深圳河流PPCPs分布及对浮游细菌生态驱动作用研究

王丝可; 罗顺才; 刘雨鑫; 潘志成; 左剑恶

doi:10.13205/j.hjgc.202508003

深圳河流PPCPs分布及对浮游细菌生态驱动作用研究

doi: 10.13205/j.hjgc.202508003

王丝可¹,
罗顺才^1,2,
刘雨鑫²,
潘志成^1,3, ,,
左剑恶^2,4

1. 深圳职业技术大学材料与环境工程学院, 广东深圳 518055;
2. 清华大学深圳国际研究生院, 广东深圳 518055;
3. 海天水务集团股份公司, 成都 610095;
4. 清华大学环境学院环境模拟与污染控制国家重点联合实验室, 北京 100084

基金项目:

深圳市科技创新委员会优秀科技创新人才培养（RCBS20221008093105020）；深圳市科技创新委员会可持续发展专项（KCXFZ20211020163556020）

详细信息

作者简介:
王丝可，博士，副教授，主要研究方向为水处理生物技术与河流生态。wangsike@szpu.edu.cn

通讯作者:
潘志成，博士，教授，主要研究方向为废水低碳处理技术。panzhicheng107@126.com

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出版历程
- 收稿日期: 2025-04-28
- 录用日期: 2025-07-09
- 修回日期: 2025-07-03

Distribution of PPCPs in rivers in Shenzhen and their ecological driving effects on phytoplankton bacteria

WANG Sike¹,
LUO Shuncai^1,2,
LIU Yuxin²,
PAN Zhicheng^{1,3
, ,},
ZUO Jian'e^2,4

1. School of Materials and Environmental Engineering, Shenzhen Polytechnic University, Shenzhen 518055, China;
2. Tsinghua Shenzhen International Graduate School, Tsinghua University, Shenzhen 518055, China;
3. Haitian Water Group Co., Ltd., Chengdu 610095, China;
4. State Key Joint Laboratory of Environmental Simulation and Pollution Control, School of Environment, Tsinghua University, Beijing 100084, China

摘要

摘要: 为评估高度城镇化的深圳城市河流中药物与个人护理品（PPCPs）的污染特征及其生态效应，选取深圳河流域4条典型城市河流（深圳河、布吉河、福田河、大沙河），检测16种PPCPs的时空分布，解析浮游细菌群落结构和PPCPs的驱动作用。结果表明：深圳河流中共检出15种PPCPs，总平均浓度为1127.75 ng/L（浓度范围148.74~2427.4 ng/L），丰水期浓度（1518.27 ng/L）显著高于枯水期（737.23 ng/L），其中，林可霉素和咖啡因为主要污染物。4条河流中，大沙河PPCPs浓度较低；深圳河流的浮游细菌群落以变形菌门（平均相对丰度38.7%）和拟杆菌门（21.3%）为优势类群，深圳河物种丰富度最高，且不同河流间浮游细菌群落组成差异显著，而对同一河流而言，丰水期与枯水期浮游细菌组成无显著差异。冗余分析发现，丰水期罗红霉素、克拉霉素、环丙沙星、阿替洛尔和咖啡因显著驱动河流细菌群落结构，而枯水期以咖啡因和阿替洛尔为主要驱动因素。结果表明：深圳河流域PPCPs污染潜在地影响河流菌群结构和微生物生态功能，需加强流域新兴污染物的动态监测与风险管控。
- PPCPs /
- 时空分布 /
- 浮游细菌 /
- 生态驱动 /
- 深圳河流域
Abstract: To assess the pollution characteristics of pharmaceuticals and personal care products （PPCPs） and their ecological effects in the highly urbanized rivers in Shenzhen， this study selected four typical urban rivers in the Shenzhen River Basin， namely the Shenzhen River， Buji River， Futian River， and Dasha River. The spatial and temporal distribution of 16 PPCPs was detected， the community structure of planktonic bacteria was analyzed， and the driving effects of PPCPs （on bacterial community） was examined. A total of 15 PPCPs were detected in the four rivers of Shenzhen， with a total average concentration of 1127.75 ng/L， range from 148.74 to 2427.4 ng/L. The concentration in the wet season （1518.27 ng/L） was significantly higher than that in the dry season （737.23 ng/L）， among which lincomycin and caffeine were the main pollutants. Among the four rivers， the Dasha River had relatively lower PPCPs concentrations. The planktonic bacterial community in the rivers of Shenzhen was dominated by Proteobacteria （average relative abundance： 38.7%） and Bacteroidetes （21.3%）. The Shenzhen River exhibited the highest species richness， and there were significant differences in planktonic bacterial community compositions among different rivers， whereas no significant differences were observed in the planktonic bacterial community compositions between the wet season and dry season for the same river. Redundancy analysis revealed that in the wet season， roxithromycin， clarithromycin， ciprofloxacin， atenolol， and caffeine significantly drove the structure of river bacterial communities； in the dry season， however， caffeine and atenolol were the main driving factors. These results indicate that PPCPs pollution in the Shenzhen River Basin potentially affects the structure of river microbial communities and their ecological functions. Therefore， dynamic monitoring and risk management of emerging pollutants in the basin should be strengthened.
- PPCPs /
- spatial and temporal distribution /
- phytoplankton bacteria /
- ecological driving /
- Shenzhen River Basin

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参考文献(28)

[1]	BU Q，WANG B，HUANG J，et al. Pharmaceuticals and personal care products in the aquatic environment in China：a review[J]. Journal of Hazardous Materials，2013，262：189-211.
[2]	WANG F，XIANG L，SZE-YIN LEUNG K，et al. Emerging contaminants：A One Health perspective[J]. Innovation，2024，5（4）：100612.
[3]	QIAO M，YING G G，SINGER A C，et al. Review of antibiotic resistance in China and its environment [J]. Environment International，2018，110（10）：160-172.
[4]	XIE W Y， SHEN Q， ZHAO F J. Antibiotics and antibiotic resistance from animal manures to soil：a review[J]. European Journal of Soil Science，2018，69（1）：181-195.
[5]	ROSI E J，BECHTOLD H A，SNOW D，et al. Urban stream microbial communities show resistance to pharmaceutical exposure [J]. Ecosphere，2018，9（1）：e02041.
[6]	MIZUKAWA A，FILIPPE T C，PEIXOTO L O M，et al. Caffeine as a chemical tracer for contamination of urban rivers[J]. RBRH， 2019，24（29）：1-10.
[7]	HUERTA-FONTELA M， GALCERAN M T， VENTURA F. Stimulatory drugs of abuse in surface waters and their removal in a conventional drinking water treatment plant[J]. Environmental Science & Technology，2008，42（18）：6809-6816.
[8]	WANG Z，ZHANG X H，HUANG Y，et al. Comprehensive evaluation of pharmaceuticals and personal care products（PPCPs） in typical highly urbanized regions across China[J]. Environmental Pollution，2015，204：223-232.
[9]	陈立春，吴春雷，曾筱荃，等.深圳典型黑臭河道精准截排及底泥修复技术应用示范[J].给水排水，2023，49（1）：22-29. CHEN L C，WU C L，ZENG X Q，et al. Implementation of pinpoint sewage separation system and in-situ sludge remediation in Shenzhen[J]. Water & Wastewater Engineering，2023，49（1）： 22-29.
[10]	HOU L，YIN G，LIU M，et al. Effects of sulfamethazine on denitrification and the associated N₂O release in estuarine and coastal sediments[J]. Environmental Science & Technology，2015， 49（1）：326-333.
[11]	FENG Y，HU J，CHEN Y，et al. Ecological response to antibiotics re-entering the aquaculture environment with possible long-term antibiotics selection based on enzyme activity in sediment[J]. Environmental Science and Pollution Research，2022，29（13）： 19033-19044.
[12]	STOVER E M，AND JUDD K E. Low-level pharmaceuticals alter stream biofilm structure and function[J]. Chemistry and Ecology， 2021，37（7）：616-632.
[13]	李可，李学云，丘汾，等.深圳主要水体中20种抗生素药物分布特征[J].环境卫生学杂志，2019，9（5 ）：455-461. LI K，LI X Y，QIU F，et al. Determination and distribution characteristics of 20 antibiotics in major rivers and bays of Shenzhen [J]. Journal of Environmental Hygiene，2019，9（5）：455-461.
[14]	HEIDLER J，HALDEN R U. Mass balance assessment of triclosan removal during conventional sewage treatment[J]. Chemosphere， 2007，66（2）：362-369.
[15]	MEHRTENS A，LICHA T，BURKE V. Occurrence，effects and behaviour of the antibiotic lincomycin in the agricultural and aquatic environment： a review [J]. Science of the Total Environment，2021，778：146306.
[16]	KUSTER M，LÓPEZ DE ALDA M J，HERNANDO M D，et al. Analysis and occurrence of pharmaceuticals， estrogens， progestogens and polar pesticides in sewage treatment plant effluents，river water and drinking water in the Llobregat River Basin（Barcelona，Spain）[J]. Journal of Hydrology，2008，358（1）：112-123.
[17]	SUN C，DONG D，HE S，et al. Multimedia fate modeling of antibiotic sulfamethoxazole， lincomycin， and florfenicol in a seasonally ice-covered river receiving WWTP effluents [J]. Environmental Science and Pollution Research，2019，26（17）： 17351-17361.
[18]	CARMONA E， ANDREU V， PICÓ Y. Occurrence of acidic pharmaceuticals and personal care products in Turia River Basin： From waste to drinking water [J]. Science of the Total Environment， 2014，484：53-63.
[19]	SHARMA B M，BEČANOVÁ J，SCHERINGER M，et al. Health and ecological risk assessment of emerging contaminants （pharmaceuticals， personal care products， and artificial sweeteners） in surface and groundwater （drinking water） in the Ganges River Basin，India[J]. Science of the Total Environment， 2019，646：1459-1467.
[20]	KIBUYE F A，GALL H E，VEITH T L，et al. Influence of hydrologic and anthropogenic drivers on emerging organic contaminants in drinking water sources in the Susquehanna River Basin[J]. Chemosphere，2020，245：125583.
[21]	SENGUPTA A，LYONS J M，SMITH D J，et al. The occurrence and fate of chemicals of emerging concern in coastal urban rivers receiving discharge of treated municipal wastewater effluent[J]. Environmental Toxicology and Chemistry，2014，33（2）：350-358.
[22]	秀措，王尘辰，吕永龙，等.潮汕地区入海河流及水生生物中PPCPs分布特征及风险评估[J].环境科学，2020，41（10）：4514-4524. XIU C，WANG C C，LÜ Y L，LU Y F，et al. Distribution characteristics and risk assessment of PPCPs in surface water and aquatic organisms in Chaoshan coastal area along the South China Sea[J]. Environmental Science，2020，41（10）：4514-4524.
[23]	ZHANG L，FANG S，HONG W，et al. Differences in pathogenic community assembly processes and their interactions with bacterial communities in river and lake ecosystems[J]. Environmental Research，2023，236：116847.
[24]	REIS M P，SUHADOLNIK M L S，DIAS M F，et al. Characterizing a riverine microbiome impacted by extreme disturbance caused by a mining sludge tsunami [J]. Chemosphere，2020，253：1-15.
[25]	SHI Z J，HU H Y，SHEN Y Y，et al. Long-term effects of oxytetracycline （OTC） on the granule-based anammox：Process performance and occurrence of antibiotic resistance genes[J]. Biochemical Engineering Journal，2017，127：110-118.
[26]	ZHANG Q，WU J，YU Y Y，et al. Microbial and genetic responses of anammox process to the successive exposure of different antibiotics[J] //Chemical Engineering Journal， 2021，420（2）： 127576.
[27]	HU A，JU F，HOU L，et al. Strong impact of anthropogenic contamination on the co-occurrence patterns of a riverine microbial community[J]. Environmental Microbiology，2017，19（12）：4993-5009.
[28]	ŚWIACKA K， MACULEWICZ J， KOWALSKA D， et al. Do pharmaceuticals affect microbial communities in aquatic environments：a review[J]. Frontiers in Environmental Science， 2023，10（1）：1-15.