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Biofuel co-products as livestock feed - Opportunities and challenges

Biofuel co-products as livestock feed - Opportunities and challenges

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<strong>Biofuel</strong>s: their <strong>co</strong>-<strong>products</strong> <strong>and</strong> water impacts in the <strong>co</strong>ntext of life-cycle analysis 497FIGURE 17Average water <strong>co</strong>nsumption in existing maize dry-mill ethanol plants7Consumptive Water Use (Liter Water/Liter Fuel Ethanol)6543215.84.74.2432.70Phillips et al., 2007 USDA 2003 Keeney <strong>and</strong> Muller Keeney <strong>and</strong> Muller20062006Wu 2008 Mueller 2010Source: Wu et al., 2011.TABLE 7Consumptive water use from maize farming to ethanol production in USDA Regions 5, 6 <strong>and</strong> 7 (litre water per litredenatured ethanol produced)USDA Region Region 5 Region 6 Region 7Share of United States ethanol production capacity (%) (1) 50 15 23Share of United States maize production (%) (2) 50 16 23Maize irrigation, groundwater (3) 12 19 224Maize irrigation, surface water (3) 2 3 12Ethanol production (4) 3 3 3Total (maize irrigation <strong>and</strong> ethanol production) without <strong>co</strong>-product allocation 17 25 239Total water <strong>co</strong>nsumption with m<strong>as</strong>s-b<strong>as</strong>ed <strong>co</strong>-product allocation (5) 11 17 160Notes: (1) B<strong>as</strong>ed on 2008 ethanol production capacity in operation (RFA, 2011). (2) B<strong>as</strong>ed on 2008 maize production (USDA-NASS, 2011).(3) USDA, 2008. (4) Production-weighted average (Wu, 2008). (5) M<strong>as</strong>s-b<strong>as</strong>ed <strong>and</strong> carbon displacement-b<strong>as</strong>ed allocation ac<strong>co</strong>rding to theheuristic that one-third of biom<strong>as</strong>s in maize kernel goes to ethanol, one-third goes to CO 2 <strong>and</strong> one-third goes to DDGS.TABLE 8Water <strong>co</strong>nsumption for cellulosic ethanol productionProcessAverage water <strong>co</strong>nsumption(litre/litre biofuel)Electricity export(kWh/litre biofuel)Average water <strong>co</strong>nsumptionafter <strong>co</strong>-product allocation(litre/litre biofuel)Biochemical (Humbird et al., 2011) 5.4 (1) 0.47–0.55 (3) 4.5–4.6G<strong>as</strong>ification (Phillips et al., 2007) 1.9 (1) 0 1.9Pyrolysis (Jones et al., 2009) 2.3 (2) 0 2.3Notes: (1) Cellulosic ethanol produced from switchgr<strong>as</strong>s. (2) Forest residue <strong>as</strong> <strong>feed</strong>stocks. (3) Maize stover 1.77 kWh/gal <strong>and</strong> Switchgr<strong>as</strong>s2.07 kWh/gal, both from a 2000-dry- ton/day ethanol plant. Source: Wu <strong>and</strong> Chiu, 2011.of ethanol, DDGS <strong>and</strong> CO 2 emissions during <strong>co</strong>nversion.Irrigation water is allocated with the same ratio (one-third<strong>as</strong>signed to maize, one-third <strong>as</strong>signed to ethanol).Table 8 <strong>co</strong>mpiles water <strong>co</strong>nsumption during productionof cellulosic ethanol from maize stover, switchgr<strong>as</strong>s,<strong>and</strong>forest residue (Wu <strong>and</strong> Chiu, 2011). No irrigation water isincluded because, in <strong>co</strong>ntr<strong>as</strong>t to maize, these <strong>feed</strong>stocksmay not require irrigation. The electricity generated duringcellulosic ethanol production can displace <strong>co</strong>nventionallyproducedelectricity, the production of which <strong>co</strong>nsumes onaverage 1.6 litres per kWh in the United States (Wu <strong>and</strong>Chiu, 2011). As a result, 0.75 to 0.89 litres of water perlitre of cellulosic ethanol are <strong>co</strong>nserved when ethanol is producedvia biochemical technology. The <strong>co</strong>nsumptive wateruse attributed to each litre of cellulosic ethanol produced istherefore 4.5 to 4.6 litres.

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