Towards the development of a standardized testing protocol for overhead island kitchen exhaust devices: Procedures, measurements and paths forward

Towards the development of a standardized testing protocol for overhead island kitchen exhaust devices: Procedures, measurements and paths forward
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DOI:
10.1016/j.buildenv.2018.06.023
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发表时间:
2018-09
影响因子:
7.4
通讯作者:
Jordan D. Clark;G. Rojas;I. Walker
Jordan D. Clark;G. Rojas;I. Walker
中科院分区:
工程技术1区
文献类型:
--
作者:
Jordan D. Clark;G. Rojas;I. Walker

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烹饪是住宅室内空气污染物的重要来源之一。烹饪引起的二氧化氮浓度升高已被广泛报道(Garrett et al. 1998; Garrett et al. 1999; Mullen et al. 2016; Ryan et al. 1988; Schwab et al. 1994; J. Spengler et al. 1994; JD Spengler et al. 1983; Wilson et al. 1995)。许多研究人员认为烹饪微粒浓度升高,和有些人由于极高的短期的微粒浓度(> 300μg / m3)和超细颗粒(> 105μg / m3)烹饪事件(阿卜杜拉希•et al . 2013; Abt et al . 2000; Afshari et al . 2005; Buonanno et al . 2009;他et al . 2004;卡尼et al . 2011;兰斯·a·华莱士et al . 2004;看到和Balasubramanian 2008; Stieb et al . 2008;华莱士和奥特2011;Wheeler et al . 2011; Zhang et al . 2010年)。烹饪也是其他气相污染物的来源,包括一氧化碳、甲醛、丙烯醛和其他挥发性有机化合物(Garrett et al. 1998; Garrett et al. 1999; Logue et al. 2013; Mullen et al. 2016; Ryan et al. 1988; Schwab et al. 1994; J. Spengler et al. 1994; JD Spengler et al. 1983; V. Seaman et al. 2007; Wilson等1995)。最后,烹饪是水蒸气的重要来源,而烹饪产生的水蒸气最终会导致与水分有关的问题(Parrott和Emmel 2003)。减少这些空气污染物来源的主要机制是通过厨房抽油烟机。许多研究都研究了这些通风橱降低烹饪过程中产生的污染物浓度的能力,并且普遍认为它们确实有效(Chiang等人2000;Fugler 1989; JM Huang等人2004;Y. Huang等人2015;Mullen等人2016;Revzan 1986; D. Rim等人2012;BC Singer等人2012c; Singer等人2011;Svendsen等人2002;Zhang等人2010)。然而,即使在个别研究中,测量的性能也存在很大差异(Delp和Singer 2012; Lunden等人2014;DH Rim等人2011;Singer等人2011)。性能的变化至少部分归因于安装、燃烧器位置、风扇速度、风扇设计、罩设计和补充空气位置的差异(Fritz 1989; Singer et al. 2010; Singer et al. 2011)和量化颗粒去除时的颗粒大小(D. Rim et al. 2012)。即使在给定的研究中,测量的绩效变化也几乎达到100% (Li et al. 1997; Li and Delsante 1996; Lim and Lee 2008; Madsen et al. 1994; D. Rim et al. 2012; Singer et al. 2011)。
Cooking is one of the most important sources of airborne pollutants in the indoor environments of residential buildings. Elevated concentrations of NO2 due to cooking have been reported widely (Garret et al. 1998; Garrett et al. 1999; Mullen et al. 2016; Ryan et al. 1988; Schwab et al. 1994; J. Spengler et al. 1994; JD Spengler et al. 1983; Wilson et al. 1995). Many researchers have attributed elevated particulate concentrations to cooking, and some have attributed extremely high short-term concentrations of fine particles (> 300 μg/m3) and ultrafine particles (> 105 μg/m3) to cooking events (Abdullahi et al. 2013; Abt et al. 2000; Afshari et al. 2005; Buonanno et al. 2009; He et al. 2004; Kearney et al. 2011; Lance A. Wallace et al. 2004; See and Balasubramanian 2008; Stieb et al. 2008; Wallace and Ott 2011; Wheeler et al. 2011; Zhang et al. 2010). Cooking is also a source of other gas-phase pollutants including carbon monoxide, formaldehyde, acrolein, and other volatile organic compounds (Garret et al. 1998; Garrett et al. 1999; Logue et al. 2013; Mullen et al. 2016; Ryan et al. 1988; Schwab et al. 1994; J. Spengler et al. 1994; JD Spengler et al. 1983; V. Seaman et al. 2007; Wilson et al. 1995). Lastly, cooking can be a significant source of water vapor, and the water vapor produced from cooking can eventually lead to moisture-related problems (Parrott and Emmel 2003)The main mechanism by which the source of these airborne pollutants is reduced is via kitchen range hoods. Many studies have looked at the ability of these hoods to reduce concentrations of pollutants generated during cooking, and it is generally believed that they are indeed effective (Chiang et al. 2000; Fugler 1989; JM Huang et al. 2004; Y. Huang et al. 2015; Mullen et al. 2016; Revzan 1986; D. Rim et al. 2012; BC Singer et al. 2012c; Singer et al. 2011; Svendsen et al. 2002; Zhang et al. 2010). However, even within individual studies the measured performance has varied widely (Delp and Singer 2012; Lunden et al. 2014; DH Rim et al. 2011; Singer et al. 2011). The variation in performance is at least partially attributable to differences in installation, burner position, fan speed, fan design, hood design, and location of makeup air (Fritz 1989; Singer et al. 2010; Singer et al. 2011) and particle size when quantifying particulate removal (D. Rim et al. 2012). Measured performance has varied up to almost 100% even within a given study (Li et al. 1997; Li and Delsante 1996; Lim and Lee 2008; Madsen et al. 1994; D. Rim et al. 2012; Singer et al. 2011).