Habitat Management for Shorebirds

 
 
     Shorebird habitat is either natural (unmanaged) or artificially managed by impoundment and hydrological control. An impoundment is a wetland that has been ditched and diked. It can be isolated from the estuary and other impoundments or it can be connected through culverts between the dike and estuary or neighboring impoundments.

      Culverts enable wetland managers to control the water depth inside the impoundment. Standard water control mechanisms include riser boards and flap gates which block the inflow or outflow of water. Several riser boards slide into a slot at the culvert mouth. Individual boards can be added or removed according to seasonal water depth objectives. Similarly, flap gates can be propped open, clamped shut, or left loose to flap open with the influx of water from the estuary. Culverts are typically capped on the impoundment-interior side, but culverts capped on both ends provide for better water control capabilities.


 
photo of duck

     Impoundments were traditionally created for two purposes: to control mosquitoes and to promote growth of waterfowl food plants (and concurrently, to prevent the growth of undesirable aquatic plants). Wetland managers are now making efforts to manage impoundments for several avian species, including waterfowl (ducks,geese, gallinaceous birds), shorebirds, and wading birds(herons, egrets, storks), as well as nonavian species (fish, invertebrates). 

     To do this, they need to know what time of year each avian group has need of the wetland, what their water depth and food resource requirements are, and how these specifications dictate management practices. For effective and practical management, it is helpful to have some baseline data on habitat selection by different species, species population sizes, prey availability, and of course, knowledge of weather patterns at a particular wetland area (e.g., a refuge).


 

Deep water presents foraging challenges for medium
sized calidrids, such as these Short-billed Dowitchers.

Water Depth

Wetlands managed for shorebirds should be kept shallow, no deeper than 10 cm for the larger species. This is necessary due to physical size constraints (body height, leg length) and foraging techniques (for example, probing and gleaning).


 

     Management Strategy

Management should limit vegetation cover so that the habitat remains relatively open for improved ability to detect predators. Locations targeting shorebirds should provide an adequate prey base for migrants, so soil substrate properties and colonization potential (e.g., culverts open for immigration of invertebrates) should be taken into consideration. Many refuges hold water deep throughout the late summer, into fall and winter for waterfowl. The water is then drawndown in late winter, around the time that waterfowl begin migrating out and shorebirds start to arrive. 

graph of Moist Soil Management
     The simultaneous occurance of waterfowl and shorebirds in some southern latitudes (e.g. Florida in the winter) makes it even more crucial to designate certain impoundments for waterfowl and other impoundment units for shorebirds, since these avian groups have opposing water depth requirements.
Shorebirds and waterfowl are temporally separated at PINWR There is temporal overlap of shorebirds and waterfowl at MINWR during the winter.

 
 
 
 
 
     Natural, unmanaged shorebird habitat include beaches, tide pools, and some marshes. Most "management" efforts in unaltered areas are proactive, for example, limiting disturbance by humans. This is especially important for nesting plovers and oystercatchers. Beach dredging and filling is a current issue, since dredge deposits have been shown to have a negative impact on invertebrate communities (i.e., shorebird prey) in the sand. photo of beach sign
warning against disturbance
of nesting birds

 

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