Biofuels – Promise / Prospects

 

 

 

Anil  Kumar  Rajvanshi, Vrijendra  Singh and Nandini Nimbkar

 

 

Nimbkar Agricultural Research Institute (NARI)

P.O. Box  44, Lonand Road,

Phaltan-415523, Maharashtra

 

Phone              : 02166-222396

Fax                  : 02166-220945

e-mail address :nariphaltan@gmail.com

 

 

 

Abstract

 

 

The prospects of using agricultural material for biofuel in India for energy purposes are evaluated. A strategy is developed so that from a given piece of land maximum bio-energy and remuneration to the farmers result. For this it is proposed that on a given land area in one year two crops can be grown, viz. sweet sorghum during monsoon followed by a winter oilseed or a monsoon oilseed followed by sweet sorghum in winter.

Thus the values of the product of bio-energy and net returns (BENR) were estimated for the different cropping systems evaluated. The highest values of BENR under rainfed conditions were obtained from a combination of sweet sorghum in monsoon and either groundnut, rapeseed, mustard, sunflower or safflower (in that order) in winter. Under irrigation highest BENR values were obtained for castor in monsoon and sweet sorghum in winter followed by sweet sorghum in monsoon with either mustard or groundnut in winter. 

It is shown that with this strategy not only the country can become self-sufficient in edible oil but will also have the potential of taking care indigenously of a substantial proportion of its energy needs.

In order that this strategy is followed on a large scale certain policy initiatives are suggested. 

   

1.  Introduction

 

The ever rising cost of fossil fuel internationally has forced major world economies, which are also major importers of fossil fuel, to examine renewable and cheaper alternatives to fossil fuel to meet their energy demands.  Biodiesel and bioethanol have emerged as the most suitable renewable alternatives to fossil fuel as their quality constituents match diesel and petrol respectively.  In addition  they are less polluting than their fossil fuel counterparts. Environmental concerns and the desire to be less dependent on imported fossil fuel, have intensified worldwide efforts for production of biodiesel from vegetable oils and ethanol from starch and sugar producing crops. 

The use of vegetable oil for energy purposes is not new. It has been used world over as a source of energy for lighting and heating since time immemorial. As early as in 1900, a diesel-cycle engine was demonstrated to run wholly on groundnut oil at the Paris exposition.  Even the technology of conversion of vegetable oil into biodiesel is not new and is well established. However the unprecedented rise in fuel prices recently has made it economically attractive. The present availability of vegetable oils in the world is more than enough to meet the edible oil requirements, and surplus quantity available can partially meet requirements of biodiesel production. However, there is a considerable potential to further enhance the oilseeds production in the world to meet the increasing demand for food and biodiesel. 

India is a huge importer of crude oil and spends about Rs. 1,200 billion of foreign exchange every year to meet 75% of its oil needs (Anand, 2006). This has affected its balance of payment adversely, especially after the unprecedented rise in crude oil prices. Being an agricultural country endowed with varied climates, nutrient-rich soil and ability to grow many different crops, India offers a great promise as a producer of surplus raw material for biodiesel and bioethanol production. Though presently it meets around 30-40% of its vegetable oil requirements through imports, India has a potential and capability to produce enough vegetable oil not only to meet its edible oil requirements but also for biodiesel production. The present paper discusses the promise and prospects of using vegetable oil as a biofuel with specific reference to Indian situation.

 

2.     World Biofuel Scenario

2.1   Area, production and productivity of oilseeds in the world and in India 

Worldwide, oilseed crops occupy an area of 166.36 million hectares with a production of 295.6 million tonnes and productivity of 1777 kg/ha (FAO, 2003). In India, area under oilseeds is 23.7 million hectares with a production of about 25 million tonnes and a productivity of just about one tonne/hectare. The oilseed production in the country presently meets only 60-70% of its total edible oil requirements and the rest is met through imports.

India also has a potential of collecting 5 million tonnes of tree-borne oilseeds (TBO) of which only 0.1-1 million tonnes are being collected presently (Kumar, 2003). In addition to the existing potential of TBO, there is about 60 million hectares of wasteland of which 30 million hectares can be suitably utilized for growing plantations of biofuel plants like Jatropha. It has been estimated that each hectare can produce about 2000 liters of  biodiesel/year after the initial 3-year period of establishment of Jatropha in the field (Shukla, 2005; Ghaisas, 2005).  This will result in the production of 60 billion liters of biofuel. Thus TBO from the wasteland can make a significant and important contribution to the energy requirement of the country in the days ahead. 

 

2.2   Global biodiesel production scenario

Biodiesel is a fast-developing alternative fuel in the U.S. and Europe.  Pilot plants for power generation and encouraging adaptation by fleet operators have established biodiesel as a viable and sustainable alternate fuel. The biodiesel production from vegetable oils during 2004-05 was estimated to be 2.36 million tonnes globally.  Of this EU countries accounted for 1.93 million tonnes, U.S. produced 0.14 million tonnes and rest of the world 0.29 million tonnes (Parikh, 2005).  The EU usage of vegetable oil for biodiesel has been rising at about 30% annually in the last two years. In EU, rapeseed is the main source of oil for biodiesel, while in the U.S. soybean oil is used for manufacturing biodiesel. Malaysia - the largest producer of palm oil has set up three palm biodiesel plants with a combined annual capacity of 60,000 tonnes.

 

2.3   World ethanol production

With the provision of addition of 5-10% of ethanol in petrol and diesel in most of the crude oil importing countries, there has been a substantial rise in ethanol production in last few years.  Among the ethanol producing countries, Brazil produces the maximum amount of ethanol (15099 million liters/year) followed by the U.S. (13381 million liters/year), China (3649 million liters/year) and India (1749 million liters/year) (Table 1). Sugar cane is the major source of ethanol in Brazil, while in the U.S. it is produced from corn (Peterson, 2006).

Biofuels in general have often been categorized as first and second generation. The first generation biofuels are the fuels which are produced from conventional agricultural crops by well-established technologies such as biodiesel from oil crops and ethanol from sugar and starch producing crops. The second-generation biofuels on the other hand are produced from the agricultural waste - mainly the lignocellulosic material. However they require advanced production (conversion) technologies. Overall, high energy conversion efficiencies and least cost of production are the key factors for selecting biofuels for the future.

 

2.4   Ethanol production from crop residues

Enough availability of crop residues as a source of feedstock is obviously mandatory for the production of second-generation biofuels. Annual crop residue availability in the world is estimated to be  about four billion tonnes, of which the U.S. and India account for one billion tonnes (Table 2). Lignocellulosic residues of cereal crops like corn, rice, wheat, sorghum and millet are  best suited for ethanol production and are estimated to be about 3 billion tonnes/annum in the world and 0.4 billion tonnes/annum each in the U.S. and India respectively (Lal, 2006). These are large quantities and a substantial part of these residues may suitably be used for biofuel production.

The potential of bioethanol production from waste crops and crop residues was estimated by Kim and Dale (2004).  According to them there are 74 Tg (Tg = Teragram = 1012 g = 1 million metric tonnes) of dry waste crops in the world that have a potential to produce 49 GL (gigaliter or 1 billion liters) of bioethanol/year. It was also estimated that conversion of 1.5 Pg (Pg = Petagram = 1015 g = 1 billion metric tonnes) of dry lignocellulosic residues of seven crops viz. corn, barley, oat, rice, wheat, sorghum and sugar cane, could produce an additional quantity of 442 GL of bioethanol per year. This potential bioethanol production of 491 GL could replace 353 GL of petrol or about one-third of the global petrol consumption. The ethanol production potential of residues from lignocellulosic crops ranges from 0.26 to 0.31 L Kg-1 (Table 3). The net energy yield of perennial crops ranges from 220-550 GJ/ha/yr, that of grasses 220-260 GJ/ha/yr and that of sugar cane 400-500 GJ/ha/yr (Hamelinck and Faaij, 2006).                           

Use of lignocellulosic agricultural residues for energy production is thus very favourable and offers good economic prospects for the future of biofuels.  EU has set a target of 1 billion liters of second generation bioethanol production to be achieved by 2012 (de Miguel, 2006). The prominent high potential fuels are ethanol produced from agricultural residues rich in lignocellulose, synthetic diesel via Fischer-Tropsch, methanol and hydrogen (Arthur D. Little, 1999; Katofsky, 1993; Turkenburg, 2000;  Williams et al., 1995). These four fuels are in attractive stages of development.

 

2.5   Comparison of  biodiesel and ethanol

Before striving for commercial scale biofuel production from food crops, it would be of paramount importance to determine whether biofuels provide any benefit over the fossil fuels they replace. This needs a thorough analysis of the direct and indirect inputs and outputs for their full production and use life-cycles.  To become a successful substitute for a fossil fuel, an alternative fuel in addition to having superior environmental benefits over the fossil fuel should also be produced economically and in sufficient quantities to meet the energy requirements. Hill et al. (2006) analyzed the net societal benefits of corn grain (Zea mays ssp. mays) for ethanol and soybean (Glycine max) oil for biodiesel - the two important alternative transportation fuels in U.S.

The study showed that both corn grain ethanol and soybean biodiesel recorded positive Net Energy Balances (NEB). The NEB for corn grain ethanol was recorded as 25% more energy than required to produce it. However, the soybean biodiesel provided 93% more energy than  needed in its production.

As far as the life-cycle environmental effects were concerned, the study showed that both corn and soybean production have negative environmental impacts through movement of agrochemicals especially nitrogen (N), phosphorus (P) and pesticides from farms to other habitats and aquifers. Data on efficiencies of net energy production from agrochemical inputs in corn and soybean reveal (after partitioning these inputs between the energy product and co-products), that biodiesel uses only 1.0% of the N, 8.3% of the P and 13% of the pesticides on  weight basis. Although blending ethanol with petrol at low levels as an oxygenate was reported to result in lower emissions of carbon monoxide (CO), total life-cycle emissions of five major air pollutants [CO, VOC, PM10, oxides of sulphur (SOx) and oxides of nitrogen (NOx)] are higher with the “E85” (85% corn grain ethanol-petrol blend) than with petrol per unit of energy released upon combustion (Hill et al., 2006). The study further revealed that production and use of corn grain ethanol releases 88% of the net green house gas (GHG) emissions of production and combustion of an energetically equivalent amount of petrol. On the other hand life-cycle GHG emissions of soybean biodiesel were recorded to be 59% of those for diesel fuel.                       

Because fossil fuel energy use imposes environmental costs not considered in market prices,  benefits of biofuel to society not only depend on its cost competitiveness compared to fossil fuel but also on its environmental costs and benefits vis-ŕ-vis its fossil fuel alternatives.  Subsidies for otherwise economically uncompetitive biofuels are justified if their life-cycle environmental impacts are sufficiently less than for alternatives.

 

3.    Status of  Biofuel Production in India

3.1  Biodiesel

India consumes more than 250 million tonnes of fossil fuels every year.  This comprises of approximately 40 million tonnes of diesel.  India is ranked fifth in the world after China, Japan, Russia and the U.S. in terms of fossil fuel consumption. Recently in India the Planning Commission, Government of India launched “National Mission on Biodiesel” with a view to find a cheap and renewable liquid fuel based on vegetable oils (Shukla, 2005). The rural development ministry has been appointed as the nodal ministry for implementing the programme.  This mission is being carried out in two phases – the first phase involving a demonstration stage for plantation of Jatropha on four lakh hectares and associated research activities for establishing the commercial viability of the fuel, and phase two for carrying out a self-sustaining expansion of the biodiesel programme.

Biodiesel production in India has reached a decisive stage and the country is about to make a beginning by introducing a five percent blend of biodiesel with conventional diesel at selected districts in different states (Behl, 2006).  In order to attract and secure private participation on larger scale, Government of India has fixed the procurement price of biodiesel as Rs. 25/liter with a provision to revise it after six months. Some biodiesel units using TBO and imported palm oil have already started manufacturing biodiesel on small scale.

Though India is the fourth largest producer of edible oilseeds in the world, it produces only 60% of its total oilseed requirement and the rest is met through imports.  Despite the low overall oilseed production presently, the country has a potential not only to become self-sufficient in but to produce surplus oilseeds simply by following the improved low-input technologies of oilseeds production and by a proper delineation of government policies favourable to oilseeds production.  These low input technologies have demonstrated 14-100% increase in seed yield over the existing practices under different conditions (DOR, 2005).

 

3.2   Ethanol production in India

In India, the world’s second largest sugar producer, ethanol is mainly produced from molasses, a sugar by-product. India’s molasses production declined from 8.0 million tonnes in 2002-03 to 5.0 million tonnes in 2004-05 due to poor sugar cane output.  However it has started rising again and is expected to achieve record levels this year.

The first phase of the ethanol-blended petrol was to have been launched in January 2003, but it took the industry a good three years to iron out start-up glitches. One issue was that the ethanol imported from Brazil was available at a lower price than domestic ethanol. Even at the 5% blend level being implemented currently there is a shortfall of 225 million liters of ethanol for the oil companies whose current demand is put at 435 million liters (Sify business, 2006).

India produced 1749 million liters of ethanol in 2004 mainly from sugar cane (Peterson, 2006), and has a very high potential to increase it further by using sweet sorghum, sugar beet and sugar cane juice as potential feedstock options.  Another potential source of ethanol can be cellulosic energy crops and crop residues as well as other waste products high in cellulose.         

 

4.  Biofuel Strategy for India

Domestic supply of crude oil meets only about 22% of the demand for surface transportation in India, while the rest is being met from imported crude.  Biodiesel and ethanol both are liquid biofuels and are considered as promising alternatives for diesel and petrol, particularly in the transport sector.

A number of developmental activities are being taken up in the country for the  production of biofuels which include 5% compulsory blend of ethanol in petrol and 5% biodiesel blend in diesel.  These trials are on in various states and the Government of India wants to increase these blends to 10%.

Though ethanol definitely has a role to play in future as a petrol supplement, there are several restraints to its use and small scale on-farm production, the major one being the onerous customs and excise regulations.  Nevertheless a strategy to use both fuels (ethanol and biodiesel) as blends will be beneficial to Indian economy.  The strategy consists of producing ethanol and biodiesel from crops to be grown on the same piece of land in different seasons.  Since sugar cane is a long duration crop, sweet sorghum which is a 4-month crop is more suitable for such rotation.

Thus it is proposed that from a given piece of land two crops can be taken, viz. sweet sorghum during monsoon followed by a winter oilseed or a monsoon oilseed followed by sweet sorghum in winter. In addition to ethanol and oil, they will also yield food grain, meal suitable for animal feed and biomass residues which can also be converted to ethanol. These crops can give a reasonable output even under rainfed conditions with low external input. Though the crops can be grown under a rainfed situation, in most cases just 2-3  irrigations at critical stages can produce a significant increase in both net returns and bio-energy production.

Four of the oilseed crops considered viz. rapeseed, mustard, safflower and linseed can be grown only in winter, while groundnut, sunflower and sesame can be grown in either monsoon or winter and castor, niger, soybean and cotton only in monsoon.  Sweet sorghum can be grown in either monsoon or winter, but there is considerable decrease in its stalk yield accompanied by an increase in the yield of grain in the winter crop.

                

4.1   Energy production from oil

The assessment of potential biodiesel yield from different oilseed crops has been done and is presented in table 4.  The results reveal that under irrigated conditions the maximum bio-energy production of  61.1 X 103 MJ/ha/season can be obtained from the oil of castor which is followed by groundnut (45.5 X 103  MJ/ha/season), sunflower (27.4 X 103 MJ/ha/season) and mustard (23.6 X 103 MJ/ha/season).  The maximum bio-energy production from oil under rainfed conditions is given by groundnut (31.2 X 103 MJ/ha/season), which is followed by castor (25.8 X 103 MJ/ha/season) and sunflower (16.7 X 103 MJ/ha/season). The agricultural residues - a potential source of second generation biofuels is generally either burnt in the field itself or is used for household purposes like cooking. It does not have any worthwhile use at present. By taking into consideration the possibility of development of suitable technology for bioethanol production from residues in near future, the production of ethanol bio-energy from agricultural residues of the oilseed crops has been estimated (Table 4).

 

4.2   Energy production from oil and crop residues 

Calculations of energy production from residues of different oilseed crops revealed that under irrigated conditions castor recorded the maximum energy output of 54.2 X 103 MJ/ha/season which was followed by mustard (51.3 X 103 MJ/ha/season) and sunflower (32.3 X 103 MJ/ha/season). Under rainfed conditions maximum energy production from crop residues is obtained from rapeseed (26.4 X 103 MJ/ha/season), which is followed by castor (22.9 X 103 MJ/ha/season) and mustard (22.7 X 103 MJ/ha/season). The aggregate biofuel production from oil and crop residues of different oilseeds was estimated to range from 7.7 X 103  MJ/ha/season obtained from cotton to 49.5 X 103 MJ/ha/season obtained from groundnut under rainfed conditions. Under irrigated conditions, aggregate biofuel production ranged from 22.8 X 103 MJ/ha/season in sesame to 115.3 X 103 MJ/ha/season in castor (Table 4).  Thus the value addition to the oilseed crop residues by using them to produce second generation biofuels will help in getting additional monetary returns from oilseeds. This will considerably raise the total remuneration from the crops to the farmer. As a result both area under the oilseed crops and their production in the country will increase. This will not only make India oil-sufficient but surplus in oil which can be used for manufacturing of  biodiesel.

 

4.3   Bio-energy production from oilseeds and sugar producing crops

The comparison of bio-energy production from oilseeds and sugar producing crops showed that sugar cane recorded a bio-energy production of 139 X 103 MJ/ha/season while sweet sorghum recorded a bio-energy production of 89.7 X 103 MJ/ha in monsoon and 35.7 X 103  and 42.5 X 103 MJ/ha/season under winter rainfed and irrigated conditions respectively (Table 4). Sugar cane was observed to produce higher energy than the highest bio-energy producing oilseed crop viz. irrigated castor. However, the comparison of bio-energy production from sugar cane with that from oilseed crops is not justified, since all the oilseed crops compared are of seasonal (4-5 months duration) nature and are grown under rainfed or limited irrigation conditions often on marginal soils. Contrary to this, sugar cane is a 12-18 month crop grown only under extensive irrigated conditions and usually on good soils with high external input.

To have energy security and to get maximum remuneration from a rainfed cropping system, it would be most desirable to have a combination of crops like sweet sorghum during monsoon and the most promising oilseed crop of the region during winter. In case of an oilseed like castor or soybean, it can be grown in monsoon followed by sweet sorghum in winter. By doing this, aggregate energy production as well as the returns from the rainfed cropping system as a whole can be maximized. Therefore an assessment of aggregate bio-energy production and net returns to farmers from both rainfed and irrigated cropping systems has been done (Tables 5 and 6).

The results indicate that bio-energy production from sweet sorghum (juice + crop residues) and oilseed crop (oil + crop residues) under rainfed conditions ranged from 139.2 X 103 MJ/ha/year in sweet sorghum + groundnut to 43.4 X 103 MJ/ha/year in the combination of cotton + sweet sorghum.  Sweet sorghum not only gives a very high yield of crop residues but also juice from stalk and grain for human consumption. Under irrigated conditions the bio-energy production ranged from 164.6 X 103 MJ/ha/year  in sweet sorghum + mustard to 76.5 X 103 MJ/ha/year in cotton + sweet sorghum.

Just the introduction of sweet sorghum in the oilseeds area during monsoon or winter for production of bio-energy from sweet sorghum juice alone, for which technology is already in place, can achieve significant biofuel production.  Even if only 50% of the 8.5 million ha of winter oilseeds area is planted with sweet sorghum in monsoon, it can produce 4165 million liters of ethanol which is equivalent to 2546 million liters of petrol energywise. This assumes a conservative estimate of 35 tonnes/ha of fresh stalk, juice extraction of 40% and production of 7 liters ethanol/100 liters of juice in monsoon. This much ethanol is nearly 3.27% of total transport fuel consumed in the country and is nearly 6% of the total crude oil produced in the country (Planning Commission, 2003). Such a system would enhance the area under sweet sorghum and oilseeds in the country to a substantial level to produce enough ethanol and surplus oilseeds to be utilized for bio-energy production.

 

4.4   Economics of the sweet sorghum-oilseed cropping system

In addition to the bio-energy production, it is important to consider the net returns a farmer is able to get from a given cropping system.  As far as a farmer is concerned the end utilization of his crop is irrelevant.  He is only interested in the total remuneration that he can  get from a given piece of land in a year.

Net returns under rainfed conditions ranged from Rs. 32680/ha/year in soybean + sweet sorghum to Rs. 19617/ha/year for sweet sorghum + sesame (Table 5, Fig. 2).  Under irrigated conditions the net returns ranged from Rs. 94743/ha/year for castor + sweet sorghum to Rs. 21741/ha/year for sweet sorghum + sesame (Table 6, Fig. 2). Thus ultimately the promise of a given cropping system can be determined from the product of its bio-energy output and net returns it can give to a farmer (BENR).

Under rainfed conditions the highest values of BENR are given by a combination of sweet sorghum in monsoon followed by either groundnut, rapeseed, mustard, sunflower or safflower (in that order) during winter (Table 5, Fig. 3).

As far as the values of BENR under irrigated conditions were considered, castor-sweet sorghum was the only crop combination which was better than sugarcane.  It was followed by combinations of sweet sorghum in monsoon with either mustard or groundnut in winter.  Cotton in monsoon followed by sweet sorghum in winter was ranked fourth (Table 6, Fig. 3).

        

4.5   Tree-borne oilseeds (TBO)

Tree-borne minor oilseeds have been accorded very high priority as a source material for biodiesel production in the country.  India is endowed with a vast potential for oilseeds of tree origin, the important of them being sal, mahua, neem, rubber,  karanja, kusum, khakan (pilu), undi, dhupa, etc. (Table 7). These oilseed-bearing trees are found widely and distributed throughout the country.  The present availability of oilseeds from them is estimated to be about 5 million tonnes annually. However, only 20% of the total availability is utilized for commercial applications (Kumar, 2003). 

The availability of TBO can be enhanced considerably without any extra land and inputs if proper network for procurement from seed collectors is established. There is a considerable scope to enhance the collection of seeds from the existing trees by developing infrastructure facilities such as seed/produce procurement centers equipped with facilities for drying, decorticating, cleaning/grading, depulping, storing and oil extraction near the areas of collection of TBO. Establishment of  biodiesel processing units near the  procurement centers will further help in reducing the cost of transportation of the raw oil to the biodiesel processing plant. This should result in reasonable remuneration to the primary seed collector and also help in getting a quality product by reducing losses caused due to delayed and improper handling of the material at different stages in the existing trade of TBO in India.

Apart from the existing trees in the country, there is 60 million hectares of wasteland, of which 50% can be suitably used for growing TBO plantations like those of Jatropha and karanja. With the recent central government drive to produce biodiesel from TBO, many state governments have given very high priority to plantations of Jatropha for biodiesel production. Information from various sources indicates that area under Jatropha plantations in the country has gone up to 20,000-30,000 hectares. Governments of states like Chhattisgarh, Gujarat and Madhya Pradesh have drawn up plans to take up Jatropha plantations on massive scale.   

In order for the above strategy to become operational, the following policy issues have to be addressed : 

 

Policy issues :

1.      Make long term policy on utilization of edible and non-edible oils by deciding their allocation for different uses.

2.      Delineate taluka-wise liquid fuel requirements to decide the cropping pattern to be adopted in them.

3.      Encourage public-private partnerships for successful large scale implementation of oilseeds program.

4.      In addition to transport sector, investigate use of vegetable oils or biodiesel for irrigation pumps, diesel generators, farm equipment, cook stoves, lanterns etc.

5.      Liberalize excise law.        

 

5.  Conclusions

The prospects of using agricultural material for biofuel in India for energy purpose appear to be promising. 

In the final analysis, the cropping systems with sweet sorghum in monsoon and an oilseed like groundnut, rapeseed or sunflower in winter appear to be the best as they have a potential to give high bio-energy production coupled with good net returns to the farmer under  both rainfed and irrigated conditions.

Cropping system with castor in monsoon and sweet sorghum in winter was also found to be promising mainly under irrigated conditions, though it gave very high returns even under rainfed situation. It is even more attractive as it produces a non-edible oil. India is the world’s leading producer of castor and the first in the world to exploit hybrid vigour in the crop on commercial scale.

Extent of bio-energy outputs and net returns obtainable from Jatropha is still a question mark and till the results of trials currently underway are in, it may not be a good idea to plant large tracts of cultivable land under this genus.  It will be better in the long run to attempt to increase the area under conventional oilseeds. This in addition to giving higher remuneration to farmers can potentially alleviate the twin problems of shortage of edible oils and energy in the country.  As a result there will be tremendous savings to the country’s foreign exchange reserve. 

 

 

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30.  Misra A, Tripathi BK (2006) Feasibility of mechanical harvesting of sugarcane (Saccharum spp. Hybrid)  Ind  J Agron  51 : 65-67

 

31.  Murti KS,  Achaya KT (1975)  Cottonseed chemistry and technology in its setting in India.  Publications and Information Directorate, CSIR, New Delhi  348 p

 

32.  NATP (2004) Annual Report of RNPS-24 entitled, “Developing sorghum as an efficient biomass and bio-energy crop and providing value addition to the rain damaged kharif grain for creating industrial demand. National Research Center for Sorghum Rajendranagar Hyderabad  pp 31

 

33.  Parikh J (2005) Growing our own oils.  Biofuels India Vol. III (3) : 7

 

34.  Peterson JBD (2006) Ethanol production from agricultural residues.  Intl Sugar J 108 : 177-180

 

35.  Planning Commission (2003) Report of the committee on development of biofuel, Government of India, New Delhi-110 001. 164 p               

 

36.  Prasad MVR (1994)  Minor oil bearing species of forest origin for diversification of vegetable oil production  In : Prasad MVR et al. (ed)  Sustainability in Oilseeds, Indian Society of Oilseeds Research, Hyderabad : 91-98

 

37.  Reddy BN, Sudhakara Babu SN, Ravishankar G, Sahadeva Reddy B, Jayapradha A (2002) Effect of levels of nitrogen and phosphorus on the performance of sunflower (Helianthus annuus L) in rice fallow vertisols.  J Oilseeds Res 19 : 226-228  

 

38.  Sarada Devi Y, Subrahmanyam MVR, Bheemaiah G (2002)  Effect of cropping systems and nitrogen levels on growth, yield and economics of rainfed castor intercropped with Melia azedarach Linn. J Oilseeds Res 19 : 154-156

 

39.  Shukla, SK (2005) Experiences of Chattisgarh biofuel development authority.  Biofuels India  Vol. III (4) : 12-13

 

40.  Sify business.  14 January 2006.  Sugar coops to supply ethanol to oil PSUs (http://sify. com/finance/fullstory.php?id=14120285)

 

41.  Singaravel R, Imayavaramban Y, Dhanunathan K, Shanmughapriya N (2001)  Response of sesame (Sesamum indicum L) to manganese and zinc nutrition. J Oilseeds Res 18 : 136-138

 

42.  Thakur NS, Deshmukh MR, Reddy RK, Sharma RS (2004) Evaluation of niger Guizotia abyssinica (Coss) productivity under resource constraints.  J Oilseeds Res 21 : 200-201

 

43.  Tree borne oilseeds  (1978) Directorate of Non edible Oils and Soap Industry.  Khadi and Village Industries Commission.  64 p 

 

44.  Turkenburg WC (2000) Renewable Energy Technologies. In : Goldemberg J (ed) World Energy Assessment, United Nations Development Programme, New York NY, USA : 219-272

 

45.  UNCTAD (2006) Info Comm Market Information in the commodities area (http://ro. unctad.org /infocomm/anglais/ cotton/crop.htm)

 

46.  Williams RH, Larson ED, Katofsky RE, Chen J (1995) Methanol and hydrogen from biomass for transportation, with comparisons to methanol and hydrogen from natural gas and coal. PU/CEES Report 292, Princeton University/Center for Energy and Environmental Studies, Princeton NJ, USA


 

 

Table 1 :  World ethanol production in 2004 and major feedstock

 

Country

Feedstock

Million Liters

           Brazil

       Sugarcane

15,099

           United States

       Corn

13,381

           China

       Corn, wheat

  3,649

           India

       Sugarcane

  1,749

           France

       Sugarbeet, wheat, corn

     829

 

Source :  F.O. Licht, cited in Renewable Fuels Association, Homegrown for the Homeland : Industry Outlook 2005 (Washington, DC), p. 14.

 

 

Table 2 : Crop residue production in India, U.S. and the world in 2001

 

Crop

India

U.S.

World

                           ------------------------    106 tonnes      -------------------------

           Cereals

396

367

2802

           Legumes

 24

  82

  305

           Oil crops

 22

  20

  108

           Sugar crops

-

  14

  170

           Tubers

-

    5

-

           Total

442

488

3385

 

Source : Adapted from Lal, 2004a, b;  2005a, b.

 

 

Table 3 :  Ethanol production from residues of some crops

 

Crop

Ethanol yield (L Kg-1)

                       Barley straw

0.31

                       Corn stover

0.29

                       Oat straw

0.26

                       Rice straw

0.28

                       Sorghum straw

0.27

                       Wheat straw

0.29

                       Sugarcane bagasse

0.28

 

Source : Adapted from Kim and Dale, 2004.

 

 


Table 4 :  Biofuel potential of different oilseed crops in comparison with sweet sorghum and sugarcane

 

Sr. No.

Crops

Seasons

Potential seed* yield/

season (kg/ha)

 

Average oil yield/ season (kg/ha)

Average dry crop residue yield/ season** (kg/ha)

Energy production  from oil/ season

(MJ/ha)

X 103 

Energy  from crop residues/ season (MJ/ha) 

 X 103

Total energy production/  season (MJ/ha)

X 103

References

1.

Castor

Rainfed

Monsoon

 

1267

 

621

 

3801

 

25.8

 

22.9

 

48.7

12, 38

Irrigated

3000

1470

9000

61.1

54.2

115.3

2.

Groundnut

Rainfed

Monsoon/Winter

 

1500

 

750

 

3045

 

31.2

 

18.3

 

49.5

3, 12,

Irrigated

2186

1093

4438

45.5

26.7

72.2

3.

Mustard

Rainfed

Winter

 

613

 

251

 

3766

 

10.4

 

22.7

 

33.1

7, 12

Irrigated

1385

568

8508

23.6

51.3

74.9

4.

Sunflower

Rainfed

Monsoon/ Winter

 

1028

 

401

 

3255

 

16.7

 

19.6

 

36.3

12, 37

Irrigated

1691

659

5355

27.4

32.3

59.7

5.

Safflower

Rainfed

Winter

 

1034

 

310

 

3102

 

12.9

 

18.7

 

31.6

12, 13

Irrigated

1688

506

5064

21.0

30.5

51.5

6.

Rapeseed

Rainfed

Winter

 

898

 

368

 

4384

 

15.3

 

26.4

 

41.7

7, 12

Irrigated

1027

421

5014

17.5

30.2

47.7

 

 

 

 

Table 4 contd….2

 

Sr. No.

Crops

Seasons

Potential seed* yield/

season (kg/ha)

 

Average oil yield/ season (kg/ha)

Average dry crop residue yield/ season** (kg/ha)

Energy production  from oil/ season

(MJ/ha)

X 103 

Energy  from crop residues/ season (MJ/ha) 

 X 103

Total energy production/  season (MJ/ha)

X 103

References

7.

Soybean

 

Monsoon

1705

307

3166

12.8

19.1

31.9

5, 12, 17

8.

Linseed

Rainfed

Winter

 

861

 

319

 

1599

 

13.3

 

9.6

 

22.9

8, 12

Irrigated

1097

406

2037

16.9

12.3

29.2

 

9.

 

Niger

 

 

Monsoon

 

304

 

122

 

3593

 

5.1

 

21.6

 

26.7

 

12, 42

10.

Sesame

Rainfed

Monsoon/ Winter/ Summer

 

516

 

258

 

1395

 

10.7

 

8.4

 

19.1

12, 41

Irrigated

616

308

1665

12.8

10.0

22.8

11.

Cotton

Rainfed

Monsoon

 

463 (268)

 

35

 

1030

 

1.5

 

6.2

 

7.7

9, 15, 18, 31

Irrigated

2060 (1195)

155

4585

6.4

27.6

34

12.

Jatropha

 

Perennial

3750

1200

-

49.9

-

49.9

1

 

 

 

 

Table 4 contd….3

 

Sr. No.

Crops

Seasons

Potential seed* yield/

Season (kg/ha)

 

Average oil yield/ season (kg/ha)

Average dry crop residue yield/ season** (kg/ha)

Energy production  from oil/ season

(MJ/ha)

X 103 

Energy  from crop residues/ season (MJ/ha) 

 X 103

Total energy production/  season (MJ/ha)

X 103

References

13.

Sweet sorghum
Monsoon

 

 

 

 

1000

 

 

980 (ethanol)

 

 

8750

 

 

26.4

(ethanol from juice)

 

 

63.3

 

 

89.7

6, 32

Winter

Rainfed

2900

236 (ethanol)

5250

6.3

(ethanol from juice)

29.4

35.7

Irrigated

7400

351 (ethanol)

6000

9.4

(ethanol from juice) 

33.1

42.5

 

14.

Sugarcane

 

July-Aug. to Oct.-Nov.

15 months

-

4400 (ethanol)

34268

118.4

(ethanol from juice)

20.6

(bagasse)

139

30, 35

 

*    Potential seed yield of each crop has been taken from the sources cited. Cotton seed yield given in paranthesis is 58% of seed cotton yield 45.

 

**  Average crop residue yield for different crops has been estimated from the potential seed yield (average) furnished in the present table and the harvest indices in the articles cited.


 

 

Table 5 : Estimated bio-energy production and net returns from sweet sorghum and oilseed-based cropping system (Rainfed)

 

Sr. No.

Season and crop

Bio-energy Production (MJ/ha X 103)

Net Returns (Rs/ha)

Bio-energy X Net returns

X 104

Monsoon

Winter

Monsoon

Winter

Total/year

Monsoon

Winter

Total/year

1.

Sweet sorghum

Groundnut

89.7

49.5

139.2

12500

18773

31273

435.3

2.

Sweet sorghum

Rapeseed

89.7

41.7

131.4

12500

11599

24099

316.7

3.

Sweet sorghum

Mustard

89.7

33.1

122.8

12500

12806

25306

310.8

4.

Sweet sorghum

Sunflower

89.7

36.3

126

12500

11839

24339

306.7

5.

Sweet sorghum

Safflower

89.7

31.6

121.3

12500

11365

23865

289.5

6.

Castor

Sweet sorghum

48.7

35.7

84.4

16810

15800

32610

275.2

7.

Sweet sorghum

Linseed

89.7

22.9

112.6

12500

10997

23497

264.6

8.

Soybean

Sweet sorghum

31.9

35.7

67.6

16880

15800

32680

220.9

9.

Sweet sorghum

Sesame

89.7

19.1

108.8

12500

7117

19617

213.4

10.

Niger

Sweet sorghum

26.7

35.7

62.4

5563

15800

21363

133.3

11.

Cotton

Sweet sorghum

7.7

35.7

43.4

7715

15800

23515

102.0

12.

Jatropha

Jatropha

-

-

49.9

-

-

15000

74.8

 


Table 6 : Estimated bio-energy production and net returns from sweet sorghum and oilseed-based cropping system (Irrigated)

 

Sr. No.

Season and crop

Bio-energy Production (MJ/ha X 103)

Net Returns (Rs/ha)

Bio-energy X Net returns

X 104

Monsoon

Winter

Monsoon

Winter

Total/year

Monsoon

Winter

Total/year

1.

Sweet sorghum

Groundnut

89.7

72.2

161.9

12500

26905

39405

638

2.

Sweet sorghum

Rapeseed

89.7

47.7

137.4

12500

15133

27633

380

3.

Sweet sorghum

Mustard

89.7

74.9

164.6

12500

30729

43229

711.5

4.

Sweet sorghum

Sunflower

89.7

59.7

149.4

12500

21855

34355

513.3

5.

Sweet sorghum

Safflower

89.7

51.5

141.2

12500

18614

31114

439.3

6.

Castor

Sweet sorghum

115.3

42.5

157.8

47943

46800

94743

1495

7.

Sweet sorghum

Linseed

89.7

29.2

118.9

12500

13188

25688

305.4

8.

Sweet sorghum

Sesame

89.7

22.8

112.5

12500

9241

21741

244.6

9.

Cotton

Sweet sorghum

34

42.5

76.5

29223

46800

76023

581.6

10.

Jatropha

Jatropha

-

-

49.9

-

-

15000

74.8

11.

Sugarcane

Sugarcane

-

-

139

-

-

85000

1181.5


 

Table 7 : Available potential of tree-borne oilseeds in India

 

Sr. No.

TBOs

Seed yield 10 (lakh tonnes)

Oil content 36, 43 (%)

Oil yield (lakh tonnes)

1.

Sal (Shorea robusta)

62.0

12

7.44

2.

Mahua (Madhuca indica)

5.2

35

1.82

3.

Neem (Azadirachta indica)

5.0

20

1.0

4.

Rubber (Hevea brasiliensis)

0.79

45

0.35

5.

Karanja (Pongamia pinnata)

1.11

27

0.30

6.

Kusum (Schleichera oleosa)

0.45

33

0.15

7.

Khakan (Salvadora oleoides)

0.44

33

0.14

8.

Undi (Calophyllam inophyllum)

0.11

60

0.07

9.

Dhupa (Vateria indica)

0.13

19

0.02

10.

Other*

2.0

 

 

 

Total

77.34

 

 

 

Source : Adapted from Damodaram and Hegde (2005).

 

* Other : Maroti (Hydnocarpus wightiana), Palash (Butea monosperma), Pisa (Actinodaphne angustifolia),  Ratanjyot (Jatropha curcas), Tumba (Citrullus colocynthis), Teak (Tectona grandis)

 

 

 


 


 


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