<?xml version="1.0" encoding="UTF-8"?><xml><records><record><source-app name="Biblio" version="7.x">Drupal-Biblio</source-app><ref-type>17</ref-type><contributors><authors><author><style face="normal" font="default" size="100%">J. Wu</style></author><author><style face="normal" font="default" size="100%">Fang, X.</style></author><author><style face="normal" font="default" size="100%">Martin, J. W.</style></author><author><style face="normal" font="default" size="100%">Z. Zhai</style></author><author><style face="normal" font="default" size="100%">Su, S.</style></author><author><style face="normal" font="default" size="100%">Hu, X.</style></author><author><style face="normal" font="default" size="100%">Han, J.</style></author><author><style face="normal" font="default" size="100%">Lu, S.</style></author><author><style face="normal" font="default" size="100%">C. Wang</style></author><author><style face="normal" font="default" size="100%">J. Zhang</style></author><author><style face="normal" font="default" size="100%">J. Hu</style></author></authors></contributors><titles><title><style face="normal" font="default" size="100%">Estimated emissions of chlorofluorocarbons, hydrochlorofluorocarbons, and hydrofluorocarbons based on an interspecies correlation method in the Pearl River Delta region, China</style></title><secondary-title><style face="normal" font="default" size="100%">Sci Total EnvironSci Total Environ</style></secondary-title></titles><keywords><keyword><style  face="normal" font="default" size="100%">Air Pollutants/*analysis</style></keyword><keyword><style  face="normal" font="default" size="100%">Air Pollution/*statistics &amp; numerical data</style></keyword><keyword><style  face="normal" font="default" size="100%">China</style></keyword><keyword><style  face="normal" font="default" size="100%">Chlorofluorocarbons/analysis</style></keyword><keyword><style  face="normal" font="default" size="100%">Emission estimation</style></keyword><keyword><style  face="normal" font="default" size="100%">Environmental Monitoring/*methods</style></keyword><keyword><style  face="normal" font="default" size="100%">Global Warming</style></keyword><keyword><style  face="normal" font="default" size="100%">Hydrocarbons, Fluorinated/*analysis</style></keyword><keyword><style  face="normal" font="default" size="100%">Interspecies correlation</style></keyword><keyword><style  face="normal" font="default" size="100%">Ozone depletion</style></keyword><keyword><style  face="normal" font="default" size="100%">Rivers</style></keyword></keywords><dates><year><style  face="normal" font="default" size="100%">2014</style></year><pub-dates><date><style  face="normal" font="default" size="100%">Feb 01</style></date></pub-dates></dates><volume><style face="normal" font="default" size="100%">470-471</style></volume><pages><style face="normal" font="default" size="100%">829-34</style></pages><isbn><style face="normal" font="default" size="100%">1879-1026 (Electronic)0048-9697 (Linking)</style></isbn><language><style face="normal" font="default" size="100%">eng</style></language><abstract><style face="normal" font="default" size="100%">Although many studies have been conducted in recent years on the emissions of chlorofluorocarbons (CFCs), hydrochlorofluorocarbons (HCFCs), and hydrofluorocarbons (HFCs) at the large regional (such as East Asia) and national scales, relatively few studies have been conducted for cities or metropolitan areas. In this study, 192 air samples were collected in the Pearl River Delta (PRD) region of China in November 2010. The atmospheric mixing ratios of six halocarbons were analyzed, including trichlorofluoromethane (CFC-11, CCl3F), dichlorodifluoromethane (CFC-12, CCl2F2), monochlorodifluoromethane (HCFC-22, CHClF2), 1,1-dichloro-1-fluoroethane (HCFC-141b, CH3CCl2F), 1-dichloro-1,1-fluoroethane (HCFC-142b, CH3CClF2), and 1,1,1,2-tetrafluoroethane (HFC-134a, CH2FCF3), and their emissions were estimated based on an interspecies correlation method using HCFC-22 as the reference species. The results showed no significant change in the regional concentration and emission of CFC in the past 10years, suggesting that the continuous regional emission of CFC has had no significant effect on the CFC regional concentration in the PRD region. Concentrations and emissions of HCFCs and HFCs are significantly higher compared to previous research in the PRD region (P&lt;0.05). The largest emission was for HCFC-22, most likely due to its substitution for CFC-12 in the industrial and commercial refrigeration subsector, and the rapid development of the room air-conditioner and extruded polystyrene subsectors. The PRD's ODP-weighted emissions of the target HCFCs provided 9% (7-12%) of the national emissions for the corresponding species. The PRD's GWP-weighted emissions of the target HCFCs and HFC-134a account for 10% (7-12%) and 8% (7-9%), respectively, of the national emissions for the corresponding species, and thus are important contributions to China's total emissions.</style></abstract><accession-num><style face="normal" font="default" size="100%">24189105</style></accession-num><notes><style face="normal" font="default" size="100%">Wu, JingFang, XuekunMartin, Jonathan WZhai, ZihanSu, ShenshenHu, XiaHan, JiaruiLu, SihuaWang, ChenZhang, JianboHu, JianxinengResearch Support, Non-U.S. Gov'tNetherlands2013/11/06 06:00Sci Total Environ. 2014 Feb 1;470-471:829-34. doi: 10.1016/j.scitotenv.2013.09.071. Epub 2013 Nov 2.</style></notes><auth-address><style face="normal" font="default" size="100%">State Key Joint Laboratory of Environmental Simulation and Pollution Control, College of Environmental Sciences and Engineering, Peking University, Beijing, China.Division of Analytical and Environmental Toxicology, Department of Laboratory Medicine and Pathology, University of Alberta, Edmonton, AB, Canada.State Key Joint Laboratory of Environmental Simulation and Pollution Control, College of Environmental Sciences and Engineering, Peking University, Beijing, China. Electronic address: jianxin@pku.edu.cn.</style></auth-address></record></records></xml>