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introduced vs exotic species
exotic species are not native to an area
“exotic species: often used interchangeably with introduced species, but some native species can be reintroduced to parts of their previous range
introductions of exotic species may be intentional or inadvert
Burmese python in southern florida
native to southeast asia
popular in North American exotic pet trade
introduced to florida everglades by:
release of individuals too large for owners to care for
escaped pet animals
destruction of breeding facility by hurricane in 1992
impacts of introduced exotic species
ruddy duck and white-headed duck
beyond consumptive effects like case of Burmese python in florida, introduced species can have wide range of impacts on local fauna
example: ruddy duck
Eurasia has similar species (white-headed duck) - IUCN threatened species
Ruddy duck introduced to Europe in late 1940s; subsequent population increases and range expansion in EU
competes with white-headed duck; also able to hybridize with white-headed duck (loss and potential extirpation from restricted ranges around Mediterranean)
in response, western EU countries implemented culling (primarily through selective hunting)
invasive species
invasive species: exotic species that spread rapidly in new area
or invasive species are exotic species that have harmful environmental impacts, esp. on native species
ecologists tend to confuse first definition (interchangeable use implies correlation between how quickly an organism spreads and the damage to environment it causes); assume becuase species spreads fast, it causes harm
do faster-spreading invasives cause larger impacts
tested whether invasive species (defined in terms of establishment and spreading rate) are more likely to reduce native species populations
quantified relationship between rate of establishment or spread and impact rank in naive species; for ~70 species
No relationship between spread rate and impact; also pooled impact ranks into low and high and compared rate of spread (<3 = low; >4 = high)
no discernable pattern when split by taxa
author conclusions: term invasive should not be used to connote particulate species that threaten biodiversity
North American Swans
populations of feral mute swans in NA have been growing at very fast rate
i.e. Chesapeake Bay (Maryland and Virginia) populations have grown from 1962 (5 birds released) to over 4000 by 2001
9.1% increase per-year in US atlantic Flyway
mute swan effects:
displace native species
attack and kill native species
hybridize with trumpeter swans (reduce genetic stock)
consume and uproot aquatic vegetation; non-migratory do not field feed (heavy competition for resources)
Mute swans on the great lakes
more locally, large population increases seen around Great lakes
combined aerial survey data, midwinter waterfowl inventory data, Christmas bird count data to estimate rates of increase
quick increase in population size of 10-21%/year; 30,000 swans in lower great lakes region
we can ask: What is carrying capacity for swans on lower great lakes?
accelerating growth phase - how can we determine K? (K = CARRYING CAPACITY)
can be determined with a graph; where population asymptotes, or birth = death
OR
what habitat do swans need
how much habitat is available
what density of birds can the habitat support
POPULATION control of mute swans
Population control began in 2001
manage by egg addling or direct killing of adults
addling: involves coating eggs with oil to prevent them from hatching; by returning eggs to nest, the bird will not attempt to re-lay
criticism of population control of mute swans:
destroying eggs is cruel, they say
despite being more gentle form of management, still criticized
global distribution of wild pigs
wild pigs have largest global range of any non-domesticated terrestrial mammal on earth
native to Eurasia; introduced to Americas and Oceania in recent history
highly damaging species, esp. to regions with few native mammal species (polynesia, Aus.); 0.5% taxa threatened in NA
wild pigs threaten 672 taxa in 54 different countries
most taxa are listed as critically endangered or endangered (mostly plants)
14 species have been driven to extinction as result of impacts from wild pigs
omnivorous opportunistic feeders: will predate small animals
root extensively in search of food; disrupt soil structure, cause erosion, damage vegetation, lead to habitat degradation
disease transmission
outcompete native WL for resources such as food and habitat
very high reproductive rates
North America’s wild pigs: Canadian population
originally brought from Europe to Canada 3 decades ago and mated to domestic pigs to produce a marketable hybrid (did not work well)
NDMNRF has found evidence that ~14 pigs in a sounder spotted in pickering ONt. this month
wild pigs detected across southern canada
North America’s wild pigs: USA population
feral swine population has increased a lot since 1982 - 2020
mostly south-eastern states
economic damage in addition to ecological damage
crop loss estimates: $61 million corn
controlling wild pig populations
fencing:
stay install fencing to exclude feral swans from crops
electric fencing is effective in some cases but may be cost prohibitive for large areas
traditional fencing + habitat modification (cleaning underbrush along fence line) can be effective
feral swine are clever so may destroy fences if motivated or agitated (should be considered during construction)
harassment:
can be effective for immediately removing from area
not practical on large scale (likely shift feral swine problems from one area to another)
also makes them wary and can reduce success rates of other control methods
vaccination of livestock and pets:
keep livestock vaccinated and parasite free and in good condition to aid disease resistance
diseases from swine that may be transferred to livestock: leptospirosis, brucellosis, porcine reproductive and respiratory syndrome, porcine circovirus T2, influenza, E. coli
trapping:
captured swine should not be moved or released to environment; humanely euthanize once in trap
intelligent so if trap is not set up properly or not pre-baited, individuals not captured will be educated and much more difficult to capture later on
snares:
can be useful alongside traps or in terrain where traps are impractical and only few individuals remian
ground shooting:
effective only when few individuals are present in the area; if larger groups are observed, shooting few individuals can disrupt social organization and make them spread further across landscape
labor intensive and unlikely to give desired relief from damage
aerial operations:
if landscape is open (grassland) then effective means of quickly and efficiently reducing feral swine numbers
not permitted in regions and may be cost-prohibitive
toxicants:
potential to be cost-effective tool for reducing populations
currently working on toxicant capable of effectively and humanely removing feral swine without having adverse effect on environment and non-target species
NO TOXICANT CURRENTLY REGISTERED FOR USE ON FERAL SWINE IN USA
Wild pig control programs in Canada
Alberta - whole Sounder trapping incentive program
encourages the elimination of entire Sounders (social groups)
$75 per set of ears per sounder
from April 1 2022 to march 31 2024
program concluded without any submissions
Saskatchewan - Feral wild boar control program
corrals set up in high traffic areas and grain placed as bait inside corral enclosure
trail cams used to monitor pig movements
when trap operators are confident that all members are inside corral, gate is triggered and pigs trapped inside
boars then euthanized
little evidence of wild boar in Ontario - mainly feral domestic animals
if seen, then report wildpigs@ontario.com, call, or inaturalist Ontario wild pig reporting