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Henslow’s sparrow (Ammodramus henslowii)<br />

Henslow‟s sparrows, a SGCN, were recorded in 2009 <strong>and</strong> were observed for four of the<br />

past five years at AHATS during INRMP surveys. None were observed during 2008. However,<br />

this could be due to the timing of 2008 surveys which were later than the previous five years, or<br />

could indicate that 2006 was the peak of a local eruption of the species (Figure 67). Henslow‟s<br />

sparrow sightings increased in the Minnesota region during the summer of 2005, the year they<br />

were first observed at AHATS. Possible causes for increased sightings may be due to a temporary<br />

population increase, a temporary population shift from another area, or a true population increase.<br />

Annual monitoring will provide information regarding their continued presence on AHATS<br />

(Dirks et al. 2009).<br />

Henslow‟s sparrows are listed as endangered by the MNDNR <strong>and</strong> six other states, but are<br />

not listed by the U.S. Fish <strong>and</strong> Wildlife Service. This species usually breeds in the grassl<strong>and</strong>s to<br />

the south <strong>and</strong> east of Minnesota. The nationwide population of this grassl<strong>and</strong> bird species has<br />

declined nearly 80 percent since 1966, due to habitat destruction <strong>and</strong>/or reforestation (National<br />

Audubon Society 2007). Management for this species should provide for large areas of suitable<br />

habitat, prevention of disturbance during the breeding season, <strong>and</strong> the control of succession<br />

(Herkert et al. 2003). Suitable habitat is usually tall, dense grass with a deep litter layer <strong>and</strong><br />

scattered tall forbs for perching. Periodic disturbance, such as prescribed fire, may be essential to<br />

maintaining suitable habitat; even though it will likely reduce the suitability of the grassl<strong>and</strong><br />

during the treatment year. Trees <strong>and</strong> shrubs should be eliminated in the center <strong>and</strong> along the<br />

edges of grassl<strong>and</strong> areas to discourage predators <strong>and</strong> nest parasites such as the brown-headed<br />

cowbird. The grassl<strong>and</strong> areas where Henslow‟s sparrows were located should not all be burned in<br />

the same year, allowing some habitat to remain each year. These grassl<strong>and</strong>s should be burned on<br />

a four or five year rotation, since it may take several years for the habitat to regain suitable<br />

structure for nesting Henslow‟s sparrows (Dirks et al. 2009). Habitat requirements <strong>and</strong><br />

management for Henslow‟s sparrows will be included in the development of future habitat<br />

restoration plans.<br />

Osprey (P<strong>and</strong>ion haleaetus)<br />

During the 2009 nesting season, an osprey (P<strong>and</strong>ion haleaetus) pair was observed on the<br />

nesting platform at Marsden Lake. In July, two female osprey chicks were b<strong>and</strong>ed <strong>and</strong> one<br />

unhatched egg was also found. The osprey chick b<strong>and</strong>ing was conducted in cooperation with the<br />

University of Minnesota Raptor Center <strong>and</strong> Excel Energy, who provided the bucket truck for<br />

access to the platform.<br />

Bird Nest Boxes<br />

Nest boxes have been installed at AHATS in previous years by the Audubon Society <strong>and</strong><br />

other local groups. These nest boxes are monitored <strong>and</strong> maintained by Craig Andreson, a<br />

volunteer with the St. Paul Audubon Society. In 2009, 388 bluebird nest boxes fledged<br />

approximately 415 eastern bluebirds, 250 tree swallows, <strong>and</strong> over 200 house wrens. In addition,<br />

2009 Conservation Program Report<br />

Page 100

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