โญ 10/10 Life Sciences Learning • B10logy = 10 out of 10 in Biology • High-Yield Visual Notes Across 23 Disciplines Explore Subjects →

Exp 2: Population Size Estimation via Mark-Release-Recapture: Lincoln-Petersen Index & Bailey’s Correction

Experiment 02Population EcologyDemographic Modeling

Population Size Estimation via Mark-Release-Recapture: Lincoln-Petersen Index & Bailey’s Correction

Duration: 4 Hours • Field Simulation / Lab Model
๐ŸŽฏ Experimental Aim & Learning Objectives
To simulate and calculate absolute animal population abundance ($N$) in an enclosed model population or natural terrestrial arthropod assemblage using the two-sample Lincoln-Petersen mark-release-recapture index, apply Bailey’s small-sample correction, and calculate theoretical variance and 95% confidence intervals.
๐Ÿ”ฌ Theoretical Foundation & Mathematical Principles

Determining animal population density cannot rely on total censuses for vagile organisms. The mark-release-recapture (MRR) framework assumes that the proportion of marked animals in a second sample equals the proportion of marked animals in the total population:

  • Lincoln-Petersen Equation:
    $$frac{m}{n} = frac{M}{N} implies hat{N} = frac{M cdot n}{m}$$
    where $M$ is the number of individuals marked and released in Sample 1, $n$ is the total number of individuals captured in Sample 2, and $m$ is the number of previously marked recaptures in Sample 2.
  • Bailey’s Correction for Small Recaptures: The standard Lincoln-Petersen estimator is positively biased when sample sizes or recapture rates are low ($m < 10$). Bailey (1951) introduced the nearly unbiased estimator: $$hat{N}_{text{Bailey}} = frac{M(n + 1)}{m + 1}$$
  • Variance & Confidence Limits:
    $$operatorname{Var}(hat{N}) = frac{M^2 cdot (n + 1)(n – m)}{(m + 1)^2 (m + 2)}$$
    The 95% Confidence Interval is given by: $hat{N} pm 1.96 cdot sqrt{operatorname{Var}(hat{N})}$.
POPULATION SIZE ESTIMATION: MARK-RELEASE-RECAPTURE (LINCOLN-PETERSEN INDEX)SAMPLE 1: CAPTURE & MARKM = 40 Marked & ReleasedRandom Mixing(Time Interval Δt)SAMPLE 2: RECAPTURETotal Recaptured (n) = 30Marked Recaptures (m) = 6=POPULATION (N)m / n = M / NN = (M × n) / mN = (40 × 30) / 6 = 200Bailey’s Unbiased:N = M(n + 1) / (m + 1)= 40(31)/7 = 177CORE ASSUMPTIONS OF THE LINCOLN-PETERSEN MODEL:• Closed Population: No births, deaths, immigration, or emigration during sampling window.• Equal Catchability: Marked animals are equally likely to be captured as unmarked (no trap-shyness or trap-addiction).• Permanent Marking: Marks are not lost, shed, or eroded, and do not increase predation vulnerability.Variance Equation Var(N):M² × n(n – m) / m³95% CI: N ± 1.96 × √Var(N)

Figure 1.2: Mark-Release-Recapture paradigm, Lincoln-Petersen ratio, Bailey’s small-sample correction, variance calculations, and fundamental ecological assumptions.
๐Ÿงช Materials & Simulation Apparatus
  • Field Trial (e.g., Tenebrionid Beetles / Snails): Pitfall traps with non-toxic collection funnels; quick-drying, waterproof, non-odorous cellulose paint markers (white or fluorescent red); fine point brushes; sorting trays.
  • Bench Simulation Alternative: Large opaque mixing bin containing 500-1000 identical white plastic beads/beans representing the unknown population; permanent colored marking pens; sampling scoop.
๐Ÿ“‹ Step-by-Step Experimental Protocol
  1. Sample 1 Capture & Tagging: Draw a random sample of $M$ individuals (e.g., $M = 50$ beetles from pitfall traps or beads from the container). Apply a discrete dot of waterproof paint onto the dorsal elytron or bead surface. Record the exact number $M$.
  2. Release & Random Mixing: Release all marked individuals back into their habitat/bin. Allow sufficient time ($Delta t = 24-48text{ h}$ in the field, or thorough hand-stirring in simulation) to ensure completely homogeneous random redistribution throughout the population.
  3. Sample 2 Recapture: Take a second random sample without replacement. Count the total number of individuals captured ($n$, e.g., $n = 45$).
  4. Recapture Tally: Inspect each individual in Sample 2 for paint marks. Record the number of marked recaptures ($m$).
  5. Statistical Calculation: Compute $hat{N}$ using both the standard Lincoln-Petersen formula and Bailey’s modification. Calculate variance and 95% confidence intervals.
๐Ÿ“Š Sample Calculation & Results

Given Data: $M = 60$, $n = 50$, $m = 12$.

Lincoln-Petersen Estimate: $hat{N} = frac{60 times 50}{12} = 250text{ individuals}$.

Bailey’s Corrected Estimate: $hat{N}_{text{Bailey}} = frac{60 times (50 + 1)}{12 + 1} = frac{60 times 51}{13} = 235.4 approx 235text{ individuals}$.

Variance: $operatorname{Var}(hat{N}) = frac{3600 times 51 times 38}{169 times 14} = frac{6,976,800}{2366} approx 2948.7$.

Standard Error: $text{SE} = sqrt{2948.7} = 54.3$.

95% CI: $235 pm (1.96 times 54.3) = [128.6, 341.4]$.

{reading_nav}

๐Ÿ“– Key Terms & Comprehensive Glossary

Key Terms in this Lecture • Ecology

Master the essential vocabulary, core concepts, and biochemical keywords covered in this chapter. Click any key term to inspect its rigorous definition in the Ecology Comprehensive Glossary.

โญ 10/10 Concept Clarity
Back to Ecology Laboratory Manual: Quantitative Sampling, Limnology & Pedology โšก One Night Revision → Explore All Disciplines