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Water Quality Program Page 3

B. Turbidity and Total Suspended Solids (TSS): Turbidity is a measurement of the visual clarity of a water sample and indicates the presence of fine suspended particulate matter. The unit used to measure turbidity is NTU (nephelometric turbidity units) which measures the absorption and reflection of light when it is passed through a sample of water. Because particles can have a wide variety of sizes, shapes and densities, there is only an approximate relationship between the turbidity of a sample and the concentration (i.e. weight) of the particulate matter present. This is why there are separate tests for NTU turbidity and suspended solids.

Turbidity is an important parameter for assessing the viability of a stream for trout propagation. Trout eggs can withstand only small amounts of silt before hatching success is greatly reduced. For this reason, the standard for trout-designated waters is 10 NTU while the standard to protect other aquatic life is 50 NTU.

 TSS quantifies solids by weight and is heavily influenced by stream flow and land disturbing activities.  Mountain streams in undisturbed forested areas remain clear even after a moderately heavy rainfall event, but streams in areas with disturbed soil will become highly turbid after even a relatively small rainfall. Deposition of silt into a stream bottom can bury and destroy the complex bottom habitat. Consequently, the habitat for most species of aquatic insects, snails, and crustaceans is destroyed by stream siltation. The absence of these species reduces the diversity of the ecosystem. In addition, small amounts of bottom-deposited sediment can severely reduce the hatch rate of trout eggs. There is no legal standard for TSS, but values below 30.0 mg/l are generally considered low, and values above 100 mg/l are considered high. A good measure of the upstream land use conditions is how much TSS rises after a heavy rainfall.

These graphs show median turbidity levels and total suspended solids concentrations for each site compared with the average median for the eight-county VWIN region.  In the past year sample collection occurred twice at a period when rains affected the streams.  On several other occasions the streams were high from rains that had occurred in previous days, but the streams had already had sufficient opportunity to clear before samples were collected.  On the two occasions when samples were most affected by sediment runoff, the sites most affected were Mill Creek, Pine Creek, and Cedar Creek.  Mill Creek and Pine Creek are at the northwestern end of the lake and Cedar Creek is at the southeastern end.  Hurricane Creek, the upstream site on Norton Creek and Glenville Creek have been relatively unaffected by sediment runoff.  The downstream site on Norton Creek has been only slightly affected by sediment runoff.

Cedar Creek also exhibits the highest median turbidity levels and sediment concentrations and also exceeds the average median for the region in both categories.  The median sediment concentrations at Mill Creek also exceed the average median for the region.  The sources of sediment to these streams should be investigated. Regionally, the most common sources are unpaved roads, construction sites, bank erosion, and agriculture, particularly livestock.

 

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