Criteria, Greenhouse Gas, and Hazardous Air Pollutant Emissions Factors from Residential Cordwood and Pellet Stoves Using an Integrated Duty Cycle Test Protocol.

ACS ES&T Air Pub Date : 2024-08-12 eCollection Date: 2024-09-13 DOI:10.1021/acsestair.4c00135
Nora Traviss, George Allen, Mahdi Ahmadi
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Abstract

Air pollution from residential wood heating (RWH) presents challenges at the intersection of climate and public health. With a revised National Ambient Air Quality Standard (NAAQS, at 9 μg/m3) for particulate matter (PM) in the United States (U.S.), the Environmental Protection Agency (EPA) will likely classify new non-attainment areas due primarily to emissions from RWH. Agencies will use emissions factors (EFs) to develop attainment strategies. Many will rely on EPA modeling platforms based on data from the National Emissions Inventory (NEI). The NEI uses RWH EFs based on data from mid-1990's in-situ studies and a speciation profile from a 2001 study of fireplace emissions. The NEI does not include greenhouse gas (GHG) emissions for this sector, which plays a key role when assessing climate reduction strategies for the buildings sector. Here, we tested seven wood stoves to determine EFs, representing various vintages and control technologies, using a novel test method that reflects in-use operational settings called the Integrated Duty Cycle. The study measured multiple pollutants concurrently: criteria pollutants (particulate matter [PM], CO, and NOx), nonmethane total hydrocarbons (NMTHCs), GHGs, black carbon (eBC), brown carbon (BrC), and multiple hazardous air pollutants (HAPs). We found no significant difference in PM EFs between uncertified and non-catalytic stove technologies. RWH EF results from this study exceeded 2020 NEI RWH EFs for NMTHC and multiple HAPs. Applying our study's EFs to the 2020 NEI suggests that RWH, compared to all other sources, ranks as the 2nd largest source category of formaldehyde; the 3rd largest of benzene, 1,3-butadiene, and acrolein; and the 4th largest of Pb emissions. RWH also emits more methane compared to natural gas or oil residential heating, raising questions about substitution of wood as a climate neutral heating fuel. However, compared to uncertified stoves, pellet stove EFs (except toxic metals) were significantly lower (p < 0.01). In summary, RWH appears to be an underestimated source of PM (non-catalytic technology), methane, NMTHC, toxic metals, and other HAPs, which has important implications for climate and public health policy in the U.S. and globally.

使用综合占空比测试协议计算住宅帘木柴炉和颗粒燃料炉的标准、温室气体和有害空气污染物排放系数。
住宅木材取暖(RWH)产生的空气污染给气候和公共健康带来了挑战。随着美国对颗粒物(PM)的国家环境空气质量标准(NAAQS,9 μg/m3)的修订,环境保护局(EPA)可能会划分出新的非达标区域,这些区域主要是由于 RWH 的排放造成的。各机构将使用排放因子 (EF) 来制定达标战略。许多机构将依靠基于国家排放清单 (NEI) 数据的 EPA 建模平台。NEI 使用的 RWH EFs 是基于 1990 年代中期的原位研究数据和 2001 年壁炉排放研究中的规格剖面图。NEI 不包括该行业的温室气体 (GHG) 排放量,而温室气体在评估建筑行业气候减排战略时起着关键作用。在此,我们测试了七种代表不同年份和控制技术的柴炉,以确定其 EFs,使用的是一种反映使用中操作设置的新型测试方法,称为 "综合占空比"(Integrated Duty Cycle)。这项研究同时测量了多种污染物:标准污染物(颗粒物 [PM]、一氧化碳 (CO) 和氮氧化物 (NOx))、非甲烷总烃 (NMTHC)、温室气体、黑碳 (eBC)、褐碳 (BrC) 和多种有害空气污染物 (HAP)。我们发现,未经认证的炉灶技术和非催化炉灶技术在 PM EFs 方面没有明显差异。本研究得出的 RWH EF 结果超过了 2020 年 NEI RWH EFs,即 NMTHC 和多种 HAP 的 EFs。将我们研究的 EFs 应用于 2020 NEI 表明,与所有其他来源相比,RWH 是甲醛的第二大来源类别;苯、1,3-丁二烯和丙烯醛的第三大来源类别;以及铅排放的第四大来源类别。与天然气或燃油住宅取暖相比,RWH 也会排放更多的甲烷,从而引发了将木材作为气候中和取暖燃料进行替代的问题。不过,与未经认证的炉灶相比,颗粒炉灶的 EFs(有毒金属除外)明显较低(p < 0.01)。总之,RWH 似乎是一个被低估的可吸入颗粒物(非催化技术)、甲烷、NMTHC、有毒金属和其他 HAPs 的来源,这对美国和全球的气候和公共卫生政策具有重要影响。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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