Figures & data
Figure 1. Lake Sammamish and tributary streams on the east and west side and Issaquah Creek subbasins.
![Figure 1. Lake Sammamish and tributary streams on the east and west side and Issaquah Creek subbasins.](/cms/asset/cf268887-e476-4e1b-b98c-bcd157683a84/ulrm_a_1606868_f0001_b.jpg)
Figure 3. Total single family, multifamily, and commercial developed land in the Sammamish watershed from 1900 to 2011 based on total “as-built” area in hectares for the specified time period.
![Figure 3. Total single family, multifamily, and commercial developed land in the Sammamish watershed from 1900 to 2011 based on total “as-built” area in hectares for the specified time period.](/cms/asset/40bbd026-3aa8-4373-8575-b611fa50fdba/ulrm_a_1606868_f0003_b.jpg)
Figure 4. Mean annual whole-lake volume-weighted TP and SRP. TP data compared with lake management goal of 22 µg/L and projected full build-out (Perkins et al. Citation1997). Arrow indicates wastewater diversion in 1968. Note: Data for 1964–1966 from METRO (Isaac et al. Citation1966); 1970–1975 from University of Washington (UW) Department of Civil Engineering (Welch Citation1977, Welch et al. Citation1980); 1982–2011 from King County (Welch and Bouchard Citation2014). Summer data only in 1981 so not included in annual means. Significant declining TP 1964–2011 (P < 0.01) and SRP 1982–2011 (P < 0.01). No significant trends in TP 1982–2011 or 1995–2011 (P > 0.10).
![Figure 4. Mean annual whole-lake volume-weighted TP and SRP. TP data compared with lake management goal of 22 µg/L and projected full build-out (Perkins et al. Citation1997). Arrow indicates wastewater diversion in 1968. Note: Data for 1964–1966 from METRO (Isaac et al. Citation1966); 1970–1975 from University of Washington (UW) Department of Civil Engineering (Welch Citation1977, Welch et al. Citation1980); 1982–2011 from King County (Welch and Bouchard Citation2014). Summer data only in 1981 so not included in annual means. Significant declining TP 1964–2011 (P < 0.01) and SRP 1982–2011 (P < 0.01). No significant trends in TP 1982–2011 or 1995–2011 (P > 0.10).](/cms/asset/82170d4e-1fc8-41b0-99f5-0f48bcc3482e/ulrm_a_1606868_f0004_c.jpg)
Table 1. Mean annual whole-lake, winter whole-lake, summer hypolimnion (Jun–turnover), and summer epilimnion (Jun–Sep) total phosphorus (TP) during equivalent periods. All values are volume-weighted (µg/L). Wastewater diversion was in 1968.
Figure 5. Volume-weighted mean summer hypolimnetic (Jun–turnover) TP and SRP and maximum TP (triangles). Arrow indicates wastewater diversion in 1968. Data for 1964–1966 from METRO (Isaac et al. Citation1966); 1970–1975 from UW Department of Civil Engineering (Welch Citation1977, Welch et al. Citation1980); 1982–2011 from King County (Welch and Bouchard Citation2014). Significant declining TP 1964–2011 (P < 0.01) and 1981–2011 (P < 0.05); SRP 1982–2011 (P < 0.01).
![Figure 5. Volume-weighted mean summer hypolimnetic (Jun–turnover) TP and SRP and maximum TP (triangles). Arrow indicates wastewater diversion in 1968. Data for 1964–1966 from METRO (Isaac et al. Citation1966); 1970–1975 from UW Department of Civil Engineering (Welch Citation1977, Welch et al. Citation1980); 1982–2011 from King County (Welch and Bouchard Citation2014). Significant declining TP 1964–2011 (P < 0.01) and 1981–2011 (P < 0.05); SRP 1982–2011 (P < 0.01).](/cms/asset/1dfa2202-1d5e-48d9-a210-a2e544cd558f/ulrm_a_1606868_f0005_c.jpg)
Table 2. Mean (± SD) sediment P release rates in mg/m2 per day for equivalent time periods. Wastewater diversion was in 1968.
Figure 6. Mean summer (Jun–Sep) epilimnetic TP and SRP concentrations. Arrow indicates wastewater diversion in 1968. No significant trends.
![Figure 6. Mean summer (Jun–Sep) epilimnetic TP and SRP concentrations. Arrow indicates wastewater diversion in 1968. No significant trends.](/cms/asset/95445f0b-8295-4aea-9ad1-20cebda853af/ulrm_a_1606868_f0006_b.jpg)
Figure 7. Mean annual whole-lake specific conductance (µS/cm) and alkalinity (mg/L CaCO3). Alkalinity for 1984 and 1989 not included due to insufficient data. Alkalinity averaged 33 mg/L in the early 1970s (Welch Citation1977). Significant increasing trends for both parameters (P < 0.01).
![Figure 7. Mean annual whole-lake specific conductance (µS/cm) and alkalinity (mg/L CaCO3). Alkalinity for 1984 and 1989 not included due to insufficient data. Alkalinity averaged 33 mg/L in the early 1970s (Welch Citation1977). Significant increasing trends for both parameters (P < 0.01).](/cms/asset/9e1d8c13-0858-4764-b691-3891446126fa/ulrm_a_1606868_f0007_b.jpg)
Table 3. Impervious area (ha) in the east, west, and Issaquah basins in 1991 compared with 2011 using the 1991 and 2011 NOAA Coastal Change Analysis Program (C-CAP) data.
Table 4. Mean (±SD) summer (Jun–Sep) epilimnetic TP and Chl-a in µg/L, and Secchi disk transparency (m) during equivalent time periods. Pre-1995 data from King County (Citation1995). Wastewater was diverted in 1968.