Fact-checked by Grok 2 weeks ago

Not evaluated

Not evaluated (NE) is a designation in the Categories and Criteria for taxa that have not yet been systematically assessed for their risk of using the IUCN's quantitative criteria. This category signifies a lack of sufficient evaluation rather than a judgment on threat level, and such taxa are not included in the published database. As of April 2025, the IUCN has assessed approximately 169,420 , leaving the vast majority of the estimated 1.5 to 2 million described in the not evaluated status due to resource constraints and prioritization of certain taxonomic groups. The designation underscores gaps in knowledge, emphasizing the need for expanded assessments to inform priorities, particularly for understudied and microorganisms. While not implying safety or peril, the not evaluated status can delay targeted interventions until data collection enables classification into categories such as , least concern, or threatened.

Definition and Criteria

Core Definition

The Not Evaluated (NE) category designates taxa that have not yet undergone assessment against the criteria for evaluating extinction risk. This status indicates a lack of formal rather than any inference about the taxon's conservation condition, distinguishing it from categories like (DD), where assessment has occurred but data insufficiency prevents categorization. NE applies to the vast majority of Earth's described , estimated at over 99% as of recent assessments, due to limited resources for comprehensive evaluation. Taxa assigned NE are excluded from the published , which focuses on assessed to inform priorities. The underscores gaps in taxonomic and ecological knowledge, as only select groups—such as mammals, birds, and certain plants—receive routine scrutiny, leaving , fungi, and many unevaluated. Reassessment may elevate a from NE once sufficient data becomes available, potentially revealing previously unrecognized threats.

Distinction from Other IUCN Categories

The IUCN Not Evaluated (NE) category applies exclusively to taxa that have not undergone any formal against the Red List criteria, distinguishing it from all other categories which require an evaluation process to determine extinction risk. Unlike the eight published categories—Extinct (EX), (EW), (CR), Endangered (EN), Vulnerable (VU), Near Threatened (NT), Least Concern (LC), and (DD)—NE taxa are not included on the itself, as no data compilation or risk analysis has occurred. This procedural status reflects a lack of rather than any inference about population status or threats. A key distinction lies between and (DD), where DD denotes taxa that have been evaluated but for which inadequate information prevents a reliable assignment to threatened, Near Threatened, or Least Concern categories, often due to genuine knowledge gaps on distribution, abundance, or threats. In contrast, indicates no evaluation attempt has been made, potentially encompassing undescribed species, newly discovered taxa, or those overlooked in assessment priorities; DD assessments, however, involve documented efforts yielding insufficient quantitative data for criteria application, such as population size reduction thresholds or geographic range metrics. The threatened categories (CR, EN, VU) and conservation-dependent ones (NT, LC) further diverge from NE by quantifying extinction probability over defined time frames—e.g., CR requires a 50% decline in three generations or a 10% probability of in 10 years—based on like habitat loss or rates, whereas NE provides no such risk appraisal. EX and EW, meanwhile, confirm absence in the wild or entirely, verified through exhaustive searches and absence records spanning 50 years post-last sighting. Thus, NE serves as a placeholder for future scrutiny, not a risk indicator, underscoring the Red List's incomplete coverage of , with millions of remaining unevaluated as of 2023.

Historical Development

Origins in IUCN Red List

The Not Evaluated (NE) category was formally introduced in the IUCN Red List Categories and Criteria version 2.3, adopted in 1994, to designate taxa that had not yet been assessed for extinction risk using the established quantitative criteria. This marked a shift from earlier IUCN Red Data Books, which began publication in 1966 with volumes on mammals and later birds, focusing primarily on listing species considered rare, endangered, or vulnerable without explicit categories for unevaluated taxa. In pre-1994 assessments, species absent from these lists were implicitly unevaluated, but lacked a standardized designation, reflecting the qualitative and selective nature of initial Red List compilations starting from 1963. The 1994 framework defined NE alongside other categories such as Extinct, Critically Endangered, Endangered, Vulnerable, Lower Risk (with subcategories), and Data Deficient, emphasizing that NE applied to taxa not subjected to the criteria-based evaluation process. This introduction addressed the need for a comprehensive system applicable across diverse taxa, acknowledging that only a fraction of described species—estimated at around 1.8 million at the time—could be practically assessed given resource constraints. The category underscored the preliminary stage of global biodiversity evaluation, where NE status highlighted gaps in knowledge rather than implying low risk. Version 3.1 of the criteria, adopted by the IUCN Council on February 9, 2000, and published in 2001, retained the category without substantive changes to its definition, maintaining it as a marker for unevaluated taxa while refining overall assessment methodologies through extensive testing and consultation since 1989. Unlike assessed categories, taxa are not published on the website, distinguishing them from species, which have undergone evaluation but lack sufficient information for categorization. This persistence of origins in the 1994 system established a foundational of transparency about assessment coverage, informing subsequent expansions where, by 2024, over 157,000 had been evaluated, leaving the majority in status.

Evolution of the NE Category

The Not Evaluated (NE) category emerged as part of the formalized Categories and Criteria system introduced in 1994, following six years of development to establish quantitative standards for risk assessment. Prior to 1994, the , initiated in 1964 through early Red Data Books, focused primarily on compiling lists of using qualitative judgments without standardized categories for unevaluated taxa. The 1994 framework (version 2.3) explicitly defined NE as applying to taxa that had not been assessed against the new criteria, thereby highlighting the distinction between unassessed species and those evaluated but data-deficient. Subsequent revisions, such as version 3.1 adopted in 2001, preserved the definition without substantive changes, maintaining its role as a marker for species outside the formal evaluation process. This stability allowed for consistent tracking of assessment coverage, revealing that encompassed the vast majority of described —estimated at over 2 million eukaryotic taxa—while only 157,000 had been assessed by 2024. The category's design ensures that the Red List publishes only evaluated , excluding to emphasize empirical evaluations over assumptions of safety. Over time, the category has underscored systemic gaps in data, prompting initiatives like specialist group collaborations and data mobilization efforts to transition from NE to assessed statuses. Despite these advances, resource constraints and the sheer scale of undescribed or unstudied taxa have sustained NE as a critical indicator of incomplete global conservation knowledge, with no alterations to its criteria reflecting a commitment to unaltered baselines for longitudinal comparisons. This evolution from an implicit unassessed state to a deliberate category has enhanced transparency in reporting assessment without implying lower risk for NE species.

Assessment Processes and Challenges

IUCN Evaluation Methodology

The IUCN evaluates species extinction risk using a standardized quantitative framework outlined in the Red List Categories and Criteria, version 3.1, adopted in 2001 and retained in the second edition published in 2012. This methodology classifies taxa into one of nine categories—Extinct (EX), (EW), (CR), (EN), Vulnerable (VU), Near Threatened (NT), Least Concern (LC), (DD), and Not Evaluated (NE)—based on the probability of extinction in the wild. A qualifies as threatened (, , or VU) if it meets quantitative thresholds under any of five criteria (A–E), prioritizing empirical data on population trends, range, and threats over qualitative judgments. The five criteria assess different facets of extinction risk:
  • Criterion A: Reduction in population size, measured over specified time frames (e.g., 10 years or three generations), with requiring ≥90% decline, ≥70%, and ≥50%.
  • Criterion B: Restricted geographic range, combining extent of occurrence (EOO) or area of occupancy (AOO) with fragmentation or decline; applies to EOO <100 km² or AOO <10 km², to EOO <5,000 km² or AOO <500 km², and to EOO <20,000 km² or AOO <2,000 km².
  • Criterion C: Small population size with observed or projected decline; for <250 mature individuals with ≥25% decline in three years or one generation, for <2,500 with ≥20% in five years or two generations, and for <10,000 with ≥10% in 10 years or three generations.
  • Criterion D: Very small or restricted population, with for <50 mature individuals, for <250, and for <1,000.
  • Criterion E: , such as population viability analysis, estimating probability; for ≥50% within 10 years or three generations, for ≥20% within 20 years or five generations, and for ≥10% within 100 years.
Assessments are conducted by expert assessors, typically IUCN Species Survival Commission (SSC) members or affiliated specialists, who compile species-specific data on , (including GIS-mapped ranges), estimates, requirements, threats, and actions via the online Species Information Service (). Assessors apply the criteria objectively, documenting evidence and rationale to ensure . Completed drafts undergo mandatory by at least two independent reviewers designated by Red List Authorities (RLAs)—specialist groups responsible for taxonomic oversight—within three months, focusing on data accuracy, criteria application, and consistency. The RLA evaluates reviewer feedback and approves the assessment for submission to the Unit (RLU). The RLU performs final quality controls, including taxonomic checks, mapping validation, and adherence to guidelines (version 16, updated March 2024), before queuing for publication on the Red List website. This multi-stage process, emphasizing transparency and expert scrutiny, aims to minimize bias and errors, though challenges persist in data-scarce taxa, often resulting in rather than definitive threat levels.

Factors Leading to NE Status

The Not Evaluated (NE) status applies to taxa that have not been formally assessed against the IUCN Red List criteria, encompassing the vast majority of described species worldwide. As of 2024, fewer than 5% of the world's described species—estimated at around 2 million—have undergone , leaving over 95% in the NE category due to the sheer scale of and the resource-intensive nature of assessments. This incomplete coverage stems from the IUCN's reliance on a decentralized of volunteer specialists who compile data on population trends, habitat extent, and threats, a process that demands substantial time and expertise for each . Primary factors include limited institutional capacity and funding, which constrain the number of assessments annually; for instance, despite assessing over 172,000 cumulatively, the pace lags behind species descriptions and emerging needs, exacerbating underrepresentation in data-poor taxa. Prioritization by IUCN and its specialist groups favors vertebrates, plants with economic or ecological significance, and regions with established research infrastructure, sidelining , fungi, and microorganisms that constitute the bulk of but often lack dedicated experts or baseline data. Newly described species, numbering thousands annually, routinely enter the NE category as taxonomic publication precedes risk evaluation, with delays arising from the need to verify distributions and threats post-description. Logistical barriers further contribute, particularly in remote or politically unstable habitats where field is hindered by issues, concerns, or insufficient local expertise; this is evident in lower assessment rates for taxa despite high . Additionally, the absence of perceived urgency for widespread or resilient species defers their evaluation, as resources are allocated to taxa showing rapid declines, perpetuating biases toward "charismatic" or threatened groups over those requiring proactive monitoring. These factors collectively result in NE status not indicating low risk but rather a gap in systematic appraisal, underscoring the Red List's role as a dynamic but incomplete inventory rather than a comprehensive .

Global Statistics and Distribution

Quantified Prevalence of NE Species

As of IUCN Red List version 2025-1, released on March 27, 2025, approximately 169,420 species have been evaluated out of an estimated 2,139,242 described across major taxonomic groups, representing 8% overall coverage and leaving roughly 92% (over 1.97 million ) in the Not Evaluated () category. This figure underscores the incomplete assessment of , with NE status indicating a lack of systematic evaluation rather than inferred low extinction risk. The total number of evaluated has grown from around 150,000 in 2023 to over 172,600 by late 2025, yet the proportion evaluated remains low due to the expansive scale of described , particularly in understudied phyla. Taxonomic disparities amplify NE prevalence. Vertebrates demonstrate high evaluation rates, with nearly all mammals (over 6,400 of ~6,500 described ) and (~11,000 species) assessed, achieving coverage exceeding 99% in these classes. Amphibians and reptiles also approach comprehensive evaluation, at around 95-100% for described species. In stark contrast, invertebrates such as arthropods (over 1.2 million described species) have evaluation rates below 1%, resulting in millions of NE insects, crustaceans, and arachnids. Plants exhibit intermediate coverage, with about 10-15% evaluated (~50,000 of ~400,000 described vascular ), while fungi and many protists remain largely NE, with less than 5% assessed due to taxonomic and data challenges. These patterns reflect resource allocation priorities toward charismatic or high-risk taxa, leaving NE dominance in hyperdiverse groups like beetles (over 400,000 described species, fewer than 1,000 evaluated). IUCN's strategic plan aims to assess 260,000 species by 2030, potentially reducing NE prevalence to under 85%, but current trajectories suggest persistent gaps in microbial and deep invertebrate lineages. Empirical data from regional assessments corroborate global trends, with NE species comprising 80-95% in tropical insect inventories and marine invertebrates.

Taxonomic and Geographic Patterns

Among taxonomic groups, the Not Evaluated (NE) status is disproportionately prevalent in and fungi, reflecting limited assessment efforts relative to their estimated . Arthropods, particularly , exhibit the highest proportions of NE species; for example, less than 0.02% of described species had been assessed by 2018, with similar low coverage for arachnids (0.3%) and crustaceans (0.3%). Fungi show comparable underrepresentation, with fewer than 5% of species assessed as of 2025, despite their critical ecological roles. In contrast, vertebrates such as , mammals, and amphibians have near-complete assessments, with virtually all species evaluated multiple times, leaving minimal NE taxa in these classes. This disparity arises from resource allocation biases favoring charismatic or economically significant vertebrates over hyperdiverse, less-studied and microbes, where basic taxonomic inventories remain incomplete. Geographically, NE species patterns align with global centers of , particularly tropical regions like the , Southeast Asian rainforests, and Central forests, where invertebrate and fungal diversity peaks but assessment coverage lags due to logistical challenges, political instability, and prioritization of accessible temperate zones. In well-studied areas such as and , NE proportions are lower even for , as national red lists and regional expertise facilitate more evaluations. Tropical hotspots host the majority of undescribed or unevaluated taxa, exacerbating knowledge gaps; for instance, estimates suggest over 90% of arthropod species in these areas remain unassessed, potentially masking elevated risks from loss and . Overall, these patterns underscore systemic underinvestment in non-vertebrate taxa and remote ecosystems, limiting comprehensive global risk profiling.

Notable Examples and Case Studies

High-Profile NE Species

Domestic sheep (), one of the most widespread livestock species with a global population exceeding 1.2 billion as of 2020, remains not evaluated by the IUCN due to its domesticated status and lack of extinction risk in wild populations. The species, descended from wild (Ovis orientalis) through starting around 10,000 years ago, supports major industries in , , and dairy, yet IUCN assessments exclude domesticated taxa to focus on wild biodiversity. Similarly, domestic cattle (Bos taurus), numbering over 1 billion individuals worldwide in 2023, are not assessed, as their managed populations obviate natural extinction threats under IUCN criteria. The domestic dog (Canis lupus familiaris), with an estimated 900 million individuals globally and a history of tracing back 15,000–40,000 years, exemplifies high-profile NE status; while feral populations impact , the itself is excluded from Red List evaluations. Domestic pigs (Sus scrofa domesticus), integral to food systems with annual slaughter exceeding 1.5 billion in 2022, share this unevaluated category, reflecting IUCN's policy against including domesticated forms derived from wild ancestors like the Eurasian boar. These highlight how NE applies to economically vital but human-dependent taxa, where conservation priorities shift to wild relatives rather than managed breeds. In semi-wild contexts, the (Canis dingo), an iconic canid introduced around 4,000 years ago and culturally significant to , is classified as , with populations stable at approximately 100,000–500,000 but unmanaged in conservation assessments. Unlike assessed wild canids, its hybridisation with domestic dogs complicates evaluation, yet it remains outside formal IUCN scrutiny due to insufficient dedicated assessment efforts. Such cases underscore that high-profile NE species often evade evaluation not from scarcity but from exclusions or low perceived wild risk, despite ecological roles.

Transitions from NE to Assessed Status

Transitions from Not Evaluated () to assessed status on the occur through targeted initiatives by Red List Authorities (RLAs) and specialist groups, which prioritize understudied taxonomic groups or species facing emerging threats. These evaluations follow the IUCN's standardized criteria for risk, involving data compilation on trends, , and threats via the Species Information Service () platform, , and final validation before publication. Such processes are driven by strategic plans like the Barometer of Life, aiming to assess at least 260,000 species by 2030 to fill knowledge gaps. The 2024 Global Tree Assessment exemplifies large-scale transitions, incorporating first-time evaluations of thousands of tree previously in NE status as part of a comprehensive review of over 47,000 . Results indicated that 38% of assessed trees are threatened with (, Endangered, or Vulnerable), primarily due to , , and habitat conversion, with documented in 192 countries. This update, including 4,485 new assessments in the initial 2024 release, revealed disproportionate risks in tropical regions and for endemic . Invertebrate groups have seen similar shifts, as in the 2025 European pollinator assessment, where nearly 100 wild species transitioned from to threatened categories, contributing to 10% of 1,928 evaluated European wild bees now at risk (Vulnerable or higher). Bumblebees and mining bees showed elevated threats from intensive , , and exposure, doubling the proportion of imperiled species over the past decade. Mammalian cases include the (Canis lupus pallipes), first assessed in 2025 as Vulnerable due to a mature population estimated at 2,877–3,310 individuals, fragmented across and parts of and . Key threats encompass habitat loss from agricultural expansion, retaliatory killings by herders, and diseases like , with the assessment recognizing its potential as a distinct lineage warranting subspecies-specific protections. These transitions frequently assign higher levels than initial expectations, as seen across taxa where data deficiencies previously masked risks, thereby enabling evidence-based interventions like expansions or mitigation. Comprehensive group assessments accelerate such moves, but resource constraints limit coverage, with over 96% of described still as of recent estimates.

Implications for Conservation Policy

Policy and Regulatory Ramifications

The Not Evaluated (NE) status signifies that a species has not undergone formal against IUCN criteria, rendering it ineligible for inclusion on the published Red List and thereby limiting its visibility in regulatory frameworks that depend on categorized threat levels for triggering protections. This absence of evaluation often results in policy gaps, as international agreements like the and national laws such as the U.S. Endangered Species Act prioritize with documented threat statuses (e.g., Vulnerable or higher) for trade restrictions, habitat safeguards, and recovery funding. Without an , NE face heightened risks from unregulated exploitation, such as commercial harvesting or habitat conversion, as regulators lack the empirical basis to impose measures like quotas or bans. In practice, this status delays interventions, allowing potential declines to proceed unchecked; for instance, among North American trees, the vast majority remain NE, complicating policies that rely on data for sustainable regulations. Similarly, in marine contexts, numerous and species classified as NE evade fisheries oversight, contributing to concerns where IUCN data informs regional management bodies like the International Commission for the Conservation of Atlantic Tunas. Empirical patterns indicate that NE taxa, particularly in understudied groups like and fungi, represent over 80% of described in some assessments, underscoring systemic under-protection in hotspots where local laws mirror IUCN categories. Regulatory responses have included directives to prioritize evaluations in funding mechanisms; the IUCN's strategic goals, aligned with the Convention on Biological Diversity's Aichi Targets (extended via post-2020 frameworks), advocate for assessing high-priority species to close these gaps, influencing national budgets for taxonomic surveys and . For example, initiatives like the 's coordination with IUCN assessments aim to transition species to evaluated statuses, enabling integration into domestic protections under the Endangered Species Act, though resource constraints persist. Critics note that without precautionary policies for unevaluated taxa—such as interim trade moratoriums— status perpetuates a reactive rather than proactive regulatory paradigm, potentially exacerbating undocumented extinctions in data-poor realms.

Influence on International Agreements

The Not Evaluated (NE) status of numerous species on the undermines the scope and enforcement of key international agreements by leaving vast numbers of potentially threatened taxa outside formal risk-based protections. Under the , which regulates for approximately 40,000 species across its three appendices as of 2023, NE species often evade listing criteria that prioritize documented extinction risks, resulting in unregulated commerce for high-volume traded groups like and . For example, analysis of global trade data revealed 904 species likely threatened by international trade but unprotected by CITES, with hundreds classified as NE or , including 376 unlisted species imported into the alone that face documented threats such as overharvesting. This evidentiary gap influences decision-making, as proposals for Appendix II or III listings frequently reference IUCN assessments; without them, may persist in volumes exceeding regulated counterparts by factors of 3.6 in and 11 in species diversity in major markets. To mitigate this, parties and committees have increasingly incorporated supplementary tools, such as trade volume analyses and rapid assessments, to flag for review, as evidenced by mechanisms developed to identify trade-vulnerable taxa for prioritization in decisions, including the 2019 proposal processes that integrated Red List data gaps. In the (), NE prevalence hampers achievement of monitoring and extinction-risk reduction targets, such as those in the adopted in 2022, which calls for halting human-induced by 2030 and assessing all by 2030 under related indicators. With over 80% of described species remaining NE—totaling more than 2 million taxa as of 2024—the , a core CBD metric for tracking trends in risk, excludes these from calculations, potentially masking broader declines and skewing national biodiversity strategies (NBSAPs) toward already-assessed charismatic vertebrates. These limitations extend to synergies between and , where joint work programs emphasize data sharing, yet NE gaps contribute to documented shortfalls: for instance, 58% of threatened terrestrial lack sufficient interventions, partly attributable to unevaluated status impeding in multilateral environmental agreements. Consequently, agreements like the (Convention on Migratory Species) face similar challenges, with NE migratory taxa underrepresented in action plans, prompting calls for accelerated assessments to align obligations with empirical risk realities.

Criticisms and Alternative Perspectives

Methodological and Bias Critiques

The IUCN Red List's Not Evaluated () category encompasses species that have not undergone formal risk , primarily due to insufficient or prioritization gaps in the process. Methodologically, this leads to significant underrepresentation of risks, as NE taxa often include inconspicuous or understudied groups like and microorganisms, where criteria emphasizing population declines and habitat loss fail to capture subtle threats such as cryptic s. A 2024 analysis found that Red List criteria poorly characterize extinction risk for such species, with few truly extinct taxa recognized, exacerbating deficiencies that hinder comprehensive global assessments. Furthermore, the assessment methodology relies on expert judgment for initial , introducing inconsistencies; ambiguities in guidelines, such as handling subpopulations under intensive , allow assessor to influence whether species enter NE or proceed to full . Taxonomic and geographic biases compound these issues, with NE status disproportionately affecting , , and tropical from the Global South, while vertebrates—particularly charismatic mammals and —receive earlier assessments due to higher research and funding focus. Over a 25-year period, funding analyses revealed deeper taxonomic biases than previously noted, skewing evaluations away from microbial and fungal diversity, which constitute vast portions of undescribed . Geographic imbalances stem from favoring well-studied regions, leaving in data-poor areas perpetually NE despite potential threats; for instance, automated risk modeling predicts many NE reptiles as vulnerable or endangered, yet resource constraints delay formal inclusion. These patterns reflect systemic priorities in academia and NGOs, where aesthetic appeal and accessibility drive assessments, potentially overlooking ecologically critical but less visible taxa. Critics argue that the category's opacity masks true risks, as predictive models indicate over half of (DD) species—often overlapping with NE in data scarcity—are likely threatened, yet the lack of mandatory thresholds for evaluation perpetuates gaps. While the IUCN's quantitative criteria mitigate earlier subjectivity, residual expert discretion in scope selection enables unconscious biases, such as overemphasizing observed declines in accessible habitats while ignoring insidious pressures like variability in remote ecosystems. Peer-reviewed evaluations highlight that such methodological shortcomings not only inflate the NE pool—estimated at millions of —but also undermine policy reliance on the Red List, as unassessed taxa evade protective measures despite evidence of comparable vulnerabilities to assessed ones. Addressing these requires expanded, unbiased protocols, though institutional inertia in funding limits progress.

Debates on Risk Prioritization and Over-Alarmism

Critics of strategies contend that the substantial proportion of Not Evaluated (NE) species—estimated at over 80% of described as of —fuels over-alarmism by implying widespread hidden threats without empirical verification, leading to inefficient toward speculative s rather than documented ones. This perspective holds that assuming high risk for NE taxa, particularly inconspicuous in biodiverse regions, exaggerates the biodiversity crisis, as Red List criteria often fail to detect threats in such groups until post-extinction evidence emerges, yet few verified extinctions occur relative to predictions. For instance, popularized narratives like "Insectageddon" have been criticized for relying on unsubstantiated extrapolations from localized data declines to global collapse, misusing Red List categories to amplify urgency without rigorous causal links to drivers like habitat loss. Proponents of heightened prioritization counter that empirical assessments of formerly NE species frequently reveal elevated threats, with studies showing that in taxa like reptiles and mammals, up to 20-30% of newly evaluated qualify as Vulnerable or worse, underscoring gaps as a barrier to accurate mapping rather than of low risk. They argue that deferring action on NE species in high-pressure ecosystems, such as tropical forests where over 90% of arthropods remain unevaluated, risks irreversible losses, as spatial modeling predicts disproportionate threats from and in these areas. However, skeptics highlight methodological flaws in such predictions, including over-reliance on IUCN categories not designed for prioritization, which can mislead by conflating assessment status with actionable threats and ignoring cost-benefit analyses. Debates intensify over resource misallocation, where over-emphasis on rare or potentially threatened NE species diverts funding from broader interventions benefiting common taxa that sustain ecosystem functions, such as pollination and soil stability provided by non-threatened insects comprising the majority of biodiversity. Conservation prioritization frameworks have been faulted for common errors like ill-defined objectives and failure to integrate risk aversion with feasibility, resulting in reactive single-species efforts that prove costly and ineffective compared to habitat-scale protections. For example, analyses of global funding reveal biases toward charismatic vertebrates, leaving NE invertebrates under-resourced despite their ecological roles, prompting calls for transparent risk-tolerant adaptive management over alarm-driven triage. This tension reflects causal realism in conservation: while NE gaps demand assessment, unsubstantiated alarmism erodes public trust and skews policies toward low-probability, high-visibility interventions at the expense of verifiable, high-impact actions.

Broader Applications and Analogues

Usage in Non-Biodiversity Contexts

The "Not Evaluated" (NE) designation, primarily established in biodiversity risk assessments by the International Union for Conservation of Nature (IUCN), has seen adaptation in non-biological domains such as evaluation. In frameworks assessing threats to (ICH)—encompassing traditions, practices, and expressions passed across generations—NE is applied to ICH projects lacking assessment against predefined criteria, signaling a need for initial data gathering before assigning threat levels. This mirrors the IUCN's use of NE for taxa or ecosystems not yet scrutinized, preventing premature categorization amid data gaps. A specific ICH threat assessment model, inspired by categories, incorporates alongside , Vulnerable, Endangered, , and others like Least Concern. Criteria evaluate two core elements: practitioners (e.g., inheritors' under A, where thresholds include fewer than 100 individuals or 5–10% project coverage) and habitats (e.g., mechanisms under F or funding under H). Grounded in theory, this approach treats ICH elements as dynamic systems analogous to biological populations, with threats arising from demographic shifts, environmental disruptions, or institutional neglect. The model's rationale emphasizes systematic, quantitative evaluation to inform policy, much like IUCN's role in prioritizing actions. Testing on 100 ICH projects in Prefecture, Province, , validated the framework's reliability, yielding 92% alignment with expert opinions on threat status. Of these, unevaluated projects were flagged for urgent baseline surveys, highlighting NE's utility in for cultural preservation amid rapid and pressures. This application extends beyond by addressing human-mediated cultural erosion, where empirical metrics (e.g., inheritor age demographics under Criterion B) enable of decline drivers. In broader non-biodiversity risk paradigms, NE-like statuses denote pending evaluations in systematic inventories, though explicit adoption of the term remains rare outside IUCN-influenced models. For example, in heritage site assessments or indices, initial identifies unassessed assets to avoid underestimating risks from incomplete inventories, prioritizing empirical over assumption. Such parallels underscore NE's foundational : deferring judgment until verifiable accumulates, fostering rigorous prioritization in diverse threat landscapes.

Comparisons to Similar Evaluation Frameworks

The IUCN Red List's category, denoting species that have not undergone formal assessment against its criteria, contrasts with the ranking system, which primarily assesses North American taxa using numerical ranks from G1 (critically imperiled) to G5 (secure) based on factors like , trends, and threats. does not employ a dedicated NE equivalent; instead, species absent from its database or unranked due to insufficient data are effectively unevaluated, though the system emphasizes subnational and global ranks for included taxa without an explicit "not assessed" designation. This approach allows for partial assessments, such as unrankable () modifiers in certain contexts, differing from IUCN's binary NE status for unprocessed species. Comparisons between assessed species reveal moderate correlations between NatureServe ranks and IUCN categories, with G1-G2 often aligning with or Endangered, but handling of unevaluated cases highlights methodological divergence: IUCN's facilitates tracking assessment gaps globally (e.g., only about 2.2 million of 8 million estimated evaluated as of ), while NatureServe's focus on regional data results in fewer global unevaluated entries but prioritizes rarity over extinction risk. NatureServe's criteria overlap with IUCN's in threat evaluation but incorporate broader ecological viability metrics, potentially leading to assessments for species IUCN deems due to limited global data. In regulatory frameworks like the U.S. Endangered Species Act (ESA) of , no direct NE parallel exists; species are either listed as Endangered or Threatened based on petition-driven evaluations or deemed not warranted, leaving most unlisted species—analogous to —in a de facto unevaluated state without systematic risk categorization. ESA assessments emphasize imminent harm and recovery potential under legal mandates, contrasting IUCN's informational by tying status to actionable protections rather than comprehensive inventories; for instance, as of 2011 analyses, ESA covered fewer IUCN-listed species than expected, underscoring gaps in evaluating NE-equivalent taxa. Regional red lists adopting IUCN criteria, such as those in or , replicate the NE category verbatim, minimizing differences but often expanding assessments beyond global efforts.

References

  1. [1]
    IUCN Red List of Threatened Species
    It divides species into nine categories: Not Evaluated, Data Deficient, Least Concern, Near Threatened, Vulnerable, Endangered, Critically Endangered, Extinct ...About · 3.1 · IUCN Green Status · Red List Index (RLI)
  2. [2]
    Frequently Asked Questions - IUCN Red List of Threatened Species
    The IUCN Red List does not include Not Evaluated species. Critically Endangered species may also be tagged as Possibly Extinct or Possibly Extinct in the Wild.
  3. [3]
    IUCN Red List Update: Global Impacts, Regional Statuses, and the ...
    Apr 9, 2025 · The IUCN Red List of Threatened Species™ now includes 169,420 species, of which 47,187 are threatened with extinction, according to the ...
  4. [4]
    Summary Statistics - IUCN Red List of Threatened Species
    The IUCN Red List is updated. For each Red List update, IUCN provides summaries of the numbers of species in each category, by taxonomic group and by country.
  5. [5]
    IUCN Red List of Threatened Species
    Currently, there are more than 172,600 species on The IUCN Red List, with more than 48,600 species threatened with extinction, including 44% of reef building ...Barometer of Life · Citing The IUCN Red List · Searching The IUCN Red List
  6. [6]
    [PDF] IUCN Red List Categories and Criteria
    Feb 9, 2000 · . NOT EVALUATED (NE). A taxon is Not Evaluated when it is has not yet been evaluated against the criteria. Page 19. 16. V. THE CRITERIA FOR ...
  7. [7]
    The IUCN Red List of Threatened Species and Sharks
    A taxon is Not Evaluated (NE) when it is has not yet been assessed under the IUCN criteria. Currently, this applies to most of the world's described species. We ...
  8. [8]
    [PDF] Guidelines for Using the IUCN Red List Categories and Criteria
    NOT EVALUATED (NE). A taxon is Not Evaluated when it is has not yet been evaluated against the criteria. Page 12. Red List Guidelines. 12. The remaining two ...
  9. [9]
    IUCN Red List Categories and Criteria
    The IUCN Red List Categories and Criteria are a system for classifying species at high risk of global extinction.
  10. [10]
    [PDF] iucn red list categories
    Nov 30, 1994 · The IUCN Red List categories, used for 30 years, highlight species under higher extinction risk. The categories are applied to wild populations ...
  11. [11]
    [PDF] IUCN RED LIST CATEGORIES AND CRITERIA
    Feb 9, 2000 · NOT EVALUATED (NE). A taxon is Not Evaluated when it has not yet been evaluated against the criteria. Page 21. 16. V. THE CRITERIA FOR ...
  12. [12]
    IUCN Red List of Threatened Species | Criteria & Facts | Britannica
    Oct 11, 2025 · Not Evaluated (NE), a category used to include any of the nearly 1.9 ... By 2024, 157,000 species had been assessed by using the IUCN Red List ...
  13. [13]
    [PDF] IUCN RED LIST
    Oct 3, 2025 · In passing 160,000 species assessments in 2024, the. IUCN Red List has become a more representative. Barometer of Life but major efforts remain ...<|separator|>
  14. [14]
    IUCN Red List categories and criteria, version 3.1, second edition
    Jan 1, 2012 · The IUCN Red List Categories and Criteria are intended to be an easily and widely understood system for classifying species at high risk of global extinction.
  15. [15]
    Red List Criteria Summary Sheet
    Version 3.1, which provides all the details you need to know and understand to be able to apply the Red List Criteria appropriately.
  16. [16]
    Assessment process - IUCN Red List of Threatened Species
    The IUCN Red List of Threatened Species is essentially a checklist of taxa that have undergone an extinction risk assessment using the IUCN Red List Categories ...Red List Authorities · Red List Index (RLI) · IUCN Species Information...
  17. [17]
    Guidelines for Using the IUCN Red List Categories and Criteria
    The Guidelines for Using the IUCN Red List Categories and Criteria are regularly updated: the current version is version 16 (March 2024).
  18. [18]
    Progress, challenges and opportunities for Red Listing - ScienceDirect
    The IUCN Red List, a key conservation resource, has incomplete and biased coverage. Most known species have yet to be assessed and published on the Red List.Perspective · 1. Introduction · 1.1. Gaps And Bias In Red...Missing: origins | Show results with:origins<|control11|><|separator|>
  19. [19]
    Not Evaluated (NE) - IUCN Classification - Environment Notes - Prepp
    Answer: "Not Evaluated (NE)" is a category in the IUCN Red List, indicating that the species has not yet been assessed for its risk of extinction. · Answer: Some ...
  20. [20]
    Catalyzing Red List Assessments of Underrepresented Taxa ... - MDPI
    Sep 1, 2022 · Several factors are emerging as leading contributors to the relatively low numbers of species assessed within Africa and represented on the Red ...<|separator|>
  21. [21]
    Rapid Least Concern: towards automating Red List assessments
    Jan 23, 2020 · There is, therefore, an urgent need to speed up the Red List assessment and documentation workflow. One reason for this lack of species coverage ...
  22. [22]
    [PDF] IUCN Red List version 2025-1: Table 1a
    Mar 27, 2025 · Table 1a: Number of species evaluated in relation to the overall number of described species, and numbers of threatened species by major groups ...
  23. [23]
    Barometer of Life - IUCN Red List of Threatened Species
    Currently, the IUCN Biodiversity Assessment and Knowledge Team is managing data for over 172,600 species, and this number is set to increase substantially in ...
  24. [24]
    Recognizing the quiet extinction of invertebrates - Nature
    Jan 3, 2019 · Underrepresentation of invertebrates on IUCN Red List. Examples for percentages of species assessed on IUCN Red List by 2018 in comparison ...Abstract · Monitoring Biodiversity And... · Towards Global Collaboration...<|control11|><|separator|>
  25. [25]
    Red List Index (RLI) - IUCN Red List of Threatened Species
    Currently, the RLI is available for five taxonomic groups only (those in which all species have been assessed at least twice): birds, mammals, amphibians, ...Missing: total | Show results with:total
  26. [26]
    Mass extinction in poorly known taxa - PMC - PubMed Central
    Sixty-seven species (33.5%) are known from one locality only, and for 37 species (18.5%) we did not find a precise locality (geographic coordinates or named ...
  27. [27]
    IUCN Red List underestimates national conservation needs of ...
    Specifically, the extinction risk evaluated under the National Red List was much higher for transboundary species (20%) than in the IUCN Red List (10%), while ...Missing: percentage | Show results with:percentage
  28. [28]
  29. [29]
    [PDF] IUCN Red List version 2024-2: Table 1a
    Oct 28, 2024 · Table 1a: Number of species evaluated in relation to the overall number of described species, and numbers of threatened species by major ...Missing: NE | Show results with:NE
  30. [30]
    [PDF] IUCN Red List version 2023-1: Table 1a
    Dec 11, 2023 · Table 1a: Number of species evaluated in relation to the overall number of described species, and numbers of threatened species by major groups ...Missing: NE | Show results with:NE
  31. [31]
    More than one in three tree species worldwide faces extinction - IUCN
    Oct 28, 2024 · The IUCN Red List now includes 166,061 species, of which 46,337 are threatened with extinction. “Today, we are releasing the global assessment ...
  32. [32]
    4485 Tree Assessments Published in First 2024 IUCN Red List Update
    Jun 28, 2024 · Today the IUCN Red List of Threatened Species released its first update for 2024 publishing 4,485 new tree species assessments.
  33. [33]
    New IUCN Red List assessment shows rising extinction ... - AGRI4POL
    Oct 16, 2025 · According to the findings, roughly 100 new wild bee species are now classed as threatened, accounting for around 10% of all assessed species.
  34. [34]
  35. [35]
    The IUCN Red List of Threatened Species 2025 (Indian Wolf)
    Oct 14, 2025 · Indian Wolf Canis lupus ssp. pallipes has most recently been assessed for The IUCN Red List of Threatened Species in 2025.
  36. [36]
    96 percent of the world's species remain unevaluated by the Red List
    Jun 28, 2012 · The Red List has only assessed 4 percent of the world's known species; for the other 96 percent, scientists simply don't know how they are faring.Missing: geographic distribution
  37. [37]
    [PDF] Coordinating the IUCN Red List of North American Tree Species
    Species that have never been processed through the IUCN Red List Categories and Criteria are considered Not Evaluated (NE), the category to which the vast ...Missing: implications | Show results with:implications<|separator|>
  38. [38]
    [PDF] Guidelines for Using the IUCN Red List Categories and Criteria
    The category Not Evaluated applies to taxa that have not yet been evaluated against the Red List Criteria. The term “red-listed” is not defined in IUCN (2001), ...
  39. [39]
    IUCN Red List criteria fail to recognise most threatened and extinct ...
    Red List criteria poorly characterize extinction risk for inconspicuous species. Few truly extinct species will be recognised as such on the Red List.
  40. [40]
    More than 900 at-risk animal and plant species not covered by ...
    The potential for gaps in species protections has been raised during recent CITES meetings, and the researchers are now calling for their findings and ...<|control11|><|separator|>
  41. [41]
    The U.S. market for imported wildlife not listed in the CITES ... - NIH
    The U.S. imports 3.6 times more unlisted species than CITES-listed, with 11 times larger trade quantities, and 376 unlisted species face conservation threats.
  42. [42]
    Identifying species likely threatened by international trade on the ...
    Jul 6, 2023 · Of 38,245 globally threatened and Near Threatened species, 5.8% (2,211 species) are likely to be threatened by international trade (Fig. 1a, ...
  43. [43]
    Global shortfalls in documented actions to conserve biodiversity
    Jun 5, 2024 · For 58% of the world's threatened terrestrial species, we find conservation interventions to be notably insufficient or absent.
  44. [44]
    CITES at CBD CoP16: “Peace with Nature” by ensuring trade in wild ...
    Nov 15, 2024 · Goal A: Human induced extinction of known threatened species is halted, and, by 2050, the extinction rate and risk of all species are reduced ...
  45. [45]
    Ambiguity in guideline definitions introduces assessor bias and ...
    Jul 27, 2015 · We highlight two major issues where such bias influences assessments: relating to fenced subpopulations that require intensive management; and ...
  46. [46]
    Limited and biased global conservation funding means most ... - PNAS
    An analysis of species-based conservation projects over a 25-y period reveals larger and deeper taxonomic biases in funding than previously described.
  47. [47]
    Automated assessment reveals that the extinction risk of reptiles is ...
    May 26, 2022 · NE species were more likely than assessed species to be VU, and EN, and less likely to be predicted as NT or LC (Fig 1B, S7 and S8 Tables). Fig ...
  48. [48]
    Dimension and impact of biases in funding for species and habitat ...
    Taxonomic and aesthetic biases permeate biodiversity conservation. We used the LIFE program—the European Union's funding scheme for the environment—to ...
  49. [49]
    More than half of data deficient species predicted to be threatened ...
    Aug 4, 2022 · However, species classified as “Data Deficient” (DD) regularly mislead practitioners due to their uncertain extinction risk. Here we present ...
  50. [50]
    Clarifying misconceptions of extinction risk assessment with the ...
    Apr 1, 2016 · With the Red List, IUCN fulfils its goal to 'provide information and analyses on the status, trends and threats to species in order to inform ...<|control11|><|separator|>
  51. [51]
    Biases in comparative analyses of extinction risk: mind the gap
    May 28, 2012 · We explore how existing biases influence results of comparative analyses of extinction risk by using subsets of data that attempt to correct for detected ...
  52. [52]
    Alarmist by bad design: Strongly popularized unsubstantiated claims ...
    Mar 19, 2019 · Our third criticism concerns the misuse of the IUCN Red List categories (citation for IUCN 2009 is actually missing from the references) to ...
  53. [53]
    Prioritizing the reassessment of data-deficient species on the IUCN ...
    Sep 26, 2023 · We devised a reproducible method to help red-list assessors prioritize reassessment of DD species and tested it with 6887 DD species of mammals, reptiles, ...Missing: debates | Show results with:debates
  54. [54]
    Using the IUCN Red List to map threats to terrestrial vertebrates at ...
    Aug 30, 2021 · To date, over 100,000 species have been assessed against the IUCN Red List Categories and Criteria, including all amphibians, birds and mammals.
  55. [55]
    Conservation importance of non-threatened species through their ...
    Protect threatened species doesn't ensure the protection of all NCPs and thus of human's well-being. •. We need to consider non-threatened species in ...Missing: criticisms | Show results with:criticisms
  56. [56]
    Six Common Mistakes in Conservation Priority Setting - PMC - NIH
    Mistake 1: Not Acknowledging Conservation Plans are Prioritizations · Mistake 2: Trying to Solve an Ill-Defined Problem · Mistake 3: Not Prioritizing Actions.
  57. [57]
    Limited and biased global conservation funding means most ... - NIH
    Feb 24, 2025 · First, fundamental taxonomic and ecological knowledge is scarce for the majority of species (e.g., arthropods, fungi) and many of these are yet ...
  58. [58]
    Effect of risk aversion on prioritizing conservation projects - PubMed
    We argue for transparency in risk tolerance and recommend that decision makers accept risk in an adaptive management framework to maximize benefits.Missing: criticism | Show results with:criticism
  59. [59]
    Proactive conservation is essential—but not sufficient - Facets Journal
    Sep 4, 2025 · We argue that single-species conservation remains essential for addressing non-habitat threats and for empowering direct recovery actions for ...
  60. [60]
    Intangible cultural heritage threatened-level categories and criteria
    Feb 27, 2025 · And other two categories are: Data Deficient and Not Evaluated, as outlined in Table 2. Evaluation criteria for intangible cultural heritage ...
  61. [61]
    NatureServe Global Conservation Status Ranks
    Listed below are definitions for interpreting NatureServe conservation status ranks at the national (N-rank) and subnational (S-rank) levels.Missing: Evaluated | Show results with:Evaluated
  62. [62]
    Definitions of NatureServe Conservation Status Ranks
    Possible ranks are GXC or GHC. This is equivalent to "Extinct in the Wild (EW) in IUCN's Red List terminology (IUCN 2001). For more detail, see Conservation ...
  63. [63]
    Differences in two species-at-risk classification schemes for North ...
    There was a significant positive correlation between IUCN and NatureServe ranks, although this was not strong (rs = 0.504). Agreement was good for non- ...
  64. [64]
    International Collaboration on Red Listing - NatureServe
    Mar 2, 2021 · The criteria for determining Red List categories have much overlap with the factors used in determining NatureServe status ranks, allowing for ...
  65. [65]
    [PDF] a comparison of the IUCN Red List and U.S. Endangered Species Act
    Oct 3, 2011 · The IUCN Red List, like any categorical imperiled species classification, must make normative de- cisions that include risk tolerance in the ...<|separator|>
  66. [66]
    Regional Assessments - IUCN Red List of Threatened Species
    The IUCN Red List Categories and Criteria were developed for assessing extinction risk at the global level, considering the global population of a taxon.Missing: distinction Evaluated