Test 3 Flashcards

1
Q

Jeschke et al 2020 2 comparisons regarding natural enemy pressure

A
  1. looked within communities (pressure of enemies of invasives and native in same community within introduced range)
  2. biogeographical comparisons (looks at enemy pressure in native AND introduced ranges)
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2
Q

examples of biotic effects of invasions

A

competition; consumption; genetic hybridization

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3
Q

examples of abiotic effects of invasions

A

change in resource availability; change frequency/intensity of disturbance; change in physical, biogeochemical structure or function of ecosystem

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4
Q

Extinction debt

A

time delay between impacts on a species, such as destruction of habitat, and the species’ ultimate disappearance

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5
Q

case study of Lake Victoria

A

in isolation, >500 spp of cichlid fish evolved with adaptive radiation. After commercial fishing began in 1930s. trawlers were used—causing overfishing that greatly declined native cichlid stock
-1950s -Nile perch was introduced—apex predator in a system that didn’t have one. Took about 20 years for population to suddenly explode in 1970s
-native diversity soon collapsed to 3 dominant cichlid spp in less than 10 yrs—many going completely extinct
-now Lake Victoria is big rich asshole trophy hunting place
—now there are huge algal blooms, detritus, hypoxic/eutrophic conditions—center of lake is more or less completely hypoxic
-Nile perch actually fuels many armed conflicts in surrounding countries—exchanging perch for guns & ammunition

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6
Q

Adaptive Radiation

A

a single or a few spp give rise to many different spp often with distinct ecological roles as they evolve in isolation to fill niches (ex: Darwin’s finches)

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7
Q

Hybridization

A

interbreeding between genetically distinct populations—often restricted to interbreeding between spp but subspecific pops may be considered

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8
Q

Introgression

A

gene flow between populations whose individuals hybridize, where hybrids backcross to one or both parent pops

-oftentimes, one spp is more affected than the other (with invasive impact, native spp genetics typically become less common and more of genome is invasive due to larger pop size)

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9
Q

Hybrid Zones

A

geographic boundaries where spp may be hybridizing—possibly assimilation of 1 group into the other

ex: tatarian X Morrow’s honeysuckle; purple X native loosestrife; cattail hybridization (invasive X native), etc

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10
Q

Demographic Swamping

A

where hybrid fitness strongly reduced relative to parent spp (outbreeding depression). If hybrids are common, one or both parental lineages may decline below replacement rate due to wasted reproduction—leads to extinction

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11
Q

Genetic Swamping

A

if outbreeding depression is less severe, pop growth rates exceed replacement rates, one or both parental lineages replaced by hybrids.

—results form asymmetry of population size and/or one-way gene flow

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12
Q

Cryptic Invasions

A

describes 2 different processes:

1) cases of mistaken identity. These errors have become less common with genetic testing, but still cases of inv spp comprised of separate spp

2) replacement of native genotype with exotic genotype

ex: interesting case of Phragmites australis (native genome was fairly uncommon spp, but suddenly starting exploding in popularity—now know it’s because of hybridization with non-native)

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13
Q

3-pronged approach for invasion management

A

1) Prevention (through education, laws & policies, research/risk assessment/monitoring tools) ALWAYS MOST COST-EFFECTIVE
2) Eradication (early detection/rapid response; removing ALL propagules paired with ecosystem restoration)
3) Control (limits the ecological / economic costs below some arbitrary threshold: mechanical / chemical / physical; biological–can be integrated approaches; novel approaches like gene drives, resistance breeding, etc)

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14
Q

Invasion Curves

A

can show options for 3-pronged management plans well: oftentimes, first detection occurs after the point where eradication is still feasible—time lags, low early detection–some spp are hard to detect early ex: EAB)

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15
Q

“dirty list” or reactive approach to invasive species prioritization

A

made of spp list that are already established and actively causing issues—all other upcoming exotic spp are permitted “innocent until proven guilty”

-take a long time to get listed
-obviously flawed (only prohibiting things we already know are bad)

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16
Q

“clean list” or proactive approach to invasive species prioritization

A

all spp are assumed to be potentially invasive unless evidence exists to the contrary “guilty until proven innocent”

-it is more costly, some lost economic opportunity
-lack of info, inadequate mechanisms for testing potential invasiveness, lag times, quarantine conditions, generation time, etc
-enforcement (if agencies like APHIS are chronically underfunded, undermanned)
-weak laws, light punishments
-lobbying groups are well-funded by opposition groups

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17
Q

The Lacey Act of 1900

A

first broad-based federal law broadly applicable to invasive spp
–although still in force as most important invasive spp law, was not intended for invasive spp at all—but for over-exploitation of wildlife for commercial purposes

18
Q

Plant Quarantine Act (1912)

A

gave APHIS authority to regulate importation of nursery stock & plants

19
Q

Federal Seed Act (1939)

A

required accurate labeling and purity of imported seeds

20
Q

Federal Noxious Weed Act (1974)

A

prohibits importation of any plant that can directly/indirectly injure crops, useful plants, and livestock (including fish & wildlife)

21
Q

National Invasive Species Act (1996)

A

specifically for invasives but scope was narrow, encompassed only aquatic spp introduced through ballast discharge

22
Q

Executive Order 13112 (1999)

A

—arguably most important legislative initiative on inv spp in US
-conceptualized a comprehensive mgmt. framework for inv spp
-attempts to solve some bureaucratic issues bt different agencies (more collaboration)
-created an advisory committee (Invasive Species Council) to brainstorm more solutions
-Key Focuses of management plan—focusing more on early detection & rapid response
—*weakness of exec orders is they are not codified into law

23
Q

Plant Protection Act (2000)

A

-replaces Federal Noxious Weed Act and many other APHIS authority acts (consolidates 10 existing plant protection laws)
-OTA 1993—the Office of Technology Assessment published comprehensive evaluation of economic costs of inv spp
-Fantle-Lepczyk et al (Feb 2022) paper looks at economic costs in modern day
-when cherry trees were gifted to D.C. from Japan, they were infested with insects, so were burned (Charles Marlatt) “Quarantine 37”
—eventually led to this Plant Protection Act

24
Q

Elements that Laws Need to Be Effective

A

-Education (public must understand WHY law is in place)
-Compliance (need public buy-in to law—can take effort)
-Enforcement (needs to be consistent and applied)
-Penalty (needs to be imposed and meaningful)

25
Elements Required for Effective Eradication of Invasive Species
1) Sufficient funding (it takes time and money. Many exhaust funding before they succeed) 2) Clear lines of authority (too many different groups/agencies increases inefficiency & wastes resources) 3) Susceptible to a control measure (eradication can only succeed with viable tools for killing/detecting it (keep on monitoring programs after assumed eradication) 4) Well-defined invaded area, spread over small scale (once area becomes too large, it is impossible to eradicate---depends on spp) 5) Prevention of reinvasion (taking time & money to eradicate something---only to have it reinvade a few years later saps morale and can lead to begrudging acceptance of spp presence). 6) Detectable at low densities (many efforts fail because we can’t detect the last few in population so it rebounds once control effort scales back) 7) Contingency plans for ecosystem restoration (invasive spp, especially those present for long time, alter ecosystems in ways that prevent recovery to natural state without active restoration)
26
Case-study of mouse eradication on Gough Island
very important for bird nesting (UNESCO world heritage site since 1995) ---house mice were introduced in late 1800s, they will prey on sea bird chicks—attack at night when birds have limited vision -will gnaw holes into head and body so chicks die slowly over days (chicks have evolved to not leave nest—so very vulnerable) -causing serious mortality for Tristan albatross, etc ---used 200 tons of rodenticide over 224 square miles and trained terriers to locate last remaining rats -on Gough, modelled project after successful South Georgia---but were unable to fully eradicate (so expensive, non-profit couldn’t afford to go back during COVID-expected to return effort in 2026)
27
Case-study example of issues possible from invasive spp eradication
-Langara Island rat eradication---home of one of Canada’s biggest seabird breeding colonies. Many seabirds breed in underground burrows that rats invade (within 9 yrs, 4 burrowing spp disappeared). Rats introduced by ships -provincial & federal agencies tried to eliminate rats by poisoning them with an anticoagulant---Developed bait dispenser that would target rats better (avoiding non-target spp) --unfortunately, ravens also learned how to extract bait from dispensers. Other scavengers were feeding on raven carcasses---and also dying (bald eagles, etc) -this operation informed other rodent campaigns (ex: S Georgia Island, captured and held endemic terrestrial birds captive so they wouldn’t eat poison)
28
3 Effects on food web through invasive eradication efforts
-Prey release -Hyperpredation -Mesopredator Release
29
Prey Release
response of lifting large effects of predator by removal---can be difficult to predict and assess in systems with multiple predators and other invasive prey. Invasive spp may be held in check by invasive predator and can increase dramatically with its removal (foxes vs rabbits; cats vs rats, etc)
30
Hyperpredation
if an abundant non-native prey spp is removed, exotic predators may shift diet onto native spp---especially big effect on rare/endangered native spp
31
Mesopredator Release
apex predators often have greater effect on an ecosystem than their numbers suggest---once eliminated, the foodweb beneath them is reset. When removed, middle level predators can become much more abundant and have larger effects on prey base
32
How Public Opposition Can Impact Eradication Efforts
eradication often not attempted even where it could succeed due to well-funded lobbying and PR campaigns that put fed, state, or non-profits in hot seat -ex: animals rights/toxicity of control methods/inv spp denialism/anti-govt/cultural affinity campaigns (ex: mute swans in NY; camels/wild horses in AUS; feral burros in Grand Canyon; wild pigs in Hawaii; inv insects in CA and NZ; cats---like everywhere)
33
What are some potential unintended consequences of eradication programs to pay attention to?
1) poisoning of native species (poisons carry considerable risk) -pay attention to bioaccumulation risks, direct toxicity 2) removal of exotic can trigger invasion or pop increase of other spp -minimizing disruption to trophic interactions 3) may need to reconstruct ecosystems and invest heavily in restoration efforts -without restoration, the transformed/degraded ecosystem will often not return to what it was prior to invasion (soil amendments, reintroducing natives, etc)
34
The main types of invasions that affect ecosystems are those that
1) Alter trophic structure (ex: Predation, Competition)---changes flow of energy in ecosystem 2) Alter abiotic factors (ex: resource availability (water, light, etc); disturbance frequency) 3) Changes to physical environment (ex: water flow; sedimentation; etc)
35
Autogenic engineers
alter the environment with their own bodies, forming part of the engineered habitat. Invasive woody plants in grasslands fit in this category as do some aquatic weeds and invasive bivalve mollusks (clams and mussels)
36
Allogenic engineers
modify the environment by transforming the physical and chemical state of living and non‐living materials (or structures). ex: Beavers
37
5 Potential Outcomes of Hybridization
(1) Nothing: Offspring of hybrid crosses may be unviable or very unfit (2) Merge: Hybrids can reproduce and viable offspring are created. Overtime, differences between the species are lost and the species merge (3) Form a hybrid zone: along some boundary, a hybrid zone forms (genetics of both). Hybrid zones can persist or be transitory. (4) Introgression – hybrid offspring backcross with the parent populations with gene flow into 1 or both populations. Over time--both can lose their genetic identity. ---may be asymmetric (5) Hybrid Species: Cross exclusively with other hybrids (= novel third species). Can happen immediately, or over time due to behavioral/ecological differences in hybrids
38
Once prevention has failed: management options available
-Eradication -Mitigation (Control) -Exclusion / Containment -or Do Nothing...
39
Eradication
Removal of every individual or propagule, thus only reintroduction would lead to a return of the species
40
Mitigation
Management to maintain a species below levels that cause significant damage to native species, ecosystems, or economic interests
41
Exclusion / Containment
Application of physical barriers or quarantines that prevent the colonization of an area by an invasive or prevent it from establishing beyond some predetermined area
42
The 3 Too's
Eradication efforts fail if: -there's TOO MUCH (area/density) -TOO LITTLE (funding) -TOO LATE (trying after eradication is certain to fail)