中温期和高温期污泥堆肥物料中典型氟喹诺酮类抗生素去除的影响因素

姚全威; 张军; 严沁颖; 王敦球; 席北斗

doi:10.13205/j.hjgc.202009032

中温期和高温期污泥堆肥物料中典型氟喹诺酮类抗生素去除的影响因素

doi: 10.13205/j.hjgc.202009032

姚全威^1,2,3,
张军^1,2,3, ,,
严沁颖^1,2,
王敦球^1,2,3,
席北斗⁴

1. 桂林理工大学环境科学与工程学院, 广西桂林 541004;
2. 桂林理工大学广西环境污染控制理论与技术重点实验室, 广西桂林 541004;
3. 桂林理工大学岩溶地区水污染控制与用水安全保障协同创新中心, 广西桂林 541004;
4. 中国环境科学研究院, 北京 100012

基金项目:

国家自然科学基金项目（51868011）；广西自然科学基金项目（2018GXNSFGA281001）；广西科技重大专项（桂科AA18118013）；"广西特聘专家"专项经费资助。

详细信息

作者简介:
姚全威(1995-),男,硕士研究生,主要从事固体废弃物处理与资源化利用。yqw@glut.edu.cn

通讯作者:
张军(1983-),男,博士,副教授,主要从事固体废弃物处理与资源化利用。zjun@glut.edu.cn

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出版历程
- 收稿日期: 2019-07-21

MAIN FACTORS ON DISSIPATION OF TYPICAL FLUOROQUINOLONES IN SEWAGE SLUDGE COMPOST DURING MESOPHILIC AND THERMOPHILIC PHASES

YAO Quan-wei^1,2,3,
ZHANG Jun^{1,2,3
, ,},
YAN Qin-ying^1,2,
WANG Dun-qiu^1,2,3,
XI Bei-dou⁴

1. College of Environmental Science and Engineering, Guilin University of Technology, Guilin 541004, China;
2. Guangxi Key Laboratory of Environmental Pollution Control Theory and Technology, Guilin University of Technology, Guilin 541004, China;
3. Collaborative Innovation Center for Water Pollution Control and Water Safety in Karst Area, Guilin University of Technology, Guilin 541004, China;
4. Chinese Research Academy of Environmental Sciences, Beijing 100012, China

摘要

摘要: 污泥处理后土地利用是氟喹诺酮类抗生素（fluoroquinolones，FQs）进入土壤环境的主要途径之一。好氧堆肥具有高效去除FQs、削减其环境风险的潜力，但目前对于堆肥过程中各阶段物料FQs去除影响因素的研究仍较少。该研究在制备典型城市污泥好氧堆肥获取其中温期、高温期物料的基础上，向堆肥中添加2种典型的FQs（ofloxacin，OFL；norfloxacin，NOR），在不同FQs初始浓度（0，2.5，5.0 mg/kg）、含水率（50%、60%、70%）和通风量（0，15 mL/min）条件下，进行56 d的抗生素去除试验，控制各堆肥物料在其对应堆肥阶段温度（中温期物料，35℃；高温期物料，55℃）。结果表明：2种物料中FQs去除率均随着初始浓度上升而逐步下降，中温期物料最佳初始FQs浓度分别为5.0 mg/kg（OFL）、2.5 mg/kg（NOR），对于高温期物料两者均为2.5 mg/kg；中温期物料中，FQs去除率随含水率增加先上升后下降，最佳含水率均为60%，高温期物料中，FQs去除率随含水率升高而逐步增加；2种物料中，通风量15 mL/min下的FQs去除率均明显高于未通风处理。与中温期物料对比，高温期物料中FQs去除过程需要较低的初始浓度和较高的含水率；在2种物料中，充分通风下FQs的去除率均明显高于未通风处理。
- 污泥 /
- 堆肥 /
- 抗生素 /
- 生物降解
Abstract: Land application after being composted is one of the main streams for the input of fluoroquinolone antibiotics into the soil environment. Aerobic composting can effectively remove FQs and reduce the potential environmental risk. However, only few studies have been reported to discuss the factors affecting the removal kinetics of FQs in sewage compost, during different composting phases. In this study, two groups of 56-day incubation were carried out in 0.5 L bioreactors by adding FQs into the compost collected from the mesophilic-phase and thermophilic-phase matrix during aerobic composting of sewage sludge without FQs added. These incubation trials in each group were performed at the different conditions varying at initial FQs content (0, 2.5, 5.0 mg/kg), water contents (50%, 60%, 70%) and aeration rates (0, 15 mL/min), while the temperatures of two-groups treatments were controlled at those corresponding composting phases (mesophilic, 35℃; thermophilic, 55℃). The removal rates of the FQs in the two groups gradually declined when the initial concentration rose, and the optimal initial FQs concentrations for the mesophilic-phase compos were 5.0 mg/kg (OFL) and 2.5 mg/kg (NOR), while 2.5 mg/kg(OFL) for both mesophilic-phase and thermophilic-phase. In the mesophilic-phase compost, the removal rate of FQs increased firstly and then decreased with increasing the water content of the compost from 50% to 70%, and the optimum water content were 60%, while the removal efficiencies of FQs of the thermophilic-phase compost gradually increased with increasing of the water content. In all composts, the ventilation was more conducive to rapidly remove the FQs in sludge compost than no ventilation. Compared with the mesophilic-phase compost, removing FQs in the thermophilic-phase compost needed a lower initial FQs concentration and a higher water content, while in both composts the sufficient ventilation resulting into aerobic environment, more conducive for removal of FQs than no ventilation.
- sludge /
- composting /
- antibiotic /
- biodegradation

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参考文献(31)

GOTHWAL R,SHASHIDHAR T. Antibiotic pollution in the environment:a review[J]. Clean-Soil, Air, Water, 2015, 43(4):479-489.

KLAUS K. Antibiotics in the aquatic environment--a review--part Ⅱ[J]. Chemosphere, 2009, 75(4);435-441.

KLAUS K. Antibiotics in the aquatic environment-A review-Part I[J]. Chemosphere, 2009, 75(4):417-434.

ZHANG Q Q, YING G G, PAN C G, et al. Comprehensive evaluation of antibiotics emission and fate in the river basins of China:source analysis, multimedia modeling, and linkage to Bacterial Resistance[J]. Environmental Science & Technology, 2015, 49(11):6772-6782.

ALCOCK R E, SWEETMAN A,JONES K C. Assessment of organic contanhnant fate in waste water treatment plants Ⅰ:selected compounds and physicochemical properties[J]. Chemosphere, 1999, 38(10):2247-2262.

JIA A, WAN Y, XIAO Y, et al. Occurrence and fate of quinolone and fluoroquinolone antibiotics in a municipal sewage treatment plant[J]. Water Research, 2012, 46(2):387-394.

MICHAEL I, RIZZO L, MCARDELL C S, et al. Urban wastewater treatment plants as hotspots for the release of antibiotics in the environment:a review[J]. Water Research, 2013, 47(3):957-995.

WANG L, QIANG Z M, LI Y G, et al. An insight into the removal of fluoroquinolones in activated sludge process:sorption and biodegradation characteristics[J]. Journal of Environmental Sciences, 2017, 56(6):263-271.

YAN Q, GAO X, HUANG L, et al. Occurrence and fate of pharmaceutically active compounds in the largest municipal wastewater treatment plant in Southwest China:mass balance analysis and consumption back-calculated model[J]. Chemosphere, 2014, 99:160-170.

CHEN Y S, YU G, CAO Q M, et al. Occurrence and environmental implications of pharmaceuticals in Chinese municipal sewage sludge[J]. Chemosphere, 2013, 93(9):1765-1772.

LI W H, SHI Y L, GAO L H, et al. Occurrence, distribution and potential affecting factors of antibiotics in sewage sludge of wastewater treatment plants in China[J]. Science of the Total Environment, 2013, 445/446:306-313.

KRISTIN M C,HALDEN R U. Pharmaceuticals and personal care products in archived U.S. biosolids from the 2001 EPA National Sewage Sludge Survey[J]. Water Research, 2010, 44(2):658-668.

VERLICCHI P,ZAMBELLO E. Pharmaceuticals and personal care products in untreated and treated sewage sludge:occurrence and environmental risk in the case of application on soil:a critical review[J]. Science of the Total Environment, 2015, 538:750-767.

YANG B, MENG L,XUE N D. Removal of five fluoroquinolone antibiotics during broiler manure composting[J]. Environmental Technology, 2018, 39(3):373-381.

YU B H, ZAKARIA M P, LATIF P A, et al. Degradation of veterinary antibiotics and hormone during broiler manure composting[J]. Bioresource Technology, 2013, 131(131C):476-484.

孟磊, 杨兵, 薛南冬,等. 高温堆肥对鸡粪中氟喹诺酮类抗生素的去除[J]. 农业环境科学学报, 2015, 34(2):377-383.

LILLENBERG M, YURCHENKO S, KIPPER K, et al. Presence of fluoroquinolones and sulfonamides in urban sewage sludge and their degradation as a result of composting[J]. International Journal of Environmental Science & Technology, 2010, 7(2):307-312.

BOURDAT-DESCHAMPS M, FERHI S, BERNET N, et al. Fate and impacts of pharmaceuticals and personal care products after repeated applications of organic waste products in long-term field experiments[J]. Science of the Total Environment, 2017, 607/608:271-280.

SELVAM A, ZHAO Z,WONG J W. Composting of swine manure spiked with sulfadiazine, chlortetracycline and ciprofloxacin[J]. Bioresource Technology, 2012, 126(12):412-417.

KHADRA A, EZZARIAI A, MERLINA G, et al. Fate of antibiotics present in a primary sludge of WWTP during their co-composting with palm wastes[J]. Waste Management, 2019, 84:13-19.

SLANA M, ŽIGON D,SOLLNER-DOLENC M. Enrofloxacin degradation in broiler chicken manure under field conditions and its residuals effects to the environment[J]. Environmental Science & Pollution Research, 2017, 24(15):13722-13731.

AMINE E, MOHAMED H, AHMED K, et al. Human and veterinary antibiotics during composting of sludge or manure:global perspectives on persistence, degradation, and resistance genes[J]. Journal of Hazardous Materials, 2018, 359:465-481.

WALTERS E, MCCLELLAN K,HALDEN R U. Occurrence and loss over three years of 72 pharmaceuticals and personal care products from biosolids-soil mixtures in outdoor mesocosms[J]. Water Research, 2010, 44(20):6011-6020.

ZHANG J C, ZENG G M, CHEN Y N, et al. Effects of physico-chemical parameters on the bacterial and fungal communities during agricultural waste composting[J]. Bioresource Technology, 2011, 102(3):2950-2956.

GE J Y, HUANG G Q, HUANG J, et al. Modeling of oxygen uptake rate evolution in pig manure-wheat straw aerobic composting process[J]. Chemical Engineering Journal, 2015, 276:29-36.

YANG Z. Characterization of the dynamic thickness of the aerobic layer during pig manure aerobic composting by fourier transform infrared microspectroscopy[J]. Environmental Science & Technology, 2014, 48(9):5043-5050.

ZENG J, SHEN X, HAN L, et al. Dynamics of oxygen supply and consumption during mainstream large-scale composting in China[J]. Bioresource Technology, 2016, 220:104-109.

DORIVAL-GARCÍA N, ZAFRA-GÓMEZ A, NAVALÓN A, et al. Removal and degradation characteristics of quinolone antibiotics in laboratory-scale activated sludge reactors under aerobic, nitrifying and anoxic conditions[J]. Journal of Environmental Management, 2013, 120:75-83.

VANČAROVÁ M, MOEDER M, FILIPOVÁ A, et al. Biotransformation of fluoroquinolone antibiotics by ligninolytic fungi-Metabolites, enzymes and residual antibacterial activity[J]. Chemosphere, 2015, 136:311-320.

PRIETO A, MÖDER M, RODIL R, et al. Degradation of the antibiotics norfloxacin and ciprofloxacin by a white-rot fungus and identification of degradation products[J]. Bioresource Technology, 2011, 102(23):10987-10995.

PARSHIKOV I A,SUTHERLAND J B. Microbial transformations of antimicrobial quinolones and related drugs[J]. Journal of Industrial Microbiology & Biotechnology, 2012, 39(12):1731-1740.

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