更新ce - quality - w2模型,用于美国陆军工程兵团在俄勒冈州西北部威拉米特河谷项目和中叉威拉米特河的水库间河段

Laurel E. Stratton Garvin, Norman L. Buccola, Stewart A. Rounds
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CE-QUAL-W2 is a two-dimensional (laterally averaged) hydrodynamic water-quality model that has previously been used to investigate the downstream effects of dam operations and other anthropogenic influences on stream temperature in the Willamette River Basin in northwestern Oregon, a region with two populations of fish species designated as threatened under the Endangered Species Act. By linking CE-QUAL-W2 river models to models of upstream, large Willamette Valley Project dams and reservoirs, these models can be used to investigate how dam operations at individual dams can influence streamflow and thermal conditions in downstream river reaches as an integrated system. Integrated model simulations that include the large dams and reservoirs linked to downstream river reaches can help managers develop a better understanding of tradeoffs associated with potential retrofits or operational changes across the multipurpose dams in the Willamette Valley Project, the effect of dam management on downstream tributaries and the Willamette River, and the resulting potential effect on threatened fish populations and habitat conditions.River models capable of simulating river corridors downstream from U.S. Army Corps of Engineers dams were previously updated and integrated to simulate conditions that occurred from March through October of 2011 (a cool and wet year), 2015 (a hot and dry year), and 2016 (a moderately hot and dry year) using CE-QUAL-W2 version 4.2. These river models encompass the following:Coast Fork Willamette and Middle Fork Willamette Rivers, the Row River, and Fall Creek downstream from Cottage Grove, Dexter, Dorena, and Fall Creek Dams, respectively;South Fork McKenzie River downstream from Cougar Dam;McKenzie River downstream from its confluence with the South Fork McKenzie River;South Santiam River downstream from Foster Dam;North Santiam River downstream from Big Cliff Dam; andWillamette River from its start at the confluence of the Middle Fork Willamette and Coast Fork Willamette Rivers to Willamette Falls (river mile 26.0; near West Linn, Oregon).This report documents model modifications, boundary condition data sources or estimation methods, and goodness-of-fit statistics for six CE-QUAL-W2 reservoir models and one river model upstream from the existing river models. These models simulate (1) Hills Creek Lake; (2) Lookout Point Lake and Dexter Reservoir on the Middle Fork Willamette River; (3) the Middle Fork Willamette River reach between Hills Creek Dam upstream and Lookout Point Lake downstream; (4) Cougar Reservoir on the South Fork McKenzie River; (5) Green Peter Lake on the Middle Santiam River and Foster Lake on the South Santiam River; and (6) Detroit Lake and (7) Big Cliff Reservoir on the North Santiam River. These CE-QUAL-W2 models were built by a variety of researchers to simulate a range of conditions in past years; this report documents their upgrade to U.S. Geological Survey (USGS) edition 7 of version 4.2 of CE-QUAL-W2 and updates each model to simulate conditions from January through December of 2011, 2015, and 2016. Also included in this report is an explanation of modifications to the CE-QUAL-W2 source code that constitute USGS edition 7 of CE-QUAL-W2 version 4.2. Each of the models described in this report can be run in isolation or linked to downstream models as a “system model” to simulate conditions in tributaries and (or) in the Willamette Valley Project as a whole.As part of the model updates described in this report, some model parameters were adjusted to improve stability or decrease model error, and boundary conditions including meteorological, hydrologic, and temperature inputs were developed and updated for model years 2011, 2015, and 2016, as necessary. In some cases, the data sources used to drive previous model versions were no longer available, which required the development and checking of new data sources or estimation techniques. Goodness-of-fit statistics for outflow from the dams and in simulated river reaches generally show a good model fit, with the models simulating subdaily water temperatures at most comparable locations with a mean absolute error of generally less than 1 degree Celsius (°C) and a reasonably low bias. Model simulation of the thermal vertical profiles in each reservoir also produced an overall mean absolute error of generally less than 1 °C for all 3 years, with the exception of the Hills Creek Lake Model and the Cougar Reservoir Model in years when the reservoirs did not fill (2015 and 2016). Both of these models have known calibration issues and tend to be sensitive to the choice of certain structural parameters in the model. Overall, the calibration process was focused on obtaining model settings that led to realistic water temperature predictions in all 3 years (2011, 2015, and 2016) without over-calibrating specifically to any single year. 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CE-QUAL-W2 is a two-dimensional (laterally averaged) hydrodynamic water-quality model that has previously been used to investigate the downstream effects of dam operations and other anthropogenic influences on stream temperature in the Willamette River Basin in northwestern Oregon, a region with two populations of fish species designated as threatened under the Endangered Species Act. By linking CE-QUAL-W2 river models to models of upstream, large Willamette Valley Project dams and reservoirs, these models can be used to investigate how dam operations at individual dams can influence streamflow and thermal conditions in downstream river reaches as an integrated system. Integrated model simulations that include the large dams and reservoirs linked to downstream river reaches can help managers develop a better understanding of tradeoffs associated with potential retrofits or operational changes across the multipurpose dams in the Willamette Valley Project, the effect of dam management on downstream tributaries and the Willamette River, and the resulting potential effect on threatened fish populations and habitat conditions.River models capable of simulating river corridors downstream from U.S. Army Corps of Engineers dams were previously updated and integrated to simulate conditions that occurred from March through October of 2011 (a cool and wet year), 2015 (a hot and dry year), and 2016 (a moderately hot and dry year) using CE-QUAL-W2 version 4.2. 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Model simulation of the thermal vertical profiles in each reservoir also produced an overall mean absolute error of generally less than 1 °C for all 3 years, with the exception of the Hills Creek Lake Model and the Cougar Reservoir Model in years when the reservoirs did not fill (2015 and 2016). Both of these models have known calibration issues and tend to be sensitive to the choice of certain structural parameters in the model. Overall, the calibration process was focused on obtaining model settings that led to realistic water temperature predictions in all 3 years (2011, 2015, and 2016) without over-calibrating specifically to any single year. 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引用次数: 0

摘要

欲了解更多信息,请联系:俄勒冈州水科学中心主任。能够模拟河流和水库的水动力学和水温的机械模型是研究热条件及其与大坝运行和河流流域流量关系的有价值的工具,在河流流域,上游的储水和管理决策对鱼类种群受威胁的河流流域有重要影响。特别是,模型允许管理人员调查新的、未经尝试的操作或假设的结构如何影响下游的流量和温度条件。CE-QUAL-W2是一个二维(横向平均)水动力水质模型,以前曾用于调查俄勒冈州西北部威拉米特河流域大坝运行对下游的影响和其他人为影响对河流温度的影响,该地区有两种根据《濒危物种法》被指定为受威胁的鱼类。通过将ce - quality - w2河流模型与上游的大型威拉米特河谷项目大坝和水库的模型联系起来,这些模型可以用于研究单个大坝的大坝运行如何影响下游河流的流量和热条件,作为一个综合系统。综合模型模拟,包括与下游河流相连的大型水坝和水库,可以帮助管理者更好地了解与威拉米特河谷项目中多用途水坝的潜在改造或运营变化相关的权衡,水坝管理对下游支流和威拉米特河的影响,以及由此产生的对受威胁鱼类种群和栖息地条件的潜在影响。能够模拟美国陆军工程兵团大坝下游河流走廊的河流模型之前已经更新和整合,以模拟2011年3月至10月(凉爽潮湿的年份)、2015年(炎热干燥的年份)和2016年(中度炎热干燥的年份)的情况,使用ce - quality - w2 4.2版本。这些河流模型包括:分别从Cottage Grove、Dexter、Dorena和Fall Creek大坝下游的海岸叉叉威拉米特河和中叉威拉米特河、Row河和Fall Creek河;从美洲狮大坝下游的南叉麦肯齐河;从与南叉麦肯齐河汇合处下游的麦肯齐河;从福斯特大坝下游的南叉麦肯齐河;和威拉米特河从中叉威拉米特河和海岸叉威拉米特河汇合处开始到威拉米特瀑布(河英里26.0;俄勒冈州西林附近)。本报告记录了6个ce - quality - w2水库模型和一个现有河流模型上游的河流模型的模型修改、边界条件数据源或估计方法以及拟合优度统计。这些模型模拟了(1)Hills Creek Lake;(2)中叉威拉米特河上的瞭望台湖和德克斯特水库;(3)在上游的希尔斯克里克大坝和下游的瞭望台湖之间的中叉威拉米特河河段;(4)南福克麦肯齐河上的美洲狮水库;(5)中圣地亚哥河上的绿彼得湖和南圣地亚哥河上的福斯特湖;(6)底特律湖和(7)北圣地亚哥河上的大悬崖水库。这些ce - quality - w2模型是由各种研究人员建立的,用于模拟过去几年的一系列条件;本报告记录了它们升级到美国地质调查局(USGS) ce - quality - w2 4.2版的第7版,并更新了每个模型,以模拟2011年1月至12月、2015年和2016年的条件。本报告还包括对ce - quality - w2源代码修改的解释,这些修改构成了美国地质调查局ce - quality - w2 4.2版的第7版。本报告中描述的每个模型都可以单独运行,也可以作为一个“系统模型”与下游模型相关联,以模拟支流和(或)整个威拉米特河谷项目的条件。作为本报告中描述的模式更新的一部分,调整了一些模式参数以提高稳定性或减少模式误差,并根据需要开发和更新了2011年、2015年和2016年模式年的边界条件,包括气象、水文和温度输入。在某些情况下,用于驱动以前模型版本的数据源不再可用,这就需要开发和检查新的数据源或评估技术。大坝流出量和模拟河段的拟合优度统计数据通常显示出良好的模型拟合,模型在大多数可比地点模拟亚日水温,平均绝对误差通常小于1摄氏度(°C),偏差相当低。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Updates to CE-QUAL-W2 models for select U.S. Army Corps of Engineers reservoirs in the Willamette Valley Project and an inter-reservoir reach of the Middle Fork Willamette River, northwestern Oregon
First posted September 5, 2023 For additional information, contact: Director, Oregon Water Science CenterU.S. Geological Survey601 SW Second Avenue, Suite 1950Portland, Oregon 97204 Mechanistic models capable of simulating hydrodynamics and water temperature in rivers and reservoirs are valuable tools for investigating thermal conditions and their relation to dam operations and streamflow in river basins where upstream water storage and management decisions have an important influence on river reaches with threatened fish populations. In particular, models allow managers to investigate how new, untried operations or hypothetical structures might influence streamflow and temperature conditions downstream. CE-QUAL-W2 is a two-dimensional (laterally averaged) hydrodynamic water-quality model that has previously been used to investigate the downstream effects of dam operations and other anthropogenic influences on stream temperature in the Willamette River Basin in northwestern Oregon, a region with two populations of fish species designated as threatened under the Endangered Species Act. By linking CE-QUAL-W2 river models to models of upstream, large Willamette Valley Project dams and reservoirs, these models can be used to investigate how dam operations at individual dams can influence streamflow and thermal conditions in downstream river reaches as an integrated system. Integrated model simulations that include the large dams and reservoirs linked to downstream river reaches can help managers develop a better understanding of tradeoffs associated with potential retrofits or operational changes across the multipurpose dams in the Willamette Valley Project, the effect of dam management on downstream tributaries and the Willamette River, and the resulting potential effect on threatened fish populations and habitat conditions.River models capable of simulating river corridors downstream from U.S. Army Corps of Engineers dams were previously updated and integrated to simulate conditions that occurred from March through October of 2011 (a cool and wet year), 2015 (a hot and dry year), and 2016 (a moderately hot and dry year) using CE-QUAL-W2 version 4.2. These river models encompass the following:Coast Fork Willamette and Middle Fork Willamette Rivers, the Row River, and Fall Creek downstream from Cottage Grove, Dexter, Dorena, and Fall Creek Dams, respectively;South Fork McKenzie River downstream from Cougar Dam;McKenzie River downstream from its confluence with the South Fork McKenzie River;South Santiam River downstream from Foster Dam;North Santiam River downstream from Big Cliff Dam; andWillamette River from its start at the confluence of the Middle Fork Willamette and Coast Fork Willamette Rivers to Willamette Falls (river mile 26.0; near West Linn, Oregon).This report documents model modifications, boundary condition data sources or estimation methods, and goodness-of-fit statistics for six CE-QUAL-W2 reservoir models and one river model upstream from the existing river models. These models simulate (1) Hills Creek Lake; (2) Lookout Point Lake and Dexter Reservoir on the Middle Fork Willamette River; (3) the Middle Fork Willamette River reach between Hills Creek Dam upstream and Lookout Point Lake downstream; (4) Cougar Reservoir on the South Fork McKenzie River; (5) Green Peter Lake on the Middle Santiam River and Foster Lake on the South Santiam River; and (6) Detroit Lake and (7) Big Cliff Reservoir on the North Santiam River. These CE-QUAL-W2 models were built by a variety of researchers to simulate a range of conditions in past years; this report documents their upgrade to U.S. Geological Survey (USGS) edition 7 of version 4.2 of CE-QUAL-W2 and updates each model to simulate conditions from January through December of 2011, 2015, and 2016. Also included in this report is an explanation of modifications to the CE-QUAL-W2 source code that constitute USGS edition 7 of CE-QUAL-W2 version 4.2. Each of the models described in this report can be run in isolation or linked to downstream models as a “system model” to simulate conditions in tributaries and (or) in the Willamette Valley Project as a whole.As part of the model updates described in this report, some model parameters were adjusted to improve stability or decrease model error, and boundary conditions including meteorological, hydrologic, and temperature inputs were developed and updated for model years 2011, 2015, and 2016, as necessary. In some cases, the data sources used to drive previous model versions were no longer available, which required the development and checking of new data sources or estimation techniques. Goodness-of-fit statistics for outflow from the dams and in simulated river reaches generally show a good model fit, with the models simulating subdaily water temperatures at most comparable locations with a mean absolute error of generally less than 1 degree Celsius (°C) and a reasonably low bias. Model simulation of the thermal vertical profiles in each reservoir also produced an overall mean absolute error of generally less than 1 °C for all 3 years, with the exception of the Hills Creek Lake Model and the Cougar Reservoir Model in years when the reservoirs did not fill (2015 and 2016). Both of these models have known calibration issues and tend to be sensitive to the choice of certain structural parameters in the model. Overall, the calibration process was focused on obtaining model settings that led to realistic water temperature predictions in all 3 years (2011, 2015, and 2016) without over-calibrating specifically to any single year. A complete investigation of model error for these reservoir submodels was beyond the scope of this investigation but could be undertaken in the future if better model performance for these two reservoirs is desired.
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