Common Name: SHRIKE, LOGGERHEAD
Phylum: CHORDATA
Class: AVES
Order: PASSERIFORMES
Family: LANIIDAE
Genus: LANIUS
Species: LUDOVICIANUS
SubSpecies: MIGRANS
Taxonomic Authority: PALMER
Taxonomy References: 002
NONGAME
STATE RANK S2
GLOBAL RANK G4
Status References: 016 , 024 , 031 , 039 , 048 , 051 , 040
"Inhabits open country with scattered trees and shrubs, fencerows and hedgerows. Prefers areas with thorny trees and short herbaceous vegetation. Require elevated foraging perches."
Primary Habitat: "Savanna/Shrub/Woodland matrix"
References: 020 , 021 , 022 , 023 , 031
"Uncommon permanent resident in west, rare in east *01*."
Known | Likely | Unknown | Not Likely | Historic | Extirpated |
---|---|---|---|---|---|
ADAIR | |||||
ANDREW | |||||
ATCHISON | |||||
AUDRAIN | |||||
BARRY | |||||
BARTON | |||||
BATES | |||||
BENTON | |||||
BOLLINGER | |||||
BOONE | |||||
BUCHANAN | |||||
BUTLER | |||||
CALDWELL | |||||
CALLAWAY | |||||
CAMDEN | |||||
CAPE GIRARDEAU | |||||
CARROLL | |||||
CARTER | |||||
CASS | |||||
CEDAR | |||||
CHARITON | |||||
CHRISTIAN | |||||
CLARK | |||||
CLAY | |||||
CLINTON | |||||
COLE | |||||
COOPER | |||||
CRAWFORD | |||||
DADE | |||||
DALLAS | |||||
DAVIESS | |||||
DEKALB | |||||
DENT | |||||
DOUGLAS | |||||
DUNKLIN | |||||
FRANKLIN | |||||
GASCONADE | |||||
GENTRY | |||||
GREENE | |||||
GRUNDY | |||||
HARRISON | |||||
HENRY | |||||
HICKORY | |||||
HOLT | |||||
HOWARD | |||||
HOWELL | |||||
IRON | |||||
JACKSON | |||||
JASPER | |||||
JEFFERSON | |||||
JOHNSON | |||||
KNOX | |||||
LACLEDE | |||||
LAFAYETTE | |||||
LAWRENCE | |||||
LEWIS | |||||
LINCOLN | |||||
LINN | |||||
LIVINGSTON | |||||
MACON | |||||
MADISON | |||||
MARIES | |||||
MARION | |||||
MCDONALD | |||||
MERCER | |||||
MILLER | |||||
MISSISSIPPI | |||||
MONITEAU | |||||
MONROE | |||||
MONTGOMERY | |||||
MORGAN | |||||
NEW MADRID | |||||
NEWTON | |||||
NODAWAY | |||||
OREGON | |||||
OSAGE | |||||
OZARK | |||||
PEMISCOT | |||||
PERRY | |||||
PETTIS | |||||
PHELPS | |||||
PIKE | |||||
PLATTE | |||||
POLK | |||||
PULASKI | |||||
PUTNAM | |||||
RALLS | |||||
RANDOLPH | |||||
RAY | |||||
REYNOLDS | |||||
RIPLEY | |||||
SALINE | |||||
SCHUYLER | |||||
SCOTLAND | |||||
SCOTT | |||||
SHANNON | |||||
SHELBY | |||||
ST. CHARLES | |||||
ST. CLAIR | |||||
ST. FRANCOIS | |||||
ST. LOUIS | |||||
STE. GENEVIEVE | |||||
STODDARD | |||||
STONE | |||||
SULLIVAN | |||||
TANEY | |||||
TEXAS | |||||
VERNON | |||||
WARREN | |||||
WASHINGTON | |||||
WAYNE | |||||
WEBSTER | |||||
WORTH | |||||
WRIGHT |
References for distribution: 001 , 003 , 004 , 005 , 006 , 007 , 008 , 010 , 011 , 012 , 013 , 014 , 016 , 017 , 018 , 019 , 037 , 050 , 015
Des Moines R.
Wyaconda R.
North Fabius R. and Middle Fabius R.
South Fabius R.
Miss. R. from Des Moines R. to MO. R.; and North R.
North Fork from Headwaters to South Fork
South Fork from Headwaters to North Fork
Salt R.
Cuivre R.
Dardenne Creek
Miss. R. from St. Louis to River Aux Vases
Meramec R.
Bourbeuse R.
Big R.
Miss. R. from River Aux Vases to Ohio R.
Castor R. and Castor R. Diversion Channel
Miss R. from Ohio R. to Arkansas Border
St. John's Ditch and Blue Ditch
St. Francis R. from Headwaters to Wappapello Dam
St. Francis R. from Wappapello Dam to Arkansas Border
Little R.
Area Bordered by Black R. and St. Francis R. South of Quintan, MO
Mo. R. from Iowa Border to Nishnabotna R.
Nishnabotna R.
Mo. R. from Nishnabotna R. to Nodaway R.
Nodaway R.
Mo.R. from Nodaway to Kansas City
Platte R.
One Hundred and Two R.
Northwest Corner of Jackson County
Grand R. from Headwaters to Shoal Creek
Thompson R.
Grand R. from Shoal Creek to MO. R.
Chariton R. from Headwaters to Shuteye Creek
Chariton R. from Shuteye Creek to Mo. R.
Little Chariton R.
Marais Des Cygnes from Headwaters to Little Osage R.
Little Osage R.
Marmaton R.
Osage R. from Headwaters to Warsaw, MO.
Sac R.
Pomme De Terre R.
South Grand R.
Osage R. from Warsaw to Bagnell Dam
Niangua R.
Osage R. from Bagnell Dam to Mo. R.
Gasconade R. from Headwaters to Big Piney R.
Big Piney R.
Gasconade R. from Big Piney R. to Mo. R.
Mo. R. from Kansas City to Little Chariton R.
Mo. R. from Little Chariton R. to Gasconade R.
Lamine R.
Blackwater R.
Mo. R. from Gasconade R. to Miss. R.
White R. above Tablerock Dam
James R.
White R. below Tablerock Dam and Little North Fork White R.
North Fork White R.
Black R.
Current R.
Fourche Creek
Warm Fork Spring R. and South Fork
Eleven Point R.
Lost Creek
Spring R.
Indian Creek
Comments: "Likely to occur in units listed, based on county occurrence."
Central Till Plains, Mississippi River Alluvial Plains, Osage Plains, Ozark Highlands
Comments: ""
Bluestem Prairie/Oak Hickory Forest
Cedar Glades
Oak-Hickory Forest
Oak-Hickory-Pine Forest
Southern Floodplain Forest
ALL
Glaciated Plains
Glaciated Plains: Western
Glaciated Plains: Grand River
Glaciated Plains: Eastern
Glaciated Plains: Lincoln Hills
Big Rivers
Big Rivers: Upper Missouri
Big Rivers: Lower Missouri
Big Rivers: Upper Mississippi
Big Rivers: Lower Mississippi
Ozark Border
Ozark Border: Missouri River
Ozark Border: Mississippi River
Ozark
Ozark: Springfield Plateau
Ozark: Upper Ozark
Ozark: St. Francois Mountains
Ozark: Elk River
Ozark: White River
Ozark: Lower Ozark
Mississippi Lowlands
Mississippi Lowlands: Crowley's Ridge
Mississippi Lowlands: Lowlands
Osage Plains
Species is associated with "Terrestrial" habitats.
References for Aquatic Associations:
Cereal Grain
Perennial Grass (Warm season)
Perennial Grass (cool-season)
Shrub-Grass
Fruiting Tree-Shrub
Eastern Red Cedar (30-70% crown closure)
Savanna (Grass-Shrub)
References for Habitat Types: 025 , 031 , 045
Savanna
Dry Savanna
Dry-Mesic Savanna
Mesic Savanna
Limestone/Dolomite Savanna
Chert Savanna
Sandstone Savanna
Sand Savanna
Igneous Savanna
Prairie
Dry Prairie
Dry-Mesic Prairie
Mesic Prairie
Wet-Mesic Prairie
Limestone/Dolomite Prairie
Dry Limestone/Dolomite Prairie
Dry-Mesic Limestone/Dolomite Prairie
Chert Prairie
Dry Chert Prairie
Dry-Mesic Chert Prairie
Sandstone/Shale Prairie
Dry Sandstone/Shale Prairie
Dry-Mesic Sandstone/Shale Prairie
Sand Prairie
Dry Sand Prairie
Dry-Mesic Sand Prairie
Hardpan Prairie
References for Terrestrial Natural Communities: 020 , 021 , 022 , 023 , 025 , 028
"Carnivore"
Comments for larval food habits:
""
References for larval food habits:
Juvenile diet similar to adult's; Not Specified
Comments for Juvenile Food Habits:
""
References Juvenile Food Habits 021 , 022 , 023 , 027 , 030 , 031 , 056
Lepidoptera (butterflies); Larva stage
Hemiptera (water bugs, water boatmen, stink bugs); Not Specified
Coleoptera (beetles); Not Specified
Diptera (flies, midges, mosquitos, gnats); Not Specified
Hymenoptera (sawflies, ants, wasps, bees); Not Specified
Osteichthyes (bony fishes); Not Specified
Amphibians; Not Specified
Arachnids (spiders, ticks, mites, scorpions, daddy longlegs); Not Specified
Crustaceans; Not Specified
Insects
Insects; Not Specified
Odonata (dragonflies, damselflies); Not Specified
Orthoptera (grasshoppers, crickets, mantids); Not Specified
Parulidae (wood warblers); Not Specified
Fringillidae (grosbeaks, sparrows, finches, and buntings); Not Specified
Terrestrial Insects; Not Specified
See comments on seasonal variation; Not Specified
Arthropods; Not Specified
Snails; Not Specified
Cricetidae (woodrats, mice, voles, lemmings); Not Specified
Birds; Not Specified
Apodidae (swifts); Not Specified
Alaudidae (larks); Not Specified
Troglodytidae (wrens); Not Specified
Muscicapidae (thrushes); Not Specified
Salientia (frogs, toads, peepers, tree frogs); Not Specified
Reptiles; Not Specified
Serpentes (snakes); Not Specified
Mammals; Not Specified
Soricidae (shrews); Not Specified
Talpidae (moles); Not Specified
Lepidoptera (butterflies); Adult Stage
Comments for Adult Food Habits:
""
References Adult Food Habits 021 , 022 , 023 , 027 , 030 , 031 , 032 , 043 , 056
References for egg niches requirements:
References for feeding larvae niche requirements:
References for resting Larvae niche requirements:
Other niche requirements specified in comments(99999)
Elevation specified in comments(00240)
General habitat association specified in comments(00270)
Edge: woodland/old field edge
Edge: woodland/grassland edge
Edge: grassland/old field edge
Successional stage: abandoned field
Shrubs
Height of herbaceous vegetation specified in comments(00630)
Hedgerows
Fencerows: shrubby fencerows
Human association: residential lawn/ornamental trees/shrubs
References for feeding juvenile niche requirements: 020 , 021 , 022 , 023 , 028 , 031
Elevation specified in comments(00240)
General habitat association specified in comments(00270)
Successional stage: abandoned field
Shrubs
Hedgerows
Fencerows: shrubby fencerows
References for resting juvenile niche requirements: 020 , 021 , 022 , 023 , 028 , 031
Other niche requirements specified in comments(99999)
Elevation specified in comments(00240)
General habitat association specified in comments(00270)
Edge: woodland/old field edge
Edge: woodland/grassland edge
Edge: grassland/old field edge
Successional stage: abandoned field
Successional stage: stable prairie/grassland
Height of nest trees specified in comments(00580)
Shrubs: multiflora rose
Shrubs
Height of herbaceous vegetation specified in comments(00630)
Hedgerows
Windbreaks
Fencerows: shrubby fencerows
Fencerows: wooded fencerows
Human association: residential lawn/ornamental trees/shrubs
References for feeding Adult niche requirements: 020 , 021 , 022 , 023 , 028 , 031 , 035 , 041 , 042 , 044 , 045 , 046 , 049 , 052
Other niche requirements specified in comments(99999)
Floodplain wetlands: remnant wetlands
Floodplain wetlands: farmed temporary
Elevation specified in comments(00240)
General habitat association specified in comments(00270)
Edge: woodland/old field edge
Edge: woodland/grassland edge
Edge: grassland/old field edge
Successional stage: abandoned field
Successional stage: stable prairie/grassland
Successional stage specified in comments(00370)
Snags
Shrubs
Height of herbaceous vegetation specified in comments(00630)
Agricultural crops: small grains
Agricultural crops: hay
Agricultural crops specified in comments(00670)
Hedgerows
Fencerows: shrubby fencerows
Human association: residential lawn/ornamental trees/shrubs
References for feeding adult niche requirements: 020 , 021 , 022 , 023 , 028 , 031 , 034 , 044 , 045 , 053 , 054
Other niche requirements specified in comments(99999)
Floodplain wetlands: remnant wetlands
Floodplain wetlands: farmed temporary
Elevation specified in comments(00240)
General habitat association specified in comments(00270)
Edge: woodland/old field edge
Edge: woodland/grassland edge
Edge: grassland/old field edge
Successional stage: abandoned field
Successional stage: stable prairie/grassland
Successional stage specified in comments(00370)
Snags
Shrubs
Height of herbaceous vegetation specified in comments(00630)
Agricultural crops: small grains
Agricultural crops: hay
Agricultural crops specified in comments(00670)
Hedgerows
Fencerows: shrubby fencerows
Human association: residential lawn/ornamental trees/shrubs
References for resting adult niche requirements: 020 , 021 , 022 , 023 , 028 , 031
Agricultural crops specified in comments(00670)
Agricultural crops: hay
Agricultural crops: small grains
Edge: grassland/old field edge
Edge: woodland/grassland edge
Edge: woodland/old field edge
Elevation specified in comments(00240)
Fencerows: shrubby fencerows
Fencerows: wooded fencerows
Floodplain wetlands: farmed temporary
Floodplain wetlands: remnant wetlands
General habitat association specified in comments(00270)
Hedgerows
Height of herbaceous vegetation specified in comments(00630)
Height of nest trees specified in comments(00580)
Human association: residential lawn/ornamental trees/shrubs
Other niche requirements specified in comments(99999)
Shrubs
Shrubs: multiflora rose
Snags
Successional stage specified in comments(00370)
Successional stage: abandoned field
Successional stage: stable prairie/grassland
Windbreaks
Code | Comment |
---|---|
005 | Perch on snags to spot prey *34*. Have developed impaling behavior where prey are impaled, dismembered, and fed to nestlings. Honey locust, osage orange, and barbed wire fences are used as impaling substrate. Prey are impaled 24.5m from nest or directly on nesting tree which acts as food storage. *056*. |
011 | Nest in dense bushes or small trees *32* |
022 | Mature at 1 year *21* |
007 | Nest March-May *27*. In MO, males arrive in mid-February and establish territories, peak nest initiation in late April *31* |
013 | Return to nest in same tree or clump of trees, sometimes to same limb, for up to 6 years *32*. In a MO study, 47% of banded males returned to the same territory, none of the banded females returned *31*. A ND study found low site fidelity in females. Females may switch mates during breeding season, or re-use nests of shrikes or other birds during a single breeding season. *38* |
014 | Nest height 5-30', usually 8-15' *21,27*, average 2.03 m *20*, in MO study, average 3.2 m, nests higher in deciduous trees, red cedars, isolated nests, and 2nd nests *31* |
017 | Incubation 16 days *20,21,28*, average 17 days, range 16-20 days in a MO study *31* |
018 | Clutch size 4-8, usually 4-5 *21,28*, 3-7, usually 5-6 *31,39* |
021 | Both parents care for young till fledging, then male cares for young for another 3-4 weeks *31* |
027 | Territory size 18.7 acres *21*. In a MO study, territories average 4.6 ha, were larger during incubating stage than during nestling stage, also, size positively correlated with % of rowcrops in territory, and negatively correlated with % of grasslands *31* |
019 | 18.4% of successful nesters attempted a second nest in a MO study *31* |
031 | Nestling mortality 44.1% *20* |
033 | Migrate in daytime, individually rather than in flocks. Birds which wintered on MO study area didn't nest there. Migration may indirectly be a response to the degree of snow cover. Late date of fall departure from MO November 15, early date of spring arrival March 11. Banding evidence indicates that winter population and breeding population are completely separate. *31* |
034 | Causes of decline: persecution, pesticides, and loss of habitat *31* |
099 | Impale prey on thorns, barbed wire, or in fork of branch *21,22,29,31,32*. Young fledge at 16-20 days *20,21*, 17-21 days, averaged 19.1 days.*31* after fledging, remain in nest tree 2-3 days, remain dependant on parents for 3-4 weeks post-fledging *31*. Become proficient at catching insects at about 37 days *33*. In a MO study, nest success 93.8 in deciduous trees, 42.9 in multiflora rose, and 62.5 in eastern red cedar. Hatching success averaged 85.3%, and fledging success averaged 59.4%. *31*. Nest failures due to predation, weather *31,20*, abandonment, and disturbance *31*. Are persistant renesters if clutch is destroyed *31*. Nests usually at least 400 m apart *20*. Perches include powerlines, fences, trees, snags, shrubs. Use of high perches increases from winter to summer *35*. A MN study found 76% hatching success, 73% nest success. Is a host to the brown-headed cowbird *059*. |
Territory size specified in comments(027)
Periodicity: active in day
Periodicity: active at dawn or dusk
Mortality rate specified in comments(031)
Migration patterns specified in comments(033)
Limiting factors specified in comments(034)
Other life history information specified in comments(099)
Origin in state: native
Seasonal distribution in state: all seasons
Foraging strategy: hovering
Foraging strategy: hawking
Foraging sites: ground
Foraging sites: air
Foraging sites: snags
Foraging sites specified in comments(005)
Breeding season specified in comments(007)
Mating system: monogamy
Display site: air
Nest/den site: shrubs
Nest/den site: trees
Nest/den site specified in comments(011)
Nest/den/spawning site tenacity specified in comments(013)
Nest height specified in comments(014)
Nest materials: grasses
Nest materials: forbs
Nest materials: twigs
Nest materials: sticks
Nest materials: vegetative down
Nest materials: bark
Nest materials: hair or feathers
Gestation/incubation period specified in comments(017)
Clutch/litter size specified in comments(018)
Number of broods/litter per year: one
Number of broods/litter per year: two
Number of broods/litters per year specified in comments(019)
Development of young at birth/hatching: altricial
Parental care of young: both parents
Parental care of young specified in comments(021)
Age at sexual maturity specified in comments(022)
Territoriality: defends entire breeding, feeding, and nesting territory
Code | Comment |
---|---|
005 | Perch on snags to spot prey *34*. Have developed impaling behavior where prey are impaled, dismembered, and fed to nestlings. Honey locust, osage orange, and barbed wire fences are used as impaling substrate. Prey are impaled 24.5m from nest or directly on nesting tree which acts as food storage. *056*. |
011 | Nest in dense bushes or small trees *32* |
022 | Mature at 1 year *21* |
007 | Nest March-May *27*. In MO, males arrive in mid-February and establish territories, peak nest initiation in late April *31* |
013 | Return to nest in same tree or clump of trees, sometimes to same limb, for up to 6 years *32*. In a MO study, 47% of banded males returned to the same territory, none of the banded females returned *31*. A ND study found low site fidelity in females. Females may switch mates during breeding season, or re-use nests of shrikes or other birds during a single breeding season. *38* |
014 | Nest height 5-30', usually 8-15' *21,27*, average 2.03 m *20*, in MO study, average 3.2 m, nests higher in deciduous trees, red cedars, isolated nests, and 2nd nests *31* |
017 | Incubation 16 days *20,21,28*, average 17 days, range 16-20 days in a MO study *31* |
018 | Clutch size 4-8, usually 4-5 *21,28*, 3-7, usually 5-6 *31,39* |
021 | Both parents care for young till fledging, then male cares for young for another 3-4 weeks *31* |
027 | Territory size 18.7 acres *21*. In a MO study, territories average 4.6 ha, were larger during incubating stage than during nestling stage, also, size positively correlated with % of rowcrops in territory, and negatively correlated with % of grasslands *31* |
019 | 18.4% of successful nesters attempted a second nest in a MO study *31* |
031 | Nestling mortality 44.1% *20* |
033 | Migrate in daytime, individually rather than in flocks. Birds which wintered on MO study area didn't nest there. Migration may indirectly be a response to the degree of snow cover. Late date of fall departure from MO November 15, early date of spring arrival March 11. Banding evidence indicates that winter population and breeding population are completely separate. *31* |
034 | Causes of decline: persecution, pesticides, and loss of habitat *31* |
099 | Impale prey on thorns, barbed wire, or in fork of branch *21,22,29,31,32*. Young fledge at 16-20 days *20,21*, 17-21 days, averaged 19.1 days.*31* after fledging, remain in nest tree 2-3 days, remain dependant on parents for 3-4 weeks post-fledging *31*. Become proficient at catching insects at about 37 days *33*. In a MO study, nest success 93.8 in deciduous trees, 42.9 in multiflora rose, and 62.5 in eastern red cedar. Hatching success averaged 85.3%, and fledging success averaged 59.4%. *31*. Nest failures due to predation, weather *31,20*, abandonment, and disturbance *31*. Are persistant renesters if clutch is destroyed *31*. Nests usually at least 400 m apart *20*. Perches include powerlines, fences, trees, snags, shrubs. Use of high perches increases from winter to summer *35*. A MN study found 76% hatching success, 73% nest success. Is a host to the brown-headed cowbird *059*. |
References for life history: 001 , 003 , 020 , 021 , 022 , 023 , 027 , 028 , 029 , 031 , 032 , 033 , 034 , 035 , 038 , 039 , 056 , 057
Shrub/brush - maintain riparian habitats
Shrub/brush - control grazing of domestic livestock
Shrub/brush - develop/maintain edge (ecotones)
Agricultural - maintain riparian habitats
Agricultural - control grazing by domestic livestock
Agricultural - prescribed/controlled burning
Agricultural - haying/mowing
Agricultural - maintain streamside vegetation
Agricultural - develop/maintain hedgerows
Agricultural - maintain woodlots
Agricultural - develop/maintain windbreaks
Agricultural - maintain fencerows
Forest - prescribed/controlled burning
Forest - develop/maintain edge (ecotones)
Grassland - maintain riparian habitats
Grassland - control grazing of domestic livestock
Grassland - prescribed/controlled burning
Grassland - develop/maintain edge (ecotones)
Grassland - haying/mowing
Beneficial Management References: 055 , 003 , 020 , 021 , 022 , 031 , 041
Shrub/brush - application of herbicides
Shrub/brush - application of pesticides
Shrub/brush - application of insecticides
Shrub/brush - maintain natural ecological ecological succession
Agricultural - application of herbicides
Agricultural - application of pesticides
Agricultural - application of insecticides
Grassland - application of herbicides
Grassland - application of pesticides
Grassland - application of insecticides
Grassland - maintain natural ecological ecological succession
Adverse Management References: 003 , 020 , 021 , 022 , 031
Comments on Management:
Should continue to monitor the breeding population *31*. Fencerows and thorny native vegetation should be encouraged. Nesting cover should be reestablished with plantings (not multiflora rose) in areas with abundant grassland *31*. Controlled grazing can be beneficial *20,21*. A SC study recommended providing territory-size (approximately 10-20 acres) mosaics of short grass and sparsely vegetated bare areas *45*. Preferred grass height has been debated, however. A canada study recommended increasing the prevalance of tall (greater than 20 cm) grass in areas with suitable breeding habitat *44*. In IL, abundance was positively correlated with the amount of ungrazed pasture and hay meadows and covercrops, and negatively correlated with the amount of harvested cropland and woodland *41*. In OH study, hunting success was not affected by mowing, though prey species taken were affected *47*. In FL, occurred in pine forest that was burned annually, disappeared from unburned plots within 5 years after fire was discontinued *55*.
References for Management Comments: 055 , 020 , 021 , 031 , 041 , 043 , 044 , 045
Reference Code | Citation |
---|---|
001 | Easterla, D.A., M.B. Robbins and R.A. Anderson. 1992. Annotated Check-List Of Missouri Birds. The Audubon Society Of Missouri. |
002 | American Ornithologists Union. 1957. Checklist Of North American Birds, 5th Ed. Lord Baltimore Press. Baltimore, Md. 691 Pp. |
003 | Unpb Wilson, Jim D. Mo Dept. Conserv. P.O. Box 180. Jefferson City, Mo 65102. (573)751-4115. |
004 | Unpb Rathert, J. Mo Dept. Of Conservation, 1110 S. College Ave., Columbia, Mo 65201. (573)-882-9880. |
005 | Birds Of Squaw Creek National Wildife Refuge. 1975. U.S. Fish And Wildlife Service. Rf-663560-2. |
006 | Birds Of The Bennett Spring State Park Area Field Checklist. Nature Interpretive Center Staff. |
007 | Duck Creek Bird Checklist. 1979. Missouri Dept. Of Conservation, Jefferson City, Mo. |
008 | Heye, P.L. 1975. A Preliminary List Of The Birds Of The Cape Girardeau, Missouri Area. S.E. Mo State Univ., Cape Girardeau, Mo. |
009 | Dierker, W.W. 1979. Birds Of The Hannibal, Missouri Area. Trans. Mo Acad. Sci. 13: 41-51. |
010 | Unpb Breeding Bird Survey(1975,1977,1978,1979). J.D. Wilson, Mo Dept Of Conservation, P.O. Box 180, Jefferson City, Mo 65102. (573)-751-4115. |
011 | Unpb Biang, L.P. (Personal Comm.). Rte. 2, Box 113 B. Norwood, Mo 65717. |
012 | Jones, D.M. 1976. Missouri Christmas Bird Count 1975. Bluebird 43(2):8-23. |
013 | Comfort, J. 1974. Missouri Christmas Bird Count 1973. Bluebird 41(1):9-15. |
014 | Heilbrun, L.H. 1978. 1977-1978 Christmas Bird Count. Amer. Birds 32(4):447-911. |
015 | Heilbrun, L.H. 1976. 1975-1976 Christmas Bird Count. Amer. Birds 30(2):182-633. |
016 | Cruickshank, A.D. 1965. Christmas Bird Count. Aud. Field Notes 19(2):85-340. |
017 | Cruickshank, A.D. 1963. Christmas Bird Count. Aud. Field Notes 17(2): 73-290. |
018 | Cruickshank, A.D. 1966. Christmas Bird Count. Aud. Field Notes 20(2):97-384. |
019 | Cruickshank, A.D. 1971. Christmas Bird Count. Amer. Birds 25(2):131-514. |
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