Soil health as a proxy for long-term reclamation success of metal-contaminated mine tailings using lime and biosolids

James A. Ippolito , Liping Li , Travis Banet , Joe E. Brummer , Cassidy Buchanan , Aaron R. Betts , Kirk Scheckel , Nick Basta , Sally L. Brown
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Abstract

Mine lands contaminted with heavy metals pose environmental risks, and thus reclamation is paramount for improving soil, plant, animal, and ecosystem health. A metal-contaminated alluvial mine tailing, devoid of vegetation, received 224 ​Mg ​ha−1 of both lime and biosolids in 1998, and long-term reclamation success was quantified in 2019 with respect to soils, plants, and linkages to animals. Reclamation success was quantified using the Soil Management Assessment Framework (SMAF), in conjunction with bioavailable (0.01 ​M CaCl2 extractable) and plant-available (Mehlich-3 extractable) soil metal concentrations, X-ray absorption spectroscopy, plant metal concentrations, and plant quality characteristics. Results showed that all soil indicators were improved in successfully-reclaimed areas as compared to on-site degraded areas, including increases in soil aggregate stability, pH, plant-available P and K, soil organic C, potentially-mineralizable N, microbial biomass C and β-glucosidase activity and decreases in soil bulk density and electrical conductivity. Ofindicators, unitless soil health scores were assigned based on the SMAF, with data suggesting that bulk density, wet aggregate stability, potentially- mineralizable N, microbial biomass C, pH, and electrical conductivity should be monitored in the future. The long-term effects of lime and biosolids application have improved soil physical, biological, and overall soil health. Plant metal concentrations have decreased by an order of magnitude since early reclamation, with most plant metal concentrations being tolerable for domestic livestock consumption. From an animal health perspective, feeding grasses from this site during latter parts of a growing season may need supplemental feed to provide greater protein and energy content, and to reduce potentially-harmful Cd concentrations from food chain bioaccumulation. However, a health concern exists based on soil bioavailable Cd and Zn concentrations that exceed ecological soil screening levels. Still, plants have stabilized the soil and acidity remains neutralized, leading to long-term improvements in soil health, with overall improved ecosystem health.

Abstract Image

土壤健康是矿山尾矿长期复垦成功的代名词
受重金属污染的矿山土地会对环境造成危害,因此复垦对于改善土壤、植物、动物和生态系统健康至关重要。1998 年,一个没有植被的金属污染冲积矿山尾矿接受了 224 兆克/公顷-1 的石灰和生物固体,并于 2019 年对土壤、植物和动物联系方面的长期复垦成功率进行了量化。利用土壤管理评估框架(SMAF),结合生物可利用(0.01 M CaCl2 可提取)和植物可利用(Mehlich-3 可提取)的土壤金属浓度、X 射线吸收光谱、植物金属浓度和植物质量特征,对复垦成功与否进行了量化。结果表明,与现场退化区域相比,成功复垦区域的所有土壤指标都有所改善,包括土壤团聚体稳定性、pH 值、植物可利用的 P 和 K、土壤有机碳、潜在矿化氮、微生物生物量 C 和 β-葡萄糖苷酶活性的提高,以及土壤容重和导电率的降低。在各项指标中,根据 SMAF 对土壤健康状况进行了无单位评分,数据表明今后应对容重、湿集料稳定性、潜在矿化氮、微生物生物量 C、pH 值和导电率进行监测。施用石灰和生物固体的长期效果改善了土壤的物理、生物和整体土壤健康状况。自早期开垦以来,植物中的金属浓度已经下降了一个数量级,大多数植物中的金属浓度可以被家畜食用。从动物健康的角度来看,在生长季节的后半期饲喂来自该地的牧草可能需要补充饲料,以提供更多的蛋白质和能量,并降低食物链生物累积可能造成危害的镉浓度。不过,由于土壤中生物可利用的镉和锌浓度超过了生态土壤筛选水平,因此存在健康问题。不过,植物稳定了土壤,酸度保持中和,从而长期改善土壤健康,全面提高生态系统健康水平。
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