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The Atlas Survey: INTRODUCTION AND METHODS
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- Introduction
- Sponsors and Funding
Administration
Atlas Coordinators
Format of the Species Accounts
- Methods
- Grid and Sampling Design
Adequacy of Coverage
Survey Procedures
Breeding Criteria and Codes
Data Collection
- Field Data Card
- Casual Observation Card
- Verification Report Form
Data processing and Analysis
- Computer Database
- Data Input Routine
- Quality Control Printouts
- Nearest Neighbor Analysis
- Data Conversion
Mapping
Final Quality Control
Safe-Dates
Limitations and Biases
A Blockbusting Postscript
In Memoriam
The goal of a Breeding Bird Atlas (BBA) project is to map the distribution
of each species that breeds (or might breed) in a defined area during
a selected period of time. These data provide a historical baseline
that can be compared with subsequent Atlas projects to detect changes
in the distribution and abundance of birds.
The first Breeding Bird Atlas project was conducted in Great Britain
and Ireland from 1968 to 1971 (Sharrock 1976). It was inspired by the
earlier Atlas of the British Flora (Perring and Walters 1962).
Atlas projects for several European countries soon followed.
In North America, Atlas projects in 36 states and 8 provinces were
planned, underway, or completed by 1990 (Smith 1990).
The idea of a Florida Breeding Bird Atlas project arose from a suggestion
made by Erma J. Fisk in 1981 to the President of the Florida Audubon
Society, Peter Mott, and its Vice President for Ornithology, Dr. Herbert
W. Kale II. In her usual style, Jonnie, as she was known to her friends,
offered to supply the seed money to cover planning costs. Although
she no longer resided in Florida, Jonnie maintained an interest in the
Florida Atlas and continued to provide financial support each year until
her death in January 1990. Thus, it is fitting that this Florida
Breeding Bird Atlas be dedicated to the memory of this nurturing
and dedicated amateur ornithologist.
During the early 1980s, presentations were made to members of various
Audubon Society chapters and the Florida Ornithological Society (FOS)
to raise enthusiasm for an Atlas project in Florida. A search for major
funding also was initiated. In 1983, the Florida Legislature established
the Nongame Wildlife Program of the Florida Game and Fresh Water Fish
Commission [Editor's note: now the Florida Fish and Wildlife
Conservation Commission] (hereafter the Commission). In 1984, funding
for the Nongame Program was provided by the creation of the Florida
Nongame Wildlife Trust Fund. A $4.00 fee was added to the $6.00 first-time
registration of motor vehicles brought into the state by new residents.
With a daily immigration of approximately 900 people into the state,
an annual income of 1.3 - 2 million dollars was projected.
Beginning in 1985, the Commission established a grants and contracts
program to fund non-Commission projects that supported nongame wildlife
management and conservation. A proposal to conduct a Breeding Bird
Atlas project was submitted by the Florida Audubon Society (FAS) and
approved by the Commission.
On 12-13 March 1985, the Commission and FAS sponsored an Atlas planning
conference in Orlando to acquaint Florida birdwatchers with the project
and to select volunteers to serve as regional and county coordinators.
Resource leaders in attendance were Chandler S. Robbins of the U.S.
Fish and Wildlife Service (USFWS), an authority on bird population surveys
and Atlasses; Janet Carroll, state coordinator of the New York BBA,
then in its final year of fieldwork; and Reed Noss of the Florida Natural
Areas Inventory, who had been involved with the Ohio BBA. An Atlas
Advisory Board was appointed and met in April 1985 to select the project's
State Coordinator.
Fieldwork for the Florida Breeding Bird Atlas began 1 January 1986
and ended 31 December 1991. More than 1,880 participants were involved
and more than 136,000 records were compiled. Approximately 200 dedicated
participants helped throughout most of the 6 years of the Atlas survey.
The Florida Breeding Bird Atlas project was sponsored by the FAS and
the FOS. Primary funding came from the Nongame Wildlife Trust Fund,
administered by the Commission. Members of the FOS and FAS chapters
provided the majority of regional and county coordinators and fieldworkers
for the project. Supplemental funding and services also were provided
by the above-mentioned organizations and by private corporations, foundations,
garden clubs, and individuals.
In 1986, the FAS sent a fundraising appeal, specifically for the Atlas
project, to each of its members. Many of those who responded were contacted
for additional support in 1988, 1990, and 1991. All contributors are
listed in the acknowledgments.
The FAS's Vice President for Ornithology and part-time Project Director,
Dr. Herbert W. Kale II, was responsible for the overall direction of
the project and supplemental fund-raising. He served in this capacity
until his death in August 1995. A fulltime State Coordinator, C. Wesley
Biggs, was hired to coordinate fieldwork and data collection and review.
He served from late 1985 to May 1991, when he became incapacitated.
Biggs was replaced by Bill Pranty, who served as the State Coordinator
until the contract terminated in February 1992. A part-time secretary
completed the paid staff at FAS.
The computer database for the project was subcontracted to Dr. Stephen
R. Humphrey of the Florida Museum of Natural History at the University
of Florida. Dr. Humphrey hired Bradley M. Stith, a graduate student
and computer programmer to develop programs and procedures for a personal
computer database.
To coordinate the Atlas fieldwork, data collection, and
review, Florida was divided into 9 regions (see Figure
1.1). Nine regional coordinators were appointed and most counties
appointed a county coordinator. Regional coordinators were responsible
for maintaining contact with county coordinators and ensuring that fieldwork
proceeded. County coordinators also assisted with recruiting and training
cooperators. For those counties without a county coordinator, the regional
coordinator assumed responsibility. We are grateful for the work and
efforts of all of our coordinators, who were the heart of the Florida
Atlas project.
Figure 1.1
Click for larger Image
The experience of other Atlas projects alerted us to the need to hire
field personnel to survey Atlas blocks in remote or inaccessible parts
of the state where few birdwatchers lived. Provisions for "blockbusting"
teams in years 4 and 5 were included in the original application for
funding but were not granted by the Commission. A grant from the Frank
Stanley Beveridge Foundation provided funds to support 4 field-workers
for several weeks in the summer of 1988. Other funds enabled the Atlas
project to support 1 person for several weeks in 1989.
In early 1990, faced with the likelihood that the project would not
be completed without supplemental atlassing, the Commission agreed to
provide funding for a sixth year of fieldwork. Additional funds provided
by the Commission enabled the project to hire 4 fieldworkers in the
spring and summer of 1991 and to put the headquarters' staff in the
field fulltime during the 1990 and 1991 breeding seasons.
In addition, many of our regional and county coordinators and atlasers,
aware of our funding difficulties, put forth extraordinary efforts during
the 2 final years of the project to reach as many incompletely surveyed
blocks and quadrangles as possible, either alone or with the help of
cooperators.
Each year during the Atlas project, the FOS sponsored a blockbusting
event during the Memorial Day weekend at a location in north Florida.
Concentrated survey efforts by expert Atlasers in 1 or 2 counties over
a 3-day period enabled a considerable amount of work to be accomplished.
There is currently a wealth of publications dealing with Florida's
avifauna. In 1992, the FOS published its sixth special publication,
Florida Bird Species: An Annotated List, by William B. Robertson,
Jr., and Glen E. Woolfenden. This book summarizes the ornithological
record of every species found in the Florida from the state's discovery
by Europeans through 1991.
The Birdlife of Florida, by Henry M. Stevenson and Bruce H.
Anderson, was published in 1994 by the University Press of Florida.
It is the long-awaited replacement for Arthur Howell's 1932 classic,
Florida Bird Life, revised by Alexander Sprunt II in 1954. The
Birdlife of Florida is the culmination of more than 20 years of
work by the late Henry Stevenson and also was funded by the Commission.
It presents a detailed account of the taxonomy, history, distribution,
and biology of every bird species reported in the state through 1993.
The Endangered Biota of Florida series published by the Florida
Committee on Rare and Endangered Plants and Animals (FCREPA) was recently
revised. The bird volume, edited by Rodgers et al., a revision of Kale
(1978), was published in 1996.
Existence of these published references eliminates the need to be repetitive,
hence, the species accounts in this Atlas are intentionally brief.
Each account includes an introduction and paragraphs dealing with breeding
occurrence and distribution in reference to the accompanying map, as
well as brief discussion of habitat, diet, and nesting biology.
Concurrent with the Atlas project, a systematic statewide inventory
of breeding bird colonies was conducted in 1987-1989 by the Nongame
Wildlife Section staff (Runde et al. 1991; Runde 1991). The goal of
that project was to revisit colony sites surveyed in 1976-1978 (Nesbitt
et al. 1982) and to resurvey the entire state to locate all extant colonies.
Originally, we planned to add those data into the Atlas database. However,
most of the colony data was obtained by aerial surveys, which estimated
numbers of adults but did not specify whether the adults were on a nest
or attending young, the criteria necessary to confirm breeding in the
Florida BBA. Undoubtedly, in most cases it is valid to presume that
a species is breeding in a colony containing numerous individuals of
that species, but because we could not verify these criteria for all
of the surveyed colonies they were not included in the Atlas database.
It is interesting that the Atlas database includes colonies not recorded
by the Commission survey; some of these may represent colonies found
outside the Commission's survey period.
Methods
U.S. Geological Survey topographic maps, which are mapped
in minutes of latitude and longitude, provided the basic grid for the
Florida BBA. Each quadrangle map is 7.5 min (equal to 1/8 of 1 degree).
Florida is covered by approximately 1,037 quadrangles, several of which
overlap into Alabama and Georgia and contain so little area in Florida
that they were excluded from the project, as were 3 quadrangles in Florida
Bay that contain no land forms. Hence, the actual number of quadrangles
surveyed was 1,028.
Each quadrangle was divided into 6 numbered blocks (see Figure
1.2). Initially, our goal was to survey every block in a quadrangle,
and in some parts of the state this was accomplished. Aware of the
enormity of such an endeavor in a large state with remote areas and
a limited number of qualified workers, we established a minimum goal
of 2 priority blocks per quadrangle. These blocks represent a combination
of stratified-random and nonrandom sampling. One priority block was
the southeastern corner block (Block 6). In those cases where Block
6 was inaccessible or contained more than 50% open water, the next lower
numbered block that qualified became the priority block. The second
priority block in each quadrangle was selected by the cooperator in
consultation with the county or regional coordinator.
Figure
1.2.
The Florida BBA grid system: the quadrangle and its 6 numbered blocks.
Atlas work in other states had shown that 75% or more of the breeding
species present in a block could be found in 16 to 20 field hours by
checking all the major habitat types present. Additional time might
have raised the percentage, but in cases where many blocks needed to
be surveyed and workers were scarce, atlasers moved to another block
when they reached or approached 16 to 20 field hours.
In Florida, with its extended breeding season and few experienced Atlasers,
we suggested that a minimum of 25 hours be spent in a block before moving
to another block. This 25-hour rule of thumb is insufficient if the
cooperator is inexperienced or if access to the block is restricted.
Conversely, in areas of habitat homogeneity (i.e., the vast marshes
of the Everglades), fewer than 25 hours were needed to finish a block.
A second guideline, and probably the one most used in Florida by experienced
Atlasers, was to list all the species likely to be nesting in the block
and then work the block until 75% or more of the species were recorded
and, secondarily, at least 50% confirmed. This secondary goal was not
pursued when blockbusting an area.
Fieldwork was conducted from 1986 through 1991, a scheduled 5-year
effort, followed by a 1-year cleanup. During the fall of 1985, training
workshops were held in each region to familiarize coordinators and cooperators
with materials and techniques. Twelve issues of the Florida Breeding
Bird Atlas Newsletter were sent to nearly 1,500 participants and
interested parties.
In addition, contact was maintained with coordinators through letters,
phone calls, and personal visits, and in January or February during
1987-1990, 2 coordinator conferences --- 1 in Tallahassee for north
Florida and 1 in Lake Placid for south Florida --- were held to discuss
progress, procedures, and problems and to exchange ideas and information.
During the first several years, many coordinators conducted workshops
with their cooperators, and some of them produced their own area newsletters.
Each cooperator received a packet containing a Handbook for Cooperators,
A Guide to Breeding Ranges, Seasons, and Habitats, Field Data Cards
(Figure 1.3 and Figure
1.4 ), Casual Observation Cards (Figure 1.5),
and Verification Report Forms.
Figure 1.5
Casual Observation Card
The Florida BBA project borrowed freely from other Atlas projects,
and the 20 breeding criteria codes selected represent what we considered
to be those most appropriate for use in Florida. These are listed below.
Except for the multiple male codes (discussed below), our codes and
criteria follow the standardized behavior code system recommended for
North America (Laughlin et al. 1982a). Categories are arranged in a
hierarchical order from least certain (Observed) to most certain (Confirmed).
| Observed |
| O |
Species observed in its breeding season but
outside of nesting habitat, and with no evidence of breeding.
Possible Breeding
|
| SH |
Species (male or female) observed in its breeding season in suitable
nesting habitat. |
| SM |
Singing males present or breeding calls (or
drumming by woodpeckers) heard, in suitable nesting habitat in breeding
season. |
|
Probable Breeding
|
| S |
Seven or more singing territorial males observed only once in
the breeding season. (Note: This code was downgraded to the possible
category when the Atlas maps were produced.) |
| P |
Pair (male and female) observed in suitable nesting habitat in
breeding season. |
| T |
Bird (or pair) apparently holding territory (e.g., a singing
male present on at least 2 days, a week or more apart, at the same
place) or territorial behavior observed (e.g., chasing conspecifics
or responding to tape playbacks). |
| C |
Courtship behavior or copulation. |
| V |
Visiting probable nest site by any species, or nest building
by woodpeckers and wrens. |
| A |
Agitated behavior or anxiety calls from adults, suggesting probable
presence of nearby nest or young. |
| B |
Brood patch on adult female (or male when applicable) or cloacal
protuberance on adult male. |
| N |
Nest building or excavation of a nest cavity (except by woodpeckers
or wrens). A bird carrying nesting material, excluding far-ranging
species. (Note: This code was upgraded to the confirmed category
when the Atlas maps were produced.) |
|
Confirmed Breeding
|
| SE |
Seven or more singing territorial males observed singing on at
least 2 days, a week or more apart, in a block. This code is limited
to territorial males only and is to be used rarely. (Note: This
code was downgraded to the probable category when the Atlas maps
were produced.) |
| DD |
Distraction display or injury-feigning, or attacking humans or
other predators. |
| NU |
Used nest or egg shells, correctly identified. |
| FE |
Female with egg in oviduct (for banders). |
| FY |
Recently fledged young or downy young (i.e., young incapable of
sustained flight). |
| ON |
Adults entering or leaving a nest site in circumstances indicating
an occupied nest. High nests, nest holes, or nest boxes, the contents
of which cannot be seen, or an adult sitting on a nest, contents
of which are unknown. |
| FS |
Adults carrying fecal sac or food for young. Could not be used
with raptors, gulls, terns, or crows. |
| NE |
Nest with eggs. If the nest also contains a cowbird egg, record
NE for both host and cowbird species. |
| NY |
Nest with young seen or heard, or identifiable dead nestlings.
If the nest contains a young cowbird, record NY for both host and
cowbird species. |
Initially, we included a multiple male code (S) for 7 or more singing
territorial males present in suitable nesting habitat during the breeding
season. This was the lowest code in the probable category, and, if
it was repeated in the same area a week or more later, we allowed this
to be upgraded to SE, the lowest code in the confirmed category. After
the first year of fieldwork, the North American Ornithological Atlas
Committee voted to not recommend use of these codes (Smith 1990). Our
decision was to continue to accept them but to discourage their use
as much as possible. Upon termination of fieldwork we decided to downgrade
these codes, assigning "S" to the highest code in the possible
category and "SE" as the highest code in the probable category
and restricting its use to only those species with relatively small
territories.
Field Data Card.
Cooperators surveying a block recorded observations on
a field data card (Figure 1.3, Figure
1.4) that listed virtually all the species known to breed in
Florida. Appropriate breeding criteria codes, quadrangle name, block
number, county, year, recorder's name, address, phone number, and date
and hours of each visit to the block were recorded. Because quadrangle
boundaries sometimes overlap county lines, we recorded the name of the
county to which the quadrangle was assigned, which was not necessarily
the county in which the observer was recording data. Space was provided
on the cover page to record up to 12 visits, showing day, month, hours,
number of observers, and number of new species. During the first year
many observers did not record their hours. In some instances it was
difficult to calculate hours spent atlassing when one lived in the atlas
block and recorded species while traveling between home and work, for
example. In such cases we asked atlasers to estimate.
The Species Observed column (O) was originally designed for 2 reasons:
1) to make a record of a species seen in a block, even though no habitat
or evidence of breeding existed; and 2) to serve as a reminder to the
atlaser to search for that species in appropriate habitat somewhere
in the block or quadrangle. Unfortunately, this category created more
confusion than clarity, especially on the first edition of the field
card where it was listed under the Breeding Evidence heading. Cooperators
often used it as a catchall, even listing common breeding species that
should have been placed under the possible category as a species in
suitable habitat (SH). During final data review, many O codes that
were misused were upgraded to SH.
Because we realized the value of obtaining quantitative data on bird
populations, we included an abundance column (A) and established codes
for estimated numbers of pairs in a block. It quickly became apparent
that we were asking too much of our volunteers to survey as many blocks
as possible and, at the same time, to count or estimate the total number
of individuals in the block. Few cooperators recorded abundance data;
of those who did, some listed actual numbers, some used the codes, and
in some cases we could not determine what the numbers represented.
This Atlas omits all references to estimated abundances.
In 1987, we revised the field data card to add, in phylogenetic order,
several new species that had appeared the first year. Subsequently,
this caused difficulty in data checking and verification because the
order birds were listed differed among cards.
In hindsight, a major shortcoming of the field data card was the lack
of a column in which the recorder could list the date of an observation.
This would have saved us considerable time and effort spent in contacting
atlasers to verify the presence of a species within its safe-dates,
especially 3 or 4 years after the data were collected.
Casual Observation Card.
The idea for the Casual Observation card (Figure
1.5) came to us from the Ontario Atlas project. It was designed
to encourage reporting of breeding evidence for 10 or fewer species
in a block that the observer was "casually" visiting or passing
through. Ironically, Ontario curtailed its use for technical reasons,
but we found it a convenient and helpful tool in Florida. An improvement
for a future Florida BBA would be to design the identification heading
to conform to that on the field data card.
Verification Report Form.
Cooperators were requested to submit Verification Report
Forms (VRF) for any species considered to be of restricted occurrence
as breeding birds or otherwise of uncertain or unclear status in Florida.
These species were asterisked on the field data card. Also, any species
found breeding outside of its known breeding range required a VRF.
Computer Database.
Breeding Bird Atlases provide a natural application for a
computer database system. Older atlases were done by hand or on mainframe
computers. At the beginning of the Florida Atlas project, we used an
IBM PCAT microcomputer with Dbase III+ software. This system had to be
upgraded as the project progressed, but advances in computer technology
were so rapid that near the end of the Atlas project, a relatively inexpensive
home personal computer could handle the entire database system. The final
corrections, printouts, and original maps all were made on an Intelbased
486/33C Gateway computer with a Hewlett-Packard LaserJet IIIp printer.
Data Input Routine.
Considerable programming effort was directed at developing the data entry
software. The primary goal was to reduce data entry errors while permitting
rapid touch-typing. Display screens were designed to mimic the field
card in appearance to provide intuitive data entry. Extensive error checking
was built into the software. Spellings of quadrangle names, bird codes,
breeding evidence, and years were checked against data dictionaries while
the typist was entering the data. We found it necessary to switch from
Dbase to Foxbase software to handle a typing speed of 80 words-per-minute.
Certain data, such as the region and county, did not have to be entered
since the data dictionary for the quadrangles contained this information.
Whenever a typing error was detected, the software would produce an audible
alarm and an error message, and the user could browse the data dictionaries
to find the misspelled entry.
To reduce the size of the final database, only a single observation code
was allowed for each bird species in each block. Upgrading breeding evidence
for a species in a given block simply required typing in the new breeding
code. We put rules in place to prevent accidentally downgrading the breeding
code for a species already in the database.
Quality Control Printouts.
As part of the data checking procedure, a program was written that
produced a legal-sized page printout of the data that exactly overlaid
the original field cards. Errors of omission and commission were detected
by placing the printout on top of the card on a light table. Unfortunately,
this procedure was only effective if all of the data for each block
were on a single field card. After the third year it became evident
that this requirement could not be met because it created a lot of extra
work for volunteers and staff, introduced another source of transcription
errors, and because data were arriving from other sources, such as casual
observation cards. The overlay printout was abandoned in favor of a
more condensed version that fit all of the data for the entire quadrangle
on a letter-sized page. This reduced the number of printouts from several
thousand pages to a more manageable 1,028 pages. These printouts also
provided a column showing the highest breeding code for each species
for the entire quadrangle and summarized the total number of confirmed,
probable, and possible breeders in each analysis.
Nearest Neighbor Analysis.
To facilitate the planning of blockbusting and to help identify species
that were likely to breed in each block, the quality control printouts
made after the third year included information about the species found
in the 4 neighboring quadrangles (some quadrangles had fewer than 4
neighbors). This summary quickly identified quadrangles with weak coverage
compared to their neighbors. The final printout retained a summary
table for the surrounding quadrangles. Also, a "7th block"
was included on the final printout to include species recorded in the
quadrangle by AtlaserAtlasers who did not record block numbers. This
situation arose during the last year of the Atlas project, when some
Atlasers went out "quadrangle busting" for missing species,
and, contrary to instructions, did not record block numbers.
Data Conversion.
Software was written to incorporate data from outside sources into
the database. Mickey Wheeler, the coordinator for Region 9, devised
her own database system, and a conversion program was written to handle
her data. Aerial survey data from state and federal agencies for wading
birds, Snail Kites, and Bald Eagles had to be converted from latitude
and longitude coordinates, obtained from LoranC, to block locations
within quadrangles. Conversion to a block location was fairly simple
because the quadrangle dictionary contained the latitude/longitude centroids
for each quadrangle. Software was written to read in an ASCII file
or to accept keyboard entry of latitude/longitude coordinates.
Throughout the project, the central office where data were received
and corrected and the computer facilities where data were entered were
in different locations. This contractual arrangement sometimes created
delays but generally worked satisfactorily. Copies of the database,
stored electronically and on paper, have been deposited at the Commission
headquarters in Tallahassee, the Florida Museum of Natural History in
Gainesville, and the FAS headquarters in Florida.
Maps form the heart of the Breeding Bird Atlas, and various mapping
options were explored. An inexpensive mapping program called AtlasGraphics
was used initially to produce work maps. The mainframe version of Sasgraph
was evaluated for producing final maps but proved to be too expensive
and inflexible. Toward the end of the project Arc/Info, a well-known
geographic information system (GIS), was acquired to produce work and
final maps. Programs were written to generate sets of maps with Arc/Info
on a laserjet printer. This worked satisfactorily, except that several
days of continuous processing were required to produce a set of maps
for all species. In the end, a program was written in Dbase to produce
the final maps. This program generates HPGL/2 standard plotter commands,
which are available in many plotters and in the Hewlett Packard LaserJet
III family of printers. By working directly with the database and the
printer, this program provided maximum control over map corrections
and was much faster than the other alternatives that were evaluated.
Although all data were recorded and computerized at the block level,
species maps in this Atlas show distribution by quadrangles.
A Breeding Bird Atlas project reliant upon hundreds of volunteers,
including backyard birdwatchers and beginning birders, must maintain
strict (even ruthless) control over the submitted data. Otherwise,
the value of the database will be compromised by inaccurate data. Insomuch
as the database is the sole source of new information published in this
Atlas, tainted data could destroy the project's basic premise, which
is to accurately map the breeding distributions of every species of
bird that breeds or might breed within Florida.
A defense against the submission of bad data would be to limit the
project only to birders with proven identification skills. However,
this is not feasible in a state as large as Florida, and for a project
that relies almost entirely on volunteers. There are simply an insufficient
number of experienced birders to thoroughly survey the state in only
5 or 6 field seasons. Therefore, we accepted all the help that was
offered.
The 5 main types of errors committed by Atlas observers were: simple
transcription errors resulting from a "slip of the pen," errors
in identification, incorrect usage of BBA codes (e.g., nest-building
for Common Nighthawk [N] or singing male [SM] for Red-shouldered Hawk),
problems associated with the safe-dates policy, and undocumented extralimital
records.
Transcription errors were commonly committed by anyone who filled out
an Atlas data card. Misidentification was largely restricted to less-experienced
observers. When BBA codes were incorrectly used, records were changed
to the most reasonable code. Within the safe-dates policy, editing
to comply with safe-dates periods for species was unambiguous. The
more challenging task was handling the "safe" records that
probably referred to late spring or early fall migrants rather than
locally breeding birds. Finally, dozens of out-of-range breeding reports
(sometimes the result of misidentification) were not accompanied by
VRFs or other written documentation.
It is difficult to safeguard against transcription errors, and many
were committed. Some transcription errors were easy to spot because
they showed up on the preliminary maps as species far out of their known
breeding range and/or species not in suitable breeding habitat. For
example, in one instance a Mangrove Cuckoo was reported from an inland
county. In another, a Spot-breasted Oriole was recorded in a Panhandle
county. In reality, these were a mistranscribed Yellow-billed Cuckoo
and an Orchard Oriole, respectively. However, not all transcription
errors involve extralimital records. A Red-bellied Woodpecker sighting,
for example, might be mistranscribed as a Downy Woodpecker. This type
of transcription error would not be noticed because both species share
the same distribution in the state. Undoubtedly, minor transcription
errors of common species appear on the maps in this Atlas.
The only transcription errors to be avoided are the ones that would
extend a species' breeding range into an area where it does not breed.
We are confident no such transcription errors remain in this Atlas.
Another type of error committed was misidentification of a bird, sometimes
resulting in an extralimital breeding report. For example, a Pine Warbler
might be misidentified as a Yellow-throated Vireo. Because the Yellow-throated
Vireo is not proven to breed south of central Florida (although its
range is increasing southward) and Pine Warblers breed throughout most
of the state, a misidentified Pine Warbler carrying food in south Florida
would extend the vireo's "confirmed" breeding range. This
one misidentification would alter the Yellow-throated Vireo's range
map. Because this Atlas will be referenced (and quoted) and because
many users of the book may use the maps exclusively rather than in conjunction
with the text, such errors could decrease its value.
A multifaceted system was created to protect the Atlas database from
erroneous identifications and extralimital records. The first safeguard
was the VRF. This form was required for a species that was observed
out of its known breeding range. If the observer failed to submit a
VRF, the appropriate county and/or regional coordinator was expected
to contact the observer, and request that a form be submitted. If this
was not done, the state coordinator needed to contact the observer.
For whatever reason, a VRF was not supplied for many of the sightings
that required verification. Because it was not feasible to ask for
details of a sighting that occurred up to 6 years ago, in late 1991,
Pranty and Kale reluctantly chose to delete all records reported by
observers with unknown field skills. For rarities reported by knowledgeable
observers, we contacted as many of the observers as possible to rule
out the possibility of transcription errors. When an observer could
not be contacted, we deleted the report. This conservative approach,
a standard practice (see guidelines by the FOS Records Committee), was
truly our only alternative.
We added some breeding records that were not (but should have been)
documented by atlasers; in these cases, the species accounts indicate
these records were not verified. "Confirmed" breeding records were
edited the most severely, as only this code implies positive breeding
in a quadrangle. For the most part, "possible" and "probable" codes
of species not too far out of their normal breeding range have been
retained on the maps. We deleted a number of other records from the
Atlas database because there was insufficient time to verify them.
Some of these may indeed be accurate and documentable by the observer,
and should be published. The Florida Field Naturalist, the official
journal of the FOS, is the obvious outlet for publishing these reports.
Even though each year's data were computerized within months of being
received, maps for every species were not produced until the end of
the sixth field season. We wholeheartedly recommend that future Atlas
projects generate maps for all species yearly in order to facilitate
quality control.
In the absence of species maps, printouts of the data were generated
by block (1986 and 1987) and by block and quadrangle (1990 and 1991).
Due to problems with the data-entry program and quality-control methods,
printouts were not produced for the years 1988 and 1989, except for
one county in the state (Pasco), which was the "guinea pig"
for the quality-control procedures being enacted.
Although full sets of maps were not printed until August 1991, sample
maps were produced in earlier years. Inspection of these made it obvious
that many migrants and winter residents were being listed as potential
breeding birds. Atlasers were starting too early in the spring and
perhaps continuing fieldwork into the fall. This was most evident for
species with large numbers of migrants or winter residents but few breeding
birds (e.g., Gray Catbird), for species with lengthy migratory periods
(e.g., Barn Swallow), and other birds that begin fall migration as early
as late June or early July (e.g., Louisiana Waterthrush).
A data Quality Control Committee (QCC) was established to assist in
cleaning up the database. The QCC was staffed by several of the most
active coordinators. Their primary task was to determine ways to purge
the database of records that did not refer to breeding birds, and to
prevent such records from being submitted by atlasers during the remaining
years of the project. The most significant policy enacted was the creation
of "safe-dates" described below.
In June 1988, the "Guidelines for Safe-dates" (pdf) was published
in the BBA Newsletter Number 6. These dates were established for most
of Florida's breeding species to delineate when lower BBA codes (i.e.,
those that did not indicate strong evidence of local breeding) could
be used safely (i.e., after most spring migrants have departed but before
most fall migrants have arrived). Simply, each species that bred in
the state was given a pair of dates that restricted its inclusion in
the Atlas database. If the species was seen outside this period, it
was not considered to be a breeding bird unless specific breeding behaviors
were observed. The codes restricted by safe-dates were: SH (suitable
habitat), SM (singing male), S (7 or more singing males), P (pair),
T (territorial behavior), and SE (7 or more males singing on at least
2 dates, at least 1 week apart). The basic concept of safe-dates was
straightforward, but implementing it turned out to be a tremendous undertaking.
The following procedure was required to clean up the database for safe-dates.
Each Field Data Card or Casual Observation Card was reviewed to determine
if any of the records were outside the species' safe-dates period.
If all the atlassing dates on the card were within a species' safe-dates
period, the record was retained. If all the atlassing dates on the
card were outside a species' safe-dates period, the record was deleted.
If the atlassing dates overlapped these periods, the county or regional
coordinator was notified and asked to contact the observer. If the
observer knew the record was outside the safe-dates, the record was
deleted. If the observer could remember no details of the sighting,
it was our plan to delete it. However, this proposal caused a major
uproar among various coordinators. They argued, for example, that a
Northern Cardinal listed as T should not be deleted, even if some atlassing
was conducted in April (outside the bird's safe-dates period of 1 May
to 1 August).
To solve this problem, the QCC allowed atlasers to retain these questionable
codes using 1 of 2 methods. The first method involved the atlaser locating
a specific date for an observation from a journal, calendar, or other
means. The second method created a "memory code." This code
was to be used solely for species that the atlaser remembered seeing
or hearing repeatedly throughout the breeding season. Insomuch as this
denotes territoriality, the memory code was to be used only for the
T or SE codes. It could not be used for SH, SM, or P codes, because
these codes implied a single observation (i.e., if the bird or pair
was observed more than once, it would have been upgraded by the atlaser
to T or SE). Unfortunately, the revised guidelines sent to QCC members
and county and regional coordinators failed to make this clear. As
a result, the memory code was misused, and hundreds of SH, SM, S, and
P records that should have been deleted were instead retained. This
became apparent in August 1991 when a complete set of maps and printouts
was produced, and it was obvious that many errors still existed in the
database. The formidable task of reviewing each of the 136,000 codes
in the database was undertaken by Pranty and required 300 hours between
August 1991 and January 1992. First, all 15,000+ Atlas data cards were
inspected to ensure that all the safe-date sensitive codes contained
on the cards were within the species' safe-dates. If they were not,
and could not be rescued via the memory code, they were deleted. More
than 8,000 changes were made, representing almost 6% of the codes in
the database.
When new printouts were generated in late January 1992, the data from
27 (of a total of 1028) randomly selected quadrangles (3 from each region)
were reviewed again, comparing the data present on the cards with the
revised database in the computer. The remaining error rate was found
to be 1.7%. This error rate, representing about 2,000 potential errors
out of a database of 136,000 records, was considered unacceptable.
In April 1994, Pranty was contracted by the Commission to conduct a
second review of the BBA database and, assisted by Stith, to produce
new, color quadrangle maps and new, black-and-white block maps. This
second review, completed in October 1994, required 4,000 additional
corrections to the database. Of the 10,344 quadrangle-based codes (in
a sample of 162 quadrangles) rechecked, 9 errors remained. If the 162
quadrangles are representative of the entire database, the database
should be about 99.91% error-free.
Several factors influence the results of any BBA project,
including varying degrees of ability and experience and the distribution
of volunteer participants. Problems with access to property and habitats
played a major role in achieving complete coverage in the Florida BBA.
Sometimes owners or managers of land denied access to atlasers, fearing
litigation in the event of accident or injury. One owner of several
large ranches in central Florida, who frequently welcomes Audubon groups
to visit and birdwatch, denied access because the project was associated
with the Commission. Two of the largest private landowners in the state,
Lykes Brothers, with huge holdings in Glades County, and the Mormon
Church, owner of Deseret Farms in Orange and Osceola County, would not
allow access because they feared the project might find endangered or
threatened species.
Often, we were able to obtain some breeding information by interviewing
managers or field-workers knowledgeable about the local avifauna, by
driving public roads bordering the lands, or by surveying waterways
penetrating the lands. Some areas that were legally accessible required
the use of 4-wheel drive vehicles, which were not available to most
atlasers.
Florida has an abundance of professional biologists and ornithologists,
but it was greatly disappointing that so few of them were active participants
in the Atlas project. Many state and federal biologists freely shared
information when interviewed but rarely volunteered it. Surprisingly,
a number of Florida's "high-intensity" birders showed a lack
of interest in the Atlas. These resources could have made a major contribution
to the Atlas. We urged county coordinators to visit parks and fire
towers and other similar facilities to personally contact people who
spend considerable time in the outdoors.
Most Atlasers conducted their work during the peak of breeding, April-June,
and during daylight hours, hence early breeders and nocturnal species
were probably missed in some blocks. Unless coordinators made special
efforts to survey these species, blank spots on data cards and maps
could mean lack of coverage, species absence, or both.
One limitation of the Florida BBA needs to be mentioned here. Because
the database contains only the highest code per species per block, it
is not possible to search the database in order to retrieve every record.
To do this one must search all the original data cards.
Every Atlas project has its share of anecdotes --- humorous, dramatic,
even hair-raising --- long to be remembered and recounted at gatherings
of Atlasers. We hope that none is as frightening or tragic as the experience
of Florida's State Coordinator, Wes Biggs, as he was blockbusting for
nocturnal species on the night of 30-31 May 1991. At about 12:30 A.M.,
Wes pulled over to the side of U.S. Highway 90, about 5 miles east of
Lake City in Columbia County. He parked in the well-lighted parking
lot of a tavern to record an Eastern Screech-Owl and Chuck-will's-widow
he had just found in that quadrangle.
A car pulled up alongside and Wes looked up as an AK-47 assault rifle
was fired through the window. The bullet tore into Wes' left forearm,
which had been resting on the steering wheel, destroying muscle, nerves,
and arteries. His assailants (someone in the tavern looked out and saw
2 men) sped off to the east. Realizing that he was bleeding to death,
Wes, a former Marine Corps medic, stopped to remove his belt and use
it as a tourniquet. He then drove on to Lake City, where he was flown
to Jacksonville for emergency surgery. He has recovered partial use
of his left arm, but will bear the handicap for the rest of his life.
Police speculate that his assailants were the same 2 men
who had shot up a house in Lake City with an AK-47 earlier that evening
and then fled town. Upon seeing Wes with his inside light on and the
car engine running, they may have thought he was a police officer waiting
for them.
During the course of a multiyear project involving more
than 1,700 individuals, it was perhaps inevitable that we should lose
some of our active participants through death. We remember them here
to commemorate their contributions to the Atlas project and to ornithology
in Florida.
Lawrence Alexander, Franklin County Cooperator
Ray Gilbert, Hillsborough County Coordinator
Erma J. Fisk, Benefactor
Herbert W. Kale II, Project Director
Margaret Lynch, Citrus County Coordinator
Virge Markgraf, Duval County Altasser
Perry W. Oldenburg, Region 3 Atlaser
John Sauer, Putnam County Atlaser
Henry M. Stevenson, Atlas Advisory Board Member
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