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A Comparison of Different Approaches to Estimate Small-Scale Spatial Variation in Outdoor NO2 Concentrations

机译:估算室外NO2浓度小尺度空间变化的不同方法的比较

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Background In epidemiological studies, small-scale spatial variation in air quality is estimated using land-use regression (LUR) and dispersion models. An important issue of exposure modeling is the predictive performance of the model at unmeasured locations. Objective In this study, we aimed to evaluate the performance of two LUR models (large area and city specific) and a dispersion model in estimating small-scale variations in nitrogen dioxide (NO2) concentrations. Methods Two LUR models were developed based on independent NO2 monitoring campaigns performed in Amsterdam and in a larger area including Amsterdam, the Netherlands, in 2006 and 2007, respectively. The measurement data of the other campaign were used to evaluate each model. Predictions from both LUR models and the calculation of air pollution from road traffic (CAR) dispersion model were compared against NO2 measurements obtained from Amsterdam. Results and conclusion The large-area and the city-specific LUR models provided good predictions of NO2 concentrations [percentage of explained variation ( R 2) = 87% and 72%, respectively]. The models explained less variability of the concentrations in the other sampling campaign, probably related to differences in site selection, and illustrated the need to select sampling sites representative of the locations to which the model will be applied. More complete traffic information contributed more to a better model fit than did detailed land-use data. Dispersion-model estimates for NO2 concentrations were within the range of both LUR estimates.
机译:背景技术在流行病学研究中,使用土地利用回归(LUR)和离散模型估算空气质量的小范围空间变化。暴露建模的一个重要问题是模型在未测量位置的预测性能。目的在本研究中,我们旨在评估两种LUR模型(大面积和城市特定)和分散模型在估算二氧化氮(NO 2 )浓度的小范围变化方面的性能。方法分别基于独立的NO 2 监测活动(分别在2006年和2007年在阿姆斯特丹和荷兰阿姆斯特丹等地开展的活动)开发了两种LUR模型。其他活动的测量数据用于评估每个模型。将这两种LUR模型的预测结果以及道路交通(CAR)扩散模型中的空气污染计算结果与从阿姆斯特丹获得的NO 2 测量结果进行了比较。结果与结论大面积区域模型和城市特定LUR模型可以很好地预测NO 2 的浓度[解释变异的百分比(R 2 )= 87%和72% , 分别]。该模型说明了其他采样活动中浓度的可变性较小,可能与选址的差异有关,并说明了需要选择代表要应用模型的位置的采样点。与详细的土地利用数据相比,更完整的交通信息为更好的模型拟合做出了更大的贡献。 NO 2 浓度的色散模型估计值在两个LUR估计值的范围内。

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