2000-2019 年华东地区泡沫塑料行业氟氯烃排放量的变化

Dayu Zhang, Jing Wu, Zehua Liu, Tong Wang, Dongmei Hu, Lin Peng
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摘要

氟氯烃(HCFCs)是温室气体和消耗臭氧层物质,现有的氟氯烃排放研究缺乏对单一消费行业中多种氟氯烃的全面研究。中国是氟氯烃的生产和消费大国。2019 年泡沫塑料行业的氟氯烃库存占全国总量的 91.3%,泡沫塑料行业也是第二大氟氯烃排放源。因此,估算泡沫塑料行业的氟氯烃排放量和库存量相当重要。本研究首先采用自下而上的方法,建立了华东地区泡沫行业从 2000 年到 2019 年的多种 HCFCs 排放清单。结果显示,2019 年的 HCFC 排放量和库存量分别为 14.9 千吨和 453.5 千吨。由于消费量大,聚氨酯泡沫塑料行业使用的 HCFC-141b 的年排放量、累计排放量和库存量最大。挤塑聚苯乙烯泡沫塑料行业使用的 HCFC-22 和 HCFC-142b 的总排放量与 HCFC-141b 相似。泡沫塑料行业的氟氯烃排放量主要分布在江苏、浙江和山东三省。氟氯烃的累计全球升温潜能值和 ODP 加权排放量分别为 2.406 亿吨二氧化碳当量和 14.3 千吨 CFC-11当量。因此,为了应对气候变化或臭氧消耗,我们应优先考虑 HCFC-22 和挤塑聚苯乙烯泡沫塑料行业的减排,或 HCFC-141b 和聚氨酯泡沫塑料行业的减排。为了共同应对这两个科学问题,有效减少上述氟氯烃和泡沫塑料行业的排放至关重要。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Changes in HCFC emissions from foam sector in eastern China from 2000-2019
Hydrochlorofluorocarbons (HCFCs) are greenhouse gases and ozone depleting substances, and existing HCFC emission studies lacked a comprehensive study of multiple HCFCs in a single consumption sector. China is a large producer and consumer of HCFCs. The HCFC bank in foam sector in 2019 accounted for 91.3% of the national total, and foam sector was also the second largest source of HCFC emissions. Therefore, the estimation of HCFC emissions and banks for the foam sector is quite important. In this study, the multiple HCFCs emission inventory for foam sector in eastern China from 2000 to 2019 was firstly established by using the bottom-up method. The results showed that the HCFC emissions and bank were 14.9 Kt and 453.5 Kt in 2019. HCFC-141b used in polyurethane (PU) foam sector had the largest annual emissions, cumulative emissions and bank due to its high consumption. The total emissions of HCFC-22 and HCFC-142b used in extruded polystyrene (XPS) foam sector were similar with those of HCFC-141b. The HCFC emissions from the foam sector were mainly distributed among the three provinces of Jiangsu, Zhejiang and Shandong. The cumulative GWP- and ODP-weighted emissions of HCFCs were 240.6 Mt CO2-eq and 14.3 Kt CFC-11-eq, respectively. So in order to response to climate change or ozone depletion, we should prioritize the emission reduction of HCFC-22 and XPS foam sector, or HCFC-141b and PU foam sector. And in order to jointly response to the two scientific questions, effective emission reductions of the above HCFCs and foam sectors are crucial.
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