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Pacific Island Ecosystems Research Center

Laysan Duck
(Anas laysanensis)

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"Translocation Feasibility of the Laysan Teal: Executive Summary"(Anas laysanensis)



The Laysan Duck, Anas laysanensis, has the most restricted range of any duck species, and is especially vulnerable to extinction because of its small population size. Laysan Island, part of the Northwestern Hawaiian Islands National Wildlife Refuge is the last refugia of this endangered species. These unique birds were formerly believed to be endemic to Laysan, until new evidence revealed Laysan Ducks were previously common and widespread in the Hawaiian archipelago. Important background information on ecosystem parameters, foraging, diet, and population dynamics is critical to management of this endangered species. This report summarizes 1998 to 1999 preliminary data from field studies on Laysan and on captive Laysan Ducks.

The Laysan Duck Recovery Plan (USFWS 1982) recommends evaluating "reintroduction" sites after the evaluation of field data. The need for this information has been identified by the USFWS Remote Island Team, USFWS Refuge biologists and managers, the USGS-BRD Pacific Islands Ecosystems Research Center, the Laysan Duck Recovery Plan (USFWS 1982), and Ducks Unlimited, Inc.

The USFWS initiated cooperative field studies in 1998 to improve population-monitoring techniques and examine poorly understood aspects of the duck's ecology to benefit recovery planning. The wild population of Laysan Ducks is approximately 322 (plus or minus 33) adults (1999 USGS data). Population monitoring from 1991 to 1999 suggests that droughts during periods of high population density are correlated with population crashes (USFWS data). In periods of lower population densities on Laysan, drought conditions resulted in poor reproductive success and recruitment (1998 USGS USFWS unpub. data). Despite a good breeding year in 1999, field studies indicate that the population growth appears to be limited by duckling survival (1998 to 1999 USGS unpub. data). Causes for high duckling mortality will be examined in the year 2000 breeding season.

Field studies indicate that the ducks have a varied diet, flexible foraging behaviors, and seasonal food shifts. Ducks spent more time foraging and foraged more on terrestrial invertebrates during dry conditions on Laysan in 1998. Terrestrial invertebrates are essential components of the duck's foraging ecology, especially during periods of drought when the wetland invertebrates are less abundant (USGS data). The survival of Laysan Ducks in the wild is dependent on the absence of introduced predators, competitors, and diseases.

Data suggest that the Laysan Duck's wide range of foraging behaviors is favorable to establishing the birds on additional islands. Laysan Ducks could utilize a restored environment with a variety of foraging substrates and prey items. We recommend fledged juveniles as the best candidates for wild translocation, and wild egg removal for establishment of a new captive flock in Hawaii to produce birds for release. The existing captive Laysan Duck stock is unsuitable for release into the wild. We also provide an evaluation of select translocation sites, and recommend necessary habitat restoration for translocation sites. We describe aspects of the duck's ecology and the range of resources (invertebrate prey, water, vegetation, and predators) under which successful translocation is possible, and predict suitability of potential release sites with respect to these resources. Of Hawaii's predator-free islands, Midway Atoll, Lisianski Island, Nihoa and Kure had the highest potential for habitat restoration and the establishment of additional Laysan Duck populations.

Timing translocation according to the population dynamics on Laysan is essential. Removal of birds during a population high point will prevent or reduce any negative impacts to the Laysan population. Post release monitoring and restoration efforts for release sites are required for establishment of new self-sustaining or minimally managed populations. Freshwater seep restoration or wetland creation, vegetative cover, absence of mammalian predators, and an abundant prey base are required at the release site.

Table 1. Habitat characteristics of the Main Hawaiian Islands

Island Size(ha) Site Estimated annual rainfall (mm) Surface fresh water Predators
Ni`ihau 25,500 Ni'ihau Playas 667 Moderate Dogs, Cats, Rats
Kauai 157,400 Wainiha Valley
Lumahai Valley
Hanalei NWR
Wailua/Opaekaa Valley
Huleia NWR
2000
2500
2000
1250
1250
Abundant Dogs, Cats, Rats
Oahu 162,400 Lualualei
Ukoa Marsh
Kahuku Point
Laie Wetlands
Waihee Marsh
Heeia Marsh
Nuupia Ponds
Kawainui Marsh
625
500
1250
1500
2000
1750
1250
1500
Abundant Dogs, Cats, Rats, Mongooses
Molokai 66,000 Molokai Playas
Kaunkakakai Wetlands
Kakahaia NWR
Paialoa Pond
250
375
625
750
Abundant Dogs, Cats, Rats, Mongooses
Lanai 35,500 Island (no site visit) 250-500 Abundant Dogs, Cats, Rats
Kaho`olawe 12,100 Deep Gullies, and Natural Gulches, coastal scrub and ephemeral wetlands
Lua Kealiaalo
Lua Keaialuna
Lua Makika
250-650 Limited Cats, Possibly Rats
Maui 182,700 Kanaha Pond Sanctuary
Kealia Pond NWR
Koanae Point
Nuu Pond
500
375
2000
1500
Abundant Dogs, Cats, Rats, Mongooses
Hawaii 1,045,800 Polulu Valley
Waimanu Valley
Waipio Valley
Loko Waka Ponds
Keanae Pond
Koloko Pond
Opaeula Pond
Aimakapa Pond
1875
2000
2000
3000
3000
250
250
250
Abundant Dogs, Cats, Rats, Mongooses

Table 2. Habitat descriptions of the Northwestern Hawaiian Islands.

Island Size(ha) Elevation(m) Annual rainfall(mm) Surface Fresh water Cover Predators TotalArthropodSpecies1 Preybase
Kure Atoll 100 6 1100 Absent Yes Absent 141 Moderate
Midway Atoll 626 5 1121 - Yes Absent 332 Moderate
Sand   5 - Limited Limited Absent - Moderate
Eastern 135 4 - Absent Limited Absent - Moderate
Spit   2 - Absent Limited Absent - Limited
Pearl and Hermes 30 3 700-1000 Absent No Absent 94 Limited
South East   2 - Absent No Absent - Limited
North   3 - Absent Yes Absent - Limited
Kittery   2 - Absent No Absent - Limited
Lisianski 150 8 700-1000 Absent Yes Absent 50 Moderate
Laysan 410 12 700-1000 Limited-Moderate Yes Absent 216 Seasonally Abundant
French Frigate Shoal 26 1-3 700-1000 Absent No Absent 73 Limited
Tern 10 2 - Absent No Absent - Limited
East 2 - Absent Limited Absent - Unknown
Necker 18 83 500 -750 Limited No Absent 73 Unknown
Nihoa 68 269 750 Moderate Yes Absent 166 Moderate
1 Currently known species diversity of the Northwestern Hawaiian Islands from Hawaii Biological Survey, Gordon Nishida, 1998. Lisianski and Necker are likely to be under-collected.

Table 3. Vegetative structure of potential reintroduction sites using Robel's analysis of nesting habitat.
Higher nesting success of ducks is associated with greater visual obscurity.

Date Island HabitatType Mean ht. cm Visual Obscurity % Freq.Veg1 % Freq.Weed2
7 Jun 99 Laysan Grassy 42 5.2 45 2
7 Jun 99 Laysan Viney 12 3.1 70 0
7 Jun 99 Laysan Wetland 25 4 75 0
11 Jun 99 Lisianski Grassy 67 6.9 69 0
11 Jun 99 Lisianski Viney 15 2.9 84 2
14 Jun 99 Pearl and Hermes -North Is Grassy 42 4.2 61 21
14 Jun 99 Pearl and Hermes -North Is Viney 19 1.6 80 0
15 Jun 99 Pearl and Hermes -South East Is Matted 7 1.6 57 35
15 Jun 99 Pearl and Hermes -South East Is Viney 11 1.7 34 0
 1 % Frequency vegetation is determined by point intercept every m along a 100 m transect.
 2 % Frequency weeds = the % of vegetated point intercepts with non-native species. All weeds found were not suitable nesting cover.

Table 4. Habitat assessments outside of the species known range.

Island Size(ha) Annual rainfall(mm) Surface fresh water Cover Predators/Feral Ungulates1 Preybase
Washington 1400 3000 Abundant Good U/U Unknown
Palmyra 1191 4200 Moderate Moderate Y/U Unknown
Fanning Atoll 3500 2000 Moderate Unknown Y/U Unknown
Pagan 4800 2000-2500 Abundant Good U/Y Unknown
Alamagam 4400 2000-2500 Limited Moderate U/Y Unknown
Guguan   2000-2500 Limited Moderate U/N Unknown

1 U=Unknown, N=No, Y=Yes

Table 5. Summary of assets and liabilities of preferred sites evaluated for possible reintroduction of Laysan Duck.

Assets Kure(Green Island) Midway(Eastern and Spit Islands) Lisianski Nihoa Kahoolawe Kauai(Hanalei) Niihau
Size of habitat Small Moderate Moderate Small Large Large Large
Fresh water Limited;Creation feasible Limited Creation feasible Limited,Restoration feasible Available Limited,Ephemeral wetlands and gulches present, wetland enhancement Proposed Abundant Abundant
Nesting cover Moderate Low, but restoration ongoing Excellent Good Moderate with restoration ongoing Good Unknown
Predicted food abundance Moderate Moderate to high Moderate Good Moderate Abundant Abundant
Logistic feasibility Limited High Moderate Difficult Moderate High Difficult
Plant foods Low Moderate Moderate Moderate Low Abundant Unknown
Infrastructure Some Good None None Some Good Some
Land Management DLNR Wildlife Reserve USFWS Wildlife Refuge and Historical Site USFWS Wildlife Refuge USFWS Wildlife Refuge KIRC Cultural and Ecological USFWS Wildlife Refuge Privately owned Ranch
Liabilities              
Human disturbance or hazards Minimal Minimal on East and Spit Islands,Moderate onSand Minimal None Minimal, after ordnance removal Moderate Unknown
Food competitors(mice, predatory alien insects) Low-moderate Low-moderate Low Low-moderate Low-moderate Moderate unknown
Disease Low? Low? Low? Low? Low? Low? Unknown
Predators No No No No Yes Yes Yes
Management Required Freshwater source 1)Revegetation 2)Freshwater source Freshwater source None Predator removal Predator removal Predator removal
Management Beneficial Weed and ant control Weed, ant, mice control Weed and ant control Unknown Wetland restoration, mice control Upland Veg. restoration Upland Veg. restoration





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