01 · Means One-sample t test | Cell biologists measure oxygen consumption in independently cultured cell lines. | 24 | 1101 | The population mean is 10.8 nmol/min, so the reference-mean null of 10 is false; the true mean difference is +0.8. | Mean = 10.75 nmol/min; n = 24 t = 2.48; df = 23; p = 0.02107 | CSV |
02 · Means Pooled two-sample t test | Evolutionary biologists compare adult beetle body length from two rearing environments. | 56 | 1118 | The true Cool minus Warm mean difference is -0.7 mm, and the two population variances are both 0.4225 mm squared. | Cool - Warm mean difference = -1.02 mm Pooled t = -4.94; df = 54.00; p = 7.927e-06 | CSV |
03 · Means Welch two-sample t test | Evolutionary biologists compare adult beetle body length from two rearing environments. | 56 | 1102 | The true Cool minus Warm mean difference is -0.7 mm. Variances differ (0.4225 versus 1.3225 mm squared). | Cool - Warm mean difference = -1.01 mm Welch t = -4.21; df = 53.33; p = 9.973e-05 | CSV |
04 · Means Paired t test | Plant physiologists measure photosynthesis in the same leaves before and after heat stress. | 20 | 1103 | The mean after-minus-before difference is -1.3 photosynthesis units, even if this sample provides limited evidence against zero. | Mean change (after - before) = -0.73 Paired t = -1.91; df = 19; p = 0.07128 | CSV |
05 · Variance and diagnostics F test of two variances | Evolutionary developmental biologists compare variation in wing length between two inbred fly lines. | 60 | 1109 | Population means are equal, but the true variance ratio A/B is 0.11 squared / 0.21 squared, approximately 0.274. | Variance ratio (A / B) = 0.376 F = 0.376; df = 29, 29; p = 0.01048 | CSV |
06 · Variance and diagnostics Levene and Brown–Forsythe tests | Microbiologists compare the variability of colony diameters across three nutrient media. | 84 | 1110 | Group geometric means are 4 mm, but variances differ. Arithmetic means also vary slightly because log-normal means depend on log-scale spread. | Brown–Forsythe F = 5.55; df = 2, 81; p = 0.005524 Original Levene F = 9.72; p = 0.0001645 | CSV |
07 · Variance and diagnostics Shapiro–Wilk and graphical checks | Cell biologists examine the distribution of time to lysis among independent cultured cells. | 36 | 1111 | The population is log-normal and positively skewed, not normal. The population geometric mean is 45 minutes. | Shapiro–Wilk W = 0.937; p = 0.04064; n = 36 Curvature in the Q–Q plot indicates a shape mismatch. | CSV |
08 · Nonparametric alternatives Sign test | Behavioral biologists record the change in refuge-use time after a predator cue. | 30 | 1104 | Positive changes are more likely than negative changes. The unrounded mean is 4 seconds, but the sign test is about direction rather than that mean. | Positive changes: 18 of 30 nonzero differences Exact two-sided p = 0.3616 | CSV |
09 · Nonparametric alternatives Wilcoxon signed-rank test | Microbiologists compare log bacterial density before and after a treatment in matched cultures. | 28 | 1105 | The symmetric difference distribution is centered at +0.28 log10 units; its zero-center null is false. | Pseudomedian change estimate = 0.249 V = 328.0; p = 0.004582 | CSV |
10 · Nonparametric alternatives Wilcoxon rank-sum test | Ecologists compare parasite burdens among fish from two independent lakes. | 64 | 1106 | The lake distributions differ, including their mean and spread. The same-distribution null is false; there is not a simple equal-shape location shift. | Observed medians: Clear 3.0; Reedy 8.0 parasites W = 362.5; asymptotic p = 0.04452 | CSV |
11 · ANOVA One-way ANOVA | Ecologists compare seedling biomass under three independent soil treatments. | 75 | 1117 | The equal-means null is false. All three populations share variance 0.85 squared; Loam minus Sand is truly 0.9 g. | Ordinary ANOVA F(2, 72) = 11.59; p = 4.335e-05 Welch ANOVA F = 8.89; denominator df = 46.37; p = 0.0005408 | CSV |
12 · ANOVA Welch one-way ANOVA | Ecologists compare seedling biomass under three independent soil treatments. | 78 | 1119 | The true means differ, and variances differ (0.36, 1.21, and 2.25 g squared). Welch addresses the equal-means null without a shared variance. | Welch ANOVA F = 13.65; df = 2, 49.85; p = 1.873e-05 Group sample sizes: Sand 20; Loam 26; Clay 32 | CSV |
13 · Nonparametric alternatives Kruskal–Wallis test | Plant pathologists score leaf damage in three independently assigned pathogen treatments. | 72 | 1107 | The score distributions differ across all three generating probabilities; expected scores are 2.0, 3.2, and 4.64. The equal-distributions null is false. | Kruskal–Wallis chi-square = 35.75; df = 2; p = 1.73e-08 Observed medians: Control 2; Strain A 3; Strain B 4.5 | CSV |
14 · ANOVA and contrasts Factorial ANOVA: interactions | Beetle larvae from two genotypes are independently reared at two temperatures. | 88 | 2101 | The temperature effect is 2 mg/week in genotype A and 4.3 mg/week in B, so the interaction is 2.3 mg/week. The interaction null is false. | Interaction = 4.30 mg/week t(84) = 5.69; p = 1.78e-07 | CSV |
15 · ANOVA and contrasts ANCOVA: an adjusted group comparison | Plant ecologists compare nutrient treatment while accounting for initial plant height. | 90 | 2102 | The nutrient treatment increases the population mean biomass by 2.4 g at any shared initial height. Both groups have slope 1.5 g/cm. The adjusted treatment null is false. | Adjusted nutrient minus control = 2.65 g t(87) = 6.55; p = 3.797e-09 | CSV |
16 · Repeated and clustered data Repeated-measures ANOVA | Physiologists measure the same animals at four assay temperatures. | 96 | 2103 | Population means are 8, 9.75, 11.5 and 13.25 µmol/hour. The endpoint difference is 5.25 µmol/hour and the equal-means null is false. | Condition F(3, 69) = 84.32 Omnibus p = 4.966e-23 | CSV |
17 · Nonparametric alternatives Friedman test | Sensory biologists record activity scores from each insect under three light conditions. | 54 | 1108 | Condition effects exist before rounding (0, +0.8, +1.6), and condition score distributions differ after rounding. Repeated observations share an insect baseline. | Independent blocks = 18; conditions = 3 Friedman chi-square = 17.63; df = 2; p = 0.0001482 | CSV |
18 · ANOVA and contrasts Tukey / Tukey–Kramer comparisons | Plant growth is compared across four nutrient regimes. | 80 | 2104 | Population means for A–D are 8, 9, 11.3 and 12.1 g; all distinct pairwise mean-equality nulls are false. | Family: all six pairwise nutrient comparisons Tukey-adjusted p = 0.0415 | CSV |
19 · ANOVA and contrasts Fisher least significant difference | Plant growth is compared across four nutrient regimes. | 80 | 2104 | Population means for A–D are 8, 9, 11.3 and 12.1 g; all distinct pairwise mean-equality nulls are false. | Omnibus p = 5.683e-12 Unadjusted p = 0.05163 | CSV |
20 · ANOVA and contrasts Scheffé contrasts | Plant growth is compared across four nutrient regimes. | 80 | 2104 | Population means for A–D are 8, 9, 11.3 and 12.1 g; all distinct pairwise mean-equality nulls are false. The specified (C+D)/2 − (A+B)/2 contrast equals 3.2 g. | Contrast: (C + D)/2 − (A + B)/2 Scheffé-adjusted p = 9.177e-11 | CSV |
21 · Rank methods Dunn rank comparisons | Ecologists compare skewed leaf-damage measurements among four treatments. | 84 | 2105 | Group distributions differ; their population medians are exp(1.2), exp(1.3), exp(1.7) and exp(1.9) mm². Dunn tests pooled-rank tendencies, not arithmetic mean equality. The distributions also differ in original-scale spread. | Kruskal–Wallis p = 1.352e-05 Two-sided Holm-adjusted p = 0.0001018 | CSV |
22 · Association Pearson correlation | Evolutionary biologists measure wing and tail lengths in adult birds from a single population. | 45 | 1112 | The generating population Pearson correlation is 0.55*5 / sqrt((0.55*5)^2 + 3.5^2), approximately 0.618. It is not the observed sample correlation. | Pearson r = 0.700 t = 6.43; df = 43; p = 8.606e-08 | CSV |
23 · Nonparametric alternatives Spearman rank correlation | Microbial ecologists compare soil salinity with bacterial richness across independent soil cores. | 45 | 1113 | The underlying mean response decreases nonlinearly with salinity, creating a negative monotonic association. No fixed numeric population Spearman coefficient was specified. | Spearman rho = -0.752; n = 45 S = 26599.8; asymptotic two-sided p = 2.549e-09 | CSV |
24 · Regression Simple linear regression | Plant ecologists grow seedlings under a gradient of nitrogen supply. | 36 | 1114 | The conditional mean intercept is 2.2 g and slope is +0.42 g per mg nitrogen. The zero-slope null is false. | Slope = 0.414 g biomass per mg nitrogen Slope t = 9.90; df = 34; p = 1.525e-11 | CSV |
25 · Regression Multiple linear regression | Evolutionary biologists relate beetle horn length to body size and larval nutrition. | 60 | 1115 | The true conditional body slope is 0.35 mm/mm and nutrition slope 0.16 mm/mg, with no interaction. Both zero-coefficient nulls are false. | Body slope, adjusted for nutrition = 0.299 mm/mm Body coefficient p = 7.658e-05; nested-model F = 18.17 | CSV |
26 · Regression Theil–Sen robust slope | Physiologists measure enzyme activity along a temperature gradient with occasional unusually high assays. | 40 | 1116 | The underlying uncontaminated linear trend has slope 1.4 U/mL per degree C. Two deliberately elevated assays illustrate robustness; the bootstrap interval comes from the saved contaminated sample. | Theil–Sen slope = 1.408 U/mL per degree C 95% pairs-bootstrap interval: 1.184 to 1.618 | CSV |
27 · Proportions and categories Exact binomial test | Host choice in a parasitoid wasp | 80 | 3101 | The true native-host probability is 0.68, so the null probability 0.50 is false. The population difference from the null is +0.18. | Native-host choices: 51 / 80 Exact two-sided p = 0.01832 | CSV |
28 · Proportions and categories One-proportion test | Germination of salt-tolerant seeds | 120 | 3102 | The true germination probability is 0.67 rather than the null benchmark 0.50; the population difference is +0.17. | Germination: 70 / 120 Two-sided p = 0.06789 | CSV |
29 · Proportions and categories Two-proportion test | Heat survival in evolved and ancestral yeast | 220 | 3103 | Evolved minus ancestral survival probability is 0.20, so the equal-probabilities null is false. The corresponding population odds ratio is approximately 2.37. | Evolved: 78 / 110; ancestral: 61 / 110 Two-sided p = 0.01748 | CSV |
30 · Proportions and categories Chi-square goodness-of-fit | Segregation in an F2 cross | 240 | 3104 | The simulated probabilities differ from 1:2:1 by -0.07, +0.04, and +0.03. The goodness-of-fit null is false. | Observed: 43, 128, 69 p = 0.03508 | CSV |
31 · Proportions and categories Chi-square test of independence | Infection across three lizard habitats | 270 | 3105 | Infection probability depends on habitat, so the independence null is false. Urban minus forest infection probability is 0.30; the simulation does not assign causality to habitat. | Infection probabilities: Forest 0.14; Grassland 0.41; Urban 0.54 p = 1.042e-07; Cramer V = 0.345 | CSV |
32 · Proportions and categories Fisher exact test | Survival of rare resistant and susceptible clones | 24 | 3106 | The resistant-to-susceptible population survival odds ratio is (0.65/0.35)/(0.20/0.80), approximately 7.43. The odds-ratio-one null is false. | Survivors: susceptible 2/12; resistant 7/12 Two-sided exact p = 0.08938 | CSV |
33 · Paired binary outcomes McNemar test | Antibody detection before and after an exposure season | 80 | 3107 | Marginal after positivity is 0.45×0.85 + 0.55×0.35 = 0.575, a +0.125 change from before. Population gain and loss probabilities are 0.1925 and 0.0675, so the McNemar null is false. | Gained detection: 10; lost detection: 5 McNemar p = 0.1967; exact paired p = 0.3018 | CSV |
34 · Paired binary outcomes Cochran’s Q test | Bee visits to three floral odors | 180 | 3108 | Increasing odor effects produce strictly increasing marginal visit probabilities across A, B, and C. The equal-probabilities null is false; the latent log-odds differences are not themselves the marginal probability differences. | Matched bees: 60; conditions: 3 Omnibus p = 0.07643 | CSV |
35 · Generalized linear models Logistic regression | Hybrid viability across parental divergence | 160 | 3110 | The true divergence coefficient is -0.5; viability odds are multiplied by exp(-0.5) ≈ 0.607 per divergence percentage point. The zero-slope null is false. The probability decline is nonlinear. | Divergence coefficient: -0.464 Likelihood-ratio p = 6.573e-09 | CSV |
36 · Counts and exposure Exact Poisson rate test | De novo mutations in sequenced microbial lineages | 60 | 3109 | The true rate is 0.40 mutations/Mb rather than the null rate 0.25/Mb. The population rate ratio to the null is 1.6. | Events: 345; exposure: 845.0 Mb Exact p = 3.246e-17 | CSV |
37 · Generalized linear models Poisson regression | Coral recruit counts and live coral cover | 120 | 3111 | The true cover coefficient is 0.016. A 10-point cover increase multiplies recruit density by exp(0.16) ≈ 1.174. The zero-slope null is false, and the exposure coefficient is fixed at one. | Rate ratio per 10 cover points: 1.200 Likelihood-ratio p = 2.64e-30 | CSV |
38 · Generalized linear models Quasi-Poisson regression | Bacterial colony counts with clumping | 120 | 3113 | High medium multiplies mean colony density by exp(0.5) ≈ 1.649; the equal-rate null is false. The true dispersion multiplier is 4, so Poisson uncertainty would be too small. | High / low mean rate ratio: 1.351 Quasi-Poisson t-test p = 0.002166 | CSV |
39 · Generalized linear models Negative binomial regression | Parasite abundance and fish body length | 130 | 3112 | The length coefficient is 0.085, so 5 cm multiplies expected parasite abundance by exp(0.425) ≈ 1.530. The slope-zero null is false; the Poisson variance assumption is intentionally violated. | Mean count ratio per 5 cm: 1.602 Wald p = 1.634e-22 | CSV |
40 · Generalized linear models Multinomial logistic regression | Fish use of three unordered feeding microhabitats | 240 | 3114 | The outcome distributions differ, so the joint no-food-effect null is false. Relative to Open, the food coefficients are log(0.30/0.50)-log(0.50/0.25) ≈ -1.204 for Shelter and log(0.20/0.50)-log(0.25/0.25) ≈ -0.916 for Surface. | Low-food probabilities: 0.217, 0.508, 0.275 Joint p = 6.115e-05 | CSV |
41 · Generalized linear models Ordinal logistic regression | Coral bleaching severity along a temperature gradient | 180 | 3115 | The common temperature coefficient is 0.8, so each °C multiplies odds of higher versus lower severity by exp(0.8) ≈ 2.226 at every cumulative threshold. The zero-effect null is false and proportional odds holds by construction. | Common odds ratio per 1°C: 2.613 p = 4.544e-23 | CSV |
42 · Repeated and clustered data Linear mixed model | Evolutionary biologists follow larval growth under two diets. | 144 | 2106 | The control slope is 2 mg/week; enrichment adds 0.9 mg/week. The diet-by-week null is false. Simulated random-intercept and slope SDs are 2.3 mg and 0.7 mg/week. | Growth-slope difference = 0.79 mg/week Satterthwaite df = 34.0; t = 3.20; p = 0.002966 | CSV |
43 · Repeated and clustered data Binary mixed model | Immunologists record repeated infection outcomes in vaccinated and control hosts. | 288 | 2107 | The conditional vaccine odds ratio is exp(−1) ≈ 0.368; the week odds ratio is exp(0.25) ≈ 1.284. The vaccine null is false. These are conditional effects, not population-average odds ratios. | Conditional vaccine odds ratio = 0.24 Wald z = -3.99; p = 6.63e-05 | CSV |
44 · Repeated and clustered data Count mixed model: Poisson and negative binomial | Pollinator visits are repeatedly counted on plants in two habitats. | 192 | 2114 | The conditional sheltered/open rate ratio is exp(0.55) ≈ 1.733; the habitat null is false. The generating distribution has extra variation beyond Poisson even after conditioning on the plant intercept. | Conditional sheltered/open rate ratio = 1.50 Wald z = 2.62; p = 0.008759 | CSV |
45 · Repeated and clustered data Ordinal mixed model | Fish behavior is scored repeatedly using ordered stress categories. | 210 | 2109 | The conditional common odds ratio for a higher score under stress is exp(0.8) ≈ 2.226. The treatment null is false. The simulated thresholds obey proportional odds. | Conditional higher-score odds ratio = 2.51 Wald z = 2.78; p = 0.005491 | CSV |
46 · Dependent observations Binary generalized estimating equations | Repeated infection screening after vaccination | 320 | 3116 | The true population-average vaccination coefficient is -0.9 and odds ratio exp(-0.9) ≈ 0.407, adjusted for week. The no-group-effect null is false. The true marginal week coefficient is 0.35. A working exchangeable correlation is an approximation, while the marginal mean model is exact. | Independent animals: 80; observations: 320 Robust Wald p = 0.06864 | CSV |
47 · Time to event Kaplan–Meier survival estimation | Ecologists follow seedling survival until death or final observation. | 120 | 2110 | The population survival function is exp(−0.018 × days); true day-40 survival is exp(−0.72) ≈ 0.487. This is an estimation target, not a null hypothesis. | 120 seedlings; 79 events; 41 censored Estimated survival at day 40 = 0.455 | CSV |
48 · Time to event Log-rank survival comparison | Plant pathologists compare time to infection under three protective treatments. | 150 | 2111 | Equal survival is false: day-30 infection-free probabilities are exp(−1.35) ≈ 0.259, exp(−0.9) ≈ 0.407 and exp(−0.54) ≈ 0.583. The high/control hazard ratio is 0.4, though the log-rank test itself does not estimate it. | Log-rank chi-square(2) = 17.18 Omnibus p = 0.0001863 | CSV |
49 · Survival Stratified log-rank test | Larval survival under stress is compared within 12 rearing blocks. | 120 | 240501 | Stress has a true hazard ratio of 1.6 within each block; the within-block equality null is false. | Stratified chi-square = 13.433 p = 0.0002472 | CSV |
50 · Time to event Cox proportional-hazards regression | Seedling death times are related to protective dose and temperature. | 180 | 2112 | The adjusted hazard ratio per dose unit is exp(−0.45) ≈ 0.638; per °C it is exp(0.12) ≈ 1.127. The dose null is false and proportional hazards holds in the generating model. | Dose hazard ratio per unit = 0.69 Wald z = -3.72; p = 0.0001969 | CSV |
51 · Time to event Parametric survival: accelerated failure time | Botanists compare germination timing after control or cold treatment. | 140 | 2113 | The population cold/control time ratio is exp(0.4) ≈ 1.492, so the equal-time null is false. The generating Weibull distribution matches the fitted AFT family. | Cold/control time ratio = 1.70 Wald z = 4.54; p = 5.745e-06 | CSV |
52 · Survival Shared-frailty survival model | Larvae from 24 populations experience a control or stress condition. | 240 | 240502 | The conditional stress hazard ratio is exp(0.5) ≈ 1.65; shared population variance is 0.5. | Conditional hazard ratio = 1.61 Wald p = 0.002373 | CSV |
53 · Simulation and multivariate methods Independent-sample permutation test | Independent insect larvae are randomly assigned to ambient or warm rearing. | 50 | 240503 | The simulated warm-minus-control mean difference is 1.1 mm; the same-distribution null is false. | Warm − control = 0.72 mm Two-sided Monte Carlo p = 0.187 | CSV |
54 · Simulation and multivariate methods Paired permutation test | Two comparable leaves per plant receive randomized control or shade treatment. | 28 | 240504 | The true mean shaded-minus-control difference is −1.2; plants also differ in their shared baseline. | Shaded − control = -0.97 units Two-sided permutation p = 0.0006 | CSV |
55 · Simulation and multivariate methods Monte Carlo null-model test | Test whether candidate sex-determination genes are unusually concentrated on the X chromosome. | 80 | 240505 | The true occupancy probability is 0.32, so the tested 0.20 null is false. | Observed on X: 32 of 80 Two-sided Monte Carlo p = 0.0002 | CSV |
56 · Simulation and multivariate methods Bootstrap confidence interval | Estimate average biomass from independent bacterial colonies with a right-skewed distribution. | 40 | 240507 | The population arithmetic mean is approximately 13.28 mg; the interval may or may not cover it in one sample. | Sample mean = 11.54 mg Percentile 95% CI = 10.15 to 13.07 mg | CSV |
57 · Simulation and multivariate methods Sampling variation and CI coverage | Independent cell cultures differ in the waiting time to a developmental transition. | 25000 | 240506 | The population mean is exactly 5 days; nominal 95% coverage is a procedure property to evaluate, not an imposed simulation result. | Mean estimated waiting time: 5.03 days Observed 95% t-interval coverage: 92.6% | CSV |
58 · Multiple testing Bonferroni correction | Compare gene expression between two conditions across 40 genes. | 960 | 240508 | The first eight genes have true mean effects of 1.1 log2 units; the other 32 nulls are true. | Unadjusted p<.05: 8 genes Adjusted p<.05: 2 genes | CSV |
59 · Multiple testing Benjamini–Hochberg FDR | Compare gene expression between two conditions across 40 genes. | 960 | 240509 | The first eight genes have true mean effects of 1.1 log2 units; the other 32 nulls are true. | Unadjusted p<.05: 7 genes Adjusted p<.05: 3 genes | CSV |
60 · Multivariate exploration Principal component analysis | Four correlated morphological traits are measured in beetles from three ecotypes. | 75 | 240510 | Groups differ in body-size means and antenna shifts; all traits share a common body-size component. | PC1 accounts for 84.3% of variance PC2 accounts for 8.6% | CSV |
61 · Multivariate exploration Classical multidimensional scaling | Four correlated morphological traits are measured in beetles from three ecotypes. | 75 | 240511 | Groups differ in body-size means and antenna shifts; all traits share a common body-size component. | Two-dimensional goodness of fit: 0.920 Euclidean distances between standardized traits | CSV |
62 · Multivariate exploration Linear discriminant analysis | Four correlated morphological traits are measured in beetles from three ecotypes. | 75 | 240512 | Groups differ in body-size means and antenna shifts; all traits share a common body-size component. | Leave-one-out classification accuracy: 82.7% Three known ecotype labels used during training | CSV |
63 · Dependent observations Count and rate GEE | Microbial ecologists count bacterial colonies in repeated water samples from experimental pond mesocosms. | 360 | 1401 | The exact population-average Warm / Ambient rate ratio is exp(0.45), approximately 1.568; the equal-rate null is false. Each week multiplies the marginal rate by exp(0.1), approximately 1.105. Marginal count variance is mu + 0.5 × mu squared. The working exchangeable correlation is approximate, while the specified marginal mean is exact. | Independent mesocosms: 90; observations: 360 Robust Wald p = 0.00243 | CSV |