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

机译:从纸浆和造纸厂复合物中化学顺序提取底灰和飞灰中的重金属和硫

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A five-stage sequential extraction procedure was used to determine the distribution of 11 metals (Gd, 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 (H_2O); (2) exchangeable fraction (CH_3COOH); (3) easily reduced fraction (NH_2OH-HC1); (4) oxidizable fraction (H_2O_2 + CH_3COONH_4); and (5) residual fraction (HF + HNO_3 + 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 (~ 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.
机译:采用五阶段顺序萃取程序确定底灰和矿渣中11种金属(Gd,Cr,Cu,Mo,Pb,Zn,As,Co,V,Ni,Ba)和硫(S)的分布来自芬兰北部奥卢的Stora Enso Oyj Oulu工厂流化床共燃(即木材和泥炭)锅炉的飞灰分为以下馏分:(1)水溶性馏分(H_2O); (2)可交换部分(CH_3COOH); (3)易于还原的馏分(NH_2OH-HCl); (4)可氧化级分(H_2O_2 + CH_3COONH_4); (5)残留部分(HF + HNO_3 + HCl)。尽管金属可在所有馏分中提取,但大多数金属的最高浓度出现在残留馏分中。从环境角度来看,这部分;是不可移动的部分,危害最小。底灰中Ca的浓度为29.3 g kg〜(-1)(干重),粉煤灰中Ca的浓度为68.5 g kg〜(-1)(干重)分别比1.6的平均值高约18倍和43倍。 g公斤〜(-1)(干重)在芬兰中部的耕地中。灰分的pH为强碱性(约12),并具有9.3%(底灰)和13%(粉煤灰)的石灰效果,以Ca当量(干重)表示。 Ca浓度升高表明灰烬是土壤修复和提高土壤肥力的潜在媒介。 pH和石灰效果值表明骨灰还具有pH缓冲能力。从环境的角度来看,值得注意的是两种灰烬中的重金属浓度均低于芬兰的灰烬利用标准。

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