科研成果

2016
Wang Z, Fang X, Li L, Bie P, Li Z, Hu J, Zhang B, Zhang J. Historical and projected emissions of HCFC-22 and HFC-410A from China's room air conditioning sector. Atmospheric EnvironmentAtmospheric Environment. 2016;132:30-35.
Su S, Fang X, Zhao J, Hu J. Spatiotemporal characteristics of consumption based CO 2 emissions from China’s power sector. Resources Conservation & RecyclingResources Conservation & Recycling. 2016.Abstract
As China’s largest CO 2 emission source, power sector has a large scale of power exchange, which results in the issue of interprovincial CO 2 emissions transfer embodied in power transmission. Based on interprovincial detailed power exchange data, a bottom-up method which takes into account the fuel mix of exported electricity is developed to calculate provincial CO 2 emissions embodied in power transmission. Provincial CO 2 emissions from power sector associated in consumption perspective in 2007, 2010 and 2012 are analyzed and compared with those in production based perspective. The calculation shows that total CO 2 emissions embodied in interprovincial power exchange is 532 Tg in 2012, accounting for 14% of total emissions from power sector. The embodied emissions have risen by 94% between 2007 and 2012. The general transfer pathway of embodied CO 2 emissions is from eastern China to western China with long-range power transmission. The disparities between consumption and production based CO 2 emissions are significant in some provinces. The production based CO 2 emissions from power sector of Inner Mongolia are 195 Tg higher than those of the consumption based, while the consumption based emissions of Beijing are 484% larger than those of the production based. This study also reveals an increasing trend of CO 2 emissions from both production and consumption principles for most provinces over the period 2007–2012.
韩佳蕊, 姜含宇, 张兆阳, 胡建信. 中国氢氟碳化物削减政策框架研究——基于现有控制臭氧消耗物质体系及发达国家经验. 环境保护环境保护. 2016;44:69-71.Abstract
摘 要: 面对国际社会积极控制非CO_2温室气体的趋势和艰巨的温室气体减排任务,中国作为氢氟碳化物(HFCs)的产销大国,控制这一高增长、难回收的强效温室气体已势在必行。鉴于HFCs与臭氧消耗物质(Ozone Depleting Substance,ODS)的削减工作具有较强传承性,中国在构建管控HFCs系统时,应在沿用现有ODS管理体制与法规体系的基础上,借鉴国外的先进经验:将现有源头管理体系向下游延伸,构建全生命周期的封闭式管理机制;充分重视高精度温室气体排放量与大气浓度数据的反馈与指导作用,并将中国成熟的行业削减机制与逐个化学品(Chemical-bychemical)削减相结合,从而逐步以更具成本有效性的方式控制HFCs排放。
2015
Li L, Liu J, Hu J. Global inventory, long-range transport and environmental distribution of dicofol. Environ Sci TechnolEnviron Sci Technol. 2015;49:212-22.Abstract
The uncertainties on whether dicofol can be identified as a persistent organic pollutant (POP) in terms of its long-range transport (LRT) potential and global distribution, are always a controversial topic during international regulation deliberations. The lack of monitoring data in remote background regions necessitates a model-based evaluation approach for assessing the global distribution of dicofol. However, few model simulations are available at present, as there is no inventory available for global historical usage of dicofol that has sufficiently high spatial and temporal resolution. To describe the current status of global emission, we first developed an inventory of global dicofol usage for the period of 2000-2012 at 1 degrees x 1 degrees latitude/longitude resolution. We then assessed the LRT potential of dicofol by calculating its Arctic Contamination Potential using the Globo-POP model. In addition, we simulated the global mass distribution and the fate of dicofol in the environment using the BETR-Global model at 15 degrees x 15 degrees latitude/longitude resolution. Our estimated inventory established that over the period of 13 years, a total of 28.2 kilo tonnes (kt) of dicofol was applied and released into the environment. East and Southeast Asia, the Mediterranean Coast, and Northern and Central America were identified as hotspots of usage and release. Dicofol exhibited a higher Arctic Contamination Potential than several confirmed Arctic contaminants, and a larger current volume of consumption than most existing POPs. The results of our BETR-Global simulation suggest that (i) dicofol can indeed be transported northward, most likely driven by both atmospheric and oceanic advections from source regions at midlatitudes, and (ii) dicofol will be enriched in remote background regions. Continuous use of dicofol in source regions will result in exposure both locally and in remote regions, and the examination of the potential for adverse effects is therefore of paramount importance. Proactive restrictions at the international level may be warranted.
Fang X, Stohl A, Yokouchi Y, Kim J, S Li, Saito T, Park S, Hu J. Multiannual top-down estimate of HFC-23 emissions in East Asia. Environ Sci TechnolEnviron Sci Technol. 2015;49:4345-53.Abstract
Trifluoromethane (CHF3, HFC-23), with a 100-year global warming potential (GWP) of 12400, is regulated under the Kyoto Protocol. HFC-23 emissions in East Asia, especially in China, are currently thought to represent the majority of global HFC-23 emissions. This study provides both a bottom-up emission inventory and the multiannual top-down estimate of HFC-23 emissions in East Asia during 2007-2012. The new bottom-up inventory yields improved simulated HFC-23 mixing ratios compared to previous bottom-up inventories. The top-down estimate uses inverse modeling to further improve the model-measurement agreement. Results show that China contributed 94-98% of all HFC-23 emissions in East Asia. Annual a posteriori emissions from China were around 6.3 Gg/yr during the period 2007-2010 after which they increased to 7.1 +/- 0.7 Gg/yr in 2011 and 8.8 +/- 0.8 Gg/yr in 2012. For the first time, this study also provides a top-down estimate of HFC-23/HCFC-22 (chlorodifluoromethane, CHClF2) coproduction ratios in non-CDM (Clean Development Mechanism) HCFC-22 production plants as well as in all HCFC-22 production plants in China.
胡建信;李力;黄俊;刘建国. PFOA/PFO环境风险管控需加快进程. 2015:002.
Li L, Zhai Z, Liu J, Hu J. Estimating industrial and domestic environmental releases of perfluorooctanoic acid and its salts in China from 2004 to 2012. ChemosphereChemosphere. 2015;129:100-109.
Li YF, Ma WL, Yang M. Prediction of gas/particle partitioning of polybrominated diphenyl ethers (PBDEs) in global air: A theoretical study. Atmospheric Chemistry and PhysicsAtmospheric Chemistry and Physics. 2015;15:1669-1681.
别鹏举, 苏燊燊, 李志方, 贾胜兰, 张兆阳, 方雪坤, 胡建信. 中国汽车空调行业淘汰HFC-134a技术选择与政策建议. 气候变化研究进展气候变化研究进展. 2015;11:363-370.Abstract
摘 要: HFC-134a在中国汽车空调行业广泛使用,并已成为中国目前排放量最大的有意生产和使用的HFCs之一。欧盟和美国已经颁布相关法律法规控制包括HFC-134a在内的含氟温室气体的消费和排放。如果选择低全球变暖潜势(GWP)替代技术,中国汽车空调行业将具有巨大的温室气体减排潜力;伴随着汽车空调系统需求呈现的多样化,现有替代技术如HFO-124yf、HFC-152a、CO2等各有优势和不足,需要综合考虑它们的经济成本、市场化可行性以及安全风险和环保标准;制定HFC-134a淘汰政策、积极推进替代技术的研究和应用,以积极响应国际社会加快淘汰HFC-134a的行动,也是落实2014年《中美气候变化联合声明》中提出的关于削减全球氢氟碳化物的行动。
苏燊燊, 赵锦洋, 胡建信. 中国电力行业1990-2050年温室气体排放研究. 气候变化研究进展气候变化研究进展. 2015;11:353-362.Abstract
摘 要: 采用《国家温室气体清单指南》推荐方法,估算了1990—2014年中国各省份电力行业的温室气体排放水平。研究时期内,中国电力行业排放增长6.2倍,达到38.0(95%信度区间为31.3~46.0)亿tCO2当量(CO2-eq),而各省排放水平及其变化趋势呈现出显著的差异,排放重心向西部省份转移,内蒙古成为全国电力行业排放最大的省份。同时基于未来电源结构的发展方案,预测了2015—2050年不同电力需求情景下电力行业温室气体排放的变化趋势和达到排放峰值情况。电力需求高增速情景下2034年达到排放峰值59.5(49.3~71.8)亿t CO2-eq,而低增速情景可以提前至2031年达到排放峰值,且峰值水平下降7.7(6.3~9.3)亿tCO2-eq。
韩佳蕊, 李力, 方雪坤, 吴婧, 苏燊, 温新元, 吴宇声, 胡建信. 基于物种间浓度相关法估算2012年中国HCFC-142b排放量. 北京大学学报自然科学版北京大学学报自然科学版. 2015;51:123-130.Abstract
摘 要: 利用北京大学定点较高时间频率浓度监测数据,甄选HCFC-22为估算HCFC-142b排放量适宜的参考物质,分析认为以往基于背景地区数据的研究中普遍采用的参考物质CO不适用于利用城市地区大气样品进行物种间浓度相关法研究。根据全国四城市(北京、杭州、兰州和广州)四季的HCFC-142b及其参考物质浓度监测数据,通过物种间浓度相关法计算2012年中国HCFC-142b排放量为16.24(13.90~18.58)kt,相当于1.06 ODP kt和37 Tg CO2-eq,占2012年中国HCFCs排放总量的9.78%(ODP),占全球HCFC-142b排放总量的30.57%。中国HCFC-142b的减排淘汰工作将在未来中国和全球成功履约中占据重要地位。
胡建信. 《维也纳公约》缔结30年来中国对保护臭氧层的贡献与成果. 世界环境世界环境. 2015:30-31.Abstract
摘 要: 1974年,加利福尼亚大学欧文分校的舍伍德·罗兰和马里奥·莫利纳在《自然》杂志上发表文章,阐述了人类大量生产和使用的全氟氯烃(CFCs)因其大气环境中寿命长,可以经过几年到十几年的迁移到达同温层(平流层),并在短波紫外线UV—C的照射下发生光解,释放出游离氯自由基;后者发生链式反应促使臭氧(O3)转化为氧气(O2),从而造成平流层臭氧耗损。
Zhai Z, Wu J, Hu X, Li L, Guo J, Zhang B, Hu J, Zhang J. A 17-fold increase of trifluoroacetic acid in landscape waters of Beijing, China during the last decade. ChemosphereChemosphere. 2015;129:110-117.
Su S, Fang X, Li L, Wu J, Zhang J, Xu W, Hu J. HFC-134a emissions from mobile air conditioning in China from 1995 to 2030. Atmospheric EnvironmentAtmospheric Environment. 2015;102:122-129.
Wang Z, Yan H, Fang X, Gao L, Zhai Z, Hu J, Zhang B, Zhang J. Past, present, and future emissions of HCFC-141b in China. Atmospheric EnvironmentAtmospheric Environment. 2015;109:228-233.
2014
Li L, Hu J, Ho YS. Global Performance and Trend of QSAR/QSPR Research: A Bibliometric Analysis. Mol InformMol Inform. 2014;33:655-68.Abstract
A bibliometric analysis based on the Science Citation Index Expanded was conducted to provide insights into the publication performance and research trend of quantitative structure-activity relationship (QSAR) and quantitative structure-property relationship (QSPR) from 1993 to 2012. The results show that the number of articles per year quadrupled from 1993 to 2006 and plateaued since 2007. Journal of Chemical Information and Modeling was the most prolific journal. The internal methodological innovations in acquiring molecular descriptors and modeling stimulated the articles' increase in the research fields of drug design and synthesis, and chemoinformatics; while the external regulatory demands on model validation and reliability fueled the increase in environmental sciences. "Prediction endpoints", "statistical algorithms", and "molecular descriptors" were identified as three research hotspots. The articles from developed countries were larger in number and more influential in citation, whereas those from developing countries were higher in output growth rates.
Wu J, Fang X, Martin JW, Zhai Z, Su S, Hu X, Han J, Lu S, Wang C, Zhang J, et al. Estimated emissions of chlorofluorocarbons, hydrochlorofluorocarbons, and hydrofluorocarbons based on an interspecies correlation method in the Pearl River Delta region, China. Sci Total EnvironSci Total Environ. 2014;470-471:829-34.Abstract
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<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.
Wu J, Martin JW, Zhai Z, Lu K, Li L, Fang X, Jin H, Hu J, Zhang J. Airborne trifluoroacetic acid and its fraction from the degradation of HFC-134a in Beijing, China. Environ Sci TechnolEnviron Sci Technol. 2014;48:3675-81.Abstract
Trifluoroacetic acid (TFA) has been attracting increasing attention worldwide because of its increased environmental concentrations and high aquatic toxicity. Atmospheric deposition is the major source of aquatic TFA, but only a few studies have reported either air concentrations or deposition fluxes for TFA. This is the first study to report the atmospheric concentrations of TFA in China, where an annular denuder and filter pack collection system were deployed at a highly urbanized site in Beijing. In total, 144 air samples were collected over the course of 1 year (from May 2012 to April 2013) and analyzed directly using high-performance liquid chromatography-tandem mass spectrometry (HPLC-MS/MS) or following derivatization by gas chromatography-mass spectrometry (GC-MS). The annual mean atmospheric concentration of TFA was 1580 +/- 558 pg/m(3), higher than the previously reported annual mean levels in Germany and Canada. For the first time, it was demonstrated that maximum concentrations of TFA were frequently observed in the afternoon, following a diurnal cycle and suggesting that a major source of airborne TFA is likely degradation of volatile precursors. Using a deposition model, the annual TFA deposition flux was estimated to be 619 +/- 264 mug m(-2) year(-1). Nevertheless, a box model estimated that the TFA deposition flux from the degradation of HFC-134a contributed only 14% (6-33%) to the total TFA deposition flux in Beijing. Source analysis is quite important for future TFA risk predictions; therefore, future research should focus on identifying additional sources.
Fang X, Miller BR, Su S, Wu J, Zhang J, Hu J. Historical emissions of HFC-23 (CHF3) in China and projections upon policy options by 2050. Environ Sci TechnolEnviron Sci Technol. 2014;48:4056-62.Abstract
Trifluoromethane (CHF3, HFC-23) is one of the hydrofluorocarbons (HFCs) regulated under the Kyoto Protocol with a global warming potential (GWP) of 14 800 (100-year). China's past, present, and future HFC-23 emissions are of considerable interest to researchers and policymakers involved in climate change. In this study, we compiled a comprehensive historical inventory (1980-2012) and a projection (2013-2050) of HFC-23 production, abatements, and emissions in China. Results show that HFC-23 production in China increased from 0.08 +/- 0.05 Gg/yr in 1980 to 15.4 +/- 2.1 Gg/yr (228 +/- 31 Tg/yr CO2-eq) in 2012, while actual HFC-23 emissions reached a peak of 10.5 +/- 1.8 Gg/yr (155 +/- 27 Tg/y CO2-eq) in 2006, and decreased to a minimum of 7.3 +/- 1.3 Gg/yr (108 +/- 19 Tg/yr CO2-eq) in 2008 and 2009. Under the examined business-as-usual (BAU) scenario, the cumulative emissions of HFC-23 in China over the period 2013-2050 are projected to be 609 Gg (9015 Tg CO2-eq which approximates China's 2012 CO2 emissions). Currently, China's annual HFC-23 emissions are much higher than those from the developed countries, while it is estimated that by year 2027, China's historic contribution to the global atmospheric burden of HFC-23 will have surpassed that of the developed nations under the BAU scenario.
Han J, Li L, Su S, Wu J, Fang X, Jia S, Zhang J, Hu J. Estimated HCFC-142b emissions in China: 2000–2050. Chinese Science BulletinChinese Science Bulletin. 2014;59:3046-3053.

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