养殖业抗生素-重金属复合污染治理研究进展

漆世英; 余少乐; 吴娟; 成水平

doi:10.12357/cjea.20210641

养殖业抗生素-重金属复合污染治理研究进展

doi: 10.12357/cjea.20210641

漆世英^1,,
余少乐²,
吴娟^{1, 3},
成水平^{1, 3, ,}

1.
同济大学长江水环境教育部重点实验室　上海　200092
2.
中国建筑第八工程局有限公司　上海　200135
3.
上海生态景观水环境工程技术研究中心　上海　200031

基金项目: 中国建设股份有限公司科技研发计划(CSCEC-2021-Z-3)资助

详细信息

作者简介:
漆世英, 主要研究方向为植物修复。E-mail: 2032824@tongji.edu.cn

通讯作者:
成水平, 主要研究方向为生态工程。E-mail: shpcheng@tongji.edu.cn

中图分类号: X592
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- 被引次数: 0
出版历程
- 收稿日期: 2021-09-22
- 录用日期: 2021-12-30
- 网络出版日期: 2021-12-31
- 刊出日期: 2022-06-09

Advance in treatment of co-contamination of antibiotics and heavy metals from stock breeding

QI Shiying^1
,,
YU Shaole²,
WU Juan^{1, 3},
CHENG Shuiping^{1, 3
, ,}

1.
Key Laboratory of Yangtze River Water Environment of Tongji University, Ministry of Education, Shanghai 200092, China
2.
China Construction Eighth Engineering Division Co., Ltd., Shanghai 200135, China
3.
Shanghai Engineering Research Center of Landscape Water Environment, Shanghai 200031, China

Funds: The study was supported by the China State Construction Engineering Corporation Science and Technology R & D Project (CSCEC-2021-Z-3).

More Information

Corresponding author: E-mail: shpcheng@tongji.edu.cn

摘要

摘要: 我国养殖业快速发展, 抗生素因其能够预防和治疗动物疾病的功能被大量使用, 在环境中残留对生态环境安全和人类健康造成威胁。重金属作为饲料添加剂也会造成污染。本文介绍了现阶段养殖业中抗生素和重金属的使用情况以及对养殖品种和生态环境的污染现状, 并梳理了现有的抗生素处理技术以及抗生素-重金属复合污染治理研究进展。抗生素和重金属共存的情况导致了养殖业产生的废水和底泥中会存在持久性抗生素-重金属复合污染, 并在一定程度上影响抗性基因的传播。针对抗生素的去除仍是以高级氧化处理为主, 生物处理和生态处理为辅。生物处理主要利用微生物对抗生素的降解以及活性炭的吸附能力, 生态处理通过人工湿地中植物及其他耦合工艺达到污染物去除的目的。高级氧化处理工艺在短时间内能够达到高效去除的效果, 而实际应用必须达到去除效果和成本费用的均衡。因而今后的研究应着重关注以下方面: 1)养殖业复合污染废水的生态治理技术, 如人工湿地等; 2)复合污染底泥植物修复技术, 优化植物的选择及种植方式; 3)生物处理技术和生态治理技术的工程应用。
- 集约化养殖 /
- 抗生素 /
- 重金属 /
- 复合污染 /
- 生态治理
Abstract: With the rapid development of stock breeding and aquaculture in China, antibiotics, which are widely used to prevent and treat diseases and protect the health of animals, are discharged into the environment, thereby posing a threat to the ecological environment and human health. The frequent use of antibiotics has also resulted in increased microbial resistance. Heavy metals, as feed additives, can accumulate in the environment and cause pollution. In this review, the use of antibiotics and heavy metals in breeding and the pollution in animal species and the ecological environment are elaborated. Additionally, the existing treatment technology of antibiotics and the research progress of combined antibiotic-heavy metal pollution are summarized. The coexistence of antibiotics and heavy metals leads to the persistent combined pollution of antibiotics and heavy metals in wastewater and sediments produced by breeding. The co-selection mechanism driven by heavy metals affects the transmission of antibiotic-resistance genes to a certain extent. At present, the removal of antibiotics is based on advanced oxidation treatment supplemented by biological and ecological treatments. Biological treatment mainly uses microbial degradation of antibiotics and the adsorption capacity of activated carbon, whereas ecological treatment achieves pollutant removal via plants and other coupling processes in constructed wetlands. Advanced oxidation processes can achieve an efficient removal effect in a short time; however, the actual application must maintain a balance between the removal effect and cost. In addition, research on the antibiotics removal effect of various methods in the presence of heavy metal ions is lacking. Future research should focus on the following aspects: 1) ecological treatment techniques for co-contaminated aquaculture wastewater, such as artificial wetlands; 2) phytoremediation of co-contaminated sediment, especially plant selection and cultivation optimization; and 3) application of a combination of biological and ecological treatment technologies in practice.
- Intensive stock breeding /
- Antibiotics /
- Heavy metal /
- Co-contamination /
- Ecological management

HTML全文

图 1 抗生素和重金属复合污染下研究网络

在Web of Science中检索[TS = (heavy metal*)] AND TS = (antibiotic*) AND TS = (risk*) AND 论文 (文献类型), 得到的文章按照年份进行了相关性分析。

Figure 1. The web of study on the coexistence of antibiotics and heavy metals

The correlation analysis according to year retrieval results that searched [TS = (heavy metal*)] AND TS = (antibiotic*) AND TS = (risk*) AND thesis (literature type) in Web of Science were conducted.

下载: 全尺寸图片幻灯片

图 2 四环素生物降解主要产物及降解途径

Figure 2. The main products and degradation pathways of tetracycline biodegradation

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图 3 四环素类抗生素与金属离子的络合方式

Figure 3. The complexation of tetracyclines antibiotics with metal ions

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表 1 抗生素在部分种植业和养殖业中的污染情况

Table 1. The contamination of antibiotics in planting and breeding industries

抗生素种类 Antibiotics		场所 Site	检出浓度 Range (mg∙kg⁻¹)	检出率 Detection rate (%)	参考文献 Reference
四环素类 Tetracyclines	四环素 Tetracycline	农田 Farmland	ND~0.232	74	[17]
		鱼类 Fish	0.042~1.20	82.5	[9]
		底泥 Sediment	ND~0.112	ND	[15]
		粪便 Manure	1.99~6.99	100	[18]
	土霉素 Oxytetracycline	农田 Farmland	0.006~0.332	100	[14]
		底泥 Sediment	0.552~13.9	100	[19]
		水体 Water	ND~0.018	93	[16]
		粪便 Manure	1.68~10.40	43	[20]
	金霉素 Chlorotetracycline	农田 Farmland	0.034~0.773	100	[17]
		水体 Water	ND~0.143	ND	[15]
		粪便 Manure	0.32~66.62	41	[20]
	强力霉素 Doxycycline	农田 Farmland	0.002~0.249	100	[14]
喹诺酮类 Quinolones	诺氟沙星 Norfloxacin	农田 Farmland	ND~0.374	55	[14]
	诺氟沙星 Norfloxacin	鱼类 Fish	1.95~22.30	100	[21]
		粪便 Manure	ND~2.71	41	[20]
	氧氟沙星 Ofloxacin	农田 Farmland	ND~0.643	65	[14]
	氧氟沙星 Ofloxacin	底泥 Sediment	ND~206.3	100	[19]
磺胺类 Sulfonamides	磺胺嘧啶 Sulphadiazine	农田 Farmland	ND~0.008	ND	[14]
	磺胺甲噁唑 Sulfamethoxazole	底泥 Sediment	ND~46.74	75	[16]
	磺胺二甲嘧啶 Sulfamethazine	农田 Farmland	ND~0.030	95	[14]
		底泥 Sediment	ND~0.100	ND	[15]
		粪便 Manure	17.55~37.32	42	[20]
		水体 Water	ND~5.654	ND	[15]
大环内酯类 Macrolides	红霉素 Erythromycin	鱼类 Fish	0.002~0.034	100	[21]
	红霉素 Erythromycin	底泥 Sediment	0.48~28.5	100	[19]
	罗红霉素 Roxithromycin	底泥 Sediment	ND~1.11	98	[16]
氯霉素类 Chloramphenicoles	氟苯尼考 Florfenicol	鱼类 Fish	0.21~2.61	47	[9]
ND表示未检出。ND indicates the concentration of antibiotics below the detection limit.

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