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

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9.0 Birds<br />

<strong>surveys</strong> at a subset <strong>of</strong> harbor locations in contrast to other historical studies that included at<br />

least monthly <strong>surveys</strong>.<br />

Differences in survey methods also may contribute to differences in the number <strong>of</strong> birds counted<br />

between recent <strong>and</strong> historical studies (Figure 9.6-2). The current <strong>and</strong> 2000–2001 (MEC 2002)<br />

<strong>surveys</strong> covered more open water than previous studies. Open water, a<strong>long</strong> with riprap <strong>and</strong><br />

dock/pilings, supports the greatest numbers <strong>of</strong> birds in the Ports. On average, several thous<strong>and</strong><br />

birds were counted per survey during these recent studies. Several thous<strong>and</strong> birds were also<br />

counted per survey during the 1973–1974 study <strong>of</strong> inner <strong>and</strong> outer harbor areas, even though<br />

those <strong>surveys</strong> excluded open-water habitat. In contrast, substantially fewer birds were counted<br />

when studies were limited to the outer harbor areas or were based on less frequent quarterly<br />

<strong>surveys</strong> (HEP 1979, MBC 1984, MEC 1988). Due to the fidelity <strong>of</strong> a number <strong>of</strong> species to<br />

particular habitats <strong>and</strong> location (e.g., Brown Pelicans <strong>and</strong> Black Oystercatchers on outer<br />

breakwaters, <strong>and</strong> Western Gulls on inner harbor docks), an increase in survey area generally<br />

corresponded to an increase in total abundance <strong>of</strong> birds, but not necessarily to an increase in<br />

abundance <strong>of</strong> each individual species.<br />

Despite the differences associated with methodology, there have been changes in the relative<br />

abundance <strong>of</strong> some bird guilds over time (Figure 9.6-3). A major difference between earlier <strong>and</strong><br />

more recent studies has been the decrease in dominance by gulls <strong>and</strong> increase in other bird<br />

guilds. Some increases in other bird guilds (e.g., Upl<strong>and</strong> Birds, Waterfowl) are likely due to<br />

exp<strong>and</strong>ed survey areas in the more recent <strong>surveys</strong>. Recent nesting <strong>of</strong> Br<strong>and</strong>t’s <strong>and</strong> Doublecrested<br />

Cormorants also increased the percent contribution <strong>of</strong> Waterfowl in the current study.<br />

Increased nesting activity <strong>of</strong> Aerial Fish Foragers such as terns in the harbors has likely<br />

contributed to the substantial increase in the percent contribution <strong>of</strong> this bird guild over time. In<br />

addition, large numbers <strong>of</strong> Brown Pelicans roost at the Ports.<br />

In some cases, the inclusion <strong>of</strong> both inner <strong>and</strong> outer harbor areas in more recent <strong>surveys</strong> has<br />

contributed to a decrease in the percent contribution <strong>of</strong> guilds that are more associated with one<br />

but not both <strong>of</strong> these harbor areas. For example, the percent contribution <strong>of</strong> Shorebirds<br />

declined from 1986–1987 <strong>surveys</strong> to 2000–2001 <strong>surveys</strong>; MEC (2002) hypothesized this was<br />

due to limited shorebird habitat being present in the inner harbor. However, Shorebirds<br />

declined again during the current study, likely due to fewer observations <strong>of</strong> Western S<strong>and</strong>pipers<br />

(only 4 were observed in 2007–<strong>2008</strong> compared to nearly 300 in 2000–2001; MEC 2002). This<br />

may be due to differences in tidal fluctuations when this species would be present on the Ports’<br />

few mudflat <strong>and</strong> s<strong>and</strong>y beach habitats.<br />

Percent composition <strong>of</strong> Wading/Marsh Birds, which includes herons <strong>and</strong> egrets, has declined<br />

somewhat since the 1986–1987 <strong>surveys</strong> (Figure 9.6-3), likely due to inclusion <strong>of</strong> both inner <strong>and</strong><br />

outer harbor areas in more recent <strong>surveys</strong> <strong>and</strong> suitable habitat being limited in the inner harbor.<br />

Although most birds were observed resting during the current <strong>and</strong> previous studies, relatively<br />

more were observed foraging (18.8%) rather than resting (66.4%) during the current study<br />

compared to foraging (10.9%) <strong>and</strong> resting (76.8%) activities observed in 2000–2001 (MEC<br />

2002). Foraging activity in 2007–<strong>2008</strong> also was higher than in 1986–1987 (13%); MEC 1988).<br />

There was a notable increase in courting/nesting activity during the 2007–<strong>2008</strong> (2.9%)<br />

compared to 2000–2001 (0.3%) <strong>surveys</strong>.<br />

Table 9.6-1 provides a historical comparison <strong>of</strong> the percent contribution <strong>of</strong> the ten most<br />

abundant species during 2007–<strong>2008</strong> compared to historical <strong>surveys</strong> using yearly averages for<br />

each species relative to total birds counted. Some <strong>of</strong> the variations in abundance have been<br />

attributed to improvements in waste treatment practices. For example, HEP (1979) attributed a<br />

decrease in the number <strong>of</strong> gulls between the 1973–1974 <strong>and</strong> 1978 <strong>surveys</strong> to the initiation in<br />

the mid 1970s <strong>of</strong> secondary treatment <strong>of</strong> sewage <strong>and</strong> reduction <strong>of</strong> cannery waste in outer Los<br />

9–12 <strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors<br />

April 2010

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