Stream report for
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Little Bear Creek-0478
Little Bear Creek-S478
Middle Fork Snoqualmie-MFk_Snq
North Fork Snoqualmie-NFk_Snq
Pine Lake Creek-A680
South Fork Snoqualmie-SFk_Snq
King County Water Quality Monitoring
King County monitors the ecological health of Kelsey Creek in a variety of ways including collecting and analyzing water, sediment, and benthic invertebrate samples. Water quality samples have been collected monthly from two sites along on the creek. Station 0444 (previously referred to as Mercer Slough in some reports) is located at the mouth of Kelsey creek at the gauging station located off Interstate 405, under the trestle near the Richards Road exit. Sampling at this site began in 1977 and continued until 2008 when budget cutbacks forced King County to reduce the breadth of its water quality monitoring program. Regular monitoring at this site resumed in February 2008.
Station D444 is located at the footbridge in the northeast quarter of Kelsey Creek Park and was sampled for water quality from 1977-2008. Sediment samples have been collected from Kelsey Creek as part of the Streams Sediment Monitoring Program starting in 1987. King County began collecting benthic macroinvertebrate samples in Kelsey Creek in 2002.
From time to time additional studies will be conducted on Kelsey Creek. Click here for more information about these
Special Studies of Kelsey Creek.
The Kelsey Creek basin comprises approximately 10,870 acres and has several streams draining west into the east channel of Lake Washington at Interstate 90. The basin includes over 19 miles of open stream encompassing Mercer Slough, Sturtevant Creek, Kelsey Creek, Valley Creek, the West Tributary, Goff Creek, Richards Creek, East Creek, and Sunset Creek. The mainstem of Kelsey Creek originates in the Phantom and Larsen Lake wetlands. Historically, the creek originated from Phantom Creek and Phantom Lake, but early pioneers redirected the Phantom Lake outlet to Lake Sammamish in the late 1880s ( KCM 1993).
Land use in the Kelsey Creek basin is 37 percent single family residential, 22 percent open space, 13 percent multi-family residential, 13 percent public roads, 8 percent commercial/office, 6 percent institutional/government, <1 percent industrial, and mixed use (
Kerwin 2001). Kelsey Creek Park, within the central part of the City of Bellevue encompasses 150 acres of forest and wetland habitat.
The Kelsey Creek basin area is considered to have reached built-out conditions and future development will be predominantly redeveloping existing properties. An analysis of vegetation in 2000 found 7 percent forest canopy, 38 percent green vegetation, and the rest of the watershed in unvegetated land cover such as impervious area and bare soils.
The suitability of Kelsey Creek for salmonids was rated as "fair" overall in 1989 (
Metro 1990). Impacts from high stormwater flows and sedimentation were cited as the primary factors for declining conditions. Numerous hydrology studies have been done on Kelsey Creek. The University of Washington evaluated the hydrologic impacts of human development in the Kelsey Creek basin using historical land development patterns (Richey et al, 1981). They found that the monthly average volume of flow had increased only slightly with urban development but the storm peaks increased two to three times over the same historical period ( Kerwin 2001). The City of Bellevue now operates six in-stream, regional detention facilities.
Volunteers with the
Salmon Watcher Program have been observing salmon at various locations throughout the basin since 1996. Chinook, coho, and sockeye salmon have been consistently observed in the basin. Less commonly seen are cutthroat trout and chum salmon. Issaquah Hatchery coho stock are planted at various life history stages throughout the basin ( Kerwin 2001).
The City of Bellevue sponsored juvenile fish surveys in four of the sub-basins in 1996 and 1997 (
Kerwin 2001). In 1996, eight fish species were observed in the Kelsey Creek basin: cutthroat, coho, rainbow, sculpins, lamprey, dace, sucker, and bluegill. Coho were observed at all sampling locations, but numbers were low, averaging seven coho per 50-meter reach. Cutthroat trout were present in fairly high numbers in all sampling locations. Similar findings were noted, when the study was replicated in 1997.
Water quality samples are analyzed monthly for temperature, dissolved oxygen (DO), pH, conductivity, turbidity, total suspended solids, ortho-phosphorus, total phosphorus, ammonia, nitrate-nitrogen, total nitrogen, and fecal coliform bacteria (FC). Results are compared to State water quality standards. Water quality standards are designed to protect public health and aquatic life. Comparing monitoring results to water quality standards allows an understanding of how safe the creek is for recreational contact as well as for aquatic life. (See link at top of page to view current water data.)
State water quality standards were revised in 2003. Kelsey Creek is now categorized as “Core Summer Salmonid Habitat” for aquatic life use. As part of the updated water quality standards the creek has been assigned an additional “Supplemental Spawning and Incubation Protection” temperature criteria of 13 ºC to be applied from September 15th through May 15th. Kelsey Creek is designated as “Extraordinary Contact” for recreational use. Both sampling sites in Kelsey Creek are listed on the 2012 Washington Department of Ecology’s (Ecology) 303(d) list for violation of dissolved oxygen (DO), temperature, and fecal coliform (FC) bacteria standards ( Category 5). See Table 1 for a summary of water quality violations in the creek during the most recent water year.
The water quality in Kelsey Creek was characterized as fair in 1989 (Metro 1990). The creek was described as having been impacted by high storm flows that resulted in degraded spawning habitats. To view charts of current data for Kelsey Creek, visit the links above.
A 25-year (1979 – 2004) trend analysis was conducted with baseflow water quality data showed some significant changes in the water quality since 1979. Water quality declined during this time period as indicated by significant increases in water temperatures and conductivity at both sampling sites. Other indications of declining water quality are a decrease in DO and pH at the mouth (0444) and an increase in nitrate-nitrogen upstream (D444). Decreased total suspended solids (TSS), and ortho-phosphorus at both sites indicate some improvements in water quality in the same 25-year period. In addition, ammonia and nitrate-nitrogen, and fecal coliform bacteria decreased at the mouth of the creek.
Water Quality Index
A Water Quality Index (WQI) rating system was developed by the State Department of Ecology that evaluates several water quality parameters and gives a single rating of “high,” “moderate,” or “low” water quality concern. To see how Kelsey Creek ratings compare with other stream sites, visit the
Water Quality Index page.
Table 1. Routine monitoring summary statistics for this station from 1977 to 2014
Parameter Number of Samples Mean Minimum Maxmium Median
Dissolved Oxygen (mg/L) 161 9.3 5.1 13.0 9.2 1.5
Temperature (oC) 320 10.6 -1.0 19.7 10.7 4.2
Turbidity (NTU) 321 4.63 0.60 135.00 2.72 8.82
pH 216 7.29 6.50 8.20 7.30 0.28
Conductivity (mSIEMS/cm) 130 204.2 98.0 255.0 210.0 34.5
Total Suspended Solids (mg/L) 320 6.96 0.70 116.00 3.30 12.72
Ortho-Phosphorus (mg/L) 319 0.0495 0.0196 0.1300 0.0470 0.0174
Total Phosphorus (mg/L) 321 0.0853 0.0190 0.4910 0.0774 0.0392
Ammonia (mg/L) 288 0.0309 0.0070 0.2620 0.0250 0.0261
Nitrate (mg/L) 319 0.6055 0.1010 2.7000 0.6000 0.2275
Total Nitrogen (mg/L) 218 0.8914 0.2740 1.8400 0.8975 0.2136
Fecal Coliform(CFU/100ML) 319 472 0 14700 180 1216
Table 2. Storm water monitoring summary statistics for this station from 1977 to 2014
Parameter Number of Samples Mean Minimum Maxmium Median
Dissolved Oxygen (mg/L) 37 8.5 5.5 11.0 8.3 1.6
Temperature (oC) 53 10.6 4.1 17.4 10.5 3.2
Turbidity (NTU) 54 11.23 2.40 37.10 9.88 7.15
pH 53 7.03 6.50 7.60 7.00 0.28
Conductivity (mSIEMS/cm) 30 94.8 41.0 193.0 88.0 33.8
Total Suspended Solids (mg/L) 54 22.56 2.90 105.00 17.45 19.72
Ortho-Phosphorus (mg/L) 54 0.0490 0.0207 0.2200 0.0416 0.0312
Total Phosphorus (mg/L) 54 0.1221 0.0500 0.4080 0.1075 0.0694
Ammonia (mg/L) 38 0.0697 0.0100 1.7000 0.0185 0.2723
Nitrate (mg/L) 54 0.4140 0.2500 0.9640 0.3890 0.1384
Total Nitrogen (mg/L) 52 0.9039 0.6040 2.3000 0.8150 0.3223
Fecal Coliform(CFU/100ML) 53 1580 50 7300 1000 1678
King County maintains a stream gage on Kelsey Creek at the NE 8th Street crossing in the city of Bellevue (
Sediment data were collected from Kelsey Creek as part of the
Stream Sediment Monitoring Program from 1987 through 2002. Data analysis identified no significant trends for any of the parameters tested.
Basin-wide sampling took place in 2007, including six sites along the Kelsey Creek reach. At sites F444, H444 and I444, concentrations of bis(2-ethylehexyl)phthalate (an ubiquitous chemical found in many plastics) exceeded the Sediment Cleanup Objective (SCO), meaning effects to sediment-dwelling animals are possible, but uncertain. At site H444, concentrations of arsenic, cadmium and nickel also exceeded SCO. Site I444 also had concentrations of dieldrin (an organochlorine pesticide) that exceeded the Cleanup Screening Level (CSL), meaning that adverse effects to sediment-dwelling animals are likely. AVS/SEM analysis suggests that metals were not bioavailable at site H444, where metals exceeded guideline concentrations.
Benthic macroinvertebrates are small animals visible to the naked eye (macro) that lack a backbone (invertebrate)
and live in or around the streambed (benthic). This group includes aquatic insects (such as mayflies and dragonflies),
crustaceans, clams, snails, and worms. Benthic macroinvertebrates are of interest to scientists and water resource
managers because they are an excellent indicator of the biological health of stream ecosystems and are a critical
component of the food web in aquatic communities. Scientists quantify the composition and diversity of benthic
macroinvertebrate populations in a stream to compare the biologic integrity of different streams. King County has utilized
benthic macroinvertebrate sampling to assess biological health of numerous creeks across the county
For more information about benthic macroinvertebrates and King County’s Benthic Macroinvertebrate Program, please visit the
King County Stream Bug Monitoring web page.
To see the benthic macroinvertebrate data for Kelsey Creek, please visit the
Puget Sound Benthos webpage.
Water Resources Inventory Area (WRIA) 8
In WRIA 8, citizens, scientists, businesses, environmentalists and governments are cooperating on protection and restoration projects and have developed a science-based plan to conserve salmon today and for future generations. Visit the
WRIA 8 Web page to see how this creek is part of this WRIA 8 planning process