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Population Estimation

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Records for each specimen seen its perpendicular distance to the transect. Equations give density by assuming declining observability with distance from transect ... – PowerPoint PPT presentation

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Title: Population Estimation


1
Population Estimation
  • BIOL 500
  • 30 November 2009

2
Population Estimation
  • Goal Estimate N, to.
  • test population-growth models.
  • compare relative abundance.
  • track game species.
  • track endangered species.

3
Total Count
  • Rarely possible, except with small populations of
    large, conspicuous animals or plants
  • Exs Whooping cranes (188 in recent aerial
  • count of nesting grounds)
  • Large mammals
  • Trees

4
Sampling and Extrapolation
  • Ex Zebra mussels discovered in Edinboro Lake in
    Oct. 2000 (data from Jim Grazio, DEP)
  • 45 randomly-chosen sampling stations
  • Attention to depth and littoral zone distribution
    by depth
  • Peaks
  • 271 mussels/m2 at 0.76 m in Nov. 2000
  • 76 mussels/m2 at 1.3 m in May 2001
  • Total estimate of 37,273,524 in Nov. 2000, prior
    to lake draw-down
  • Population down to just 21,991,379 in May 2001

5
Line Transect Estimates
  • Observer moves in straight line through habitat
  • Records for each specimen seen its perpendicular
    distance to the transect
  • Equations give density by assuming declining
    observability with distance from transect

6
HANDOUTLacki et al. 1994
7
Index of Relative Abundance
  • Quantifications that do not yield estimates of N
    and thus are only useful on a comparative basis
  • Catch per trap-night or per unit effort
  • Counting feces, burrows, mud chimneys of
    crayfish, gorilla nests, etc.
  • Listening for calls

8
HANDOUTNelson and Graves 2004
9
Mark-Release-Recapture Methods
  • Rely on the ratio of markedunmarked animals in
    subsequent samples
  • Model assumptions are vitally important
  • Lincoln-Peterson method
  • Schnabel method (aka Schumacher-Eschmayer method)
  • Jolly-Seber method (aka Jolly-Seber-Cormack
    method)

10
Lincoln-Peterson Estimator
  • Two samples
  • N total population (unknown)
  • n total captured in second sample
  • m marked animals captured in second sample
  • M total marked and released during first sample
    (assumed to be present when second sample is
    taken)

11
Lincoln-Peterson Estimator
  • n/N ? m/M
  • Proportion of total population
  • caught in the second sample left
  • approximately equal to
  • proportion of the marked population
  • caught in the second sample right
  • N (nM)/m


12
Fig. 8.4 p. 119

N (2016)/5 64
13
Critical Assumptions of the Lincoln-Peterson
Estimator
  • n/N ? m/M if and only if
  • a) No marks are lost.
  • b) The population is closed.
  • c) Marked and unmarked animals are equally
    catchable.
  • Trap-happy or trap-shy behavior would
    introduce bias into estimate of N

14
Schnabel Estimator
  • Multiple recapture censusing periods
  • Yields weighted average of L-P estimates
  • N ?niMi / ?mi 1


15
Critical Assumptions of theSchnabel Estimator
  • Same three as for L-P

16
Jolly-Seber Estimator
  • Published simultaneously in Biometrika in 1965
  • Allows for an open population
  • Series of estimates of Ni (allowed to vary)
  • Also, estimates of rate of loss and number of
    additions between sampling periods
  • Key estimate Mi, rather than simply keeping a
    running log of how many animals have been marked
    and released

17
Fig. 8.2 p. 116
18
New Variables for the J-S Estimator
  • Zi animals caught prior to i, not at i, and
    after i
  • Assumed present at i, but not caught at that time
  • Ri animals caught at i and at least once again
    thereafter

19
HANDOUTKrebs 5th edition
20
J-S Equation
  • Zi /Mi mi ? Ri /ni
  • The proportion of marked animals present at i
    which
  • we do not account for then, but do later left
  • approximately equal to
  • proportion of the total catch at i that we catch
    later right
  • Mi Zi ni /Ri mi
  • Thus Ni niMi /mi




21
Critical Assumptions of the J-S Estimator
  • 1) No loss of marks
  • 2) No individual variation in capture probability
  • 3) No animals leave, then re-enter the population
  • Doing so would invalidate Zi

22
Sample Calculations
  • Z3 5221884 39
  • R3 33138 54
  • M3 (39?164)/54 37 155
  • N3 (169?155)/37 708



23
Calculating Survivorship Rates
  • pi survivorship rate, i to i1
  • Mi1/Mi ni mi
  • ni mi represents new marked animals
  • Ex p3-4 205/155 164 37 0.727
  • Estimates that 72.7 remain in the
    populationalive and not emigratedbetween Sample
    3 and Sample 4




24
Calculating Numbers of Additions
  • Bi number of births, i to i1
  • Ni1 Nipi
  • Ex B3-4 765 (708?0.727) 250
  • Estimates 250 new animals (births immigrants)
    between Sample 3 and Sample 4





25
HANDOUTRegehr et al. 2006
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