1
State Wildlife Grants (SWG) were created with the intent of protecting and managing wildlife species in greatest conservation need. With 80 percent of the Mississippi Alluvial Valley (MAV) original forest cover lost, breeding birds of the MAV warrant our conservation efforts. Louisiana Wildlife and Fisheries commissioned Breeding Bird Surveys (BBS) on the state’s wildlife management areas to look at how forest management techniques in the MAV impact bird populations. At Boeuf Wildlife Management Area (WMA) species richness and diversity were compared across treatments. A list of confirmed breeding birds on the WMA is being generated as well as a checklist of all avian species encountered to include those detected outside the constraints of the BBS. Boeuf WMA is 51,000 + acres of bottomland hardwoods and wetland habitat in northeast Louisiana. The land is owned by the Louisiana Department of Wildlife and Fisheries. Point count locations were randomly selected using a map of Boeuf WMA, projected with ArcView software. Locations were chosen for comparisons of different silvicultural practices. Accessibility and spatial concerns were considered. Multiple point counts (Hamel et al. 1996) were conducted within each compartment on the WMA. Each point count was sampled approximately once monthly during April, May, and June. Point counts were conducted between 0.5 hours before sunrise and 3.0 hours after sunrise. Point counts were not conducted during periods of high wind or rain. All birds seen or heard within 100m of the observer were recorded. Distances from the observer to all birds detected were broken down between three categories; less then 25m, 25m to 50m, and greater then 50m. Each count was conducted for 10 minutes. The point count was subdivided into three intervals: 1-3 min, 2-5 min, and 5-10 min. Literature shows that a diversity of habitats is most beneficial to the avian community and the environment as a whole. Future management should seek to find a sustainable balance between conservation and preservation when making decisions concerning bottomland hardwoods and the Mississippi Alluvial Valley (MAV). At Boeuf Wildlife Management Area (WMA), further monitoring is necessary to determine reasons for low numbers of HOWA, KEWA, WOTH, and EAPW. Low abundance may be due to the factors within the WMA, but may also be part of the larger trend in the declining population of neo-tropical migrants throughout the MAV. A greater understanding of the dynamics of new plantations will also improve the success of future forest regeneration efforts. Protecting and managing wildlife species of greatest conservation need will become more necessary as natural habitats are pressured by the expansion of agriculture and exurban areas. Boeuf WMA hosts a diverse range of habitats and is a valuable refuge in which to protect threatened species in the Mississippi Alluvial Valley. Avian response to silviculture practices in the Mississippi Alluvial Valley: A breeding bird survey of Boeuf Wildlife Management Area JOHN QUINN and KIM MARIE TOLSON, Department of Biology, University of Louisiana at Monroe To effectively manage southern forests in the Mississippi Alluvial Valley, a thorough understanding of the impacts of various silviculture techniques is needed. Wilson et al. (1996) have identified the need to survey biological resources as the first step in developing effective management strategies. The first step in a biological resource survey is an estimation of diversity at one time and location. For this study, we are looking to estimate the total number of breeding species in each community within the WMA. We will examine the difference between managed and unmanaged forests and how age and structure of a plantation influences the avian population. To increase use of Boeuf WMA by the A complete species list and a copy of the poster can be found at: http://www.ulm.edu/~tolson/johnqiv.htm Unmanaged Introduction Methods Aim Results Conclusion Further Information Acknowledgements We thank Elbert Rachal for advice and helpful discussions, Buddy Dupris, David Breithaupt, Tommy Tuma, and Fred Hagaman for field data about Boeuf WMA. Funding for this project was provided by the LDWF & USFWS, Division of Federal Aid through the State Wildlife Grants Program. Photos by Mike Baranski T15 Managed Timber Cut/Individual Managed Timber T12 Unmanaged T13 Unmanaged/Tornado T16 Unmanaged/ Greentree T17 Unmanaged T21 Unmanaged T22 Unmanaged T25 Unmanaged T31 Unmanaged/Flooded T06 Managed Timber Cut/Group T06B Managed Timber Cut/Group Speciesrichnesspertransect T36 T63 T32 T37 T38 T01 T33 T05 T06b T18 T31 T13 T09 T12 T21 T25 t06 T17 T22 T07 T15 T10 0 5 10 15 20 25 Works Cited Hamel, P.B., W.P. Smith, D.J. Twedt, J.R. Woehr, E. Morris, R.B. Hamilton, and R.J. Cooper. 1996. A land manger’s guide to point counts of birds in the southeast. U.S.D.A Forest Service, Report SO-120 Wilson, D.E., F.R. Cole, J.D. Nichols, R. Rudran, M.S. Foster 1996. Measuring and Monitoring Biological Diversity. Smithsonian Institution Press A total of 198 point counts were conducted on 22 transects in plantations, managed and unmanaged forests. A total of 38 species were counted during the 2005 BBS T01 Replantation High/Low T32 Replantation/Moist Soil/WRP T33 Replantation High/Low T36 Replantation High/Low T37 Replantation WRP T38 Replantation WRP T63 Replantation High/Low T05 Natural Area/Flooded T07 Natural Area Description of Transects Managed Reforested BBS abundance per species BAOR, RTHB, GRCB, WOTH, BLJA, EAPW , EATO , HOWA, KEW A, G C F L,1 COYT,1 OROR, R H W P ,1 N O B W ,1 YTVI,1 D O W P ,2 R EVI,2 PABU,3 B G G N ,3 BHCB,3 NOPA,4 PIW P,4 SUTA,4 YBCH,4 ACFL,4 EAM L,5 P R O W ,7 IN BU ,8 YBCU,8 W IVI,9 TUTM,9 R BW P,9 D IC K , 10 CACH,17 N O C L,21 HAWP, MODO, C A W R ,14 Reforested Species Richness S = 23 Simpson's Index (D) D = 0.113 Simpson's Index of Diversity 1-D = 0.887 Shannon's Index (H‘) H'= 3.629 Simpson's Evenness 1/D E = 0.377 Managed Species Richness S = 29 Simpson's Index (D) D = 0.074 Simpson's Index of Diversity 1-D = 0.926 Shannon's Index (H‘) H'= 4.163 Simpson's Evenness 1/D E = 0.451 Unmanaged Species Richness S = 32 Simpson's Index (D) D = 0.067 Simpson's Index of Diversity 1-D = 0.933 Shannon's Index (H‘) H'= 4.243 Simpson's Evenness 1/D E = 0.463 Percent Similarity of Relative Abundance Unmanaged Reforested Managed 83.42 31.25 Reforested 34.43

State Wildlife Grants (SWG) were created with the intent of protecting and managing wildlife species in greatest conservation need. With 80 percent of

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Page 1: State Wildlife Grants (SWG) were created with the intent of protecting and managing wildlife species in greatest conservation need. With 80 percent of

State Wildlife Grants (SWG) were created with the intent of protecting and managing wildlife species in greatest conservation need. With 80 percent of the Mississippi Alluvial Valley (MAV) original forest cover lost, breeding birds of the MAV warrant our conservation efforts. Louisiana Wildlife and Fisheries commissioned Breeding Bird Surveys (BBS) on the state’s wildlife management areas to look at how forest management techniques in the MAV impact bird populations. At Boeuf Wildlife Management Area (WMA) species richness and diversity were compared across treatments. A list of confirmed breeding birds on the WMA is being generated as well as a checklist of all avian species encountered to include those detected outside the constraints of the BBS.

Boeuf WMA is 51,000 + acres of bottomland hardwoods and wetland habitat in northeast Louisiana. The land is owned by the Louisiana Department of Wildlife and Fisheries.

Point count locations were randomly selected using a map of Boeuf WMA, projected with ArcView software. Locations were chosen for comparisons of different silvicultural practices. Accessibility and spatial concerns were considered.

Multiple point counts (Hamel et al. 1996) were conducted within each compartment on the WMA. Each point count was sampled approximately once monthly during April, May, and June. Point counts were conducted between 0.5 hours before sunrise and 3.0 hours after sunrise. Point counts were not conducted during periods of high wind or rain.

All birds seen or heard within 100m of the observer were recorded. Distances from the observer to all birds detected were broken down between three categories; less then 25m, 25m to 50m, and greater then 50m.

Each count was conducted for 10 minutes. The point count was subdivided into three intervals: 1-3 min, 2-5 min, and 5-10 min.

Literature shows that a diversity of habitats is most beneficial to the avian community and the environment as a whole. Future management should seek to find a sustainable balance between conservation and preservation when making decisions concerning bottomland hardwoods and the Mississippi Alluvial Valley (MAV).

At Boeuf Wildlife Management Area (WMA), further monitoring is necessary to determine reasons for low numbers of HOWA, KEWA, WOTH, and EAPW. Low abundance may be due to the factors within the WMA, but may also be part of the larger trend in the declining population of neo-tropical migrants throughout the MAV. A greater understanding of the dynamics of new plantations will also improve the success of future forest regeneration efforts.

Protecting and managing wildlife species of greatest conservation need will become more necessary as natural habitats are pressured by the expansion of agriculture and exurban areas. Boeuf WMA hosts a diverse range of habitats and is a valuable refuge in which to protect threatened species in the Mississippi Alluvial Valley.

Avian response to silviculture practices in the Mississippi Alluvial Valley:

A breeding bird survey of Boeuf Wildlife Management AreaJOHN QUINN and KIM MARIE TOLSON,

Department of Biology, University of Louisiana at Monroe

To effectively manage southern forests in the Mississippi Alluvial Valley, a thorough understanding of the impacts of various silviculture techniques is needed. Wilson et al. (1996) have identified the need to survey biological resources as the first step in developing effective management strategies. The first step in a biological resource survey is an estimation of diversity at one time and location.

For this study, we are looking to estimate the total number of breeding species in each community within the WMA. We will examine the difference between managed and unmanaged forests and how age and structure of a plantation influences the avian population.

To increase use of Boeuf WMA by the general public and the birding community, we will develop an avian species list for the WMA, providing the community and birders with species present.

A complete species list and a copy of the poster can be found at:http://www.ulm.edu/~tolson/johnqiv.htm

Unmanaged

Introduction Methods

Aim

Results Conclusion

Further Information

AcknowledgementsWe thank Elbert Rachal for advice and helpful discussions, Buddy Dupris, David Breithaupt, Tommy Tuma, and Fred Hagaman for field data about Boeuf WMA. Funding for this project was provided by the LDWF & USFWS, Division of Federal Aid through the State Wildlife Grants Program. Photos by Mike Baranski

T09Managed Timber Cut/Individual

T15Managed Timber Cut/Individual

T18Managed Timber Cut/Individual

T10 Unmanaged

T12 Unmanaged

T13Unmanaged/Tornado

T16Unmanaged/Greentree

T17 Unmanaged

T21 Unmanaged

T22 Unmanaged

T25 Unmanaged

T31Unmanaged/Flooded

T06Managed Timber Cut/Group

T06BManaged Timber Cut/Group

Species richness per transect

T36T63

T32T37 T38

T01 T33T05

T06b T18 T31T13

T09 T12 T21 T25t06 T17 T22

T07 T15 T10

0

5

10

15

20

25

Works Cited

Hamel, P.B., W.P. Smith, D.J. Twedt, J.R. Woehr, E. Morris, R.B. Hamilton, and R.J. Cooper. 1996. A land manger’s guide to point counts of birds in the southeast. U.S.D.A Forest Service, Report SO-120Wilson, D.E., F.R. Cole, J.D. Nichols, R. Rudran, M.S. Foster 1996. Measuring and Monitoring Biological Diversity. Smithsonian Institution Press

A total of 198 point counts were conducted on 22 transects in

plantations, managed and unmanaged forests. A total of 38

species were counted during the 2005 BBS season. Total species

richness for the management area currently stands at 171 species.

T01 Replantation High/Low

T32Replantation/Moist Soil/WRP

T33 Replantation High/Low

T36 Replantation High/Low

T37 Replantation WRP

T38 Replantation WRP

T63 Replantation High/Low

T05Natural Area/Flooded

T07 Natural Area

Description of TransectsManaged Reforested

BBS abundance per species

BA

OR

, 3

RT

HB

, 3

GR

CB

, 5

WO

TH

, 5

BLJA

, 6

EA

PW

, 6

EA

TO

, 6

HO

WA

, 7

KE

WA

, 8

GC

FL, 10

CO

YT

, 14

OR

OR

, 14

RH

WP

, 14

NO

BW

, 17

YT

VI, 1

9

DO

WP

, 25

RE

VI, 2

7

PA

BU

, 35

BG

GN

, 36

BH

CB

, 37

NO

PA

, 41

PIW

P, 41

SU

TA

, 43

YB

CH

, 46

AC

FL, 48

EA

ML, 57

PR

OW

, 73

INB

U, 81

YB

CU

, 86

WIV

I, 9

2

TU

TM

, 95

RB

WP

, 97

DIC

K, 101

CA

CH

, 172

NO

CL, 217

HA

WP

, 5

MO

DO

, 12

CA

WR

, 141

Reforested

Species Richness S = 23

Simpson's Index (D) D = 0.113

Simpson's Index of Diversity 1-D = 0.887

Shannon's Index (H‘) H'= 3.629

Simpson's Evenness 1/D E = 0.377

Managed

Species Richness S = 29

Simpson's Index (D) D = 0.074

Simpson's Index of Diversity 1-D = 0.926

Shannon's Index (H‘) H'= 4.163

Simpson's Evenness 1/D E = 0.451

Unmanaged

Species Richness S = 32

Simpson's Index (D) D = 0.067

Simpson's Index of Diversity 1-D = 0.933

Shannon's Index (H‘) H'= 4.243

Simpson's Evenness 1/D E = 0.463

Percent Similarity of Relative AbundanceUnmanaged Reforested

Managed 83.42 31.25

Reforested 34.43