No targets are currently set for this indicator.
The summer low flow indicator measures current conditions and long-term trends in stream flows that occur during summer months when there is less rain and temperatures are warmer. The indicator tells us how often summer flows are below normal, relative to a 50-year baseline, in unregulated streams and rivers across Puget Sound. When flows are below normal, less water is available for people and wildlife to use, less habitat is available for salmon and it can contribute to increased water temperatures and lower water quality.
Status of annual summer low flow at indicator streamgages. Each cell is color coded for a category of frequency of below normal flow. Categories are based on the percent of days each year between July 15th and September 15th where the mean daily flow was below normal (i.e., below the 1948-1998 baseline 25th percentile). When most days (50% or more) were below normal, the cell is shaded purple. When fewer than 50% of the days were below normal, the cell is shaded blue. Streamgages are grouped as 1) rain-sourced, 2) transitional (between rain- and snow-sourced), or 3) snow-sourced based on the center of timing date.
When water in streams and rivers goes down, it places pressure on municipal, residential, industrial, and agricultural water supplies. Keeping track of flows in the summer, the driest and warmest time of year, and the causes for change, helps resource managers and communities formulate strategies that help to minimize or mitigate declining flows where possible and respond to climate change.
Below normal summer flows also adversely affect fish and wildlife habitats. During the period of summer low flows, there are several salmon species and life histories living in Puget Sound streams and rivers. When flows are too low, it has the potential to impact habitat capacity for rearing juvenile salmon and to prevent access to, or the availability of, adult spawning areas.
Climate change impacts summer streamflows. With rising snow elevations and less snowpack, summer low flows are becoming lower and longer lasting throughout the region (see State of Salmon in Watersheds, Water Quantity Risk Factors).
Streamflow Monitoring Program, Washington Department of Ecology
U.S. Geological Survey Groundwater and Streamflow Information Program - Streamgaging Network, compiled by the Streamflow Monitoring Program at the Washington Department of Ecology
Summer low flows in streams and rivers occur at the time of year characterized by warm temperatures, little rainfall, and depleted snowpacks. This coincides with the time when water demands are greatest, yet supply is lowest. The USGS Groundwater and Streamflow Information Program collects streamflow data through a network of streamgages that continuously monitor streamflow year-round and from which daily mean streamflows are computed and made available online.
The summer low flow indicator reports annually on the number of days during the summer period (July 15 through September 15) that a river’s mean daily flow falls below “normal” relative to the baseline data for that river. Normal flows are defined by conditions observed over a 50-year baseline, from 1948 to 1998. This baseline was selected:
From the baseline record, we calculate daily percentiles for each river to describe the range of flows that occurred between 1948 and 1998. We use these percentiles to interpret the status, or condition, of summer flows each year. Within the 50-year baseline period, half of the daily flow values fall in the middle range (between the 25th and 75th percentiles). This is the “normal” range of summer flow values, relative to the baseline. We interpret daily flows that are below the 25th percentile to be “below normal”, or low, relative to the baseline range for a given river.
The indicator tracks the number of days each year where the mean daily flow was below the baseline 25th percentile. We show the number of days as a percentage of the total days during the summer flow period (total of 63 days during the low flow period). This tells us how often summer flows each year were below normal.
The indicator reports on conditions at 19 streamgages throughout Puget Sound to describe the regional picture of status and trends in summer low flows. We selected gages distributed across Puget Sound with a complete record of streamflow data available from 1948 to present (some exceptions were made for gages with incomplete records if the data gap was less than 10 years) and little to no upstream regulation (no dams or significant barriers impeding the flow of water). Preference was given to gages in the USGS Hydro-Climatic Data Network which represents a subset of gages that primarily reflect climatic variations with minimal anthropogenic disturbances. The gages that met these criteria generally represent minimally disturbed, upland streams with a low percentage of impervious cover in the basin.
We also examined trends in streamflow timing through a center of timing (CT) analysis (Kormos et al. 2016). The CT is defined by the date when half of the total streamflow in a water year (12-month period beginning October 1) has passed by the gage station. CT is influenced by the timing of snowmelt runoff in areas with substantial annual snowpack as well as the contribution of rain to snow (EPA Technical Documentation: Streamflow, 2021). We grouped the 19 indicator gages into three categories based on their average CT over the baseline period:
Finally, we identified five gages where summer flows are enhanced by glacier meltwater based on the presence of glaciers in the basin headwaters and qualitative descriptions of the streams and rivers. The five gages (and site code) include:
Summer low flow period: July 15 – September 15
Baseline period: 1948 – 1998, which encompasses a complete PDO cycle including a cool (1948-76) and warm (1977-98) phase.
Center of timing (CT): the date when half of the total streamflow in a water year (12-month period beginning October 1) has passed by the gage station.
Figure 1 shows a chart of daily summer flows between July 15 and September 15 in 2021 (black line) relative to the 1948-1998 baseline range for each of the 19 indicator gages that met our criteria. Flows lower than the baseline 25th percentile (yellow band and below) are interpreted as “below normal”. When flows in a given year are consistently below the 25th percentile, we conclude that flows that year were regularly below the normal range. In 2021, summer flows were below normal most of the time at about three-quarters of the 19 selected gages.
Figure 2 shows the status of summer flows at a given gage for each year. Systems are grouped by their Center of Timing (CT) date as rain-sourced, transitional, or snow-sourced. Systems under each of the three categories show an increasing trend in the percentage of days where flows are below normal. After 1985, these below normal flows occur more consistently across the region and occur over consecutive years, indicated by a shift from predominantly blue cells to purple cells from left to right. Beginning in 2015, we see consecutive years where nearly all systems had below normal summer flows over 75% of the time, indicated by the dark purple cells.
Summer flows are enhanced by glacier meltwater at three transitional and two snow-sourced indicator gages (denoted with an asterisk (*) in Figure 2). These systems with substantial glaciers in their basin headwaters have fewer days with below normal flows compared to the other rain, transitional, and snow-sourced rivers. The more stable flows observed in these systems is likely a temporary offset from accelerated glacial melt.
Flows below the lowest flow observed over the 50-year baseline, were recorded at all but one indicator gage (Huge Creek near Wauna, Site Code 12073500) during the 1999-2021 study period (Figure 3). The streamgage at Huge Creek near Wauna represents flows at a system that is smaller than others measured for the indicator (6.5 sq mi drainage area compared to an average area of 303.4 sq mi). Huge Creek is also the only system with a significant groundwater input and was not subject to below normal summer flows in recent years as seen in other Puget Sound systems.
The count of years between 1999 and 2021 where flows were below the baseline minimum ranged from 2 years (rain-sourced Taylor Creek near Selleck, Site Code 12117000) up to 14 of 23 years (snow-sourced Sauk River near Sauk, Site Code 12189500). In 2015, summer flows at all but two of the non-glacier enhanced systems were below the baseline minimum over half the time.
Supporting Analysis - Changes in Streamflow Timing
Key Center of Timing Results
Center of Timing Approach
In addition to reporting on status and trends in summer low flow, we explored changes in streamflow timing. Center of timing (CT), also known as center of mass, or center of volume, is the date in the water year (October 1 to September 30) when half of the cumulative flow occurs. The cumulative flow is the total volume of water passing a gage in an entire water year.
CT tells us how flows are distributed over a water year and correlate with the type of stream (Stewart et al. 2005). For example, a later CT indicates a higher proportion of the flows come from snowmelt; earlier CT indicates a higher proportion of the flows come from rainfall or that snowmelt is occurring earlier in the year.
We calculated the annual CT from 1948 to 2021 for all 19 indicator gages. We used the approach described in Kormos et al. (2016), to classify each streamgage based on the mean annual CT from 1948 to 1998 (the baseline period) as follows:
We calculated CT for each of the 13 snow-sourced or transitional gages and the six rain-sourced gages. To test whether CT changed between 1948 and 2021, we conducted a trend analysis on the 13 snow-sourced or transitional gages and compared average CT across multiple time periods.
Center of Timing Results and Interpretation
Table 2 compares the average CT from 1948-1998 and 1999-2021. CT occurred on average 7 days earlier during the latter period.
Recognizing the significant global climate shift that occurred in the mid- to late-1980s, Table 3 compares the average CT from 1948-1985 and 1986-2021. For the 13 snow-sourced and transitional gages, CT occurred on average 13 days earlier over the 1986-2021 period compared to the 1948-1985 period. Changes in the CT at rain-sourced gages varied and was on average 2 days earlier during the latter period.
Trend analyses show with certainty (p<0.10) that the CT is occurring earlier in the year at 10 of the 13 snow-sourced and transitional gages from 1948 to 2021 (Table 4). Only two of the six rain-sourced systems showed a significant change in the CT date over time, with one site indicating the occurrence shifted earlier in the year and the other indicating the occurrence had shifted later in the year.
Both the trend and comparative analyses suggest that overall, CT in Puget Sound streams and rivers is regressing to earlier occurrences over time, especially in the snow-sourced and transitional systems. This means the low flow season in our region is becoming longer as larger fractions of total annual runoff are occurring progressively earlier in the year.
Recent studies indicate earlier CT dates are mostly related to warmer temperatures and reduced snowpack. (Kormos et al. 2016; Georgiadis et al. 2022). Warming winter and spring temperatures force more precipitation to fall as rain rather than snow, and further hasten earlier snowmelt (Stewart et al. 2005).
Annual cumulative flows (not shown) declined at 9 of the 13 snow-sourced or transitional gages analyzed from 1948 to 2021. However, none of the gages showed a significant trend in decreasing or increasing cumulative flows. Three of the four gages with increasing cumulative flows were from the Puyallup and Nisqually River basins with substantial glaciers at their headwaters. The fourth gage, showing a slight increase, is the North Fork Nooksack River near Glacier which also has glacial input.
The presence of glaciers and their melting may cause different responses on streamflows than that of non-glacial basins (Stewart et al. 2005). We see this distinction quite clearly between streams with substantial glacial inputs and those without, both in the CT and summer flows analyses.
Mean Center of Timing (CT) Between Baseline and 1999-2021 | ||||
---|---|---|---|---|
Source Classification | Site Name |
1948-1998 (baseline) |
1999-2021 | Days Different from Baseline |
Snow | NF Nooksack R. near Glacier* | May 19 (231) | May 9 (221) | -10 |
Dungeness R. near Sequim | April 19 (201) | April 9 (191) | -10 | |
Sauk R. near Darrington | April 20 (202) | April 9 (191) | -11 | |
Thunder Cr. near Newhalem* | June 13 (256) | June 8 (251) | -5 | |
Sauk River near Sauk | April 19 (201) | April 9 (191) | -10 | |
Transitional | Puyallup River near Electron* | April 13 (195) | April 13 (195) | 0 |
Greenwater River at Greenwater | April 7 (189) | April 1 (183) | -6 | |
Nisqually River near National* | March 30 (181) | March 29 (180) | -1 | |
Duckabush River near Brinnon | March 11 (162) | Feb. 24 (147) | -15 | |
Skykomish River near Gold Bar | March 30 (181) | March 18 (169) | -12 | |
Puyallup River near Orting* | March 19 (170) | March 22 (173) | 3 | |
Cedar River near Cedar Falls | March 14 (165) | March 11 (162) | -3 | |
Rex River near Cedar Falls | Feb. 28 (151) | Feb. 23 (146) | -5 | |
Rain | NF Skokomish River below Staircase Rpds | Feb. 26 (149) | Feb. 7 (130) | -19 |
Taylor Creek near Selleck | Feb. 21 (144) | Feb. 23 (146) | 2 | |
NF Stillaguamish River near Arlington | Feb. 14 (137) | Feb. 6 (129) | -8 | |
Deschutes River near Rainier | Feb. 4 (127) | Feb. 2 (125) | -2 | |
Newaukum Creek near Black Diamond | Feb. 16 (139) | Feb. 18 (141) | 2 | |
Huge Creek near Wauna | Feb. 14 (137) | Feb. 7 (130) | -7 |
Mean Center of Timing (CT) Between 1948-1985 and 1986-2021 | ||||
---|---|---|---|---|
Source Classification | Site Name |
1948-1985 |
1986-2021 | Days Different from 1948-1985 |
Snow | NF Nooksack R. near Glacier* | April 18 (200) | April 10 (192) | -8 |
Dungeness R. near Sequim | April 24 (206) | April 7 (189) | -17 | |
Sauk R. near Darrington | April 27 (209) | April 5 (187) | -22 | |
Thunder Cr. near Newhalem* | June 15 (258) | June 7 (250) | -8 | |
Sauk River near Sauk | April 25 (207) | April 6 (188) | -19 | |
Transitional | Puyallup River near Electron* | April 18 (200) | April 10 (192) | -8 |
Greenwater River at Greenwater | April 10 (192) | March 29 (180) | -12 | |
Nisqually River near National* | April 3 (185) | March 25 (176) | -9 | |
Duckabush River near Brinnon | March 13 (164) | Feb. 27 (150) | -14 | |
Skykomish River near Gold Bar | April 4 (186) | March 16 (167) | -19 | |
Puyallup River near Orting* | March 21 (172) | March 19 (170) | -2 | |
Cedar River near Cedar Falls | March 19 (170) | March 8 (159) | -11 | |
Rex River near Cedar Falls | March 4 (155) | Feb. 20 (143) | -12 | |
Rain | NF Skokomish River below Staircase Rpds | Feb. 28 (151) | Feb. 12 (135) | -16 |
Taylor Creek near Selleck | Feb. 21 (144) | Feb. 22 (145) | 1 | |
NF Stillaguamish River near Arlington | Feb. 15 (138) | Feb. 8 (131) | -7 | |
Deschutes River near Rainier | Feb. 2 (125) | Feb. 5 (128) | 3 | |
Newaukum Creek near Black Diamond | Feb. 14 (137) | Feb. 19 (142) | 5 | |
Huge Creek near Wauna | Feb. 11 (134) | Feb. 12 (135) | 1 |
Center of Timing (CT) 1948-2021 Trend | |||
---|---|---|---|
Source Classification | Site Name |
Regression Slope |
Significance (p-value) |
Snow | NF Nooksack R. near Glacier* | -0.388 | 0.002 |
Dungeness R. near Sequim | -0.436 | 0.008 | |
Sauk R. near Darrington | -0.466 | 0.006 | |
Thunder Cr. near Newhalem* | -0.156 | 0.009 | |
Sauk River near Sauk | -0.421 | 0.006 | |
Transitional | Puyallup River near Electron* | -0.166 | 0.305 |
Greenwater River at Greenwater | -0.294 | 0.077 | |
Nisqually River near National* | -0.218 | 0.142 | |
Duckabush River near Brinnon | -0.423 | 0.006 | |
Skykomish River near Gold Bar | -0.505 | 0.003 | |
Puyallup River near Orting* | -0.019 | 0.888 | |
Cedar River near Cedar Falls | -0.325 | 0.057 | |
Rex River near Cedar Falls | -0.530 | 0.042 | |
Rain | NF Skokomish River below Staircase Rpds | -0.467 | 0.002 |
Taylor Creek near Selleck | 0.019 | 0.880 | |
NF Stillaguamish River near Arlington | 0.218 | 0.061 | |
Deschutes River near Rainier | 0.004 | 0.968 | |
Newaukum Creek near Black Diamond | 0.581 | 0.561 | |
Huge Creek near Wauna | -0.038 | 0.680 |
Summer low flows in the Puget Sound basin respond to a variety of drivers including rainfall, snowfall, temperature, evapotranspiration, land-use conversion, forest practices, and human water use. Our analysis aims to describe the regional condition and change pattern in summer low flow but does not specifically evaluate drivers of a trend.
That said, the streamgages selected for this indicator represent primarily large, minimally disturbed streams and rivers. Since 1985, the increasing trend in consecutive years with below normal summer flows, consistent across the region, suggests climate impacts rather than development impacts on low flows. Research shows a significant global climate shift occurred in the mid- to late 1980s, with an increase in temperature as the main factor behind the shift (Reid et al. 2015). Flows at most of the indicator gages are sensitive to snowpack changes. With global warming changing when and where it snows and when snow melts, we can point to climate change as likely the most significant driver of change to summer low flows over the Puget Sound region.
For more information on distinguishing impacts on low flows, please see the Georgiadis et al. (2022) report Distinguishing Climate Change Impacts from Development Impacts on Summer Low Flows in Puget sound Streams.
References
Georgiadis, N., K. Bogue, C. DeGasperi. 2022. Distinguishing climate change impacts from development impacts on summer low flows in Puget Sound streams. Puget Sound Institute. University of Washington.
Kormos, P.R., C.H. Luce, S.J. Wenger, W.R. Berghuijs. 2016. Trends and sensitivities of low streamflow extremes to discharge timing and magnitude in Pacific Northwest Mountain streams. Water Resources Research, 52, 4990–5007. DOI:10.1002/2015WR018125
Reid, P.C., R.E. Hari, G. Beaugrand, D.M. Livingstone, C. Marty, D. Straile, J. Barichivich, E. Goberville, R. Adrian, Y. Aono, R. Brown, J. Foster, P. Groisman, P. Helaouet, H. Hsu, R. Kirby, J. Knight, A. Kraberg, J. Li, T. Lo, R.B. Myneni, R.P. North, J.A. Pounds, T. Sparks, R. Stubi, Y. Tian, K.H. Wiltshire, D. Xiao, Z. Zhu. 2015. Global impacts of the 1980s regime shift. Global Change Biology. DOI: 10.1111/gcb.133106
Stewart, I.T., D.R. Cayan, M.D. Dettinger. 2005. Changes toward earlier streamflow timing across Western North America. Journal of Climate, Volume 18: Issue 8.
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Rain, Transitional, Snow
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