Spatial and temporal variability in air concentrations of short-chain (C10-C13) and medium-chain (C14-C17) chlorinated n-alkanes measured in the UK atmosphere

被引:93
作者
Barber, JL [1 ]
Sweetman, AJ
Thomas, GO
Braekevelt, E
Stern, GA
Jones, KC
机构
[1] Univ Lancaster, Inst Environm & Nat Sci, Dept Environm Sci, Lancaster LA1 4YQ, England
[2] Inst Freshwater, Dept Fisheries & Oceans, Winnipeg, MB R3T 2N6, Canada
关键词
D O I
10.1021/es047949w
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Two studies were carried out on short-chain (C-10-C-13) and medium-chain (C-14-C-17) polychlorinated n-alkanes (sPCAs and mPCAs) in U.K. air samples. The first study entailed taking 20 24-h air samples with a pair of Hi-Vol air samplers at the Hazelrigg field station, near Lancaster University. These samples were carefully selected to coincide with times when air masses were predicted to have a fairly constant back trajectory for 24 h and to give a broad spectrum of different origins. The second study was a spatial survey of PCAs in the air at 20 outdoor sites in northern England and four indoor locations in Lancaster, using polyurethane foam (PUF) disk passive air samplers. Levels of the sPCAs in the Hi-Vol samples ranged from < 185 to 3430 pg m(-3) (average 1130 pg m(-3)) and were higher than those previously measured at this site in 1997. Levels of the mPCAs ranged from < 811 to 14 500 pg m(-3) (average 3040 pg m(-3)); that is, they were higher than sPCAs. Both sPCA and mPCA air concentrations are of the same order of magnitude as PAH at this site. Back trajectory analysis showed that the history of the air mass in the 48 h prior to sampling had an important effect on the concentrations observed, with overland samples having higher levels than oceanic, implying that the U.K. is probably responsible for most of the PCAs measured in the U.K. atmosphere. Amounts of both sPCAs and mPCAs in the passive air samples followed a rural-urban gradient. PCAs appear to be released from multiple sources around the country, as a result of the diffusive, open industrial and construction use of the technical mixtures.
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页码:4407 / 4415
页数:9
相关论文
共 34 条
[1]  
Borgen AR., 2002, ORGANOHALOGEN COMPD, V59, P303
[2]  
Draxler R.R., 2010, HYSPLIT HYBRID SINGL
[3]  
Drouillard KG, 1998, ENVIRON TOXICOL CHEM, V17, P1252
[4]   Estimating the aqueous solubilities of individual chlorinated n-alkanes (C10-C12) from measurements of chlorinated alkane mixtures [J].
Drouillard, KG ;
Hiebert, T ;
Tran, P ;
Tomy, GT ;
Muir, DCG ;
Friesen, KJ .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 1998, 17 (07) :1261-1267
[5]  
*EUR CHEM BOARD, 2002, RISK ASS ALK C1J C17
[6]   Toxicity of C10-, C11-, C12-, and C14-polychlorinated alkanes to Japanese medaka (Oryzias latipes) embryos [J].
Fisk, AT ;
Tomy, GT ;
Muir, DCG .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 1999, 18 (12) :2894-2902
[7]   Dietary accumulation and depuration of individual C10-, C11- and C14-polychlorinated alkanes by juvenile rainbow trout (Oncorhynchus mykiss) [J].
Fisk, AT ;
Cymbalisty, CD ;
Tomy, GT ;
Muir, DCG .
AQUATIC TOXICOLOGY, 1998, 43 (2-3) :209-221
[8]  
Fisk AT, 2000, ENVIRON TOXICOL CHEM, V19, P1508, DOI 10.1897/1551-5028(2000)019&lt
[9]  
1508:DAAQSA&gt
[10]  
2.3.CO