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Silver Creek - Division of Water Quality - Utah.gov

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<strong>Silver</strong> <strong>Creek</strong> <strong>Water</strong>shed TMDL Final Report<br />

6.0 SOURCES<br />

6.1 Known Sources <strong>of</strong> Contaminants<br />

Existing data were adequate for determining contaminant loading between data sampling points<br />

along <strong>Silver</strong> <strong>Creek</strong> (contaminant loading is presented in pounds per mile <strong>of</strong> stream rather than by<br />

responsible parties in Section 4.3). However, sufficient data are unavailable to adequately<br />

allocate contribution <strong>of</strong> contaminants by specific site. Further, there are numerous smaller<br />

source areas not specifically listed in Table 11 that undoubtedly contribute zinc and cadmium to<br />

the creek. Table 11 identifies the major land owners within the various major source areas <strong>of</strong><br />

<strong>Silver</strong> <strong>Creek</strong>. Figure 22 identifies the major contaminated areas, which are referred to as source<br />

areas.<br />

Table 11 : List <strong>of</strong> Known Sources<br />

Description<br />

Owner<br />

Upper <strong>Water</strong>shed Sources<br />

United Park City Mines<br />

Prospector Square groundwater drain Park City Municipal Corporation<br />

<strong>Silver</strong> Maple Claims<br />

BLM<br />

Flood Plain Tailings<br />

United Park City Mines<br />

Richardson Flats<br />

United Park City Mines<br />

Meadow Area<br />

Various Private Land Owners<br />

All indications suggest that the metals <strong>of</strong> concern in this watershed are from historical mining<br />

activities in the Park City area. Most <strong>of</strong> the mining activity occurred within the upper watershed,<br />

primarily within Empire Canyon. Tailings from these mines were stored onsite or removed to<br />

another location, typically downstream.<br />

Several downstream locations were used to further reduce and process the discarded mine<br />

tailings in an attempt to remove additional metals. The lower reaches <strong>of</strong> the stream have<br />

significant amounts <strong>of</strong> mine tailings that are easily detected by the casual observer. These<br />

locations include, but are not limited to, <strong>Silver</strong> Maple Claims, Richardson Flats, Flood Plain<br />

Tailings and the Meadow area.<br />

Contamination mechanisms vary from site to site but are generally attributed to surface or<br />

ground water contact with mining related metals contamination. The upper watershed, due to its<br />

overall steepness, is characterized by relatively high flow velocities and concentrations that have<br />

a tendency to carry sediments and other materials to receiving waters, in this case <strong>Silver</strong> <strong>Creek</strong><br />

and its tributaries. Contaminated areas that are exposed or saturated by shallow ground water<br />

will contribute to metals loading in the stream channels.<br />

The Upper watershed source area includes discharges from two mining tunnels, the Judge and<br />

Spiro Tunnels. The majority <strong>of</strong> these flows are captured for use in the Park City Municipal<br />

drinking water system. Zinc concentrations for these tunnels have been reported at 0.81 mg/l for<br />

the Judge and 0.22 mg/l for the Spiro Tunnel (NPDES Form 2A October 2002). Estimated zinc<br />

loads from the respective tunnel flows that actually enter <strong>Silver</strong> <strong>Creek</strong> are less than 100 lbs. per<br />

year from the Judge Tunnel and 300 lbs. per year from the Spiro Tunnel. These values are not<br />

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