Korea Biochar Research Center, O-Jeong Eco-Resilience Institute (OJERI), Division of Environmental Science and Ecological Engineering, Korea University, Seoul 02841, Republic of Korea.
Department of Microbiology, College of Natural Science, Pukyong National University, 45 Yongso-ro, Nam-gu, Busan 608-737, Republic of Korea.
Environ Int. 2019 May;126:791-801. doi: 10.1016/j.envint.2019.02.061. Epub 2019 Mar 21.
Little is known about the effects of applying amendments on soil for immobilizing metal(loid)s on the soil microbial community. Alterations in the microbial community were examined after incubation of treated contaminated soils. One soil was contaminated with Pb and As, a second soil with Cd and Zn. Red pepper stalk (RPS) and biochars produced from RPS in either N atmosphere (RPS) or CO atmosphere (RPS) were applied at a rate of 2.5% to the two soils and incubated for 30 days. Bacterial communities of control and treated soils were characterized by sequencing 16S rRNA genes using the Illumina MiSeq sequencing. In both soils, bacterial richness increased in the amended soils, though somewhat differently between the treatments. Evenness values decreased significantly, and the final overall diversities were reduced. The neutralization of pH, reduced available concentrations of Pb or Cd, and supplementation of available carbon and surface area could be possible factors affecting the community changes. Biochar amendments caused the soil bacterial communities to become more similar than those in the not amended soils. The bacterial community structures at the phylum and genus levels showed that amendment addition might restore the normal bacterial community of soils, and cause soil bacterial communities in contaminated soils to normalize and stabilize.
关于将改良剂应用于土壤以固定金属(类)对土壤微生物群落的影响,人们知之甚少。在对处理过的污染土壤进行培养后,研究了微生物群落的变化。一种土壤受到 Pb 和 As 的污染,另一种土壤受到 Cd 和 Zn 的污染。红辣椒茎(RPS)和在 N 气氛(RPS)或 CO 气氛(RPS)中产生的 RPS 生物炭以 2.5%的比例施用于两种土壤中,并培养 30 天。使用 Illumina MiSeq 测序对对照和处理土壤的细菌群落进行了 16S rRNA 基因测序。在两种土壤中,添加改良剂后细菌丰富度均增加,但处理方式之间略有不同。均匀度值显著降低,最终整体多样性降低。pH 值的中和、减少可利用的 Pb 或 Cd 浓度以及可利用的碳和表面积的补充可能是影响群落变化的因素。生物炭改良剂使土壤细菌群落变得比未改良土壤的群落更相似。在门和属水平上的细菌群落结构表明,添加改良剂可能会恢复土壤的正常细菌群落,并使污染土壤中的土壤细菌群落正常化和稳定化。