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King County Water Quality Monitoring

The Watershed Resource Inventory Area 7 (WRIA 7) Routine Streams Monitoring Program was established during 2011 and consists of twelve sampling sites that are distributed throughout the Snoqualmie and Skykomish watersheds. Historically in King County, routine streams monitoring has been centered on WRIA 8 (Lake Washington/Cedar/Sammamish) and WRIA 9 (Green-Duwamish). However, in 2011, a Surface Water Management (SWM) fee increase allowed King County to expand its regular water quality monitoring efforts to include the King County portions of the WRIA 7 drainage. Objectives of this program are focused on quantifying long-term water quality trends to help inform the management of salmon recovery efforts, land use regulation, and to prepare for expected increases in climate variability.

King County collects monthly water quality samples on Patterson Creek just upstream of the West Snoqualmie Valley Road bridge in the Snoqualmie River Valley. King County is not currently conducting benthic macroinvertebrate or stream sediment monitoring in the WRIA 7 Routine Streams Monitoring Program.


Water Shed Image

Patterson Creek, drains nearly 13,000 acres and is the largest left bank tributary to the Snoqualmie River downstream of Fall City. The subbasin has a broad elevation range from 70 feet above mean sea level to more than 1400 feet in the headwaters (King County, 2004). The mainstem originates in a low-gradient upland catchment with many lateral wetlands that extend nearly the entire length of the stream from Redmond-Fall City Road to the Snoqualmie River confluence (King County, 2004). Patterson Creek flows in a southeasterly direction for most of its length before turning north and intersecting the Snoqualmie River’s floodplain through farmland. Like many other tributaries in the watershed, the lower portions of Patterson Creek lie within an agriculture production district (APD).


Much of Patterson Creek is considered Core summer salmonid habitat by the WDFW that requires special thermal protections . Despite the important designation, fish habitat conditions in the mainstem of Patterson Creek are generally regarded as poor, owing to riparian degradation, fish passage barriers and a lack of large wood in the stream (Haring, 2002). In spite of relatively poor habitat conditions, salmonids are known to make extensive use of the Patterson Creek subbasin. Steelhead and coho salmon use the mainstem and several key tributaries for both spawning and rearing. Chinook also utilize a substantial portion of the mainstem of Patterson Creek (Haring, 2002).

Water Quality

Water quality samples are analyzed monthly for temperature, dissolved oxygen, pH, conductivity, turbidity, total suspended solids, ortho-phosphorus, total phosphorus, ammonia, nitrate-nitrogen, total nitrogen, and fecal coliform 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. Patterson Creek is now categorized as “Core Summer Salmonid Habitat” for aquatic life use and “Primary Contact” for recreational use under the 2003 rules. 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 February 15th through June 15th. Patterson Creek is listed on the 2012 Washington State Department of Ecology's (Ecology) 303(d) list for violations of fecal coliform bacteria, dissolved oxygen, and water temperature standards (Category 4a).

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 Patterson Creek ratings compare with other stream sites, visit the Water Quality Index page.

Table 1. Routine monitoring summary statistics for this station from 2011 to 2018
ParameterNumber of SamplesMeanMinimumMaxmiumMedianStandard Deviation
Dissolved Oxygen (mg/L)889.97.712.09.91.0
Temperature (°C)889.52.614.99.93.5
Turbidity (NTU)775.671.7745.204.056.61
Conductivity (mSIEMS/cm)88129.848.9184.0122.037.9
Total Suspended Solids (mg/L)888.290.90107.005.4012.51
Ortho-Phosphorus (mg/L)880.02240.00890.03970.02280.0074
Total Phosphorus (mg/L)870.04880.02920.09350.04650.0130
Ammonia (mg/L)880.01630.00400.04480.01540.0066
Nitrate (mg/L)880.70280.35601.37000.69500.1758
Total Nitrogen (mg/L)871.01830.71901.77000.95700.1945
Fecal Coliform(CFU/100ML)881513460048505


King County operates several stream gages in the Patterson Creek watershed. Gage 48a is located on the mainstem of Patterson Creek along SE Redmond-Fall City Road near the Aldarra Golf Club (this gage was moved slightly upstream near SE Duthie Hill Rd in January 2013 and is listed as 48AN). Canyon Creek is also gaged at the Aldarra Golf Club (48b). The northern headwaters of Patterson Creek near Redmond-Fall City Road are gaged at 48c. There also is an inactive gage (48t) in the southern headwaters. A rain gage (48u), located near 48c, was relocated in April 2002 and is now referred to as 48Y.

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 web page.

While King County is not conducting benthic macroinvertebrate monitoring on Patterson Creek as part of the WRIA 7 Routine Streams Monitoring, King County (Roads) collected benthic samples on Canyon Creek in 2010. To see this data, please visit the Puget Sound Benthos webpage.