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Combined use of WEPS and Models-3/CMAQ for simulating wind erosion source emission and its environmental impact

机译:WEPS与Models-3 / CMAQ的组合使用,用于模拟风蚀源排放及其对环境的影响

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摘要

The wind erosion source is the greatest contributor of PM_(10) in Tianjin, China. It is difficult to establish a PM_(10) emission inventory for the wind erosion source because of the complicated conditions affecting PM_(10) emissions from wind erosion. In this study, a novel method is developed to establish a PM_(10) emission inventory for the wind erosion source by using the Wind Erosion Prediction System (WEPS) model with 1 × 1 km spatial resolution. In 2011, the average annual emission of PM_(10) in Tianjin was 0.373 tons km~(-2) (1.113 tons km~(-2) in the heating period, 0.237 tons km~(-2) in the sand period, and 0.013 tons km~(-2) in the non-heating period), and the total PM_(10) emission was 904,871.6 tons (221,080.7 tons in the heating period, 52,977.8 tons in the sand period, and 1953.2 tons in the non-heating period). After establishing the PM_(10) emission inventory for the wind erosion source in this manner, the data were input into Model-3/SMOKE. The contribution of the PM_(10) concentration from the wind erosion source was estimated using the Community Multi-scale Air Quality (Model-3/CMAQ) model and was compared with the monitoring value and the source apportionment results using the chemical mass balance (CMB) method. For this comparison, over the entire year, the R~2 was 0.711. More specifically, R2 was 0.664,0.733, and 0.679 in the heating, non-heating, and sand periods, respectively. Thus, we have obtained a reliable method for estimating the source of PM_(10) from wind erosion.
机译:风蚀源是中国天津PM_(10)的最大贡献者。由于影响风蚀PM_(10)排放的复杂条件,很难为风蚀源建立PM_(10)排放清单。在这项研究中,通过使用空间分辨率为1×1 km的风蚀预测系统(WEPS)模型,开发了一种新的方法来建立风蚀源的PM_(10)排放清单。 2011年,天津PM_(10)的年平均排放量为0.373吨km〜(-2)(采暖期为1.113吨km〜(-2),沙期为0.237吨km〜(-2),在非供暖期间为0.013吨km〜(-2)),PM_(10)的总排放为904,871.6吨(供暖期间为221,080.7吨,沙期为52,977.8吨,非供热期间为1953.2吨)。加热期)。在以此方式建立风蚀源的PM_(10)排放清单后,将数据输入到Model-3 / SMOKE中。使用社区多尺度空气质量(Model-3 / CMAQ)模型估算了来自风蚀源的PM_(10)浓度的贡献,并使用化学质量平衡将其与监测值和源分配结果进行了比较( CMB)方法。为了进行比较,在全年中,R〜2为0.711。更具体地,在加热,非加热和沙土时期,R 2分别为0.664、0.733和0.679。因此,我们获得了一种可靠的方法,用于从风蚀中估算PM_(10)的来源。

著录项

  • 来源
    《Science of the total environment》 |2014年第1期|762-769|共8页
  • 作者单位

    Chinese Research Academy of Environmental Sciences, Beijing 100012, China,College of Urban and Environmental Science, Tianjin Normal University, Tianjin 300387, China;

    College of Information Technical Science, Nanka1 University, Tianjin 300071, China,China State Environmental Protection Key Laboratory of Urban Ambient Air Particulate Matter Pollution, Tianjin 300071, China;

    Chinese Research Academy of Environmental Sciences, Beijing 100012, China;

    Chinese Research Academy of Environmental Sciences, Beijing 100012, China;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    WEPS; Model3/CMAQ; Wind erosion source; Emission inventory; Tianjin;

    机译:WEPS;Model3 / CMAQ;风蚀源;排放清单;天津;

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