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中国巢湖水中的全氟烷基酸(PFAAs)在水生动物中的残留、生物积累和生物放大作用。

Residues, bioaccumulations and biomagnification of perfluoroalkyl acids (PFAAs) in aquatic animals from Lake Chaohu, China.

机构信息

MOE Laboratory for Earth Surface Processes, College of Urban & Environmental Sciences, Peking University, Beijing 100871, China.

MOE Laboratory for Earth Surface Processes, College of Urban & Environmental Sciences, Peking University, Beijing 100871, China.

出版信息

Environ Pollut. 2018 Sep;240:607-614. doi: 10.1016/j.envpol.2018.05.001. Epub 2018 May 12.

Abstract

Residual levels of perfluoroalkyl acids (PFAAs) in seven species of aquatic animals were analyzed by liquid chromatography-mass spectrometry. The distribution, composition, bioaccumulation, and biomagnification of PFAAs and their effect factors were studied. The results showed that: 1) Wet weight concentrations of 17 PFAAs in the aquatic animals ranged from 1.77 to 38.65 ng/g, with a mean value of 12.71 ± 9.21 ng/g. PFOS was the predominant contaminant (4.57 ± 4.57 ng/g, 6.76%-46.25%), followed by PFDA (1.95 ± 1.37 ng/g, 11.68%-21.25%) and PFUdA (1.84 ± 1.21 ng/g, 9.73%-35.34%. 2) PFAA residual levels in Culter erythropterus (30.98 ± 6.65 ng/g) were the highest, followed by Hemibarbus maculatus (16.79 ± 1.88 ng/g), while the PFAA levels in Carassius auratus were the lowest (2.22 ± 0.60 ng/g). 3) Biota-water bioaccumulation factors (BAFs), biota-suspended solid accumulation factors (BSSAFs) and biota-sediment accumulation factors (BSAFs) ranged from 0.35 to 12,370.51, 7.77 to 8452.92 and 9.10 to 6984.61, respectively. Bioaccumulation by shrimp and snails was significantly affected by Kow. 4) Food web magnification factors were greater than 1, indicating that biomagnification of PFAAs occurs across trophic levels. The bioaccumulation and biomagnification of PFAAs were significantly correlated with carbon chain length.

摘要

采用液相色谱-质谱法分析了七种水生动物中全氟烷基酸(PFAAs)的残留水平。研究了 PFAAs 的分布、组成、生物积累和生物放大及其影响因素。结果表明:1)水生动物中 17 种 PFAAs 的湿重浓度范围为 1.77-38.65ng/g,平均值为 12.71±9.21ng/g。PFOS 是主要污染物(4.57±4.57ng/g,6.76%-46.25%),其次是 PFDA(1.95±1.37ng/g,11.68%-21.25%)和 PFUdA(1.84±1.21ng/g,9.73%-35.34%)。2)Culter erythropterus(30.98±6.65ng/g)的 PFAAs 残留水平最高,其次是Hemibarbus maculatus(16.79±1.88ng/g),而Carassius auratus 的 PFAAs 水平最低(2.22±0.60ng/g)。3)生物-水生物浓缩因子(BAFs)、生物-悬浮固体浓缩因子(BSSAFs)和生物-沉积物浓缩因子(BSAFs)范围分别为 0.35-12370.51、7.77-8452.92 和 9.10-6984.61。虾和螺类的生物积累受 Kow 的显著影响。4)食物网放大因子大于 1,表明 PFAAs 在营养级间发生生物放大。PFAAs 的生物积累和生物放大与碳链长度显著相关。

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