Coosa River Project Wildlife Management Plan
Transcription
Coosa River Project Wildlife Management Plan
ALABAMA POWER COMPANY BIRMINGHAM, ALABAMA COOSA RELICENSING PROJECT DRAFT1 WILDLIFE MANAGEMENT PLAN FOR THE COOSA HYDROELECTRIC PROJECT July 2005 Prepared By: KLEINSCHMIDT ASSOCIATES 1 Note: Alabama Power Company, Alabama Department of Conservation and Natural Resources, and US Fish and Wildlife are currently working out the final details of this Draft Wildlife Management Plan. The consensus-based executed copy of the Final Plan will be filed with the FERC upon it's completion. ALABAMA POWER COMPANY BIRMINGHAM, ALABAMA COOSA RELICENSING PROJECT DRAFT1 WILDLIFE MANAGEMENT PLAN FOR THE COOSA HYDROELECTRIC PROJECT July 2005 Prepared By: KLEINSCHMIDT ASSOCIATES 1 Note: Alabama Power Company, Alabama Department of Conservation and Natural Resources, and US Fish and Wildlife are currently working out the final details of this Draft Wildlife Management Plan. The consensus-based executed copy of the Final Plan will be filed with the FERC upon it's completion ALABAMA POWER COMPANY BIRMINGHAM, ALABAMA COOSA RELICENSING PROJECT DRAFT WILDLIFE MANAGEMENT PLAN FOR THE COOSA HYDROELECTRIC PROJECT TABLE OF CONTENTS 1.0 INTRODUCTION ...............................................................................................................1 2.0 PURPOSE OF THE PLAN..................................................................................................3 3.0 WILDLIFE MANAGEMENT OBJECTIVES ....................................................................4 4.0 SHORELINE MANAGEMENT .........................................................................................5 4.1 Management Actions ...............................................................................................5 4.1.1 Shoreline Classification System ..................................................................5 4.1.2 Shoreline Buffers .........................................................................................6 4.1.3 Planting of Native Species ...........................................................................6 5.0 WEISS WATERFOWL MANAGEMENT AREA .............................................................8 5.1 Management Actions ...............................................................................................8 6.0 MITCHELL DEVELOPMENT RED-COCKADED WOODPECKER MANAGEMENT PLAN .................................................................................................................................11 6.1 Management Actions .............................................................................................11 6.1.1 Cavity Tree Cluster Buffer Zones..............................................................11 6.1.2 Management of Foraging Habitat ..............................................................12 6.1.3 Timber Management..................................................................................13 6.1.4 Prescribed Burning.....................................................................................14 6.1.5 Forest and Cavity Tree Inventory ..............................................................14 6.1.6 Monitoring and Reporting..........................................................................15 7.0 TIMBER MANAGEMENT...............................................................................................18 7.1 Management Actions .............................................................................................19 7.1.1 Coosa Wildlife Management Area.............................................................19 7.1.2 Remaining Project Lands...........................................................................21 8.0 BALD EAGLE MONITORING AND MANAGEMENT ................................................23 8.1 Management Actions .............................................................................................23 9.0 WILDLIFE OPENINGS....................................................................................................24 9.1 Management Actions .............................................................................................24 10.0 HANDICAPPED HUNTING AREAS ..............................................................................26 -i- Table of Contents (continued) 10.1 Management Actions .............................................................................................26 11.0 WILDLIFE ENHANCEMENT FUND .............................................................................28 12.0 LITERATURE CITED ......................................................................................................29 LIST OF FIGURES Figure 1: Figure 2: Figure 3: Figure 4: Figure 5: Coosa Project Location Map....................................................................................2 Proposed Weiss Waterfowl Management Area .....................................................10 Proposed Red-cockaded Woodpecker (RCW) Management Area........................17 Coosa Wildlife Management Area (Lake Mitchell) Cover Type Map ..................22 Proposed Jordan Development Handicap Deer Hunting Area ..............................27 LIST OF TABLES Table 1: Wildlife Enhancement Fund – Summary Table.....................................................28 LIST OF APPENDICES Appendix A: E13 - Wildlife Management Plan Issue Sheet Appendix B: Wildlife Habitat Enhancement and Restoration Program - ii - ALABAMA POWER COMPANY BIRMINGHAM, ALABAMA COOSA RELICENSING PROJECT DRAFT WILDLIFE MANAGEMENT PLAN FOR THE COOSA RIVER, MITCHELL, AND JORDAN HYDROELECTRIC PROJECTS 1.0 INTRODUCTION This Wildlife Management Plan was developed as part of Alabama Power Company (APC)’s efforts to acquire new operating licenses from the Federal Energy Regulatory Commission (FERC) for seven hydroelectric developments in the Coosa River Basin in Alabama (Figure 1). These developments include the Weiss, Neely Henry, Logan Martin, Lay, and Bouldin Developments, which currently are licensed collectively as the Coosa River Project; and the Mitchell and Jordan Developments, which are licensed as the Mitchell and Jordan Projects, respectively. Upon issuance of a new license from the FERC, these projects will be licensed collectively as the Coosa Hydroelectric Project. APC’s relicensing process in the Coosa Basin included a multi-year cooperative effort between APC and interested stakeholders to address operational, recreational, and ecological concerns associated with hydroelectric project operations. During the initial (scoping) phase of the relicensing process, APC consulted a wide variety of stakeholders, including state and federal resource agencies, non-governmental organizations, and concerned citizens, seeking their input on important relicensing issues. Relicensing stakeholders identified several issues they believe need to be addressed during this relicensing process, including management of the wildlife resources within the project boundaries of the Coosa River hydroelectric developments. -1- Figure 1: Coosa Project Location Map -2- 2.0 PURPOSE OF THE PLAN The overall purpose of this Wildlife Management Plan is to protect and enhance the available wildlife habitat within the project boundaries of APC’s Coosa Basin hydroelectric developments. The plan consolidates numerous wildlife management activities currently in place in the basin into a single document and provides the additional technical information and management guidelines requested by resource agencies and other stakeholders during relicensing. -3- 3.0 WILDLIFE MANAGEMENT OBJECTIVES Specific wildlife management objectives for the lands surrounding the Coosa Project were initially identified during the scoping phase of the relicensing process (E13 Issue Sheet Appendix A). These objectives were further refined through subsequent meetings with the Alabama Department of Conservation and Natural Resources (ADCNR) and U.S. Fish and Wildlife Service (USFWS) and include: 1. Management of shoreline areas for native vegetative communities and enhanced value as wildlife habitat; 2. Continued management and enhancement of red-cockaded woodpecker (RCW) habitat on project lands; 3. Implementation of timber management methods that result in enhanced value of project lands as wildlife habitat; 4. Protection and monitoring of bald eagle nesting areas; 5. Establishment of additional forest openings on project lands to provide foraging areas for wildlife; 6. Establishment of additional public hunting areas for the physically disabled; and 7. Development of a waterfowl refuge and/or Waterfowl Management Area within the project boundaries for consumptive and non-consumptive uses. -4- 4.0 SHORELINE MANAGEMENT Protection and enhancement of available shoreline habitat for wildlife will be accomplished through implementation of the proposed Shoreline Management Plan (SMP). Pending approval from the FERC, the SMP will be implemented for the more than 1,600 miles (mi) of shoreline within the FERC boundaries of the Coosa Basin developments. The exception to the SMP is the Coosa Wildlife Management Area, located within the project boundary of the Mitchell Development, which will be managed according to this Wildlife Management Plan. 4.1 Management Actions 4.1.1 Shoreline Classification System As part of the proposed SMP, APC will implement a Geographic Information System (GIS)-based shoreline classification system to guide future management actions to protect natural resources, including wildlife habitat. This system classifies reservoir shorelines into one of five land use categories according to their current and future designated uses. While not solely designed for protection of wildlife habitat, two of these categories, Sensitive Resource Lands (Class 4) and Natural / Undeveloped Lands (Class 5), often include valuable wildlife habitats and thus are described in greater detail below. Sensitive Resource Lands are project lands (generally privately-owned with APC maintaining a flood easement) that are managed for protection and enhancement of sensitive resources. Sensitive resources include archaeological sites; sites/structures listed on or eligible for listing on the National Register of Historic Places; wetlands; floodplains; Rare, Threatened and Endangered (RTE) habitat protection areas; significant scenic areas; and other sensitive ecological areas. Permitted activities, if applicable, in these areas will be highly restrictive to avoid potential impacts to sensitive resources and will trigger an environmental review by APC’s environmental department prior to issuance of a Shoreline Use Permit. -5- Natural / Undeveloped Lands are project lands, typically owned in fee by APC, that are to remain in an undeveloped state for specific project purposes including: to protect environmentally sensitive areas; to maintain natural aesthetic qualities; to serve as buffer zones around public recreation areas; and to provide a means for preventing overcrowding of partially developed shoreline areas. This classification allows for public hiking trails, nature studies, primitive camping, wildlife management (excluding hunting), and normal forestry management practices. 4.1.2 Shoreline Buffers Upon acceptance from the FERC, the proposed SMP will provide for preservation or establishment of a shoreline buffer zone of unmanaged vegetation around the reservoirs. Establishment of a minimum 15-foot (ft)-wide vegetated buffer, measured horizontally from the top of the normal full pool, will be required on all project lands owned in fee by APC and will be recommended as a Best Management Practice (BMP) on privately-owned project lands adjacent to the reservoirs. Unmanaged vegetation associated with these buffers strips, and in particular buffer strips in excess of the 15 ft minimum, would enhance available food and cover for wildlife species, provide corridors that enhance linkages between larger habitat patches, and protect nearshore environments. Nearshore environments provide important breeding and nursery areas for numerous fish and amphibian species and are utilized for feeding and cover by species such as river otter, beaver, and various wading birds and waterfowl. At a microhabitat level, accumulated leaf litter, pine needle duff, and course woody debris (Fallen logs, etc.) in these vegetated buffers will provide much needed refugia for reptiles and amphibians. 4.1.3 Planting of Native Species The proposed SMP will also recommend, and in some instances require, planting of native trees, shrubs, and plant species for landscaping and for purposes of shoreline stabilization. Plants native to the soils and climate of a particular -6- area typically provide the best overall food sources for wildlife, while generally requiring less fertilizer, less water, and less effort in controlling pests. Planting of native species will be required on all Recreation Lands (Class 2) and recommended as a BMP on all other project lands. -7- 5.0 WEISS WATERFOWL MANAGEMENT AREA APC, in cooperation with the ADCNR, will develop and operate a waterfowl management area within the project boundary of the Weiss Development. By utilizing dikes to seasonally flood cultivated fields within the Weiss Project Boundary, the proposed management areas will provide enhanced foraging habitat and resting areas for resident and overwintering waterfowl and wading birds, as well as additional breeding habitat for amphibians. Finally, the proposed management areas will provide increased wetland acreage areas within the project boundary. 5.1 Management Actions 1. Within one year following issuance of a license for the Coosa Project, a shallow impoundment of approximately 10.6 acres (ac) will be constructed within and on the east side of Weiss Reservoir at the location indicated in Figure 2. The pond will be constructed by installation of two dikes which have a combined length of approximately 260 ft. This impoundment will serve as a resting area for waterfowl in the area and will be located adjacent to approximately 16.5 ac of crop land currently owned by the licensee, which lies to the northeast of the impoundment at the location shown in Figure 2. A low dike, typically two ft in height or less and approximately 4,967 ft in length will be constructed around the crop land and the crop land will be flooded following harvest of the crop grown on the land. This crop land is currently used to grow grain crops (e.g. corn and soybeans). The licensee will ensure a percentage of the grain crop raised on this land is not harvested prior to flooding. 2. Within two years following issuance of a license for the Coosa Project, the licensee will construct a low dike, typically two ft in height or less, around four additional parcels of crop land that total approximately 42.9 ac. These parcels are located on the west side of the Weiss Reservoir directly across the main river channel from the location referenced in item 1 (Figure 2). This crop land, which is located as shown in Figure 2, will also be flooded -8- following harvest of the crop grown on the land. This crop land is currently used to grow grain crops (e.g. corn and soybeans). The licensee will ensure a percentage of the grain crop raised on this land is not harvested prior to flooding. 3. If deemed necessary in consultation with the ADCNR, the licensee will work cooperatively with the agency to construct, within five years following issuance of a license for the Coosa Project, an additional shallow impoundment of approximately 72.6 ac within and on the west side of the Weiss Reservoir at the location indicated in Figure 2. The pond will be constructed by installation of two dikes which have a combined length of approximately 1,140 ft. This impoundment will serve as an additional resting area for waterfowl in the area and will be located adjacent to approximately 42.9 ac of crop land, currently owned by APC, which lies to the northeast of the impoundment at the location shown in Figure 2. 4. If deemed feasible or desirable, the ADCNR shall manage the Weiss Waterfowl Management Area previously described for public hunting. Construction and operation of the Weiss Waterfowl Management Area will be funded as described in the Wildlife Enhancement Fund Summary Table (Table 1). -9- Figure 2: Proposed Weiss Waterfowl Management Area - 10 - 6.0 MITCHELL DEVELOPMENT RED-COCKADED WOODPECKER MANAGEMENT PLAN The federally endangered Red-cockaded Woodpecker (RCW) (Picoides borealis) presently inhabits certain portions of Alabama Power Company’s (APC) Lake Mitchell Project Lands in Coosa and Chilton Counties in the Coosa River Basin. As part of relicensing of the Mitchell Project during the 1980’s, FERC approved a Red-cockaded Woodpecker Management Plan in 1987, the substance of which was developed based on an RCW study conducted on the Mitchell Project Lands in 1985 (Holliman 1985a). This plan was implemented for approximately 1087 ac of the 3000 ac of project lands within the Coosa Wildlife Management Area. The 1987 RCW Management Plan included monitoring of RCW populations on a five year basis. The most recent survey (Bailey 2004), conducted in 2003 2004, found nine active RCW clusters on Mitchell Project Lands. The RCW Management Plan described herein updates and replaces the plan approved by FERC in 1987. This new RCW Management Plan was developed in close consultation with the U.S. Fish and Wildlife Service (USFWS). The USFWS has determined that implementation of this RCW Management Plan will protect and enhance the present population of RCWs inhabiting the Mitchell Project Lands. 6.1 Management Actions All lands within the Mitchell Project identified in Figure 3 as within the RCW Management Area will be managed for RCWs as described below. These lands in aggregate comprise a total of approximately 1057 ac. 6.1.1 Cavity Tree Cluster Buffer Zones A 200 ft-wide buffer zone will be maintained around all cavity trees and cavity start trees within each active RCW cluster. Within the 200 ft buffer, midstory will be controlled by physical cutting and pruning, chemical injecting, and/or basal spraying as needed. Within this buffer zone every effort will be made to protect potential cavity trees while maintaining 20 – 25 ft spacing - 11 - between these trees. Selected snags will be left within the buffer to provide cavity trees for other cavity nesters, thus reducing demand on RCW cavities. Finally, timbering or management activities, such as pruning or injecting to control the midstory, will not be practiced in the buffer zone during the nesting season (April – June). 6.1.2 Management of Foraging Habitat Upland pine and mixed pine/hardwood stands within the area identified on Figure 3 as the RCW Management Area will be managed towards providing each active cluster with a minimum of 75 ac of suitable foraging habitat. For purposes of this goal, foraging habitat is defined as follows: 1. Provide each group of RCWs a minimum 3000 square feet (ft2) of pine basal area, including only pines with diameter at breast height (DBH) > 10 inches (in). 2. Provide the above pine basal area on a minimum of 75 ac. 3. Count only those pine stands that potentially are suitable habitat and that have each of the following characteristics: a. Stands that are at least 30 years old and older. b. An average pine basal area of pines > 10 in between 40 and 70 square feet per acre (ft2/ac). c. An average pine basal area of pines < 10 in less than 20 ft2/ac. d. No hardwood midstory or if a hardwood midstory is present, it is sparse and less than 7 ft in height. e. Total stand basal area, including overstory hardwoods, less than 80 ft2/ac. - 12 - f. Foraging habitat will be located to the extent feasible within 0.25 mi of the cluster, and to the extent feasible any stand counted as foraging habitat will be within 200 ft of another foraging stand or the cluster itself. g. Prescribed burning of foraging habitat shall occur a minimum of once every 5 years. Reasonable progress toward meeting the goal of 75 ac of foraging habitat for each active cluster will be demonstrated by maintenance or increases in the area of foraging habitat that meets all of the characteristics of foraging habitat set forth above (items a - g). Reasonable progress can also be demonstrated by maintaining or increasing habitat area that meets all elements but one, with no corresponding decrease in the habitat area meeting all elements. Finally, reasonable progress can also be demonstrated if one or more of the individual components are being moved toward the desired condition. Any of these improvements in foraging habitat have to be current (within the past 5 years) to be considered reasonable progress. Typical management practices to be utilized to increase the quality and quantity of foraging habitat are described herein and include prescribed burning, selective herbicide application, and timber stand improvement through timber harvest, increased rotation lengths, and pre-commercial thinning. Given the inherent variation of on-the-ground conditions at the Mitchell Project Lands, the mix of management practices used to achieve the goals for RCW foraging habitat will likely vary from site to site and over time. 6.1.3 Timber Management All longleaf pine stands managed for RCWs shall be managed on a rotation interval of not less than 100 years and an 80 year rotation for other pine species crop trees. An exception to this management rotation interval will be - 13 - made based for stands under high risk of mortality due to insects, disease, or other site-related problems after consultation with the USFWS. Prior to initiation of timbering or other development activities on lands covered by this RCW Management Plan, a survey will be made to determine the presence of additional active RCW colonies. If additional colonies are found, they will be managed as described in this plan. In the event of a natural disaster such as fire, tornado, ice storm or southern pine beetle damage, timber salvage operations will be conducted to remove affected trees. 6.1.4 Prescribed Burning Prescribed burns will be conducted within the RCW Management Area on a minimum 5-year return interval. Prescribed burns will normally be conducted during the growing season (March-September). Initial fuel reduction burns may be conducted during the non-growing season (November-February) to reduce the risk of catastrophic damage to nesting and foraging resources. The goal of prescribed burns will be reduction of non-herbaceous (woody) vegetation in the understory, and control of hardwood trees/shrubs that have entered the midstory. All known RCW cavity trees will be protected from accidental ignition during prescribed firing operations by removing fuels at the base of cavity trees. Protecting human health and safety will take priority over meeting the prescribed burning schedules in this plan. 6.1.5 Forest and Cavity Tree Inventory A complete forest and RCW cavity tree inventory of the RCW Management Area will be completed on a minimum 10 year interval. The forest inventory data will be used to develop timber management prescriptions for the lands being managed for RCWs. Pine size, age, and density will be determined using standard forestry techniques. For example, the age of pine trees can be determined by coring a sample and determining the relationship between age and size. During the forest inventory, all RCW cavity trees identified will be mapped - 14 - using a Global Positioning System (GPS), imported into a Geographic Information System (GIS), and locations made available to the USFWS and the ADCNR. The forest inventory data will be utilized to monitor the quality and quantity of foraging habitat for each active group or cluster, based on the following criteria: 1. the number of ac of foraging habitat that meets all elements of foraging habitat listed in section 6.1.2. 2. the number of ac of foraging habitat that meets all elements listed in section 6.1.3 but one, and for each forest stand, identify the missing element. 3. the number of ac of foraging habitat that meets all elements listed in section 6.1.3 but two, and for each forest stand, identify the missing elements. 6.1.6 Monitoring and Reporting Known RCW clusters will be evaluated annually for the first 10 years following issuance of the license for the Coosa Project and once every 5 years thereafter to determine if they are active. Generally, this will involve observing each cluster in the morning and/or evening to determine if one or more RCWs are using each of the cavity trees. A cavity tree may also be deemed active if it exhibits fresh resin as a result of RCW activity. The USFWS and ADCNR will be invited for a site visit annually during the monitoring of cavity activity to inspect the RCW clusters. A report will be submitted to the USFWS by January 31 each year that monitoring occurs following issuance of the license for the Coosa River Project. USFWS shall grant a reasonable extension for the filing of the report if APC demonstrates that conditions beyond its control (for example, weather or other natural conditions) have delayed monitoring or management activities. The report - 15 - shall include summary of all habitat management actions undertaken since the last monitoring report and include a summary of the activity status of each cluster. The monitoring report format shall consist of all applicable sections contained the USFWS Regional Annual RCW Property Data Report. - 16 - Figure 3: Proposed Red-cockaded Woodpecker (RCW) Management Area - 17 - 7.0 TIMBER MANAGEMENT APC’s Corporate Real Estate Department has had an active forest management program since World War II. Currently, the number of ac under forest management on the Coosa River Hydro Projects is approximately 12,700 ac. Shortly after WW II, Company timber stands on these projects were inventoried and long range timber management plans were developed. These plans directed an all-aged, sustained-yield management scheme with the forest rotation age of 60 years. Under this management strategy, trees would be grown to an average age of 60 years and would produce forest products on a continuous basis. Sawtimber would be harvested on 16 year cutting cycles and pulpwood would be thinned as a secondary product at interim periods of 10 years. In the early 1970's, the cutting cycle for sawtimber was lengthened to 20 years because power skidders were then being used. As a result, more volume was being cut per acre and more reseeding was occurring (from the additional exposure of mineral soil caused by the skidders). The extended cutting cycle allowed for per acre volumes to recover and the young seedlings to put on additional volume. This all or uneven-aged management scheme has produced a notably diverse forest both in terms of species composition and in forest products. The result is not only the production of valuable high-quality products but the production of diverse quality habitat for both game and non-game wildlife species. These planned and controlled forest management practices have, over the years, aided in the protection of the watersheds of the associated reservoirs which indirectly have enhanced the fisheries habitat of these lakes, rivers, and streams. These practices have also produced habitats that have, over the years, promoted and sustained several rare and endangered species of plants and animals. Forest lands located within the project boundaries of APC’s Coosa basin developments will be managed according to the action described below. The exception to this will be the Mitchell Project Lands designated in Figure 3, which will be managed for enhancement and protection of the endangered red-cockaded woodpecker as described in Section 6.0 of this plan. - 18 - 7.1 Management Actions 7.1.1 Coosa Wildlife Management Area Forest resources on the Coosa Wildlife Management Area, located on the Mitchell Project Lands, will be managed as follows: 1. The pure hardwood stands on better sites as indicated on Licensee cover-type map (Figure 4) would be left in the present type with selective cutting on a 20 - 30 year cycle. Target DBH for trees to be harvested would be 22 -26 in. These sites are scattered in pockets and hollows throughout the area with more extensive stands in the eastern half of Section 26, Township 22N, Range 16E (adjacent to the Coosa’s mainstem just upstream of the mouth of Hatchet Creek). Some 400 + ac fall into this category. Hardwood cutting would be done to favor various oaks (Quercus spp.), hickories (Carya spp.), and selected den trees. 2. The pine-hardwood type would be managed using single-tree selection harvest and all-aged management. Stands will be marked for improvement cuts simultaneous with harvest cuts. Target DBH for trees to be harvested would be 16 -20 in for pine and 20 - 22 in for hardwoods. Hardwood cutting would be done to favor various oaks and selected hickories. Fire is not recommended in any hardwood stand. All-age management with moderate basal area (50 - 60 ft2) will maximize vertical stratification thereby increasing niche availability and "edge effect". This system will allow sunlight penetration that stimulates understory food and cover production by herbs, shrubs, and soft mast producers including dogwoods (Cornus spp.), blueberries (Vaccinium spp.). Smilax spp., etc. and possibly wild native legumes. 3. The longleaf pine stands will be managed similarly to those occupied by RCWs; i.e., single-tree selection with crop trees at least 100 years - 19 - old at harvest. These stands should be open (30 - 80 ft2 basal area) with 30 - 50 ft2 in sawtimber. Target DBH for trees to be harvested will have to be adjusted according to site index and the desired age of removal. The hardwood component in areas under the pine habitat category will be managed for the production of quality hardwood sawtimber. Prescribed burns will be conducted on longleaf pine stands where feasible, on a minimum 5-year return interval. 4. The uneven-aged pine stands of loblolly and slash or mixtures thereof will be managed for sawtimber and poles. The stands will carry 50 - 90 ft2 of basal area of which 30 - 40 should be in pole or sawtimber size trees. Target DBH for trees to be selectively removed should be 14 18 in. Fire will be used in these stands where feasible to enhance understory food production and timber stand improvement. Unevenaged management does not lend itself to generalized prescribed fire or specific burning cycles. The hardwood components in areas under the pine habitat category will be managed for the production of quality hardwood sawtimber. 5. The 75 - 100 ± ac of pine regeneration (plantations) will be managed on a sawtimber rotation (not less than 60 years) and thinned to 300 ± trees/acre at the first thinning (15-20 years). These stands will be thinned again at 35 ± years to carry 50 - 70 ft2 of basal area to the end of the cycle. The size and location of these plantations are already compatible with recommended wildlife management and enhancement procedures. Fire will be used where feasible in these stands every 3-5 years following the first commercial thinning. 6. On the 1057 ac of the Mitchell project land utilized by the endangered red-cockaded woodpecker. The licensee will manage the land in accordance with the management plan contained in Section 6.0. 7. Licensee will limit timber harvesting to 240 ac contiguous tracts. - 20 - 7.1.2 Remaining Project Lands APC will continue to manage project forest lands according to the existing all or uneven-aged management schemes, with a sawtimber cycle of 20 years and an overall forest rotation of 60 years (see above description). Prescribed burning and/or use of herbicides will be considered on stands within the project forest lands, and such use will be based on conditions and characteristics of the individual stands. APC will continue to utilize selective cutting as the primary means of timber harvest on project lands, with those trees that are mature or of poor quality being removed. Natural regeneration will continue to be the primary means by which harvested forests are replaced. However, if a particular timber stand cannot be regenerated naturally, or if a stand is destroyed by some catastrophic event, any residual trees will be harvested, the site prepared, and the stand planted with genetically improved seedling stock. - 21 - Figure 4: Coosa Wildlife Management Area (Lake Mitchell) Cover Type Map - 22 - 8.0 BALD EAGLE MONITORING AND MANAGEMENT The bald eagle is federally listed as a threatened species. Bald eagles may be found throughout North America, typically around water where they feed primarily on fish and scavenge carrion. The species thrives around bodies of water where adequate food exists and human disturbance is limited. Eagles nest in large trees near water and typically use the same nest for several years, making repairs to it annually (Degraaf and Rudis 1986). APC has periodically assisted the ADCNR with monitoring of bald eagle populations in the vicinity of its Coosa Basin developments since the early 1980’s. When surveys were initiated in 1983, only one unsuccessful nesting attempt had been documented within the basin in recent history (Holliman 1986b, Mount 1984). Currently, there are three known active eagle nests in the vicinity of APC’s Coosa Basin developments: one each within the Project Boundaries of the Jordan and Mitchell Developments and one on private land approximately one half mi from the Mitchell Project Boundary (J. Lochamy, APC, Personal Communication). 8.1 Management Actions APC will continue to participate in the ADCNR's efforts to monitor nesting bald eagles in the Coosa Basin. In addition, APC will also continue the current practice of restricting all disruptive activities (including timbering, construction, road building, etc.) within 1500 ft of any known nest during the nesting season. At other times of the year, low disturbance activities may occur as close as 750 ft. - 23 - 9.0 WILDLIFE OPENINGS At the local level, forest openings, and in particular those maintained in an herbaceous state, provide forage and cover for game species such as white-tailed deer, wild turkey, and cottontail rabbits. In addition, the grasses and forbs in herbaceous opening harbor a variety of insects that are an important source of protein for bobwhite quail, kestrels, sparrows, and many other resident and migratory bird species. The herbaceous layer often supports an abundance of small rodents and other mammals that are prey for raptors, such as red-tailed and broad-winged hawks. Creation of multiple openings in continuous forest blocks results in increased botanical diversity on the forested landscape. The resulting mosaic of vegetative communities is in turn not only able to support a greater variety of wildlife species, but also results in an increase in “edge” habitat, where different plant communities come together. By placing food and cover closer to one another, incresed edge habitat can reduce the space requirements of individuals, thereby allowing a forest to support greater numbers of a given species. 9.1 Management Actions Over the next 10 years, 100 ac of permanent openings will be created on the Coosa Wildlife Management Area, located on the Mitchell Project Area. These openings will be no larger than 5 nor smaller than 2 ac in size. These openings must be located where severe slopes can be avoided. Existing power rights-of-way could be used to great advantage for these openings. As these openings are established they will be limed and fertilized according to Alabama Agricultural Experiment Station guidelines and maintained year-round in native grasses and other herbaceous cover. Annual planting of some wildlife-friendly species, such as chufa and clover, may be undertaken in some years. Licensee shall place gates across access roads which are constructed during development of the permanent openings to restrict public vehicle access to these wildlife openings. It will be the responsibility of the ADCNR to maintain the gates. - 24 - Since accessibility is severely limited and erosion is a likely hazard on many project lands, these sites must be developed over time and often in conjunction with timber harvest. There are currently no existing access roads to some of the better suited sites. Licensee will provide to the ADCNR upon annual written request an annual contractors report summarizing the acreages of permanent openings established, the dates established, and application rates of fertilizer, seed and lime on all established wildlife openings and the dates and types of maintenance performed on the permanent openings. - 25 - 10.0 HANDICAPPED HUNTING AREAS APC will assist the ADCNR with development of additional handicapped-accessible deer hunting areas on the Jordan Project Area, as described below. 10.1 Management Actions 1. Within one year of the issuance of a license for the Coosa Project, APC will construct two shooting houses, specifically designed to accommodate disabled hunters, at the locations depicted on Figure 5. Additional shooting houses will be constructed as demand and land allow based on consultation with the ADCNR. APC will plant and maintain greenfields and/or other wildlife openings in the vicinity of these shooting houses. If needed, APC will also build and maintain road access to the shooting houses. 2. The ADCNR shall be responsible for supervising hunting activities at the Jordan sites in accordance with the rules and regulations appropriate for Physically Disabled Hunting Areas. This is to include issuance and enforcement of permits granting hunters access to the Jordan site, establishment of a calendar for hunting on the site, and resolution of disputes regarding the use or scheduling of the Jordan handicapped hunting sites. - 26 - Figure 5: Proposed Jordan Development Handicap Deer Hunting Area - 27 - 11.0 WILDLIFE ENHANCEMENT FUND As part of the Wildlife Management Plan, APC proposes to establish a Wildlife Habitat Enhancement and Restoration Program in cooperation with the Alabama Department of Conservation and Natural Resources. The purpose of the Program is to establish a framework for working together, in a mutually beneficial manner, to develop and execute projects to enhance and restore wildlife and their habitats over the life of the new licenses issued to APC for the Coosa and Warrior River Projects. APC will establish a Wildlife Habitat Enhancement and Restoration Fund (Fund) for the support of various wildlife management projects developed over the life of the license on project lands. Typical projects may be development and management of a waterfowl area on Weiss Reservoir, wildlife enhancement on the Mitchell Development in the Coosa Wildlife Management Area, and providing funding for matching grants for projects designed for wildlife restoration and enhancement on project lands. A summary table of this funding is provided below, and a copy of the Wildlife Enhancement and Restoration Program, which provides the annual funding schedule, is contained in Appendix B. Table 1: Wildlife Enhancement Fund – Summary Table 50-Year Total in 2004 Dollars Proposed Wildlife Enhancement Measure Creation of waterfowl area Managing waterfowl area $650,000 $1,200,000 General Wildlife Management Projects $700,000 Wildlife Habitat Enhancement on Coosa Wildlife Management Area Permanent Openings (100 acres). Annual Maintenance of permanent openings – food plots. Road Construction and maintenance – 25 miles of road. GRAND TOTAL $50,000 $500,000 $50,000 $3,150,000 - 28 - 12.0 LITERATURE CITED Bailey, M.A. 2004. Red-cockaded Woodpecker Status and Recommendations: Mitchell Lake Project Lands, Coosa and Chilton Counties, Alabama. Prepared for Alabama Power Company, Birmingham, Alabama. DeGraff, R.M., and D.D. Rudis. 1986. New England Wildlife: habitat, natural history, and distribution. Gen. Tech. Report NE-108. U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station, Broomall, Pennsylvania. Holliman, D.C. 1985a. Red-Cockaded Woodpecker Study on Mitchell Project Lands. Appendix 2 in Wildlife Management Plan for Mitchell Project, FERC Project No. 82. Prepared for Alabama Power Company, Birmingham, Alabama. Holliman, D.C. 1985b. Bald Eagle Survey on Mitchell Project Lands. Appendix 3 in Wildlife Management Plan for Mitchell Project, FERC Project No. 82. Alabama Power Company, Birmingham, Alabama. Mount, R.H., ed. 1984. Vertebrate Wildlife of Alabama. Alabama Agricultural Experiment Station, Auburn University, Alabama. 44 pp. \\wren\sc_job\535-004 Alabama Power Coosa-Warrior\Ecological Issues\E-13 Wildlife Management Plan\Final Coosa Widlife Managment Plan (07-25-05).doc - 29 - APPENDIX A E13 - WILDLIFE MANAGEMENT PLAN ISSUE SHEET E13 Wildlife Management Plan – Management of the aquatic and terrestrial resources within the project study area. Description of the Issue: Stakeholders have requested that APC prepare a Wildlife Management Plan that addresses both aquatic and terrestrial resources within the project study area. The purpose of this plan would be to make sure that resource agency management goals are incorporated with project operations and APC development plans for the project study area. The plan should also consider non-consumptive uses, handicapped access, bank access and viewing/education of unique habitats and resources on project lands and waters. Stakeholders also want to include in the management plan, any protection, enhancement, or mitigation measure that might be included as part of the relicensing process. The goal is to identify APC and resource agency management plans that exist or need to be developed to provide adequate management of the aquatic and terrestrial resources within the project study area and consolidate these plans into a comprehensive “Wildlife Management Plan” that provides protection, enhancement, mitigative measures, and future management plans for the resources of the project study area. Specific issues or requests identified include: - Develop a Habitat Conservation Plan to identify and protect aquatic species; - Reduce the effect of erosion and siltation on fish habitat; - Develop a Wildlife Conservation Plan to identify and protect wildlife habitats; - Provide additional nesting structures; - Maintain flexibility in management of project lands to optimize value of recreation, fish and wildlife resource, timber production and development. Specific questions and suggestions identified include: - All APC owned islands should be maintained for wildlife habitat (Birds, mammals, etc.) – develop wildlife management plan for islands; - APC needs to permanently protect project lands and establish conservation easements in sensitive habitat areas (e.g., Hatchet Creek); - Is APC still encouraging partnerships on habitat enhancement? - What is the impact to project revenue of APC contributing money to Alabama Fish & Wildlife to enhance fisheries; - Provide additional fish habitat and fish stocking. APPENDIX B WILDLIFE HABITAT ENHANCEMENT AND RESTORATION PROGRAM Wildlife Habitat Enhancement and Restoration Program Introduction As part of the Wildlife Management Plan(s) for the Coosa River Project and the Warrior River Project, Alabama Power Company (APC) proposes to establish a Wildlife Habitat Enhancement and Restoration Program (WHERP) in cooperation with the Alabama Department of Conservation and Natural Resources (ADCNR). The purpose of this WHERP is to develop a framework for working together in a mutually beneficial manner to enhance and restore wildlife and their habitats over the life of the new licenses issued to APC for the Warrior River Project and the Coosa River Projects. Organizational Structure A WHERP Committee will be formed by one representative each from APC and ADCNR. The WHERP Committee will meet at a minimum annually to develop mutually agreeable projects on which to work during the coming year. These projects shall be designed to enhance and/or restore wildlife and their habitats on lands within the Warrior River Project and/or the Coosa River Project. Funding APC will establish a Wildlife Habitat Enhancement and Restoration Fund (Fund), the purpose of which is to provide a source of financial support for the conduct of the projects selected by the WHERP Committee. The Fund shall be maintained by APC and money will accrue annually into the Fund in accordance with the FINANCIAL SUPPORT SCHEDULE contained herein. APC and ADCNR will be able to draw on this Fund for reimbursement of material, labor, equipment, office supplies, matching funds for grants, and subcontract services required to plan, construct, manage and maintain all WHERP projects as administered by the WHERP Committee. FINANCIAL SUPPORT SCHEDULE: a. Upon execution hereof, APC agrees to establish a Fund. APC agrees to make payments into the Fund in accordance with the Base Amount funding schedule in Table 1 (but subject to adjustments in accordance with sub paragraph b of this Section) for the use of APC and ADCNR in enhancing and restoring wildlife over the life the Coosa and Warrior River Project Licenses on the Project(s) lands. Actual payment of such contributions shall be on the following schedule. Annually in arrears, each payment being the annualized amount as adjusted in accordance with sub paragraph b. The first payment shall be due on the last day of February, in the year following issuance of the new licenses for the Coosa and Warrior Projects by the Federal Energy Regulatory Commission (FERC) and acceptance of the licenses by APC, which is expected to occur in 2007. The first payment shall be for the full Base Amount of the first funding year. All subsequent payments will be made on the last day of the month February. b. The annualized contributions outlined above in sub paragraph a. shall be adjusted as follows: The calendar year 2004 shall be deemed the Base Year as used in this provision. It is the intent of this agreement that APC shall make an annual payment into the Fund each year after the licenses for the Coosa and Warrior Projects are issued by FERC and approved by APC, as scheduled in sub paragraph a. The annual payment shall be for an adjusted annual amount which reflects any change in the average annual Consumer Price Index series defined as follows: Title: Consumer Price Index – All Urban Consumers (Current Series), U.S. City Average, All Items Series ID: CUUR0000SA0, CUUS0000SA0 Seasonal Adjustment: Not Seasonally Adjusted Index Base Period: 1982-84 = 100 Frequency: Monthly Source:Bureau of Labor Statistics of the U. S. Department of Labor (herein the “Consumer Price Index – All Urban Consumers (Current Series), Not Seasonally Adjusted or “CPI”). Therefore, beginning with the first year and each year thereafter, APC and ADCNR agree that the Base Amounts outlined in paragraph a. shall be adjusted on the last day of February, or as soon as possible after the CPI for all months of the preceding calendar year have been published, of each year during the remainder of the term of this agreement and any extensions thereof as follows: The Base Amounts shall be adjusted on the last day of February , or as soon as possible after the CPI for all months of the preceding calendar year have been published, of each year to reflect any change in the CPI between the Base Year (hereinafter referred to as BCPI) and the average annual Consumer Price Index for the calendar year just completed (hereinafter referred to as ECPI). The change will be computed as follows: [(ECPI – BCPI) + 1.00] x (Base Amount) = New Adjusted Annual Amount for BCPI forthcoming year If the said CPI published by the Bureau of Labor Statistics of the U. S. Department of Labor, as the same is now computed and published, should be discontinued, or enlarged upon, or changed, upward or downward, the payment adjustments will be calculated on the equivalent of the CPI, and for the purpose of determining and calculating the equivalent of the present Consumer Price Index, use shall be made of the successor index or indexes and the formulae announced or published by the Bureau of Labor Statistics of the United States Department of Labor, and its successors, as being proper for conversion of any such successor index to the equivalent of the present Consumer Price Index. Initial Projects The following projects, among others, will be considered by the WHERP Committee following issuance of new 50 year license for the Warrior River Project and Coosa River Project 1. Development and management of a waterfowl area on the Weiss Development. 2. Wildlife Habitat Enhancement on Coosa Wildlife Management Area lands contained within the Mitchell Project boundary. 3. Applications for matching grants for wildlife restoration and enhancement projects to be conducted on Warrior River and/or Coosa River Project lands. Funding Year 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 Base Amount Funds (2004 Dollars) Provided $718,000 $159,000 $247,000 $43,000 $43,000 $348,000 $43,000 $43,000 $43,000 $43,000 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 $35,500 Total Base Funding $3,150,000