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纸浆和造纸厂联合体底灰和飞灰中重金属及硫的化学顺序提取法

Chemical sequential extraction of heavy metals and sulphur in bottom ash and in fly ash from a pulp and paper mill complex.

作者信息

Nurmesniemi Hannu, Pöykiö Risto, Kuokkanen Toivo, Rämö Jaakko

机构信息

Stora Enso Oyj, FI-94800 Kemi, Finland.

出版信息

Waste Manag Res. 2008 Aug;26(4):389-99. doi: 10.1177/0734242X07079051.

Abstract

A five-stage sequential extraction procedure was used to determine the distribution of 11 metals (Cd, Cr, Cu, Mo, Pb, Zn, As, Co, V, Ni, Ba), and sulphur (S) in bottom ash and in fly ash from a fluidized bed co-combustion (i.e. wood and peat) boiler of Stora Enso Oyj Oulu Mill at Oulu, Northern Finland, into the following fractions: (1) water-soluble fraction (H2O); (2) exchangeable fraction (CH3COOH); (3) easily reduced fraction (NH2OH-HCl); (4) oxidizable fraction (H2O2 + CH3COONH4); and (5) residual fraction (HF + HNO3 + HCl). Although metals were extractable in all fractions, the highest concentrations of most of the metals occurred in the residual fraction. From the environmental point of view, this fraction is the non-mobile fraction and is potentially the least harmful. The Ca concentrations of 29.3 g kg(-1) (dry weight) in bottom ash and of 68.5 g kg(-1) (dry weight) in fly ash were correspondingly approximately 18 and 43 times higher than the average value of 1.6 g kg(-1) (dry weight) in arable land in Central Finland. The ashes were strongly alkaline pH (approximately 12) and had a liming effects of 9.3% (bottom ash) and 13% (fly ash) expressed as Ca equivalents (dry weight). The elevated Ca concentrations indicate that the ashes are potential agents for soil remediation and for improving soil fertility. The pH and liming effect values indicate that the ashes also have a pH buffering capacity. From the environmental point of view, it is notable that the heavy metal concentrations in both types of ash were lower than the Finnish criteria for ash utilization.

摘要

采用五阶段连续提取程序,测定了芬兰北部奥卢斯托拉恩索奥伊耶奥卢工厂流化床共燃烧(即木材和泥炭)锅炉底灰和飞灰中11种金属(镉、铬、铜、钼、铅、锌、砷、钴、钒、镍、钡)以及硫(S)在以下组分中的分布:(1)水溶性组分(H₂O);(2)可交换组分(CH₃COOH);(3)易还原组分(NH₂OH-HCl);(4)可氧化组分(H₂O₂ + CH₃COONH₄);(5)残留组分(HF + HNO₃ + HCl)。尽管所有组分中均能提取出金属,但大多数金属的最高浓度出现在残留组分中。从环境角度来看,该组分是不可移动的,潜在危害最小。底灰中钙浓度为29.3 g kg⁻¹(干重),飞灰中钙浓度为68.5 g kg⁻¹(干重),分别约为芬兰中部耕地平均钙含量1.⁶ g kg⁻¹(干重)的18倍和43倍。灰呈强碱性pH(约为12),以钙当量(干重)表示的石灰效应分别为9.3%(底灰)和13%(飞灰)。钙浓度升高表明这些灰是土壤修复和提高土壤肥力的潜在介质。pH值和石灰效应值表明这些灰还具有pH缓冲能力。从环境角度来看,值得注意地是,两种灰中的重金属浓度均低于芬兰灰利用标准。

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