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Modeling Toxic Compounds From Nitric Oxide Emission Measurements

机译:从一氧化氮排放量测量模拟有毒化合物

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Determining the amount and rate of degradation of toxic pollutants in soil and groundwater is difficult and often requires invasive techniques, such as deploying extensive monitoring well networks. Even with these networks, degradation rates across entire systems cannot readily be extrapolated from the samples. When organic compounds are degraded by microbes, especially nitrifying bacteria, oxides or nitrogen (NO_x) are released to the atmosphere. Thus, the flux of nitric oxide (NO) from the soil to the lower troposphere can be used to predict the rate at which organic compounds are degraded. By characterizing and applying biogenic and anthropogenic processes in soils the rates of degradation of organic compounds. Toluene was selected as a representative of toxic aromatic compounds, since it is inherently toxic, it is a substituted benzene compound and is listed as a hazardous air pollutant under Section 12 of the Clean Air Act Amendments of 1990. Measured toluene concentrations in soil, microbial population growth and NO fluxes in chamber studies were used to develop and parameterize a numerical model based on carbon and nitrogen cycling. These measurements, in turn, were used as indicators of biore-mediation of air toxic (i.e. toluene) concentrations. The model found that chemical concentration, soil microbial abundance, and NO production can be directly related to the experimental results (significant at P < 0.01) for all toluene concentrations tested. This indicates that the model may prove useful in monitoring and predicting the fate of toxic aromatic contaminants in a complex soil system. It may also be useful in predicting the release of ozone precursors, such as changes in reservoirs of hydrocarbons and oxides of nitrogen. As such, the model may be a tool for decision makers in ozone non-attainment areas.
机译:确定土壤和地下水中有毒污染物的降解量和降解速率很困难,并且通常需要采用侵入性技术,例如部署广泛的监测井网络。即使有了这些网络,也无法从样本中轻易推断出整个系统的退化率。当有机化合物被微生物(尤其是硝化细菌)降解时,氧化物或氮(NO_x)释放到大气中。因此,一氧化氮(NO)从土壤到对流层低层的流量可用于预测有机化合物的降解速度。通过在土壤中表征和应用生物和人为过程,可以降解有机化合物。选择甲苯作为有毒芳香族化合物的代表,因为它具有内在毒性,因此它是取代的苯化合物,并且在1990年的《清洁空气法》修正案第12节中被列为有害空气污染物。土壤,微生物中甲苯的测定浓度室内研究中的种群增长和NO通量被用于开发和参数化基于碳和氮循环的数值模型。这些测量结果又被用作空气毒性(即甲苯)浓度的生物修复指标。该模型发现,对于所有测试的甲苯浓度,化学浓度,土壤微生物丰度和NO的产生都可以与实验结果直接相关(在P <0.01时显着)。这表明该模型可能在监测和预测复杂土壤系统中有毒芳香族污染物的归因方面很有用。在预测臭氧前体的释放(例如碳氢化合物和氮氧化物的储层中的变化)方面也可能有用。因此,该模型可能是臭氧不达标地区决策者的工具。

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