College of Resources and Environment, Hunan Agricultural University, Changsha 410128, China; Environmental Microbiomics Research Center, School of Environmental Science and Engineering, Southern Marine Science and Engineering Guangdong Laboratory (Zhuhai), Sun Yat-sen University, Guangzhou 510006, China.
College of Resources and Environment, Hunan Agricultural University, Changsha 410128, China.
J Environ Sci (China). 2021 Apr;102:263-272. doi: 10.1016/j.jes.2020.09.029. Epub 2020 Oct 10.
Heavy metal pollution affects soil ecological function. Biochar and compost can effectively remediate heavy metals and increase soil nutrients. The effects and mechanisms of biochar and compost amendments on soil nitrogen cycle function in heavy-metal contaminated soils are not fully understood. This study examined how biochar, compost, and their integrated use affected ammonia-oxidizing microorganisms in heavy metal polluted soil. Quantitative PCR was used to determine the abundance of ammonia-oxidizing archaea (AOA) and bacteria (AOB). Ammonia monooxygenase (AMO) activity was evaluated by the enzyme-linked immunosorbent assay. Results showed that compost rather than biochar improved nitrogen conversion in soil. Biochar, compost, or their integrated application significantly reduced the effective Zn and Cd speciation. Adding compost obviously increased As and Cu effective speciation, bacterial 16S rRNA abundance, and AMO activity. AOB, stimulated by compost addition, was significantly more abundant than AOA throughout remediation. Correlation analysis showed that AOB abundance positively correlated with NO-N (r = 0.830, P < 0.01), and that AMO activity had significant correlation with EC (r = -0.908, P < 0.01) and water-soluble carbon (r = -0.868, P < 0.01). Those seem to be the most vital factors affecting AOB community and their function in heavy metal-polluted soil remediated by biochar and compost.
重金属污染会影响土壤生态功能。生物炭和堆肥可以有效地修复重金属并增加土壤养分。生物炭和堆肥改良对重金属污染土壤氮循环功能的影响和机制尚不完全清楚。本研究探讨了生物炭、堆肥及其综合利用如何影响重金属污染土壤中的氨氧化微生物。采用定量 PCR 法测定氨氧化古菌(AOA)和细菌(AOB)的丰度。采用酶联免疫吸附试验(ELISA)评估氨单加氧酶(AMO)活性。结果表明,堆肥而不是生物炭改善了土壤中的氮转化。生物炭、堆肥或其综合应用显著降低了有效 Zn 和 Cd 的形态。添加堆肥明显增加了 As 和 Cu 的有效形态,细菌 16S rRNA 丰度和 AMO 活性。添加堆肥明显刺激了 AOB 的生长,使其在整个修复过程中比 AOA 更为丰富。相关性分析表明,AOB 丰度与 NO-N 呈正相关(r=0.830,P<0.01),而 AMO 活性与 EC(r=-0.908,P<0.01)和水溶性碳(r=-0.868,P<0.01)显著相关。这些似乎是影响生物炭和堆肥修复重金属污染土壤中 AOB 群落及其功能的最重要因素。