EFFECTS OF TEMPERATURE ON ABUNDANCE AND POTENTIAL HOST OF ARGs DURING SLUDGE COMPOSTING
-
摘要: 为探究污泥堆肥高温期起始温度(约50 ℃)和最高温度(约70 ℃)这2个关键温度节点对抗生素抗性基因(antibiotic resistance genes, ARGs)的影响,利用实时温度补偿反应器设置3种温度条件(R1—室温;R2—50 ℃和R3—70 ℃),分析ARGs和可移动基因元件(mobile genetic elements, MGEs)的变化规律及其潜在宿主微生物。结果表明:在高温期,3种温度条件均可降低目标ARGs和MGEs的相对丰度,其中sul2、tetG、aphA1和IntI1对温度变化具有极度敏感性且丰度变化趋势相似;而对tetM、mefA、sul1和Tn916的削减效果存在显著差异。在冷却和腐熟期,R2和R3均可抑制sul1、sul2、tetG和IntI1丰度的回升。在细菌群落结构方面,R2和R3在高温期提高了厚壁菌门的相对丰度,在腐熟期削减了放线菌门和变形菌门的相对丰度。共现性网络分析表明,变形菌门、厚壁菌门和放线菌门是目标ARGs和MGEs的主要潜在宿主。由IntI1引起的水平基因转移可能是sul1、sul2和tetG相对丰度在堆肥后期回升的原因。该研究可为探究ARGs在不同污泥堆肥温度下的变化机制提供参考。Abstract: In order to explore the impact of the two key temperatures, the initial temperature (about 50 ℃) and the maximum temperature (about 70 ℃), on the antibiotic resistance genes (ARGs) during the thermophilic period of sludge composting, a real-time temperature compensation reactor was used to set three temperature conditions (R1: room temperature; R2: 50 ℃; R3: 70 ℃) to analyze the changing laws of ARGs, mobile genetic elements (MGEs) and their potential host. The results showed that the relative abundance of ARGs and MGEs could be reduced under the three temperatures during the thermophilic phase. Among them, sul2, tetG, aphA1 and IntI1 were extremely sensitive to temperature changes and showed similar removal rates, but the removal rates of tetM, mefA, sul1 and Tn916 were significantly different. In the cooling and maturity phase, R2 and R3 inhibited the recovery of the abundance of sul1, sul2, tetG and IntI1. In terms of bacterial community structure, R2 and R3 increased the relative abundance of Firmicutes during the thermophilic period, and decreased the relative abundance of Actinobacteria and Proteobacteria during the maturity phase. Co-occurrence network analysis showed that Proteobacteria, Firmicutes and Actinobacteria were the main potential hosts of target ARGs and MGEs. Meanwhile, horizontal gene transfer caused by IntI1 may be responsible for the rebound of sul1, sul2 and tetG during the cooling and maturity phase. This study can provide a reference for exploring the changing mechanism of ARGs at different sludge composting temperatures.
-
Key words:
- aerobic composting /
- sludge /
- temperature /
- ARGs /
- potential host
-
[1] 张爱生, 曲俊荣, 许斌, 等. 外环境温度对堆肥过程中抗生素抗性基因的影响[J]. 环境工程, 2021, 39(5): 104-110. [2] 勾长龙, 王雨琼, 张喜庆, 等. 高温堆肥对猪粪中四环素类抗生素及抗性基因的影响[J]. 环境科学学报, 2017, 37(4): 1454-1460. [3] MARTA C, WILLIAM C, SIHEM J, et al. Antibiotic resistance genes in bacterial and bacteriophage fractions of Tunisian and Spanish wastewaters as markers to compare the antibiotic resistance patterns in each population[J]. Environment International, 2014, 73: 167-175. [4] 韦蓓, 黄福义, 李虎, 等. 污泥堆肥过程中磺胺类和大环内酯类抗性基因的残留[J]. 应用与环境生物学报, 2014, 20(3): 395-400. [5] 卢晓梅. 超高温堆肥微生物群落特征及其削减污泥抗性基因研究[D]. 福州:福建农林大学, 2018. [6] WU N, XIE S Y, ZENG M, et al. Impacts of pile temperature on antibiotic resistance, metal resistance and microbial community during swine manure composting[J]. Science of the Total Environment, 2020, 744: 140920. [7] 张燕茹. 厌氧消化强化技术对剩余污泥中微生物和抗生素抗性基因的影响研究[D]. 长沙:湖南大学, 2020. [8] ANTTI K, TIMOTHY A, CHRISTINA L, et al. High-throughput quantification of antibiotic resistance genes from an urban wastewater treatment plant[J]. Fems Microbiology Ecology Advance Access, 2016, 92(3):fiw014. [9] 王晓诚, 郭颖, 颜开红. 超高温自发热好氧堆肥工艺处理生活垃圾探究[J]. 环境工程, 2020, 38(10): 183-189. [10] HU J H, YANG Z H, HUANG Z L, et al. Co-composting of sewage sludge and Phragmites australis using different insulating strategies[J]. Waste Management, 2020, 108: 1-12. [11] 晏琛, 曹雷鹏, 刘玉环, 等.利用新型高温好氧堆肥器提高鸡粪谷壳有机肥肥效[J]. 环境工程学报, 2021, 15(3): 1103-1111. [12] LIAO H P, LU X M, RENSING C, et al. Hyperthermophilic composting accelerates the removal of antibiotic resistance genes and mobile genetic elements in sewage sludge[J]. Environmental Science & Technology, 2018, 52(1): 266-276. [13] 郭夏丽, 席晓黎, 张红娟, 等. 抗生素菌渣堆肥进程中微生物群落的变化[J]. 环境工程学报, 2012, 6(12): 4671-4675. [14] 黄魁, 夏慧, 陈景阳, 等. 蚯蚓对城市污泥蚯蚓堆肥过程中微生物特征变化的影响[J]. 环境科学学报, 2018,38(8): 3146-3152. [15] QIAN X, SUN W, GU J, et al. Variable effects of oxytetracycline on antibiotic resistance gene abundance and the bacterial community during aerobic composting of cow manure[J]. Journal of Hazardous Materials, 2016, 315: 61-69. [16] ZHANG Y R, YANG Z H, XIANG Y P, et al. Evolutions of antibiotic resistance genes (ARGs), class 1 integron-integrase (intI 1) and potential hosts of ARGs during sludge anaerobic digestion with the iron nanoparticles addition[J]. Science of the Total Environment, 2020, 724:138248. [17] CHEN Z Q, FU Q Q, WEN Q X, et al. Microbial community competition rather than high-temperature predominates ARGs elimination in swine manure composting[J]. Journal of Hazardous Materials, 2021, 423: 127149. [18] DOGAN B, BOOR K J, et al. Genetic diversity and spoilage potentials among Pseudomonas spp. isolated from fluid milk products and dairy processing plants[J]. Applied and Environmental Microbiology, 2003, 1: 130-138.
点击查看大图
计量
- 文章访问数: 133
- HTML全文浏览量: 12
- PDF下载量: 5
- 被引次数: 0