Yali Shi

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Organization: University of Chinese Academy of Sciences
Department: Research Center for Eco-Environmental Science
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Co-reporter:Yuan Wang, Robin Vestergren, Yali Shi, Dong Cao, Lin Xu, Yaqi Cai, Xiaoli Zhao, and Fengchang Wu
Environmental Science & Technology 2016 Volume 50(Issue 20) pp:10923-10932
Publication Date(Web):September 27, 2016
DOI:10.1021/acs.est.6b01980
The use of cyclic perfluoroalkyl acids as anticorrosive agents in hydraulic fluids remains a poorly characterized source of organofluorine compounds to the environment. Here, we investigated the presence of perfluoroethylenecyclohexanesulfonate (PFECHS) isomers in environmental samples for the first time using a combination of high resolution and tandem mass spectrometry. Five distinct peaks attributed to different isomers of PFECHS and perfluoropropylcyclopentanesulfonate (PFPCPeS) were identified in environmental samples. The sum of PFECHS and PFPCPeS isomers displayed logarithmically decreasing spatial trends in water (1.04–324 ng/L) and sediment samples (
Co-reporter:Zhen Zhou, Yong Liang, Yali Shi, Lin Xu, and Yaqi Cai
Environmental Science & Technology 2013 Volume 47(Issue 16) pp:9249-9257
Publication Date(Web):July 24, 2013
DOI:10.1021/es402120y
Short-chain perfluoroalkyl acids (PFAAs), which have less than seven fluorinated carbons, have been introduced as substitutes for eight-carbon homologue products. In this study, water, sediment, and biological samples (fish and plant) were collected from Tangxun Lake, which is located near a production base of the fluorochemical industry in Wuhan, China. Perfluorobutane sulfonate (PFBS) and perfluorobutanoic acid (PFBA) were the predominant PFAAs in surface water, with average concentrations of 3660 ng/L and 4770 ng/L, respectively. However, perfluorooctane sulfonate (PFOS) was the most abundant PFAA in sediments, with an average concentration of 74.4 ng/g dw. The organic carbon normalized distribution coefficients (KOC) indicated that short-chain PFAAs (CF2 < 7) tended to have lower adsorption potentials than PFOS, perfluorooctanoic acid (PFOA), and longer perfluoroalkyl chain compounds. PFBS and PFBA could transport to a farther distance in the horizontal direction along the water flow and infiltrate into deeper depths in the vertical direction. However, levels of PFOS and PFOA in water dropped exponentially along the current, and their proportions were decreased gradually with the increasing depth in sediment cores. Furthermore, values of log bioconcentration factor (BCF) of the short-chain PFAAs were all relatively low (<1), indicating no bioaccumulation potentials for short-chain PFAAs in aquatic species.
Co-reporter:Zhen Zhou;Wenhui Li;Lin Xu
Bulletin of Environmental Contamination and Toxicology 2012 Volume 89( Issue 3) pp:519-524
Publication Date(Web):2012 September
DOI:10.1007/s00128-012-0745-1
The concentrations of 16 perfluorinated compounds (PFCs) were measured in surface water and organisms from Baiyangdian Lake. Perfluorooctanoic acid (PFOA), perfluorooctane sulfonic acid, and perfluorobutanoic acid (PFBA) were the major PFC species in the water at 6.8–56.8, 0.1–17.5 and 3.0–14.6 ng/L, respectively. The PFC contamination in Baiyangdian Lake was significantly impacted by the inflow from Pinghe River and Fuhe River. There was no significant correlation between the concentrations of PFCs and the trophic levels in aquatic organisms. There were no significant PFC risks in Baiyangdian Lake according to the risk assessment of PFCs in water.
Cyclohexanesulfonic acid, decafluoro(pentafluoroethyl)-
S-(4-METHYLPHENYL) BENZENECARBOTHIOATE
1-[(2R,3R)-1,1,2,6-tetramethyl-3-(propan-2-yl)-2,3-dihydro-1H-inden-5-yl]ethanone
1-(1,1,2,3,3,6-Hexamethyl-2,3-dihydro-1H-inden-5-yl)ethanone
Bis(2-methylpropyl) Hydrogen Phosphate
2-[(6-CHLORO-1,1,2,2,3,3,4,4,5,5,6,6-DODECAFLUOROHEXYL)OXYL]-1,1,2,2-TETRAFLUOROETHANESULFONIC ACID,POTASSIUM SALT
Hexadecasiloxane,1,1,1,3,3,5,5,7,7,9,9,11,11,13,13,15,15,17,17,19,19,21,21,23,23,25,25,27,27,29,29,31,31,31-tetratriacontamethyl-
Nonasiloxane,1,1,1,3,3,5,5,7,7,9,9,11,11,13,13,15,15,17,17,17-eicosamethyl-
Pentadecasiloxane,1,1,1,3,3,5,5,7,7,9,9,11,11,13,13,15,15,17,17,19,19,21,21,23,23,25,25,27,27,29,29,29-dotriacontamethyl-
Tetradecasiloxane,1,1,1,3,3,5,5,7,7,9,9,11,11,13,13,15,15,17,17,19,19,21,21,23,23,25,25,27,27,27-triacontamethyl-