ICAR AICE-JRF/SRF - Agricultural Statistics, Computer Application, Bioinformatics (PhD admission and fellowship) · India · National Testing Agency for ICAR
Original practice questions written to the published syllabus · not past papersCounting what cannot be counted directly: capture-recapture and distance sampling, quadrat and line-transect methods, diversity indices and species-abundance models, fish stock assessment, forest inventory sampling and environmental monitoring designs.
In the exams: AICE-JRF Ag Stat Unit 5 'livestock and fishery statistics' (present); ICAR MSc/PhD elective; light in national exams
How our questions for ICAR AICE-JRF/SRF spread across the units of Statistical Ecology, Environmental & Fisheries Statistics. Difficulty: 7 easy, 23 medium, 12 hard.
| Capture-recapture: Lincoln-Petersen and open-population models | 5 | |
| Diversity indices: Shannon, Simpson and species richness estimators | 5 | |
| Extreme value analysis of rainfall and floods | 5 | |
| Spatial patterns: random, clumped and regular; dispersion indices | 4 | |
| Quadrat, line-transect and distance sampling | 4 | |
| Population dynamics models: logistic and Leslie matrix | 4 | |
| Fish stock assessment: growth (von Bertalanffy), mortality and yield-per-recruit | 4 | |
| Forest inventory: plot sampling, point sampling and volume estimation | 4 | |
| Environmental monitoring designs and trend detection | 4 | |
| Species-abundance and species-area models | 3 |
Choose an answer, then open the working. Each explanation says why the right answer is right and why the others are not.
The Clark–Evans nearest-neighbour ratio for a perfectly regular hexagonal pattern is about:
A. 2.15
1 indicates randomness, values below 1 clumping, and about 2.15 the maximum regularity.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
The critical assumption of conventional distance sampling is that:
A. Objects on the line are always seen
g(0) = 1; detection is allowed to fall with distance.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
If marked animals become trap-shy, the Lincoln–Petersen estimate will tend to be:
D. Too high
Fewer recaptures (smaller R) inflate MC/R.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
In closed-population capture–recapture model Mh, capture probability varies:
A. Among individuals
Mt varies by occasion and Mb by behaviour; M₀ is constant.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
Many singletons in a sample of a community suggest that:
D. Many species remain undetected
Chao estimators use singletons to estimate unseen species.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
Why do species–area extrapolations tend to overestimate immediate extinctions after habitat loss?
D. Species persist in the matrix; losses lag
The matrix is not an ocean, and extinction debts take time.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
In a Ford–Walford plot of Lₜ₊₁ against Lₜ, the slope equals:
D. e^(−K)
Where the line crosses Lₜ₊₁ = Lₜ gives L∞.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
Huber's formula estimates log volume as:
A. Mid-length area times length
Smalian's formula averages the end areas.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
The Weibull plotting position assigns the m-th largest of n annual maxima an exceedance probability of:
A. m/(n + 1)
It avoids assigning probability 0 or 1 to observed extremes.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
Why are 500-year return levels estimated from a 30-year record very uncertain?
A. They extrapolate far beyond the data
Confidence intervals widen rapidly beyond the record length; regional analysis helps.
Further reading: Krebs, Ecological Methodology (1999); Buckland et al., Introduction to Distance Sampling (2001); Magurran, Measuring Biological Diversity (2004); Sparre and Venema, FAO Fisheries Technical Paper 306/1 (1998); Coles, Statistical Modeling of Extreme Values (2001)
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