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Advanced bio-hydrocarbons are second generation biofuels and are derived from lignocellulosic biomass such as trees, grasses, waste, agricultural or forest residues, or algae. These fuels are not produced using the agricultural commodities like corn, sugarcane, soybean, etc.

Introduction

The advance biohydrocarbons does not require significant modification in the existing fuel distribution infrastructure and also the vehicle engine. Advanced biohydrocarbons are also known as drop-in fuel. The energy content of advanced bio-hydrocarbons is equivalent to that of their petroleum-based counterparts. There are several pathways that can produce advanced bio-hydrocarbons. NSF (2008) suggests these primary methods:

  • Fermentation (Microbial Processing):The biomass is pre-treated with heat, enzymes, or acids to make the cellulose easier to break down into simple sugars using a chemical reaction called hydrolysis. Genetically engineered microorganism is specially introduced in the sugars from the biomass for the fermentation process quite similar to the process used to ferment corn or sugarcane to produce ethanol. However, instead of breaking the sugars further to alcohol these special micro-organisms break the sugars to hydrocarbons.
  • Gasification: In this process, the solid woody biomass at very high temperature is converted to Carbon Monoxide (CO) and Hydrogen (H2), called syngas. Syngas is then further converted to liquid fuel through the Fischer-Tropsch (FT) synthesis. Syngas is the starting material for catalytic chemical reactions for the Fischer-Tropsch synthesis. Hydrocarbon synthesis from biomass-derived syngas (bio-syngas) has been investigated as a potential way to use biomass. Only biomass offers the possibility to produce liquid, carbon neutral, transportation fuels (Tijmensen et al., 2002).
  • Pyrolysis: Similar to gasification, the untreated solid woody biomass is heated in high temperature in the absence of oxygen for breaking down the complex lignin structure into intermediate bio-oil. Furthermore, catalytic reaction called hrdrotreating is used to refine the bio-oil produced by pyrolysis.
  • Algal conversion: There are currently three main way to produce a fuel from algae: (1) Algae is genetically engineered to secrete bio-oils efficiently; (2) A bio-oil extract from algae is chemically treated to produce a bio-oil; or (3) Algae cultures are converted in their entirety via pyrolysis. The algae can be genetically modified to prosper in otherwise harsh conditions (e.g., high salinity or nonpotable water). In all cases, the bio-oil product derived from algae is refined via hydrotreating and becomes a liquid fuel similar to diesel or gasoline.

Figure 1 illustrates chemical, biological and thermal production pathways for advanced bio-hydrocarbons derived from woody biomass and algae. The production of gasoline, jet fuel and diesel depends on the pathways one follows.

Biological and Chemical Catalysts: All the production processes discussed above are formed as the result of biological and chemical catalysis. Catalysis is a process in which a catalyst is added to a chemical reaction to increase the rate of reaction without being consumed by the reaction. As shown in Figure 1 most of the steps of the biofuel production undergoes with help of chemical reaction.

Feasibility of technology and operational necessities

This algal conversion technology is still in research and development phase and commercially not available. Many studies are been carried out to harvest the algae in large scale. The harvesting technique had been addressed successfully by many industries. Studies show that it will take another 10-15 years for commercial scale production of algal biofuels. For this to be achieved, an economic process must be established that will include efficient algal cultivation, harvesting and extraction (Kovalyova, 2009)

On the other hand, the liquid fuel produced by the FT synthesis has similar characteristics as that of gasoline. The fuel contains neither sulfur nor aromatic compounds which is responsible for soot formation. Commercial airlines in South Africa has been using 50% blend of FT liquids. Plants in Malaysia, Qatar and South Africa (existing and planned) can produce up to 75,000 barrels of jet fuel per day at a cost of $ 1.40 to $2.50 per gallon. (Hileman et al., 2009).

Status of the technology and its future market potential

The blue map scenario of Energy Technology Perspective analyses until 2050 shows that biofuels can provide 27% (32 EJ) of the total transportation fuel demand in 2050. As advanced biofuels commercialize, they will eventually provide the major share of biofuel, whereas most oil- and starch-based conventional biofuels are expected to be phased out because of rising and increasingly volatile feedstock prices. The projected use of biofuels could avoid around 2.1 Gt of CO2 emissions per year when produced sustainably (IEA, 2011).

Many developing countries rely on fossil fuel import to meet their domestic energy demands. Developing countries therefore can establish a sustainable biofuel industry to diversify their energy source and decrease their dependency on fossil fuels. This will help improve the economic situation of these countries (UN energy, 2007).

Advanced biohydrocarbons encourages feedstock trade in future for the developing countries. It can also attract the foreign investment, which can help in development of rural sector ultimately leading to enhanced development of feedstock cultivation and handling skills.

In 2009, five major oil companies – BP, Chevron, ExxonMobil, Royal Dutch Shell, and Total announced joint ventures with biofuel companies to work on the development of advanced bio-hydrocarbons. Shell Company in Malaysia has the world’s first commercial-scale gas-to-liquid (GTL) plant based on FT synthesis operating since 1993, and continues to produce approximately 15,000 barrels per day. Estimates of global production of GTL in 2017 are between 200,000 and 300,000 barrels per day (Hileman et al., 2009).

Currently, there are no low-cost technologies to convert the large fraction of energy in biomass or the bio-oils derived from algae into liquid fuels efficiently. There is a need to reduce the production cost for making the bio-hydrocarbon fuels cost competitive (Smith and Allen, 2011). Unless the biofuels becomes cheaper than fossil fuel it cannot compete the fossil fuel market.

Second and third generation biofuel can be successfully developed and deployed only after significant technology improvements. These barriers exist in processes such as selective thermal processing, liquid-phase catalytic processing of sugars and bio-oils, and catalytic conversion of bio-gas (Pew Center, 2010; Sims et al. 2009).

Current support for biofuels generally falls into three categories:1) Policies that mandate levels of use of biofuels, 2) Policies that offer subsidies or tax credits for fuel production and/or use, and 3) Research initiatives.

Policies can play a crucial role in developing the market of biofuels. According to a study by REN21 (2011), almost 31 countries have blending mandates in national level. Similarly, policies that offer fuel-tax exemptions and production subsidies exist in at least 19 countries.

For example, Thailand has blending mandates of B3 and E10, Ethiopia of E10, Brazil of E20-25, India of B10 and E10 as of 2008; B20 and E20 by 2017 etc. Similarly, there is subsidies for public-access biofuel station in USA and fuel tax exemption in countries like Argentina, France, UK , USA, South Africa ( REN 21, 2011).

How the technology could contribute to socio-economic development and environmental protection

Socio-economic development: Growing interest in second generation biofuels worldwide is not just due to climate change and energy security but also due to its possible contribution to socio-economic development, outlined below:

  • Advanced biohydrocarbons addresses the food security issues as the feedstock for producing these fuels are not the food crops.
  • Advanced biohydrocarbons can help protecting the trade balance and foreign exchange of a country. This is achieved by importing less petroleum products.
  • Unlike the first generation biofuels, the second generation biofuels create more employment opportunity in the innovative industry which is a highly skilled job and less educated employment in the agricultural sector (Londo et al., 2009).
  • The value addition to the residues can increase the rural incomes (IEA, 2010).
  • The use of biohydrocarbons has positive health impacts, reducing the level of air pollution and related illnesses (Ewing and Msangi, 2009).

Environmental Benefit / Emission Reduction Potential: The environmental benefits of advanced bio-hydrocarbons are significant. Since climate change is an emerging issue, biofuels have very good potential to address the climate change, land use change and food security issues.

  • The primary feedstock for advanced bio-hydrocarbons is woody biomass and algae. These feedstock are unlikely to change the land-use change pattern much and affect the bio-diversity as compared to first generation fuels.
  • Advanced bio-hydrocarbon fuels are chemically equivalent to the fuels derived from petroleum, which may make it possible to link bio-refining processes to existing petroleum refineries. This has the potential to reduce the environmental impact of construction of new refineries and distribution networks and other fueling infrastructure.
  • Life Cycle analyses of biofuels show that it can replace fossil fuels. Since bio-hydrocarbon fuels have the potential to displace the fossil fuels it has GHG reduction potential as well (Carriquiry et al., 2010). Table 1 compares the GHG mitigation potential of selected biofuels compared to fossil fuels using the LCA technique (Land use changes not included in the analysis).

Financial requirements and costs

Currently, second generation biofuels are more capital intensive than the first generation biofuels. It is very important that the biofuel cost is competitive to cost of fossil fuel in order to displace it. IEA (2010) reports that currently the investment cost of second generation biofuel plant with capacity of 50-150Ml/yr. are estimated to be USD 125-250 (IEA, 2008). This is around ten times more than the first generation biofuel. However, in Brazil, China, India and Thailand, large bioenergy projects with investments exceeding USD 200 million have already been successfully completed (IEA, 2010).

There are four primary factors that determine the cost of the biofuels; the feedstock, capital cost (e.g. chemical processing, refining and finishing the crude product), operation and maintenance cost and the transportation and distribution of finished fuel.

  • Feedstock Cost: The cost of woody biomass feedstock is dependent on a number of factors including, but not limited to: crop yield, land availability, harvesting, storage and handling, and transportation costs. According to a study by Hamelinck and Faaij (2006) feedstock cost can be up to 45-58% of the total production costs. Hubert (2006) estimates a cost of $34 to $70 per dry ton, or $5 to $15 per barrel of oil energy equivalent. These studies focus mainly on feedstocks like agricultural residue, non-food crops, forest residue, dedicated energy crops and Jatropha and algae. Table 2 shows the estimated cost of selected feedstocks.
  • Capital Investment and production cost:Piccolo and Bezzo (2009) presented the capital invested by the processes used to produce the biohydrocarbons fuel; namely enzymatic hydrolysis and fermentation (EHF) process and Gasification and Fermentation (GF) process. The cost is divided into sections for ease. The five sections are a) biomass feedstock pre-treatment, b) Cellulose Hydrolysis, c) Fermentation, d) Separation and e) Effluent treatment. Table 3 gives the detailed breakdown of the overall cost. The plant is assumed to process 700 thousand dry tones of biomass per year.

According to Hamelinck et al. (2005), advanced conversion technologies can reduce the capital investment from $0.95-$1.27 per liter ethanol and reduce the operating cost to $0.11-$0.25 per liter of ethanol.

IEA (2008) have noted that the second generation ethanol production to be around $0.60-1.30/liter range. However, technological advances can reduce the production costs down to as low as $0.30-0.40 per liter by 2020. Though most studies (IEA, 2008; Hamelick et al., 2005; Picolo and Bezzo, 2009) project different cost for biofuel, this is still more expensive than fossil fuels (Smith and Allen, 2011). The most optimistic assumption for cost estimation targets the price of bio-hydrocarbons to come near that of diesel. However, these estimates can vary for large scale productions.

The cost of transporting biomass feedstocks can increase production costs considerably. The savings derived from economies of scale at centralized facilities are often offset by the increased transportation costs of the raw material. Developing a distribution system that is built on local and distributed production facilities rather than large centralized facilities will help reduce transportation costs.

In terms of net production, various start-up companies anticipate that in the long term, advanced bio-hydrocarbons will be competitive with conventional petroleum products at oil prices of about $40–60 per barrel (Regalbuto, 2008).

References

  • Carriquiry, M. A., Du, X. and Timilsina, G. R. (2010). Second Generation Biofuels: Economics and Policies. Policy Research Working Paper, 5406.
  • Carriquiry, M. A., Du, X., and Timilsina, G. R. Hamelinck, C., and Faaij, A. (2006). Outlook for Advanced Biofuels.Energy Policy.Vol. 34, pp 3268-3283.
  • Ewing, M. and Msangi, S. (2009). Biofuels Production in Developing Countries: Assessing Tradeoffs in Welfare and Food Security.Environmental Science and Policy. Vol. 12 (4). pp. 520-528.
  • Hamelinck, C., and A. Faaij,(2006). Outlook for Advanced Biofuels.,Vol. 34, pp. .3268-3283.
  • Hamelinck, C., Hooijdonk, G. and Faaij, A. (2005). “Ethanol from Lignocellulosic Biomass: Techno-economic Performance in Short-, Middle- and Long-term.”Biomass and Bioenergy28: 384-410.
  • Hileman, J. I., Ortiz, D. S., Bartis, J. T., Wong, H. M., Donohoo, P. E., Weiss, m. A. and Waitz, I. A. (2009). Near Term feasibility of Alternative Jet fuels. Pittsburg. RAND corporation.
  • Hubert, G. W., et al. (2006) “Synthesis of Transportation Fuels from Biomass: Chemistry, Catalysis, and Engineering.” I, 106, pp. 4044-4098.
  • International Energy Agency (IEA) 2008. From First to second-generation Biofuel Technologies: An Overview of Current Industry and RD&D activities, OECD/IEA, Paris. [[1]]
  • International Energy Agency (IEA), (2011). Technology Roadmaps: Biofuels for Transport. France. Available at: [[2]]
  • International Energy Agency (IEA), (2010). Sustainable Production of Second Generation Biofuels. (Retrieved on December 27, 2011). [[3]]
  • Junginger, M., Faaij, A., Bjorheden, R., and Turkenburg, W. C. (2005). Technological Learning and Cost Reductions in the Wood Fuel Supply Chains in Sweden.Biomass and Bioenergy. Vol. 29 (6), pp 399-418.
  • Kovalyova, S. (2009). European body sees algae fuel industry in 10-15 years. Available at: [[4]].
  • Londo, M., Lensink, S., Wakker, A., Fischer, G., Prieler, S., Velthuizen, H., Wit, m., Faaij, A., Junginger, M., Berndes, G., Hansson, J., Egeskog, A., Duer, H., Lundbaek, J., Kupczyk, A., Konighofer, K. (2009). The REFUEL EU road map for biofuels in transport: Application of the project's tools to some short-term policy issues. Biomass and Bioenergy. Vol. 34 (2), pp. 244-250.
  • Manzone, M., Airold, G., and Balsari, P. (2009). Energetic and economic evaluation of poplar cultivation for the biomass production in Italy.Biomass & Bioenergy, Vol.33, pp 1258-1264.
  • Mapemba, L., Eppin, F.M., Taliaferro, C.M., and R.L. Huhnke. (2007). Biorefinery Feedstock Production on Conservation Reserve Program Land.Review of Agricultural Economics.Vol. 29, pp 227-246.
  • National Renewable Energy Laboratory (NREL). (1998). Lignocellulosic Feedstock Resource Assessment. TP-580-24189, Sep. 1998.
  • NSF. 2008. Breaking the Chemical and Engineering Barriers to Lignocellulosic Biofuels: Next Generation Hydrocarbon Biorefineries.Ed. George W. Huber, University of Massachusetts Amherst. National Science Foundation. Chemical, Bioengineering, Environmental, and Transport Systems Division. Washington D.C. 180 p.
  • Organization for Economic Co-operation and Development . (2008). Economic Assessment of Biofuel Support Policies. Paris.
  • Pew center (2010). Advanced biohydrocarbons. Global Climate Change Centre. Available at:www.dev-pewclimateteam.p2technology.com/docUploads/Advanced biohydrocarbons final.pdf
  • Piccolo, C., and F. Bezzo. (2009). A Techno-economic Comparison between Two Technologies for Bioethanol Production from Lignocellulose.Biomass and Bioenergy.Vol. 33, pp 478-491.
  • REN21. (2011). Renewable 2011 Global Status Report. Paris. Ren21 Secretariat. Available at: [[5]] (Accessed April, 2012).
  • Regalbuto, J. (2008). Cellulosic Biofuels – Got Gasoline?Science, Vol. 325, 5492, pp. 822-824.
  • Sims, R. E. H., Mabee, W., Saddler, J.N., and Taylor, m. (2009). An overview of second generation biofuel.Bioresource Technology. Vol. 101(6). Pp 1570-1580.
  • Smith, C. D. and Allen. S. (2011). Biofuels from algae. The parliamentary office of science and technology. London. Available at: www.parliament.uk/briefing-papers/POST-PN-384.pdf (Accessed April, 2012).
  • Tijmensen, M.J.A., Faaij, A.P.C., Hamelinck, C.N. and van Hardeveld, M.R.M. (2002), Exploration of the possibilities for production of Fischer–Tropsch liquids and power via biomass gasification.Biomass Bioenergy, Vol. 23, pp. 129–152
  • UN Energy, (United Nations Energy) (2007). Sustainable Bioenergy: A Framework for Decision Makers, Available at: [[6]]
  • Wang, M., Wu, M., and Huo, H. (2007). Life-Cycle Energy and Greenhouse Gas Emission Impacts of Different Corn Ethanol Plant Types.Environmental Research Letters. Vol. 2, pp 1-13.
  • Whitaker, M, and G. Heath. 2009. Lifecycle Assessment of the Use of Jatropha Biodiesel in Indian Locomotives. Technical Reports NREL/TP -6A2-44428, National Renewable Energy Laboratory. Available at: [[7]]
  • World Watch Institute. (2007). Biofuels for Transport: Global Potential and Implications for Sustainable Energy and Agriculture.” Ed. S. Hunt. Sterling VA.
  • World Bank, (2010). “Second Generation Biofuels: Economics and Policies”. Policy Research Working Paper, 5406.
Collection

Advanced biofuels

  • Objective

    Background: This invention relates to systems and methods for the production of linear and branched-chain hydrocarbons such as triterpenes. In particular the invention relates to transgenic plants for use in the production of triterpenes as an alternative source for biofuels and petrochemicals. Technology Description: Terpenes are a large and diverse class of organic compounds and triterpenes are one type of terpenes consisting of six isoprene units and having the molecular formula C30H48. Linear branched-chain triterpenes have direct commercial value in numerous fields.

  • Objective
    Technology

    Summary: The Wisconsin Alumni Research Foundation (WARF) is seeking commercial partners interested in developing a cell-free system that can be used to discover and produce target polypeptides capable of transforming biomass into fermentable sugars for use in the efficient production of biofuels. Detailed Technology Description: Biofuels produced from biomass provide a promising alternative to fossil fuels. Biomass is an inexpensive readily available and renewable resource. However the process of converting biomass into biofuels is difficult and costly.

  • Objective

    To achieve high yields of glucose and other products for use in biofuels and bio-based chemicals lignocellulose must first be pretreated. The goal of pretreatment is to decrease the crystallinity of cellulose increase the biomass surface area remove hemicellulose and break the lignin seal. Current pretreatments use liquid ammonia dilute acid organosolvents and steam among others. Each of these methods has drawbacks in its ability to effectively and efficiently pretreat and process lignocellulosic biomass.

  • Objective

    Ethanol from cellulose promises to provide a replacement for gasoline in greater quantity and at lower cost than ethanol from corn. The anaerobic bacterium Clostridium thermocellum is an excellent candidate for conversion of renewable cellulose biomass to ethanol because it is a robust thermophile with stable enzymes. Clostridium thermocellum is a thermophile with cellulase genes. It is an ideal candidate for these genetic manipulations. Although C.

  • Objective

    Solid carbon-containing materials such as wood chips may be converted into liquid fuels using a gasification process. The potential of this technology has been long overlooked because energy production using traditional methods has been more cost-effective. However with the recent increases in the cost of energy and concerns about carbon emissions gasification is becoming more attractive as an alternative energy source.

  • Objective
    Technology

    Background: Whether we are past right on top of or heading towards peak oil production we are experiencing a consistent increase in demand for renewable energy sources as our dependence on oil becomes more prominent. There is much need for biofuel as a renewable source of energy as it has positive sustainability factors. Shell ExxonMobil and British Petroleum have made substantial investments in algal biofuel production. Any amount of fuel produced would be easily consumed by the market. Current methods of biofuel production utilize crops that could otherwise be used for agriculture.

  • Objective

    The primary synthesis product is methanol an alcohol with chemical and physical properties that are nearly identical to ethanol. The means to synthesize carbon-neutral fuels is designed to be self-contained easily transportable and may be operated at existing sites that emit carbon dioxide (e.g. fermentation plants) and/or sites with abundant (renewable) low cost electricity which may be used to disassociate water in order to obtain the requisite hydrogen. The plant consumes carbon dioxide from the atmosphere or carbon dioxide destined to be emitted into the atmosphere (e.g.

  • Objective

    Lignocellulosic biomass is a very desirable feedstock for biofuel production. If the fermentation process for lignocellulose could be optimized conversion of this biomass could yield 25 to 50 billion gallons of ethanol or other biofuels per year. However lignocellulose which is composed of lignin cellulose and hemicelluloses is resistant to chemical or enzymatic hydrolysis. This resistance is a key limiting step in the conversion of biomass into fermentable sugars.

  • Objective
    Technology

    Ethanol can be produced from most raw ingredients that contain sugar or starch, which can in turn be broken down to sugar. In the Norrköping factory wheat, rye and barley are used as raw ingredients. Around 550,000 tonnes of grain are required to produce 210,000 m3 of ethanol. With a yield of 5.5 tonnes per hectare for wheat/triticale in Central Sweden, the factory's capacity is equivalent to a plantation of 100,000 hectares.