Chapters 1 - U.S. Fish and Wildlife Service
Chapters 1 - U.S. Fish and Wildlife Service
Chapters 1 - U.S. Fish and Wildlife Service
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Chapter 3 <br />
For the California least tern, annual pre-nesting site preparation involves killing weedy<br />
vegetation at the NASA Isl<strong>and</strong> nesting site through the use of chemical or mechanical means;<br />
cleaning up any debris <strong>and</strong>/or trash; improving substrate quality when necessary by spreading<br />
additional clean, light s<strong>and</strong> <strong>and</strong> shell fragments over some or all of the site; inspecting <strong>and</strong><br />
repairing the electrified perimeter fence; <strong>and</strong> addressing any erosion problems around the<br />
outer edges of the nesting site. In 2007, approximately 40 percent of NASA Isl<strong>and</strong> was<br />
mechanically scraped <strong>and</strong> clean, light s<strong>and</strong> was deposited over the prepared area. Volunteers<br />
then assisted in manually removing vegetation from the remainder of the site. This was<br />
followed in 2008 by the placement of crushed oyster shells on those areas of the site that were<br />
recently covered in clean s<strong>and</strong>. Vegetation growing on the site is normally killed in late winter<br />
through use of approved herbicides or salt water treatments.<br />
California least tern monitoring begins at NASA Isl<strong>and</strong> when the first least terns are observed<br />
on the Refuge, which is generally between April <strong>and</strong> early May of each year. Monitoring is<br />
conducted one day per week until the terns leave the nest site, which usually occurs in late July<br />
or August each year. To monitor the nesting terns, terra cotta tiles are placed inside the<br />
colony for grid marking. These tiles also provide protection for tern chicks from avian<br />
predators. The grid spacing is generally set at 30 feet. This grid assists the tern monitors in<br />
recording <strong>and</strong> mapping tern nests. Monitoring data provide information about the number of<br />
adults present at the nesting site, the numbers of nests, chicks, <strong>and</strong> successful fledges, <strong>and</strong><br />
information about adult, chick, <strong>and</strong>/or egg mortality <strong>and</strong>/or predation. This monitoring data<br />
are provided to the California Department of <strong>Fish</strong> <strong>and</strong> Game for inclusion in the statewide<br />
California Least Tern Annual Report <strong>and</strong> are also maintained at the Refuge Headquarters for<br />
use in comparing population levels <strong>and</strong> productivity from year to year <strong>and</strong> over extended<br />
periods of time.<br />
To reduce the potential for predation by avian predators, particularly crows, ravens, <strong>and</strong> gulls,<br />
a least tern predator monitoring program is implemented annually on the Refuge during the<br />
nesting season. This program, often referred to as the Eyes on the Colony Program, involves<br />
the use of volunteers <strong>and</strong>/or contractors who are stationed at a lookout site a short distance<br />
from the nesting colony. From this location, they can observe the activities going on at the<br />
nesting site. When participants observe potential avian predators in the vicinity of the nesting<br />
colony, they take actions to haze (scare off) the potential predators from entering the site.<br />
Participants stay in contact with the Refuge Manager to provide updates on site conditions <strong>and</strong><br />
nesting activity, as well as to report potential threats or apparent evidence of predation<br />
activity.<br />
Pre-nesting season preparation for the light-footed clapper rail involves conducting annual<br />
inspections of, <strong>and</strong> when necessary, repairs to the clapper rail nesting platforms that have been<br />
placed within the marsh (refer to Chapter 4 for additional information). Navy contractors <strong>and</strong><br />
Refuge volunteers assist the Refuge Manager in this task. The design of these platforms is<br />
continually being improved to ensure that the rails have safe <strong>and</strong> secure locations to nest <strong>and</strong><br />
take refuge during higher high tide events that occur throughout the year. Each year a<br />
number of new platforms are placed within the marsh to replace old or damaged platforms.<br />
From 2003 to 2008, the total number of nesting platforms located within the Refuge was<br />
between 79 <strong>and</strong> 82 (Hoffman 2009).<br />
Light-footed clapper rail monitoring involves annual fall high tide counts <strong>and</strong> spring call<br />
counts. Fall high tide counts are conducted at least once a year in the fall during daytime +6.7<br />
foot or higher tides in order to estimate the overall Refuge population. Spring call counts are<br />
conducted annually during early phases of rail breeding, usually in March or April in order to<br />
3-14 Seal Beach National <strong>Wildlife</strong> Refuge