Green diesel production by hydrorefining renewable feedstocks
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Green diesel production by hydrorefining renewable feedstocks Life cycle analysis of green diesel produced from renewable feedstocks indicates relatively high energy efficiency and low greenhouse gas emissions Tom N Kalnes and Terry Marker UOP David R Shonnard and Ken P Koers Michigan Technological University A pproximately 50% of globally produced crude petroleum is refined Water, CO 2 into transportation fuels, the fastest growing component of the energy sector. This sharply rising use of a non-renewable Hydrogen feedstock has a significant impact on Oil, fat grease Light greenhouse gas emissions. Biomass is the R1 Separation fuels only renewable energy source that can be converted into liquid transportation fuels. Product Green diesel R2 recovery Therefore, increasing biofuel usage in the transportation sector can significantly reduce greenhouse gas emissions as well as diversify energy sources, enhance energy Figure 1 Simplified Ecofining process diagram security and stimulate the rural agricultural economy. Worldwide production of biofuels and the volumetric yield of deoxygenated operates in mild conditions and integrates has experienced rapid growth and increased hydrocarbon products is greater than 100%. well within existing petroleum refineries. If international market demand. Projected Selectivity to diesel boiling-range paraffin required, a portion of the light fuel co-product future shortages of crude oil coupled is very high. The primary deoxygenation can be steam reformed to generate all of the with the growing worldwide demand for reaction by-products are propane, water hydrogen consumed in the process. transportation fuels has also raised interest and carbon dioxide. The effluent from R1 is in synthetic diesels (syndiesels) produced by immediately separated at reactor pressure Feedstocks Fischer-Tropsch (FT) synthesis of a syngas to remove carbon dioxide, water and low Feedstocks that are suitable for the process stream derived from coal (CTL), stranded molecular weight hydrocarbons. The include plant-derived oils such as soybean, natural gas (GTL) or biomass (BTL). resultant diesel is mixed with additional rapeseed and palm. However, in the future, This article describes the UOP/Eni hydrogen gas and then routed to an non-edible oils such as jatropha and algal oils Ecofining process for green diesel production, integrated catalytic hydro-isomerisation will become increasingly important sources and compares the energy efficiency and reactor (R2), where a branched paraffin- of Ecofining feedstock. Unlike base-catalysed green house gas (GHG) emissions associated rich diesel fuel is produced. In this manner, transesterification, the Ecofining process is with green diesel to those of petroleum the cold flow properties of the diesel are robust to high concentrations of free fatty diesel, biodiesel and syndiesel derived from adjusted to meet required specifications. The acids, enabling other, lower-cost materials coal and natural gas. isomerisation reaction is also selective and, such as tallow oil and waste greases to be used as a result, consumes very little hydrogen. as feedstocks. Feedstocks rich in saturated Two-stage hydrorefining Isomerised product is separated from fats, such as palm and tallow oils, require The Ecofining process is an integrated two- excess hydrogen in a conventional gas/ substantially less hydrogen than feedstocks stage hydrorefining process. A simplified liquid separator. After purification, the excess with a higher olefin content, such as soybean block flow diagram of the process is shown hydrogen is recycled back to R1 and R2 to and rapeseed oils. However, depending on in Figure 1. In the process, feedstock is maintain the minimum required hydrogen the concentration of specific contaminants, pumped to process pressure, mixed with partial pressure. Make-up hydrogen is added a pretreatment of these materials to remove recycle hydrogen, then sent to a multi-stage to the process to balance both chemical solids and salts may be required. adiabatic, catalytic hydrodeoxygenation consumption and solution losses. The liquid reactor (R1), where the renewable oil is product is sent to the product recovery Product range saturated and completely deoxygenated. section of the process, where conventional While the primary product of the Ecofining Gas recycle to R1 is set to achieve a minimum distillation steps are employed to separate process is green diesel, smaller amounts of hydrogen partial pressure at the reactor co-products such as propane and naphtha. other renewable fuels are also produced. outlet. Conversion of feed is complete The process for producing green diesel Table 1 contrasts Ecofining inputs and www.biofuels-tech.com BIOFUELS TECHNOLOGY 7
produced in the refinery’s fluid catalytic Comparison of process feeds and main products cracking (FCC) unit. The basis of the study was as follows: Feeds Ecofining green diesel Weight, % Volume, % Feeds Biodiesel Weight, % Volume, % • Northern European location Vegetable oil 100 100 Vegetable oil 100 100 • 150 000 barrels per day (bpd) capacity Hydrogen 1.5–3.8 – Methanol 10 11 • Crude mix: 50% Brent/44% Arab Chemicals 4 – Light/6% Arab Heavy Products Propane Weight, % Volume, % 5 9 Products FAME Weight, % Volume, % 96 100 • Crude price: $491/MT Brent, $458/MT Butane 0–2 0-3 Glycerol 10 7 Arab Light, $423/MT Arab Heavy Naphtha
rapeseed oil, palm oil and inedible tallow. forms of that energy (fossil, biomass and so are transported to a processing facility, Four inventory data sources were included on). Of further interest is the Fossil Energy where they are crushed to extract oil. The in the scope of the expanded study, with Demand (FED), which accounts for all of conversion of plant oil to biodiesel was the aim of adding confidence to the study’s the fossil energy sources used throughout modelled using data from a 2003 Nexant conclusions. The study’s major assumptions the life cycle, including the fossil energy report,1 and conversion to green diesel and references are shown in Table 4. Even contained in the fuel. This is particularly was modelled using data from UOP and though the LCAs reported in the sources in important, because biofuels often require Eni. Tallow, unlike energy crops, is Table 4 used different allocation methods, larger amounts of biomass-derived energy, considered a waste from the meat their inventory data enabled us to calculate which is a renewable source of energy. processing industry, and thus carries no and apply energy allocation factors to the Greenhouse gas emissions were calculated environmental burdens. However, tallow LCAs reported here based on product and co- using the Eco-indicator 95 method in units must still be transported and rendered to product lower heating values. These studies of CO2 equivalents for all GHGs. Primary become a usable feedstock. Once tallow highlight important differences in LCA input GHGs of concern were CO2, N2O and CH4 has been rendered, it can be processed data for many raw material choices. Other (IPCC, 2007). GHG emissions were derived into biofuel in accordance with input data important study assumptions for green from all combustion processes consuming supplied by a 2002 literature source,5 or diesel and biodiesel are the inclusion of N2O fuels containing fossil carbon (diesel for converted into green diesel in accordance emissions, which contribute significantly to transportation, electricity consumption with data supplied by UOP. the greenhouse gas inventories of biofuels and so on). The combustion of bio-based Unlike the cases based on rapeseed from agricultural activities, and the effects fuels in vehicle engines was not included and tallow oils, the palm oil case can vary of land use. Although N2O emissions are in the GHG assessment. For example, green greatly, depending on the process.7 As included in this study, the effects of N2O diesel contains carbon derived only from standard practice, palm meal from the oil variation are not. This factor and land use renewable oils, and therefore CO2 emissions extraction step is burned on-site for power change, although important, are not within following combustion do not count towards generation, so displacing fossil fuels. Palm the scope of this study, but will be included GHG totals. For biodiesel, only methanol- oil mill effluent (POME), a nutrient-rich in future work. derived CO2 (assumed to be of fossil liquid, is anaerobically digested on-site to The system boundaries include the origin) was included in GHG totals from produce a solid that can be used as fertiliser following life cycle stages: raw material combustion emissions. on the palm plantation, a measure that extraction, raw material transportation, raw displaces imported fertiliser. A methane- material processing to final product, product Comparisons of diesel life cycles rich biogas is produced as a digestion by- transportation and end use (combustion in a LCA inputs for low sulphur petroleum diesel product. This is a factor in establishing direct injection-internal combustion engine). were taken from the ecoinvent database in GHG emissions, because the biogas can For end use, biodiesel is often mixed with SimaPro 7.0, assuming average European contain as much as 70% methane by mass. petroleum diesel at a concentration of 20% technology. Biodiesel and green diesel For this study, the composition is assumed (B20). Green diesel can be used as a straight inventory data were input into SimaPro 7.0 to be 70% methane, 20% carbon dioxide, 7% diesel substitute. However, this study only using values from the studies cited in Table nitrogen, 1% hydrogen and 2% hydrogen accounts for the combustion of petroleum 4. Inputs for biofuel production include sulphide. This biogas is often simply vented diesel, syndiesel and biofuels. the farming of an energy crop, in this case to the atmosphere, but can be captured and The functional unit for this LCA is rapeseed or palm oil, or the production of burned on-site for energy production.8 Thus, one megajoule (MJ) of petroleum fuel, tallow. Energy crop production requires there are two likely scenarios: one in FT syndiesel, biodiesel or green diesel. four major inputs: seeds, fertilisers, which the biogas is vented, and another in Inventories of inputs of materials and energy chemicals such as pesticides, and fuel used which the biogas is combusted to produce over the life cycle for each fuel product were for harvesting and sowing, among other electricity for the oil extraction/biofuel accumulated based on this functional unit. farm uses. After harvesting, the seeds processing stage. The software used for this LCA was SimaPro 7.0, and for processes not already in the SimaPro library (such as biodiesel and green Study assumptions and sources diesel conversion process steps) the data were obtained either from the sources cited Diesel source Transportation Study allocation method Data source Coal gasification Estimated Energy Marano, 20016 in Table 1 or supplied by UOP for certain FT synthesis processes such as green diesel production Wax refining via the Ecofining process. NG gasification Estimated Energy Marano, 20016 For this study, the impact assessment FT synthesis methods used in SimaPro were Cumulative Wax refining Energy Demand (CED) and total GHGs Rapeseed Not included Displacement Concawe, 2006 from Eco-indicator 95. The Cumulative Palm oil Estimated Not allocated Yusoff, 20077 Energy Demand is all of the energy that is Tallow Estimated Energy/economic Judd, 20025 consumed throughout the entire life cycle, FT = Fischer-Tropsch, NG = Natural gas including the energy that is contained within the product of interest, as well as primary Table 4 www.biofuels-tech.com BIOFUELS TECHNOLOGY 9
energy inputs compared to those for coal syndiesel. Rapeseed oil biodiesel and green diesel both have a slightly lower CED than 3.5 FT syndiesel, with green diesel requiring Renewable, water 3.0 Renewable, biomass slightly lower inputs than biodiesel. When M J (inp ut )/ M J (o ut p ut ) Non-renewable, nuclear palm oil is used as a feedstock, the CED is 2.5 Non-renewable, fossil substantially higher than for petroleum 2.0 diesel. This reflects the reuse of biomass waste from palm oil production as a fertiliser 1.5 or a thermal energy source. 1.0 Since all of the by-products of palm oil 0.5 production are used in the oil extraction process, the biomass energy inputs are 0.0 higher. Furthermore, all of the environmental el al G el D el C D C el D i es co m N i es O G ies w / B O G w / B i es w G burdens are carried by the oil because no d m o o d S o d l P o d o o fr bi bi e D bi ll um T f r R es G Ta by-products leave the process. Rapeseed as le F FT SO O di O o w rto P o P l l feedstock, for example, shares 39% of the R bi Ta Pe PO burdens with rapeseed cake. So although the inputs for palm oil are much lower, the Figure 2 Cumulative energy demand for petroleum diesel, FT syndiesel, biodiesel and green diesel lack of an allocation somewhat distorts the results. As with rapeseed oil, green diesel from palm oil shows slight benefits over palm oil biodiesel. And for the palm oil 2.5 Use case, fewer energy inputs are needed when Transportation biogas is used as a fuel. 2.0 Fuel production Tallow looks promising as a feedstock. M J (inp ut )/ M J (o ut p ut ) Oil production Cultivation Tallow biodiesel has a slightly higher CED 1.5 than petroleum diesel, while tallow-derived green diesel is the only fuel to have a lower CED than petroleum diesel. 1.0 Fossil Energy Demand (FED) values are shown in Figure 3. The FED of petroleum 0.5 diesel is very close to the CED value, at 1.25 MJ per MJ of fuel. Coal and natural 0.0 gas syndiesel have significantly higher FED el al G se l D G i es e l C D C el D values compared with petroleum diesel, es co N ie /B G / B i es G di m o m o d SO o d l w PO w o d l o w requiring about 60% more fossil energy for o r i i e D i l um T f r f b R b es G b Ta le F FT SO O di O lo w the same energy content of fuel. All of the rto R P i o P l Pe b Ta biofuels have very similar FED values. For PO all feedstocks, green diesel has a slightly lower energy requirement than biodiesel Figure 3 Fossil energy demand for petroleum diesel, FT syndiesel, biodiesel and green diesel (with a more significant reduction for tallow), and palm oil has a slightly lower FED than The production of FT syndiesel varies Energy.6 The impact of carbon sequestration rapeseed oil. In palm oil production, the FED slightly from biofuel production. The coal technologies was not included in this study. is reduced when biogas is combusted. An pathway includes inventory data for the assessment of the processes that contribute current European Union (EU) hard coal Summary of LCA results to the FED shows that fuel use (the mix, as well as gasification using steam Figure 2 indicates Cumulative Energy embodied energy of the fuel itself) is a major reforming and partial oxidation followed by Demand (CED) for petroleum diesel, contributor for FT syndiesel and petroleum FT synthesis. The life cycle for the conversion FT syndiesel, biodiesel and green diesel diesel, but has a negligible effect for biofuels. of natural gas to syndiesel is assumed to derived from various feedstocks. Table 5 For rapeseed oil, cultivation is the largest represent average conditions in Europe, contains a legend for the abbreviations used contributor, with oil processing taking about which includes long-distance transport from in Figure 2. Petroleum diesel, which is used as much energy as fuel production. The Russia and the Middle East. As with the coal as the baseline for comparison, requires cultivation of oil palms requires less energy pathway, steam reforming of natural gas 1.27 MJ of input energy to yield 1 MJ of compared with the cultivation of rapeseed, followed by FT synthesis is included. For diesel fuel. FT syndiesel requires higher as well as fewer oil processing requirements, the syndiesel life cycles, inventory data was energy inputs throughout the life cycle, but more energy is used for processing the input into SimaPro 7.0 from data supplied regardless of feedstock, although natural fuel. Almost all of tallow’s energy demands by a 2001 study for the US Department of gas FT syndiesel requires slightly lower are from fuel production. 10 BIOFUELS TECHNOLOGY www.biofuels-tech.com
GHG emissions associated with fuel life cycles are shown in Figure 4. FT syndiesel 250 produced from a feedstock of coal produces Use more than twice as much greenhouse gas (in Transportation CO2 equivalents) over its life cycle compared 200 Fuel production Oil production with petroleum diesel. Syndiesel from Cultivation g CO2 eq ./ M J natural gas generates fewer emissions than 150 syndiesel from coal, but still produces higher emissions than petroleum diesel. Neither of 100 the syndiesel cases considered the potential impact of emerging carbon sequestration technologies to capture process emissions. 50 All of the biofuels considered produce lower GHG emissions than petroleum diesel. 0 Overall, green diesel emits less GHG than el al G el D el C D C el D i es co N i es O G i es w / B O G w / B i es w G d m o m o d S o d l P o d o biodiesel for all feedstocks. For rapeseed fr D l um T f r o bi R bi es e G bi Ta l oil-based biofuels, cultivation accounts for a le F FT SO O di O o w rto P o P l l R bi Ta significant portion of life cycle GHG, due in Pe PO part to emissions of N2O from the field. Oil palms are responsible for fewer emissions in cultivation compared with rapeseed. Figure 4 Greenhouse gas emissions for petroleum diesel, FT syndiesel, biodiesel and green diesel However, depending on whether or not biogas is burned, palm oil processing can diesel produced via the Ecofining process California Alternative Diesel Symposium, August have a significant effect on GHG production. has environmental benefits over petroleum 2003. If biogas is burned, emissions are low and life diesel, biodiesel and fossil-derived syndiesel 3 Blending Study: Comparative profitability of cycle GHG emissions are very low. Inedible (without carbon sequestration). Although blending green diesel or FAME to meet B5 and B10 Blending Targets, UOP confidential report, tallow, because it carries no environmental green diesel consumes more total energy November 2007. burdens, has very low GHG emissions. to produce than petroleum-derived diesel, 4 Kalnes T, Marker T, Shonnard D, “Green Diesel: A Processing tallow for biodiesel adds a small the majority of this energy is renewable. Second Generation Biofuel”, International Journal amount of GHGs.9 Green diesel produced Compared to biodiesel, green diesel shows of Chemical Reactor Engineering, Vol 5, Article A48, from tallow has emissions that are greatly higher savings in fossil energy per tonne January 2007. reduced, with life cycle GHG emissions as of biofuel, regardless of the source of input 5 Judd B, Biodiesel from Tallow, prepared for low as 2% of petroleum diesel’s emissions. data or differences in study assumptions. Energy Efficiency and Conservation Authority, Overall, green diesel can contribute to the November 2002. Summary world’s growing need for clean diesel fuel. Its 6 Marano J, Life Cycle Greenhouse Gas Emissions Growing worldwide demand for diesel fuel, environmental benefits alone are substantial, Inventory for Fischer-Tropsch Fuels, prepared for coupled with concerns over global warming, but when its fuel properties compared to US DOE National Energy Technology Laboratory by Energy and Environmental Solutions, June has sparked interest in renewable alternatives those of biodiesel are taken into account it 2001. that show the potential for reduced GHG is clear that green diesel technology merits 7 Yusoff S, “Feasibility Study of Performing a Life emissions at a reasonable cost of production. further investigation towards large-scale Cycle Assessment on Crude Palm Oil Production LCA studies indicate that green diesel industrial production. in Malaysia”, International Journal of LCA, Vol 12, produced via the UOP/Eni Ecofining process No 1, January 2007. can be an attractive supplement to petroleum Ecofining is a mark of UOP LLC and Eni SpA. 8 Yusoff S, “Renewable Energy from Palm Oil diesel, biodiesel and syndiesel. However, the — Innovation on Effective Utilization of Waste”, amount of green diesel that can be produced References Journal of Cleaner Production, Vol 14, 2006. will be limited ultimately by feedstock 1 Nexant Chem Systems, PERP Report Biodiesel 9 Zheng D, “Preparation and Properties of Methyl 02/03S2, December 2003. Esters of Beef Tallow”, Bioresource Technology, Vol availability and price. 2 Rockwell J, Conoco Phillips Gas-to-Liquids, 57, No 2, August 1996. Green diesel has quality attributes comparable with those of syndiesel, including complete compatibility with List of abbreviations used Tom N Kalnes is Senior R&D Associate, UOP, US. petroleum diesel, high energy density (44 Email: Tom.Kalnes@uop.com Terry Marker is Ecofining Team Leader, Renewables MJ/kg), low specific gravity (0.78), excellent Acronym Meaning FT Fischer-Tropsch R&D, UOP, US. storage stability and very low combustion NG Natural gas Ken P Koers is an MS candidate, Department of emissions. Furthermore, the cold flow GD Green diesel Chemical Engineering, Michigan Technological properties of green diesel can be adjusted RSO Rapeseed oil University, Houghton, MI, US. within the Ecofining process, enabling the PO Palm oil David R Shonnard is a Professor in the Department producer to adapt to varying feedstock BC Biogas combustion of Chemical Engineering and Deputy Director sources and seasonal product specifications. of the Sustainable Futures Institute, Michigan As determined by LCA studies, green Table 5 Technological University, Houghton, MI, US. www.biofuels-tech.com BIOFUELS TECHNOLOGY 11
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