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King County Water Quality Monitoring

King County monitors the ecological health of Mill Creek in a variety of ways, including collecting and analyzing water, sediment, and benthic invertebrate samples. Station A315 is located at the bridge at 68th Ave and South 261st Street. Water quality samples were collected from 1979 to 2008 when budget cutbacks forced King County to reduce the breadth of its water quality monitoring program. Sampling at this site resumed in February 2013. Beginning in 1987, sediment quality samples have been collected from this site. King County began collecting benthic macroinvertebrate samples in 2002 to monitor stream health.

From time to time additional studies have been conducted on Mill Creek. Click here for information about Special Studies of Mill Creek.


Water Shed Image The Mill Creek watershed (sometimes referred to as Hill Creek in literature) is located in South King County in WRIA 9. The watershed is roughly 22 square miles in size and includes portions of the cities of Kent, Auburn, Algona, and Federal Way (Kerwin and Nelson, 2000; Herrera, 2005). The creek originates from Lake Doloff and Lake Geneva in the west Green River Valley and flows through the steep Preasley Canyon before entering the Green River at River Mile (RM) 23.9. The creek is approximately 8.35 miles long (note: there is another Mill Creek located within WRIA 9 that drains into Springbrook Creek further downstream on the Green River).

Historically, Mill Creek has served as an important flood storage area as water is conveyed from nearby wetlands to the Green River (Kerwin and Nelson, 2000). The creek has provided important refuge for fish during periods of high winter flows. Several studies related to flood control have been produced in the last 40 years (Kerwin and Nelson, 2000). Land use in the Mill Creek watershed consists of forested and residential land in the upper basin, and residential and agricultural in the lower basin (Herrera, 2005).

For more information about the Mill Creek watershed, please visit the WRIA 9 website for the Lower Green River Subwatershed.


Coho, chum, and winter steelhead have been observed spawning in Mill Creek. Juvenile coho, chum, winter steelhead, cutthroat, and Chinook have been captured in the creek (Kerwin and Nelson, 2000). The Lower Green River Baseline Habitat Survey Report (Anchor Environmental, 2004) provides detailed information about fisheries habitat conditions in the Mill Creek area.

Water Quality

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 (FC) bacteria. 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. Mill (Hill) Creek is now categorized as “Salmonid Spawning, Rearing and Migration Habitat” for aquatic life use, and “Primary Contact” for recreational use. As part of the updated water quality standards, portions of Mill Creek have been assigned an additional “Supplemental Spawning and Incubation Protection” temperature criteria of 17.5 °C. The creek is on the Washington State Department of Ecology’s (Ecology) 303(d) list for violation of FC bacteria, zinc, pH, and bioassessment standards (Category 5). The creek has an EPA-approved Green River Temperature Watershed total maximum daily load (TMDL) plan in place and implemented (Category 4a). See Table 1 for a summary of water quality violations in the creek during the most recent water year.

Water quality conditions in Mill Creek have historically been characterized as poor due to high temperatures, low DO, high nutrient concentrations, and high FC bacteria counts (Metro, 1989).

Long-term Trends

A 25-year (1979 – 2004) trend analysis was conducted with water quality data collected from the mouth of Mill Creek. This analysis shows some improvements in water quality since 1979. Turbidity, total suspended solids, ortho-phosphorus, total phosphorus, ammonia, nitrate-nitrogen, and FC bacteria have all shown a significant decrease; and DO concentrations have increased significantly in this 25 year time period. In contrast, pH values have shown a significant decrease, but have remained within acceptable range relative to the state standards. While these trends indicate improvements in water quality since 1979, another water quality data assessment conducted for the Green-Duwamish River in 2003 found that Mill (Hill) Creek still had low DO concentrations and high ortho-phosphorus and FC bacteria counts relative to the rest of the Green-Duwamish watershed (Herrera, 2005).

Water Quality Index

A Water Quality Index (WQI) rating system was developed by Ecology that evaluates several water quality parameters and gives a single rating of “high,” “moderate,” or “low” water quality concern. To see how these ratings compare with other stream sites, please visit the Water Quality Index webpage.

Table 1. Routine monitoring summary statistics for this station from 1977 to 2018
ParameterNumber of SamplesMeanMinimumMaxmiumMedianStandard Deviation
Dissolved Oxygen (mg/L)2207.33.612.47.11.4
Temperature (°C)35710.90.520.911.14.7
Turbidity (NTU)35410.580.4089.808.2010.55
Conductivity (mSIEMS/cm)193217.446.8379.0215.055.7
Total Suspended Solids (mg/L)3559.970.50174.006.9013.67
Ortho-Phosphorus (mg/L)3540.07600.00782.42000.04310.1463
Total Phosphorus (mg/L)3550.14990.00702.90000.11300.1835
Ammonia (mg/L)3550.17260.00889.81000.06460.6476
Nitrate (mg/L)3540.46290.01401.69000.43200.2606
Total Nitrogen (mg/L)2721.07880.379013.60000.95150.9613
Fecal Coliform(CFU/100ML)3537925460001902937

Table 2. Storm water monitoring summary statistics for this station from 1977 to 2018
ParameterNumber of SamplesMeanMinimumMaxmiumMedianStandard Deviation
Dissolved Oxygen (mg/L)447.13.310.17.41.5
Temperature (°C)6410.22.917.89.33.5
Turbidity (NTU)6314.161.9077.0011.9011.53
Conductivity (mSIEMS/cm)33153.873.0273.0131.065.1
Total Suspended Solids (mg/L)6421.063.00119.0016.4519.15
Ortho-Phosphorus (mg/L)630.10970.01680.47700.06840.0955
Total Phosphorus (mg/L)630.21880.03980.76600.17200.1360
Ammonia (mg/L)630.17120.01301.70000.08280.3085
Nitrate (mg/L)630.51500.08501.23000.51000.2396
Total Nitrogen (mg/L)611.30520.55203.65001.21000.5540
Fecal Coliform(CFU/100ML)62234937170009703118


King County has operated several stream and rain gages in the Mill Creek watershed.

Stream gages: near its confluence with the Green River at route 181 (41a - inactive since 2006); at 29th Ave NW (41b - inactive since 1992); at Peaseley Canyon Road (41c); Mullen Slough at 277th St (41D2); Lower Green West Tributary 0049 at S 272nd WY (41e)

Rain gages: at Star Lake (41u); at Lake Dolloff (41v)

US Geological Survey stream gages: at Earthworks Park in Kent, WA (12113347); near mouth at Orillia, WA (12113349)

Stream Sediment

In 2010, eight samples were collected along the Mill Creek reach in Auburn. Arsenic concentrations at sites ED315, FR315, TS315, and UH315 exceeded the Sediment Cleanup Objective (SCO). This means adverse effects in benthic animals are possible, but uncertain. Concentrations of bis(2-ethylehexyl)phthalate (a ubiquitous chemical found in many plastics) also exceeded the SCO at sites ED315, FR315, PR315, and TS315. Another phthalate, di-n-octyl phthalate, exceeded the SCO at site FR315. Nickel concentrations exceeded the SCO at sites PR315 and UH315. Additional data (acid volatile sulfide/simultaneous extracted metals ratio) suggests that among sites where metal concentrations exceeded the SCO, metals are only bioavailable at FR315 and PR315.

Benthic Invertebrates

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 (see map).

For more information about benthic macroinvertebrates and King County’s Benthic Macroinvertebrate Program, please visit the King County Stream Bug Monitoring webpage. To see the benthic macroinvertebrate data for Mill Creek, please visit the Puget Sound Benthos webpage.

Special Studies

Green-Duwamish Water Quality Assessment

In 2001, King County initiated a separate comprehensive study of the Green-Duwamish Watershed, called the Green-Duwamish Watershed Water Quality Assessment (GDWQA). Several reports evaluate data collected as part of the GDWQA. Mill Creek is included in this analysis. More information about the GDWQA, as well as the reports, can be found at the Green - Duwamish Water Quality Assessment website.