2001Europe PMC (PubMed Central)Requires access

Dabbling duck production from a wild rice farming landscape in northwest Minnesota

Jay T. Huseby, W. Daniel Svedarsky, R. D. Crawford

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Abstract

A primary concern for waterfowl managers is continued loss and modification of natural habitats and resulting effects on waterfowl populations. Thus it is increasingly important to understand use of manipulated environments. We studied the use by breeding dab- bling ducks of cultivated wild rice (Zizania palustris) paddies and associated uplands in northwestern Minnesota during 1993-95. During 3 field seasons, we recorded an aver- age of 1,196 (SE=285.9) breeding pairs (0.80 pairs/ha of wild rice paddy) on the study area. Mallards (Anasplatyrhynchos), blue-winged teal (Anas discors), and northern shov- elers (Anas clypeata) comprised >950/o of the breeding population. We monitored 336 nests, and Mayfield's estimate of nesting success was 1 9.90/o (950/o C1 = 1 5.9-25.0%), with an average clutch size of 10.0 eggs (SE=0.13). We used nest success as a conservative estimate of hen success because we could not generate a reliable estimate of renesting rate from our data. Kaplan-Meier survival estimates for 70 radio-marked mallard duck- lings from 19 broods was 42% (95% CI=25-58%). A production estimate from our 3,444-ha study area was 999 fledged ducklings/year (0.29/ha) and about 0.67 duck- ling/ha of wild rice paddy. Because wild rice production areas can attract and concen- trate large numbers of breeding waterfowl, techniques that increase nest success and duckling survival (e.g., preserving large blocks of nesting cover, deploying secure nesting structures, and predator control) should be considered to maximize local production.

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What this paper is about

A primary concern for waterfowl managers is continued loss and modification of natural habitats and resulting effects on waterfowl populations. Thus it is increasingly important to understand use of manipulated environments. We studied the use by breeding dab- bling ducks of cultivated wild rice (Zizania palustris) paddies and associated uplands in northwestern Minnesota during 1993-95. During 3 field seasons, we recorded an aver- age of 1,196 (SE=285.9) breeding pairs (0.80 pairs/ha of wild rice paddy) on the study area. Mallards (Anasplatyrhynchos), blue-winged teal (Anas discors), and northern shov- elers (Anas clypeata) comprised >950/o of the breeding population. We monitored 336 nests, and Mayfield's estimate of nesting success was 1 9.90/o (950/o C1 = 1 5.9-25.0%), with an average clutch size of 10.0 eggs (SE=0.13). We used nest success as a conservative estimate of hen success because we could not generate a reliable estimate of renesting rate from our data. Kaplan-Meier survival estimates for 70 radio-marked mallard duck- lings from 19 broods was 42% (95% CI=25-58%). A production estimate from our 3,444-ha study area was 999 fledged ducklings/year (0.29/ha) and about 0.67 duck- ling/ha of wild rice paddy. Because wild rice production areas can attract and concen- trate large numbers of breeding waterfowl, techniques that increase nest success and duckling survival (e.g., preserving large blocks of nesting cover, deploying secure nesting structures, and predator control) should be considered to maximize local production.

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Available abstract

A primary concern for waterfowl managers is continued loss and modification of natural habitats and resulting effects on waterfowl populations. Thus it is increasingly important to understand use of manipulated environments. We studied the use by breeding dab- bling ducks of cultivated wild rice (Zizania palustris) paddies and associated uplands in northwestern Minnesota during 1993-95. During 3 field seasons, we recorded an aver- age of 1,196 (SE=285.9) breeding pairs (0.80 pairs/ha of wild rice paddy) on the study area. Mallards (Anasplatyrhynchos), blue-winged teal (Anas discors), and northern shov- elers (Anas clypeata) comprised >950/o of the breeding population. We monitored 336 nests, and Mayfield's estimate of nesting success was 1 9.90/o (950/o C1 = 1 5.9-25.0%), with an average clutch size of 10.0 eggs (SE=0.13). We used nest success as a conservative estimate of hen success because we could not generate a reliable estimate of renesting rate from our data. Kaplan-Meier survival estimates for 70 radio-marked mallard duck- lings from 19 broods was 42% (95% CI=25-58%). A production estimate from our 3,444-ha study area was 999 fledged ducklings/year (0.29/ha) and about 0.67 duck- ling/ha of wild rice paddy. Because wild rice production areas can attract and concen- trate large numbers of breeding waterfowl, techniques that increase nest success and duckling survival (e.g., preserving large blocks of nesting cover, deploying secure nesting structures, and predator control) should be considered to maximize local production.

Key concepts: Waterfowl, Anas, Nest (protein structural motif), Biology, Predation, Breeding pair, Anatidae, Population

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