Black Carbon from Rice Residues as Soil Amendment and for Carbon Sequestration

Black Carbon from Rice Residues as Soil Amendment and for Carbon Sequestration
Haefele, SM, Konboon, Y, Knoblauch, C, Koyama, S, Gummert, M, Ladha, JK
Cornell University Poster Presented to International Rice Research Institute, September 14 2006

On highly weathered soils in tropical and subtropical climates, maintenance of soil organic matter is essential to sustain system productivity and avoid rapid soil degradation. But climatic conditions as well as soil characteristics favor the rapid decomposition of organic matter. However, several recent studies indicated that black carbon, the product of incomplete combustion of organic material, could combine characteristics highly beneficial for soil nutrient dynamics with high stability against chemical and microbial breakdown. Lasting soil amelioration by incorporation of black carbon from wooden plants was proposed based on the beneficial evidence from ?Terra Preta? soils in Western Amazonia. Theoretically, charred crop residues in rice-based systems could serve the same purpose but this hypothesis has never been tested. Within this context, our objectives were to 1) assess possible options for the use of charred rice residues, to 2) test the effect of charred rice residues on important soil fertility parameters and rice growth, and 3) to evaluate the effect and stability of charred rice residues in a variety of rice growing environments. Initial investigations showed that charred rice husks are already used in several Asian countries, e.g. in Japan for seed bed preparation of rice and vegetable crops, and in the Philippines for soil amelioration in ornamental plant production. Charring of rice husks in Japan is known as ?Kuntan? and simple techniques for its production are even part of agricultural training courses. First experiments showed that charring rice husks slightly increases the relative carbon content but the weight loss from fresh to charred rice husks is about 70%. Similarly to carbon, the relative concentration of other nutrient elements (e.g., N, P, K, Ca, Mg) is maintained or even increased. Greenhouse studies in pot experiments conducted in the Philippines and northeast Thailand in 2005 showed positive effects of charred rice husks on rice biomass, rice yield, and cation exchange capacity. No increased leaching of organic carbon was observed when charred rice husks were added to the soil. Randomized and replicated field trials including control treatments and +/- inorganic fertilizer treatments were established in a variety of rice-growing environments including irrigated lowlands, rainfed uplands (both in the Philippines), rainfed lowlands (northeast Thailand), and the rice-wheat system (India). In these trials, the quantity of carbon applied equaled about 1.4% in the surface soil layer (0.0 - 0.1 m) or about 16 t carbon per hectare. Converted to biomass, this is equivalent to the crop residues of about 10 to 20 seasons, depending on the system's productivity (including straw and assuming the above mentioned efficiency in black carbon production). In the first cropping season, observed agronomic effects of the charred rice husks were variable and depended on the cropping system and the indigenous soil fertility. Contrary to that, the effects on soil characteristics were more consistent and major effects were an increase of the cation exchange capacity, a decrease of soil bulk density, and a stable increase of soil organic carbon. However, preliminary results strongly suggest that a continuation of the field trials is necessary to better evaluate the long-term treatment effects. If the greater part of the applied black carbon proves to be stable in some or all tested cropping systems, this technology could be an interesting option for carbon sequestration. If used at a large scale, considerable research efforts would be needed to evaluate the various and far-reaching consequences of the proposed technology.

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Conversion of Municipal Solid Waste (MSW) into Charcoal

Charcoal Pellets made from MSWCoal, oil and gas were formed during the past million years from decomposing biomass. This inspired Prof. Dr. Ernst Bayer (Germany) and Dr. Mohamed Kutubuddin (India) to develop the Low Temperature Conversion (LTC) in 1980. LTC operates at low temperatures and normal pressure.

Seeing these advantages Dr. Trutz-Ulrich Stephani and Jalaj Kumar Chaturvedi tried to adapt LTC under Indian conditions. WBREDA and Bidhan Nagar Municipality supported providing land and MSW. Technical problems made LTC not viable. The novel process of 2 Chamber Conversion led a way out .

The operators feed the MSW through the charging unit into the upper chamber of the reactor. There the MSW is gasified .The gases leave the reactor through the gas outlet and are combusted in the burning chamber. The partly decomposed MSW falls into the lower chamber. There LTC is forming charcoal and a combustible gas. This gas is burned with air entering through slits in order to support gasification in the upper chamber. The charcoal is discharged at the bottom.

First Plant with this new technology has been installed at Barasat , West Bengal by West Bengal Renewable Development Agency & Barasat Municipality & Implemented by M/s Shivam Enterprises headed by Dr. TU Stephani (Germany) & Mr. Jalaj Kr. Chaturvedi (India)

Currently the plant is running for 8 hours daily 6 days in a week. The plant is converting 5 ton of DRY MSW to 2 ton (approx) of Charcoal .

At, Present the plant is not using the Gas. Gas, is burning in a Combustion Chamber & generating 1 MW of thermal power.

Analysis Report of Charcoal from Barasat Plant-
Charcoal MSW Bio Mass Baggase Pure Grass
ASH 55.9 40.57% 24.67% 54.80%
Moisture 02.8% 05.66% 07.34% 04.99%
V.M 18.1% 15.11% 10.30% 11.12%
Fixed Carbon 23.0% 38.66% 57.43% 29.09%
G.C.V KCAL/kg 2932 4039 5414 2700 kcal/kg

Plant operates in a continuous process with about 12 employees converting 500kg/h dry MSW into 200kg/h charcoal having a GCV of about 3000 kcal/kg (price aprox. 1.5 Rs/kg).

The plant gives employment to the local people (about 12 labours), reduces cost in maintaining the dump yard (no leveling) and removes the stench from the decomposing material. The pollution of the groundwater will be stopped. The local industry and household will have a new source of fuel.

Development will continue. The process is suitable for other organic materials like biomass, agro-waste and industrial waste. In a next step – Plant will use the huge amount of gas either for electrical power generation, process heat or even bio fuel. Another task will be up scaling or even downscaling.

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