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Chemical forms of Zn, Ni, Cu, and Pb in municipal sewage sludge were investigated by adding humus soil to sludge and by
performing sequential extraction procedures. In the final sludge mixtures, Zn and Ni were mainly found in Fe/Mn oxide-bound (F3) and
organic matter/sulfide-bound (F4) forms. For Zn, exchangeable (F1), carbonate-bound (F2), and F3 forms were transformed to F4 and
residual forms (F5). For Ni, F1 and F2 forms were transformed to F1, F2, and F3 forms. Both Cu and Pb were strongly associated with
the stable forms F4 and F5. For Cu, F2 and F3 forms were major contributors, while for Pb, F3 and F4 forms were major contributors to
F5. Humus soil dosage and pH conditions in the sludge were strongly correlated with the forms of heavy metals. Five forms were used
to evaluate metal mobilities in the initial and final sludge mixtures. The mobilities of the four heavy metals studied decreased after 28
days. The metal mobilities in the final sludge mixtures were ranked in the following order: Ni > Zn > Cu = Pb. Leaching tests showed
that the mobilities of Zn and Ni in lower pH conditions (pH 4) were higher than those in higher pH conditions (pH 8). 相似文献
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以北京市某生活垃圾填埋场作为研究对象,探究了正规填埋场陈腐垃圾资源化利用问题。填埋区多点采集样品,按不同粒径段筛分和人工分拣后,对其理化特性进行分析。结果表明:腐殖土粒径主要集中在<60 mm区间,占垃圾总量的53.08%,而塑料等易燃垃圾多集中在>60 mm,占总量的30.46%,采用60 mm筛进行筛分,可有效实现该填埋场中腐殖土和易燃垃圾的分类。参照GB 8172—1987《城镇垃圾农用控制标准》,腐殖土总氮含量低,个别点位蛔虫卵死亡率未达标,其他指标均符合标准,可通过堆肥、补充氮源、作为水泥窑替代原料实现再利用。易燃垃圾平均热值为23.13 MJ/kg,含水率和灰分分别为15.32%和10.21%,依据GB 50634—2010《水泥窑协同处置工业废物设计规范》,可作为水泥窑替代燃料进行再利用。 相似文献
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通过前期盆栽模拟试验发现,汞污染土壤种植香根草木屑和腐殖土或者添加木屑和腐殖土后再种植香根草都能极大抑制汞通过地表径流迁移,但是尚没有开展野外试验进行验证。因此为了进一步验证其效果,本研究在贵州万山汞矿区大水溪村汞污染农田建立了地表径流小区,现场研究了种植香根草及添加木屑和腐殖土后种植香根草对土壤汞固定的影响,研究结果显示:(1)在所有处理小区的地表径流中,颗粒态汞占总汞的96%以上,是汞迁移的最主要途径;(2)在汞污染土壤中种植香根草或者土壤中分别添加木屑或者腐殖土后再种植香根草,都能显著降低地表径流中颗粒态汞含量(46%~67%),进而减少土壤汞通过地表径流向周围环境迁移,且香根草与木屑或腐殖土结合效果更佳;(3)不同处理均降低了地表径流中可溶态汞(13%~31%)的含量。本研究能为汞矿区汞污染土壤修复提供一定理论支持和技术指导。 相似文献
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生活垃圾腐殖土物化性质及资源化利用途径——以浙江省某高龄期填埋场为例 总被引:1,自引:0,他引:1
以填埋龄期23~37a、粒径<15mm腐殖土为对象,测试分析了其物质组成、理化性质和浸出液性质.测试与分析结果表明:腐殖土中粒径范围2~15mm、0.075~2mm和<0.075mm的组分分别占比42.9%~53.9%、40.9%~44.1%和5.1%~13.0%,属于细粒砂土;随着填埋龄期增加,腐殖土特征粒径d50和d10呈现减小趋势,比重明显增大,并在30a后趋于稳定.腐殖土中有机质含量(18.1%~19.1%,)、氮磷钾含量、浸出液pH值(7.26~8.30)及电导率(1.08~2.51mS/cm)等指标均满足国家现行《绿化用有机基质》要求.腐殖土中重金属Cu、Zn、Cd、Cr含量均超出国家现行《土壤环境质量农用地土壤污染风险管控标准(试行)》、《绿化种植土壤》和《绿化用有机基质》的标准要求,内梅罗综合污染指数高达15.48~17.95,属于重度污染类型,且重金属主要富集在粒径<2mm的细颗粒.建议将腐殖土进一步精细化筛分为粒径2~15mm与粒径<2mm两部分,针对粒径<2mm部分采用微生物诱导碳酸盐沉淀等技术,降低重金属浸出浓度.处理后的腐殖土可作为园林绿化、填埋场覆盖以及废弃矿山修复的绿化土层. 相似文献
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