2013-18水年期间六个美国地质调查局国家水质网络站点估算农药浓度的替代模型比较

S. Alex. Covert, Aubrey R. Bunch, Charles G. Crawford, Gretchen P. Oelsner
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引用次数: 1

摘要

欲了解更多信息,请联系:俄亥俄州-肯塔基州-印第安纳州水科学中心主任。地质调查局湖滨大道5957号在2013-18年的水年里,美国地质调查局国家水质评估项目全年对国家河流和溪流水质网络进行采样,并报告了美国72个地点的221种农药。农药很难测量,它们的浓度通常代表时间上的离散快照,捕获峰值浓度是昂贵的。开发了三种类型的回归模型来估计六个国家河流和溪流水质网络站点中每个站点的两种选定农药的浓度。回归模型使用连续测量的水流和水质特性(pH值、比电导、浊度和水温的不同组合);分析了离散水质样品中的阿特拉津、唑虫胺、苯他松、溴马止、吡虫啉、辛马嗪和三氯吡虫啉;时间是季节性的另一个解释变量。建模方法包括:(1)标准回归,其中包括替代变量(pH值、比电导、浊度和水温的不同组合)和农药使用的周期函数(正弦余弦)作为预测变量;(2)包含季节分量和流量异常但不包含替代量的流量调节模型的季节波;(3)包含季节分量、流量异常和代用品的流量调整模型的季节波。采用三种模型性能指标对模型进行评价:广义决定系数(generalized coefficient of determination, R2)、赤池信息标准(Akaike’s Information Criteria)和尺度(tobit回归误差项的估计标准差)。由于观测数少,本研究的结果可以被认为是一个试点的努力,有可能有些模型是过拟合的。在所有情况下,用SEAWAVE-Q模型估计的农药浓度都优于标准代理回归模型;与标准代理回归模型相比,所有39个广义R2值增加了3 - 56%(中位数为25%),所有赤池信息标准和量表值都降低了。在SEAWAVE-Q基础模型中加入替代变量,如pH值、比电导、浊度和水温,以改善农药浓度的估计,结果只有适度的改善;广义R2值仅增加0 - 10%(中位数为3%)。在某些情况下,替代物的组合在模型结果中产生了更有价值的改进,但在这些情况下,我们假设替代物与一些与农药运输直接相关的未知测量相关。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Comparison of surrogate models to estimate pesticide concentrations at six U.S. Geological Survey National Water Quality Network sites during water years 2013–18
First posted January 31, 2023 For additional information, contact: Director, Ohio-Kentucky-Indiana Water Science CenterU.S. Geological Survey5957 Lakeside Blvd.Indianapolis, IN 46278-1996Contact Pubs Warehouse During water years 2013–18, the U.S. Geological Survey National Water-Quality Assessment Project sampled the National Water Quality Network for Rivers and Streams year-round and reported on 221 pesticides at 72 sites across the United States. Pesticides are difficult to measure, their concentrations often represent discrete snapshots in time, and capturing peak concentrations is expensive. Three types of regression models were developed to estimate concentrations for two selected pesticides at each of six National Water Quality Network for Rivers and Streams sites. The regression models used continuously measured streamflow and water-quality properties (differing combinations of pH, specific conductance, turbidity, and water temperature); discrete water-quality samples analyzed for atrazine, azoxystrobin, bentazon, bromacil, imidacloprid, simazine, and triclopyr; and time as an additional explanatory variable for seasonality.The modeling approaches included (1) a standard regression that included surrogates (differing combinations of pH, specific conductance, turbidity, and water temperature) and periodic functions (sine-cosine) of pesticide application use as predictor variables; (2) the seasonal wave with flow adjustment model that included a seasonal component and flow anomalies but excluded surrogates; and (3) the seasonal wave with flow adjustment model that included a seasonal component, flow anomalies, and surrogates. Models were evaluated using three measures of model performance: generalized coefficient of determination (generalized R2), Akaike’s Information Criteria, and scale (the estimated standard deviation of the tobit regression error term). Because of low observation numbers, results from this study can be considered a pilot effort with the possibility that some models are overfit.In all cases, estimated pesticide concentrations modeled with base SEAWAVE-Q were better than the standard surrogate regression models; all 39 generalized R2 values increased by 3–56 percent (median of 25 percent) when compared to the standard surrogate regression models, and all Akaike’s Information Criteria and scale values decreased. The addition of surrogate variables such as pH, specific conductance, turbidity, and water temperature to the base SEAWAVE-Q model to improve estimates of pesticide concentrations resulted in only modest improvements; generalized R2 values increased by only 0–10 percent (median of 3 percent). In some instances, combinations of the surrogates produced more appreciative improvements in model results, but in those instances, we hypothesize that the surrogates correlated with some unknown measure that directly relates to pesticide transport.
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