Hatcher Pass Water Quality Sampling Report (May 2008 Through February 2009)

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Hatcher Pass Water Quality Sampling Report (May 2008 Through February 2009) Hatcher Pass Water Quality Sampling Report (May 2008 through February 2009) Prepared for the Matanuska-Susitna Borough by Jeffrey C. Davis and Gay A. Davis P.O. Box 923, Talkeetna, AK 99676 (907) 733.5432 www.arrialaska.org April 2009 Aquatic Restoration and Research Institute Hatcher Pass 2008 Report Aquatic Restoration and Research Institute Hatcher Pass 2008 Report Summary Seasonal water chemistry and biological sampling was conducted at five Little Susitna River sampling locations from the Goldmint Trailhead to Edgerton Park Road in Hatcher Pass. This study provided the fourth year of water quality data. Water samples collected in May, August, October, and February were analyzed for total fecal coliform bacteria, ammonia nitrogen, nitrate plus nitrite nitrogen, pH, specific conductivity, and turbidity. August samples were analyzed for aromatic hydrocarbons. Stream macroinvertebrates were sampled at three locations and analyzed using the ASCI methods as a biotic measure of water quality. Data loggers were used to measure and record water temperatures. Stream water nutrient concentrations were generally consistent with previous years. Ammonia nitrogen concentrations were high downstream from the sampling location at Mile Post 12 to the Edgerton Park Road Bridge. However, previous similarly high values were observed in 2005. Nitrate nitrogen concentrations decreased during the growing season, but not to the degree previously recorded. Decreasing summer nitrate concentrations are most likely related to uptake by terrestrial vegetation. Cooler air temperatures and cloudy days may have reduced terrestrial vegetation uptake of nitrate resulting in higher stream concentrations. These cooler temperatures were reflected in measures of water temperature, which were lower than recorded in 2007. Discharge recorded by the U.S.G.S gauging station showed rising flow during the summer related to glacial melting but no large fall increases due to storms as seen in previous years. The hydrograph likely explains the moderate increases in turbidity up to 3 NTU and no large drop in pH during storm events as seen in prior years. In addition, the fecal coliform bacteria counts remained low. Concentrations of hydrocarbons remained below detection limits in August samples. The macroinvertebrate community showed an increase in water quality likely reflecting a recovery from the August 2006 flood. Water quality sampling in 2008 demonstrated the range of natural variability in water chemistry and biotic measures. Understanding the range of natural variability and the related environmental factors will provide for clearer evaluation of potential changes in water quality due to increased development or recreational uses. An additional year of data should be collected to adequately describe reference water quality within the Little Susitna River in Hatcher Pass. Aquatic Restoration and Research Institute Hatcher Pass 2008 Report Introduction The Little Susitna River is within the Cook Inlet Ecoregion (Gallant et al. 1995). The Cook Inlet Ecoregion includes portions of the Kenai Peninsula, the Knik and Matanuska River drainages, and the Susitna River drainage up to 500 m elevation. The Cook Inlet Ecoregion extends north of Talkeetna, east to the Talkeetna Mountains and west to the Alaska Range. Average annual precipitation ranges from 280 to 680 mm. Winter temperatures range from lows of -15°C to highs of -5°C and summer highs of about 5 to 8°C. May through September is generally frost free (Gallant et al. 1995). The Little Susitna River flows an estimated 113 miles from the Talkeetna Mountains to Cook Inlet, with an elevation change of over 4,000 feet. The Little Susitna River is an important recreational area for south-central Alaska. The river supports a popular Chinook and coho sport fisheries. The river is road accessible upstream from the Park’s Highway. Access downstream of the Park’s Highway and the Miller’s Reach subdivision (river mile 62) is limited to the Public Use Facility (river mile 25) located at the end of Ayrshire Road. The Little Susitna River is one of the rivers managed under the Susitna Area Recreational Rivers Management Plan. The lower river is located within the Susitna Flats State Game Refuge, and a small portion of the river downstream from the Park’s Highway flows through the Nancy Lake State Recreation Area. The river is within the Hatcher Pass State Management Area upstream of the Edgerton Park Road Bridge. Residential and commercial development is restricted to the road accessible areas near the cities of Wasilla and Houston. The Little Susitna River’s headwaters begin at the Mint Glacier in the Talkeetna Mountains in Hatcher Pass within the Matanuska-Susitna Borough (MSB). Hatcher Pass is a historic gold mining district and there are still active mines within the area. The Independence Mine State Historical Park is managed by Alaska Department of Natural Resources (ADNR), Division of Parks and Outdoor Recreation. Most of the gold mining on the Little Susitna side of Hatcher Pass is historic, with the most recent mining occurring in the 1970’s. There has been recent interest in reactivating some of the hard rock mines located outside of the 20-acre Independence Mine State Historical Site located on upper Fishhook Creek. The area geology is mostly diorite and granite. Most of the gold in the area is associated with granite seams. There is some pyrite (which is associated with sulphides and acid mine or rock drainage) but it is not high. Most of the gold mining on the Little Susitna side of Hatcher Pass was done with tunnels. ADNR, Division of Mining Land and Water, does not know if any of the old tunnels are leaking or if they connect to groundwater and/or tributaries to the Little Susitna River. The population within the Matanuska-Susitna Borough has been increasing rapidly over the past few years. This has resulted in an increase in development and recreational use along the Little Susitna River. Residential development and recreational use have the potential to negatively affect the aquatic ecosystem. Residential development and 1 Aquatic Restoration and Research Institute Hatcher Pass 2008 Report associated road construction can result in the direct loss of fish habitat and indirect effects to water quality. Riparian vegetation often is removed for home construction or to provide unimpeded river views. The removal of bank vegetation can cause accelerated bank erosion rates. Increases in bank sediments in excess of the stream transport capacity can cause areas of sediment deposition. Fine sediment deposition can affect the transport of water and oxygen through the substrate, reducing the quality of fish spawning habitat and the living space for aquatic insects. Road construction can be a source of sediment, concentrating surface flows along ditch lines, and delivering sediment to streams at road crossings. The delivery of toxic hydrocarbons can increase at road crossings. The construction and use or failure of residential septic systems can result in an increase in concentrations of fecal coliform bacteria in adjacent waters causing increased risk to human health through direct or indirect contact with contaminated waters. Increases in stream water nutrient concentrations resulting in blooms of nuisance algae also have been associated with residential development. Water quality monitoring in the upper portion of the Little Susitna watershed was initiated in the spring of 2005. Intensive sampling was conducted throughout the summer of 2005 with monthly water samples collected June through October and in January, February and March of 2006 (Davis et al. 2006). Water quality sampling was continued through 2006 and 2007 with spring, summer, fall, and winter water chemistry measures and spring and fall biotic measures of water quality (Davis and Davis 2006, 2008) There is an active USGS gauging station (15290000) with 57 years of record downstream of the bridge on Palmer Fishhook Road as the river exits the Hatcher Pass area. The objectives of this project were to continue the evaluation of water quality within the upper Little Susitna River by obtaining chemical and biotic measures of water quality through the summer of 2008 and winter of 2009. These data will be used to support the overall goal of obtaining long-term measures of base-line water quality that can be used to assess potential future changes due to development, mining, or increased recreational use. Methods Water sampling in 2008 was conducted at five sampling sites on the Little Susitna River within Hatcher Pass. Sampling sites were located at the Goldmint Trailhead, Mile 12 (just upstream from Fishhook Creek), Mile 10.2, the USGS gauging station (below the Palmer Fishhook Road bridge), and upstream from the Edgerton Park Road bridge. Sites were labeled HP-1 through HP-5 from upstream to downstream (Figure 1). 2 Aquatic Restoration and Research Institute Hatcher Pass 2008 Report A A r r c F c h is h a h a n h n g o g e o e l l k C C r C r e r e e e e k e k k HP-1 HP-2 Little Susitna River HP-3 Figure 1. Map showing the location of the Hatcher Pass sampling sites. Edgerton Park Road Water samples were collected from all site H P and October 6, 2008; and February 23, 2009. -4 H in Anchorage for total fecal coliform bacteria analyses.P Samples were submitted to AM - Palmer Fishhook Road Fishhook Palmer Test Inc. in Kirkland, WA to be analyzed 5 Road Fishhook Palmer nitrogen. Water samples were also returned specific conductance, and tu analyzed for the BTEX aromatic hydrocarbons total xylene) components of gasoline. 3 rbidity. Water samples collecteds for inchemical August analyseswere also on June 9, August 14, Samples were submitted to SGS laboratory for nitrate plus nitrite nitrogen and ammonia to the ARRI laboratory for measures of pH, (benzene, ethyl ben zene, toluene, and Aquatic Restoration and Research Institute Hatcher Pass 2008 Report Stream water temperature was measures at HP-2 (Mile 12) and at the Edgerton Park Road Bridge.
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