柳枝稷、芒草和阿罗多用于生物燃料生产的矿区复垦

J. Skousen, Travis Keene, Mike Marra, B. Gutta
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引用次数: 17

摘要

利用生物质能来补充国家对乙醇生产和发电厂绿色燃料的能源需求,创造了对不断增长的可靠原料的需求。柳枝稷(Panicum virgatum L.)、芒草(miscanthus x giganteus)和巨型甘蔗(Arundo donax L.)是可能的生物燃料作物,因为它们在广泛的生长条件下产生大量的生物质,包括边缘和开垦的土地。西弗吉尼亚州的气候和大面积可开垦的矿山土地为生物燃料工业提供了大量生物质的土地基础。本研究的目的是确定三种生物质作物在西弗吉尼亚州中部开垦矿区的产量。在WV Alton附近的一个有25年历史的开垦场地,使用除草剂清除了5公顷区域内所有现有的冷季植被。建立了23块面积为0.4 ha的地块。矿区土壤样品的平均pH值为7.5,植物养分供应充足。2个柳枝稷品种(Kanlow和BoMaster)随机分配到10个地块(5个重复),以11 kg ha -1的速度将种子钻入被杀死的草皮。两种类型的芒草(不育的公共品种和私人品种)随机分配到10个地块,在0.8 m的中心种植苗塞。甘蔗分为3个地块,根茎种植在1.5 m的中心。种植后第二年和第三年的9月进行产量测量。Kanlow柳枝稷的产量从2011年的平均4000公斤公顷-1到2012年的4900公斤公顷-1不等。2011年BoMaster柳枝稷的产量较低,为2750公斤/公顷,2012年为3981公斤/公顷。公共品种芒草在2011年的产量为7500公斤/公顷,但在2012年下降到平均4900公斤/公顷。私人芒草品种的产量则大得多,2011年为21880公斤/公顷,2012年为15500公斤/公顷。甘蔗产量较低,2012年平均产量为515公斤公顷。杂草竞争和栽培条件差阻碍了巨藤的生存和生长。维州环境保护部制定的复垦土地产量目标是柳枝稷5000公斤公顷-1和芒草15000公斤公顷-1,但柳枝稷和公共品种的芒草没有达到目标,但私人品种的芒草达到了目标。随着时间的推移,林分不断发展,可能需要更多的时间来实现这些产量目标。
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RECLAMATION OF MINED LAND WITH SWITCHGRASS, MISCANTHUS, AND ARUNDO FOR BIOFUEL PRODUCTION 1
Use of biomass to supplement the nation's energy needs for ethanol production and green fuel for power plants has created a demand for growing reliable feedstocks. Switchgrass (Panicum virgatum L.), miscanthus (Miscanthus x giganteus), and giant cane (Arundo donax L.) are possible biofuel crops because they produce large amounts of biomass over a wide range of growing conditions, including marginal and reclaimed land. West Virginia's climate and large acreage of available reclaimed mine land provide a land base to generate high amounts of biomass for a biofuel industry. The purpose of this study was to determine the yield of three biomass crops on reclaimed mined land in central West Virginia. A 25-year-old reclaimed site near Alton, WV was prepared using herbicides to eliminate all existing cool-season vegetation on a 5-ha area. Twenty-three plots of 0.4-ha in size were established. Mine soil samples showed an average pH of 7.5 and adequate supplies of plant nutrients. Two switchgrass varieties (Kanlow and BoMaster) were randomly assigned to 10 plots (five replications) and seeds were drilled into the killed sod at a rate of 11 kg ha -1 . Two types of miscanthus (sterile public and private varieties) were randomly assigned to 10 plots and planted with seedling plugs on 0.8-m centers. Giant cane was assigned to three plots and rhizomes were planted on 1.5-m centers. Yield measurements were taken in September the second and third years after planting. Yields for Kanlow switchgrass varied from an average of 4,000 kg ha -1 in 2011 to 4,900 kg ha -1 in 2012. BoMaster switchgrass was lower at 2,750 kg ha -1 in 2011 and 3,981 kg ha -1 in 2012. The public variety of miscanthus showed yields 7,500 kg ha -1 in 2011, but decreased to an average of 4,900 kg ha -1 in 2012. The private miscanthus variety was much greater at 21,880 kg ha -1 in 2011 and 15,500 kg ha -1 in 2012. Giant cane yields were low with an average yield of 515 kg ha -1 in 2012. Survival and growth of giant cane was hindered by weed competition and poor establishment. Target yields for reclaimed lands, as established by the WV Department of Environmental Protection of 5,000 kg ha -1 for switchgrass and 15,000 kg ha -1 for miscanthus were not attained with switchgrass and the public variety of miscanthus, but was achieved with the private variety of miscanthus. More time may be needed for these yield goals to be achieved as stands continue to develop over time.
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