Stream report for
--pick a locator--
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 Juanita 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 Juanita Creek. Station 0446 is located at the USGS gauging station north of Juanita Park and has been monitored since 1975. Station C446 is located at the bridge on NE 128th, east of 100th NE. Monitoring at this station began in 1976 and continued until 2008 when budget cutbacks forced King County to reduce the breadth of its water quality monitoring program.Sediment samples have been collected from Juanita Creek as part of the Streams Sediment Monitoring Program starting in 1987. King County began collecting benthic macroinvertebrate samples in Juanita Creek in 2010.
From time to time special studies have been conducted at various streams in King County. (
Click here for information about Special Studies involving Juanita Creek.)
The mainstem of Juanita Creek originates east of Interstate 405, and flows approximately five miles west and south entering Lake Washington on the west side of Juanita Beach Park. The Juanita Creek drainage basin is roughly 4,000 acres. There are three main tributaries flowing into Juanita Creek, an upper West (Simonds Tributary), a lower West, and a lower East (Totem Lake Tributary).
Land use in the area has changed rapidly over the last 20 years. In 1981 only 40 percent of the basin was characterized as being "urban/suburban" (
PSCOG, 1981). Since then, much of the basin has been developed and the basin is now described as "highly developed" ( Greater Lake Washington Technical Committee. August 22, 2001).
Historically, cutthroat trout have been found throughout the basin along with small populations of coho and chinook salmon. Electro fishing conducted in 1998 found both coho salmon and cutthroat trout (
Kerwin 2001). Both species are believed to use the entire length of the mainstem of Juanita Creek from Lake Washington to Interstate 405. Volunteers in the King County Salmon Watcher Program have consistently sighted kokanee, sockeye, and coho salmon. Cutthroat trout have also been spotted on occasion.
In 1989 Juanita Creek was rated as "fair" for salmon habitat suitability condition (
METRO September 1990). Removal of riparian vegetation during development in the basin was cited as a primary factor leading to declining habitat conditions. In-stream habitat complexity is significantly degraded and measures of complexity factors (e.g. large woody debris, channel form, pool quality) show lower frequencies than values determined for "natural" conditions ( Kerwin 2001).
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. Juanita Creek is now categorized as “Core Summer Salmonid Habitat” for aquatic life use and “Extraordinary Contact” for recreational 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. Both sampling sites in Juanita Creek are listed on the 2012 Washington Department of Ecology’s (Ecology) 303(d) list 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.
To view charts of current data for Juanita 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 has declined over this 25-year period with significant increases in water temperatures and conductivity at both sampling sites. Other indications of declining water quality are a decrease in DO at the mouth (0446) and a decrease in pH upstream (C446). Decreased total suspended solids (TSS), and decreased nutrient concentrations (ortho-phosphorus and total nitrogen) at both sites indicate some improvements in water quality in the same 25-year period. In addition, fecal coliform bacteria decreased at the mouth of the creek and nitrate-nitrogen decreased at the upstream station.
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 Juanita Creek ratings compare with other stream sites, visit the
Water Quality Index page.
Table 1. Routine monitoring summary statistics for this station from 1975 to 2014
Parameter Number of Samples Mean Minimum Maxmium Median
Dissolved Oxygen (mg/L) 218 10.3 6.5 13.1 10.4 1.2
Temperature (oC) 431 11.8 1.2 19.1 12.6 3.8
Turbidity (NTU) 327 6.24 0.10 120.00 2.25 12.07
pH 269 7.42 6.47 9.50 7.44 0.27
Conductivity (mSIEMS/cm) 190 186.8 56.3 256.0 196.0 36.5
Total Suspended Solids (mg/L) 359 20.22 0.50 2486.70 3.10 134.73
Ortho-Phosphorus (mg/L) 360 0.0299 0.0022 0.1180 0.0269 0.0163
Total Phosphorus (mg/L) 362 0.0662 0.0110 1.3090 0.0498 0.0799
Ammonia (mg/L) 314 0.0318 0.0060 0.3400 0.0230 0.0334
Nitrate (mg/L) 361 1.2570 0.2770 2.3200 1.2700 0.3681
Total Nitrogen (mg/L) 266 1.4714 0.7330 2.5000 1.4700 0.2877
Fecal Coliform(CFU/100ML) 440 641 0 11000 270 1225
Table 2. Storm water monitoring summary statistics for this station from 1975 to 2014
Parameter Number of Samples Mean Minimum Maxmium Median
Dissolved Oxygen (mg/L) 42 10.6 8.4 13.9 10.6 1.3
Temperature (oC) 58 10.4 4.2 17.4 10.1 3.2
Turbidity (NTU) 51 27.42 3.30 365.00 14.00 53.32
pH 54 7.24 6.40 8.30 7.23 0.33
Conductivity (mSIEMS/cm) 30 118.9 56.3 180.0 120.0 34.6
Total Suspended Solids (mg/L) 59 70.86 4.50 608.00 36.80 103.02
Ortho-Phosphorus (mg/L) 59 0.0287 0.0127 0.1220 0.0227 0.0187
Total Phosphorus (mg/L) 59 0.1428 0.0325 0.7350 0.0950 0.1275
Ammonia (mg/L) 53 0.0429 0.0120 0.1710 0.0360 0.0311
Nitrate (mg/L) 59 0.6816 0.3190 1.4000 0.6500 0.2336
Total Nitrogen (mg/L) 57 1.2242 0.7520 2.3900 1.1800 0.3014
Fecal Coliform(CFU/100ML) 59 2096 95 8000 1700 1925
King County maintains three streamflow gauges on Juanita Creek: Juanita Creek at the mouth (
27a), Juanita Tributary 0236 above Simonds R/D ( 27e), and Juanita Tributary 0241 above High Woodlands ( 27f) and one water temperature gauge: Juanita Creek Rain Gauge ( 27u).
Sediment samples were collected from four stations approximately a mile apart, along a four mile reach of Juanita Creek in the summer of 2005 (
see Map). Nickel concentrations in samples at all four sites were above the Sediment Cleanup Objective (SCO). AVS/SEM ratios suggest metals are bioavailable at all sites, except the most downstream site (0466).
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 Juanita Creek, please visit the
Puget Sound Benthos webpage.
Swimming Beach Monitoring
Juanita Creek is monitored in the summer as part of the summer
swimming beach bacteria monitoring program.
Streams Toxicity/Pesticide Study
In 1999, King County conducted a
pesticide study on Juanita, Lyon, and Lewis creeks. The County collected water samples for analysis of pesticides, other organic compounds, metals, suspended solids, and toxicity ( Ceriodaphnia dubia - a zooplankton, and Selenastrum capricornutum- an algae). A total of 24 pesticides were detected over the course of the year in Juanita Creek. Toxicity to S. capricornutum was observed in the Juanita creek samples during spring, summer and early fall. Toxicity observed during the spring sampling event appeared to be associated with copper. The cause of toxicity during the rest of the year was unclear; however, it was associated with the particulate fraction of the samples.
Habitat Inventory and Assessment
In August of 2000, habitat on Juanita Creek was assessed using methods derived from standard assessment protocols. The goals of the assessment project for Juanita Creek were threefold: (1) characterize instream and riparian habitat quality - primarily for salmonids; (2) establish a baseline for future evaluation of trends in habitat quality and watershed function; and (3) provide information for process of prioritizing areas for restoration and preservation. The habitat assessment results indicate that channel and habitat structure in a number of the Juanita Creek segments are degraded relative to values from published "properly functioning conditions" for the Puget Sound or the Pacific Northwest region. This decreased quality of slow water rearing habitat may limit juvenile carrying capacity as well as hinder upstream migration by adult salmon. More information about this assessment can be found in the
Habitat Inventory and Assessment of Juanita Creek in 2000 Report.
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.