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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

漆世英, 余少乐, 吴娟, 成水平. 养殖业抗生素-重金属复合污染治理研究进展[J]. 中国生态农业学报 (中英文), 2022, 30(6): 1014−1026 doi: 10.12357/cjea.20210641
引用本文: 漆世英, 余少乐, 吴娟, 成水平. 养殖业抗生素-重金属复合污染治理研究进展[J]. 中国生态农业学报 (中英文), 2022, 30(6): 1014−1026 doi: 10.12357/cjea.20210641
QI S Y, YU S L, WU J, CHENG S P. Advance in treatment of co-contamination of antibiotics and heavy metals from stock breeding[J]. Chinese Journal of Eco-Agriculture, 2022, 30(6): 1014−1026 doi: 10.12357/cjea.20210641
Citation: QI S Y, YU S L, WU J, CHENG S P. Advance in treatment of co-contamination of antibiotics and heavy metals from stock breeding[J]. Chinese Journal of Eco-Agriculture, 2022, 30(6): 1014−1026 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
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

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

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

    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

    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

    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]
    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]
    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]
    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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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

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