LAND
BIRD
GRAND
THE
COMMUNITIES
BAHAMA
STRUCTURE
OF
AN
OF
ISLAND:
AND
DYNAMICS
AVIFAUNA
BY
JOHN
T.
EMLEN
Department of Zoology
University of Wisconsin
ORNITHOLOGICAL
MONOGRAPHS
PUBLISHED
THE
AMERICAN
BY
ORNITHOLOGISTS'
1977
NO.
UNION
24
LAND
BIRD
GRAND
THE
COMMUNITIES
BAHAMA
STRUCTURE
OF
AN
OF
ISLAND:
AND
AVIFAUNA
DYNAMICS
ORNITHOLOGICAL
MONOGRAPHS
This series,publishedby the AmericanOrnithologists'
Union, hasbeenestablished
for major paperstoo long for inclusionin the Union'sjournal, The Auk. Publicationhasbeenmadepossiblethroughthe generosityof Mrs. Cafil Tucker and the
Marcia Brady Tucker Foundation, Inc.
Correspondence
concerning
manuscripts
for publicationin the seriesshouldbe
addressedto the Editor-elect,Dr. MercedesS. Foster, Department of Biology,
Universityof SouthFlorida, Tampa, Florida 33620.
Copiesof OrnithologicalMonographsmay be orderedfrom the Assistantto the
Treasurerof the AOU, Glen E. Woolfenden,Departmentof Biology,Universityof
SouthFlorida, Tampa, Florida 33620. (See price list on back and inside back
cover.)
OrnithologicalMonographsNo. 25, xi + 129 pp.
Editor of A.O.U. Monographs,John William Hardy
SpecialAssociateEditorsof this issue,FrancesC. James,Department
of Biology, Florida State University, Tallahassee,and Ned K.
Johnson,Museumof VertebrateZoology,Universityof California,
Berkeley
Assistant Editor, June B. Gabaldon
Author, John T. Emlen, Departmentof Zoology,Universityof Wisconsin, Madison, 53706
First receivedDecember 1975; accepted,October 1976; final revision,
December
1976
Issued November 22, 1977
Price $9.00 prepaid ($8.00 to AOU Members)
Library of CongressCatalogueCard Number 77-90792
Printedby the Allen Press,Inc., Lawrence,Kansas66044
Copyright ¸
American Ornithologists' Union, 1977
ii
LAND
BIRD
GRAND
THE
COMMUNITIES
BAHAMA
STRUCTURE
OF
AN
OF
ISLAND:
AND
DYNAMICS
AVIFAUNA
BY
JOHN
T.
EMLEN
Department of Zoology
University of Wisconsin
ORNITHOLOGICAL
MONOGRAPHS
PUBLISHED
THE
AMERICAN
BY
ORNITHOLOGISTS'
1977
NO.
UNION
24
iv
TABLE
PREFACE
OF
CONTENTS
........................................................................................................
1--INTRODUCTION
2--METHODS
......................................................................................
...............................................................................................
xi
1
2
HABITAT MEASUREMENTS ..........................................................................
2
ANALYSIS OF HABITAT DISTRIBUTION .........................................................
3
BIRD POPULATION MEASUREMENTS ...........................................................
4
WITHIN-HABITAT
4
3--GRAND
DISTRIBUTION AND ACTIVITY MEASUREMENTS ..............
BAHAMA
ISLAND
THE ENVIRONMENT
..................................................................
...................................................................................
Geology ...............................................................................................
5
5
5
Physiographic
history............................................................................ 5
Climate ................................................................................................
6
Recent history ......................................................................................
6
THE BIRDS ................................................................................................
7
Geographicdistributionof the breedingspecies.................................
7
Originsand routesof invasion..............................................................
8
Colonizationpatterns............................................................................ 10
Turnover
4
rates ......................................................................................
THE HABITATS
AND
THEIR
BIRD
COMMUNITIES
........................
VEGETATION PATTERNS ..............................................................................
11
12
12
Generaldescription
................................................................................ 12
The structure of Grand Bahama habitats ............................................
13
Groupingof standsinto habitattypes.................................................. 15
Alignment of standsalonggradients....................................................
THE BIRD COMMUNITIES
............................................................................
19
21
Communitystructure............................................................................ 21
Bird speciesdiversity............................................................................ 25
Total bird density............................................................................
DISCUSSION-•DIVERSITY
AND DENSITY CORRELATES ................................
V
28
30
5-•BIRD
DISTRIBUTION
THROUGH
THE
HABITATS
..........................
DYNAMICS OF DENSITY DISTRIBUTION ......................................................
Conceptsand models ............................................................................
32
32
32
Habitat distributionpatterns................................................................. 33
HABITAT
SELECTION
.................................................................................
36
Distributionby types............................................................................ 36
Distribution along gradients............................................................... 36
DISPERSION
AMPLITUDES--SPECIALIZATION
............................................
39
Dispersionof speciesthroughthe 25 stands........................................ 39
Dispersionby types .............................................................................. 39
Dispersionalong gradients....................................................................
DENSITY
DISPERSION RELATIONS ...........................................................
OVERLAP AND SIMILARITY
41
48
..........................................................................
51
Measuring overlaps ..............................................................................
51
Overlap and phylogeneticrelationships................................................ 52
Overlap and geographicderivation...................................................... 52
Ecologicalspacing................................................................................
6--THE
PINE
FOREST
COMMUNITY-•SEASONAL
PROCEDURES AND DEFINITIONS
CHANGES
..........
54
55
.................................................................
55
SEASONAL CHANGES ....................................................................................
58
The breedingseasoncommunity.......................................................... 59
The wintering community...................................................................
60
The transientcommunity...................................................................
62
IMPACT
OF THE WINTER
7--SPATIAL
DISTRIBUTION
VERTICAL
MIGRANT
INVASION ........................
WITHIN
DISTRIBUTION-•LAYERS
THE
PINE
FOREST
_...................
63
..................
66
............................................................
67
Vegetativestructureand avian utilizationat five levels...................... 67
Populationstructurein the five layers.................................................
COMPARTMENT
DISTRIBUTION ....................................................................
70
70
Physicalcharacteristics
of the compartments
........................................ 72
Bird speciesdistributionthroughthe compartments............................ 73
Populationstructurein the compartments
............................................ 75
Seasonalchangesin spatialdistribution.............................................
8--GUILD
DISTRIBUTION
WITHIN
CONCEPTS AND DEFINITIONS
THE
PINE
FOREST
........................
......................................................................
76
80
80
PROCEDURES ...............................................................................................
81
THE FORAGING GUILDS OF THE GRAND BAHAMA PINE FOREST ................
83
Ground-gleaning herbivores ................................................................
83
Stemseedpluckers................................................................................
94
Fruit and bud harvesters .....................................................................
94
Nectar sippers......................................................................................
95
Sap and cambium eaters ......................................................................
96
Foliage browsers..................................................................................
96
Ground-gleaningcarnivores..................................................................
96
Ground pouncers.................................................................................
97
Flower probers...................................................................................... 97
Shrubfoliage gleaners.......................................................................... 97
Shrub stem drillers ..............................................................................
98
Pine bark and wood drillers ................................................................
98
Bark gleaners........................................................................................
98
Pine twig gleaners................................................................................
99
Pine coneprobers................................................................................ 100
Pine needle gleaners..............................................................................
101
Air sallyers........................................................................................... 102
Air screeners ...........................................................................................
103
GUILD BIOMASS AND FOOD ABUNDANCE .....................................................
103
GUILD STRUCTURE AND COMMUNITY DYNAMICS .......................................
106
Guild structureand diversity................................................................ 106
Dispersionof speciesthroughthe guilds.............................................. 106
SPECIES OVERLAP AND COMPETITION .......................................................
ACKNOWLEDGMENTS
SUMMARY
................................................................................
.....................................................................................................
vii
109
111
112
CONCLUSIONS
LITERATURE
..............................................................................................
CITED
APPENDIX---SPECIES
115
.................................................................................
115
ACCOUNTS
118
............................................................
ooo
V1H
LIST
Figure
OF
FIGURES
1. Plant types and foliage compartments...............................................................
2. Map of the westernBahama Islands ....................................................
3. Continental and Antillean ranges of the breeding land birds of Grand
Bahama
..................................................................................................
4. Faunal derivation of the breeding land birds of Grand Bahama ..................
4
6
9
10
5. Map of Grand Bahama Island showingextent of forests and location of
survey stands ...............................................................................................
12
6. Cross-island profile showing vegetation zones and positions of survey
stands
7.
8.
9.
10.
...............................................................................................
13
Submaturepine forests on Grand Bahama Island ............................................ 14
Young pine forest types and open stands............................................................ 15
Other Grand Bahama habitat types .................................................................... 16
Distribution of the 25 survey stands on canopy height-canopycover
coordinates
.....................................................................................
17
11. Distribution of the 25 standson habitat gradient diagrams ..................
20
12. Bird speciesdiversity plotted on habitat gradient diagrams ........................... 26
13. Species number and diversity plotted against foliage height diversity at
25 sites .........................................................................................................
27
14. Bird species
numberand diversityplottedagainstvegetationdensity(volume)
at 25 sites ..............................................................................................................
15.
16.
17.
18.
19.
Total bird density plotted on habitat gradient diagrams ...........................
Total bird densityplotted againsttotal vegetationvolume ..................
Hypothetical density distribution through habitats of declining quality .......
Decreasingdensitythrough 10 favored standsfor 34 common species.......
Habitat distribution of Grand Bahama specieswith respect to tree, shrub,
and exposedground cover ..........................
20. Habitat distributionof Grand Bahama specieswith respectto vegetation
height and arboreal foliage volume ....................................................................
28
29
31
33
34
40
42
21. Habitat distribution of Grand Bahama specieswith respect to shrub type
and shrub plus ground cover foliage volume .................................................
22. Permanent resident densitiesplotted on habitat gradient diagrams ................
23. Winter residentdensitiesplotted on habitat gradient diagrams ........................
24. Density in preferred stand plotted against dispersionamplitude ...............
44
46
47
51
25. Ordination of the Grand Bahama bird speciesfor similarity of habitat
selection
.................................................................................................
58
26. Physioguomicstructureand compositionof the submaturepine forests........ 59
27. Temporal limits of the seasonalbird communitiesof Grand Bahama ..........
62
28. Monthly changesin size and composition of the pine forest bird com.......................................................................................................
63
29. Geographic sourcesof the migrant invaders•species .......................................
30. Geographic sourcesof the migrant invaders--numerical representation....
31. Relation of arian insect gleaner biomass to food resource levels in 7
munities
64
65
32.
33.
34.
35.
36.
37.
compartments .....................................................................................
66
Vertical distributionof commonspeciesin the pine forests...................
Speciesdiversityand densityin 5 equal layers of the pine forests.........
Relative abundanceof speciesin the 5 equal layers ..........................
Winter invader and permanentresidentrepresentationin the 5 equal layers ....
Compartmentdistributiondiagramsfor 30 pine forest species ....................
Relativeabundanceof speciesin the 4 major compartments...........................
67
69
71
71
74
75
38. Relative abundanceof speciesin 16 foraging guilds ........................................ 85
ix
TABLES
Table
1. Vegetation measurements in the 25 Grand Bahama habitats ..............................
2. Bird densities at the 25 habitat sites--winter 1969 ..............................................
14
22
3. Relation of dispersiontypesand behaviortypesin Grand Bahama land birds .... 35
4. Percent distribution of the 34 common bird speciesthrough the 25 survey
stands
........................................................................................................................
37
5. Distribution of speciesthrough 7 habitat types on Grand Bahama Island ........ 48
6. Positionand dispersionof 5 pine foliage gleanersalong 9 gradientsof the pine
forest habitat
............................................................................................................
7. Habitat specialization along 7 gradients for various elements of the Grand
Bahama land bird community ...............................................................................
8. Overlap in habitat selectionin winter ..................................................................
9. Habitat overlap and geographic derivation ............................................................
10. Habitat overlap and residency status ....................................................................
11. Physiognomic characteristicsof the submature pine forests ...............................
12. Dominant tree and shrub speciesin submature pine forests ................................
13. Size, density and biomass of the 4 residency elements in the 3 seasonal pine
forest
commtmities
................................................................................................
50
50
53
54
54
56
57
60
14. Residencystatus, density, and biomassof member and visitor speciesin the 3
seasonalpine forest communities ......................................................................... 61
15. Vertical distribution of bird populations in the wintering commtmity of the
pine forest ................................................................................................................
68
16. Volume and structural characteristicsof the major habitat compartments of
the pine forests ....................................................................................................... 72
17. Demographic characteristicsof the bird populations in the 4 major compartments of the pine forest ........................................................................................77
18. Compartmentpreferencesof membersof the wintering and breedingcommunities
19.
20.
21.
22.
23.
24.
25.
26.
.........................................................................................................................
78
Guilds and guild provincesrecognized in the submature pine forests ............. 82
Foraging guild distributionsof members of the pine forest bird commtmity .... 84
Speciesdensitiesin the foraging guilds ................................................................ 86
Biomass of each speciesin the foraging guilds .................................................... 88
Percent speciesdensity compositionof foraging guilds .................................... 90
Percent biomasscompositionof foraging guilds ................................................. 92
Foraging methods of members of the needle-gleaningguild ............................. 102
Composition and structure of the 18 foraging guilds of the Grand Bahama
forest
communities
.................................................................................................
107
27. Overlap in guild membershipin the wintering commtmity ............................... 110
28. Overlap in guild membershipin the breedingseasoncommtmity........................ 111
PREFACE
This monographhad its beginning24 yearsago when I undertooka study of
the habitat distribution
and structure of several communities of land birds in
Central Africa. As I launchedinto this project it becameclear that available
techniques
were totally inadequatefor the quantitativeanalysesI neededand
that it was up to me to developnew ones. Some progresswas made that year
with a systemfor describing
andmeasuring
habitats(Emlen 1956), but I returned
to the Stateswith no soliddata on eitherpopulationdensitiesor habitatrelations.
Returningto other researchactivities,I postponedfurther fieldwork on these
problemsuntil 1967 when I was able to devotea springsemesterto a studyof
the structureand dynamicsof the winteringbird communities
of a grass-bushland
area in southernTexas (Emlen 1972). The vegetativestructurewas relatively
simplehere,and besidesimprovingmy techniques
of habitatdescriptionI worked
intensivelyon developing
censusmethodsfor smallland birds,methodsthat would
provideabsolutedensityvaluesby equatingvariablesin transectcountswith the
detectabilitycharacteristics
of eachspecies(Emlen 1971).
After testingthesehabitat measurementand censustechniquesin a variety of
situations,I selectedthe extensivepinelandforestsof the southeastern
statesand
neighboringBahamaislandsfor the type of studyI had tried to conductin Africa
15 yearsbefore. The work of William B. Robertsonin this area provideda valuable backgroundon ecologicalconditionsand faunal composition(Robertson
1955), and I beganthe studiesdescribedin this monographin Januaryof 1968.
During the 20 yearssincethe conceptionof this project,approaches
to the study
of communityecologyhave changedconsiderably.Important new conceptson
the niche, competition,and communitydynamicshave appeared,and emphasis
has shiftedstronglyfrom descriptivestudiesto model buildingand testing. Work
in the old patternseemsdimmedby the brillianceof thesenew studies.But I am
repeatedlyimpressedthat the imaginativecreationsof theoreticalecologistsrarely
survivelong in this modernera of scientificfermentunlessthey are built on solid
empiricaldata. Most of the speculationsand interpretationsin this monograph
will doubtlessbe ephemeralas our scienceprogresses;
I only hope that the materials on which they are basedwill prove to be solid and clearly presented.
xi
1--INTRODUCTION
This monograph
represents
an attemptto analyzethe populationstructureand
dynamicsof a definitiveavifauna.Unlike a typicalfaunalstudyit focuseson the
densities
and ecological
distributions
of species
throughthe habitatsand foraging
substrates
of the vegetation
and undertakes
to evaluateand interpretsomeof the
factorsunderlyingcommunitystructureand regulation.My approachis descriptive
with an attemptto presenta broadand balancedpictureof the entiresystem.
I selected
an islandasthe sitenot because
of a particularinterestin the problemsof insularity,but becausean islandcommunityis shieldedby surrounding
water barriersfrom the confusionof irregularingressand egressby speciesthat
belongonlyperipherally
or reallydo notbelongat all.
As an islandsite for the study,Grand Bahamawas large enoughto provide
an assortment
of habitattypes,yet smallenoughto minimizethe confusing
effects
of regionalnomadismand local geographicvariation. One type, lowland pine
forest,was represented
extensivelywhile otherswere restrictedto small blocks
or beltsadequate
to holdonlylimitedpopulations.GrandBahamais particularly
well situatedfor observingthe extent and impact of seasonalmigrant invasions
on the structureand integrityof residentcommunities.Little ornithological
work
has been done on Grand Bahama, but the avifauna of the region has been well
coveredduringthe past 50 years.
The fieldwork was done during the months of January through May in 1968
and 1969. In 1968 I spentalternate2-week periodson Grand Bahamaand in
southernFlorida censusingthe bird populationsand plotting their distribution
throughthe vegetationof the pine forestsfor comparativematerial. In 1969 I
spent the entire period on Grand Bahama, measuringcommunity structuresand
populationdensitiesat 25 survey sites during January, February, and March,
and conductingfurther censusand behaviorobservations
in the pine forestsin
April and May. I returnedfor brief visitsin Januaryand May of 1971 to check
severaldetailsand to collectmaterialon avian food resourcesin the pine foliage.
The studycoveredthe small land birds only, thosethat interacteddirectlyin
exploitingthe resourcesof the terrestrialvegetationand its invertebrates.Other
membersof this trophicassemblage,
especiallythe lizards,shouldlogicallyhave
beenincluded. They are a minor elementexceptin the shrubsand groundvegetation, but their omissionis due primarilyto my limitedversatilityand lack of time.
The rationale for ecologicalanalysisin this study is to recognizethree hierarchicalsystems
of decreasing
inclusiveness
throughwhichdispersioncan be charted:
a habitat level, a within-habitat compartmentlevel, and a substratelevel. Individual birds are regardedas ranging through the various subdivisions
of these
systemsbut concentratingtheir activitiesin those subdivisionswhere conditions
are most favorablefor their morphologicaland physiologicalcharacteristics.The
organization
of thismonograph
is basedon thisapproach.After presenting
backgroundmaterial in the first three chapters,! examineacross-habitatdistribution
in chapters4 and 5, and then compartmentand substratedistributionin the pine
foresthabitat in chapters6, 7, and 8.
Descriptivematerialon the bird specieswith scientificnamesand quantitative
2
ORNITHOLOGICAL
MONOGRAPHS
NO.
24
data on ecologicaland distributionalcharacteristics
is presentedin an appendix.
Nomenclaturefor North American speciesfollows the A.O.U. Checklist (1957)
and supplements
(1973); for the Antilleanspecies
I havefollowedBond (1971).
2--METHODS
SELECTION OF SURVEY SITES
I first surveyedthe physiognomic
and floristiccharacteristics
of the vegetation
of the islandto determinethe natureand rangeof habitatvariationand to provide
a basisfor selectingappropriatetractsfor intensivestudy. I thenselected25 tracts
representingthe full range of variationbut each showingmaximuminternal uniformity of structureover at least20 ha. Sketchmapsof eachtract were prepared,
and transectroutes0.9-1.8 km in lengthwere laid out bisectingthe most typical
portion of the tract, avoidingedges,and taking advantageof existingtrails and
roadways.Threetractsin the submature
pineforeststhat dominated
the island
were used for intensivestudiesof within-forestdistributionin 1968 (chapters 6,
7, and 8). The other 22 representedvarioushabitat types and, togetherwith the
3 submature forest areas, were used for studies of across-habitatdistribution in
1969 (chapters4 and 5).
HABITAT
MEASUREMENTS
The vegetationat each of the 25 sites was sampledalong a seriesof habitat
dimensionsof presumedimportanceto the birds. Data were recorded according
to a systematicplan in the 3 submaturepine forest tracts and less formally for
the other 22 tracts.
In
the 3 submature
forests the measurements
were
made
at stationslocatedby random number serieswithin each of 60 blocks (20 in each
stand) 66 m long and 90 m wide, evenly straddlingthe transectroute. Each
station point served as the center for measurements(trunk diameter, height,
crown diameter,crown depth, and distance)of the nearesttree in each of three
size classes(emergent, canopy, subcanopy)in each of four radial quadrants.
Twenty points surroundingeach station point (at 3-m intervals) along 4 equispacedradii) were used for data on tree canopy, shrubvegetation,and ground
vegetation. Tree canopy (presenceand type) was recordedwith a zenith sighting device (Emlen 1967); shrub type, height, crown diameter,and species,and
ground cover type, depth, and density were recordedby plumb line contacts.
A total of 240 data pointswas thus obtainedfor most arborealdimensions,and
1200 for the others.
Becauseof time limitations,vegetationevaluationson the other 22 tracts were
madeby lesssystematic
sampling,pacing,and subjectivecomparisonwith diagrammatic representations
of canopycover. A shorthandsystem(Emlen 1956) was
usedin whichvegetationtype,foliagetype,foliagedensity,canopyheight,canopy
cover, and patchinesswere recordedin formulae representingthe tree, shrub,
and groundcoverstrata.
For within-habitat'distributionstudiesthe vegetationin all standswas apportionedinto compartments
basedon plant type, vertical zone, and horizontalzone
in the tree, shrub, and-groundcover strata (Fig. 1). I recognized7 plant types
1977
EMLEN:
GRAND
BAHAMA
BIRD
COMMUNITIES
3
in the forestfrom deadstumpsand emergentpines(toweringabovethe dominant
canopy) to ground cover, 5 vertical divisionsor levels in each plant from the
lower stem to upper crown, and 5 horizontaldivisionsarrangedas concentric
zonesaroundeachplant from the tree trunk or shrubcore to the peripheryand
the emptyspacearoundand betweenplants. Any point in the entirespacebetweenthe canopytop and the groundis thus assignable
to 1 of 175 compartments
in this system.In practice,many compartments
were nonexistent,
undetectable,
or unmeasurable,
and for data analysisthe numberwas reducedby combinations
and eliminations
to 11.
The volumeof standingvegetation(numberof m3 of spacecontainingplant
stemsof foliage) was calculatedfor the 3 vegetationstrata and the 1! recognized
compartments
of eachstand. Viewing the averagetree crown as a verticalcylinder
with roundedtop and bottom, I multipliedthe mean crown depth in metersby
0.75 by the canopycoverin m3 per ha for each tree classto give a volumetric
densityvalue in m• per ha. A similar procedurewas used for the shrub and
groundvegetationstrata. Volumesfor all compartmentsper ha were derivedby
calculatingthe percentrepresentation
of each in its stratumand multiplyingby
the stratumvolume. Volume of the air spacebetweenplants was obtainedby
subtracting
all compartment
volumesfrom the total spacebetweengroundsurface
and tree tops. Values for bark and wood surfaceson tree trunks and stumps
were calculatedin surfaceunits (m 2) by multiplying mean trunk circumference
in theupperandlowerhalf of treesby the trunklengths.
The complexityof the habitat is important as a comprehensive
environmental
parameterin communitystudiesbut is difficultto reduceto a simple,meaningful
index. In this study I followed the procedureintroducedby MacArthur and
MacArthur (1961), using the densityof vegetationin three horizontallayers
corresponding
to the trees,shrubs,and groundcover as the basisfor calculating
an overall habitat diversityindex. Becauseof marked differencesin texture and
screeningcharacteristicsof the foliage in the three layers on Grand Bahama,
however,andbecause
of the presumed
importance
of twigsand stemsas perching
substrates,
I used the presenceor absenceof standingvegetationin blocksof
volumetric space as the basis of measurementsrather than the leaf surface or
foliage screeningmeasuresadoptedby the MacArthurs. The information theory
equation(H' = p• loge pi) was usedto calculatethe index values. Natural logarithmswere usedin all diversitycalculations.
ANALYSIS OF HABITAT DISTRIBUTION
The relativepositionsof the 25 standswith respectto three basichabitat fea-
tures-canopyheight,canopycoverage,and foliagetype--are graphicallydisplayedin Figure10. The groupings
of symbolsin this figureprovidea relatively
objectivebasisfor recognizing7 habitat typesuseful in generaldiscussions
of
speciesdistributions.This approachof plotting standpositionson bicoordinate
gridswasalsousedasthebasisfor tracingthe quantitative
distribution
of species
and of variouscommunityattributesalongselectedhabitatgradients(Fig. 11).
Densityor indexvaluesfor a species
are simplyenteredat the coordinate
position
4
ORNITHOLOGICAL
MONOGRAPHS
/.
Emergent
•.•/
•
I
/
/
/
/
• ! • /'• //f'•
/
/• •
........
........
--- ....
/
YJYYoYYYY¾
.,,o
NO.
24
Pines
Subcanopy
Pines
DeadPineStumps
Broadleaf
Trees
// •"•-----Canopy
Pines
/-----Shrubs
(3size
crosses)
/
/--Ground Cover
o.1,,,
o,,,
L,Io,looJQ
3o,H1,,,,9,.,1,
0o-T/o
Qcl,..........
SEVEN
PLANT
TYPES
Crown
Trunk
Top
• Lower
-- --M,I.
Upper OpenSpoce
Air
Shrubs
Space
Upper
Lower
Ground
Cover
FIVE
LEVELS
FIVE
CONCENTRIC
ZONES
ELEVEN
COMPARTMENTS
Fromm 1. Plant types and foliage compartmentsused in structural analysesof the forest
habitat. M.O. = middle outside, M.I. = middle inside, L.O. = low outside, L.I. -----low
inside.
of eachstandin thesediagrams.The resultingpatternsprovidegraphicportrayals
of densityandattributedistributions
alongtheselected
gradients.
BIRD
POPULATION
MEASUREMENTS
Populationdensitiesfor all bird specieswere obtainedfrom transectcounts
convertedto absolutevaluesby applyinglocally determineddetectabilitycoefficientsbasedon the lateral distributionpattern of detectionpoints (Emlen 1971).
All counts were started within
a half hour after local sunrise and extended for
from 1.2 to 2.1 hours. I alwayswalked the transectsalone, coveringthe route
without deviationsat between1.0 and 1.6 km/hr. All detections,visual or auditory, were recorded.
WITHIN-HABITAT
DISTRIBUTION
AND ACTIVITY
MEASUREMENTS
In addition to identifyingeach bird and estimatingits lateral distancefrom
the trail, I was able to recordbasicinformationon activity and positionwithin
the habitat for most of the detections tallied on the census transects. These ob-
servations
includedactivitywhenfirst detected(whetherforaging,singing,resting,
being agressive),plant type in which located, vertical position (level) in the
plant, radial position(zone) in the plant, and heightabovethe ground. Weather
conditions(temperature,
cloudcover,wind directionand speed,wetnessof vegetation) were alsorecordedfor all trips afield.
Close attention to the task of detectingand recordingall birds encountered
on the morningtransectcountsprecludedsustainedobservationsof behavior and
1977
EMLEN:
GRAND
BAHAMA
BIRD
COMMUNITIES
5
foragingmethods. Unscheduledobservationtime later in the day was used for.
suchwork as well as for measuringvegetation,findingnests,and mappingterritories.
In these unscheduled observations I recorded the basic information
de-
scribedaboveplusdata on ageof the subjects,
presenceand activityof conspecific
and allospecific
associates,
the foragingperch,the food substrate,
and the foraging method. After an observationor seriesof observations
in one place I evaluated the local habitat selectionby recordingthe type, size, and densityof foliage
within approximately1 m of the bird, and the proportionof tree cover,shrub
cover,and exposedgroundcoverwithin an estimated36-m radius (1 acre).
I usedspacedobservationunits rather than secondsof continuousobserving
on the assumptionthat they would give a more balancedand representative
pictureof foragingactivityby a population.In orderto furthersuppress
biasesrelated
to atypicallocal conditionsor individualidiosyncrasies,
I attemptedto distribute
observations
as widelyas possiblein theseactivityobservations.Where one individual or an uncommonspeciesremainedfor continuousobservation,I spaced
the entries at a minimum of • min, and limited the record to 5 entries in a series.
For compartmentdistributionanalyses,the bias inherentin selectedobservation
situations
wasavoidedby usingonlythe transectcounttallies.
3--GRAND
TI-IE
BAHAMA
ISLAND
ENVIRONMENT
Geology.-•Geologically,
Grand BahamaIsland is a long low ridge of oolitic
limestoneof Pleistoceneage, risingat its highestpoint to only about 10 m above
sea level. The groundsurfaceis heavilyerodedwith innumerablepits and deep
solutionholes. Soil is essentiallyabsent,the organicmaterialsdepositedfrom the
vegetation
leachingor settlingto thebottomof theholes.
Physiographic
history.--Beinga tectonicallystableborder ridge of the Little
BahamaBank (Fig. 2), the surfacearea of Grand Bahamaexpandedmany fold
when sea levelswere low duringthe Pleistocene
glacialepochsand alternately
shrankto zero or nearlyzero duringthe interglacialperiod of high sealevel. Thus
the terrestrialflora and fauna were probably annihilatedrepeatedlyby marine
inundation,the last suchepisode,accordingto data from southernFlorida, end-
ing about80,000 yearsago (Alt and Brooks1965). No directland connections
exceptwith neighboring
Abaco Islandhave existedsincethe tertiary. During
the Pleistoceneice advances,however, the broad low surfaceof the Little Bahama
land mass,of which Grand Bahama is a part, extendedto within 50 km of the
Great Bahamaland massto the southwhich, in turn, approachedto within 35
km of Cuba. All of this complexhasbeenseparatedfrom the peninsulaof Florida
sinceat leasttertiarytimesby the deepand relativelywide (105 km) rapidly
flowingcurrentof the Florida straits.
Since
emerging
fromthedeep
seas
oftheSangamon
interglacial
period
(80,000
years ago) Grand BahamaIsland has fluctuatedin size from its present1200
km2 or smaller to 16,500 km2, the area of the Little Bahama Bank of which it is
a part. Estimatesof a sea-levelsubsidence
to the -120 m mark duringthe last
Wisconsinice advance(about 15,000 years ago) (Milliman and Emery 1968)
6
ORNITHOLOGICAL
FIGURE 2.
MONOGRAPHS
NO.
24
Map of the western Bahama Islands showingtheir position with relation to neigh-
boring land masses and to shallow "banks" that mark the extent of the island areas
during Pleistoceneglacial periods.
would indicate an expansionto about 15,000 km2 at that time. Since then the
seahasbeenrisingslowly,reachinga stageof -7 m about4,000 yearsago (Scholl
et al. 1969). At this level the island of Grand Bahama must still have been six
or eighttimesits presentsizeand formeda continuous
land masswith neighboring Abaco Island. The major shrinkingin size has occurredover the past few
thousand
yearsduringwhichsealevelshavebeenrisingat about0.5 m per 1,000
years(Schollet al., op. cit.).
Clirnate.--The climateof Grand BahamaIsland is subtropicalwith temperaturesrangingfrom a mean of 20.3øC in Januaryto 28.2 in July (data from the
Freeportairport). Annual rainfall averages1,216 mm and occursthroughout
the year with about twice as much in summeras in winter. The trade winds
producea dominantsoutheasterly
air flow varyingin directionand intensityunder
the influenceof cyclonicdisturbances
to the north. Hurricanesoccuroccasionally
in late summer,the most recentseverestormshitting the islandin 1941 and 1949.
Recenthistory.--GrandBahamawas almostundisturbed
and essentially
unpopulateduntil 1929 when extensivetimber cuttingwas initiated. Most of the
timberwasstrippedfrom the islandfor minepropsor pulp duringthe late 1940's
1977
EMLEN:
GRAND
BAHAMA
BIRD
COMMUNITIES
7
and 1950's,but reproduction
has beenrapid sincethat time, and no extensive
cuttingother than local clearancefor real estatedevelopment
has been done
since1959. Standscut between 1946 and 1949 were 10 and 12 m high in 1968
and possessed
a lush shrubunderstoryon the southhalf of the Island, lesslush
on the north half. Standscut duringthe 1950's showedvariousstagesof recovery
re_flecting
meangrowthratesof roughly0.5-0.6 m per year. Height,density,
and understory
vegetation
are secondarily
influenced
by irregulargroundfires
and occasional
crownfires. A few smalltractsof pine wereapparentlydenuded
by saltwaterencroachments
duringstorms.
The principalmethodusedin timbercuttingin the 1940'sand 1950'swas to
removeall treesotherthan saplingsand a few tall scatteredstems(aboutfive
treesper acre) usedfor anchoring
the haulinggearand supposedly
as seedtrees
for forestreproduction.The remainingsmalltreesand brushwere then usually
levelledand burned. This procedurehasresultedin rathereven-aged
standswith
a scatteringof slenderrelic "emergents"
abovethe dominantyoungcanopy. One
patchof about4.4 km• on the northsidewascompletely
clearedand kept open
for habitationand farmingduringthe early lumberingperiod. Abandonedfor
10-12 years,it is now vegetatedwith bracken,coarseforbs, and tall grasses,
and exceptfor the narrowcoastalstripsand a few urbanareasand golf courses,
constitutes
the only openland on the island.
Furtherdisturbances
causedlargelyby real estateoperationssince1959 include
the construction
of the city of Freeport-Lucayawest of the Island'scenter,now
coveringabout30 km-ø,and a networkof unpaveddevelopment
roadspenetratingin an irregularnetworkintonearlyone-halfof theIsland'sinterior.
THE
BIRDS
At the time of this study (1968-69) there were apparently33 speciesof land
birdsexcluding
birdsof preybreedingon GrandBahamaIsland. Thirty of these
were permanentresidents,and three were summerresidentsmigratingin from
winter rangesto the south. An additional34 speciesmovedin from the north
duringthe winterseason,and 8 morewerepresentbrieflyas transients
duringthe
springmigrationperiod.
Geographicderivation of the breedingspecies.--Grand Bahama, an oceanic
island,containsno relict continentalspeciesin its breedingfauna and has been
populatedentirely by over-watercolonizationfrom the neighboringcontinents
and islands. Becauseof the relative recencyof its final emergenceas an island
capableof supporting
a terrestrialfauna,it presents
a goodopportunity
to study
the geographic
originsof its colonists.The two primary sourcesare obviously
the North American continent to the north and west and the Antillean Islands to
the south.The nearestland on the continentis 105 km awayacrossthe deepand
geologically
ancientFloridastraits(Fig. 2). Cuba,the nearestand alsothe largestof theAntilles,liesabout500 km away,but onelarge"steppingstone"(Andros
Island) and a seriesof smalleroneshavebeencontinuously
availablefor dispersing birdssinceGrandBahama's
emergence.
The waterbarriersto the southand
north of Androswere about 35 and 50 km wide respectively
at lowestsea level
15,000yearsago,andare 190 and180 km wideat thepresenttime.
8
ORNITHOLOGICAL
MONOGRAPHS
NO. 24
AbacoIsland,lying about30 km to the eastof Grand Bahama,is merelyanother ridgeon the Little BahamaBank, and, not surprisingly,
has a very similar
avian fauna.
Originsand routesof invasion.--In the absenceof a direct record of invasions
and colonizations,
the presentgeographicrangesof the membersof the fauna
providethe bestavailableindicationof originsand routesof invasion.The direction andextentof the rangesof eachof the 33 membersof the breedingland bird
fauna are graphicallyportrayedin Figure 3. Circlesto the left of the central
circlein this diagramindicatecontinentalaffinities;circlesto the right indicate
Antilleanaffinities.The degreeof shadingin eachlateralcirclereflectsthe closenessof phylogenetic
relationship
of the relatedformsin eachof four increasingly
remoteregions.Informationincorporated
in thesediagrams,togetherwith analyses
of avian dispersalin the area by Chapman(1891) and Bond (1963), provides
a basisfor tentativedeductionson the geographicderivationof each memberof
the Grand Bahamacommunity. The deductionsare presentedin code form at
the right of each speciesdiagramin Figure 3. A graphicrepresentation
of the
deducedoriginsand routesof invasionis presentedin Figure 4.
Of the 32 species(exludingthe introducedHouse Sparrow), 7 are best representedby conspecifics
or othercloselyrelatedformson the continentto the northwestand are accordingly
considered
to have arriveddirectlyfrom North America.
Two of these,the wide-rangingMourningDove and the Blue-grayGnatcatcher,
have apparentlydevelopedno taxonomically
recognizedmorphological
changes
sincecolonizingGrand Bahama(Co). Four, the Hairy Woodpecker,the BrownheadedNuthatch, the Yellow-throatedWarbler, and the Pine Warbler have been
recognized
by taxonomists
assubspecifically
distincton thoisland(C•), andone,
the BahamaYellowthroat,is consideredto have evolvedto full speciesstatus(C2).
The ancestorsof 11 of the communitymembersappearto have come from
North or CentralAmericarelativelyrecentlybut reachedGrand Bahamaby way
of the Greater Antilles. All of thesehave changedmorphologicallyin the course
of their Caribbeanperegrinations.The sequenceof eventsin the courseof their
historyof dispersal
requires
considerable
speculation,
but threespecies,
the Cuban
Nighthawk,NorthernMockingbird,
andYellowWarbler,apparently
subspeciated
in the Greater Antillesbefore spreadingnorth into the Bahamas(C• A0); one,
the Ground Dove, has severaldistinctracesin the West Indies, all differentfrom
the continentalforms, and probablyhas subspeciated
at least twice in reaching
Grand Bahama (C• A•). Five speciesare found in the Greater Antilles as well
as in the Bahamasand belongto superspecies
or siblingspeciesgroupsalsooccur-
ring on the North Americancontinent.Their ancestraldispersalroutesthus
probablyincludedearlyinvasions
of the GreaterAntilleswheretheyspeciated
beforespreading
northwardto the Bahamas.Two of these,the Black-whiskered
Vireo andOlive-capped
Warbler,showno furthermorphological
changes
en route
to the northern Bahamas (C2 A•). Two species,the Bahama Swallow and the
Thick-billedVireo, I regardas belongingto superspecies
groupswith specifically
distinctrepresentatives
on severalAntilleanislandsaswell as the Bahamas.Ancestorsof the Grand Bahama forms probably speciatedseveral times en route
to theirpresentrange(C2 A2). The interpretation
of the BahamaSwallow(Cal-
1977
EMLEN:
GRAND BAHAMA BIRD COMMUNITIES
White-cr,
Pigeon
Zenoido
Dove
A0
A0
Mourning
Dove
9
CiAo
CO
Brown-hd.
Nuthotch
Northern
Mockingbird
Bahoreo
Mockingbird
GroundDove
CtAi
Red-legged
Thrush
AI
K.-W.
QuoilDove
Smooth-billed
Ani
Cubon
Nighthowk
A0
Blue-groy
Gnotcotcher
AO
Thick-billed
Vireo
CtAO BIk-whlskered
Vireo
CO
CgA
2
C2A
0
Cubon
Era.Hummer
Bohomo
Woodstot
HoiryWoodpecker
A1
A2
C•
Bohomo
Bononoquit
Yellow
Worbler
Boh.
Yellowthr.
Worbler
C•Ao
C
Red-bellß
Woodp.
C2AI Olive-copped
Worbler
C2A
0
Groy
Kingbird
Loggerheod
Flyc.
AO
AI
Stolid
Flycotcher
Gr.Ar•tilleon
Pewee
Bohomo
Swollow
C2Ai House
Spotrow
C2At Striped-hd.
Tonoger
C2A2 BIk-foced
Grossquit
Bohomo
Pine
Worbler
Bohomo
Yellowthroot
A•
C2
X0
A
Gr.AntilL Bullfinch
FIGURE3. Continental and Antillean ranges of the breeding land birds of Grand Bahama
Island. The presenceof the sameor relatedforms (samesubspecies,
species,superspecies)
is indicated at four increasinglyremote stationsin each of the two directions. (Except
for the Bahama Swallow, taxonomy follows Bond (1971) and the AOU Checklist
(1957) and supplementsthereof (1973). My deductionsconcerningthe geographic
derivationof each form on Grand Bahama are indicated by symbolsat the right of the
diagrams. Symbolsfor degree of relationshipare: Solid circle = same subspecies;
circle with cross= samespecies,different subspecies;
circle with horizontalline = same
superspecies,
different species;
diagonalline cuttingcircle = limited occurrence;vertical
line cuttingcircle = recent colonizer. Symbolsfor deducedderivationare: C = North
American continental origin, A ---- Antillean origin, CA = Continent via Antilles.
X • introducedby modernman, /1 ----subspeciated
with invasion,/2 • speciatedwith
invasion, 70 = no change recorded.
lichelidon)as congenericwith Lamprochelidon
is basedon a compositeof taxonomists'opinions(L. Short in litt.).
The 14 speciesclassedas of Antillean origin belongto generathat probably
derivedat an earlyperiodfrom ancestralformsin eitherCentralor SouthAmerica
(Bond 1963). Five of these,the White-crownedPigeon, the Zenaida Dove, the
Key WestQuail Dove, the Smooth-billed
Ani, and the Gray Kingbird,now have
dispersed
rangesin the WestIndiesandshowno taxonomically
recognized
changes
in their northward extensioninto the Bahamas (A0). Nine specieshave undergonetaxonomically
recognized
changes
in the Bahamas;
eightof these,the Cuban
EmeraldHummingbird,
Loggerhead
Flycatcher,BahamaMockingbird,Red-legged
Thrush,BahamaBananaquit,Striped-headed
Tanager,Black-facedGrassquit,and
i0
ORNITHOLOGICAL
c-
MONOGRAPHS
NO.
24
FROM
AMERICAN
CONTINENT
CA- FROM
CONTINENT
VIA ANTILLES
Cc
C2
C,
ClA1
C
C2A1
C2A2
A2
A•
Ao
A-FROM
ANTILLES
FIGURE4. Faunal derivation of the speciescomprising the breeding land bird fauna of the
Grand Bahama Island. Each arrow represents a group of species. The width of the
arrow indicates the number of species in the group. A cross line on the arrow shaft
showsthat subspeciationhas occurred; a double line, that full speciation has occurred.
The symbolsat the baseof each arrow match thoseusedin Figure 3.
Greater Antillean Bullfinch, to the subspecieslevel (A•)
Woodstar, to the specieslevel (A2).
and one, the Bahama
Colonization
patterns.--Generalizations
basedon patternsof dispersion
through
island chains can provide suggestions
on colonizationhistoriesand sequences.
Of the seven speciescolonizing Grand Bahama directly from North America
only two have pushedfarther into the Antillesthan the first few northernBahama
Islands (cf. Fig. 3) and thesetwo, the Mourning Dove and the Pine Warbler,
occurringas distinctsubspecies
in the Greater Antilles, may have reachedthose
sitesby an earlier invasionor a separateinvasionfrom Central America. Such
patternsof limited and essentiallyunbrokenpenetrationof the island chain suggestrecentinvasion,i.e. an earlystagein taxondispersion
asvisualizedby Ricklefs
and Cox (1972) in their taxon cycle model for archipelagos.From the other
direction,the Southeast,Grand Bahamais at the end of a long islandchain of
dispersion. The 25 speciesconsideredto have come by this route tend to show
the extendedand broken distributionpatternsthat characterizeadvancedstages
in the taxoncycleof Ricklefsand Cox.
Theseobservations
suggestthat membersof the Antillean faunal elementhave,
in general,a longerhistoryin the northernBahamaIslandsthan thoseof the
NorthAmericanelement.Otherfactorsmustbe considered,
however,especially
the vegetationpatternsthroughthe Bahamasand the habitat characteristics
of
1977
EMLEN:
GRAND
BAHAMA
BIRD
COMMUNITIES
11
the bird species.Pine forestsdominateGrand Bahama and the other northern
islands,while brushyvegetationcoverthe islandsto the southand east. With the
exceptionof the MourningDove, a highly eurytopicspecies,all sevenof the
colonizersfrom North America are pine forest inhabitantson Grand Bahama,
eventhe Gnatchatcherand the Yellowthroat,whichelsewhereare characteristically
broad leaf forest and marshlandbirds respectively.This does not conform with
Ricklef and Cox's generalizationthat recent (stage I) colonizerstend to occupy
open, coastal, or disturbed habitats. On Grand Bahama these habitats are, in
fact, occupiedby speciesbelongingto the Antilleanelement,speciesthat according to the island penetrationand broken distributioncriteria, should be in advancedstagesof the taxoncycle.
More direct evidencethat the bird speciesof the North American elementof
pinelandbirds did not invade the northern Bahamasuntil quite recently comes
from fossil pollen data indicating that pines were uncommon in the southern
Florida vegetationuntil about 5,000 years ago (Watts 1971). T/he conditions
of rising sea levels and permeablelimestonerock associatedwith this spreadof
pine forestsin Florida must have also existedand could have producedsimilar
effectson the Little BahamaBank. BahamianPines (Pinuscaribaea)probably
reachedGrand Bahamafrom the south (Howell 1972), but whetherthe present
forestswere established
before the postglacialperiod of sealevel elevationis unknown. Avian fossil materialsfrom New ProvidenceIsland (Brodkorb 1959)
indicatethat arborealbird speciesand hence trees were presenton the Great
Bahama Bank to the southeastduring the last glacial stage of the Wisconsin
glaciation.
Turnoverrates.--The faunal historyof an islandsuch as Grand Bahama is of
coursemore than a progressive
succession
of colonizations.Many extinctionsand
replacements
have undoubtedlyoccurredover the millenia, and some species
may have had a historyof repeatedextinctionsand recolonizations.MacArthur
and Wilson (1967) proposedthat the number of speciespresenton an island at
a giventime reflectsan equilibriumbetweenthe colonization
rate relatedparticularly to distancefrom colonization
sources,and the extinctionrate relatedparticularlyto islandsize. Recentstudieson previouslysurveyedislandsoff southern
California(Diamond1969), in the SouthPacific(Diamond1970), in the Virgin
Islands (Robertson 1962), the Cayman Islands (Johnston1975), and on Mona
Island near Puerto Rico (Terborgh and Faaborg 1973) suggestthat a considerable number of both extinctions and new colonizations have occurred on all of
theseislandsduringthe past 50-75 years. Suchdata, if accurate,suggestthat
turnoverratesof roughly1.0-1.5% per year may be representative
for islandsof
the size and positionof Grand Bahama,but other observers(Lynch and Johnson
1976, Lack 1976) have challengedthese values as artifacts of modern human
intervention.
Historical data do not exist to permit direct estimatesof colonizationor extinctionrateson Grand Bahama. One species,the WestIndian Red-belliedWoodpecker,listed as an uncommonspeciesin coastalscrubforestby Bond in 1936,
was apparentlymissingin 1968-69, and two speciesnot noted by Bond, the
MourningDove and HouseSparrow,were presentlocally and in small numbers
12
ORNITHOLOGICAL
MONOGRAPHS
NO.
24
Mangrove
flats
:[•
Hawksbill
Creek
LacayaBeach
KM
FIGURE5. Map of Grand Bahama Island showingin A the distributionof pine forestsand
mangroveflats and in B the locationof the 25 standssurveyedin this study.
in the latter years. The BahamaMockingbird,not reportedon Grand Bahama
by Bond, was collectedin 1960 (Schwartzand Klinikowski1963) and was seen
by severalamateurobserv.
ersduringthe early60's and by me in 1969.
4--THE
HABITATS
AND
THEIR
BIRD
COMMMUNITIES
The term bird communityis usedin this chapterto designateall the birds that
co-occupyan area of habitat at a particularseasonand henceinteractdirectly
with each other. The fauna of Grand Bahama Island is thus composedof an
array of communitiesdifferingboth spatiallyand temporally. Variation is continuousalongboth axes,but I have assigneda seriesof spatialcategories
on the
basis of localities or vegetation types, and of temporal categorieson the
basisof the arrival and departureperiodsof seasonalmigrants.In this chapter
I examinethe spatialdistributionof the birds presenton the Island between10
Januaryand 31 March 1969 while the winter migrantswere still present,i.e.
the winteringcommunities.
VEGETATION
PATTERNS
General description.--Mostof the interior of Grand Bahama Island (roughly
80% of the land surface) is coveredwith moderatelydenseforestsof Caribbean
1977
EMLEN:
1õ16
SOUT. V
CO•ST
$0
I00
75
GRAND
14
9
6
4
V
V
V
V
75
200
200
I
2
VV
BAHAMA
:5 13
VV
BIRD
COMMUNITIES
1719212410222õ23
VVV
VV
13
õ
7
8 1820
12
II
V V
V
VVV
V
VNORTH
COAST
500
I00
500
0 C
o
FmURE 6. Cross-islandprofile (schematic) transectingthe major vegetationzones and types;
approximate average widths of zones are given in meters. The positions of the 25
survey standswith respect to the vegetation zones are indicated above the diagram; the
numberscorrespondto thosein Table 17 and the map in Figure 5.
Pine (Pinus caribaea). Much of this forest was clear cut during the late 1940's
and early 1950's, but the very rapid growthhas restoredthe appearanceof submature forest over most of the area. Broad tidal flats with open, low mangrove
scrubseparatethe pine forestsfrom the sea on the north or leeward side of the
island. The higherwindwardfront on the southernshoresupportsa seriesof
parallel vegetationbelts generallyprogressingfrom a narrow beach backed by
low sanddunesand occasional
palms,througha narrowcoastalstripof halophytic
grasses,herbs, and low denseshrubsand a strip of dense 3-m-high broad-leaf
scrubwith pocketsof cattail marsh to a wider band of 4-5 m scrub that blends
back into the pines. The distributionof thesemajor vegetationtypesis mapped
in.Figure5 and shownin a cross-island
profilein Figure6.
Photographs
in Figure7 depictconditionsin the submaturepine forestsas they
appearedin 1968; thosein Figure 8 show the vegetationin recentlycut forests
and in one older stand. Vegetationfeaturesof other habitat types are shownin
Figure 9.
The structure of Grand Bahama habitats.--Measurements and evaluations of
habitatfeaturesconsidered
to be significantto birdsare presented
in Table 1 for
eachof the 25 standssurveyedin this study. Includedare featuresof each of the
threestratain the vegetation
plus an indexof overallhabitatcomplexityor diversity. The figuresin eachcaseare averagesfor conditionswithin the stand.
Mean tree height varied from 2 m in a recentlycut stand (stand #24-•est. 4
yrs.) to 16 m (max. 22 m) in the oldestof the submatureforests(#1-•est. 30+
yrs.). Trunk diametersin thesetwo standsaveraged5.5 cm and 28 cm (max.
35 cm) respectively.
Old cut stumpsrarelyexceeded
35 cm in diameterat any
site, suggesting
that this approximates
the maximumsize attainedlocallyby the
Carib Pine in undisturbed
forests.
Exceptfor two badlydisturbed
sitesand onemarginalpine-broadleaf
thicket,
tree canopycovervariedfrom 19-45% with densitiesas greatas 60% in patches
of up to 3fiha. In severalstandstherewere2 distinctheightclasses
reflecting2
major disturbancesspaced8-10 years apart. In such casesthe lower stratum