Laserfiche WebLink
<br />~, <br /> <br />, <br /> <br />1.2 Description of Study Area <br /> <br />Fourmile Creek originates in the mountains north of the town of Cripple Creek in <br />Teller County. In 1994 three sites downstream of the Cripple Creek and Fourmile Creek <br />confluence were sampled (Table 1 and Figure 1), <br /> <br />In 1995 due to the DOWs need for additional fisheries information, Fourmile Creek <br />was sampled from the headwaters to a point approximately eight river miles upstream of <br />the confluence with the Arkansas River in Canon City, Data from this additional 1995 <br />. . .. -.. " ~,.,' -~ r" ..--.'::::5' .'C' <br />sampling were Included In this report. ". <br /> <br />From 1996 on, the Fourmile Creek aquatic community will be monitored at four sites <br />in a downstream gradient. The upstream control site will be Fourmile Creek upstream of <br />Cripple Creek on the Chapman Ranch. Fourmile Creek downstream of Cripple Creek will <br />be used to evaluate the effects of Cripple Creekwater on Fourmile Creek, Fourmile Creek <br />downstream of the Carlton Tunnel will be sampled to evaluate effects of the tunnel. <br />Fourmile Creek at the Lion's Club stream restoration project (8 miles north of Canon City) <br />will be used as a downstream control site. <br /> <br />'-) <br />':-. , <br />~""""'! <br /> <br />Cripple Creek and Ariqua Gulch will also be sampled each year at the four 1995 <br />DOW sites described in Table 1 and Figure 1., <br /> <br />2.0 Methodology <br /> <br />2.1 Water-Quality <br /> <br />Water-quality samples were collected prior to macroinvertebrate and fish collection. <br />Alkalinity, hardness, conductivity, temperature and pH measurements were performed in <br />the field using titration methodology (Standard Methods 1985), a Yellow Springs <br />Instruments conductivity meter and a Beckman Phi 10 pH meter. Meters were calibrated <br />each time before use, Samples were collected for the analyses of both dissolved and total <br />cadmium, copper, iron, manganese, lead and zinc, A two-ounce aliquot of water from <br />each site was field filtered through a 0.45 micron disposable Nucleopore filter, using a <br />reusable plastic syringe device and analyzed Jor determination of the dissolved metal. <br />Each sample was preserved with 0.5 ml Ultrex nitric acid and placed in ice for <br />transportation to the DOW Fort Collins laboratory for analyses by atomic absorption <br />spectroscopy. <br /> <br />,- <br />l';' ~."', <br />....:~...;.. <br /> <br />A second, two-ounce aliquot was preserved using Ultrex without filtration, iced and <br />transported to the DOW Fort Collins laboratory to be analyzed for total metals. Since this <br />second sample was not digested in a further manner, a better term may be acid leachable <br />fraction. Dissolved metals represent the fraction of each contaminant that is biologically <br />available to aquatic life. The total fraction represents what could realistically become <br />available under anoxic (oxygen-depleted) conditions in nature. A duplicate sample and <br /> <br />2 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />, <br />