Chapter 3: Bivens Arm Lake 3.1 Introduction Bivens Arm is a small
Transcription
Chapter 3: Bivens Arm Lake 3.1 Introduction Bivens Arm is a small
Chapter 3: Bivens Arm Lake Draft 10/24/02 3.1 Introduction Bivens Arm is a small shallow lake located in southwest Gainesville. The surface area of the lake is approximately 189 acres (Lakewatch 2000). Bivens Arm is a unique environment which supports a wide diversity of plant and animal life in an urban setting. The lake is part of the Tumblin Creek watershed. Tumblin Creek, which is fed by small springs and seeps originating upstream of Shands at AGH, drains into Bivens Arm and is the primary source of drainage into the lake. Bivens Arm is also part of the larger Orange Creek Basin and forms the northern extension of Paynes Prairie. Figure 3.1 Location of Bivens Arm Lake in the Tumblin Creek watershed. The early history of Bivens Arm is not well documented given that it is a relatively small body of water. The earliest known use of the land around the lake was as hunting grounds by Native Americans. Beginning in the late 1800’s, the land was used mostly for agricultural purposes including cattle ranching, swine farms, vegetable farms, and orange groves. In the 1930’s, Bivens Arm was designated as a bird sanctuary and rookery which a resident ranger to cared for (Pickard 1994). In 1965, the State of Florida designated the lake area as a wildlife sanctuary (Bill No. 1356 Chap. 65 1005). In 1981, the City of Gainesville purchased the land between the lake and Williston Road to form the Bivens Arm Nature Park. This park features a lush live oak hammock habitat and marshlands, which periodically become inundated with rising water levels from the lake. Bivens Arm Lake Bivens Arm is a solution lake in which the underlying limestone has been eroded by fluvial (water) processes. Sediments surrounding the lake are fine to medium grained sands, silts, and clays, of PlioPleistocene age and those of the Miocene age Hawthorn Group consisting of quartz sands, silts, clays, phosphates, and carbonates (limestone and dolomite) (Scott 1988, White 1970). 3-1 Chapter 3: Bivens Arm Lake Draft 10/24/02 Bivens Arm Lake provides an ideal habitat for many species of plants and animals. Alligators can often be seen basking on the lake’s surface, and osprey and bald eagles can be observed hunting overhead. Other common bird species include herons, egrets, ibis, gallinule, cormorants, and anhingas. Wildlife can best be observed from the Bivens Arm Nature Park, as all other land around Bivens Arm is privately owned or has limited access. An array of freshwater fish exist in the lake including native species such as the Florida largemouth bass and exotic species such as blue tilapia. Angling on the lake is a popular activity and species commonly caught include catfish, tilapia, crappie, bass, and sunfish (bluegill and shell-crackers). location and impervious drainage basin, the lake receives large quantities of stormwater runoff from urban and commercial lots and surrounding roads including SW 13th Street (US 441) which bisects the lake. The lake is classified as hypereutrophic as indicated by the high levels of nutrients, extensive algal and vascular plant growth, and high productivity (Florida Lakewatch 2000). A summary of water quality parameters is presented in Table 3.1. In many ways water quality in Bivens Arm is similar to other large lakes in the Orange Creek Basin. Total kjeldahl nitrogen Parameter Count (n) Mean Alkalinity (mg/L) 19 82.47 Chlorophyll a (mg/L) 19 57.5 Dissolved Oxygen (mg/L) 69 9.7 Nitrate/Nitrite, dissolved (mg/L) 19 0.002 Orthophosphate (mg/L) 19 0.034 PH 65 8.78 Secchi (m) 19 0.637 Total Kjeldahl Nitrogen, total (mg/L) 19 1.437 Total Phosphorous, total (mg/L) 19 0.157 Turbidity (ntu) 13 16.115 Table 3.1 Water quality summary for Bivens (TKN) levels are nearly identical or slightly lower than other large lakes in the region (Figure 3.2), however phosphorous levels in the lake are among the highest (Figure 3.3). High phosphorous levels may be attributed to the flow of Tumblin Creek through the phosphorous-rich Hawthorn Group materials, current and historical agricultural activities in the watershed, and runoff from residential landscape and turf grass fertilization. Fishing on Bivens Arm Lake 3.2 Water Chemistry Bivens Arm Lake is surrounded by a restaurant, a hotel, apartments, private residences, and restricted access University of Florida property. According to CH2MHILL (1993), up to sixty percent of the basin is impervious. Due to its urban 3-2 Chapter 3: Bivens Arm Lake Draft 10/24/02 native species of plants have become established in Bivens Arm. Of these species four are classified as ‘Category I’ invasive exotics by the Florida Exotic Plant Pest Council and have been targeted for control within the lake. 4 TKN (mg/L) 3.5 3 2.5 2 1.5 1 Hydrilla (Hydrilla verticillata) was introduced to Florida in the 1950's and has become a major aquatic weed problem in many waterbodies in the state. Several strategies for control have been implemented in Bivens Arm. In the spring of 1999, Alachua County released 2500 Triploid Grass Carp into Bivens Arm to provide a control mechanism to manage the hydrilla that was engulfing the lake. The management plan specified the addition of the grass carp combined with periodic spraying of the herbicide Aquathol-K to reduce the levels of hydrilla. By summer 2000, the carp had cleared hydrilla in all but the shallow bank areas of the lake. In fact, the grass carp were so successful in the summer of 2000 that there was no additional spraying of Aquathol-K. This change in vegetation is reflected in water quality changes. After the removal of the hydrilla, planktonic algae became the dominant open-water plant species, turning the water a green color. The evidence of this switch can be seen in the amount of chlorophyll a in the water column. Figure 3.4, shows chlorophyll a levels remained steady in the years prior to the introduction of grass carp, but increased sharply post- introduction. Newnans Lake Lochloosa Lake Orange Lake 0 Bivans Arm Lake 0.5 Figure 3.2 Total Kjeldahl (TKN) values in Bivens Arm and surrounding lakes 0.15 0.1 Newnans Lake Lochloosa Lake 0 Orange Lake 0.05 Bivans Arm Lake TP (mg/L) 0.2 Figure 3.3 Total Phosphorus (TP) values in Bivens Arm and surrounding lakes 3.3 Aquatic Plant Management Aquatic weeds have been a problem in Bivens Arm since the 1950’s. Not all aquatic plants pose a nuisance, as they provide a habitat for mating fish and their eggs, protective cover for young fish, and food and cover for lower trophic level organisms. The problem arises primarily from non-native invasive species of aquatic plants, which crowd out the native species and quickly spread throughout the water body (IFAS 2000). Several non- Water hyacinth (Eichhornia crassipes) was introduced into Florida in the late 1890's. Since that time it has spread to become one of Florida's major invasive plant problems. However, with current 3-3 Chapter 3: Bivens Arm Lake Draft 10/24/02 Water lettuce (Pistia stratiotes) is an invasive species first recorded in Florida in 1765. It is less prevalent in Bivens Arm and is controlled in the same manner as water hyacinth. Chlorophyll a (uncorrected) (mg/m3) 180 160 140 120 100 80 60 Wild taro (Colocasia spp.) is an emergent non-native invasive species which inhabits the shoreline of many Florida wetlands. In Bivens Arm this species has recently inhabited the shore and is becoming dominant along several areas. Control of this species is slated to begin in 2002/2003 along state owned property. 40 20 0 1997 1998 1999 2000 Year Figure 3.4 Chlorophyll values in Bivens Arm Lake before and after the introduction of Grass Carp. 3.4 Summary and Recommendations Existing water quality data indicate elevated concentrations of chlorophyll a and nutrients. Potential sources of elevated nutrients fornd in Tumblin Creek and directed to Bivens Arm Lake include: stormwater runoff containing fertilizers from residential, commercial, and agricultural activities; leachate from landfill areas in Tumblin Creek Park; wild animal and/or pet waste; failing septic tanks systems; leaking sanitary sewer lines or connections; and atmospheric deposition. Stormwater quality data indicate that nutrients and suspended solids increase in Tumblin Creek at US 441 (TUM441), directly upstream of and contributing to Bivens Arm Lake. plant control practices this plant is now under control in most areas. In Bivens arm, maintenance control (Haller, 1981) of water hyacinth has been achieved and only moderate amounts of control are necessary. Water hyacinth was the only chemically controlled plant, and was controlled using Reward and 2,4-D. The former discharge of air conditioner and heating system water from the Park 16th apartments added an estimated one MGD of groundwater, which is typically low in nutrients, to Tumblin Creek and Bivens Arm Lake. This discharge effectively served to augment the lake, keeping the stage (or water level) relatively con- Water Hyacinth (Eichhornia crassipes), an invasive exotic plant in Bivens Arm Lake 3-4 Chapter 3: Bivens Arm Lake Draft 10/24/02 stant. The discharge ceased in April 2002 (Chapter 2, Section 2.4, page 2-7). Since that time, the water level in Bivens Arm Lake has dropped in response to low rainfall. The lake level is beginning to rise as summer convective storms move into the area, but will likely drop with the end of the summer wet season. City of Gainesvillemust work together to secure funding for these efforts Water quality monitoring is proposed to continue on Bivens Arm Lake, as long as the lake is accessible by boat. Recommendations outlined in the Chapter 2: Tumblin Creek, Section 2.8 (page 2-17) apply to improving the quality of Bivens Arm Lake and should be implemented. Additionally, consideration should be given to augmenting the lake with reclaimed water from the GRU Main Street WRF. The existing water quality data should be evaluated in detail and the monitoring program modified to address changes in the Tumblin Creek/ Bivens Arm watershed including the restoration of the wetlands on the north side of the lake. As with all restoration activities, there are large capital expenditures and significant recurring operation and maintenance costs. The local partner agencies, the SJRWMD, Alachua County, and the Bivens Arm Lake at sunset 3-5