FNR24150 -- Week 16 Notes
Biodiversity crisis
Loss and reduction in diversity at all levels (genetics → ecosystems)
Primarily focus on single spp. conservation due to lack of resources for anything much bigger (e.g. habitat/environment)
Extinction
Rate has greatly exceeded the “normal” historical rates
Could lead to cascading extinction events
The loss of one spp. causes the loss of multiple
World-wide amphibian declines
1,260 of 6,000 spp. (21%) are endangered
1,856 of 6,000 spp. (32%) are threatened
2,469 spp. are in decline (43%)
World-wide reptile declines
Reptiles not completely assessed (mostly Chelonians)
Best estimate 833 of 6,500 spp. (13%) endangered
Turtles and tortoises well reviewed
108 of 257 spp. (42%) threatened
Humans have modified the environment everywhere through
Habitat modification, fragmentation, loss
Most visible human mediated environmental change
Agriculture
Urban growth and paving
Overall consequences:
Habitat alteration and fragmentation (dispersal barriers)
Increased mortality due to road kills
Loss of breeding, foraging, & over-winter areas
Population declines and extinction in some cases
Road mortality
Skewed sex ratios in turtle populations
Predicted higher sex ratio skew in high road density
Road mortality of females on nesting migrations
Historical male-biased sex ratio?
Proportion of males increased linearly
Synchronized with increase in paced roads
Indiana Road Mortality
Surveyed Lindberg Road for 1.5 years
Vertebrate road mortality N=8,176
Herps represented n=8, 016
Miles of paved roads in Indiana ~93,600
Harvest
Mostly for commercial exploitation
Consumption (food and folk medicines)
Luxury trade (leathers, jewelry)
Pet Trade
Focused on a relatively few spp. in any locality (developing countries)
Sustainable harvest by small communities can also decimate populations
Examples
Consumption: larger, long-lived spp. (Chelonians, specifically the Apalone and also Varanus lizards)
1990’s Europe imported 6,000 tons of frog legs/year
India and Indonesia exported 50 million frogs/year
Banned exports in 1987 and 1992
Depleted natural insecticide from paddy fields
Luxury Trade: American Caimans → leather
Pet Trade: Box turtle declines in 16 states (~30,000 box turtles since 1995)
High prices for rare and brightly colored spp.
Introduction of exotic spp.
Exotic spp.: Introduced/non-native
Black and Norway Rats → great impact on islands (lizards, tuataras, tortoises)
Domestic cats → widespread damage in suburban and rural areas
Herbivores (goats, rabbits) → change vegetation
American Bullfrog
Game spp. (frog legs)
large
High mobility
Live 7-9 years
Huge reproductive potential
Generalized feeding habits
Snakes, worms, crustaceans, insects--anything that fits in its mouth
California: bullfrogs reduced leopard frog survivorship by 33%
Arizona: bullfrogs responsible for leopard frog declines (79 out of 80 sites now extirpated; 79 sites completely devoid of leopard frogs)
Management Tools
Establishment of refuges and corridors
Main objective: prevent extinction
Key issue: How much area to preserve?
Location, size, and shape of refuges and corridors is dependent on:
Whether spp., communities, and/or ecosystems are targeted for conservation
Natural history characteristics of the above
Minimum Viable Population (MVP)
Minimum area required for a population or spp. to survive
Studies of terrestrial buffer zones with freshwater turtles
Savannah River Ecology Laboratory (SREL)
Do protected acreage of wetlands protect areas critical for nesting and hibernating?
No, they do not
Management of animals in captivity
Animals can be managed in captivity for:
Short periods (temporary)
“Headstart” (from hatchling to 6-12 months)
Hatcheries (egg incubation)
Long periods
Duration of an individual’s life
Sometimes several generations
Crocodilian farming and ranching
Reintroductions of wild spp.
Intentional release of individuals to establish or enlarge the population of a target spp.
Target spp. usually threatened or endangered
Some problems
Generally very few of the animals that are re-introduced survive
Introduction of diseases into healthy populations
Outbreeding depression
Pollution
Diseases
Phase 1
Health & Genetics
Sampled 10 states, 70 rivers, and 1200 samples
Blood draws for health screens and DNA samples
Two large clusters
Ohio River Drainage (Indiana, Ohio, West Virginia, Pennsylvania)
Tennessee River Drainage (Georgia, Tennessee, North Carolina, Virginia)
i.e. Hellbenders in Indiana are genetically similar to those in Ohio
Sampling
Population Assessment
Understand how many Hellbenders you have
88 in Dr. Williams’ case
Density
0.06/100m^2
Spatial Ecology
Health (blood work, sperm, weight class, etc.)
Habitat & Home Ranges (radio transmitters and radio telemetry)
Hellbenders are very rare; distributed randomly across the landscape with very little interaction between other Hellbenders
Survival
Annual Hellbender survival if no action is taken: 0.804
Phase 2
Population Manipulation
Recovery Strategies
Population Viability Analyses
Captive rearing and release
Translocations
Intra-river translocation
10 native adults & 10 translocated adults
Captive relreases
10 native adults
10 captive juveniles
Spatial Ecology
Home range size nearly cut in half (2212 v. 1348 m^2)
Extensive HR overlap among individuals
Two egg clutches
Post-translocation
No impact on annual survivorship of adults (80% v. 78%)
50% juvenile survivrship had exceeded 30% threshold to prevent extinction :D
Outreach & Education
Mail survey
1378 Distributed
281 to Riparian Landowners
541 Completed (41%)
In-person survey
242 surveys conducted
6 access sites
Focus
Awareness, attitudes, behaviour
Approach
“3D Model” of O & E
Develop the portal
Design the content
Deliver the programs
Evaluate impact
HelpTheHellbender.org
Impact
Nationally
25 organizations (6 state/fed agencies, 8 zoos, 11 universities)
63% monthly
82% follow
81% recommend to others
Population Modeling
2011-2012, 33 Hellbenders
2018, 5 male Hellbenders
Must focus on juveniles
Increase juvenile survivorship → expected local extinction in 26 years goes up to 35
30-50% increase → almost completely reverse the probability of Hellbender extinction
Problems with heavy predation → low juvenile survivorship
Phase 3
Restoration
Captivity can deprive animals of experiences/natural stimuli
Predator cues
Stochastic events
Refuge
Live prey
Habitat variability
Advancing Headstarting
Introduce captive, juvenile Hellbenders to natural conditions to better prepare them for the wild
Investigate the effects of:
Moving water
Predator cues
Microbiome
90% survivorship in 200 days, then averages around 75%
Phase 4
Providing farmers federal grant money to implement conservation practices in watersheds
Research
Education/Outreach
Management
Captive breeding
Partnerships
A collaboration with many interested bodies
Semiannual meetings
Action Teams
Habitat
Outreach & Education
Captive Rearing/Breeding
Animal Health
Biodiversity crisis
Loss and reduction in diversity at all levels (genetics → ecosystems)
Primarily focus on single spp. conservation due to lack of resources for anything much bigger (e.g. habitat/environment)
Extinction
Rate has greatly exceeded the “normal” historical rates
Could lead to cascading extinction events
The loss of one spp. causes the loss of multiple
World-wide amphibian declines
1,260 of 6,000 spp. (21%) are endangered
1,856 of 6,000 spp. (32%) are threatened
2,469 spp. are in decline (43%)
World-wide reptile declines
Reptiles not completely assessed (mostly Chelonians)
Best estimate 833 of 6,500 spp. (13%) endangered
Turtles and tortoises well reviewed
108 of 257 spp. (42%) threatened
Humans have modified the environment everywhere through
Habitat modification, fragmentation, loss
Most visible human mediated environmental change
Agriculture
Urban growth and paving
Overall consequences:
Habitat alteration and fragmentation (dispersal barriers)
Increased mortality due to road kills
Loss of breeding, foraging, & over-winter areas
Population declines and extinction in some cases
Road mortality
Skewed sex ratios in turtle populations
Predicted higher sex ratio skew in high road density
Road mortality of females on nesting migrations
Historical male-biased sex ratio?
Proportion of males increased linearly
Synchronized with increase in paced roads
Indiana Road Mortality
Surveyed Lindberg Road for 1.5 years
Vertebrate road mortality N=8,176
Herps represented n=8, 016
Miles of paved roads in Indiana ~93,600
Harvest
Mostly for commercial exploitation
Consumption (food and folk medicines)
Luxury trade (leathers, jewelry)
Pet Trade
Focused on a relatively few spp. in any locality (developing countries)
Sustainable harvest by small communities can also decimate populations
Examples
Consumption: larger, long-lived spp. (Chelonians, specifically the Apalone and also Varanus lizards)
1990’s Europe imported 6,000 tons of frog legs/year
India and Indonesia exported 50 million frogs/year
Banned exports in 1987 and 1992
Depleted natural insecticide from paddy fields
Luxury Trade: American Caimans → leather
Pet Trade: Box turtle declines in 16 states (~30,000 box turtles since 1995)
High prices for rare and brightly colored spp.
Introduction of exotic spp.
Exotic spp.: Introduced/non-native
Black and Norway Rats → great impact on islands (lizards, tuataras, tortoises)
Domestic cats → widespread damage in suburban and rural areas
Herbivores (goats, rabbits) → change vegetation
American Bullfrog
Game spp. (frog legs)
large
High mobility
Live 7-9 years
Huge reproductive potential
Generalized feeding habits
Snakes, worms, crustaceans, insects--anything that fits in its mouth
California: bullfrogs reduced leopard frog survivorship by 33%
Arizona: bullfrogs responsible for leopard frog declines (79 out of 80 sites now extirpated; 79 sites completely devoid of leopard frogs)
Management Tools
Establishment of refuges and corridors
Main objective: prevent extinction
Key issue: How much area to preserve?
Location, size, and shape of refuges and corridors is dependent on:
Whether spp., communities, and/or ecosystems are targeted for conservation
Natural history characteristics of the above
Minimum Viable Population (MVP)
Minimum area required for a population or spp. to survive
Studies of terrestrial buffer zones with freshwater turtles
Savannah River Ecology Laboratory (SREL)
Do protected acreage of wetlands protect areas critical for nesting and hibernating?
No, they do not
Management of animals in captivity
Animals can be managed in captivity for:
Short periods (temporary)
“Headstart” (from hatchling to 6-12 months)
Hatcheries (egg incubation)
Long periods
Duration of an individual’s life
Sometimes several generations
Crocodilian farming and ranching
Reintroductions of wild spp.
Intentional release of individuals to establish or enlarge the population of a target spp.
Target spp. usually threatened or endangered
Some problems
Generally very few of the animals that are re-introduced survive
Introduction of diseases into healthy populations
Outbreeding depression
Pollution
Diseases
Phase 1
Health & Genetics
Sampled 10 states, 70 rivers, and 1200 samples
Blood draws for health screens and DNA samples
Two large clusters
Ohio River Drainage (Indiana, Ohio, West Virginia, Pennsylvania)
Tennessee River Drainage (Georgia, Tennessee, North Carolina, Virginia)
i.e. Hellbenders in Indiana are genetically similar to those in Ohio
Sampling
Population Assessment
Understand how many Hellbenders you have
88 in Dr. Williams’ case
Density
0.06/100m^2
Spatial Ecology
Health (blood work, sperm, weight class, etc.)
Habitat & Home Ranges (radio transmitters and radio telemetry)
Hellbenders are very rare; distributed randomly across the landscape with very little interaction between other Hellbenders
Survival
Annual Hellbender survival if no action is taken: 0.804
Phase 2
Population Manipulation
Recovery Strategies
Population Viability Analyses
Captive rearing and release
Translocations
Intra-river translocation
10 native adults & 10 translocated adults
Captive relreases
10 native adults
10 captive juveniles
Spatial Ecology
Home range size nearly cut in half (2212 v. 1348 m^2)
Extensive HR overlap among individuals
Two egg clutches
Post-translocation
No impact on annual survivorship of adults (80% v. 78%)
50% juvenile survivrship had exceeded 30% threshold to prevent extinction :D
Outreach & Education
Mail survey
1378 Distributed
281 to Riparian Landowners
541 Completed (41%)
In-person survey
242 surveys conducted
6 access sites
Focus
Awareness, attitudes, behaviour
Approach
“3D Model” of O & E
Develop the portal
Design the content
Deliver the programs
Evaluate impact
HelpTheHellbender.org
Impact
Nationally
25 organizations (6 state/fed agencies, 8 zoos, 11 universities)
63% monthly
82% follow
81% recommend to others
Population Modeling
2011-2012, 33 Hellbenders
2018, 5 male Hellbenders
Must focus on juveniles
Increase juvenile survivorship → expected local extinction in 26 years goes up to 35
30-50% increase → almost completely reverse the probability of Hellbender extinction
Problems with heavy predation → low juvenile survivorship
Phase 3
Restoration
Captivity can deprive animals of experiences/natural stimuli
Predator cues
Stochastic events
Refuge
Live prey
Habitat variability
Advancing Headstarting
Introduce captive, juvenile Hellbenders to natural conditions to better prepare them for the wild
Investigate the effects of:
Moving water
Predator cues
Microbiome
90% survivorship in 200 days, then averages around 75%
Phase 4
Providing farmers federal grant money to implement conservation practices in watersheds
Research
Education/Outreach
Management
Captive breeding
Partnerships
A collaboration with many interested bodies
Semiannual meetings
Action Teams
Habitat
Outreach & Education
Captive Rearing/Breeding
Animal Health