Institute of Natural Resources and Ecology Heilongjiang Academy of Sciences, National and Provincial Joint Engineering Laboratory of Wetlands and Ecological Conservation, Collaborative Innovation Center for Development and Utilization of Forest Resource, Harbin 150040, PR China.
State Key Laboratory f Black Soils Conservation and Utilization, Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Harbin 150081, PR China.
Ecotoxicol Environ Saf. 2024 Nov 1;286:117179. doi: 10.1016/j.ecoenv.2024.117179. Epub 2024 Oct 14.
There is a close relationship between microbial activity and the bioavailability of heavy metals, and heavy metal resistance genes can affect the activity of heavy metals. To evaluate the effects of coupled earthworm and biochar composting on Cd forms and Cd resistance genes in sludge, the BCR continuous extraction method was applied to classify the Cd forms, and Cd resistance genes were quantitatively determined with heavy metal gene chip technology. The results showed that the changes in earthworm biomass during composting were sufficiently fitted by logistic models and that adding biochar effectively increased earthworm biomass. The coupled treatment of earthworms and biochar promoted the degradation of sludge. The coupled treatment of earthworms and biochar reduced the proportion of acid-extractable and reducible Cd relative to total Cd, increased the proportion of oxidized and residual Cd relative to total Cd, transformed Cd forms from active to inert, and reduced the gene copy number of Cd resistance genes (czcA, czcB, czcC, czcD, czcS, czrA, czrR, cadA, and zntA). czcB was identified as a key gene that affected acid-extractable Cd and residual Cd contents; czcA, czcB, czcD, and czcS were identified as key genes that affected the reducible Cd content; czrR and cadA were identified as key genes that affected the oxidized Cd content; and czcC was identified as a key gene that affected the total Cd content. Cd resistance genes could directly affect the Cd form or indirectly affect Cd form through their interactions with each other.
微生物活性与重金属生物可利用性之间存在密切关系,重金属抗性基因可以影响重金属的活性。为评估蚯蚓和生物炭共堆肥对污泥中 Cd 形态和 Cd 抗性基因的影响,采用 BCR 连续提取法对 Cd 形态进行分类,并采用重金属基因芯片技术定量测定 Cd 抗性基因。结果表明,堆肥过程中蚯蚓生物量的变化可以用 logistic 模型充分拟合,添加生物炭可以有效增加蚯蚓生物量。蚯蚓和生物炭的共同处理促进了污泥的降解。蚯蚓和生物炭的共同处理降低了酸可提取态和可还原态 Cd 占总 Cd 的比例,增加了氧化态和残渣态 Cd 占总 Cd 的比例,将 Cd 形态从活性转化为惰性,降低了 Cd 抗性基因(czcA、czcB、czcC、czcD、czcS、czrA、czrR、cadA 和 zntA)的基因拷贝数。czcB 被鉴定为影响酸可提取态 Cd 和残渣态 Cd 含量的关键基因;czcA、czcB、czcD 和 czcS 被鉴定为影响可还原态 Cd 含量的关键基因;czrR 和 cadA 被鉴定为影响氧化态 Cd 含量的关键基因;czcC 被鉴定为影响总 Cd 含量的关键基因。Cd 抗性基因可以直接影响 Cd 形态,也可以通过相互作用间接影响 Cd 形态。