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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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Figure AX7-2.2.6. Frequency distribution <strong>of</strong> ambient and natural levels <strong>of</strong> surface water<br />

dissolved lead (µg/L).<br />

Due to the preponderance <strong>of</strong> non-detectable (ND) measurements, assessing national trends<br />

in surface water-dissolved Pb concentrations was not possible. However, areas with elevated Pb<br />

concentrations were identified by classifying the data with detectable Pb concentrations above<br />

and below the 99th percentile. The 99th percentile (versus the 95th percentile) was chosen in<br />

this instance to represent extreme conditions given the small window <strong>of</strong> variability in the dataset.<br />

By convention, the 95th percentile was used in subsequent analyses <strong>of</strong> this type. Areas with high<br />

surface water Pb concentrations were observed in Washington, Idaho, Utah, Colorado, Arkansas,<br />

and Missouri (Figure AX7-2.2.7). The maximum measured Pb concentration was located in<br />

Canyon Creek at Woodland Park, ID, a site classified as mining land use.<br />

Sediment<br />

There were approximately one-half <strong>of</strong> the number <strong>of</strong> surface water data available <strong>for</strong><br />

sediments (N = 1466). In contrast to the surface water data, however, very few sediment data<br />

were below the detection limit (7/1466 ambient ND, 3/258 natural ND; Table AX7-2.2.3).<br />

As expected, the mean ambient Pb concentration was higher than the mean natural Pb<br />

AX7-131

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