State Key Joint Laboratory of Environmental Simulation and Pollution Control, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; Department of Water Pollution Control, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China.
State Key Joint Laboratory of Environmental Simulation and Pollution Control, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; Department of Water Pollution Control, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; University of Chinese Academy of Sciences, Beijing 100049, China; Institute of Energy, Jiangxi Academy of Sciences, Nanchang 330096, China.
Environ Pollut. 2019 Feb;245:353-362. doi: 10.1016/j.envpol.2018.11.003. Epub 2018 Nov 2.
Swine waste is a reservoir of microbial pollutants, including pathogens, antibiotic resistance genes (ARGs) and antibiotic resistant bacteria (ARB); therefore, soil fertilized with swine waste is an essential pathway for the dissemination of microbial pollutants from concentrated swine farms to the public. To rationalize the intervals of swine wastes application and investigate the effects of soil type on the occurrences of microbial pollutants and antibiotic resistance, pot experiments were conducted with three typical soils, humic acrisol, calcaric cambisols and histosols, being collected from south, northwest and northeast China (soil-R, soil-Y and soil-B, respectively). The soils were amended with swine slurry, digestate and chemical fertilizers and then conducted for 172 days. The influence of microbial pollutants and antibiotic resistance in soil posed by digestate application was similar to that of the chemical fertilizers, while swine slurry posed high risks to the soil. Soil-B which had the highest organic matter and neutral pH was least influenced by the swine slurry amendment. tetG, tetM and ermF were persistent ARGs in the slurry treated soil, and their decay rates fitted to first-order kinetics in the order soil-B> soil-Y > soil-R. Putative pathogens showed strong correlations with ARGs, suggesting a risk of dissemination. The initial 43-82 days was the active phase of microbial pollution in slurry treated soil, during which time heavy metals, moisture content, total organic carbon and the microbial community were key factors contributing to changes in antibiotic resistance. Fertilization intervals of livestock wastes should be lengthened over the ARG active phase.
猪粪是微生物污染物的储存库,包括病原体、抗生素耐药基因(ARGs)和抗生素耐药菌(ARB);因此,施有猪粪的土壤是从集约化养猪场向公众传播微生物污染物的重要途径。为了合理化猪粪施用的间隔,并研究土壤类型对微生物污染物和抗生素耐药性出现的影响,本研究从中国南部、西北部和东北部采集了三种典型土壤(腐殖质暗棕壤、石灰性栗钙土和腐殖质沼泽土,分别标记为土壤-R、土壤-Y 和土壤-B)进行了盆栽实验。土壤分别用猪粪浆、消化液和化肥进行了 172 天的处理。与化肥相比,消化液的应用对土壤中微生物污染物和抗生素耐药性的影响相似,而猪粪浆对土壤的风险较高。土壤-B 具有最高的有机质和中性 pH 值,受猪粪浆改良的影响最小。tetG、tetM 和 ermF 是粪浆处理土壤中持久存在的 ARGs,其衰减率符合一级动力学,顺序为土壤-B>土壤-Y>土壤-R。假定的病原体与 ARGs 呈强相关性,表明存在传播风险。在粪浆处理土壤中,微生物污染的活跃期为 43-82 天,在此期间,重金属、含水量、总有机碳和微生物群落是导致抗生素耐药性变化的关键因素。应在 ARG 活跃期延长家畜废物的施肥间隔。