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Mediterranean monk seal

The (Monachus monachus) is a characterized by its robust body, short dense fur ranging from black in males to brown or in females, blunt , and small external openings. Adults typically reach lengths of 2.4 to 3 meters and weights up to 330 kilograms, with pups born black and featuring a distinctive white ventral patch. Endemic to the coastal regions of the and eastern , particularly around , , , and northwestern , the prefers secluded sea caves and rocky shorelines for resting and pupping. Once abundant across a wider range, M. monachus populations plummeted due to direct through for , oil, and , as well as incidental capture in gear, reducing numbers to critically low levels by the mid-20th century. Current global estimates place the population at 815 to 997 individuals, primarily in three isolated subpopulations, rendering it one of the most endangered pinnipeds. Classified as Endangered by the , ongoing threats include in fisheries, loss from coastal development, , and occasional intentional killings by fishermen viewing seals as competitors. Opportunistic benthic foragers, Mediterranean monk seals primarily consume cephalopods, crustaceans, and bony fishes, diving to depths exceeding 100 meters while exhibiting a shift toward more solitary and cave-dependent behavior in response to historical human pressures. efforts, including protected areas and programs in key sites like the and Cabo Blanco, have stabilized some colonies, though recovery remains precarious without addressing root causes like unregulated and expansion.

Taxonomy and phylogeny

Scientific classification

The Mediterranean monk seal is classified in the family Phocidae, the true seals, and subfamily , which includes the monk seals as a distinct lineage of southern phocids characterized by tropical affinities and specialized cranial features. Its binomial name is Monachus monachus (Hermann, 1779), originally described from Mediterranean specimens, with the genus name reflecting the species' hooded appearance reminiscent of monastic cowls.
Taxonomic rankClassification
KingdomAnimalia
PhylumChordata
ClassMammalia
Order
FamilyPhocidae
Subfamily
GenusMonachus
SpeciesM. monachus
The genus Monachus formerly included three species: the extant Mediterranean monk seal, the extinct Hawaiian monk seal (M. schauinslandi), and the extinct Caribbean monk seal (M. tropicalis), with mitochondrial and nuclear DNA analyses confirming the of Monachus as a cohesive branching deeply within , distinct from other phocid subfamilies. Historical proposals to split Monachus monachus into (e.g., Atlantic vs. Mediterranean forms) have been refuted by molecular studies revealing low genetic differentiation insufficient for subspecific status, instead indicating panmictic populations shaped by recent bottlenecks rather than long-isolated lineages.

Evolutionary history

The Mediterranean monk seal (Monachus monachus) belongs to an ancient lineage within the Phocidae family, with crown-group phocids originating in the North Atlantic or Mediterranean region during the late to early , approximately 27–20 million years ago, based on distributions and phylogenetic reconstructions. The subfamily , encompassing monk seals, diverged from other phocid subfamilies prior to the middle , over 14.6 million years ago, with estimates placing the monachine split from northern seals () around 12 million years ago. Late s from the North Atlantic and Sea regions document early monachine diversity, including transitional forms with specialized cranial and dental adaptations for benthic foraging, though direct antecedents to Monachus remain sparsely represented in the Mediterranean record. Phylogenetic analyses of mitochondrial and nuclear DNA position M. monachus as a basal member of Monachinae, distinct from the monophyletic New World monk seals (Hawaiian and extinct Caribbean species, now classified in Neomonachus). Divergence between Mediterranean and New World lineages occurred in the late Miocene, estimated at 6–12 million years ago depending on calibration methods, reflecting vicariant events tied to Tethys Sea closure and Atlantic circulation changes rather than recent gene flow. This deep split underscores the evolutionary isolation of Monachus, with fossil evidence suggesting monachines dispersed across hemispheres by the Pliocene, though Mediterranean populations adapted to coastal, cave-associated niches amid regional tectonic shifts. Genetic surveys reveal exceptionally low diversity in M. monachus (e.g., mitochondrial control region variation comparable to the lowest in mammals), driven by severe historical bottlenecks from human exploitation since , rather than vicariance or ancient . models indicate effective population sizes plummeted over the last millennium, with levels elevated across remaining subpopulations (e.g., fixation index F_IS >0.2 in loci), contrasting with expectations for an ancient lineage and emphasizing recent causation over phylogenetic . Compared to the extinct , M. monachus exhibits parallel vulnerabilities—low resilience to overhunting due to philopatric breeding and slow —but without evidence of hybridization or shared recent ancestry, as cytochrome b sequences confirm their separation predates Pleistocene glaciations.

Physical description

Morphology and adaptations

The (Monachus monachus) possesses a streamlined, torpedo-shaped optimized for , with a rounded head and short, broad muzzle. Adults range from 2.3 to 2.8 meters in total length and weigh 240 to 400 kilograms, with males attaining slightly greater dimensions than females. The pelage consists of short, dense fur, typically dark brown to on the surface in adult males, transitioning to medium to dark gray in females, with paler ventral regions in both sexes; juveniles are born with a unique white abdominal patch that persists variably into adulthood. Foreflippers are proportionally short with the first elongated, while hindflippers are slender and rotatable, enabling forward propulsion on land through a galloping motion akin to other phocids. Sensitive vibrissae on the muzzle facilitate prey detection in turbid or dark waters, complementing the seal's reliance on nearshore . Physiological adaptations support haul-out in marine caves, including tolerance for confined, humid environments with limited ventilation, though empirical data on thresholds specific to this species remain limited; diving capabilities extend to shallow coastal depths, typically under 100 meters, with extended apnea durations facilitated by elevated stores in muscle tissue.

Reproduction and life history

Mediterranean monk seals exhibit a polygynous mating system, with dominant males defending territories and mating with multiple females, while in size remains limited. Mating takes place in the water, often near caves. lasts 9 to 11 months, after which females give birth to a single pup on land, typically in secluded sea caves. Births occur year-round across the species' range but peak in autumn, from September to November, with October showing the highest incidence in monitored populations such as those in . Females can in consecutive years, though overall fecundity remains low at one pup annually. Pups, born at lengths of about 1 meter and weights of 15-18 , are for 4 to 7 weeks, after which occurs, marking a transition to independent . Some observations indicate potential extensions in nursing duration up to 16-17 weeks, an atypically prolonged pattern among phocid seals. is attained at 4 to 5 years for females and 5 to 6 years for males, with variations noted across subpopulations; for instance, females in the Cabo Blanco colony reach maturity as early as 3 years. Wild lifespan averages 20 to 30 years, though many individuals succumb earlier due to environmental pressures. Pup mortality is empirically high, with mark-recapture studies estimating first-year survival at approximately 46% in the Cabo Blanco population, primarily from , storm-induced displacement in habitats, or abandonment rather than predation. These rates underscore the ' vulnerability during early life stages, as documented through long-term monitoring of tagged and observed individuals.

Ecology and behavior

Diet and foraging

The Mediterranean monk seal (Monachus monachus) exhibits an opportunistic diet dominated by benthic and , as evidenced by stomach content analyses of stranded individuals. Cephalopods, particularly octopuses such as Octopus vulgaris (comprising approximately 43% of prey by number) and Eledone cirrhosa (14%), form the bulk of the diet, often exceeding 90% in some regional samples from the . Benthic fish like eels, mullets, , and from the family are consumed secondarily, with occasional crustaceans such as lobsters and rare pelagic items like sardines or . Dietary composition varies regionally, reflecting local prey availability in coastal habitats, though cephalopods consistently predominate across Aegean and western Mediterranean samples. Stable of seal hair and tissues further corroborates a primary reliance on coastal, benthic resources, showing limited trophic overlap with pelagic targeted by commercial fisheries. Foraging occurs solitarily and targets shallow reefs and seabeds near shorelines, employing bottom-oriented dives to pursue prey in crevices or along currents. Observational and tagging indicate average foraging dive depths of 26 m for shallow bouts and 102 m for deeper benthic excursions, with maximum depths recorded up to 200 m in rehabilitated or free-ranging adults. Pups initiate independent toward the end of (around 4-5 months), starting with shallower U-shaped dives averaging 11 m and progressing to longer bottom times suggestive of active prey pursuit. display flexibility in foraging timing, with patterns including diurnal "spot feeding" in fixed nearshore locations or nocturnal adaptations tied to prey activity, supported by a low that minimizes energy demands during extended bottom phases.

Social behavior and habitat use

The Mediterranean monk seal (Monachus monachus) typically exhibits solitary behavior, with individuals most often observed alone or in small groups of two to three, such as mother-pup pairs or transient aggregations near haul-out sites. This shift from historically more gregarious colonial formations—documented in ancient accounts and early 20th-century photographs of groups numbering dozens—to current solitary tendencies is attributed to chronic human disturbance, which has reduced inter-individual interactions and aggression levels remain low outside of brief mating contexts influenced by moderate . Vocalizations play a key role in , particularly for mother-pup contact; recent acoustic monitoring in the Inner confirmed underwater vocal activity, including pulsed sounds used in pup recognition and bonding, with aerial barks and squawks emitted by pups during nursing interactions. Habitat use centers on secluded coastal environments for resting, pupping, and molting, with a strong preference for sea caves featuring submerged or semi-submerged entrances, protective barriers against , and interior beaches shielded from predators and storms. Rocky coastlines adjacent to these caves serve as primary haul-out zones, where bask diurnally before in nearby shallow waters; and camera-trap data indicate minimal migratory tendencies, with individuals maintaining localized home ranges spanning approximately 15-50 km, as evidenced by repeated use of caves on islands like Kefalonia and in the Greek . While demonstrate behavioral flexibility by shifting from open beaches to caves in response to anthropogenic pressures, empirical observations link persistent disturbances—such as or —to site abandonment, reducing suitability and in affected areas.

Distribution and status

Historical range

The historical range of the Mediterranean monk seal (Monachus monachus) encompassed the entire Mediterranean Sea, including its coastal regions, as well as the Sea of Marmara and the Black Sea, where colonies were established in suitable haul-out sites such as caves and beaches. Evidence from ancient texts, including Aristotle's History of Animals (circa 350 BC), describes the species as living in herds that hauled out on open shores, indicating abundance and widespread distribution across Greek waters during classical antiquity. Pliny the Elder, in Natural History (circa 77 AD), further documented encounters with large groups, corroborating the seal's commonality in Roman-era Mediterranean habitats. Subfossil and archaeological records, including assemblages from prehistoric and ancient sites, confirm the ' presence and utilization by humans across this , with remains found in Bulgarian coastal deposits dating to the and earlier. In the eastern Atlantic, historical distributions extended from the southward to , supported by subfossil evidence and early explorer accounts of rookeries along northwest African coasts prior to intensive exploitation in the . Roman-era mosaics and writings depict seal colonies near coastal settlements, suggesting naive behavior toward humans and large breeding aggregations on accessible beaches throughout the . Empirical estimates derived from find densities and historical narratives indicate pre-exploitation numbered in the thousands across multiple colonies, with genetic studies revealing low historical effective sizes consistent with widespread but structured groups rather than panmictic abundance. These baselines, reconstructed from undiluted archaeological , highlight a once ecologically prominent in coastal ecosystems before systematic hunting reduced rookeries by the late .

Current populations and abundance

The global population of the Mediterranean monk seal (Monachus monachus) is estimated at 600–700 individuals, including 350–450 mature individuals, based on recent surveys and demographic modeling. The species persists in isolated subpopulations, with limited contributing to low and elevated risks, as evidenced by analyses showing reduced haplotypic diversity across groups. The largest core population inhabits the , particularly the Aegean and Ionian Seas, where hosts an estimated 337–450 individuals derived from pup counts multiplied by demographic ratios. In adjacent Turkish waters, abundance along the Aegean and Mediterranean coasts reaches approximately 120 individuals, confirmed through ongoing monitoring. Scattered individuals occur elsewhere in the region, including confirmed presences in and via camera traps and acoustic surveys as of 2024. In the northeastern Atlantic, the Cabo Blanco subpopulation (spanning and ) numbers around 350 individuals, assessed through long-term pup production and survival rate estimates. Smaller, isolated groups persist at sites like (fewer than 30 individuals) and scattered Atlantic islands, with no viable connectivity to mainland populations. These fragmented distributions underscore the ' vulnerability to localized events. In the late , genetic analyses revealed severe population bottlenecks in the Mediterranean monk seal, primarily attributable to intensive during the 19th and early 20th centuries, which drastically reduced across remaining subpopulations rather than environmental factors like variability exerting primacy. These bottlenecks manifested as sharp declines, with effective sizes contracting to levels implying near-extinction risks, evidenced by deficits in heterozygosity and rare alleles in sampled tissues from the onward. A major fluctuation occurred in the summer of 1997 at the Cabo Blanco colony in Mauritania, where approximately two-thirds of the estimated 300 individuals—over 200 seals—died within two months due to saxitoxin poisoning from a toxic dinoflagellate bloom in their prey. This event reduced the colony to roughly 100 survivors, representing a ~67% loss and threatening the subspecies' viability given its status as the largest breeding group. Post-die-off, the population demonstrated natural resilience, rebounding through an intrinsic annual growth rate of approximately 12%, reaching about 200 individuals by the 2020s without reliant translocation efforts. Since the 1990s, overall abundance has exhibited gradual increases, with global estimates rising from fewer than 500 individuals to 600–700 by 2024, driven by diminished direct and localized protections enabling modest . Subpopulations in the , particularly the Aegean, have shown signs of stabilization in recent monitoring, with persistent sightings and vocal detections confirming occupancy amid low but steady numbers around 250–300 scattered individuals as of 2024–2025. This trend contrasts with historical crashes, attributing incremental gains to reduced human-induced mortality rather than abrupt environmental shifts.

Threats and declines

Direct human impacts

Historically, Mediterranean monk seals were extensively hunted for their fur, blubber oil used in lamps and medicines, and meat, contributing significantly to population declines from antiquity through the 20th century. In Greece, deliberate killings by fishermen—often via shooting or explosives in caves—account for approximately 43% of documented adult seal deaths, with incidents persisting into the 2020s despite legal prohibitions. Accidental bycatch in fishing gear, particularly trammel nets, gillnets, and set nets deployed near haul-out sites, remains a direct mortality factor, entangling seals during foraging and leading to drownings. Tourism-related disturbances, including close boat approaches and entries into pupping caves, displace seals from haul-out and breeding sites, with acoustic in 2025 confirming increased vocal activity correlated to vessel noise in the inner . Coastal development, such as holiday housing and infrastructure expansion, has destroyed over 80% of potential open-beach haul-outs and restricted access to sea caves, prompting empirical observations of site abandonment in and since the 1980s.

Environmental and incidental threats

Disease outbreaks represent a significant environmental threat to Mediterranean monk seals, with the most notable event occurring in 1997 when approximately half of the Cabo Blanco population—estimated at over 100 individuals—succumbed to (CeMV) infection along the coasts of and . Necropsies indicated viral pathology consistent with CeMV, though concurrent factors such as from algal blooms of Gymnodinium catenatum may have exacerbated mortality, as evidenced by toxin detection in seal tissues and good body condition of carcasses ruling out starvation. has also emerged as a persistent risk, with serological evidence in strandings and potential co-infection amplifying susceptibility to pathogens like CeMV. These episodic events highlight seals' vulnerability to infectious agents and biotoxins in coastal ecosystems, independent of direct human intervention. Pollution contributes indirectly through ingestion of and of contaminants, as confirmed by necropsies and non-invasive sampling. Fecal analysis from seals in caves detected 166 microplastic particles across samples, with 75% smaller than 3 mm, alongside plastic additives like that could impair health. Trace elements such as and mercury, measured in tissues from strandings, exceed thresholds potentially disrupting immune and endocrine functions, linking elevated levels to anthropogenic runoff and industrial discharges. Oil spills and persistent organic pollutants further compound exposure risks, though quantitative impacts on or remain understudied relative to acute episodes. Incidental entanglement in abandoned or active gear, including and lines, accounts for sporadic mortality across the ' range, often documented via strandings with marks or embedded materials. This threat arises from interactions with static apparatuses in nearshore habitats, with reports indicating as a primary outcome, though precise annual rates vary by region and are derived from fisher observations rather than comprehensive surveys. Predation pressure remains negligible, as the seals' preference for inaccessible underwater caves effectively mitigates attacks from or other predators. While climate-driven changes, such as altering cave accessibility or shifts in prey distribution, are posited as potential stressors, for dominant impacts is limited, with local ecological data emphasizing , , and incidental capture over broader climatic forcings.

Conservation efforts

The Mediterranean monk seal (Monachus monachus) is classified as Vulnerable on the , reflecting a 2023 reassessment that downlisted it from Endangered based on population recovery evidence in key areas. It is listed under Appendix I of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (), which bans international commercial trade in the species and its parts to prevent exploitation-driven declines. Within the , the species receives stringent protection under Annex II and Annex IV of the (Council Directive 92/43/EEC), mandating the designation of Special Areas of Conservation for its habitats—such as marine caves—and prohibiting deliberate capture, killing, or disturbance, with member states required to establish management plans. Under the Barcelona Convention for the Protection of the Marine Environment and the Coastal Region of the Mediterranean, the monk seal is designated a priority species for conservation, with protocols like the Specially Protected Areas and Biological Diversity Protocol obligating signatory states to safeguard breeding sites and prohibit harmful activities. Nationally, protections vary but include full legal bans on and ; in , hosting the largest population, the species is safeguarded in marine protected areas such as Island, designated an in 2014 with no-take zones to minimize human-seal conflicts. These frameworks explicitly prohibit killing, capture, and disruption, yet enforcement remains inconsistent, as evidenced by ongoing deliberate killings linked to interactions. Reports document 49 intentional killings in between 1994 and 2014, often involving shootings due to perceived gear depredation, while isolated cases persist elsewhere, such as a shot seal in in 2017, underscoring gaps in compliance monitoring and deterrence. Fisher surveys indicate seals damage gear on 21% of trips in some regions, correlating with retaliatory acts despite legal penalties.

Monitoring and recovery programs

Monitoring programs for the Mediterranean monk seal employ non-invasive techniques such as photographic identification (photo-ID), which utilizes unique pelage patterns on adult males for individual recognition and population estimation through capture-recapture models. In , the Hellenic Society for the Study and Protection of the Monk Seal (MOm) integrates photo-ID with sighting networks like the Rescue and Information Network (RINT), operational since 1991, to track distribution and abundance. Camera traps are deployed in sea caves across , , and to observe breeding and pupping activities with minimal disturbance, as implemented in Turkish caves since the early and Cypriot surveys identifying multiple individuals during pupping seasons. Satellite tagging provides data on home ranges and movements, with telemetry devices attached to rehabilitated juveniles revealing ranges of approximately 466 km² in the eastern . The Specially Protected Areas Regional Activity Centre (SPA/RAC) under UNEP/MAP coordinates standardized protocols, including camera trap adaptations and telemetry guidelines, with training conducted in Kefalonia, , in September 2023 to enhance across beneficiary countries. In Turkey, the Turkish Research (TUDAV) and SAD-AFAG maintain coastal observation networks for ongoing surveillance, including cave monitoring extended through 2025 in regions like Fethiye-Göcek. Recovery initiatives include rehabilitation centers for orphaned or injured . In , SAD-AFAG operates and rehab facilities, releasing pups such as those documented in ongoing coastal interventions near and since the 2010s. In , MOm has rehabilitated and released dozens of , incorporating post-release monitoring via tags. campaigns by organizations like TUDAV and MOm target fishers to mitigate incidental entanglement and deliberate killings, distributing educational materials on seal presence and avoidance. SPA/RAC-supported efforts in 2024 include capacity-building for monitoring in southern Mediterranean ranges, with projects extending through 2026 to compile standardized data on movements and use. Translocations remain infrequent due to logistical challenges, with focus instead on in-situ rehab and release protocols.

Effectiveness, challenges, and debates

Conservation efforts have yielded localized successes, particularly in protected areas with strict enforcement. In the colony, shared between and , the population demonstrated an intrinsic growth rate of approximately 12% following habitat protections implemented after a 1997 , contributing to a rebound from near collapse. Similarly, in , , monitoring data indicate an increase from 19 individuals in 2013 to 27 in 2021, attributed to reduced human disturbance and fishery regulations. These upticks underscore the efficacy of enforced no-take zones and anti-poaching measures in mitigating direct pressures, though overall abundance remains critically low at 600-700 individuals globally. Persistent challenges include inadequate enforcement across fragmented jurisdictions, ongoing fishery interactions such as in gillnets, and the species' extreme genetic depauperity, which exacerbates evidenced by reduced fertility and skewed sex ratios in remnant populations. Economic disincentives for local fishers, who face income losses from gear damage or restricted access without compensatory programs, hinder compliance and sustain incidental mortality. Coordination deficits among Mediterranean states further undermine transboundary efforts, as past initiatives have faltered due to inconsistent funding and political will. Debates center on threat prioritization, with empirical data emphasizing direct activities—like deliberate killings and encroachment—as proximal causes of decline over secondary factors such as climate-driven prey shifts, which lack causal primacy in models absent human pressures. strategies face contention between reserve-centric approaches, which yield demographic gains but impose regulatory costs on and fisheries (estimated to generate billions annually in the region), and incentive-based alternatives like gear modifications or compensation, potentially more sustainable per economic analyses of similar recoveries. Genetic augmentation via translocations remains controversial; while proposed to counter , analogs in other taxa reveal risks of from with divergent lineages, though intra-Mediterranean exchanges may pose lower threats if genetic distances are minimal.

Human dimensions

Historical exploitation

The Mediterranean monk seal (Monachus monachus) has faced human exploitation since , primarily for its pelts, blubber-derived , , and medicinal substances such as and . Archaeological evidence from sites in the western Mediterranean indicates direct hunting and processing of seals for these resources as early as 10,000 years ago. In antiquity, Roman-era accounts by (ca. 77 AD) highlight the species' docility, which enabled beach-based captures using clubs to target the head or spears and tridents for quick kills, yielding products like fats for treatments and skins valued for their purported tidal sensitivity and protection. Such practices intensified during the period, with seals also captured alive for performances—trained to perform tricks or fight bears—and skins emerging as , priced at 1,250–1,500 denarii in the Edict of Diocletian (301 AD). Conflicts with fishers over net damage and fish predation further drove targeted killings, contributing to early regional declines by the 3rd century AD. Medieval commercial sustained pressure on recovering post-Roman populations, but peaked in the 19th and early 20th centuries through organized slaughters of colonies for oil (used in lamps and treatment) and hides (for and tents), decimating accessible beach-haulouts across the Mediterranean and Atlantic coasts. Historical records document the eradication of large groups, such as those at Cape Blanco in , where colonies numbering in the thousands were targeted until the 1940s, reducing overall abundance by over 80% from pre-industrial levels. In the Black Sea subpopulation, Soviet-era and post-war persecution—including deliberate shootings by fishermen viewing seals as competitors and captures for zoos and aquaria in the —led to functional extirpation, with no confirmed sightings after 1997 despite occasional unverified reports. These direct harvests, peaking before , shifted thereafter toward incidental as commercial incentives waned, but left fragmented remnants totaling fewer than 1,000 individuals by the 1950s.

Cultural and symbolic roles

In ancient , the Mediterranean monk seal featured prominently in narratives tied to sea deities, such as , the "shepherd of the seals" in Homer's , where seals symbolized prophetic and magical elements but were also derided for their "hideous stench" that repelled humans. Seals appeared as divine agents, including a "great dog-seal" sent by to kill Hippolytus, and were linked to transformations, as in the Psamathe turning into a seal to escape pursuit, giving rise to place names like . Their cries were likened to sirens' ominous calls, reinforcing associations with peril at sea, though ancient texts like those of Aelian and emphasized revulsion, describing seals as "malignant" and "evil-smelling." Artistic representations include a Caeretan hydria dating to circa 520 B.C., depicting a monk seal observing a hero's battle with a sea monster, and seal motifs on Phocaean coins from 625–326 B.C., reflecting regional cultural significance. In Roman-era folklore, sealskin was attributed protective qualities against lightning, as noted by Pliny the Elder, yet seals were generally feared for their foul odor and perceived malignancy, appearing in literature as chaotic flood harbingers in Ovid's Metamorphoses. Compared to more ubiquitous marine mammals like dolphins, the monk seal remained relatively obscure in broader folklore, with depictions grounded in localized Mediterranean traditions rather than widespread symbolism. Post-classically, the species influenced heraldry, such as the Madeiran governor's 15th-century coat of arms featuring a "sea-wolf" emblem, denoting the seal's prominence among early settlers. In modern contexts, it has emerged as an emblematic figure in regional awareness efforts, with social and news media coverage of sightings—such as those mapped in from 2020 onward—amplifying public interest despite persistent biases in reporting. Fisher communities have occasionally perceived the seal negatively as a competitor for resources, viewing it as a nuisance akin to historical Roman-era pests, though legal protections have shifted such attitudes in documented cases.

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