ASRB NET - Agricultural Statistics (and Computer Application / Bioinformatics) · India · Agricultural Scientists Recruitment Board (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 ASRB NET spread across the units of Statistical Ecology, Environmental & Fisheries Statistics. Difficulty: 1 easy, 19 medium, 1 hard.
| Spatial patterns: random, clumped and regular; dispersion indices | 3 | |
| Quadrat, line-transect and distance sampling | 2 | |
| Capture-recapture: Lincoln-Petersen and open-population models | 2 | |
| Diversity indices: Shannon, Simpson and species richness estimators | 2 | |
| Species-abundance and species-area models | 2 | |
| Population dynamics models: logistic and Leslie matrix | 2 | |
| Fish stock assessment: growth (von Bertalanffy), mortality and yield-per-recruit | 2 | |
| Forest inventory: plot sampling, point sampling and volume estimation | 2 | |
| Environmental monitoring designs and trend detection | 2 | |
| Extreme value analysis of rainfall and floods | 2 |
Choose an answer, then open the working. Each explanation says why the right answer is right and why the others are not.
For quadrat counts with mean 4 and variance 10, the moment estimate of the negative binomial k is about:
B. 2.7
k = x̄²/(s² − x̄) = 16/6 ≈ 2.67; small k means strong aggregation.
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 Taylor's power law s² = a x̄ᵇ, a value b > 1 indicates:
A. Aggregation that increases with density
b = 1 corresponds to Poisson-like variance; b > 1 to aggregation.
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)
Morisita's index is often preferred to the variance-to-mean ratio because it:
C. Quadrat size affects it less
Its value for a given pattern changes less with quadrat size.
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)
Animals that move away from the observer before being detected cause distance-sampling density estimates to be:
A. Biased
Detection at original positions is assumed; evasive movement typically biases density downwards.
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)
The same logic as capture–recapture is used for estimating human populations from overlapping lists, where it is called:
D. Multiple-systems estimation
Overlaps between lists play the role of recaptures.
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)
Compared with Simpson's index, Shannon's index is more sensitive to:
B. Rare species
Simpson's index weights common species heavily.
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)
Why do modern harvest strategies often target fishing levels below those giving MSY?
D. MSY is uncertain
Precautionary reference points allow for uncertainty and risk of collapse.
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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