it is feasible alternative for
utilization of treated effluent; as the same generates revenue thus offsetting
the costs and further leading to reduction in pay back period.
CONCLUSION
8. One
of the most important environmental problems faced by the world is management
of wastes.
Now-a-days emphasis is laid on waste minimization and revenue generation through byproduct recovery. Pollution prevention focuses on preventing the generation of wastes, while waste minimization refers to reducing the volume or toxicity of hazardous wastes by water recycling and reuse, and process modifications and the byproduct recovery as a fall out of manufacturing process creates ample scope for revenue generation thereby offsetting the costs substantially.
Now-a-days emphasis is laid on waste minimization and revenue generation through byproduct recovery. Pollution prevention focuses on preventing the generation of wastes, while waste minimization refers to reducing the volume or toxicity of hazardous wastes by water recycling and reuse, and process modifications and the byproduct recovery as a fall out of manufacturing process creates ample scope for revenue generation thereby offsetting the costs substantially.
9. The cost of effluent treatment in
distilleries is likely to be compensated substantially by availability of
methane gas. Effluent application will reduce the nutrient requirement through
fertilisers. However, high salt load, mainly potassium and sulphur, into the
soil system may hamper the sustained crop yields due to continued long-term
application of effluents. Therefore the effect on crop productivity has to
be visualised on long-term and sustainable basis. Application of post
methanation effluent suitably diluted according to crop requirements and soil
conditions seems to be viable alternative. If all the distilleries present in India resort to biomethanation, then approximately 2.0 million cubic metres of biogas shall be generated per day,
with a calorific value of approximately 5000 Kcal/m. This is equivalent to
saving of 2240 tonnes of coal per day,
in turn avoiding CO of about 3100 tonnes per day.
10. The present
study coupled with the corresponding techno market survey has been aimed at
reviewing the existing technological status of treatment and disposal of
distillery spentwash in our country and comparing with that of the contemporary
international technologies, thus identifying the gaps in the technologies and
suggesting an action plan for overcoming these. Some relative issues in the
areas of quality criteria with respect to gaps in technologies and financial
implication in implementing the technological options, has been highlighted in
this study. It has to be stressed that recovery from the distillery effluents
is a better way to reduce the cost of wastewater treatment for decreasing its
pollution level which is actually a very costly affair. So this is a matter
great importance for the Indian distilleries and breweries. Various recommendations
are given for the establishment of recovery plants in India . It has also been elucidated
during the study that several technological options that are available in our
country need to be exploited to the maximum so that, this will help to control
the pollution created by the distillery wastewaters and also enable to derive
by-products which are commercially beneficial.
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