Research assessment · 29 September 2026

THE EVIDENCE
DOES NOT SAY YES.

Worldwide extinction is a defined objective, not an achieved or demonstrated capability. This page shows the observations, internal model results, rejected approaches, and unanswered questions behind that assessment.

Start with the current decisions ↓

Current assessment

The project's literature reviews and conditional models do not establish a safe route to literal worldwide extinction. These decisions concern the evidence available now.

Worldwide extinction
YELLOWUnresolved. Neither worldwide feasibility nor a fatal universal barrier has been demonstrated.
Reservoirs and global reach
YELLOWAnimal-associated populations make human-only coverage insufficient. The complete occupied universe and repeat detection are unknown.
Contact plus lasting reproductive loss
REDThe necessary surviving-recipient viable-offspring effect is unmeasured, and untouched refuges remain fertile.
Heritable or autonomous suppression
REDNo target-species suppressive inherited system is demonstrated; reproductive disconnection blocks spread.
Shared nutritional function (F03)
UNRESOLVABLE FROM EXISTING DESK EVIDENCELab vitamin rescue weakens a simple universal symbiont claim. Natural-diet function across all three species remains unmeasured.

RED rejects the studied architecture as a credible global solution on present evidence. It is not a proof that all possible approaches are impossible. The F03 desk decision concerns a different biological hypothesis and does not change the overall YELLOW verdict.

A mapped frontier.
A reached desk limit.

The frontier map ranks 12 meaningful research branches across the three working target species. The F03 nutritional-function desk audit is now complete at project record 46fba5f. No demonstrated mission-killing barrier or evidenced three-species extinction route has emerged. Worldwide extinction remains YELLOW; the contact and heritable architectures remain RED. Read the F03 decision →

WHAT THE F03 DESK AUDIT ESTABLISHED

A simple weak point failed scrutiny.

In C. lectularius laboratory work, dietary B vitamins restored nymph development, adult survival, and egg hatch after verified Wolbachia loss; body size and egg production recovered only partly. Riboflavin rescued hemoglobin digestion in a later assay, but not every digestive deficit. A single named symbiont or absolutely irreplaceable measured vitamin contribution cannot be assumed across the targets. [Hickin 2022] [Wiles 2025]

These laboratory substitutions do not establish natural-diet rescue or rule out another shared function. Comparative genomes predict pathways but do not measure host dependence, and L. boueti was not in that genomic sample. The three-species functional question is UNRESOLVABLE FROM EXISTING DESK EVIDENCE. [Yu 2025]

WHAT NOW REQUIRES NEW EVIDENCE

Function. Reach. Absence.

F03 first needs fresh, voucher-confirmed L. boueti material from a sustaining human-associated population and a partner/nutrient inventory; C. hemipterus needs strain and partner resolution linked to natural-diet viable daughters; C. lectularius needs lifetime viable-daughter results across human and bat-associated natural-diet lineages. A PCR-negative marker is not evidence of functional independence. [Tehran 2026]

The other mapped walls remain: F01 occupied-population reach, F02 low-density detection, F04 tiny-founder establishment, F05 alternate-host persistence, and F12 target taxonomy and nontarget consequences. F11 historical source linkage and F12 voucher inventory still allow bounded desk work, but they cannot certify global absence.

The desk audit closed. The biological question remains open. None of these findings establishes an extinction method.

The species boundary

The working list is subject to taxonomic review. It concerns species associated with sustained human infestation, and every sustaining population of each target species counts.

Cimex lectularius

Human-associated populations are widespread. Bat-associated lineages are genetically distinct in sampled sites and constitute the strongest nonhuman maintenance inference. Their global extent and exchange with human lineages remain uncertain. [Booth 2015]

Cimex hemipterus

A human-infesting species with distinct field-derived life histories. [How & Lee 2010] Heavy poultry-barn infestation has been reported, but independent long-term maintenance and worldwide animal-host extent are not established. [Rosen 1987]

Leptocimex boueti

Historical human-house specimens and one species-identified bat encounter are on record. A sustaining bat population, current range, life history, and human–bat connectivity remain unknown. [Bernard 1970] [Nartey 2015]

A species survives if any independently fertile population survives, whether or not it continues to infest human dwellings.

What has been observed in the field

These findings are local and setting-specific. None is a worldwide infestation rate or an extinction forecast.

5 of 6

source apartments

had marked C. lectularius recovered in neighboring apartments over 32 days. This documents local movement, not a universal movement rate. [Cooper 2015]

49%

resident-unaware

of protocol-detected infestations in a study of 2,372 apartments across 43 New Jersey buildings. Resident silence is a weak absence test in that setting. [Wang 2016]

9% → 3%

building infestation rate

after 12 months of building-wide management in one study; new infestations were still found during follow-up. This is control evidence, not extinction. [Wang 2019]

What the models actually say

Both models are conditional internal analyses. Their results are tests of assumptions, not achieved field effects or forecasts of a global campaign.

Closed population model

The first model uses a laboratory life table for one C. lectularius strain. It explores combinations of sustained mortality, exposure, and reduced reproduction that would drive a closed population below replacement. It includes no immigration, animal reservoir, resistance evolution, or other target species. [Polanco 2011]

Connected population model

A two-patch extension makes the untreated-source problem explicit. With illustrative assumed rates, the reached human patch declines while an untreated refuge grows. The whole system remains above replacement. New movement and intervention rates are hypothetical, not empirically calibrated.

Reached human patchλ = 0.92429Declining under assumed conditions
Untreated refugeλ = 1.05290Growing under assumed conditions
Connected systemλ ≈ 1.05195Not below replacement

Illustrative V2 case: effective primary contact of 0.20/day in the human patch and zero in the refuge, assumed kill fraction 0.65, assumed lasting viable-egg reduction 0.75, and symmetric movement 0.001/day. λ is the model's daily growth multiplier; below one means decline under fixed assumptions. These values cannot be read as worldwide requirements or intervention performance.

Methods, with the limits exposed

The assessment keeps three kinds of evidence separate: what a study observed, what a model implies if its assumptions hold, and what the project decides from the gap between them.

Primary evidence

Species and host claims are tied to specimen, field, or laboratory records. One bat encounter is not treated as a sustaining population; a pooled egg count is not assigned to a surviving recipient. The species table and source list expose the selected evidence behind this assessment.

V1: closed population

A daily stage model uses one published C. lectularius life table. The replacement boundary is the dominant daily growth multiplier λ = 1; seeded integer simulations ask when a finite, closed modeled population reaches zero. Calibration to that paper is not field validation. [Polanco 2011]

V2: connected patches

The extension applies the same one-species biology to a reached human patch and a refuge to isolate the source problem. New contact, transfer, reproductive, and movement rates are scenario inputs, not fitted observations. Code checks verify model behavior, not biological performance.

Decision gates

YELLOW records an unresolved global reach question. RED rejects the studied contact and inherited architectures as credible worldwide routes on current evidence. Neither label proves universal feasibility or impossibility. The Research Log preserves the dated path to each decision.

Unresolved limits: no worldwide population inventory or calibrated low-density detection; no V2 life histories for C. hemipterus or L. boueti; no measured lasting viable-daughter effect in secondary-contact survivors; no demonstrated safe, selective, lawful global intervention. These omissions prevent a worldwide extinction forecast.

Two attractive routes did not clear the evidence gate

The project has rated both studied suppression architectures RED for literal global extinction on present evidence.

Contact-mediated, lasting reproductive loss

Secondary fungal transfer has been measured in C. lectularius, but pooled arena eggs and recipient mortality cannot establish remaining-life viable daughters for individually identified surviving secondary recipients. That decisive outcome is missing. Even complete sterility among reached bugs would not remove an untouched fertile refuge. [Aak 2018]

Heritable or autonomous suppression

Inheritance could, in theory, carry an effect through connected mating. No self-sustaining suppressive system is demonstrated in the three target species. Strong host-associated differentiation in C. lectularius and unknown connectivity in the others mean no worldwide reproductive network has been established. [Booth 2015]

Evidence still needed

These are conditions for testing an extinction claim, not a schedule for conducting an intervention.

  • Map the target.Specimen-backed records of all sustaining host populations, including animal-associated and unsurveyed settings.
  • Calibrate detection.Repeat-detection and false-positive rates at very low density in each host environment.
  • Measure effects in the field.Species-specific safety, selectivity, coverage, durable reproductive outcomes, movement, and resistance under realistic conditions.
  • Test connected areas.Preregistered multi-building and regional studies that detect new introductions and verify sustained elimination.
  • Define global proof.Independent audit, international governance, lawful access, and an explicit bound on the risk of undetected survivors.

Primary sources

The links below support the specific observations on this page. The project’s extinction assessments and models are its own conditional research judgments.

  1. Booth et al. (2015). Host-associated genetic structure of C. lectularius. Molecular Ecology ↗
  2. How & Lee (2010). Life histories of field-derived C. hemipterus strains. Medical and Veterinary Entomology ↗
  3. Rosen et al. (1987). C. hemipterus in poultry housing. Avian Pathology ↗
  4. Bernard (1970). L. boueti specimens from human habitations. IRD research archive ↗
  5. Nartey (2015). Ghana thesis reporting a L. boueti specimen on a bat. University of Ghana ↗
  6. Cooper et al. (2015). Marked bed bug dispersal among apartments. PLOS ONE ↗
  7. Wang et al. (2016). Detection and resident awareness in New Jersey apartments. Journal of Medical Entomology ↗
  8. Wang et al. (2019). Building-wide management and follow-up. Journal of Integrated Pest Management ↗
  9. Polanco, Brewster & Miller (2011). Laboratory life table of a C. lectularius field strain. Insects ↗
  10. Aak et al. (2018). Fungal material transfer among bed bugs. Journal of Pest Science ↗
  11. Hosokawa et al. (2010). Nutritional symbiont function and vitamin rescue in C. lectularius. PNAS ↗
  12. Hickin et al. (2022). Endpoint-specific B-vitamin rescue after verified symbiont loss in C. lectularius. Scientific Reports ↗
  13. Wiles et al. (2025). Riboflavin rescue of a hemoglobin-digestion deficit in C. lectularius. Scientific Reports ↗
  14. Yu et al. (2025). Comparative cimicid symbiont turnover and predicted pathways; L. boueti was not sampled. mSystems ↗
  15. C. hemipterus survey (2026). Geographically uneven Wolbachia marker detection; function was not tested. Scientific Reports ↗