墨水河表层沉积物中多环芳烃(PAHs)的分布特征、来源解析及生态风险评价
Distribution, source and ecological risk assessment of polycyclic aromatic hydrocarbons (PAHs) in surface sediments from Moshui River
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摘要: 本文运用GC-MS测定了墨水河表层沉积物中16种优控多环芳烃(PAHs)浓度,采用多种数据分析技术解析了PAHs的来源.结果表明,苊烯、苊、蒽和苯并(a)蒽在部分样品中未检出,其余12种在所有样品中均有检出,16种PAHs总浓度为196.51-8549.33 ng·g-1,平均浓度为3320.03 ng·g-1.沉积物中PAHs的环数分布以高环为主,运用轻重比、分子比值和主成分分析-多元线性回归模型(PCA-MLR)等3种方法,共同确定PAHs的主要来源分别为混合源(煤炭、生物质和汽油燃烧源)、柴油燃烧源和石油源,这3种来源对总PAHs的贡献分别为59.8%、26.0%和14.2%.效应区间低/中值法(ERL/ERM)对PAHs生态风险分析表明,芴、菲、苯并(a)蒽、、苯并(b)荧蒽、苯并(k)荧蒽和苯并(a)芘在墨水河中下游偶尔会产生负面生态风险,二苯并(a,h)蒽存在经常产生负面生态效应的可能;平均效应区间中值商法(M-ERM-Q)分析表明,墨水河上游和入海口处PAHs的综合生态风险较低,而中下游站位则具有中低风险.Abstract: Sixteen priority polycyclic aromatic hydrocarbons(PAHs) in the surface sediments from Moshui River were quantified by GC-MS, and sources of PAHs were analyzed based on a variety of data analysis methods. Twelve PAHs were detected in all the samples, excluding acenaphthylene, acenaphthene, anthracene and benzo(a)anthracene, which were not detected in some samples. The total concentrations of PAHs ranged from 196.51 to 8549.33 ng·g-1, with a mean value of 3320.03 ng·g-1. The proportion of 4—6 ring-PAHs was quite high. Low molecular weight/high molecular weight PAHs (LMW/HMW), molecular diagnostic ratios and principal component analysis-multiple linear regression (PCA-MLR) were used to determine the sources of PAHs. The results suggested that the source contributions were 59.8% from the mixed source (coal, biomass and gasoline combustion), 26% from diesel engine emission, and 14.2% from petroleum source. Methods of effects range low/effects range median(ERL/ERM) and mean effects range-median quotient (M-ERM-Q) were used to analyze the ecological risks of PAHs. ERL/ERM results indicated that fluorine, phenanthrene, benzo(a)anthracene, chrysene, benzo(b)- fluoranthene, benzo(k)fluoranthene and benzo(a)pyrene might cause occasionally adverse ecological effects and dibenzo(a,h)anthrancene might cause frequently adverse ecological effects at the middle and lower reaches of Moshui River. Results of M-ERM-Q suggested that the combined risk of PAHs is relatively low for the upper reach and estuary region, and is low to middle for the middle and lower reaches.
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[1] ARIAS A H, VAZQUEZ-BOTELLO A, TOMBESI N, et al. Presence, distribution, and origins of polycyclic aromatic hydrocarbons (PAHs) in sediments from Bahía Blanca estuary, Argentina[J]. Environmental Monitoring and Assessment, 2008, 160(1-4):301-314. [2] SUN J H, WANG G L, CHAI Y, et al. Distribution of polycyclic aromatic hydrocarbons (PAHs) in Henan Reach of the Yellow River, Middle China[J]. Ecotoxicology and Environmental Safety, 2009, 72(5):1614-1624. [3] LIN Y, DENG W, LI S, et al. Congener profiles, distribution, sources and ecological risk of parent and alkyl-PAHs in surface sediments of Southern Yellow Sea, China[J]. Science of The Total Environment, 2017, 580(3):1309-1317. [4] LI J F, DONG H, ZHANG D H, et al. Sources and ecological risk assessment of PAHs in surface sediments from Bohai Sea and northern part of the Yellow Sea, China[J]. Marine Pollution Bulletin, 2015, 96(1-2):485-490. [5] CULOTTA L, STEFANO C D, GIANGUZZA A, et al. The PAH composition of surface sediments from Stagnone coastal lagoon, Marsala (Italy)[J]. Marine Chemistry, 2006, 99(1):117-127. [6] DENG W, LI X G, LI S Y, et al. Source apportionment of polycyclic aromatic hydrocarbons in surface sediment of mud areas in the East China Sea using diagnostic ratios and factor analysis[J]. Marine Pollution Bulletin, 2013, 70(1-2):266-273. [7] [8] LONG E R, MACDONALD D D, SMITH S L, et al. Incidence of adverse biological effects within ranges of chemical concentratlons in marine and estuarine sediments[J]. Environmental Management, 1995, 19(1):81-97. [9] WANG X C, SUN S, MA H Q, et al. Sources and distribution of aliphatic and polyaromatic hydrocarbons in sediments of Jiaozhou Bay, Qingdao, China[J]. Marine Pollution Bulletin, 2006, 52(2):129-138. [10] 许云竹,花修艺,董德明,等. 地表水环境中PAHs源解析的方法比较及应用[J]. 吉林大学学报:理学版, 2011, 49(3):565-574. XU Y Z, HUA X Y, DONG D M, et al. Comparison among methods of source apportionment of pahs and their application in surface water analysis[J]. Journal of Jilin University (Science Edition), 2011, 49(3):565-574(in Chinese).
[11] YUNKER M B, MACDONALD R W, VINGARZAN R, et al. PAHs in the Fraser River basin:A critical appraisal of PAH ratios as indicators of PAH source and composition[J]. Organic Geochemistry, 2002, 33(4):489-515. [12] CHEN C F, CHEN C W, DONG C D, et al. Assessment of toxicity of polycyclic aromatic hydrocarbons in sediments of Kaohsiung Harbor, Taiwan[J]. Science of The Total Environment, 2013, 463-464(5):1174-1181. [13] PANDEY P K, PATEL K S, LENICEK J. Polycyclic aromatic hydrocarbon:need for assessment of health risks in India Study of an urban-industrial location in India[J]. Environmental Monitoring and Assessment, 1999, 59(3):297-319. [14] LEMIEUX P M, LUTES C C, SANTOIANNI D A. Emissions of organic air toxics from open burning:A comprehensive review[J]. Progress in Energy and Combustion Science, 2004, 30(1):1-32. [15] LARSEN R K, BAKER J E. Source apportionment of polycyclic aromatic hydrocarbons in the urban atmosphere:A comparison of three methods[J]. Environmental Science & Technology, 2003, 37(9):1873-1881. [16] BOONYATUMANOND R, WATTAYAKORN G, TOGO A, et al. Distribution and origins of polycyclic aromatic hydrocarbons (PAHs) in riverine, estuarine, and marine sediments in Thailand[J]. Marine Pollution Bulletin, 2006, 52(8):942-956. [17] MARR L C, KIRCHSTETTER T W, HARELY A. Characterization of polycyclic aromatic hydrocarbons in motor vehicle fuels and exhaust emissions[J]. Environmental Science & Technology, 1999, 33(18):3091-3099. [18] PAROLINI M, BINELLI A, MATOZZO V, et al. Persistent organic pollutants in sediments from the Lagoon of Venice-A possible hazard for sediment-dwelling organisms[J]. Journal of Soils and Sediments, 2010, 10(7):1362-1379. [19] MCCREADY S, BIRCH G F, LONG E R, et al. Predictive abilities of numerical sediment quality guidelines in Sydney Harbour, Australia, and vicinity[J]. Environment International, 2006, 32(5):638-649. [20] HUANG W, WANG Z, YAN W. Distribution and sources of polycyclic aromatic hydrocarbons (PAHs) in sediments from Zhanjiang Bay and Leizhou Bay, South China[J]. Marine Pollution Bulletin, 2012, 64(9):1962-1969. -

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