Development of Management Objectives for Waterfowl and Shorebirds in the Mississippi Alluvial Valley

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Development of Management Objectives for Waterfowl and Shorebirds in the Mississippi Alluvial Valley Development of Management Objectives for Waterfowl and Shorebirds in the Mississippi Alluvial Valley Charles R. Loesch Daniel J. Twedt Kimberly Tripp William C. Hunter Mark S. Woodrey Abstract—The goal of the Lower Mississippi Valley Joint Ven- Waterfowl ______________________ ture of the North American Waterfowl Management Plan is to provide sufficient habitat to support 4.3 million wintering ducks Long-term declines in waterfowl populations prompted and 1.0 million wintering geese annually. Under the assumption the development of the North American Waterfowl that the amount of foraging habitat is the primary limitation to Management Plan (NAWMP) during the early 1980s. The supporting waterfowl population goals in the Mississippi Alluvial NAWMP identified the Mississippi Alluvial Valley (MAV) as Valley (MAV), a habitat objective to make available 285,000 ha of one of several regions in North America containing habitat waterfowl foraging habitat is divided among seven states. This vital to the recovery of waterfowl populations. The Lower habitat objective is further divided between public and private Mississippi Valley Joint Venture (LMVJV) was organized in ownership and among three habitat types: Bottomland hardwood the late 1980s to develop a strategy for conserving, manag- forest, moist-soil sites, and agricultural fields. Management objec- ing, and restoring wetland habitats that support wintering tives for shorebirds within the MAV which provide foraging habitat waterfowl populations in a joint venture area that includes for 0.5 million shorebirds during their southward migration have the MAV. Midwinter Waterfowl Inventory data, harvest been tentatively established. Several as yet unverified assumptions data from 1970 to 1979, and population goals set in the were used in establishing these objectives; consequently, we caution NAWMP were used to set state-specific waterfowl popula- that the objectives are subject to revision as the assumptions are tion goals. The overall goal for the MAV is to provide habitat tested. We assumed that 0.5 million shorebirds move through the to support 4.3 million wintering ducks and 1.0 million MAV during late summer and fall, each foraging for an average of wintering geese annually. 10 days. During this migration period, foraging shorebirds are Assuming that foraging habitat is limiting for waterfowl assumed to require sufficient forage to gain 1 g of biomass per day, wintering in the MAV, we calculated the energetic needs of in addition to their basal metabolic needs. Given an invertebrate waterfowl, winter mortality rates, length of the wintering food supply that provides 17.6 kj • g-1, we calculated that an average period, and the energy available in various foraging habi- 45 g shorebird requires about 8 g of invertebrate forage per day. tats. Then we incorporated the population goal to determine Further assuming that each ha of managed shorebird habitat can that approximately 285,000 ha of foraging habitat are needed provide 20 kg of invertebrate food resources available to shorebirds, to support wintering waterfowl in the MAV. Within each we extrapolated a need for 2000 ha of shorebird foraging habitat. We state, habitat goals are divided between public and private suggest that the bulk of this foraging habitat be provided on public ownership and three main foraging habitats: Bottomland lands and that it be distributed throughout the MAV. hardwood forest, moist-soil sites, and agricultural fields. Availability of waterfowl foraging habitat depends on ad- equate precipitation and resultant ponding or overbank flooding, and water-control infrastructure (i.e., levees, dikes, water-control structures, pumps) to facilitate flooding. The rationale and methodology used to develop these waterfowl population goals and habitat objectives for waterfowl have been published previously (Lower Mississippi Valley Joint In: Bonney, Rick; Pashley, David N.; Cooper, Robert J.; Niles, Larry, Venture Management Board 1990; Loesch and others 1994). eds. 2000. Strategies for bird conservation: The Partners in Flight plan- Refer to these documents for details and clarification of ning process; Proceedings of the 3rd Partners in Flight Workshop; 1995 October 1-5; Cape May, NJ. Proceedings RMRS-P-16. Ogden, UT: U.S. waterfowl goals and objectives. Department of Agriculture, Forest Service, Rocky Mountain Research Station. Charles R. Loesch, USFWS Habitat and Population Evaluation Team, 3425 Miriam Ave. Bismarck, ND 58501. Daniel J. Twedt, USGS Patuxent Shorebirds _____________________ Wildlife Research Center, 2524 South Frontage Road, Vicksburg, MS 39180. Kimberly Tripp and William C. Hunter, U.S. Fish and Wildlife Service, 1875 Although some shorebirds breed (Robbins and others Century Boulevard, Suite 200, Atlanta, GA 30345. Mark S. Woodrey, Missis- 1986) or winter (Ouchley 1992) in the MAV, many more sippi Department of Wildlife, Fisheries and Parks, Mississippi Museum of Natural Science, 111 North Jefferson Street, Jackson, MS 39201. shorebirds, both total individuals and species, use this floodplain as a migratory corridor between breeding areas to 8 USDA Forest Service Proceedings RMRS-P-16. 2000 the north and wintering areas to the south (Helmers 1994; Establishing Shorebird Population Twedt and others 1998) (table 1). Thus, we feel that the greatest conservation need for shorebirds within the MAV is Goals _________________________ foraging habitat during migration. Neither census data nor any specific estimates of shore- Typically, winter floodwater that recedes during early bird populations moving through the MAV during south- spring and the agricultural practice of shallow-flooding rice ward migration are available. To establish such an estimate fields during late spring provide abundant shallow-water and thereby set a tentative population goal, we examined and mudflat foraging habitat within the MAV during north- data from International Shorebird Survey sites (Manomet ward migration. During southward migration, however, in Bird Observatory 1993) and consulted shorebird biologists late summer and fall, naturally occurring floodwater is rare (e.g., D. L. Helmers and B. A. Harrington) knowledgeable of because of seasonally low precipitation. Also, agricultural migration patterns and continental population estimates fields are purposefully kept dry at this time to facilitate (Howe and others 1989). Based on these sources, we have harvest of crops. Therefore, the period from 15 July through assumed that about 0.5 million shorebirds (table 1) move 30 September has tentatively been identified as the time through the MAV during fall migration. Maintenance of this interval when foraging habitat for migrating shorebirds is number is our population goal. This is a relatively unambi- least available. Our primary conservation objective is to tious effort to maintain the assumed status quo, and should ensure that adequate shallow-water habitat is available in be reexamined within the context of evolving continent-wide the MAV to meet or exceed the foraging requirements of goals for shorebird populations. shorebirds during their southward migration. Table 1—Shorebird species, mass, and hypothesized abundance during southward migration through the Mississippi Alluvial Valley (Manomet Bird Observatory 1993). Common name Scientific name Mass (g) Abundance Wilson’s Phalarope Phalaropus tricolor 50 171 American Avocet Recurvirostra americana 150 232 Black-necked Stilt Himantopus mexicanus 125 778 Common Snipe Gallinago gallinago 150 2,374 Dowitcher species Limnodromus spp. 125 2,242 Stilt Sandpiper Calidris himantopus 75 3,310 Red Knot Calidris canutus 140 162 Pectoral Sandpiper Calidris melanotos 60 121,077 White-rumped Sandpiper Calidris fuscicollis 40 221 Baird’s Sandpiper Calidris bairdii 40 690 Least Sandpiper Calidris minutilla 25 151,119 Dunlin Calidris alpina 35 7,866 Semipalmated Sandpiper Calidris pusilla 30 37,713 Western Sandpiper Calidris mauri 30 3,382 Sanderling Calidris alba 60 5,052 Calidris spp. (‘peeps’) Calidris spp. 30 32,286 Marbled Godwit Limosa fedoa 200 39 Greater Yellowlegs Tringa melanoleuca 125 3,235 Lesser Yellowlegs Tringa flavipes 75 21,120 Solitary Sandpiper Tringa solitaria 60 2,608 Willet Catoptrophorus semipalmatus 175 92 Upland Sandpiper Bartramia longicauda 125 237 Buff-breasted Sandpiper Tryngites subruficollis 50 964 Spotted Sandpiper Actitis macularia 40 4,112 Black-bellied Plover Pluvialis squatarola 150 769 American Golden-Plover Pluvialis dominica 130 449 Killdeer Charadrius vociferus 50 91,838 Semipalmated Plover Charadrius semipalmatus 35 4,765 Piping Plover Charadrius melodus 40 121 Ruddy Turnstone Arenaria interpres 140 405 Other shorebirds 40 571 mean weighted mass = 45 total = 500,000 USDA Forest Service Proceedings RMRS-P-16. 2000 9 Estimating Forage Needs of Determining Habitat Requirements Shorebirds During Migration ______ for Migrating Shorebirds _________ Although data on the composition of species moving through For the purpose of proposing the amount of habitat re- the MAV are fragmentary, some information for the MAV quired to support migrating shorebirds, we have assumed during southward migration is available from International that habitat will be provided primarily in the form of shallow Shorebird Survey sites as well as from local study sites (e.g., water managed to create optimal foraging depths for shore- Reid and others 1983; Ouchley 1992; Twedt and others birds and about 2 g of benthic invertebrates are available per 1998). These data indicate
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