Scat Diet Composition Calculator – Free Carnivore Diet Tool

Scat Diet Composition Calculator – Free Carnivore Diet Tool

📥 Step 1 — Enter Your Scat Diet Data

Comma-separated (default). One value per prey item. Example: 52, 48, 55, 61, 47 means 52 scats contained Prey 1, 48 contained Prey 2, etc.

Headers detected automatically. After upload, choose which column contains the prey item names and which contains the scat counts.

⚙️ Step 2 — Configure Analysis

If left blank, calculated from your data assuming each value is "scats containing item".

Items below this %FO are flagged as minor / incidental prey.

📊 Step 3 — Summary Results

Scat Diet Composition Equations

Two complementary metrics describe diet composition from scat:

%FOi = niN × 100
%POi = ni∑ nj × 100
  • %FOi: Frequency of occurrence of prey item i (% of scats containing item i)
  • %POi: Percent occurrence of prey item i (share of all prey hits)
  • ni: Number of scats containing prey item i
  • N: Total number of scats analysed
  • nj: Sum of all prey occurrences across every prey item
  • Note: %FO can sum to > 100% (one scat may contain multiple prey items); %PO sums to 100%.

📋 Full Diet Composition Table

# Prey Item Scats with Item (n) %FO %PO Diet Tier

🏆 Top Prey Spotlight

The single most important prey item identified in the diet — a hero callout you can drop straight into a presentation or report.

🎯 Diet Tier Breakdown

Prey items grouped by their dietary importance class. PRIMARY items are dominant (≥50% of scats); SECONDARY items are common; INCIDENTAL items are rare or scavenged.

📐 Advanced Diet Diversity Metrics

Standard ecological diversity indices computed on %PO. Useful for cross-study comparison and reviewer requests.

📖 What do these metrics mean?
  • Shannon-Wiener H' — combines richness and evenness; higher = more diverse diet. Typical range 0–3.5.
  • Simpson's D — probability that two randomly chosen prey hits are the same species; lower = more diverse.
  • Inverse Simpson (1/D) — effective number of equally-common prey items.
  • Pielou's J' — evenness on 0–1 scale; 1 = perfectly even, < 0.5 = highly skewed diet.
  • Berger-Parker d — proportion of the most dominant prey item; complements diet skew.
  • Margalef's DMg — richness corrected for sample size.
  • Hill N₁ & N₂ — effective species numbers (exp(H') and 1/D respectively).
  • Levins' B (standardised BA) — niche breadth; BA > 0.6 = generalist, < 0.4 = specialist.

⚖️ Diet Niche Breadth (Levins' Standardised B)

Where this carnivore sits on the specialist–generalist continuum. Standardised Levins' B (BA) ranges from 0 (perfect specialist on one prey) to 1 (perfect generalist).

BA
0 — Specialist 0.5 — Mixed 1 — Generalist

📈 Statistical Confidence & Significance

Wilson 95% confidence interval for the dominant prey's %FO, plus a chi-square goodness-of-fit test against a uniform-diet null hypothesis.

95% Confidence Interval — Dominant Prey %FO

Chi-Square Test — Uniform Diet Null Hypothesis

🗂️ Quick Reference Summary

All key numbers in one glance — handy for citing in a manuscript or pasting into a results table.

📌 At-a-Glance

📤 Export Results

📎 Copy Summary to Clipboard

🔬 Detailed Interpretation Results

📝 How to Write Your Results in Research

Five ready-to-use reporting templates plus a research poster panel — auto-filled with your computed values.

🔍 Detailed Conclusion

📊 What Was Found

🌱 Ecological Significance

🌿 Conservation & Management Implications

    🔭 Next Steps & Methodological Guidance

    🎯 Take-Home Synthesis

    🧮 Technical Notes — Formulas, Assumptions & Limitations

    Extended Formula Derivation

    The two core diet composition metrics share the same numerator (ni) but differ in their denominator. Frequency of occurrence (%FO) uses the total number of scat samples (N) as the denominator, treating each scat as a Bernoulli trial that either contains or does not contain prey item i. Percent occurrence (%PO) uses the sum of all prey hits across all items (∑nj), so each prey item's share is normalised to total prey occurrences rather than to total scats.

    Because a single scat can contain multiple prey items, the sum of %FO across all prey items often exceeds 100%, while the sum of %PO is always exactly 100%. This is why both metrics should be reported together — %FO answers "how many scats contained this prey?" while %PO answers "what fraction of the diet does this prey item make up?"

    Assumptions

    • Scats are correctly identified to the predator species (use genetic confirmation when sympatric carnivores overlap).
    • Prey remains are correctly identified from hair, bone, feather, scale, or seed fragments.
    • Differential digestion among prey is not corrected for in raw %FO and %PO — small/soft prey may be under-detected.
    • Sampling effort is sufficient to reach the asymptote of a cumulative prey-item curve (typically ≥ 50–100 scats).
    • Each scat is treated as an independent observation; collect across spatial and temporal replicates to avoid pseudo-replication.

    Limitations

    • %FO and %PO do not estimate biomass consumed — large prey items contribute disproportionately to nutrition but may appear in fewer scats.
    • Highly digestible prey (e.g., small mammals consumed whole) may be over-represented relative to large prey.
    • Hair-only identification cannot distinguish scavenging from predation.
    • Insect remains may be over-represented because of their indigestible chitinous exoskeletons.
    • For biomass-corrected estimates, apply correction factors from Floyd, Mech & Jordan (1978) or Ackerman, Lindzey & Hemker (1984).
    🎯 When to Use This Tool — Decision Checklist

    Use this calculator when:

    • ✓ You have collected scats from a known predator species and identified prey remains in each sample.
    • ✓ You want to summarise diet composition as %FO and %PO for a manuscript, thesis, or report.
    • ✓ You want to compare diet between seasons, sites, or sex/age classes within a species.
    • ✓ Your sampling effort is at or near the cumulative prey-item asymptote (typically ≥ 50 scats).

    Do NOT use this calculator when:

    • ✗ Sample sizes are very small (< 30 scats) — confidence intervals become uninformative.
    • ✗ You need biomass estimates — apply published correction factors first.
    • ✗ You want to test diet selectivity — combine with prey-availability data and use Manly's α or Ivlev's E.
    • ✗ Predator species identification is uncertain — confirm scat origin with genetic methods.

    Real-world USA examples:

    1. Coyote diet in Yellowstone (Wyoming) — quantifying ungulate vs small-mammal contributions across summer and winter.
    2. Bobcat scat analysis in Texas Hill Country — assessing the role of cottontail and small rodents during drought years.
    3. Gray wolf diet on Isle Royale (Michigan) — long-term moose dependency and beaver subsidy.
    4. Mountain lion scat in Idaho — evaluating mule deer reliance versus elk during winter.

    Sampling design guidance:

    • Collect 50–100 scats per season per site.
    • Plot a cumulative prey-item curve to confirm sample size adequacy.
    • Stratify by season and habitat type to capture diet shifts.
    • Store scats frozen or in alcohol; process under sterile conditions.
    📚 How to Use This Tool — Step-by-Step Guide
    1. Enter your data — Paste scat counts (e.g., 52, 48, 55, 61, 47) into the textarea, or use Column Entry for labelled prey items, or upload a CSV/Excel file.
    2. Choose a sample dataset — Five USA carnivore datasets are pre-loaded for testing.
    3. Set the study area — Optional but recommended; populates reporting templates and the PDF cover.
    4. Edit the group name — Default is "Coyote (Canis latrans)"; change to your study species.
    5. Enter total scats (N) — Required for %FO calculation; defaults to the dataset's reported N.
    6. Configure thresholds — Choose diet-diversity threshold and minor-prey cutoff.
    7. Click "Run Scat Diet Analysis" — Computes %FO and %PO for every prey item, with diet tier classification.
    8. Read the four colourful charts — %FO bar, %PO donut, cumulative contribution, and diet profile scatter.
    9. Read the diet composition table — Each row shows raw count, %FO, %PO, and diet tier (primary/secondary/incidental).
    10. Read the detailed interpretation and conclusion — Plain-language paragraphs with study area substitution.
    11. Copy a reporting example — Five styles (ecology journal, thesis, plain-language, conference abstract, monitoring) plus a research poster panel.
    12. Export — Download Doc (.txt) or PDF for archiving.

    ❓ Frequently Asked Questions

    What is scat diet composition analysis?
    Scat diet composition is the quantitative description of what a carnivore or omnivore eats, based on identifying undigested prey remains — hair, bone, feathers, scales, seeds, insect parts — in faecal samples. It is one of the least invasive and most widely used methods for studying carnivore feeding ecology in the field.
    What is %FO and how is it calculated?
    %FO (frequency of occurrence) is the percentage of scat samples that contain a given prey item: %FOi = (ni / N) × 100, where ni is the number of scats containing item i and N is the total number of scats analysed.
    What is %PO and how does it differ from %FO?
    %PO (percent occurrence) normalises each prey item's count by the sum of all prey occurrences: %POi = (ni / ∑nj) × 100. While %FO can sum to more than 100% (one scat may contain multiple prey items), %PO sums to exactly 100%.
    Should I report %FO, %PO, or both?
    Best practice is to report both. %FO answers "how often does this prey appear in scats?" while %PO answers "what share of total prey hits does this item make up?" Modern carnivore-diet papers typically report both alongside sample size N and the season of collection.
    How many scat samples are needed for a reliable diet study?
    A minimum of 50–100 scats per season is recommended for terrestrial carnivores. Always plot a cumulative prey-item discovery curve and confirm it has reached an asymptote before drawing dietary conclusions.
    How do I distinguish predation from scavenging in scat?
    Scat analysis alone cannot distinguish scavenging from predation. Combine scat-based diet composition with kill-site investigations, GPS-cluster analysis, or stable-isotope ratios for a complete picture of feeding ecology.
    Can I use this for omnivores like black bears?
    Yes. The tool works for any carnivore or omnivore with identifiable food remains in scat. For omnivores, food categories typically include vertebrate prey, insects, fruit/berries, and vegetation — any of these can be entered as separate items.
    How are biomass estimates calculated and why aren't they shown here?
    Biomass estimates require species-specific correction factors (e.g., Floyd, Mech & Jordan 1978 for wolves; Ackerman, Lindzey & Hemker 1984 for mountain lions). These convert %FO of identified prey into estimated biomass consumed. The current tool reports raw %FO and %PO; apply correction factors externally if biomass is required.
    What software can I use to compare two scat datasets statistically?
    For comparing diet composition between two groups (sites, seasons, sexes), use chi-square tests, Fisher's exact test, or Pianka's overlap index. In R, the spaa or vegan packages provide straightforward implementations.
    Is this tool free to use for graduate research?
    Yes. This calculator is free to use for any academic, conservation, government, or non-profit research. If you publish results derived using this tool, please cite it as: Stats Unlock (2026). Scat Diet Composition Calculator. https://statsunlock.com/scat-diet-composition-calculator

    📚 References

    The following references support the methods used in this scat diet composition calculator, covering frequency of occurrence, percent occurrence, and best practices in carnivore feeding ecology across USA wildlife studies.

    1. Floyd, T. J., Mech, L. D., & Jordan, P. A. (1978). Relating wolf scat content to prey consumed. Journal of Wildlife Management, 42(3), 528–532. https://doi.org/10.2307/3800814
    2. Ackerman, B. B., Lindzey, F. G., & Hemker, T. P. (1984). Cougar food habits in southern Utah. Journal of Wildlife Management, 48(1), 147–155. https://doi.org/10.2307/3808462
    3. Klare, U., Kamler, J. F., & Macdonald, D. W. (2011). A comparison and critique of different scat-analysis methods for determining carnivore diet. Mammal Review, 41(4), 294–312. https://doi.org/10.1111/j.1365-2907.2011.00183.x
    4. Litvaitis, J. A. (2000). Investigating food habits of terrestrial vertebrates. In L. Boitani & T. K. Fuller (Eds.), Research techniques in animal ecology (pp. 165–190). Columbia University Press. Columbia University Press
    5. Reynolds, J. C., & Aebischer, N. J. (1991). Comparison and quantification of carnivore diet by faecal analysis: a critique, with recommendations, based on a study of the fox Vulpes vulpes. Mammal Review, 21(3), 97–122. https://doi.org/10.1111/j.1365-2907.1991.tb00113.x
    6. Ciucci, P., Boitani, L., Pelliccioni, E. R., Rocco, M., & Guy, I. (1996). A comparison of scat-analysis methods to assess the diet of the wolf Canis lupus. Wildlife Biology, 2(1), 37–48. https://doi.org/10.2981/wlb.1996.006
    7. Trites, A. W., & Joy, R. (2005). Dietary analysis from fecal samples: How many scats are enough? Journal of Mammalogy, 86(4), 704–712. https://doi.org/10.1644/1545-1542(2005)086[0704:DAFFSH]2.0.CO;2
    8. Bartnick, T. D., Van Deelen, T. R., Quigley, H. B., & Craighead, D. (2013). Variation in cougar (Puma concolor) predation habits during wolf (Canis lupus) recovery in the southern Greater Yellowstone Ecosystem. Canadian Journal of Zoology, 91(2), 82–93. https://doi.org/10.1139/cjz-2012-0147
    9. Vanak, A. T., & Gompper, M. E. (2009). Dietary niche separation between sympatric free-ranging domestic dogs and Indian foxes in central India. Journal of Mammalogy, 90(5), 1058–1065. https://doi.org/10.1644/09-MAMM-A-107.1
    10. Spaulding, R., Krausman, P. R., & Ballard, W. B. (2000). Observer bias and analysis of gray wolf diets from scats. Wildlife Society Bulletin, 28(4), 947–950. JSTOR 3783847
    11. Mukherjee, S., Goyal, S. P., & Chellam, R. (1994). Standardisation of scat analysis techniques for leopard (Panthera pardus) in Gir National Park, western India. Mammalia, 58(1), 139–143. https://doi.org/10.1515/mamm.1994.58.1.139
    12. Hayward, M. W., Henschel, P., O'Brien, J., Hofmeyr, M., Balme, G., & Kerley, G. I. H. (2006). Prey preferences of the leopard (Panthera pardus). Journal of Zoology, 270(2), 298–313. https://doi.org/10.1111/j.1469-7998.2006.00139.x
    13. R Core Team. (2024). R: A language and environment for statistical computing. R Foundation for Statistical Computing. https://www.R-project.org/
    14. Oksanen, J., Simpson, G. L., Blanchet, F. G., et al. (2022). vegan: Community ecology package. R package version 2.6-4. https://CRAN.R-project.org/package=vegan
    15. Stats Unlock. (2026). Scat Diet Composition Calculator. https://statsunlock.com/scat-diet-composition-calculator

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