|
|
Stressors/Threats
|
Relevance to Species
|
HABITAT LOSS
|
|
breeding
|
unknown
|
dispersal
|
unknown
|
foraging
|
size of foraging area is unknown, but will forage over large distances; thought to prefer "edges" of habitat
|
wintering
|
winter roosts are generally caves or mines, threatened by closure
|
migratory stops
|
roosts are necessary for migrants
|
diurnal preferences - day, temporary
|
unknown and unlikely
|
diurnal preferences - day, long-term
|
caves and mines are extremely important
|
diurnal preferences - night
|
needed, includes bridges, buildings, drainage culverts?, and other unknown
|
fire threat
|
probably minor
|
HABITAT ALTERATION
|
|
prey
|
moths, 3-10 mm, Noctuidae; but includes other insects; loss of prey= loss of bats
|
nest sites
|
maternity roosts critically important
|
vegetation composition/density
|
important as source of prey; protect riparian and other edges
|
habitat conversion
|
unknown
|
escape cover
|
unknown
|
fragmentation
|
potentially does not matter, it lives in a fragmented landscape
|
invasive plant species
|
unknown, probably affects prey base
|
invasive animal species
|
unknown
|
habitat rehabilitaion potential
|
limited for roosts; conditions needed are generally unknown; gating roosts could be beneficial
|
HABITAT ALTERATION continued
|
contaminants
|
unknown; there is some indication that bats can acquire toxic materials in roosts, and considerable evidence that some species can acquire toxic doses of insecticides by consuming contaminated prey
|
nutrient enrichment
|
|
water accessibility
|
drinks from and forages over water; very small water sources are used, large water bodies have not been surveyed; could benefit by vegetation around water
|
drought
|
|
flood
|
|
groundwater depletion
|
|
root zone water loss
|
|
artificial water sources
|
drinks from and forages over water; very small water sources are used, large water bodies have not been surveyed; could benefit by vegetation around water
|
infiltration
|
|
runoff
|
|
edge effects
|
prefers foraging along edges
|
fire threat
|
may affect prey
|
water quality - turbidity
|
broadly tolerant of water quality
|
water quality - salinity
|
|
water quality - conductivity
|
|
water quality - dissolved oxygen
|
|
water quality - effluent
|
|
sheetflow disruption
|
|
flow rate
|
may prefer still or slow moving water
|
land use history
|
|
roads - dust
|
|
roads - erosion
|
|
roads - surface water diversion/ponding
|
may be beneficial
|
roads - asphalt/contaminants
|
unknown
|
SPECIES CHARACTERISTICS
|
|
dispersal mechanism
|
|
behavior traits
|
sensitive to disturbance at roosts
|
habitat rehabilitation potential
|
potential to increase prey base; could benefit by gating mines and caves; experiment with creating habitat?
|
colonization potential
|
|
effective population size
|
|
total population size
|
|
fecundity
|
1 young per year, fecundity is low as with most bats
|
knowledge/data on species
|
|
seasonal specialization
|
|
captive breeding/translocation potential
|
no success with moving from roosts
|
genetic isolation
|
|
inbreeding
|
very low variability suggests inbreeding or small gene pool
|
diurnal specialization
|
|
off-site mortality - migratory
|
no information is available
|
off-site mortality - from surrounding land uses
|
could be driven from areas by renewed mining, urban expansion, human disturbance
|
breadth of resource use
|
|
sensitivity to disturbance
|
highly sensitive; outreach to recreational cavers and mine explorers is needed
|
adaptability
|
not very adaptable to some changes, especially loss of roosts
|
charisma
|
mixed bag: bats have had a major change in public image in past two decades but some people still fear or hate; need to emphasize that they eat pest insects
|
INTERSPECIFIC FACTORS
|
|
predation
|
limited knowledge; may be subject to predation by cats but this is not likely
|
disease
|
rabies may affect; others unknown
|
pollinators/seed dispersers
|
|
competition
|
unknown; has been found in roosts with other species
|
INTERSPECIFIC FACTORS continued
|
brood parasitism
|
|
domestic/feral animals
|
may be preyed on by cats, but this is not likely
|
invasive species
|
|
ANTHROPOGENIC FACTORS
|
|
edge effect
|
edges are preferred foraging sites
|
disease
|
|
fire threat
|
|
off-road vehicles - dust
|
ORVs may be a problem because they get people to roost sites and result in disturbance
|
off-road vehicles - erosion
|
|
off-road vehicles - noise
|
|
mining
|
renewed mining in areas with old mines may result in disturbance or loss of roosts
|
passive recreation
|
disturbance of roosts; should route trails to avoid roosts
|
grazing - vegetation impacts
|
may affect prey base
|
grazing - soil impacts
|
|
collection/hunting
|
not thought to be a problem
|
herbicides
|
not thought to be a problem, except as they may affect prey base
|
insecticides
|
impacts have been reduced over time, but still may be a problem
|
pesticides - impacts to species
|
impacts have been reduced over time, but still may be a problem
|
pesticides - impacts to prey
|
this could be significant
|
direct take/mortality
|
little effect except from mine hazard abatement practices, which could be serious impacts; road paving and de-icing may affect
|
noise
|
unknown
|
light
|
bright lights near roosts may affect
|
movement
|
|
ANTHROPOGENIC FACTORS continued
|
landscaping
|
native plants could provide beneficial opportunities for habitat improvement
|
invasives
|
|
domestic/feral animals
|
|
dumping
|
may affect if in roost sites
|
undocumented immigrants
|
may affect when they use caves and mines for shelter or dumping grounds
|
increased road density
|
may be a problem, low-flying bats could get hit by cars while foraging along road edges
|
road kill
|
may be a problem, low-flying bats could get hit by cars while foraging along road edges
|
electrocution on powerlines/towers
|
|
CONNECTIVITY
|
|
fragmentation
|
|
barriers
|
large cities with abundant lights could be barriers
|
traffic volumes
|
increased volume could lead to increased road kill
|
wash incision
|
could create roost sites but could also take some away
|
corridor width
|
buffers along washes would be good but width unknown
|
habitat patchiness
|
depend on what is around them; patchiness could be good because it could increase insect diversity
|
riparian/upland connection
|
bridges could be improved as bat roosts
|
road crossings
|
could be opportunity for foraging or hazard due to roadkill
|
road width
|
|
vegetation next to roads
|
could be opportunity or hazard; recommend not planting edges along larger and faster roads, allow space between trees and roads
|
|
|
Stressors/Threats
|
Relevance to Species
|
HABITAT LOSS
|
foraging
|
size of foraging area is unknown, but will forage over large distances; thought to prefer "edges" of habitat
|
wintering
|
winter roosts are generally caves or mines, threatened by closure
|
migratory stops
|
roosts are necessary for migrants
|
diurnal preferences - day, temporary
|
unknown and unlikely
|
diurnal preferences - day, long-term
|
caves and mines are extremely important
|
diurnal preferences - night
|
needed, includes bridges, buildings, drainage culverts?, and other unknown
|
fire threat
|
probably minor
|
HABITAT ALTERATION
|
prey
|
moths, 3-10 mm, Noctuidae; but includes other insects; loss of prey= loss of bats
|
nest sites
|
maternity roosts critically important
|
vegetation composition/density
|
important as source of prey; protect riparian and other edges
|
fragmentation
|
potentially does not matter, it lives in a fragmented landscape
|
invasive plant species
|
unknown, probably affects prey base
|
habitat rehabilitaion potential
|
limited for roosts; conditions needed are generally unknown; gating roosts could be beneficial
|
contaminents
|
unknown; there is some indication that bats can acquire toxic materials in roosts, and considerable evidence that some species can acquire toxic doses of insecticides by consuming contaminated prey
|
water accessibility
|
drinks from and forages over water; very small water sources are used, large water bodies have not been surveyed; could benefit by vegetation around water
|
artifical water sources
|
drinks from and forages over water; very small water sources are used, large water bodies have not been surveyed; could benefit by vegetation around water
|
edge effects
|
prefers foraging along edges
|
fire threat
|
may affect prey
|
water quality - turbidity
|
broadly tolerant of water quality
|
flow rate
|
may prefer still or slow moving water
|
roads - surface water diversion/ponding
|
may be beneficial
|
SPECIES CHARACTERISTICS
|
behavior traits
|
sensitive to disturbance at roosts
|
habitat rehabiitation potential
|
potential to increase prey base; could benefit by gating mines and caves; experiment with creating habitat?
|
fecundity
|
1 young per year, fecundity is low as with most bats
|
captive breeding/translocation potential
|
no success with moving from roosts
|
inbreeding
|
very low variability suggests inbreeding or small gene pool
|
off-site mortality - from surrounding land uses
|
could be driven from areas by renewed mining, urban expansion, human disturbance
|
sensitivity to disturbance
|
highly sensitive; outreach to recreational cavers and mine explorers is needed
|
adaptibility
|
not very adaptable to some changes, especially loss of roosts
|
charisma
|
mixed bag: bats have had a major change in public image in past two decades but some people still fear or hate; need to empasize that they eat pest insects
|
INTERSPECIFIC FACTORS
|
predation
|
limited knowledge; may be subject to predation by cats but this is not likely
|
disease
|
rabies may affect; others unknown
|
competition
|
unknown; has been found in roosts with other species
|
domestic/feral animals
|
may be preyed on by cats, but this is not likely
|
ANTHROPOGENIC FACTORS
|
edge effect
|
edges are prefered foraging sites
|
off-road vehicles - dust
|
ORVs may be a problem because they get people to roost sites and result in disturbance
|
mining
|
renewed mining in areas with old mines may result in disturbance or loss of roosts
|
passive recreation
|
disturbance of roosts; should route trails to avoid roosts
|
grazing - vegetation impacts
|
may affect prey base
|
collection/hunting
|
not thought to be a problem
|
herbicides
|
not thought to be a problem, except as they may affect prey base
|
insecticides
|
impacts have been reduced over time, but still may be a problem
|
pesticides - impacts to species
|
impacts have been reduced over time, but still may be a problem
|
pesticides - impacts to prey
|
this could be significant
|
direct take/mortality
|
little effect except from mine hazard abatement practices, which could be serious impacts; road paving and de-icing may affect
|
light
|
bright lights near roosts may affect
|
landscaping
|
native plants could provide beneficial opportunities for habitat improvement
|
dumping
|
may affect if in roost sites
|
undocumented immigrants
|
may affect when they use caves and mines for shelter or dumping grounds
|
increased road density
|
may be a problem, low-flying bats could get hit by cars while foraging along road edges
|
road kill
|
may be a problem, low-flying bats could get hit by cars while foraging along road edges
|
CONNECTIVITY
|
barriers
|
large cities with abundant lights could be barriers
|
traffic volumes
|
increased volume could lead to increased road kill
|
wash incision
|
could create roost sites but could also take some away
|
corridor width
|
buffers along washes would be good but width unknown
|
habitat patchiness
|
depend on what is around them; patchiness could be good because it could increase insect diversity
|
riparian/upland connection
|
bridges could be improved as bat roosts
|
road crossings
|
could be opportunity for foraging or hazard due to roadkill
|
vegetation next to roads
|
could be opportunity or hazard; recommend not planting edges along larger and faster roads, allow space between trees and roads
|