Week 2 Questions Flashcards

1
Q

Define: Population, Deme, Subpopulation, Metapopulation

A

population: A collection of organisms in the same species that interbreed

deme: Individuals of the same species that have a high likelihood of interbreeding

subpopulation: or a portion of a population in a specific geographic location or as delineated by nonbiological criteria

metapopulation: when a species whose range is composed of more or less geographically isolated patches, interconnected through patterns of gene flow, extinction, and recolonization

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2
Q

population viability

A

likelihood of persistence of well-distributed population > 100 years

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3
Q

dispersal

A

one-way movement, typically of young away from natal area

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4
Q

Migration

A

a seasonal, cyclic movement typically across latitudes or elevations:
a. to track resources or
b. to escape harsh conditions changed by season

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5
Q

home range

A

movement throughout a known space over a day/week/month to locate resources

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6
Q

functional response

A

refers to changes in the behaviour of organisms

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7
Q

source populations

sink populations

A

Source: populations of stable reproductive populations

Sink: habitats predominated by subdominant individuals and young of the year

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8
Q

ecological traps

A

poor-quality habitat appears better than it is

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9
Q

native species

non-native species

A

native: a species that is located in its presumed area of evolutionary origin and nonhuman-aided dispersal,

non-native species: (of a person, plant, or animal) not indigenous or native to a particular place

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10
Q

Introducing’ wildlife

re-introducing wildlife

‘augmenting’ wildlife

A

Introducing’ wildlife: Species or genotypes not known to have existed there previously are established at a site. Species may or may not be native to a broader geographic area

re-introducing wildlife: Reestablishment of species or genotypes historically present at the project site but was extirpated.

‘augmenting’ wildlife: Individuals of a species are added to a site where the species occurs presently—also called restocking

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11
Q

resident wildlife

translocated wildlife

A

resident wildlife: Species, populations, or genotypes native to a local site. These can be extracted from a local site for onsite restoration or augmentation

translocated wildlife: Genotypes are collected offsite for planting or release at a project site within the species’ natural range.

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12
Q

genetic drift

A

the change in frequency of an existing gene variant in the population due to random chance

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13
Q

hard release

soft release

A

hard release: animals are released into the wild without any conditioning at the release site

soft release: captured animals are held in captivity for an extended period

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14
Q

minimum viable population

A

smallest size population (typically measured in absolute number of organisms rather than density or distribution of organisms) that can sustain itself over time

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15
Q

numerical response

A

numerical response: refers to absolute changes in the abundance of individuals through changes in recruitment.

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16
Q

Explain the concept of metapopulation. How does it relate specifically to restoring wildlife populations (factoring in dispersal ability)?

A
  • when a species whose range is composed of more or less geographically isolated patches, interconnected through patterns of gene flow, extinction, and recolonization
  • occur when environmental conditions or species characteristics retard the complete interchange of reproductive individuals
  • there is greater demographic and reproductive interaction among individuals within, rather than among, subpopulations
  • Identifying formerly occupied locations is a first step in prioritizing restoration efforts, need to identify:
  • the metapopulation structure, and
  • estimate of the abundance of individuals within each subpopulation,
  • one goal - identify the metapopulation structure and then locate restoration sites to enhance this structure
17
Q

50-500 rule, and 10-50 generation rule

A

50–500 rule:
- populations of at least 50 breeding individuals are needed for short-term viability (factoring in environmental and demographic variability) and
- 500 individuals are needed for long-term viability (genetics)

10-50 rule:
- populations persist for 10 generations for environmental / demographic variability (population demography/dynamics*), or
- 50 generations for enhancing genetic variability

18
Q

Why is density a misleading indicator of habitat quality?

A

Does not provide information on:
- Reproduction, survival, dispersal rates, etc

19
Q

How does varying habitat quality affect metapopulation structure?

A

Because of the metapopulation structure, not all suitable habitats will be occupied at any one time:
o thus, unoccupied habitats must be monitored and conserved for many years,
o monitoring needs an adequate sample size to avoid concluding ‘absence,’
o this can be avoided with adequate sample size and monitoring duration,
o designing a restoration plan depends upon the size and fragility of the population and its habitats, and on project objectives,
o thus, identifying the structure of the population(s) of interest is critical if a restoration project is to be successful.

20
Q

How does the distribution pattern influence the approach to restoration?

A
  • Many species have a bull’s-eye distribution:
  • the greatest areas of abundance are toward the middle of their overall ranges and peripheral portions of the range in marginal conditions
21
Q

How does an understanding of dispersal influence restoration planning?

A
  • provides information on where to prioritize the restoration
  • e.g., breeding locations and natal areas
22
Q

How does an understanding of migration influence restoration planning?

A
  • animals need food, water, cover, and space, and some animals will travel significant distances to obtain these resources.
23
Q

How does an understanding of home range influence restoration planning?

A
  • detailed information on what animals use must be gathered to specify the vegetation and special habitat features needed
  • Temporal aspect
24
Q

Why is knowing whether your measured population response is a ‘functional’ or ‘numerical’ response
essential?

A
25
Q

Explain the source-sink dynamics of populations and their impact on restorations

A
  • Individuals in sink habitats are maintained by continuous immigration from source habitats.
  • the metapopulation dynamic reflects frequent movements due to changing source-sink conditions among the individual populations.
26
Q

Describe how exotic species can impact restoration activities

A
  • Exotics can quickly negate efforts to enhance native species following restoration
  • sometimes native species rely on exotics….
27
Q

Why would you initiate ‘conservation breeding? (3 goals)

A
  • to provide demographic and genetic support for wild populations,
  • to establish sources for founding new populations in the wild,
  • to prevent species extinction with no immediate chance of survival in the wild.
28
Q

What are the main concerns about captive breeding and restoring rare populations (3). Include concerns around genetic bottlenecks

A

1) Captive breeding is expensive, and translocation is problematic
2) the captive breeding program can induce additional mortality in the already-rare species, BC’s spotted owl
3) it is complex

Genetic bottlenecks:
- genetic manipulation could be required to restore/maintain evolutionary potential
- captive breeding can lead to loss of genetic variation through random drift

29
Q

What are the five key considerations to consider before augmenting a population?

A

1) are there two lines of evidence (e.g., genetic, demographic, and behavioural) that support the hypothesis that a severe population bottleneck has occurred?

2) would adding additional animals degrade resource conditions, driving the wild animals to a more rapid extinction?

3) was the population bottleneck due to a disease outbreak (or other specific and known occurrence), and can the source of the problem be eliminated?
4) are there habitat patches nearby to establish a larger population (or metapopulation) rather than a single, isolated population?
5) how should the sex and age composition of an augmentation be structured?

30
Q
  1. Why is genetic variability in a population good?

How does conservation breeding compromise this variability?

A
  • genetic variation largely determines the ability of populations to persist through changing environments
  • captive breeding selection can eliminate alleles that are maladaptive (faulty adaptations) in the captive situation yet important for survival in the wild,
  • random genetic drift can cause the cumulative loss of both adaptive and maladaptive alleles
31
Q

How does metapopulation structure enhance genetic variability?

A

Increasesit
- retain greater gene diversity (expected heterozygosity)
- greater allelic diversity than would a single, large (panmictic1) population

32
Q

Successful reintroduction: characteristics of the source population (3)

A

i. they may come from a captive population or an existing wild population

ii. given that mortality is high among reintroduced animals
- remove individuals only if the source population is not compromise
- only animals descending from the most prolific lineages

iii. the source population should have high genetic diversity, genetic similarity, and environmental similarity compared to the new population

33
Q

Successful reintroduction: b. evaluation of the reintroduction site (2)

A
  • reintroduction programs must use high-quality habitat
  • you must identify critical factors and their status in the release location
34
Q

Successful reintroduction: size of the reintroduction population

A
  • For native game species, 20–40 founding animals have been sufficient for success.
  • Some recommended that at least 30–50 individuals be released if possible.
35
Q

The success of any restoration program—rests fundamentally on

A

the habitat condition and niche of the species in question.

36
Q

What is the primary cause of failure in reintroductions?

A

Mortality due to predation is a primary cause of failure in reintroductions