Zagury Gerald J, Rincon Bello Jhony A, Guney Mert
Department of Civil, Geological and Mining Engineering, École Polytechnique de Montréal, H3C 3A7, Montréal, Québec, Canada.
Northex Environnement Inc., J0L 1C0, Contrecoeur, Québec, Canada.
Environ Monit Assess. 2016 Apr;188(4):222. doi: 10.1007/s10661-016-5223-5. Epub 2016 Mar 11.
The present study aims to transform a treated soil (TS) into a more desirable resource by modifying physico-chemical properties via amendments while reducing toxic metals' mobility and oral bioaccessibility. A hydrocarbon-contaminated soil submitted to treatment (TS) but still containing elevated concentrations of Cu, Ni, Pb, and Zn has been amended with compost, sand, and Al2(SO4)3 to render it usable for horticulture. Characterization and sequential extraction were performed for TS and four amended mixtures (AM1-4). P and K availability and metal bioaccessibility were investigated in TS and AM2. Amendment improved soil properties for all mixtures and yielded a usable product (AM2 20 % TS, 49 % compost, 30 % sand, 1 % Al2(SO4)3) satisfying regulatory requirements except for Pb content. In particular, AM2 had improved organic matter (OM) and cation exchange capacity (CEC), highly increased P and K availability, and reduced total metal concentrations. Furthermore, amendment decreased metal mobile fraction likely to be plant-available (in mg kg(-1), assumed as soluble/exchangeable + carbonates fractions). For AM2, estimated Pb bioavailability decreased from 1.50 × 10(3) mg kg(-1) (TS) to 238 mg kg(-1) (52.4 % (TS) to 34.2 %). Bioaccessible concentrations of Cu, Ni, and Zn (mg kg(-1)) were lower in AM2 than in TS, but there was no significant decrease for Pb. The results suggest that amendment improved soil by modifying its chemistry, resulting in lower metal mobile fraction (in %, for Cu and Zn) and bioaccessibility (in %, for Cu only). Amending soils having residual metal contamination can be an efficient valorization method, indicating potential for reducing treatment cost and environmental burden by rendering disposal/additional treatment unnecessary. Further studies including plant bioavailability are recommended to confirm results.
本研究旨在通过添加改良剂改变理化性质,降低有毒金属的迁移性和口服生物可及性,从而将经过处理的土壤(TS)转化为更理想的资源。一种经过处理但仍含有高浓度铜、镍、铅和锌的碳氢化合物污染土壤(TS),已用堆肥、沙子和硫酸铝进行改良,使其可用于园艺。对TS和四种改良混合物(AM1 - 4)进行了表征和连续萃取。研究了TS和AM2中磷和钾的有效性以及金属生物可及性。改良提高了所有混合物的土壤性质,并得到了一种可用产品(AM2:20% TS、49%堆肥、30%沙子、1%硫酸铝),除铅含量外均符合监管要求。特别是,AM2的有机质(OM)和阳离子交换容量(CEC)得到改善,磷和钾的有效性大幅提高,总金属浓度降低。此外,改良降低了可能对植物有效的金属可移动部分(以mg kg⁻¹计,假定为可溶/可交换 + 碳酸盐部分)。对于AM2,估计的铅生物有效性从1.50×10³ mg kg⁻¹(TS)降至238 mg kg⁻¹(从TS的52.4%降至34.2%)。AM2中铜、镍和锌的生物可及浓度(mg kg⁻¹)低于TS,但铅没有显著降低。结果表明,改良通过改变土壤化学性质改善了土壤,导致金属可移动部分(以%计,对于铜和锌)和生物可及性(以%计,仅对于铜)降低。改良残留金属污染的土壤可能是一种有效的增值方法,表明有可能通过无需处置/额外处理来降低处理成本和环境负担。建议进行包括植物生物有效性在内的进一步研究以证实结果。