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阿累尼乌斯方程模型利用温度和日粮粗蛋白估算牛舍氨气排放

Arrhenius equation for modeling feedyard ammonia emissions using temperature and diet crude protein.

出版信息

J Environ Qual. 2013 May-Jun;42(3):666-71. doi: 10.2134/jeq2012.0371.

Abstract

Temperature controls many processes of NH volatilization. For example, urea hydrolysis is an enzymatically catalyzed reaction described by the Arrhenius equation. Diet crude protein (CP) controls NH emission by affecting N excretion. Our objectives were to use the Arrhenius equation to model NH emissions from beef cattle () feedyards and test predictions against observed emissions. Per capita NH emission rate (PCER), air temperature (), and CP were measured for 2 yr at two Texas Panhandle feedyards. Data were fitted to analogs of the Arrhenius equation: PCER = () and PCER = (,CP). The models were applied at a third feedyard to predict NH emissions and compare predicted to measured emissions. Predicted mean NH emissions were within -9 and 2% of observed emissions for the () and (T,CP) models, respectively. Annual emission factors calculated from models underestimated annual NH emission by 11% [() model] or overestimated emission by 8% [(,CP) model]. When from a regional weather station and three classes of CP drove the models, the () model overpredicted annual NH emission of the low CP class by 14% and underpredicted emissions of the optimum and high CP classes by 1 and 39%, respectively. The (,CP) model underpredicted NH emissions by 15, 4, and 23% for low, optimum, and high CP classes, respectively. Ammonia emission was successfully modeled using only, but including CP improved predictions. The empirical () and (,CP) models can successfully model NH emissions in the Texas Panhandle. Researchers are encouraged to test the models in other regions where high-quality NH emissions data are available.

摘要

温度控制着 NH 挥发的许多过程。例如,尿素水解是一种酶促催化反应,可用阿累尼乌斯方程来描述。日粮粗蛋白(CP)通过影响氮排泄来控制 NH 排放。我们的目的是用阿累尼乌斯方程来模拟肉牛()饲粮场的 NH 排放,并根据观测到的排放来检验预测值。在德克萨斯潘汉德尔两个饲粮场,连续 2 年测定了每头奶牛 NH 排放速率(PCER)、空气温度()和 CP。数据符合阿累尼乌斯方程的模拟物:PCER = () 和 PCER = (,CP)。将模型应用于第三个饲粮场,以预测 NH 排放并将预测值与实测值进行比较。对于()和(T,CP)模型,预测的平均 NH 排放分别与实测排放值相差 9%以内和 2%以内。根据模型计算的年排放因子低估了年 NH 排放量 11%(()模型)或高估了排放量 8%((,CP)模型)。当使用来自一个区域气象站和 3 个 CP 类别的数据驱动模型时,()模型高估了低 CP 类别的年 NH 排放量 14%,低估了最优和高 CP 类别的排放量 1%和 39%。(,CP)模型分别低估了低、最优和高 CP 类别的 NH 排放量 15%、4%和 23%。仅用就成功地对 NH 排放进行了建模,但包括 CP 则提高了预测值。经验()和(,CP)模型可以成功地对德克萨斯潘汉德尔的 NH 排放进行建模。鼓励研究人员在其他有高质量 NH 排放数据的地区测试这些模型。

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