FAILURE MAP

Understand the failure.
Verify the repair.

Small, reproducible software failures. The broken implementation, the fix that didn’t work, and the one that passed—preserved together.

Explore the cases ↓How results are verified ↗
100840Executable case variants
20168Distinct failure mechanisms
302520Executed implementations
20168Open-access cases

WHAT THE ARCHIVE CONTAINS

100840 executable cases. 20168 are open.

Every case records the implementation that fails, the fix that did not work, and the repair that passed its checks—with recorded outputs and source hashes. This release adds 100840 cases across 20168 failure mechanisms and 254 domains.

The open tier gives you the failure and the unsuccessful fix for one case in every mechanism. The remaining 80672 cases, 5 variants per mechanism, are member-only: the verified repair, its recorded checks, and the full fixture suite are held in the member archive. Read the methodology ↗

A RECORD OF WHAT WENT WRONG

Browse the archive / 100840

Python · Standard library
REFERENCEFAILURE MECHANISMDOMAINACCESS
FA-65701

Two-patch source-sink dispersal with ceilings: ceiling ordering · case 01

Excess recruits above the ceiling disperse into the other patch.

Ecological population dynamics● Open access↗
FA-65702

Two-patch source-sink dispersal with ceilings: ceiling ordering · case 02

Excess recruits above the ceiling disperse into the other patch.

Ecological population dynamics◈ Members↗
FA-65703

Two-patch source-sink dispersal with ceilings: ceiling ordering · case 03

Excess recruits above the ceiling disperse into the other patch.

Ecological population dynamics◈ Members↗
FA-65704

Two-patch source-sink dispersal with ceilings: ceiling ordering · case 04

Excess recruits above the ceiling disperse into the other patch.

Ecological population dynamics◈ Members↗
FA-65705

Two-patch source-sink dispersal with ceilings: ceiling ordering · case 05

Excess recruits above the ceiling disperse into the other patch.

Ecological population dynamics◈ Members↗
FA-65706

Two-patch source-sink dispersal with ceilings: dispersal conservation · case 01

Dispersal creates individuals.

Ecological population dynamics● Open access↗
FA-65707

Two-patch source-sink dispersal with ceilings: dispersal conservation · case 02

Dispersal creates individuals.

Ecological population dynamics◈ Members↗
FA-65708

Two-patch source-sink dispersal with ceilings: dispersal conservation · case 03

Dispersal creates individuals.

Ecological population dynamics◈ Members↗
FA-65709

Two-patch source-sink dispersal with ceilings: dispersal conservation · case 04

Dispersal creates individuals.

Ecological population dynamics◈ Members↗
FA-65710

Two-patch source-sink dispersal with ceilings: dispersal conservation · case 05

Dispersal creates individuals.

Ecological population dynamics◈ Members↗
FA-65711

Two-patch source-sink dispersal with ceilings: dispersal base · case 01

Dispersal numbers ignore this year's reproduction.

Ecological population dynamics● Open access↗
FA-65712

Two-patch source-sink dispersal with ceilings: dispersal base · case 02

Dispersal numbers ignore this year's reproduction.

Ecological population dynamics◈ Members↗
FA-65713

Two-patch source-sink dispersal with ceilings: dispersal base · case 03

Dispersal numbers ignore this year's reproduction.

Ecological population dynamics◈ Members↗
FA-65714

Two-patch source-sink dispersal with ceilings: dispersal base · case 04

Dispersal numbers ignore this year's reproduction.

Ecological population dynamics◈ Members↗
FA-65715

Two-patch source-sink dispersal with ceilings: dispersal base · case 05

Dispersal numbers ignore this year's reproduction.

Ecological population dynamics◈ Members↗
FA-65716

Two-pass removal abundance estimate: estimator numerator · case 01

Abundance is underestimated and becomes zero when the second pass is empty.

Ecological population dynamics● Open access↗
FA-65717

Two-pass removal abundance estimate: estimator numerator · case 02

Abundance is underestimated and becomes zero when the second pass is empty.

Ecological population dynamics◈ Members↗
FA-65718

Two-pass removal abundance estimate: estimator numerator · case 03

Abundance is underestimated and becomes zero when the second pass is empty.

Ecological population dynamics◈ Members↗
FA-65719

Two-pass removal abundance estimate: estimator numerator · case 04

Abundance is underestimated and becomes zero when the second pass is empty.

Ecological population dynamics◈ Members↗
FA-65720

Two-pass removal abundance estimate: estimator numerator · case 05

Abundance is underestimated and becomes zero when the second pass is empty.

Ecological population dynamics◈ Members↗
FA-65721

Two-pass removal abundance estimate: catchability · case 01

Capture probability falls as depletion gets stronger.

Ecological population dynamics● Open access↗
FA-65722

Two-pass removal abundance estimate: catchability · case 02

Capture probability falls as depletion gets stronger.

Ecological population dynamics◈ Members↗
FA-65723

Two-pass removal abundance estimate: catchability · case 03

Capture probability falls as depletion gets stronger.

Ecological population dynamics◈ Members↗
FA-65724

Two-pass removal abundance estimate: catchability · case 04

Capture probability falls as depletion gets stronger.

Ecological population dynamics◈ Members↗
FA-65725

Two-pass removal abundance estimate: catchability · case 05

Capture probability falls as depletion gets stronger.

Ecological population dynamics◈ Members↗
FA-65726

Two-pass removal abundance estimate: variance exponent · case 01

Variance estimates explode for strongly depleted streams.

Ecological population dynamics● Open access↗
FA-65727

Two-pass removal abundance estimate: variance exponent · case 02

Variance estimates explode for strongly depleted streams.

Ecological population dynamics◈ Members↗
FA-65728

Two-pass removal abundance estimate: variance exponent · case 03

Variance estimates explode for strongly depleted streams.

Ecological population dynamics◈ Members↗
FA-65729

Two-pass removal abundance estimate: variance exponent · case 04

Variance estimates explode for strongly depleted streams.

Ecological population dynamics◈ Members↗
FA-65730

Two-pass removal abundance estimate: variance exponent · case 05

Variance estimates explode for strongly depleted streams.

Ecological population dynamics◈ Members↗
FA-65731

Discrete delayed logistic (Hutchinson) with lag: lag index · case 01

Oscillations are weaker than the stated delay produces.

Ecological population dynamics● Open access↗
FA-65732

Discrete delayed logistic (Hutchinson) with lag: lag index · case 02

Oscillations are weaker than the stated delay produces.

Ecological population dynamics◈ Members↗
FA-65733

Discrete delayed logistic (Hutchinson) with lag: lag index · case 03

Oscillations are weaker than the stated delay produces.

Ecological population dynamics◈ Members↗
FA-65734

Discrete delayed logistic (Hutchinson) with lag: lag index · case 04

Oscillations are weaker than the stated delay produces.

Ecological population dynamics◈ Members↗
FA-65735

Discrete delayed logistic (Hutchinson) with lag: lag index · case 05

Oscillations are weaker than the stated delay produces.

Ecological population dynamics◈ Members↗
FA-65736

Discrete delayed logistic (Hutchinson) with lag: pre-history · case 01

Early growth explodes because the population is assumed absent before time 0.

Ecological population dynamics● Open access↗
FA-65737

Discrete delayed logistic (Hutchinson) with lag: pre-history · case 02

Early growth explodes because the population is assumed absent before time 0.

Ecological population dynamics◈ Members↗
FA-65738

Discrete delayed logistic (Hutchinson) with lag: pre-history · case 03

Early growth explodes because the population is assumed absent before time 0.

Ecological population dynamics◈ Members↗
FA-65739

Discrete delayed logistic (Hutchinson) with lag: pre-history · case 04

Early growth explodes because the population is assumed absent before time 0.

Ecological population dynamics◈ Members↗
FA-65740

Discrete delayed logistic (Hutchinson) with lag: pre-history · case 05

Early growth explodes because the population is assumed absent before time 0.

Ecological population dynamics◈ Members↗
FA-65741

Discrete delayed logistic (Hutchinson) with lag: growth base · case 01

Recruitment tracks the lagged population instead of current breeders.

Ecological population dynamics● Open access↗
FA-65742

Discrete delayed logistic (Hutchinson) with lag: growth base · case 02

Recruitment tracks the lagged population instead of current breeders.

Ecological population dynamics◈ Members↗
FA-65743

Discrete delayed logistic (Hutchinson) with lag: growth base · case 03

Recruitment tracks the lagged population instead of current breeders.

Ecological population dynamics◈ Members↗
FA-65744

Discrete delayed logistic (Hutchinson) with lag: growth base · case 04

Recruitment tracks the lagged population instead of current breeders.

Ecological population dynamics◈ Members↗
FA-65745

Discrete delayed logistic (Hutchinson) with lag: growth base · case 05

Recruitment tracks the lagged population instead of current breeders.

Ecological population dynamics◈ Members↗
FA-65746

Discrete delayed logistic (Hutchinson) with lag: overshoot reference · case 01

Overshoot is measured from the initial density instead of carrying capacity.

Ecological population dynamics● Open access↗
FA-65747

Discrete delayed logistic (Hutchinson) with lag: overshoot reference · case 02

Overshoot is measured from the initial density instead of carrying capacity.

Ecological population dynamics◈ Members↗
FA-65748

Discrete delayed logistic (Hutchinson) with lag: overshoot reference · case 03

Overshoot is measured from the initial density instead of carrying capacity.

Ecological population dynamics◈ Members↗
FA-65749

Discrete delayed logistic (Hutchinson) with lag: overshoot reference · case 04

Overshoot is measured from the initial density instead of carrying capacity.

Ecological population dynamics◈ Members↗
FA-65750

Discrete delayed logistic (Hutchinson) with lag: overshoot reference · case 05

Overshoot is measured from the initial density instead of carrying capacity.

Ecological population dynamics◈ Members↗
FA-65751

MacArthur-Wilson island equilibrium: distance decay · case 01

Remote islands receive more immigrants than near ones.

Ecological population dynamics● Open access↗
FA-65752

MacArthur-Wilson island equilibrium: distance decay · case 02

Remote islands receive more immigrants than near ones.

Ecological population dynamics◈ Members↗
FA-65753

MacArthur-Wilson island equilibrium: distance decay · case 03

Remote islands receive more immigrants than near ones.

Ecological population dynamics◈ Members↗
FA-65754

MacArthur-Wilson island equilibrium: distance decay · case 04

Remote islands receive more immigrants than near ones.

Ecological population dynamics◈ Members↗
FA-65755

MacArthur-Wilson island equilibrium: distance decay · case 05

Remote islands receive more immigrants than near ones.

Ecological population dynamics◈ Members↗
FA-65756

MacArthur-Wilson island equilibrium: area effect on extinction · case 01

Large islands lose species faster than small ones.

Ecological population dynamics● Open access↗
FA-65757

MacArthur-Wilson island equilibrium: area effect on extinction · case 02

Large islands lose species faster than small ones.

Ecological population dynamics◈ Members↗
FA-65758

MacArthur-Wilson island equilibrium: area effect on extinction · case 03

Large islands lose species faster than small ones.

Ecological population dynamics◈ Members↗
FA-65759

MacArthur-Wilson island equilibrium: area effect on extinction · case 04

Large islands lose species faster than small ones.

Ecological population dynamics◈ Members↗
FA-65760

MacArthur-Wilson island equilibrium: area effect on extinction · case 05

Large islands lose species faster than small ones.

Ecological population dynamics◈ Members↗
FA-65761

MacArthur-Wilson island equilibrium: equilibrium richness · case 01

Predicted richness can exceed the mainland pool.

Ecological population dynamics● Open access↗
FA-65762

MacArthur-Wilson island equilibrium: equilibrium richness · case 02

Predicted richness can exceed the mainland pool.

Ecological population dynamics◈ Members↗
FA-65763

MacArthur-Wilson island equilibrium: equilibrium richness · case 03

Predicted richness can exceed the mainland pool.

Ecological population dynamics◈ Members↗
FA-65764

MacArthur-Wilson island equilibrium: equilibrium richness · case 04

Predicted richness can exceed the mainland pool.

Ecological population dynamics◈ Members↗
FA-65765

MacArthur-Wilson island equilibrium: equilibrium richness · case 05

Predicted richness can exceed the mainland pool.

Ecological population dynamics◈ Members↗
FA-65766

Monthly population with seasonal breeding window: month wrap · case 01

December is treated as month 0 and every month is shifted.

Ecological population dynamics● Open access↗
FA-65767

Monthly population with seasonal breeding window: month wrap · case 02

December is treated as month 0 and every month is shifted.

Ecological population dynamics◈ Members↗
FA-65768

Monthly population with seasonal breeding window: month wrap · case 03

December is treated as month 0 and every month is shifted.

Ecological population dynamics◈ Members↗
FA-65769

Monthly population with seasonal breeding window: month wrap · case 04

December is treated as month 0 and every month is shifted.

Ecological population dynamics◈ Members↗
FA-65770

Monthly population with seasonal breeding window: month wrap · case 05

December is treated as month 0 and every month is shifted.

Ecological population dynamics◈ Members↗
FA-65771

Monthly population with seasonal breeding window: wrapping window · case 01

Breeding seasons that span the new year never occur.

Ecological population dynamics● Open access↗
FA-65772

Monthly population with seasonal breeding window: wrapping window · case 02

Breeding seasons that span the new year never occur.

Ecological population dynamics◈ Members↗
FA-65773

Monthly population with seasonal breeding window: wrapping window · case 03

Breeding seasons that span the new year never occur.

Ecological population dynamics◈ Members↗
FA-65774

Monthly population with seasonal breeding window: wrapping window · case 04

Breeding seasons that span the new year never occur.

Ecological population dynamics◈ Members↗
FA-65775

Monthly population with seasonal breeding window: wrapping window · case 05

Breeding seasons that span the new year never occur.

Ecological population dynamics◈ Members↗
FA-65776

Monthly population with seasonal breeding window: inclusive window end · case 01

The last breeding month produces no births.

Ecological population dynamics● Open access↗
FA-65777

Monthly population with seasonal breeding window: inclusive window end · case 02

The last breeding month produces no births.

Ecological population dynamics◈ Members↗
FA-65778

Monthly population with seasonal breeding window: inclusive window end · case 03

The last breeding month produces no births.

Ecological population dynamics◈ Members↗
FA-65779

Monthly population with seasonal breeding window: inclusive window end · case 04

The last breeding month produces no births.

Ecological population dynamics◈ Members↗
FA-65780

Monthly population with seasonal breeding window: inclusive window end · case 05

The last breeding month produces no births.

Ecological population dynamics◈ Members↗
FA-65781

Monthly population with seasonal breeding window: survival before births · case 01

Newborns are subjected to the month's mortality.

Ecological population dynamics● Open access↗
FA-65782

Monthly population with seasonal breeding window: survival before births · case 02

Newborns are subjected to the month's mortality.

Ecological population dynamics◈ Members↗
FA-65783

Monthly population with seasonal breeding window: survival before births · case 03

Newborns are subjected to the month's mortality.

Ecological population dynamics◈ Members↗
FA-65784

Monthly population with seasonal breeding window: survival before births · case 04

Newborns are subjected to the month's mortality.

Ecological population dynamics◈ Members↗
FA-65785

Monthly population with seasonal breeding window: survival before births · case 05

Newborns are subjected to the month's mortality.

Ecological population dynamics◈ Members↗
FA-65786

Monthly population with seasonal breeding window: density-dependent births · case 01

Populations above the cap lose animals through negative births.

Ecological population dynamics● Open access↗
FA-65787

Monthly population with seasonal breeding window: density-dependent births · case 02

Populations above the cap lose animals through negative births.

Ecological population dynamics◈ Members↗
FA-65788

Monthly population with seasonal breeding window: density-dependent births · case 03

Populations above the cap lose animals through negative births.

Ecological population dynamics◈ Members↗
FA-65789

Monthly population with seasonal breeding window: density-dependent births · case 04

Populations above the cap lose animals through negative births.

Ecological population dynamics◈ Members↗
FA-65790

Monthly population with seasonal breeding window: density-dependent births · case 05

Populations above the cap lose animals through negative births.

Ecological population dynamics◈ Members↗
FA-65791

Rosenzweig-MacArthur equilibrium and enrichment stability: prey equilibrium · case 01

The prey equilibrium ignores handling time.

Ecological population dynamics● Open access↗
FA-65792

Rosenzweig-MacArthur equilibrium and enrichment stability: prey equilibrium · case 02

The prey equilibrium ignores handling time.

Ecological population dynamics◈ Members↗
FA-65793

Rosenzweig-MacArthur equilibrium and enrichment stability: prey equilibrium · case 03

The prey equilibrium ignores handling time.

Ecological population dynamics◈ Members↗
FA-65794

Rosenzweig-MacArthur equilibrium and enrichment stability: prey equilibrium · case 04

The prey equilibrium ignores handling time.

Ecological population dynamics◈ Members↗
FA-65795

Rosenzweig-MacArthur equilibrium and enrichment stability: prey equilibrium · case 05

The prey equilibrium ignores handling time.

Ecological population dynamics◈ Members↗
FA-65796

Rosenzweig-MacArthur equilibrium and enrichment stability: conversion feasibility · case 01

Predators that cannot convert prey fast enough are reported as persisting, or vice versa.

Ecological population dynamics● Open access↗
FA-65797

Rosenzweig-MacArthur equilibrium and enrichment stability: conversion feasibility · case 02

Predators that cannot convert prey fast enough are reported as persisting, or vice versa.

Ecological population dynamics◈ Members↗
FA-65798

Rosenzweig-MacArthur equilibrium and enrichment stability: conversion feasibility · case 03

Predators that cannot convert prey fast enough are reported as persisting, or vice versa.

Ecological population dynamics◈ Members↗
FA-65799

Rosenzweig-MacArthur equilibrium and enrichment stability: conversion feasibility · case 04

Predators that cannot convert prey fast enough are reported as persisting, or vice versa.

Ecological population dynamics◈ Members↗
FA-65800

Rosenzweig-MacArthur equilibrium and enrichment stability: conversion feasibility · case 05

Predators that cannot convert prey fast enough are reported as persisting, or vice versa.

Ecological population dynamics◈ Members↗

INSPECTABLE BY DESIGN

Every result has a runnable source.

Runnable implementations with recorded outputs, source hashes, and explicit contracts. Related variants share a failure mechanism and belong together in evaluation splits.

Read the methodology ↗