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S.R. Derrickson

Publications and source records attributed to S.R. Derrickson.

18 recordsLinked to original sources

Limitations of captive breeding in endangered species recovery

The use of captive breeding in species recovery has grown enormously in recent years, but without a concurrent growth in appreciation of its limitations. Problems with (1) establishing self-sufficient captive populations, (2) poor success in reintroductions, (3) high costs, (4) domestication, (5) preemption of other recovery techniques, (6) disease outbreaks, and (7) maintaining administrative continuity have all been significant. The technique has often been invoked prematurely and should not normally be employed before a careful field evaluation of costs and benefits of all conservation alternatives has been accomplished and a determination made that captive breeding is essential for species survival. Merely demonstrating that a species’ population is declining or has fallen below what may be a minimum viable size does not constitute enough analysis to justify captive breeding as a recovery measure. Captive breeding should be viewed as a last resort in species recovery and not a prophylactic or long-term solution because of the inexorable genetic and phenotypic changes that occur in captive environments. Captive breeding can play a crucial role in recovery of some species for which effective alternatives are unavailable in the short term. However, it should not displace habitat and ecosystem protection nor should it be invoked in the absence of comprehensive efforts to maintain or restore populations in wild habitats. Zoological institutions with captive breeding programs should operate under carefully defined conditions of disease prevention and genetic/behavioral management. More important, these institutions should help preserve biodiversity through their capacities for public education, professional training, research, and support of in situ conservation efforts.

Conservation Biology↗

The scientific bases for preservation of the Mariana crow

The Panel recently released the report and recommendations resulting from its work over the last six months. Although primarily focused on the Mariana Crow, the report highlights that this is a matter potentially far more serious than the preservation of the crow on Guam and Rota. The report includes major sections dealing with the need to intensify research and control activities on the Brown Tree Snake both on Guam and in all appropriate areas to which the snake could spread if uncontained and on the population biology and behavior of the Mariana Crow on Guam and Rota.

Book↗

Migrational homing by a pair of mallards

It is generally assumed that wild, North American female dabbling ducks (Anatinae: Anatini) select new mates each year and may return to the same nesting areas in consecutive years (McKinney 1964, Wildfowl 16: 93). Lincoln (1934, Bird-Banding 5: 151) first documented migrational homing in a female Mallard ( Anas platyrhynchos ), and Sowls (1955, Prairie ducks, Harrisburg, Pennsylvania, Stackpole Co., pp. 25-45), working with color-marked birds, established that female Pintails ( A. acuta ), Gadwalls ( A. strepera ), Shovelers ( A. clypeata ), and Blue-winged Teal ( A. discors ) also return to previously used nesting areas. Black-bellied Tree Ducks ( Dendrocygna autumnalis ), in the same subfamily as the true geese (Anserinae), not only home to previously used nesting sites, but also retain the same mates in consecutive years (Bolen 1971, J. Wildl. Mgmt. 35: 386). Instances are recorded of males in the subfamily Anatinae returning to the same locality in consecutive years (Sowls, ibid.; Lewis Cowardin, pers. comm.), but no information exists on the homing of pairs. During the course of a study on the social behavior and habitat use of various dabbling ducks in North Dakota, we documented the migrational homing of a pair of Mallards. On 6 May 1971 we captured a pair of Mallards in a cannon-net trap and affixed numbered nasal saddles and a miniature radio transmitter to both the hen and drake. The drake's transmitter failed in a few days, but the hen's transmitter allowed us to locate the pair several times until 2 June 1971. Our last record for the hen was on 15 June 1971. We never found a nest site, and feel that she did not raise a brood.

The Auk↗