Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtse River), Ministry of Agriculture and Rural Affairs, College of Resources and Environment, Huazhong Agricultural University, Wuhan, 430070, China.
Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtse River), Ministry of Agriculture and Rural Affairs, College of Resources and Environment, Huazhong Agricultural University, Wuhan, 430070, China.
Chemosphere. 2022 Aug;301:134794. doi: 10.1016/j.chemosphere.2022.134794. Epub 2022 Apr 30.
Very little attention has been paid to the mineralization of soil organic matter (SOM) during the remediation of soil heavy metal pollution. This study observed SOM mineralization during the remediation of soil heavy metal pollution by treating polluted soil with montmorillonite, birnessite, goethite or ferrihydrite. All examined minerals significantly decreased the availability of both Cu and Cd in soil, the decrease by birnessite was the most significant. Birnessite significantly increased the percentage of reducible fraction of heavy metals. The availability of both Cu and Cd was significantly negatively correlated with the percentage of residual fraction of heavy metals. The mineralization of SOM was facilitated by montmorillonite and birnessite but was decreased by goethite and ferrihydrite. The information indicated that iron oxyhydroxides were promising additives for simultaneously stabilizing both heavy metal and organic carbon in soil. During the remediation of soil heavy metal pollution, the examined minerals regulated SOM mineralization by modulating the abundance and diversity of soil bacterial community, the activity of β-glucosidase, the content and structural complexity of dissolved organic matter (DOM), the content of soil available phosphorous, and soil pH.
在土壤重金属污染修复过程中,人们很少关注土壤有机质(SOM)的矿化作用。本研究通过用蒙脱石、水钠锰矿、针铁矿或水铁矿处理污染土壤来观察土壤重金属污染修复过程中 SOM 的矿化作用。所有研究的矿物质都显著降低了土壤中 Cu 和 Cd 的有效性,其中水钠锰矿的降低作用最为显著。水钠锰矿显著增加了重金属可还原态的比例。Cu 和 Cd 的有效性与重金属残留态的比例呈显著负相关。蒙脱石和水钠锰矿促进了 SOM 的矿化作用,但针铁矿和水铁矿则降低了 SOM 的矿化作用。这些信息表明,铁的氢氧化物是同时稳定土壤中重金属和有机碳的有前途的添加剂。在土壤重金属污染修复过程中,这些矿物质通过调节土壤细菌群落的丰度和多样性、β-葡萄糖苷酶的活性、溶解有机物质(DOM)的含量和结构复杂性、土壤有效磷的含量以及土壤 pH 值来调节 SOM 的矿化作用。