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Mercury emission control for coal fired power plants using coal and biomass

机译:利用煤和生物质控制燃煤电厂的汞排放

摘要

Mercury is a leading concern among the air toxic metals addressed in the 1990 CleanAir Act Amendments (CAAA) because of its volatility, persistence, and bioaccumulationas methylmercury in the environment and its neurological health impacts. TheEnvironmental Protection Agency (EPA) reports for 2001 shows that total mercuryemissions from all sources in USA is about 145 tons per annum, of which coal firedpower plants contribute around 33% of it, about 48 tons per annum. Unlike other tracemetals that are emitted in particulate form, mercury is released in vapor phase inelemental (Hg0) or oxidized (Hg2+, mainly HgCl2) form. To date, there is no postcombustion treatment which can effectively capture elemental mercury vapor, but theoxidized form of mercury can be captured in traditional emission control devices such aswet flue gas defulrization (WFGD) units, since oxidized mercury (HgCl2) is soluble inwater.The chlorine concentration present during coal combustion plays a major role inmercury oxidation, which is evident from the fact that plants burning coal having highchlorine content have less elemental mercury emissions. A novel method of co-firingblends of low chlorine content coal with high chlorine content cattle manure/biomass was used in order to study its effect on mercury oxidation. For Texas Lignite and Wyomingcoal the concentrations of chlorine are 139 ppm and 309 ppm on dry ash free basis, whilefor Low Ash Partially Composted Dairy Biomass it is 2,691 ppm.Co-firing experiments were performed in a 100,000 BTU/hr (29.3 kWt) Boiler Burnerfacility located in the Coal and Biomass Energy laboratory (CBEL); coal and biomassblends in proportions of 80:20, 90:10, 95:5 and 100:0 were investigated as fuels. Thepercentage reduction of Hg with 95:5, 90:10 and 80:20 blends were measured to be 28-50%, 42-62% and 71-75% respectively. Though cattle biomass serves as an additive tocoal, to increase the chlorine concentration, it leads to higher ash loading. Low Ash andHigh Ash Partially Composted Dairy Biomass have 164% and 962% more ash thanWyoming coal respectively. As the fraction of cattle biomass in blend increases inproportion, ash loading problems increase simultaneously. An optimum blend ratio isarrived and suggested as 90:10 blend with good reduction in mercury emissions withoutany compromise on ash loading.
机译:汞是1990年《清洁空气法》修正案(CAAA)中涉及的空气有毒金属中的主要关注问题,因为它的挥发性,持久性和生物蓄积性是甲基汞在环境中的存在及其对神经健康的影响。环境保护局(EPA)2001年的报告显示,美国所有来源的汞排放总量约为每年145吨,其中燃煤电厂约占其总排放量的33%,即每年约48吨。与以微粒形式排放的其他痕量金属不同,汞以气相非元素(Hg0)或氧化(Hg2 +,主要是HgCl2)形式释放。迄今为止,尚无能有效捕获元素汞蒸气的燃烧后处理方法,但由于氧化汞(HgCl2)可溶于水,因此可以在传统的排放控制装置(如湿法烟气脱硫(WFGD)装置)中捕获汞的氧化形式。煤燃烧过程中存在的氯浓度在汞氧化中起主要作用,这从燃烧高氯含量煤的植物元素汞排放较少的事实中可以明显看出。为了研究其对汞氧化的影响,使用了一种将低氯含量的煤与高氯含量的牛粪/生物质混合燃烧的新方法。对于德州褐煤和怀俄明州煤,无灰分的氯含量分别为139 ppm和309 ppm,而低灰分部分堆肥的乳制品生物质的氯含量为2,691 ppm。以100,000 BTU / hr(29.3 kWt)的锅炉进行共烧实验位于煤炭和生物质能实验室(CBEL)的燃烧器设施;研究了比例为80:20、90:10、95:5和100:0的煤炭和生物质混合物作为燃料。测得95:5、90:10和80:20的Hg减少百分比分别为28-50%,42-62%和71-75%。尽管牛的生物量可以用作煤的添加剂,但是它会增加氯的浓度,但会导致更高的灰分装载量。低灰分和高灰分部分堆肥的乳制品生物质分别比怀俄明州的煤多164%和962%的灰分。随着掺混物中牛生物量的比例增加,灰分装载问题同时增加。达到了最佳的混合比例,建议以90:10的比例混合,同时具有良好的汞排放降低效果,且不会影响灰分负载。

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