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appendix b final 2008 biological surveys of los angeles and long ...

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9.0 Birds<br />

9.0 BIRDS<br />

9.1 INTRODUCTION<br />

Southern California’s coastal areas, including its shorelines, estuaries, bays, <strong>and</strong> harbors,<br />

provide several types <strong>of</strong> habitat for large numbers <strong>of</strong> waterfowl, shorebirds, wading birds, <strong>and</strong><br />

birds that forage from the air. The open water <strong>and</strong> other habitats within the Ports <strong>of</strong> Long Beach<br />

<strong>and</strong> Los Angeles (Ports) provide opportunities for nesting, foraging, <strong>and</strong> resting by a diversity <strong>of</strong><br />

bird species, including three species listed as endangered by the California <strong>and</strong>/or Federal<br />

Endangered Species Acts: California Brown Pelican, California Least Tern, <strong>and</strong> Peregrine<br />

Falcon. The Ports have conducted several previous studies <strong>of</strong> the avifauna over the past thirty<br />

years to document bird use <strong>of</strong> Port habitats; the current study represents a continuation <strong>of</strong> those<br />

efforts.<br />

9.2 METHODOLOGY<br />

9.2.1 Field Surveys<br />

Methods used in the current study were<br />

similar to those <strong>of</strong> the 2000 baseline study<br />

(MEC 2002), including the same 31 survey<br />

zones (Figure 9.2-1). The survey zones<br />

generally correspond to those established<br />

during the 1983–1984 (MBC 1984) <strong>and</strong><br />

1986–1987 (MEC 1988) studies. Survey<br />

zones number from 1–15 <strong>and</strong> 19–34; the<br />

gap in the numbering sequence (16–18)<br />

reflects minor modifications to eliminate<br />

overlaps among studies <strong>and</strong> changes in<br />

harbor development, including the Pier 400<br />

l<strong>and</strong>fill <strong>and</strong> Pier J expansion (MEC 2002).<br />

Saturation <strong>surveys</strong> were completed from a<br />

boat in all survey zones. Bird counts were<br />

conducted with binoculars by one observer <strong>and</strong> recorded by another observer who assisted with<br />

observations. Boat travel within survey zones was conducted in a manner that minimized<br />

flushing <strong>of</strong> birds to avoid double counts or observer-induced changes in bird behavior or habitat<br />

use.<br />

A total <strong>of</strong> 20 <strong>surveys</strong> were conducted twice monthly from December 14 through March 22 <strong>and</strong><br />

from August 14 through November 23, <strong>and</strong> once monthly from April 10 through July 26. For<br />

months with two <strong>surveys</strong>, they are designated as survey “A” <strong>and</strong> “B” in the report text <strong>and</strong><br />

graphics. Surveys were more frequent during the fall <strong>and</strong> winter months to more thoroughly<br />

document the increase in avian activity that typically occurs in southern California during postbreeding<br />

dispersal, migration, <strong>and</strong> over-wintering; previous <strong>surveys</strong> (MBC 1984, MEC 1988,<br />

MEC 2002) also used this survey frequency. Each survey was conducted under suitable<br />

environmental conditions over a two- to three-day period, beginning early in the morning <strong>and</strong><br />

ending in the late morning or early afternoon. Surveys were discontinued for the day if high<br />

winds, fog-limited visibility, rain, or other factors were deemed to be unsuitable for accurate <strong>and</strong><br />

effective data collection.<br />

Data recorded for each observation included species identity, numbers <strong>of</strong> individuals, habitat in<br />

which the birds occurred, <strong>and</strong> bird activity. Habitats were designated as anchor line, bridge,<br />

<strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors 9–1<br />

April 2010

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