
抗生素作为一种新兴污染物一直是国内外的研究热点[1].随着人们生活水平的不断提高, 抗生素被广泛应用于人类医疗和畜禽、水产养殖中.由于人或动物在服用抗生素后, 不能完全吸收, 所以导致大量的抗生素以原态和代谢物状态排入环境中造成污染.抗生素在对环境产生污染的同时, 也会导致病原微生物产生耐药性, 对生态环境及人类健康带来严重威胁.抗生素除了能引起细菌的耐药性, 对其他生物也可能产生潜在毒性[2~4].
据报道, 大多数国家和地区的环境介质(水体、沉积物及土壤)中均检测到了抗生素的残留[5~13]. 2022年发布的《新污染物治理行动方案》指出要加强对环境介质中抗生素的监测和治理[14].目前, 国内外科研工作者对于抗生素的污染调查和研究主要着重于部分地区、部分污染物和环境介质.李柏林等[15]对长江武汉段水源地不同区域采集样品, 分析典型抗生素和抗性基因(ARGs) 的分布特征和相关性以及潜在生态风险.李富娟等[16]分析了宁夏第三排水沟中各类抗生素的污染水平, 探讨其浓度与水体指标的相关性, 并进行生态风险评估.张小红等[17]分析了银川市农田土壤中土霉素、四环素、金霉素和强力霉素的污染特征及空间分布状况, 并评价了其生态风险.王璠等[18]研究了武汉市东湖抗生素污染现状及生态风险评估.但全面分析抗生素在水体、沉积物和土壤中的污染特征的研究还未见报道, 本文重点探讨了我国典型抗生素在环境介质中的污染特征与生态风险评估, 以期为我国环境介质中抗生素指标质量基准或管理标准的建立及抗生素指标环境污染的监管工作提供科学依据.
1 材料与方法 1.1 数据来源本研究数据来源于已发表的文献, 共收集全国170个水体(包括地表水和污水)、106个沉积物(包括江河及养殖场沉积物)和119个土壤环境中的抗生素暴露浓度数据.共收集4类抗生素数据, 包括大环内酯类(红霉素、罗红霉素、克拉霉素)、四环素类(四环素、土霉素、金霉素)、磺胺类(磺胺甲
根据欧盟风险评价技术指导文件(technical guidance document on risk assessment, TGD)[19], 本研究采用风险商值(risk quotients, RQs)法评估我国环境介质中典型抗生素的潜在生态风险, 其计算公式为:
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(1) |
式中, MEC为环境暴露浓度; PNEC为预测无效应浓度.
本研究中水体、沉积物、土壤环境中典型抗生素的暴露含量来源于文献, PNEC值为本课题组前期研究推导, 各种抗生素在不同环境介质中的PNEC值见表 1, PNEC值的具体推导方法见文献[20].根据RQs分类方法来评估生态等级, RQs<0.01为无风险; 0.01≤RQs<0.1为低风险; 0.1≤RQs<1为中风险; RQs≥1为高风险[21].
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表 1 抗生素在不同环境介质中的PNEC值1) Table 1 PNEC values of antibiotics in different environmental media |
1.3 统计分析
本研究使用ArcGIS绘制抗生素调查点位分布, 利用Origin软件对抗生素的分布情况进行绘图, 用SPSS 23.0对抗生素数据进行分析.
2 结果与讨论 2.1 水体、沉积物和土壤中典型抗生素污染特征 2.1.1 水体中典型抗生素污染特征我国部分地区水体中抗生素的浓度最大值统计见图 1. 4类抗生素在水体中均有不同程度检出, 其中四环素、金霉素和磺胺甲
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数据整理自已有研究:红霉素[24~33], 罗红霉素[24~27, 29~32, 34~39], 克拉霉素[27, 31, 35, 39], 四环素[24~27, 32, 36, 38, 40~47], 土霉素[24~27, 32, 36, 38, 40~43, 45, 48~50], 金霉素[24~26, 30, 32, 36, 44~46], 磺胺甲![]() |
在各种水体的利用类型中, 红霉素、罗红霉素、克拉霉素、四环素、金霉素和磺胺甲
对于水体中各种抗生素的浓度最大值的统计均值, 红霉素超过100 ng·L-1的有出水、河水和养殖水, 而井水中的浓度则相对较低; 罗红霉素超过100 ng·L-1的有出水和河水, 而井水中的浓度则相对较低; 克拉霉素无超过200 ng·L-1的水体; 四环素超过115 ng·L-1的有江水, 而养殖水中的四环素浓度则相对较低; 土霉素超过4.93×103 ng·L-1的有养殖水, 而井水中的土霉素浓度则相对较低; 金霉素超过240 ng·L-1的有出水和入海口, 而井水及部分养殖水中的金霉素浓度则相对较低; 磺胺甲
8种抗生素的浓度平均值为208 ng·L-1.其中, 磺胺类、四环素类、喹诺酮类和大环内酯类的浓度平均值分别为483、228、134和29.4 ng·L-1.8种抗生素中, 罗红霉素残留浓度在0.350~169 ng·L-1范围之间, 浓度整体上较为稳定, 这可能是由于罗红霉素为大尺寸分子, 具有较强的疏水性, 其次是罗红霉素在水和沉积物间的分配系数差异过大, 造成了水体中罗红霉素浓度值波动较小.
2.1.2 沉积物中典型抗生素污染特征沉积物调查点位中土霉素、金霉素、诺氟沙星和恩诺沙星的含量最大值统计见图 2, 其在沉积物中的含量范围分别为ND(未检出)~900、ND~347、ND~5.77和ND~0.360 mg·kg-1.经济发展水平、土地利用方式和人类活动强度因素等不同均可导致沉积物中抗生素含不同, 使得我国不同区域沉积物中抗生素污染程度存在一定的差异.例如:在调查的江河沉积物中, 抗生素含量平均值大小为:诺氟沙星(1.21 mg·kg-1)>土霉素(0.29 mg·kg-1)>恩诺沙星(0.06 mg·kg-1)>金霉素(0.04 mg·kg-1), 诺氟沙星是主要污染物.在各种养殖场沉积物中, 抗生素含量平均值大小为:土霉素(145.35 mg·kg-1)>金霉素(111.03 mg·kg-1)>诺氟沙星(0.39 mg·kg-1)>恩诺沙星(0.14 mg·kg-1), 土霉素和金霉素是主要污染物. 因此, 在调查的4种抗生素中, 江河沉积物主要污染物为诺氟沙星, 而养殖场沉积物主要污染物为土霉素及金霉素.综合长江三角洲[71]、白洋淀[62, 77]、苕溪[70]、大沽河[79]、黄河、海河、辽河[69]和珠江[68]等江河沉积物含量, 发现不同江河沉积物的诺氟沙星含量略有差别, 除海河(0.032~5.77 mg·kg-1)、白洋淀(0.049 4~1.14 mg·kg-1)和珠江(0.088~1.12 mg·kg-1)检出含量超过1 mg·kg-1外, 其余江河含量均低于1 mg·kg-1.在养殖场沉积物中, 土霉素含量大小为:水产养殖塘>养鸡场>养猪场, 而金霉素含量大小为:养猪场>养鸡场>水产养殖场.
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数据整理自已有研究:土霉素[35, 68~76], 金霉素[69~71, 74~76], 诺氟沙星[62, 71~79], 恩诺沙星[35, 62, 69, 71, 75, 77, 79~80]; a1.养猪场, a2.水产养殖场, a3.养鸡场, a4.江河流域, a5.其他; b1.养猪场, b2.养鸡场, b3.江河流域, b4.其他养殖场; c1.养猪场, c2.养鸡场, c3.底泥, c4.江河流域, c5.污水; d1.养猪场, d2.沉积物, d3.底泥, d4.养鸡场, d5.江河流域, d6.畜禽废物, d7.废水 图 2 我国部分地区沉积物中抗生素含量最大值统计 Fig. 2 Statistics of the maximum antibiotic content in sediments in some regions of China |
土壤调查点位中四环素、土霉素和金霉素含量见表 2.在调查的土壤点位中, 金霉素质量分数最高, 范围为1.10% ~98.6%, 平均值为41.8%; 其次为土霉素, 质量分数范围分别为0.07% ~86.0%, 平均值为38.1%; 最后为四环素, 质量分数范围为0.19% ~65.0%, 平均值为20.1%.因此, 在3种四环素类抗生素中, 主要污染物为金霉素.
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表 2 我国部分地区土壤中抗生素的含量1)/ng·g-1 Table 2 Antibiotic content in soil in some regions of China/ng·g-1 |
2.2 生态风险评价 2.2.1 我国部分地区水体中典型抗生素的生态风险评估
将我国部分地区水体中典型抗生素(红霉素、罗红霉素、克拉霉素、四环素、土霉素、金霉素、磺胺甲
为进一步表征抗生素的潜在生态风险, 使用ArcGIS绘制出抗生素在我国的RQs等级化分布, 结果见图 3.可以看出, 全国约75%的点位RQs值小于1, 生态风险等级属于无风险、低风险或中风险.高风险(RQs值大于1)的点位主要分布在山东、湖北、浙江、四川、广东、海南、江苏和江西等地.可见, 南方地区水体污染较为严重, 而西部地区则较轻.结合现状分析, 主要来源为医疗和畜禽养殖业废水的排放, 为人口活动密集和经济产业快速发展所导致.通过分析生态风险等级较高地区的抗生素的分布可知, 磺胺甲
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基于自然资源部标准地图服务网站GS(2020)4619号标准地图制作, 底图无修改; 数据整理自文献[24~67]; STP为污水处理厂, DQE、DBE、DTE、DJE、DQ、DB和DT为调查点位 图 3 我国部分地区水体点位RQs等级化分布 Fig. 3 Distribution map of contaminated water RQs site in some regions of China |
如图 4所示, 风险商值热图中有4种抗生素对地表水表现为高风险, 分别是罗红霉素、四环素、磺胺甲
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1.北京温榆河, 2.半岛诸河, 3.小清河, 4.海河, 5.淮河, 6.淀山湖, 7.大辽河, 8.贡湖湾, 9.大通湖, 10.乌伦古湖, 11.博斯腾湖, 12.九龙江, 13.黄浦江; 白色填充表示无数据 图 4 地表水中抗生素的风险商 Fig. 4 RQs of antibiotics in surface water |
如图 5所示, 有6种抗生素对污水表现为高风险, 分别是红霉素、罗红霉素、四环素、金霉素、磺胺甲
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1.清河STP出水DQE, 2.北小河STP出水DBE, 3.高碑店STP出水DTE, 4.酒仙桥STP出水DJE, 5.清河直接排放样DQ, 6.坝河直接排放样DB, 7.通惠河直接排放样DT, 8.环鄱阳湖水产养殖区, 9.广州污水处理厂出水, 10.渤海湾养鱼塘, 11.高淳中华绒螯蟹养殖塘, 12.鄱阳湖区养猪场排污渠, 13.杭州C处养猪场污水, 14.北方地区陆源入海口, 15.广州污水处理厂进水, 16.中山三角镇水产养殖地, 17.天津大沽排污河, 18.杭州生活污水出水, 19.广州生活污水出水, 20.香港生活污水出水; STP为污水处理厂, DQE、DBE、DTE、DJE、DQ、DB和DT为调查点位; 白色填充表示无数据 图 5 污水中抗生素的风险商 Fig. 5 RQs of antibiotics in sewage |
将我国部分地区各类型沉积物中典型抗生素(四环素、土霉素、金霉素、诺氟沙星和恩诺沙星)的含量与PNEC值(表 1)相比较, 沉积物中抗生素RQs的空间分布情况见图 6.结果表明, 江河流域的沉积物中四环素、土霉素、金霉素和恩诺沙星的含量均小于PNEC值, 其生态毒性风险均处于可接受水平.但诺氟沙星在6个江河中有4个沉积物的RQs>1.RQs值从大到小依次为:海河(64.6)>珠江(12.5)>辽河(1.97)>黄河(1.58).以上江河沉积物中高诺氟沙星含量可能会对底栖水生生物造成危害, 值得关注.
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基于自然资源部标准地图服务网站GS(2020)4619号标准地图制作, 底图无修改; 数据整理自文献[68~80] 图 6 我国部分地区沉积物点位RQs等级化分布 Fig. 6 Distribution map of contaminated sediment RQs site in some regions of China |
各类养殖场沉积物中四环素类抗生素的检出率相对较高, RQs平均值从大到小依次为:金霉素(564)>四环素(146)>土霉素(6.50)>诺氟沙星(4.17)>恩诺沙星(0.01).但不同沉积物类型中抗生素含量差异较大, 如猪场和鸡场沉积物中的金霉素风险商值均远大于1, 如新兴市簕竹镇养猪场金霉素含量为347 mg·kg-1, 是金霉素PNEC值的1.76×103倍, 表明我国部分地区养殖场沉积物环境中金霉素处于高含量水平.沉积物中高金霉素含量可能会存在潜在生态环境风险, 值得关注.
沉积物中抗生素RQs的分布情况见图 6, 结果表明, 全国约88.9%的点位江河沉积物RQs值小于1, 生态风险等级属于低风险、中风险或无风险.高风险的点位主要分布在黄河、海河、辽河和珠江, 这些地区沉积物中的主要污染物为诺氟沙星.而在养殖场沉积物中有72.5%的点位RQs值大于1, 主要污染物为金霉素.
如图 7所示, 风险商值热图中只有诺氟沙星对江河沉积物表现为高风险, 占整个研究区域内点位的14.8%, 中风险、低风险和无风险点位分别占22.2%、44.4%和18.5%.而在养殖场沉积物中, 4种抗生素表现为高风险, 分别是四环素、土霉素、金霉素和诺氟沙星, 高风险、中风险、低风险和无风险点位占比分别为73.7%、3.95%、7.89%和14.7%.
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1.长江三角洲, 2.苕溪, 3.黄河, 4.海河, 5.辽河, 6.珠江, 7.佛岗市龙山镇养猪场, 8.清远市石角镇养猪场, 9.广州增城市中新镇养猪场, 10.广州新塘镇养猪场, 11.从化市石岭镇养猪场, 12.三水市养猪场, 13.新兴市簕竹镇养猪场, 14.新丰市板岭镇养猪场, 15.东莞市横沥镇养猪场, 16.清远市莲塘镇养猪场, 17.乳源市龙南镇养猪场, 18.广州增城市福新镇养猪场, 19.广州增城市福和镇养猪场, 20.广州增城市广三保养猪场, 21.三水市养鸡场, 22.新兴市簕竹镇养鸡场; 白色填充表示无数据 图 7 沉积物中抗生素的风险商 Fig. 7 RQs of antibiotics in sediments |
将我国部分地区土壤环境中抗生素的含量与PNEC值相比较, 土壤中抗生素RQs的分布情况见图 8.结果显示, 15个省份和区域中有4个省份的土壤中四环素RQs>1, RQs值由大到小依次为:辽宁(7.25)>四川(4.60)>天津(1.38)=山东(1.38). 8个省份(四川、辽宁、云南、天津、福建、北京、江苏和浙江)的土壤金霉素RQs>1.以上地区土壤存在潜在生态风险, 应当引起重视.在所有省份中, 土霉素的RQs值均小于1, 表明我国大部分地区土壤环境中土霉素处于可接受水平.图 8中显示我国土壤中主要污染物为金霉素.
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基于自然资源部标准地图服务网站GS(2020)4619号标准地图制作, 底图无修改; 数据整理自文献[81~113] 图 8 我国部分地区土壤点位RQs等级化分布 Fig. 8 Distribution map of contaminated soil RQ sites in some regions of China |
如图 9所示, 四环素和金霉素对我国部分地区土壤表现为高风险, 占整个研究区域的28.6%, 中风险、低风险和无风险点位分别占33.3%、26.2%和11.9%.
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1.北京, 2.天津, 3.辽宁, 4.河北, 5.山东, 6.上海, 7.江苏, 8.浙江, 9.福建, 10.云南, 11.江西, 12.四川, 13.广东, 14.珠江三角洲 图 9 土壤中抗生素的风险商 Fig. 9 RQs of antibiotics in soil |
(1) 从水体、沉积物、土壤的调查结果来看, 我国各地环境介质中不同程度地受到了抗生素的污染, 其中, 养殖场沉积物污染最严重.
(2) 空间分布特征结果表明, 南方地区水体污染较为严重, 而西部地区则较轻.结合现状分析, 主要来源为医疗和畜禽养殖业废水的排放, 人口活动密集和经济产业快速发展所导致.
(3) 生态风险评价结果表明我国水体中红霉素、罗红霉素、四环素、金霉素、磺胺甲
(4) 需要进一步补充水体、沉积物和土壤中抗生素在国内其他区域的空间分布特征, 以形成抗生素的全覆盖空间分布特征, 为我国抗生素污染防控和管理提供精准数据支撑.
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