<?xml version="1.0" encoding="UTF-8"?>
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<title>Studies in Oregon Ornithology/Yaquina Studies in Natural History</title>
<link href="http://hdl.handle.net/1957/8288" rel="alternate"/>
<subtitle/>
<id>http://hdl.handle.net/1957/8288</id>
<updated>2013-05-22T16:46:25Z</updated>
<dc:date>2013-05-22T16:46:25Z</dc:date>
<entry>
<title>Review : bird predation of juvenile salmonids and management of birds near 14 Columbia Basin dams</title>
<link href="http://hdl.handle.net/1957/8430" rel="alternate"/>
<author>
<name>Bayer, Range D., 1947-</name>
</author>
<id>http://hdl.handle.net/1957/8430</id>
<updated>2008-08-26T22:36:50Z</updated>
<published>2003-02-01T00:00:00Z</published>
<summary type="text">Review : bird predation of juvenile salmonids and management of birds near 14 Columbia Basin dams
Bayer, Range D., 1947-
Bird predation of juvenile salmonids and/or bird predation control are reviewed for 14 of the 18&#13;
mainstem dams on the Columbia and Snake Rivers, but there was little information for some of these dams.&#13;
California gulls, ring-billed gulls, Caspian terns, double-crested cormorants, American white&#13;
pelicans, and several other bird species have been reported as predators of juvenile salmon and steelhead at&#13;
these dams. Most estimates of the amount of this predation have been 2% or less of salmonids passing a&#13;
dam. This is less than the percentage of juvenile salmonids killed during dam passage, and it has not been&#13;
determined what proportion of salmonids taken by birds were already dead or mortally injured from dam&#13;
passage. Thus, it is not clear what portion of bird predation is of viable salmonids that would have&#13;
otherwise survived. Further, it appears that most juvenile salmonids in the Columbia Basin are not federally&#13;
listed as threatened or endangered, so it is not known what impact bird predation at dams may have on listed&#13;
salmonids. Nevertheless, predation may significantly affect certain salmon stocks, so it cannot be dismissed&#13;
as unimportant.&#13;
Bird management includes installing wires above the water at dam tailraces. Closely spaced wires&#13;
are effective in keeping out flying birds. However, not all areas where birds feed on fish below dams can be&#13;
covered with wires, the wires have sometimes been placed too far apart to keep out flying birds, and&#13;
nonflying birds can go under wires. Consequently, Wildlife Services (which was known as Animal&#13;
Damage Control prior to 1998) of the U.S. Department of Agriculture has also nonlethally harassed and&#13;
lethally taken birds at dams after it has been requested to do so. Studies by staff of the U.S. Army Corps of&#13;
Engineers have shown that nonlethal and lethal control by Washington Wildlife Services at The Dalles and&#13;
John Day Dams needed to be repeated because birds would return. During 1997-1998, Wildlife Services&#13;
dispersed at least 20,682 birds (mostly gulls) and lethally took at least 3,143 birds at these two dams.&#13;
Most juvenile salmonids migrate past dams from April through early June, although many&#13;
subyearling chinook migrate during July and August. Thus, bird control to protect juvenile salmonids&#13;
would be most effective during April-July and perhaps through August for subyearling chinook. Beginning&#13;
in August, many juvenile American shad are also migrating over lower Columbia dams and then can be&#13;
more abundant than migrating salmonids; however, few shad pass Snake River dams and at least one&#13;
mid-Columbia dam. Washington Wildlife Services' bird control has been during April-September&#13;
at mid-Columbia dams and apparently during spring through winter at lower Columbia dams, so its control&#13;
may sometimes occur when few juvenile salmonids are migrating.&#13;
Although bird management at some dams has occurred since at least 1992, it has not yet been&#13;
determined if this control is cost effective (i.e., the costs of bird control are less than the costs of predation).&#13;
Washington Wildlife Services asserts that the cost of bird predation can be estimated by the cost of&#13;
controlling predation. With this circular logic, Wildlife Services could spend a considerable amount of&#13;
taxpayer or electric ratepayer money controlling predators that may be taking an insignificant number of&#13;
viable juvenile salmonids and justify doing so because it has spent so much money. Consequently, it is&#13;
important for there to be realistic evidence for the need or benefits of predator control, so that control is&#13;
cost effective.&#13;
Washington Wildlife Services has not been forthcoming in answering general questions about its&#13;
activities at Columbia Basin dams and asserts that a federal Texas court case precludes disclosure of&#13;
information. However, it seems that Wildlife Services may be using that court case to avoid scrutiny&#13;
because the court ruled that Wildlife Services not provide information that could identify cooperators with&#13;
Wildlife Services, not that it withhold all information about its activities. Further, Wildlife Services appears&#13;
to have violated this court decision by providing other agencies with reports of its predator control activities&#13;
that identifies specific cooperators, so Washington Wildlife Services seems to have selectively chosen when to use the court ruling as an excuse to not give out general information.&#13;
Fish-eating bird control has proceeded very differently in the Columbia Estuary than at Columbia&#13;
Basin dams. In the Estuary, bird predation was quantified in 1997 to establish a need for bird control;&#13;
agency, tribal, and public consultations about a management plan were conducted, management actions&#13;
began to be implemented in 1999, and predation reduction began to be quantified in 2000. At dams,&#13;
Washington Wildlife Services assumed bird predation to be significant, initiated bird management before&#13;
the amount of predation was measured, appears to have done less consultation with the public, other&#13;
agencies, or tribes about its management actions; and assumed that its predator control actions have&#13;
significantly reduced predation.
</summary>
<dc:date>2003-02-01T00:00:00Z</dc:date>
</entry>
<entry>
<title>1884-1923 Oregon coast bird notes in biological survey files</title>
<link href="http://hdl.handle.net/1957/8429" rel="alternate"/>
<author>
<name>Bayer, Range D., 1947-</name>
</author>
<id>http://hdl.handle.net/1957/8429</id>
<updated>2008-08-26T22:36:58Z</updated>
<published>1986-01-01T00:00:00Z</published>
<summary type="text">1884-1923 Oregon coast bird notes in biological survey files
Bayer, Range D., 1947-
The purpose of this work is to make available reports and letters for&#13;
the Oregon Coast that were in the files of the Biological Survey and that&#13;
are now in the files of the Biological Survey's successor, the U.S. Fish and&#13;
Wildlife Service. I have changed outdated bird names to those that are used&#13;
today, so that the reader can more easily understand the reports. But this&#13;
monograph does not analyze these reports or letters; that is left to the&#13;
reader.&#13;
Not all of these reports were done for the Biological Survey. The&#13;
reports in 1884 and 1885 were for the American Ornithologists' Union&#13;
Committee on Bird Migration, reports in 1886-1890 were for the U.S.&#13;
Department of Agriculture (USDA), Division of Entomology, Investigations in&#13;
Economic Ornithology; reports in 1891-1896 were for the USDA, Division&#13;
of Economic Ornithology and Mammalogy or Division of Ornithology and&#13;
Mammalogy; reports in 1897-1905 were for the USDA, Division of Biological&#13;
Survey; and reports in 1906-1923 were for the USDA, Bureau of Biological&#13;
Survey.&#13;
Ira N. Gabrielson and Stanley G. Jewett both worked for the Biological&#13;
Survey and used some of the unpublished information in the Biological Survey&#13;
files in writing their classic 1940 book. They discussed the work of the&#13;
Biological Survey in Oregon on their pages 56-58.&#13;
The observations in the Biological Survey files and those cited by&#13;
Gabrielson and Jewett (1940) are sometimes the only information available&#13;
about birds in some parts of Oregon prior to 1940. Unfortunately, it has&#13;
not been widely known that at least some of the files accumulated by the&#13;
Biological Survey still exist and are on microfilm ("Bird Migration&#13;
Schedules, Reel 17, North Dakota, Oklahoma, Oregon, and Ohio") at the U.S.&#13;
Fish and Wildlife Service's Patuxent Wildlife Research Center Library in&#13;
Laurel, Maryland. Upon request, the Patuxent Library may loan out the&#13;
microfilm reel through Interlibrary Loan to an established library, where&#13;
the reader can then peruse the contents.
</summary>
<dc:date>1986-01-01T00:00:00Z</dc:date>
</entry>
<entry>
<title>Records of bird skins collected along the Oregon coast</title>
<link href="http://hdl.handle.net/1957/8428" rel="alternate"/>
<author>
<name>Bayer, Range D., 1947-</name>
</author>
<id>http://hdl.handle.net/1957/8428</id>
<updated>2008-08-26T22:27:35Z</updated>
<published>1989-01-01T00:00:00Z</published>
<summary type="text">Records of bird skins collected along the Oregon coast
Bayer, Range D., 1947-
In spite of imperfections, this monograph is useful in locating bird &#13;
skins collected along the Oregon Coast that are stored in about 80 museums. &#13;
This monograph lists over 11,000 records of skins for 279 bird species and &#13;
192 records of skeletons for 52 bird species. Each record includes the &#13;
species, subspecies (if given), sex or age class, date of collection, &#13;
location of collection, collector, and museum number. &#13;
Most bird skins were collected in Tillamook County, but most bird &#13;
skeletons were from Lincoln County. 62% of the bird skins were collected in &#13;
the 1930's and 1940's with five collectors accounting for 74% of the skins. &#13;
61% of the bird skeletons were collected in the 1970's and 1980's with the &#13;
top five collectors collecting 65% of the skeletons. &#13;
Each record is indexed by species, subspecies, collection site (i.e., &#13;
county, beached or pelagic specimen, offshore island, lake, and/or shell &#13;
mound), and collector.
</summary>
<dc:date>1989-01-01T00:00:00Z</dc:date>
</entry>
<entry>
<title>Birds of the Coast Range of Lincoln County, Oregon : v.1. Birds of Thornton Creek</title>
<link href="http://hdl.handle.net/1957/8419" rel="alternate"/>
<author>
<name>Faxon, Darrel</name>
</author>
<author>
<name>Bayer, Range D., 1947-</name>
</author>
<id>http://hdl.handle.net/1957/8419</id>
<updated>2010-04-27T14:39:55Z</updated>
<published>1991-01-01T00:00:00Z</published>
<summary type="text">Birds of the Coast Range of Lincoln County, Oregon : v.1. Birds of Thornton Creek
Faxon, Darrel; Bayer, Range D., 1947-
Incidental to his outdoor activities such as farming, fern-picking, and &#13;
horse logging, Darrel Faxon made 17.4 years of detailed observations at &#13;
Thornton Creek during 1973-1990. He determined bird presence, not bird &#13;
abundance, and made about 99,800 records, where a record is one bird species &#13;
found during one day. &#13;
Depending upon the calendar month, Faxon averaged 19-24 observation &#13;
days/month, 13-34 bird species/day, and 34-66 species/month. He noted an &#13;
average of 101 species each year. &#13;
Faxon found 12 species only during casual observations prior to 1973 &#13;
and 179 species in 1973-1990. He detected 47 waterbird species, so most &#13;
birds he noted were terrestrial. 30% of waterbird species and 20% of &#13;
terrestrial species were recorded in only one year, and just 16% of the &#13;
waterbird species were seen in 16-18 years. However, Faxon noted the &#13;
majority (50.4%) of terrestrial species in 16 or more years. &#13;
For each species, daily relative frequencies of occurrence for each &#13;
month and average monthly relative frequencies of occurrence for the &#13;
1973-1981 and 1982-1990 periods are given. Further, arrival and departure &#13;
dates are listed for each species for each year, if appropriate. &#13;
Faxon's records indicate that many migratory terrestrial species are &#13;
often not present in the 10 days following their arrival or prior to their &#13;
departure. Thus, determining arrival or departure dates may be very &#13;
dependent upon daily observation effort. For example, if there are &#13;
inadequate daily observations, then the actual arrival date may be missed, &#13;
and it may be several days or a week before the species may re-appear. This &#13;
inconsistency of presence after their "arrival" results in many species not &#13;
being found on their "average" arrival date. &#13;
Although Faxon did not record a spring migration wave, he usually noted &#13;
a major movement of passerines during August-September. In fall, his &#13;
records also indicate that some raptors appeared to be migrating through. &#13;
In addition to his bird observations, Faxon recorded daily &#13;
precipitation from 1975-1990, and monthly totals are given.
</summary>
<dc:date>1991-01-01T00:00:00Z</dc:date>
</entry>
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