Kaufmann Philip R, Carlisle Daren M, Faustini John M, Weber Marc H, Herlihy Alan T, Hill Ryan A, Kasprak Alan, Paulsen Steven G
U.S. Environmental Protection Agency, Office of Research and Development, Center for Public Health and Environmental Assessment, Pacific Ecological Systems Division, 200 SW 35th Street, Corvallis, OR 97333, USA.
Department of Fisheries, Wildlife, and Conservation Sciences, Oregon State University, Corvallis, Oregon 97331, USA.
Geomorphology (Amst). 2024 Dec 1;466. doi: 10.1016/j.geomorph.2024.109360.
Reliable estimates of low flow and flood discharge at ungaged locations are required for evaluating stream flow alteration, designing culverts and stream crossings, and interpreting regional surveys of habitat and biotic condition. Very few stream gaging stations are located on small, remote streams, which typically have complex channel morphology. Adequate gaging is also lacking on larger streams that are remote, smaller than those typically gaged, or have channel morphology not conducive to installation of gages. Complex channels typically contain large scale hydraulic roughness elements that dominate flow patterns (i.e., form roughness), making it difficult to measure channel cross-section area and water velocity, or to measure channel volume even where discharge is known. In channels with large channel form roughness, it is equally difficult to estimate discharge using commonly applied equations based on slope and channel dimensions or basin area. We employed a novel approach that explicitly accounts for hydraulic resistance from large wood and riffle-pool morphology (form roughness) in calculating low flow and bankfull discharge from stream and river physical habitat data collected from 4,229 stream and river sites in the conterminous US (CONUS) sampled in 2008-9 and 2013-14 as part of the US Environmental Protection Agency's National Rivers and Streams Assessment (NRSA). Hydraulic resistance derived from form roughness clearly dominated resistance derived from bed particles (particle resistance) during summer low flows in wadeable streams across the spectrum of channel slopes and substrate sizes smaller than boulders. Under bankfull conditions, the influence of form resistance relative to particle resistance was diminished, but form resistance still dominated except in large low gradient rivers lacking complex channels, and in streams or rivers with boulder-size bed particles. We validated our hydraulic resistance estimates by comparing measured discharges with calculated discharges that used those hydraulic resistance estimates along with measured NRSA channel morphology data. Morphology-based summer discharge (low flow) estimates and direct field measurements of discharge in 2,333 wadeable CONUS streams showed reasonable agreement (median difference <2.5x) for discharges ranging from 3.6x10 to 123 m/s and drainage areas of 0.12 to 171,000 km. In a subset of 759 of NRSA's larger wadeable stream and non-wadeable river sites where nearby U.S. Geological Survey (USGS) gage data were available and adequate, our morphology-based summer discharge estimates agreed fairly well (median difference <2.0x) with USGS 20-y average August mean flows ranging from 0.003 to 16,000 m/s. Similarly, morphology-based estimates of bankfull flow ranging from 0.3 to 100,000 m/s agreed reasonably well with the 1.5-yr recurrence interval flood in these gaged sites (median deviation <2.2x). These findings demonstrate the importance of quantifying flow resistance from large-scale form roughness features in natural channels and provide a novel approach for estimating discharge from widely available survey data. This will allow examination of discharge and its ecological influence across the full range of stream and river sizes sampled by NRSA or other synoptic surveys where comprehensive measures of biota, physical habitat, and chemistry are also made. Although these morphology-based estimates exhibit some variability, they are adequate for examining regional patterns in discharge and flow alteration and their association with instream biota and anthropogenic disturbances, providing summer low and bankfull flow information where reliable estimates are lacking.
为了评估河流流量变化、设计涵洞和跨河设施以及解读栖息地和生物状况的区域调查结果,需要对未设测量站地点的枯水流量和洪水流量进行可靠估算。在小型偏远河流上设置的水文测量站极少,而这些河流通常具有复杂的河道形态。在偏远的大型河流、比通常测量的河流小的河流或河道形态不利于安装测量仪器的河流上,也缺乏足够的测量。复杂的河道通常包含主导水流模式的大型水力粗糙要素(即形态糙度),这使得测量河道横截面积和水流速度变得困难,甚至在已知流量的情况下测量河道容积也很困难。在具有较大河道形态糙度的河道中,使用基于坡度、河道尺寸或流域面积的常用公式来估算流量同样困难。我们采用了一种新方法,在根据2008 - 2009年和2013 - 2014年在美国本土(CONUS)4229个溪流和河流站点收集的溪流和河流物理栖息地数据计算枯水流量和满岸流量时,明确考虑了大型木材和浅滩 - 深潭形态(形态糙度)产生的水力阻力,这些数据是美国环境保护局国家河流和溪流评估(NRSA)的一部分。在整个河道坡度范围以及小于巨石尺寸的底质条件下,在可涉水溪流的夏季枯水期,由形态糙度产生的水力阻力明显主导了由河床颗粒产生的阻力(颗粒阻力)。在满岸条件下,形态阻力相对于颗粒阻力的影响有所减弱,但除了缺乏复杂河道的大型低坡度河流以及具有巨石尺寸河床颗粒的溪流或河流外,形态阻力仍然占主导地位。我们通过将测量流量与使用这些水力阻力估算值以及测量的NRSA河道形态数据计算得出的流量进行比较,验证了我们的水力阻力估算。基于形态的夏季流量(枯水流量)估算值与美国本土2333条可涉水溪流中的直接野外流量测量结果显示,对于流量范围从3.6×10至123立方米/秒以及流域面积从0.12至171,000平方千米的情况,两者具有合理的一致性(中位数差异<2.5倍)。在美国国家河流和溪流评估(NRSA)中759个较大的可涉水溪流和不可涉水河流站点的子集中,在有附近美国地质调查局(USGS)测量数据且数据充足的情况下,我们基于形态的夏季流量估算值与USGS 20年平均8月平均流量范围从0.003至16,000立方米/秒的结果相当吻合(中位数差异<2.0倍)。同样,基于形态的满岸流量估算值范围从0.3至100,000立方米/秒与这些测量站点的1.5年重现期洪水结果也相当吻合(中位数偏差<2.2倍)。这些发现证明了量化天然河道中大型形态糙度特征产生的水流阻力的重要性,并提供了一种从广泛可用的调查数据估算流量的新方法。这将允许在NRSA或其他进行生物群落、物理栖息地和化学综合测量的概要调查所采样的整个溪流和河流大小范围内,研究流量及其生态影响。尽管这些基于形态的估算值存在一定变异性,但它们足以用于研究流量和流量变化的区域模式及其与河流水生生物和人为干扰的关联,在缺乏可靠估算的地方提供夏季枯水流量和满岸流量信息。