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-à-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.