Inverse AERMOD and SCIPUFF Dispersion Modeling for Farm-Level PM10 Emission Rate Assessment

IF 1.4 4区 农林科学 Q3 AGRICULTURAL ENGINEERING
Binghong Cheng, Aditya Kumar, Lingjuan Wang-Li
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引用次数: 1

Abstract

HighlightsAERMOD and SCIPUFF were employed to back-calculate farm-level PM10 emission rates based on inverse modeling.Both AERMOD and SCIPUFF did not capture the diurnal and seasonal variations of farm-level PM10 emission rates.AERMOD modeling results were affected by wind speed, with higher wind speed leading to higher emission rates.Higher numbers of receptors and PM10 measurements with greater time resolution may be recommended in the future.Abstract. Air pollutant emissions from animal feeding operations (AFOs) have become a serious concern for public health and ambient air quality. Particulate matter with aerodynamic equivalent diameter less than or equal to 10 µm (PM10) is one of the major air pollutants emitted from AFOs. To assess the impacts of PM10 emissions from AFOs, knowledge about farm-level PM10 emission rates is needed but is challenging to obtain through field measurements. The inverse dispersion modeling approach provides an alternative way to estimate farm-level PM10 emission rates. In this study, two dispersion models, AERMOD and SCIPUFF, were employed to back-calculate farm-level PM10 emission rates based on hourly PM10 concentration measurements at four downwind locations in the vicinity of a commercial egg production farm in the southeast U.S. Onsite meteorological data were simultaneously recorded using a 10 m weather tower to facilitate the dispersion modeling. The modeling results were compared with PM10 emission measurements from two layer houses on the farm. Single-area source, double-area source, and double-volume source were used in AERMOD, while only single-point source was used in SCIPUFF. The inverse modeling results indicated that both SCIPUFF and AERMOD did not capture the diurnal and seasonal variations of the farm-level PM10 emission rates. In addition, the AERMOD modeling results were affected by wind speed, and higher emission rates may be predicted at higher wind speeds. The single-point source for SCIPUFF, the plume rise simplification for AERMOD, and insufficient concentration measurement resolution in response to temporal changes in wind direction may have added uncertainties to the modeling results. The results of this study suggest that more receptors covering more representative downwind locations should be considered in future modeling for farm-level emissions assessment. Moreover, ambient data collection with greater time resolution (e.g., less than one hour) is recommended to capture diurnal and seasonal patterns more rigorously. Only in this way can researchers achieve a better understanding of the effectiveness of inverse dispersion modeling for estimation of pollutant emission rates. Keywords: AERMOD, Animal feeding operations, Egg production, Farm-level emission rate, Inverse dispersion modeling, PM10, SCIPUFF.
基于AERMOD和SCIPUFF扩散模型的农田PM10排放率评估
HighlightsAERMOD和SCIPUFF基于反演模型反演农田PM10排放率。AERMOD和SCIPUFF都没有捕捉到农场水平PM10排放率的日变化和季节变化。AERMOD模拟结果受风速影响,风速越大,排放率越高。未来可能会推荐更多的受体数量和更大时间分辨率的PM10测量。动物饲养作业(afo)排放的空气污染物已成为公众健康和环境空气质量的严重问题。空气动力学等效直径小于或等于10µm的颗粒物(PM10)是afo排放的主要空气污染物之一。为了评估afo排放的PM10的影响,需要了解农场水平的PM10排放率,但通过实地测量很难获得。反向扩散建模方法提供了一种估算农场水平PM10排放率的替代方法。在本研究中,采用AERMOD和SCIPUFF两种扩散模型,基于美国东南部一个商业鸡蛋生产农场附近四个顺风位置每小时PM10浓度的测量数据,反计算农场水平的PM10排放率。将模拟结果与农场两层房屋的PM10排放测量结果进行了比较。AERMOD中使用了单区域源、双区域源和双音量源,而SCIPUFF中只使用了单点源。反比模型结果表明,SCIPUFF和AERMOD均不能反映农田水平PM10排放率的日变化和季节变化。此外,AERMOD模拟结果受风速影响,风速越大,预测的排放率越高。SCIPUFF的单点源、AERMOD的羽流上升简化以及响应风向时间变化的浓度测量分辨率不足可能会增加模拟结果的不确定性。这项研究的结果表明,在未来的农场排放评估模型中,应该考虑更多的受体覆盖更多有代表性的下风位置。此外,建议以更高的时间分辨率(例如少于一小时)收集环境数据,以更严格地捕捉日和季节模式。只有这样,研究人员才能更好地理解逆弥散模型在估计污染物排放率方面的有效性。关键词:AERMOD,动物饲养操作,产蛋量,农场级排放率,反向扩散模型,PM10, SCIPUFF
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来源期刊
Transactions of the ASABE
Transactions of the ASABE AGRICULTURAL ENGINEERING-
CiteScore
2.30
自引率
0.00%
发文量
0
审稿时长
6 months
期刊介绍: This peer-reviewed journal publishes research that advances the engineering of agricultural, food, and biological systems. Submissions must include original data, analysis or design, or synthesis of existing information; research information for the improvement of education, design, construction, or manufacturing practice; or significant and convincing evidence that confirms and strengthens the findings of others or that revises ideas or challenges accepted theory.
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