The Hudson Valley is a treasured landscape that has undergone tremendous change over the past century. This forum explores how science-based stewardship on private land can help protect and promote healthy forests and open spaces, now and for future generations.
Presentations explore threats our forests and natural areas face – from invasive species and climate change to deer overabundance – and actions that can be taken on a site-by-site basis to optimize conditions. A special focus will be given to the overlap between sport hunting and conservation communities, with a roundtable discussion on advancing common ground. Hosted April 12, 2014 at Cary Institute of Ecosystem Studies
Presentation Part IV by: Raymond Winchcombe, Wildlife Ecologist, Cary Institute of Ecosystem Studies
1. Impacts to Forests by Deer and the Use of Annual
Controlled Hunts to Mitigate those Impacts
www.pa.audubon.org/search/node/PA Deer
Ecosystem Forum Report
2. Take Home Message
• Deer overabundance leads to serious negative impacts
on forested ecosystems.
• These impacts affect the abundance, distribution and
diversity of plant & animal species.
• Over-browsing by deer threatens the survival &
perpetuation of our oak dominated forests.
• Loss of oaks & the mast they produce would be
devastating for a host of animal species & an economic
loss of timber resources.
• A hunting program focused on consistent female
removal can address the impacts of over-browsing by
deer.
5. Discussion Outline
• Life History of White-tailed Deer
•Impacts to Forest Ecosystems by Deer
•Cary Institute’s Deer Management Program
•Role of Hunters & Landowners in Managing Deer
7. • Most abundant large herbivore in the United States
• Can live a long time; 10+ years in the wild
• Exhibit a polygamous breeding system
• Potential for rapid population growth in the absence
of predators
• Humans are the most significant contemporary
predator in most areas
8. • Adult females usually have twins, triplets possible
• Yearlings usually have singles, twins possible
• Well nourished fawns can breed & produce a fawn
their first year
• Single male will breed with several females
Reproduction
9. Population growth experiment results:*
1928-34 6 deer grew to 222 in seven years
1975-80 10 deer grew to 212 in six years
* - George Reserve in southern Michigan inside a 1,146 acre fenced site
controlling for all sources of mortality.
10. Polygamous breeding system requires control efforts
be focused on females if population control is desired.
Contrary to early deer management efforts where
females were protected & herds allowed to expand.
Early Goals: restock ranges where deer were
extirpated due to market & subsistence hunting &
habitat destruction.
12. Ecological Impacts of Too Many Deer
• Over browsed habitats
• Reduced species diversity (Flora)
• Reduced species diversity (Fauna)
• Loss of forest structural diversity
• Loss of forested systems functionality
• Overall decline in deer health/disease transmission
16. Deer are Selective Browsers
• Select foods that are
nutritious and highly
palatable
• Selections based on food
availability (feeding
progresses from most
desirable to least desirable
species)
• Food abundance & species
diversity are dependent on
contemporary deer #’s &
historical deer densities
0
500
1000
1500
2000
2500
3000
3500
#Budsavailable
Mean Available Buds/Species - 1998-2013
0
2
4
6
8
10
12
14
16
%BudsBrowsed
Mean % Browsing on Index Species
Cary Institute - 1998-2013
17. Overbrowsing: Direct Effects
• Reduced species richness & abundance
• Altered species composition (loss of desired species)
• Reduced advanced regeneration of desirable species
(important timber & mast producing species)
19. Overbrowsing: Indirect Effects
• Proliferation of undesirable & browse resistant
species (Hay scented & NY fern, beech, striped maple)
• Can lead to a shift in balance between native &
introduced species (introduced species less palatable)
• Can change the direction of forest development
(competitive exclusion of desirable by undesirable species)
• Reduced abundance of forest dwelling animals (direct
competition for food [acorns], altered habitats)
21. Impacts of Structural Component Loss
Loss of shrub & mid-canopy layers & spatial
distribution of these layers:
• Songbirds: reduced species richness & abundance (loss of
feeding, nesting & escape cover).
• Reduced abundance & higher predation on small mammal
community; eventual decline in predators.
• Insect diversity is dependent on vegetation diversity
(feeding, egg deposition, larval development).
23. Structural/Habitat Loss
• Microclimate shift: increased
light, wind, temperature and lower humidity at the
forest floor (impacts germination & survival of some tree
species, snails, salamanders, frogs etc.)
• Higher survival of less desirable shade intolerant
species due to increased ambient light conditions
(Hay Scented Fern).
• Degraded or loss of habitat for deer (loss of wintering
areas, escape cover, food resources).
25. Deer Population Management Options
1. Allow nature to take its course
2. Trap & transfer excess deer
3. Use fertility control agents to regulate herd size
4. Reintroduce predators to control deer numbers
5. Control deer numbers with sharpshooters
6. Use regulated hunting
26. Program Goals
Protect the structure & function of
forested ecosystems.
Minimize conflicts with planned uses of
the property.
Cary Deer Management Program
27. Program Elements
• Vegetation monitoring - via surveys
• Population index - hunter observations
• Population control - annual hunts
Cary Deer Management Program
28. Vegetation Monitoring
• 45 Deer browse survey areas (spring)
• 4 deer exclosures with paired unfenced plots
Cary Deer Management Program
29. 0
2
4
6
8
10
12
14
16
18
97 98 99 00 01 02 03 04 05 06 07 08 09 10 11 12 13 AVG
%Browsed
Year
Percent Buds Browsed for All Species
Cary Institute 1997 - 2013
Mean
Cary Browse Survey Results – 1997 - 2013
37. Population Control - Annual Reductions
Specific Goals
• Stabilize or reduce local deer numbers
• Achieve younger female age distribution
• Efficient and safe control effort
Cary Deer Management Program
38. Population Control via Controlled Access Hunt
• Participation by invitation
• Firearms proficiency requirement
• Orientation meeting requirement
• Antlerless permit requirement
• Effort requirement
Cary Deer Management Program
40. Cary Deer Management Program
Population Control - Hunt Specifics
Daily sign in/out at check station
Required deer check
Blaze orange requirement
Designated parking areas
Avoid research & restricted areas
47. Cary Deer Management Program
Population Control - Hunt Specifics
Daily sign in/out at check station
Required deer check
Blaze orange requirement
Designated parking areas
Avoid research & restricted areas
55. Landowner’s Role in Deer Management
1. Control access to the resource
2. Should take a pro-active stance in deer mgmt.
3. Can customize programs/access as needed
4. Require doe harvest for access privileges
5. Require sincere hunter effort for access privileges
6. Don’t tolerate irresponsible behavior
56. The Role of Hunters in Deer Population
Management
57. Role of Hunters in Deer Management
The primary role of hunters in deer population
management is the removal of deer.
Hunters are the tool deer managers use to control
deer numbers.
To maximize their effectiveness, hunters must
focus their efforts on adult females.
Hunters provide important ecosystem level
services to the community when adequate female
harvests are achieved.
58. Hunter Responsibilities
1. Safety, safety, safety
2. Respect- for property & all persons
3. Exhibit the highest of ethical standards
4. Zero tolerance for unsafe & unethical behavior
5. Never forget, access is a privilege
6. Embrace their role as deer managers when making
decisions regarding which deer to harvest.
60. Challenges for Deer Managers
1. Adequate access at the landscape scale?
2. Sufficient numbers of antlerless permits?
3. Sufficient hunter effort ( #’s of hunters)
4. Focused hunter harvest (adult females)
5. Providing a quality hunting experience ?
61. Is There a Recreational Threshold?
Is there a deer density at which many hunters do not see
enough deer to justify continuing to hunt? (Moyer and
Shissler).
Basis for a Recreational Threshold – expectations based on
past experience
Problem: Oscillations in deer #’s based on hunter interest
would not be good when the management objective is
forest ecosystem /habitat protection .
Challenges for Deer Managers
62. Result When the Need to See more Deer Trumps Habitat Protection
64. Primary Question
Are these oak dominated forests positioned to perpetuate
themselves under these different deer management scenarios?
65. 1976 – 2013 Summary Stats, Firearms
284 Different Hunters Participated
15,746 Hunter Visits
67,030 Hours of Hunting Effort
2,078 Deer Harvested (171 additional deer with archery)
2,249 Total Hunter Harvest (mean 58/yr.)
66.
67. Linking hunters and landowners
P.G.C. must attempt to match the general population, who are
the owners of public and private land, with those who hunt in a
way that is beneficial to both and mutually agreeable. This is
likely to depend on the willingness of P.G.C. to:
• enforce trespass laws on private land
• surrender the traditional value of equitable distribution (the
concept that all hunters should harvest an equal number of
animals)
• adopt more liberal season and bag limits that would allow
hunters to be effective in resolving landowners’ problems with
deer overbrowsing
Cited from the PA Audubon Deer Ecosystem Forum Report
68. IES Deer Exclosure Study
Ray Winchcombe & Charles Canham
• Central Dutchess County
• 3 Locations
• 4 sites/location
• 2 plots/site (fenced & unfenced 10x10 M plots)
• 1992 - present
69. Deer Management Scenario's
• Unhunted property – 1,000 acres; primarily forested
habitat (borders 900 acres of hunted forest lands).
• Gun club property – 1,500 acres; mix of
forest, cultivated field & old field habitat. Several
decades of deer hunting; inconsistent doe harvest
policy. Focus is on recreation and hunter satisfaction
• Cary Institute – 2,000 acres; mix of forest, old field &
open field habitats. Over three decades of deer
population management via controlled access
hunting; consistent doe harvests. Focus is on
protecting the structure & function of the forested
ecosystem.
72. Response to Primary Question
Unhunted site: data suggests this oak forest will not be able to perpetuate itself.
Complete lack of any advanced regeneration.
73. Response to Primary Question
Cary Inst.: data suggests this oak forest will perpetuate itself. Presence
of seedlings in the various height classes bodes well for this forest.
Focused deer management must continue.
74.
75.
76.
77. Consequences of Deer Over Abundance
• Severe overbrowsing of forested habitats
•Altered plant species composition, distribution &
abundance
• Reduction of understory structural diversity
• Reduced habitat quality (deer & other fauna)
78. When overly abundant, deer can have serious
negative effects on forest communities
• Mechanism – consumption of vegetation
• These effects can be either direct (species loss) or
indirect (shifts in species composition).
• Overbrowsing alters the physical structure of forests
thus having a negative impact on a host of other animal
species (vertebrate & invertebrate).
• High deer densities & overbrowsing combine to
threaten the future existence of our forests as we know
them today.
79. Consequences of Deer Overabundance
• Long-term reduction in BCC (deteriorated winter habitat)
• Decline in herd health (disease transmission, losses)
• Conflicts with CCC (acceptable limits that people will endure)
• Increased frequency of deer/vehicle encounters
• Excessive damage to agricultural, nursery &
landscape plantings & timber production.