Special distribution and seasonal variation of perfluoroalkyls substances in Lhasa River Basin, China
SUN Dian-chao1,3, GONG Ping1,2, WANG Xiao-ping1,2,3, WANG Chuan-fei1,2
1. Key Laboratory of Tibetan Environment Changes and Land Surface Processes, Institute of Tibetan Plateau Research, Chinese Academy of Sciences, Beijing 100101, China;
2. Chinese Academy of Sciences Center for Excellence in Tibetan Plateau Earth Sciences, Beijing 100101, China;
3. University of Chinese Academy of Sciences, Beijing 100049, China
The levels and compositions of 17 Perfluoroalkyls Substances (PFASs) were determined by UltiMate 3000DGLC-MS/MS for the first time in river water, wastewater of Lhasa, one of the highest plateau city (average elevation 3700m), during wet and dry season in 2016. Lhasa was commonly contaminated by PFASs. The average Σ13 PFASs concentration of surface water of Lhasa River was 322pg/L, ranged from 60 to 1724pg/L. The predominant PFASs were short-chain pefluorobutanoate (PFBA) (25%), perfluoropentanoate (PFPeA) (22%), perfluorooctanoic acid (PFOA) (14%), perfluorooctanesulfonate (PFOS) (14%) and perfluorobutanesulfonate (PFBS) (13%). The spatial distribution of PFASs in Lhasa River revealed that the wastewater not totally assimilated into wastewater treatment plant, and Lhasa River basin was mainly polluted by point sources emission. There was a limited transform of production and use from PFOA and PFOS in Tibet. Seasonal variation of profiles and levels of PFASs in both wet and dry seasons suggested that the use and discharge schema of PFASs in Lhasa were influenced by season. The annual discharge load of PFASs from WWTP to Lhasa River was estimated to be 37mg/a, input amount of PFASs from The Lhasa River basin into YarlungZangbo River were estimated to be 292t/a. In the future, all the wastewater should be strictly incorporated into WWTP and PFASs-based product should be restrained.
孙殿超, 龚平, 王小萍, 王传飞. 拉萨河全氟化合物的时空分布特征研究[J]. 中国环境科学, 2018, 38(11): 4298-4306.
SUN Dian-chao, GONG Ping, WANG Xiao-ping, WANG Chuan-fei. Special distribution and seasonal variation of perfluoroalkyls substances in Lhasa River Basin, China. CHINA ENVIRONMENTAL SCIENCECE, 2018, 38(11): 4298-4306.
Wang Z, Cousins I T, Scheringer M, et al. Global emission inventories for C4-C14 perfluoroalkyl carboxylic acid (PFCA) homologues from 1951 to 2030, part Ⅱ:the remaining pieces of the puzzle[J]. Environ Int, 2014,69:166-76.
[2]
Wang T, Vestergren R, Herzke D, et al. Levels, Isomer Profiles, and Estimated Riverine Mass Discharges of Perfluoroalkyl Acids and Fluorinated Alternatives at the Mouths of Chinese Rivers[J]. Environmental Science & Technology, 2016,50(21):11584-11592.
Zhao Z, Xie Z Y, Tang J H, et al. Seasonal variations and spatial distributions of perfluoroalkyl substances in the rivers Elbe and lower Weser and the North Sea[J]. Chemosphere, 2015,129:118-125.
[6]
Tsuda T, Inoue A, Igawa T, et al. Seasonal Changes of PFOS and PFOA Concentrations in Lake Biwa Water[J]. Bulletin of Environmental Contamination and Toxicology, 2010,85(6):593-597.
[7]
Zhu Z Y, Wang T Y, Meng J, et al. Perfluoroalkyl substances in the Daling River with concentrated fluorine industries in China:seasonal variation, mass flow, and risk assessment[J]. Environmental Science and Pollution Research, 2015,22(13):10009-10018.
[8]
Pignotti E, Casas G, Llorca M, et al. Seasonal variations in the occurrence of perfluoroalkyl substances in water, sediment and fish samples from Ebro Delta (Catalonia, Spain)[J]. Science of the Total Environment, 2017,607:933-943.
[9]
Boiteux V, Bach C, Sagres V, et al. Analysis of 29per- and polyfluorinated compounds in water, sediment, soil and sludge by liquid chromatography-tandem mass spectrometry[J]. International Journal of Environmental Analytical Chemistry, 2016,96(8):705-728.
[10]
Pan C G, Ying G G, Zhao J L, et al. Spatiotemporal distribution and mass loadings of perfluoroalkyl substances in the Yangtze River of China[J]. Science of the Total Environment, 2014,493:580-587.
[11]
Yeung L W Y, Yamashita N, Taniyasu S, et al. A survey of perfluorinated compounds in surface water and biota including dolphins from the Ganges River and in other waterbodies in India[J]. Chemosphere, 2009,76(1):55-62.
[12]
Habibullah-Al-Mamun M, Ahmed M K, Raknuzzaman M, et al. Occurrence and distribution of perfluoroalkyl acids (PFAAs) in surface water and sediment of a tropical coastal area (Bay of Bengal coast, Bangladesh)[J]. Science of the Total Environment, 2016,571:1089-1104.
[13]
Zushi Y, Ye F, Motegi M, et al. Spatially Detailed Survey on Pollution by Multiple Perfluorinated Compounds in the Tokyo Bay Basin of Japan[J]. Environmental Science & Technology, 2011,45(7):2887-2893.
[14]
Lam N H, Cho C R, Lee J S, et al. Perfluorinated alkyl substances in water, sediment, plankton and fish from Korean rivers and lakes:A nationwide survey[J]. Science of the Total Environment, 2014,491:154-162.
[15]
Ahrens L, Felizeter S, Sturm R, et al. Polyfluorinated compounds in waste water treatment plant effluents and surface waters along the River Elbe, Germany[J]. Mar Pollut Bull, 2009,58(9):1326-33.
[16]
Levengood J M, Soucek D J, Sass G G, et al. Interspecific and Spatial Comparisons of Perfluorinated Compounds in Bighead and Silver Carp in the Illinois River, Illinois, USA[J]. Bulletin of Environmental Contamination and Toxicology, 2015,95(5):561-566.
[17]
Zhao Z, Xie Z Y, Moller A, et al. Distribution and long-range transport of polyfluoroalkyl substances in the Arctic, Atlantic Ocean and Antarctic coast[J]. Environmental Pollution, 2012,170:71-77.
[18]
Zhao P J, Xia X H, Dong J W, et al. Short- and long-chain perfluoroalkyl substances in the water, suspended particulate matter, and surface sediment of a turbid river[J]. Science of the Total Environment, 2016,568:57-65.
[19]
Yao Y M, Zhu H K, Li B, et al. Distribution and primary source analysis of per- and poly-fluoroalkyl substances with different chain lengths in surface and groundwater in two cities, North China[J]. Ecotoxicology and Environmental Safety, 2014,108:318-328.
[20]
Zhang Y Z, Wang B, Wang W, et al. Occurrence and source apportionment of Per- and poly-fluorinated compounds (PFCs) in North Canal Basin, Beijing[J]. Sci Rep, 2016,6:36683.
[21]
Kwok K Y, Wang X H, Ya M L, et al. Occurrence and distribution of conventional and new classes of per- and polyfluoroalkyl substances (PFASs) in the South China Sea[J]. Journal of Hazardous Materials, 2015,285:389-397.
[22]
Zhang W, Zhang Y T, Taniyasu S, et al. Distribution and fate of perfluoroalkyl substances in municipal wastewater treatment plants in economically developed areas of China[J]. Environmental Pollution, 2013,176:10-17.
[23]
Zhang X M, Lohmann R, Dassuncao C, et al. Source Attribution of Poly- and Perfluoroalkyl Substances (PFASs) in Surface Waters from Rhode Island and the New York Metropolitan Area[J]. Environmental Science & Technology Letters, 2016,3(9):316-321.
[24]
Wang X P, Halsall C, Codling G, et al. Accumulation of Perfluoroalkyl Compounds in Tibetan Mountain Snow:Temporal Patterns from 1980 to 2010[J]. Environmental Science & Technology, 2014,48(1):173-181.
[25]
Kim H Y, Seok H W, Kwon H O, et al. A national discharge load of perfluoroalkyl acids derived from industrial wastewater treatment plants in Korea[J]. Science of the Total Environment, 2016,563:530-537.
[26]
Chen H, Wang X M, Zhang C, et al. Occurrence and inputs of perfluoroalkyl substances (PFASs) from rivers and drain outlets to the Bohai Sea, China[J]. Environmental Pollution, 2017,221:234-243.