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Composting design and development
India is an Agro Based economy. About 60% of the Indian population relies directly or indirectly on agriculture. India has an
estimated potential of producing about 4.3 million tones of compost each year from Municipal Solid Waste (MSW), which
could help in reducing the wide gap between availability and requirement of organic manure for soils in India (Composting
Report). The organic content of MSW tends to decompose causing odour nuisance which also pollutes the environment. In
order to ensure a safe disposal of the MSW, it is desirable to reduce its pollution potential for which several processing methods
are available. Composting is one of the most efficient and commonly used methods of processing biodegradable solid waste
under controlled (predominantly) aerobic conditions. It results in the production of a stable product i.e. compost which can be
used as a low grade manure and soil conditioner in agricultural and horticultural areas depending upon its quality. Compost
obtained is rich in macro nutrients such as Nitrogen, Phosphorous and Potassium as well as micro nutrients and thus can be
utilized for the growth of plants. When it is used in conjunction with chemical fertilizers optimum results are obtained. Among
different methods of composting such as (Indore method, Bangalore method, passively aerated composting method, In-vessel
composting method, NADEP method of composting and Vermicomposting) NADEP method of composting have been as base
method selected for the Designing rapid composting for agricultural residues in this study.
1.1 SITE SELECTION
Field of a local marginal Farmer been selected for the Construction of Pit which is situated at Kapsi Village, Nagpur.
1.2 FEEDING MATERIAL SELECTION
Paddy and Citronella grass both are the major crop in the selected field. Rice Straw and Oil extracted Citronella grass were
selected for the feeding as they were present in an abundant amount in the selected agricultural field as residues. The particle
size of rice straw used was approximate 1 feet in length and that of Citronella grass used was about 1-2 feet long. Two types of
mixtures were adopted for feeding. These were:
a. Rice straw and
b. Rice straw: citronella grass (1:1 w/w).
- MATERIAL & METHOD
2.1 DESIGN OF RAPID COMPOSTING PIT
Two pits were constructed for the process. One of Rice Straw and other of a mixture of Rice straw&citronella grass.
Construction of pits completed in 4 days. Both the rectangular pits were made of brick masonry (using 172 bricks each of
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standard size 273mm x 104mm x 73mm with 0.915m3 of mortar) with a concrete base. The size taken of the pit adopted was 10′
(length) x 6′ (breadth) x 1′ (height). Perforated Pipes each of 2.5″ diameter were laid in the tank for providing passive aeration.
4″ thick PCC plinth was also laid in order to make the base leak-proof. Plan of Rapid Composting pit is shown in Figure 1.
Figure 1: Plan of Rapid Composting (Line Diagram & 3D view)
2.2 PREPARATION of BIOLOGICAL ACTIVATOR
20 litres of Biological Activator was prepared for feeding each pit in the following manner. A solution was made by adding 2
kg jaggery in 2 litres of water. Two kg of old compost, 200 g Component 1 and 200 mg Component 2 were added & mixed
thoroughly. 1 litre each suspended culture of selected microorganisms and 10 litres of water was added in the mixture. The
solution was then kept for fermentation for 5 days. After Fermentation, the solution was scaled up to 20 litres.
2.3 COST ESTIMATION OF RAPID COMPOSTING PROCESS
The overall cost for the process was calculated for the year 2015-16.
Labour required : two masons per pit are adequate
No. of Working Hours : 8 hours per day
Pay per Labor : Rs. 400 per day
No. of Working days : 2 days
Total Labor Cost : Rs. 1600/-
Total Construction Cost: Rs. 3700
Jaggery = 2 kg x Rs. 38/kg = Rs. 76/-
Jute Bags = 15 nos. x Rs. 18 per bag = Rs. 270/-
Plastic Cover (Tirpaal ) = Rs. 410/-
Culture Cost = Rs. 500/-
Total accessories cost = Rs. 1256/-
Total Cost for Composting: Rs. 6556/-
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2.4 METHODOLOGY ADOPTED
In Pit-1: 250 kg of rice straw was feed in 5 layers of approx. 50 kg each. Sufficient amount of water and activator was
sprinkled on each layer.
In Pit-2: 220 kg of rice straw and citronella grass was feed in 5 layers of approx 45 kg each. Sufficient amount of water and
activator was sprinkled on each layer.
Pits were then properly covered with jute bags. Visual Monitoring of both the pits was done and the growth of fungi was
observed. The temperature of the pits was recorded regularly up to 7 days and then periodically at an interval of 10 days.
Periodical assessment of variation in physiochemical parameters of feed material was done. At a regular interval of 10 days
concentration of parameters such as moisture content, Ash content, Total Volatile Solids, Carbon, Hydrogen, Nitrogen,
Sulphur, Sodium, Potassium, Phosphorus and Lignin was determined in the laboratory. Figure 2: Feeding of Rice straw-Citronella grass (Pit-2) Figure 3: Feeded Pit - RESULTS & DISCUSSION
After 60 days of Rapid Composting Period, Compost formed in both the pits was taken to a lab for various tests and results
generated were as follows:-
3.1 Color & Odor:
Compost in both the Pits was Dark brown in colour and had an earthy odour as shown in Figure 4 and Figure 5.
Figure 4: Compost formed in Pit-1 Figure 5: Compost formed in Pit-2
3.2 Temperature
The variation in temperature of composting materials in Pit-1 and Pit-2 with time has been illustrated in Figure 6 and Figure 7
respectively.
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Fig.6: Variation in temperature during the composting process (Pit-1)
Figure 7: Variation in temperature during the composting process (Pit-2)
It was observed that after feeding, temperature shoots up the next day. This temperature rise was a result of intense microbial
activity, which was further favored by the high concentration of easily decomposable organic matter. The thermophilic phase of
microorganisms initiated on 2nd day in both the Pits and thus the temperature reached above 55 ºC in both the Pits i.e. 58.1ºC in
Pit-1 and 55.4ºC in Pit-2 respectively. This temperature rise makes the compost pathogen free.
3.3 Moisture Content
The variation in moisture content of composting materials in Pit-1 and Pit-2 with time is presented in Table-1.
Table-1 Variation of Moisture content with time during composting
S. No. Period of Composting (in Days) Moisture Content (in %)
It can be observed from Table-1 that the initial moisture content of feed was low as the matter taken up for feeding was dry.
Moisture lost during the composting process can be viewed as an index of decomposition rate, because heat generated during
the process accompanies decomposition. After observing moisture content of 10th day sample, it was found to increase moisture
content in both the pits to maintain it nearly 40% -50% which was best suited for the composting process. At the end of the
process, Compost was sun-dried which showed a sudden decrease in the moisture content of the final products.
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3.4. Total Solids, Total Volatile Solids and Ash Content
The ash content is an important indicative parameter for decomposition and mineralization of any composting material
(Khwairakpam and Bhargava, 2009b). The ash content increment in the Pit-1 and Pit-2 with respect to the period of composting
has been presented in the form of a graph in Fig.8.
Fig.8 Ash Content v/s Period of Composting
The results of the analysis indicated that ash content of Pit-1moderately multiplied three folds than its initial value while that of
Pit-2 becomes doubled than its initial value. The enhanced mineralization of agro waste materials due to composting may be the
reason for higher Ash content in the final product. Decrease in Total Volatile Solids in the pits i.e. 29.71% loss in Pit-1 and
19.86% loss in Pit-2 also indicated the degradation of organic material.
3.5 Carbon Content and Nitrogen Content
C/N ratio is the key parameter for the maturity of the compost. Degradation of carbon and mineralization of nitrogen, both are
important aspects of composting. Carbon degraded by 32.65% in Pit-1 while 30.99% in Pit-2. Nitrogen mineralized with the
course of time, nitrogen content reached up to 1.988% in Pit-1 and 1.876% in Pit-2, which is more than 1%, compared to the
compost formed as per standards. Fig. 9 has showed a variation of C/N ratio in both the pits with time during the process of
composting.
Fig. 9 C/N Ratio v/s Period of Composting
The results clearly indicate that there was a continuous decrease in the values of C/N ratio after 10 days of the stabilization
process. The decrease in C/N ratio was 80.66% in Pit-1 as compared to 67.43% in Pit-2. The initial level of C/N ratio was
64.466 in Pit-1, which reduced to a final value of 12.469. Similarly, the value of C/N ratio in Pit-2 reduced to 14.835 from an
initial value of 45.553. This shows a significant amount of carbon degradation as well as Nitrogen mineralization. C/N ratio
reached below 20, which revealed that the compost formed, was as per Municipal Waste (Management & Handling) Rules,
1999.
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3.6 Phosphorus Content
Phosphorous content gradually increased during the composting process. The change in phosphorus throughout the composting
period has been tabulated in Table 2. Variation in Phosphorous was due to the net loss of dry mass. The initial amount of
Phosphorus present in Rice Straw was less than that of Rice straw-Citronella grass mixture. There was only a slight increase of
29.28% in phosphorus in Pit-1 i.e. from 102.68 mg/kg to 132.74 mg/kg whereas the increase in the concentration of
Phosphorous in Pit-2 was 24.24% i.e. from an initial value of 161.37 mg/kg to 200.48 mg/kg.
Table-2 Variation of Phosphorous content with time during composting
S. No. Period of Composting
(in Days)
Phosphorous Content (in mg/kg)
3.7 Lignin Content
Lignin degradation during composting is governed by- temperature, the original lignin content and the thickness of the
material. During the Thermophilic phase, rapid degradation of lignin was measured. In Pit-1 the lignin concentration was
reduced to 14.5% in 10 days period from an initial concentration of 21.5% whereas, in Pit-2 the concentration reduced to 16.4%
in 10 days period of composting from an initial concentration of 25.8%. Lesser degradation was observed in Pit-2 because of
long leaf size (not more than 2 feet) of citronella grass.