No targets are currently set for this indicator.
The summer low flow indicator measures current conditions and long-term trends in streamflows 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 percentage of days each year between July 15th and October 31st where the 7-day 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 highlighted as 1) (R) rain sourced, 2) (T) transitional (between rain and snow sourced), or 3) (S) snow sourced. Streams with substantial glaciers in their headwaters are denoted with an asterisk. Streams are arranged in order from streams with lowest mean basin elevation to highest.
When flows in streams and rivers diminish, 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, helps resource managers and communities create 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 and other species at various life stages in Puget Sound streams and rivers. Low flows have the potential to impact habitat capacity for rearing juvenile salmon and can prevent access to, and reduce the availability of, adult spawning areas.
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 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, despite that supply is lowest. The USGS Groundwater and Streamflow Information Program collects streamflow data through a network of streamgages that continuously monitor streams, which report mean daily flows year-round and are available online. From these streamflow records, 7-day mean daily streamflows were computed and serves as the basis for this analysis. Note: The 7-day mean daily flow value refers to the moving-average flow of a stream calculated over 7 consecutive days. This metric differs from the daily flow metric used in the 2023 analysis. The 7-day mean flow is more widely used and not subject to short term flow fluctuations that may affect daily flows.
This indicator reports on the number of days during the summer period (July 15 through October 31) that a stream’s 7-day 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 to encompass a complete Pacific Decadal Oscillation (PDO) cycle, including a cool phase (1948-76) and warm phase (1977-98). The PDO is a long-lived (lasting decades) pattern of climactic variability characterized by distinct warm and cool phases (Mantua,1999). Our aim was to capture within the baseline period the variability inherent in flow regimes as the result of climatic influences from both phases of the PDO cycle.
Separately we also compare the periods before and after 1985. Beginning in the mid-1980s the frequency of below normal flows appears to accelerate.
From the baseline record, we calculate 7-day mean daily percentiles for each stream 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. Thus, we interpret 7-day mean daily flows that are below the 25th percentile to be “below normal”, or low, relative to the baseline in each stream.
This indicator tracks the number of days each year where the 7-day 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 109 days during the low flow period). This tells us how often summer flows each year were below normal. We also track the percentage of 7-day mean daily flows that fall below the baseline minimum. The baseline minimum is the lowest 7-day mean for a given date recorded at a gage in the period from 1948 to 1998. Flows below the baseline minimum, while they may not be the lowest flow of the period of record, are extraordinarily low flows.
This indicator reports on conditions at 18 streamgages throughout Puget Sound to describe the regional picture of status and trends in summer flows. Criteria for gage selection included:
The gages that meet these criteria generally represent minimally disturbed, upland streams with a low percentage of impervious cover in the basin.
We also examine trends in streamflow timing through a center of timing (CT) analysis (Kormos et al. 2016). The CT is defined as 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 and rate of snowmelt runoff in areas with substantial annual snowpack among other factors. We grouped the 18 indicator gages into three categories based on their average CT over the baseline period (table 1).
Source Classification |
Center of Timing |
Count of Gages |
Rain-sourced |
Before 2/27 |
2 |
Transitional (rain to snow) |
Between 2/27 and 4/18 |
12 |
Snow-sourced |
After 4/18 |
4 |
Table 1. Source classification based on Center of Timing (CT) date (Kormos et al. 2016).
In addition, we compared the average of annual CT dates from the 1948 to 1998 baseline with the average CT dates of the 1999 to 2023 period. We also compared the average annual CT dates of the 1948 to 1985 period with CT averages from 1986 to 2023 to investigate changes in CT associated with the apparent increase in lower summer flows after the mid-1980s. We also compare the CT average of the short but more recent 2015 to 2023 timeframe with the baseline period. We analyzed CT in this period because beginning in 2015, the occurrence of summer low flow increased substantially. Lastly, we execute a Theil-Sen slope trend analysis (Vannest, et al, 2016) to determine if, and to what degree, CT has changed through the 1948 to 2023 period.
Finally, we identified four 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 four gages (and site code) include:
· Puyallup River near Electron (12092000)
· Nisqually River near National (12082500)
· Thunder Creek near Newhalem (12175500)
· NF Nooksack River below Cascade Creek near Glacier (12205000)
Summer low flow period: July 15 – October 31
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 the status of summer flows at a given gage for each year. Gages are noted as rain-sourced, transitional, or snow-sourced according to their Center of Timing (CT) date. Gages in each of the three categories show an increasing trend in the percentage of days where flows are below normal since 1985. 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 shaded cells from left to right. Beginning in 2015, we see consistent consecutive years where nearly all gages had below normal 7-day summer flows over 50% of the time, indicated by the purple cells. The dark purple cells indicate below normal flows occurring greater than 75% of the time. In 2023, 11 of the 16 gages showed 7-day mean daily flows were below normal greater than 75% of the time.
Summer flows may be enhanced by glacier meltwater at two transitional and two snow-dominated indicator gages (denoted with an asterisk (*) in Figure 1). These watersheds with substantial glaciers in the basin headwaters have generally fewer days with below normal flows compared to the other watersheds. The more stable flows observed at these gages are likely a temporary boost to summer flows from accelerated glacial melt.
Figure 1. Percent of days between July 15th and October 31st where the mean daily flow was below normal (i.e., below the 1948-1998 baseline 25th percentile) each year, by streamgage.
Flows below the minimum observed over the 50-year baseline, were recorded at least once at all indicator gages during the 1999-2023 study period (Figure 2). The total count of years between 1999 and 2023 where flows were below the baseline minimum ranged from just one year (rain-dominated Huge Creek near Wauna (12073500)) up to 13 of the 25 years analyzed (transitional North Fork Snoqualmie (121420000), and North Fork Skokomish Rivers (12056500) ). Figure 2 shows all the analyzed streams, except Huge Creek, recorded 7-day flows below the baseline minimum in 2023. In 2023, summer flows falling below the baseline minimum occurred greater than 50% of the time at half the streams analyzed.
The streamgage at Huge Creek near Wauna is unique in that it represents flows in a basin 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 the only basin with significant groundwater input and was not subject to below normal summer flows in recent years as seen in other Puget Sound watersheds.
Figure 2. Percent of days between July 15th and October 31st where the 7-day mean daily flow was below the 7-day minimum flow observed over the 1948-1998 baseline period.
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 2023 (or period of record available) for all 18 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 (baseline period) as follows:
Snow-sourced systems: mean CT occurs after April 18 (after water year Julian day 200)
Transitional systems (between snow and rain sourced): mean CT occurs between February 28 to April 17 (between water year Julian day 150 to 200)
Rain-sourced systems: mean CT occurs before February 27 (before water year Julian day 150)
We calculated CT for each of the 16 snow-sourced or transitional gages and the two rain-sourced gages. To test whether CT changed between 1948 and 2023, we conducted a Theil-Sen slope trend analysis on the 16 snow-sourced or transitional gages. In addition, we compared average CTs across multiple time periods.
Center of Timing Results and Interpretation
Table 2 compares the average CT from 1948-1998 and 1999-2023. CT occurred an average of 7 days earlier over the latter period.
Recognizing the overall increase in occurrences of lower than normal 7-day mean daily flows beginning in the mid- 1980s, Table 3 compares the average CT from 1948-1985 and 1986-2023. For the 16 snow-sourced and transitional gages, CT occurred on average 12 days earlier over the 1986-2023 period compared to the 1948-1985 period.
Trend analyses show with certainty (α <0.10) that CT is occurring earlier in the year at 10 of the 16 snow-dominated and transitional gages from 1948 to 2023 (Table 4). Neither of the two rain-sourced basins showed a significant change in the CT date over time.
Both the trend and comparative analyses suggest that CT in many Puget Sound streams and rivers are regressing to earlier occurrences over time, in snow-sourced and transitional systems. This means the low flow season in our region may become 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).
Additional analysis not central to the indicator revealed annual cumulative flows (not shown) declined at 11 of the 16 snow-sourced or transitional gages analyzed from 1948 to 2023; however, none of the records showed a significant trend (α < 0.10) in decreasing or increasing cumulative flows.
The presence of glaciers and their melting may cause different responses to 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.
Table 2.
Mean Center of Timing (CT) Between Baseline and 1999-2023 |
|||||
Streamgage |
1948-1998 (baseline) |
1999-2023 |
Days Different from Baseline |
Mean basin elevation (ft.) |
|
Snow Sourced |
NF Nooksack R. near Glacier* |
May 19 (231) |
May 10 (222) |
-9 |
4250 |
Dungeness R. near Sequim |
April 19 (201) |
April 8 (190) |
-11 |
4160 |
|
Sauk R. near Darrington |
April 20 (202) |
April 8 (190) |
-12 |
3860 |
|
Thunder Cr. near Newhalem* |
June 13 (256) |
June 8 (251) |
-5 |
3170 |
|
Transitional |
Puyallup River near Electron* |
April 13 (195) |
April 13 (195) |
0 |
4650 |
Greenwater River at Greenwater |
April 7 (189)** |
April 2 (184) |
-5 |
3980 |
|
Nisqually River near National* |
March 30 (181) |
March 29 (180) |
-1 |
3870 |
|
Duckabush River near Brinnon |
March 11 (162) |
Feb. 24 (147) |
-15 |
3530 |
|
Skykomish River near Gold Bar |
March 30 (181) |
March 18 (169) |
-12 |
3450 |
|
SF Snoqualmie River nr Garcia |
1962-98 Mar 18 (169) |
March 21 (172) |
3 |
3420 |
|
MF Snoqualmie River nr Tanner |
1962-98 March 15 (166) |
March 9 (160) |
-6 |
3410 |
|
Cedar River near Cedar Falls |
March 14 (165) |
March 12 (163) |
-2 |
3300 |
|
Rex River near Cedar Falls |
Feb. 28 (151) |
Feb. 24 (147) |
-4 |
3270 |
|
NF Skokomish River below Staircase Rapids |
Feb. 26 (149) |
Feb. 7 (130) |
-19 |
3250 |
|
NF Snoqualmie River nr Snoqualmie Falls |
1962-98 March 2 (153) |
Feb 24 (147) |
-6 |
3060 |
|
NF Stillaguamish nr Arlington |
Feb. 14 (137) |
Feb. 6 (129) |
-8 |
2150 |
|
Rain Sourced |
Taylor Creek near Selleck |
1957-98 Feb. 21 (144) |
Feb. 23 (146) |
2 |
2280 |
Huge Creek near Wauna |
Feb. 14 (137) |
Feb. 6 (129) |
-8 |
347 |
** Greenwater R. at Greenwater missing cumulative flow data from 1978-1993.
*Substantial glaciers in headwaters.
Table 3.
Mean Center of Timing Between 1948-1985 and 1986-2023 |
|||||
Streamgage |
1948-1985 |
1986-2023 |
Days Different from Baseline |
Mean basin elevation (ft.) |
|
Snow Sourced |
NF Nooksack R. near Glacier* |
May 25 (237) |
May 7 (219) |
-18 |
4250 |
Dungeness R. near Sequim |
April 24 (206) |
April 6 (188) |
-18 |
4160 |
|
Sauk R. near Darrington |
April 27 (209) |
April 5 (187) |
-22 |
3860 |
|
Thunder Cr. near Newhalem* |
June 15 (258) |
June 7 (250) |
-8 |
3170 |
|
Transitional |
Puyallup River near Electron* |
April 18 (200) |
April 10 (192) |
-8 |
4650 |
Greenwater River at Greenwater |
April 10 (192)** |
March 30 (181) |
-11 |
3980 |
|
Nisqually River near National* |
April 3 (185) |
March 26 (177) |
-8 |
3870 |
|
Duckabush River near Brinnon |
March 13 (164) |
February 27 (150) |
-14 |
3530 |
|
Skykomish River near Gold Bar |
April 4 (186) |
March 16 (167) |
-19 |
3450 |
|
SF Snoqualmie River nr Garcia |
March 22** (173) |
March 17 (168) |
-5 |
3420 |
|
MF Snoqualmie River nr Tanner |
March 19 (170) |
March 8 (159) |
-11 |
3410 |
|
Cedar River near Cedar Falls |
March 19 (170) |
March 8 (159) |
-11 |
3300 |
|
Rex River near Cedar Falls |
March 4 (155) |
February 21 (144) |
-11 |
3270 |
|
|
NF Skokomish River below Staircase Rapids |
February 28 (151) |
February 12 (135) |
-16 |
3250 |
|
NF Snoqualmie River nr Snoqualmie Falls |
March 5 (156) |
February 23 (146) |
-10 |
3060 |
|
NF Stillaguamish River near Arlington |
February 15 (138) |
February 7 (130) |
-8 |
2150 |
Rain Sourced |
Taylor Creek near Selleck |
February 22 (145) |
February 22 (145) |
0 |
2280 |
Huge Creek near Wauna |
February 11 (134) |
February 11 (134) |
0 |
347 |
** Greenwater R. at Greenwater missing cumulative flow data from 1978-1993.
*Substantial glaciers in headwaters.
Table 4.
Mean Center of Timing Trend Slope |
|||
1948-2023 CT |
1948-2023 |
||
Streamgage |
Regression Slope |
Significance (p value) |
|
Snow Sourced |
NF Nooksack R. near Glacier* |
-0.290 |
0.001 |
Dungeness R. near Sequim |
-0.400 |
0.004 |
|
Sauk R. near Darrington |
-0.413 |
0.002 |
|
Thunder Cr. near Newhalem* |
-0.131 |
0.017 |
|
Transitional |
Puyallup River near Electron* |
-0.120 |
0.388 |
Greenwater River at Greenwater |
-0.333** |
0.089 |
|
Nisqually River near National* |
-0.194 |
0.219 |
|
Duckabush River near Brinnon |
-0.374 |
0.014 |
|
Skykomish River near Gold Bar |
-0.500 |
0.003 |
|
SF Snoqualmie River nr Garcia (period of record 1962-2023) |
-0.188 |
0.553 |
|
MF Snoqualmie River nr Tanner (period of record 1962-2023) |
-0.371 |
0.123 |
|
Cedar River near Cedar Falls |
-0.268 |
0.119 |
|
Rex River near Cedar Falls |
-0.280 |
0.067 |
|
NF Skokomish River below Staircase Rapids |
-0.427 |
0.001 |
|
NF Snoqualmie River nr Snoqualmie Falls (period of record 1962-2023) |
-0.333 |
0.114 |
|
NF Stillaguamish River near Arlington |
-0.250 |
0.026 |
|
Rain Sourced |
Taylor Creek near Selleck |
0.04 |
0.987 |
Huge Creek near Wauna |
-0.111 |
0.230 |
** Greenwater R. at Greenwater missing cumulative flow data from 1978-1993.
*Substantial glaciers in headwaters.
Numbers in bold signify trend is significant (α < 0.10)
Declining summer flows in the Puget Sound basin are a likely response to a variety of drivers including changes in rainfall, snowfall, temperature, evapotranspiration, land-use conversion, forest practices, and increased 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 the trend.
The streamgages selected for this indicator represent primarily large, minimally disturbed streams and rivers. The CT analysis suggests flows at most of the gages selected for this indicator are sensitive to snowpack changes. Since 1985, the increasing trend in consecutive years with below normal summer flows is consistent across the region. By highlighting gages in largely undisturbed basins, changes in climate dynamics are likely the primary influence on summer flows in these systems.
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.
Georgiadis, N., Bogue, K., DeGasperi, C., 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., Luce C. H., Wenger, S. J., and Berghuijs, W. R., 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.
Mantua, N.J. 1999: The Pacific Decadal Oscillation. A brief overview for non-specialists, Encyclopedia of Environmental Change.
Stewart, I.T., Cayan, D.R., Dettinger, M.D., 2005. Changes toward earlier streamflow timing across Western North America. Journal of Climate, Volume 18: Issue 8.
Vannest, K.J., Parker, R.I., Gonen, O., & Adiguzel, T. (2016). Single Case Research: web-based calculators for SCR analysis. (Version 2.0) [Web-based application]. College Station, TX: Texas A&M; University. Accessed 2/11/2025. https://singlecaseresearch.org/calculators/theil-sen/.
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Source Classification |
Rain, Transitional, Snow
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