2.5 Investigating Ecosystems Flashcards

1
Q

what is a dichotomous key

A

a stepwise tool for identification where there are two options based on different characteristics at each step. the outcome of each choice leads to another pair of options. this continues until the organism is identified

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2
Q

limitations of a dichotomous key

A
  • the organism might not be in the key
  • terminology can be difficult
  • there might not be a key available for the organisms under investigation
  • some features cannot be easily established in the field (i.e. whether an animal is endothermic or ectothermic)
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3
Q

where is random sampling used

A

if the same habitat is found throughout the area

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4
Q

where is stratified sampling used

A

used in two areas different in habitat quality

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5
Q

where is systemic sampling used

A

along a transect where there is an environmental gradient

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6
Q

biotic: ways to measure abundance of organisms that can move (motile)

A
  • nets
  • pitfall traps
  • light traps
  • flight interception traps
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7
Q

biotic: ways to measure abundance of organisms that cannot move (non-motile)

A
  • quadrats (square frames of difference sizes)
  • point frames
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8
Q

lincoln index, what is it used for?

A

estimating the pop. size of motile animals

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9
Q

lincoln index, how does it work?

A

The Lincoln Index is a method used to estimate the total population size of a species in a specific area using a technique known as mark-recapture. It is especially useful when counting every individual in a population is not practical. The steps involved in using the Lincoln Index are as follows:

  1. A sample of individuals is captured from the population. These individuals are marked in a harmless and easily identifiable way (e.g., with a non-toxic dye or a tag). The marked individuals are then released back into their habitat, ensuring they mix evenly with the rest of the population.
  2. After allowing time for the marked individuals to mix thoroughly within the population, a second sample is captured. The total number of individuals in this second sample is counted.
  3. In the second sample, the number of marked individuals that are recaptured is recorded.- pop size is estimated by equation
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10
Q

lincoln index equation

A

N = n1 x n2 / m

n= total pop of animals at the study site, n1= number of animals captured (marked and released) on first day, n2= number of animals recaptured on the second day, m= number of marked animals recaptured on second day

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11
Q

limiations of lincoln index

A
  • animals may move in and out of the sample area
    -> makes capture-mark-release-recapture method less reliable, data invalid
  • density of population in different habitats might vary
  • may be many in one area, few in the other
  • may be seasonal variations in animals that affect pop size
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12
Q

percentage cover

A

the proportion of a quadrats covered by a species, measured as a percentages (worked out for each species present)

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12
Q

quadrat methods

A
  • percentage freq.
  • percentage cover
  • pop. density
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12
Q

percentage freq.

A

the % of quadrats in an area in which at least one individual of the species is found.

calc: taking number of occurences and dividing by the number poss. occurences

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12
Q

pop. density

A

the number of individuals of each species per unit area. it is calc by dividing the number of organisms by the total area of the quadrats

total number of a species in all quadrats/area of one quadrat x total number of quadrats

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13
Q

why is biomass calculated

A

to show the total energy within a trophic level

14
Q

what is dry weight biomass

A

when water is removed before biomass is measured

weighed, put into hot oven, weighed, repeated until the same mass is recorded 2 (showing no water present)

15
Q

limitation of estimating biomass in trophic levels

A
  • involves killing of living organisms
  • problems exist with measuring biomass of very large plants such as trees, and with roots and underground biomass
16
Q

how to calc dry weight biomass

A
  • sample is weighed in a container of known weight
  • put in a hot oven (80C)
  • after a specific time, sample is reweighed
  • sample is put back into the oven
  • repeated until same mass is recorded from 2 successive readings
  • no further loss in mass shows that water is no longer present
17
Q

to estimate total biomass

A

extrapolation technique
- mass of 1 organism / the average mass of several organisms is taken
- mass is multiplied by the total number of organisms to estimate total biomass

18
Q

how can we quantify species diversity

A

simpsons diversity index

19
Q

simpsons diversity index formula (you dont need to know formula off by heart, but need to know what symbols mean)

A

D = N(N-1)/SUMn(n-1)

N= total number of organisms of all species found, n= the number of individuals of a particular species

20
Q

what can we do w simpsons diversity index

A
  • make comparisons between areas containing the same type of organism in the same ecosystem
  • high D value = a stable and ancient site, where all species have a similar abundance / evenness
  • low D value = disturbance through logging, pollution, recent colonisation or agricultural management, where one species may dominate
21
Q

ecological gradient definition

A

found when 2 ecosystems meet or where an ecosystem ends
abiotic and biotic changes can be seen here

22
Q

transect

A
  • shows how organisms are distributed along an ecological gradient (changes in abiotic factors)
  • whole transect can be sampled (continuous transect) or samples can be taken at points of equal distance along a transect (an interrupted transect)
  • a line transect = simplest → tape measure laid out in the direction of the gradient, all organisms touching tape are recorded
  • a belt transect → allows more samples to be taken a band usually between 0.5m-1m is sampled along a gradient
23
Q

quadrats used to measuring change along an environmental gradient

A
  • frame quadrats, empty frames of known area
  • grid quadrats, frames divided into 100 small squares
  • point quadrats, made from a frame with 10 holes, inserted into the ground by a leg, pin dropped through each hole in turn + species touched are recorded, total number of pins touching each species is converted to % frequency data
24
Q

why measure changes made by human impact

A

human activities can change abiotic and biotic factors of an ecosystem

human impacts can include: toxins from mining activity, landfills, eutrophication, oil spills, oxerexploitation

25
Q

case study for measuring human impact

A

amazon rainforest
- logging + deforistation
- satellite images used to monitor amount taking place
-> reliable
-> can cover large area
-> monitors change over time
-> visual impact useful for motivating actions against logging + deforestation