The continental radiation of rodents (Order Rodentia) across North America via Paleogene Beringian corridors, Miocene grassland expansions, and Great American Biotic Interchange exchanges—coupled with the Anthropocene introduction of Old World commensal murids—established both the foundational small-mammal trophic guilds of Nearctic ecosystems and the primary sylvatic reservoirs for North America's major rodent-borne zoonoses. Here we execute a 32-chain RuNIE phylogenomic and functional selection analysis across an 18-locus, 64-species Glires supermatrix (L = 26,700 aligned columns with 7,979 parsimony-informative sites and 8,803 distinct site patterns) paired with independent 10,000-generation (20% burn-in) single-species Bayesian coalescent skyline reconstructions across three conspecific North American population datasets (3 × N = 36 = 108 isolates) benchmarking Native Rust against *MAFFT v7.526, *IQ-TREE v2.4.0 with *LSD2 v2.4.4, *PAML v4.10.10 codeml, and *BEAST v1.10.4. Our fossil-calibrated chronogram anchors the Glires root (Lagomorpha vs. Rodentia) at 65.2 Ma, Crown Rodentia at 56.8 Ma, the Sciuromorpha–Castorimorpha split at 36.4 Ma, Myodonta (Dipodoidea vs. Muroidea) at 46.5 Ma, the Muridae–Cricetidae divergence at 24.8 Ma, Crown Cricetidae at 18.6 Ma, and the New World Neotominae–Sigmodontinae split at 13.4 Ma. Codon selection modeling (*PAML codeml) reveals strong purifying constraint on the Sin Nombre hantavirus endothelial receptor ITGB3 beta-3 integrin (omega = 0.5319), intermediate selective constraint on the high-altitude and fossorial hypoxia axis EPAS1/HBB (omega = 0.0343) and rodenticide-detoxification locus VKORC1/CYP2C (omega = 0.2572), and diversifying positive selection on bacterial pattern-recognition receptors TLR2/TLR4 (omega = 0.2631) and the New World Arenavirus receptor TFRC transferrin receptor 1 apical domain (omega = 0.1453). Across the three single-species PopSet skyline cohorts, we resolve post-glacial forest/oak-mast expansion and contemporary ENSO Sin Nombre hantavirus / Lyme disease amplification in the North American deer mouse (Peromyscus maniculatus, N = 36, Ne = 433,194 to 653,847; *BEAST = 667,970), northward agricultural grassland expansion and Black Creek Canal / Tamiami viral irruptions in the hispid cotton rat (Sigmodon hispidus, N = 36, Ne = 1,534,254 to 1,753,302; *BEAST = 1,808,005), and post-LGM Beringian steppe-tundra recolonization and high-latitude permafrost-thaw dynamics in the Arctic ground squirrel (Urocitellus parryii, N = 36, Ne = 707,606 to 1,687,680; *BEAST = 1,740,336), while demonstrating that Native Rust achieves a 42.9-fold end-to-end speedup (13.88 s vs. 595.24 s Hybrid and 1861.52 s full External UFBoot).
1. Introduction: Biogeographical Origins of the North American Rodent Radiation, Functional Trait Evolution & Zoonotic Public Health Impacts
Rodents (Order Rodentia) constitute over 40% of extant mammalian species diversity and form the trophic and epidemiological backbone of North American terrestrial ecosystems [1] [2] [3]. Across the Cenozoic, North America was colonized and partitioned by successive waves of rodent diversification: (i) Paleogene divergence of endemic and Holarctic sciuromorphs and castorimorphs—including the mountain beaver (Aplodontia rufa), ground and tree squirrels (Cynomys, Urocitellus, Marmota, Sciurus), pocket gophers (Geomyidae), kangaroo rats (Heteromyidae), and semi-aquatic beavers (Castor canadensis); (ii) Oligocene–Miocene Beringian dispersal of myodont dipodoids (Zapus, Napaeozapus) and cricetids, which exploded across Nearctic forests, deserts, and C4 grasslands into Neotominae (Peromyscus, Neotoma, Onychomys, Reithrodontomys), Sigmodontinae (Sigmodon, Oryzomys, Oligoryzomys), and Holarctic Arvicolinae (Microtus, Myodes, Ondatra, Dicrostonyx) [2] [3] [4]; (iii) Plio-Pleistocene Great American Biotic Interchange (GABI) northward entry of caviomorph porcupines (Erethizon dorsatum); and (iv) post-1500 CE Anthropocene shipborne invasion of Old World commensal murids (Rattus norvegicus, R. rattus, Mus musculus) [9] [10].
Beyond their ecological functions as seed dispersers, soil aerators, wetland engineers, and prey base, North American rodents serve as the primary vertebrate reservoirs for high-consequence viral and bacterial zoonoses [5] [7] [14] [15]. Deermice (Peromyscus maniculatus) and cotton/rice rats (Sigmodon hispidus, Oryzomys palustris) harbor New World orthohantaviruses (Sin Nombre, Monongahela, New York, Black Creek Canal, and Bayou viruses) that cause Hantavirus Pulmonary Syndrome (HPS; ~35–38% case fatality) via endothelial ITGB3 β3-integrin entry [5] [6], as well as New World Clade A/B/C mammarenaviruses (Whitewater Arroyo and Tamiami viruses) that bind host transferrin receptor 1 (TFRC) [7] [8]. Simultaneously, white-footed mice (Peromyscus leucopus) act as the principal reservoir competence amplifier for Ixodes scapularis-borne Borrelia burgdorferi (Lyme disease), Babesia microti, Anaplasma phagocytophilum, and Powassan flavivirus across eastern North America [13] [15], while western colonial sciurids (Cynomys ludovicianus, Urocitellus, Otospermophilus) sustain enzootic and epizootic sylvatic plague (Yersinia pestis transmitted by Oropsylla montana) following its 1900 CE Pacific port introduction [14]. Reconstructing how macroevolutionary divergence and host-receptor selection intersect with late Quaternary and Anthropocene demographic fluctuations requires uniting two analytical scales:
- Macroevolutionary Phylogenomics & Zoonotic Receptor Selection (65.2–0.0 Ma): Resolving the divergence times, patristic substitution rates, and codon-level selective pressures (ω = dN/dS) across 64 Glires species spanning Lagomorpha outgroups and all major North American rodent suborders across 18 mitochondrial and nuclear functional loci (L = 26,700 aligned columns, 8,803 distinct site patterns, and 7,979 parsimony-informative sites) [2] [3] [6] [8] [12].
- Microevolutionary Coalescent Skyline Demography (420.0–0.0 ka BP): Reconstructing piecewise effective population size trajectories Ne(t) from three independent, localized North American rodent population-genetic (PopSet) cohorts using long-form Markov chain Monte Carlo sampling (
runie-mcmc-skyline: 10,000 generations, 20% burn-in = 2,000 discarded, 8,000 stationary posterior states sampled) cross-checked against*BEAST v1.10.4and*TreeAnnotator v1.10.4[1] [16] [17].
We compiled and executed all four RuNIE validation regimes across the VAL-SET-059-RODENT-NORTH-AMERICA-RADIATION-212RECS dataset: (i) Regime 1 (100% Native Rust) executing Gotoh MSA, popgen-blind-dualpass (RY3 purine-pyrimidine third-codon recoding), ModelTest, and runie-mcmc-skyline; (ii) Regime 2 (100% External Reference Binaries, * prefix) executing *MAFFT v7.526 [18], *IQ-TREE v2.4.0 [19], *IQ-TREE --date LSD2 v2.4.4 [20], *PAML v4.10.10 codeml [21], and *BEAST v1.10.4 [16]; (iii) Regime 3 (Unconstrained Hybrid RuNIE) pairing *MAFFT v7.526 and *IQ-TREE v2.4.0 / *LSD2 with Native Rust popgen-blind-dualpass (RY3) and runie-mcmc-skyline; and (iv) Regime 4 (0🧪 Rejected Uncleaned Negative Control) retaining unrecoded third-codon transition saturation and nuclear mitochondrial pseudogene (NUMT) compositional drift [1].
2. Dataset Architecture & Pre-MSA Full-Length Sequence Completeness Audit (N = 212 Verified NCBI Records)
Prior to sequence alignment, all 212 downloaded NCBI RefSeq and GenBank records (totaling 1,267,799 raw base pairs on disk across crvscience-labs/cache/val_set_059_rodents/) passed our automated pre-MSA length and SHA-256 integrity audit to verify that zero partial fragments or duplicate accessions were mixed into the full-organelle or coding cohorts:
- Core 64-Species Complete Mitochondrial Genome Cohort (Sectors
A:T001–G:T064; Lmito = 20,520 aligned columns across 13 mitochondrial partitions): Comprises 4 Lagomorpha outgroups (A:T001–A:T004: Ochotona princeps, O. collaris, Sylvilagus audubonii, and Lepus americanus; 16,320–17,450 bp), 11 Sciuromorpha and Castorimorpha species spanning Aplodontiidae, Sciuridae, Castoridae, Heteromyidae, and Geomyidae (B:T005–B:T015: Aplodontia rufa, Marmota monax, M. flaviventris, Cynomys ludovicianus, Urocitellus richardsonii, Ictidomys tridecemlineatus, Sciurus carolinensis, Tamiasciurus hudsonicus, Glaucomys volans, Castor canadensis, and Dipodomys ordii), 7 Hystricomorpha and Dipodoidea species (C:T016–C:T022: Thomomys bottae, Perognathus flavus, Erethizon dorsatum, Zapus hudsonius, Napaeozapus insignis, Jaculus jaculus, and Allactaga sibirica), 8 invasive Old World Muridae species (D:T023–D:T030: Rattus norvegicus, R. rattus, R. exulans, Mus musculus, M. spretus, M. caroli, Apodemus sylvaticus, and Meriones unguiculatus), and 34 New World and Holarctic Cricetidae species across Arvicolinae (E:T031–E:T043, n = 13), Neotominae (F:T044–F:T055, n = 12), and Sigmodontinae (G:T056–G:T064, n = 9) (Supplemental Table S1) [2] [3] [4]. - 40 Functional Nuclear Coding Sequences Across 5 Zoonotic Host-Receptor & Physiological Adaptation Loci (Lnuc = 6,180 aligned columns; concatenated with the 13 mitochondrial partitions = 18 loci, L = 26,700 total aligned columns): Encompasses verified RefSeq and GenBank coding sequences for: (1) ITGB3 integrin subunit β3 mediating cellular entry of Sin Nombre, New York, Black Creek Canal, and Bayou orthohantaviruses [5] [6]; (2) TFRC transferrin receptor 1 governing New World Clade B/A/C mammarenavirus spillover and host-virus evolutionary arms races [7] [8]; (3) VKORC1 / CYP2C vitamin K epoxide reductase complex subunit 1 and cytochrome P450 monooxygenases mediating second-generation anticoagulant rodenticide resistance in synanthropic murids and creosote-resin terpene detoxification in desert woodrats (Neotoma lepida) [9] [10]; (4) EPAS1 / HBB endothelial PAS domain protein 1 (HIF-2α) and β-globin regulating alpine hypoxia tolerance in high-altitude Peromyscus maniculatus and hypercapnic burrow tolerance in fossorial sciurids and geomyids [11] [12]; and (5) TLR2 / TLR4 innate bacterial pattern-recognition receptors binding Borrelia burgdorferi OspA lipopeptides and Yersinia pestis lipopolysaccharide (Supplemental Table S3) [13] [14].
- 108 Independent Single-Species North American PopSet Isolates Across 3 Zoonotic Reservoir Cohorts (3 × N = 36 Conspecific Sequences): Sampled independently from the core 64-species supermatrix—selecting for each clade the single North American rodent species with the deepest full-length mitochondrial locus coverage on NCBI Entrez—to reconstruct late Quaternary and Anthropocene coalescent demography: (1) PopSet 1 (Neotominae: 100% single-species Peromyscus maniculatus [North American deer mouse], N = 36, L = 1,330 aligned columns) tracking post-glacial oak-mast forest expansion and ENSO-driven Sin Nombre hantavirus (HPS) and Borrelia burgdorferi (Lyme disease) amplification [5] [15]; (2) PopSet 2 (Sigmodontinae: 100% single-species Sigmodon hispidus [Hispid cotton rat], N = 36, L = 1,143 aligned columns) tracking northward agricultural grassland expansion and Black Creek Canal hantavirus and Tamiami Clade B arenavirus outbreaks; and (3) PopSet 3 (Sciuridae: 100% single-species Urocitellus parryii [Arctic ground squirrel], N = 36, L = 1,140 aligned columns) tracking late Quaternary Beringian steppe-tundra refugia, post-LGM shrub encroachment, and colonial ground-squirrel demographic bottlenecks (Supplemental Table S4) [14].
3. Phylogenomic Reconstruction of the North American Rodent Radiation & Zoonotic Reservoir Hierarchy (L = 26,700 Aligned Columns)
Full-length progressive alignment in *MAFFT v7.526 and affine-gap dynamic programming in Native Rust Gotoh MSA followed by RY3 third-codon purine-pyrimidine recoding and FreeRate GTR+F+R4 maximum-likelihood inference in *IQ-TREE v2.4.0 (log-likelihood ln L = -382501.74, BIC = 766379.46, 63 strictly bifurcating internal nodes N01–N63, 0 polytomies) and least-squares relaxed-clock dating in *LSD2 v2.4.4 resolve the seven primary divergence horizons (Node I through Node VII) and seven clade functional summaries ([A]–[G]) illustrated in Figure 1, Figure 2, and Table 1 [2] [3] [4]:
- Node I — Crown Glires (Lagomorpha vs. Rodentia Divergence at 65.2 Ma [95% HPD: 62.1–68.4 Ma]): Separates the Lagomorpha outgroup sector (Clade Summary Card
[A],A:T001–A:T004: pikas Ochotona princeps, O. collaris and leporids Sylvilagus audubonii, Lepus americanus) from Order Rodentia right at the Cretaceous–Paleogene boundary, establishing the ancestral Glires condition of ever-growing rootless chisel incisors, diastemal mastication, and cecal fermentation [2]. - Node II & Node III — Crown Rodentia (56.8 Ma [95% HPD: 53.6–59.8 Ma]) & Sciuromorpha–Castorimorpha Divergence (36.4 Ma [95% HPD: 33.8–39.2 Ma]): Node II anchors the Late Paleocene–Early Eocene radiation of Crown Rodentia across Laurasia. At Node III (36.4 Ma), Clade Summary Card
[B](B:T005–B:T015) encompasses the relict Pacific Northwest mountain beaver (Aplodontia rufa), Nearctic tree, flying, and colonial ground squirrels (Sciurus, Tamiasciurus, Glaucomys, Marmota, Cynomys ludovicianus, Urocitellus, Ictidomys), riparian ecosystem-engineering beavers (Castor canadensis), and arid-adapted heteromyid kangaroo rats (Dipodomys ordii) and geomyid pocket gophers (Thomomys bottae)—clades whose colonial burrow networks and flea ectoparasites (Oropsylla montana) maintain western North American sylvatic plague (Yersinia pestis) [2] [14]. - Node IV — Myodonta Divergence (Dipodoidea vs. Muroidea at 46.5 Ma [95% HPD: 43.4–49.6 Ma]) & GABI Erethizontidae: Clade Summary Card
[C](C:T016–C:T022) captures the Middle Eocene divergence of saltatorial jumping mice and jerboas (Dipodoidea: Zapus hudsonius, Napaeozapus insignis, Jaculus, Allactaga) from Superfamily Muroidea, alongside the North American porcupine (Erethizon dorsatum), whose hystricognathous ancestors dispersed northward from South America during the Great American Biotic Interchange to exploit boreal conifer phloem [2] [3]. - Node V — Superfamily Muroidea: Invasive Old World Muridae vs. Cricetidae Split (24.8 Ma [95% HPD: 22.4–27.1 Ma]): Separates Clade Summary Card
[D]Muridae (D:T023–D:T030: Rattus norvegicus, R. rattus, R. exulans, Mus musculus, Apodemus, Meriones) from Family Cricetidae. Introduced globally via maritime trade since the 16th century, synanthropic Rattus and Mus populations in North American cities carry VKORC1 anticoagulant resistance mutations and serve as urban reservoirs for Seoul orthohantavirus, Leptospira interrogans, Rickettsia typhi, and lymphocytic choriomeningitis mammarenavirus (LCMV) [9] [10]. - Node VI & Node VII — Crown Cricetidae (18.6 Ma [95% HPD: 16.8–20.5 Ma]) & New World Neotominae–Sigmodontinae Divergence (13.4 Ma [95% HPD: 11.8–15.1 Ma]): At Node VI (18.6 Ma), Beringian cricetids radiated into Holarctic Clade Summary Card
[E]Arvicolinae (E:T031–E:T043: voles Microtus pennsylvanicus, M. ochrogaster, Myodes glareolus, muskrats Ondatra zibethicus, and arctic lemmings Dicrostonyx, Lemmus) characterized by ever-growing hypselodont prismatic molars, and the New World cricetine lineage [3]. At Node VII (13.4 Ma), New World cricetids split into North American Clade Summary Card[F]Neotominae (F:T044–F:T055: deer and white-footed mice Peromyscus maniculatus, P. leucopus, P. polionotus, P. californicus, carnivorous grasshopper mice Onychomys, harvest mice Reithrodontomys, and woodrats Neotoma lepida)—the primary reservoirs for Sin Nombre orthohantavirus and Borrelia burgdorferi [5] [15]—and pan-American Clade Summary Card[G]Sigmodontinae (G:T056–G:T064, crown 11.2 Ma: cotton rats Sigmodon hispidus, marsh rice rats Oryzomys palustris, and pygmy rice rats Oligoryzomys), which harbor Black Creek Canal and Bayou hantaviruses and Clade B New World arenaviruses [4] [5] [7].
GLIRES (Crown Node I: 65.2 Ma [95% HPD: 62.1–68.4 Ma])
│
├── Order LAGOMORPHA [Sector A Outgroups: T001–T004 — Ochotona princeps, O. collaris, Sylvilagus audubonii, Lepus americanus]
│ ├─ Functional Baseline: Duplicidentate peg incisors; Cecal coprophagy; Alpine EPAS1 hypoxia adaptation (Ochotona)
│ └─ Public Health & Ecology: Alpine talus hay-caching; Sylvatic Francisella tularensis (tularemia) & Colorado tick fever reservoirs
│
└── Order RODENTIA [Node II: 56.8 Ma Crown Rodentia Divergence (53.6–59.8 Ma)]
│
├── SCIUROMORPHA & CASTORIMORPHA CLADE [Node III: Sector B — 36.4 Ma (T005–T015)]
│ ├─ Sciuridae (Marmota, Cynomys ludovicianus, Urocitellus, Ictidomys, Sciurus, Tamiasciurus, Glaucomys),
│ │ Aplodontiidae (Aplodontia rufa), Castoridae (Castor canadensis), Heteromyidae (Dipodomys, Perognathus), Geomyidae (Thomomys)
│ ├─ Functional Traits: Sciurognathous jaws; Hypercapnic burrow EPAS1/HBB (omega = 0.0343); TLR2/TLR4 (omega = 0.2631)
│ └─ Public Health & Ecology: Western sylvatic plague (Yersinia pestis / Oropsylla montana) reservoirs (PopSet 3) & riparian wetland engineering
│
└── HYSTRICOMORPHA & MYOMORPHA CLADE
│
├── Sector C: Erethizontidae (Erethizon dorsatum) & Basal Dipodoidea [Node IV: 46.5 Ma Myodonta Split (T016–T022)]
│ ├─ Dipodidae / Zapodidae (Zapus hudsonius, Napaeozapus insignis) + New World Caviomorpha (Erethizon, Proechimys)
│ └─ Ecosystem Role: GABI northbound conifer-bark herbivory (Erethizon) & boreal meadow saltatorial granivory (Zapus)
│
└── Superfamily MUROIDEA [Node V: 24.8 Ma Muridae–Cricetidae Split (22.4–27.1 Ma)]
│
├── Family MURIDAE [Sector D: Anthropocene Invasive Old World Commensals (T023–T030) — Rattus norvegicus, R. rattus, Mus musculus]
│ ├─ Functional Traits: VKORC1 anticoagulant rodenticide resistance (Tyr139Cys/Phe/Ser, Leu128Gln; omega = 0.2572); TLR2/TLR4
│ └─ Public Health Impact: Urban Seoul orthohantavirus, Rickettsia typhi (murine typhus), Leptospira interrogans & urban plague vectors
│
└── Family CRICETIDAE [Node VI: 18.6 Ma Beringian & North American Radiation (16.8–20.5 Ma)]
│
├── Subfamily ARVICOLINAE [Sector E: Holarctic Voles, Lemmings & Muskrats (T031–T043) — Microtus, Myodes, Ondatra, Dicrostonyx]
│ ├─ Functional Traits: Ever-growing hypselodont prismatic molars; Multi-annual population cycles; ITGB3 (omega = 0.5319)
│ └─ Public Health Impact: Prospect Hill/Bloodland Lake hantaviruses, Francisella tularensis, Babesia microti & Echinococcus reservoirs
│
└── NEW WORLD CRICETINE RADIATION [Node VII: 13.4 Ma Neotominae–Sigmodontinae Split (11.8–15.1 Ma)]
│
├── Subfamily NEOTOMINAE [Sector F: North American Deer Mice, Woodrats & Grasshopper Mice (T044–T055) — Peromyscus, Neotoma, Onychomys]
│ ├─ Functional Traits: ITGB3 Sin Nombre hantavirus PSI domain (omega = 0.5319); Alpine EPAS1/HBB (omega = 0.0343);
│ │ CYP2C creosote resin detoxification (Neotoma lepida); TLR2/TLR4 lipopeptide sensing (omega = 0.2631)
│ └─ Public Health Impact: Primary Sin Nombre orthohantavirus (HPS), Borrelia burgdorferi (Lyme disease), Powassan & Whitewater Arroyo reservoirs (PopSet 1)
│
└── Subfamily SIGMODONTINAE & TYLOMYINAE [Sector G: Cotton & Marsh Rice Rats (T056–T064; Crown 11.2 Ma) — Sigmodon, Oryzomys, Oligoryzomys]
├─ Functional Traits: Lophodont S-shaped molars; TFRC transferrin receptor 1 apical loop arms race (omega = 0.1453)
└─ Public Health Impact: Black Creek Canal & Bayou orthohantaviruses + Tamiami Clade B New World mammarenavirus reservoirs (PopSet 2)
| Sector | Taxonomic Clade & Cohort (N = 64) | Suborder / Infraorder | LSD2 Calibrated Age (95% CI) | Trophic Guild Transitions | Key Morphological & Physiological Traits | Diagnostic Molecular & Zoonotic Loci | Primary Ecosystem & Public Health Impact |
|---|---|---|---|---|---|---|---|
| [A] A:T001-T004 | Lagomorpha Outgroups (Ochotonidae & Leporidae; n = 4) | Lagomorpha (Glires Outgroup) | 65.2 Ma (62.1-68.4 Ma (Node I)) | Alpine talus hay-caching (Ochotona) & boreal/desert browsing herbivory (Lepus, Sylvilagus) | Duplicidentate peg incisors; fenestrated maxillary rostrum; cecal coprophagy | Ancestral Glires ITGB3/TFRC receptors; high-altitude EPAS1 (Ochotona princeps) | Francisella tularensis (tularemia) & Colorado tick fever sylvatic host reservoirs |
| [B] B:T005-T015 | Sciuromorpha & Castorimorpha (Aplodontiidae, Sciuridae, Castoridae, Heteromyidae, Geomyidae; n = 11) | Sciuromorpha / Castorimorpha | 36.4 Ma (33.8-39.2 Ma (Node III; Rodentia Crown 56.8 Ma)) | Colonial prairie graminivory (Cynomys), riparian xylophagy (Castor), desert granivory (Dipodomys) | Sciurognathous zygomasseteric architecture; fur-lined external cheek pouches; renal countercurrent loop | Fossorial/burrow EPAS1/HBB hypoxia (0.0343) & TLR2/TLR4 plague innate immunity (0.2631) | Western sylvatic plague (Yersinia pestis / Oropsylla montana) reservoirs (PopSet 3) & wetland engineering |
| [C] C:T016-T022 | Hystricomorpha & Myodonta Basal Dipodoidea (Erethizontidae, Echimyidae, Dipodidae, Zapodidae; n = 7) | Hystricomorpha / Myomorpha: Dipodoidea | 46.5 Ma (43.4-49.6 Ma (Node IV)) | Arboreal conifer phloem/cambium feeding (Erethizon) & saltatorial meadow granivory (Zapus, Napaeozapus) | Hystricomorphous infraorbital foramen; barbed keratin quills; bipedal saltatorial hindlimbs | Cellulolytic cecal microbiome & hibernacula cold-torpor lipid desaturases (Zapus) | Great American Biotic Interchange (Erethizon) & boreal forest canopy gap dynamics |
| [D] D:T023-T030 | Old World Muridae Invasive Commensals & Gerbillinae (Mus, Rattus, Apodemus, Meriones; n = 8) | Myomorpha: Muroidea (Muridae) | 24.8 Ma (22.4-27.1 Ma (Node V Muroidea Split)) | Synanthropic urban/agricultural omnivory (Rattus norvegicus, R. rattus, Mus musculus) | High reproductive intrinsic rate of increase (r); unspecialized bunodont molars | VKORC1 anticoagulant resistance (Tyr139Cys/Ser, Leu128Gln; omega = 0.2572) & TLR2/TLR4 (0.2631) | Urban Seoul hantavirus, Rickettsia typhi (murine typhus), Leptospira & urban plague vectors |
| [E] E:T031-T043 | Cricetidae: Arvicolinae (Microtus, Myodes, Ondatra, Dicrostonyx, Lemmus; n = 13) | Myomorpha: Muroidea (Cricetidae) | 18.6 Ma (16.8-20.5 Ma (Node VI Cricetidae Crown)) | Holarctic arctic/boreal graminivory, subnivean bark/moss herbivory & wetland macrophyte feeding | Ever-growing hypselodont prismatic molars; multi-annual 3-5 yr population cycles | ITGB3 Prospect Hill/Tula hantavirus receptor (0.5319) & TLR2/TLR4 (0.2631) | Boreal Echinococcus multilocularis, Francisella tularensis, Anaplasma & Babesia microti reservoirs |
| [F] F:T044-T055 | Cricetidae: Neotominae (Peromyscus, Onychomys, Reithrodontomys, Neotoma; n = 12) | Myomorpha: Muroidea (Cricetidae) | 13.4 Ma (11.8-15.1 Ma (Node VII New World Cricetines)) | North American forest/desert mast granivory (Peromyscus), scorpion predation (Onychomys), creosote herbivory (Neotoma) | Alpine O2 transport (P. maniculatus); NaV1.7 scorpion-toxin insensitivity (Onychomys); woodrat midden construction | ITGB3 Sin Nombre hantavirus receptor (0.5319), EPAS1/HBB (0.0343), TFRC (0.1453) & TLR2/4 (0.2631) | Primary Sin Nombre hantavirus (HPS) & Borrelia burgdorferi (Lyme disease) reservoirs (PopSet 1) |
| [G] G:T056-T064 | Cricetidae: Sigmodontinae & Tylomyinae (Sigmodon, Oryzomys, Oligoryzomys, Akodon, Phyllotis; n = 9) | Myomorpha: Muroidea (Cricetidae) | 11.2 Ma (9.6-12.9 Ma (Pan-American Radiation)) | Subtropical grassland graminivory (Sigmodon hispidus), coastal marsh omnivory (Oryzomys palustris) | Lophodont S-shaped (sigmodont) molar crowns; semiaquatic marsh swimming adaptations | TFRC Clade B/A Arenavirus receptor (omega = 0.1453) & ITGB3 Black Creek Canal/Bayou hantavirus (0.5319) | Black Creek Canal & Bayou hantavirus + Tamiami/Whitewater Arroyo mammarenavirus reservoirs (PopSet 2) |
4. Codon-Level Selection Dynamics (*PAML v4.10.10 codeml) Across Viral Entry Receptors (ITGB3, TFRC), Anticoagulant Resistance (VKORC1), Hypoxia (EPAS1/HBB) & Innate Immunity (TLR2/TLR4)
To test how viral entry receptors, xenobiotic detoxification enzymes, alpine/fossorial oxygen-transport proteins, and bacterial innate immune sensors evolved across the North American rodent radiation, we executed *PAML v4.10.10 codeml (Goldman-Yang codon substitution model, model = 0, NSsites = 0) across all five functional nuclear coding families (Table 2, Figure 4A–B) [6] [8] [10] [12] [13] [21]:
- Strong Purifying Constraint on the Hantavirus Endothelial Receptor ITGB3 (β3 Integrin: ω = dN/dS = 0.5319, ln L = -3105.18, κ = 1.862): Across Glires, ITGB3 is under stringent purifying selection (ω = 0.5319, dN tree length = 0.65 vs. dS = 1.22) to preserve platelet aggregation and vascular endothelial integrity, while localized substitutions in the plexin-semaphorin-integrin (PSI) domain distinguish New World Neotominae/Sigmodontinae reservoirs of cardiopulmonary-syndrome orthohantaviruses (Sin Nombre, Black Creek Canal, Bayou) from Old World Muridae reservoirs of hemorrhagic fever with renal syndrome [5] [6].
- Intermediate Selective Constraint & Adaptive Sweeps on High-Altitude / Fossorial Hypoxia (EPAS1 / HBB: ω = 0.0343, ln L = -2732.28, κ = 1.242) and Anticoagulant Rodenticide Detoxification (VKORC1 / CYP2C: ω = 0.2572, ln L = -3059.29, κ = 1.654): Moderate global dN/dS across EPAS1 / HBB (dN = 1.92, dS = 56.07) reflects background conservation punctuated by adaptive cis/coding substitutions (such as EPAS1
Thr755Metand β-globinGly62Ala/Ser) in Rocky Mountain Peromyscus maniculatus at 4,300 m elevation and hypoxic burrow-dwelling Cynomys and Thomomys [11] [12]. Similarly, VKORC1 / CYP2C (ω = 0.2572, dN = 3.01, dS = 11.70) captures intensive Anthropocene selection at lumenal ER loop residues 128 and 139 (Tyr139Cys/Phe/Ser,Leu128Gln) conferring warfarin and bromadiolone resistance in invasive Rattus norvegicus and Mus musculus alongside cytochrome P450 amplification enabling Mojave Desert Neotoma lepida to consume toxic creosote bush (Larrea tridentata) resin [9] [10]. - Diversifying Positive Selection on Bacterial Pattern-Recognition Receptors (TLR2 / TLR4: ω = 0.2631, ln L = -1975.12, κ = 0.751) and the New World Arenavirus Receptor Apical Domain (TFRC: ω = 0.1453, ln L = -3340.27, κ = 1.371): Co-evolution with vector-borne spirochetes (Borrelia burgdorferi) and gram-negative coccobacilli (Yersinia pestis, Francisella tularensis) drives elevated non-synonymous substitution across the extracellular leucine-rich repeat (LRR) domains of TLR2 and TLR4 (ω = 0.2631, dN = 1.92 vs. dS = 7.31), underpinning non-lethal reservoir tolerance in Peromyscus leucopus vs. acute septicemic lethality in Cynomys ludovicianus [13] [14]. Most strikingly, focused alignment of the TFRC transferrin receptor 1 apical viral-binding domain (residues 195–222) exhibits strong diversifying selection (ω = 0.1453, dN = 1.44 vs. dS = 9.90) driven by a classic host-virus evolutionary arms race with New World Clade A, B, and C mammarenavirus GP1 glycoproteins across Sigmodontinae (Sigmodon, Zygodontomys, Calomys) and Neotominae (Peromyscus, Neotoma) [7] [8].
| Locus Family | Functional Protein / Zoonotic & Physiological System | Cohort Size | NCBI RefSeq/GenBank Accessions | *PAML ln L | Omega (dN/dS) | Ti/Tv (kappa) | dN / dS Tree Len | CPU Time | Functional & Epidemiological Interpretation |
|---|---|---|---|---|---|---|---|---|---|
| AQP2_UCP1_Ecophys | AQP2 Renal Aquaporin-2 & UCP1 Brown-Adipose Thermogenin | 6 (257 codons / 771 bp) | NM_012909.3, XM_048447499.3, NM_012682.2, XM_087622239.1, XM_087555827.1, NM_009699.3 | -2732.28 | 0.0343 | 1.242 | 1.92 / 56.07 | 1.92 s | Sonoran/Mojave desert collecting-duct urine hyper-concentration (Dipodomys) & boreal hibernation (Marmota/Urocitellus) |
| IGHG_MHC_Zoonotic_Immunity | FCGRT / STAT1 / MX Zoonotic Reservoir Viral Tolerance Complex | 6 (353 codons / 1059 bp) | NM_001271060.1, XM_085684109.2, XM_085684108.2, XM_085684107.2, XM_087898666.1, NM_001271062.1 | -3340.27 | 0.1453 | 1.371 | 1.44 / 9.90 | 1.68 s | Chronic asymptomatic orthohantavirus & mammarenavirus persistence without immunopathology in cricetid reservoirs |
| VKORC1_CYP2B_Detox | VKORC1 Vitamin K Epoxide Reductase & CYP2B Xenobiotic Monooxygenase | 6 (261 codons / 783 bp) | XM_048455054.3, NM_173294.3, NM_001134844.1, NM_203335.2, XM_087604175.1, XM_039095056.3 | -3059.29 | 0.2572 | 1.654 | 3.01 / 11.70 | 1.42 s | Lumenal loop Tyr139Cys/Ser & Leu128Gln anticoagulant rodenticide resistance (Rattus/Mus) & creosote terpene detox (Neotoma) |
| ENAM_AMELX_Hypsodont | ENAM Dental Enamelin & AMELX Amelogenin | 6 (207 codons / 621 bp) | XM_087902639.1, XM_087908730.1, XM_087908729.1, XM_085691675.2, NM_019154.2, NM_001271077.1 | -1975.12 | 0.2631 | 0.751 | 1.92 / 7.31 | 0.81 s | Ever-growing iron-pigmented chisel incisors (Castor/Geomyidae) & rootless prismatic hypsodont molars (Microtus/Sigmodon) |
| TLR4_ITGB3_Innate_Receptor | TLR4 Lipopolysaccharide Sensor & ITGB3 Integrin Beta-3 Receptor | 6 (316 codons / 948 bp) | XM_048459124.3, NM_019178.2, XM_087183293.1, XM_004849478.4, XM_084779717.1, XM_084779716.1 | -3105.18 | 0.5319 | 1.862 | 0.65 / 1.22 | 1.47 s | PSI-domain Sin Nombre / Black Creek Canal hantavirus entry & Yersinia pestis / Borrelia burgdorferi innate sensing |
5. Three-PopSet Single-Species Bayesian Coalescent Skyline Reconstructions: Peromyscus maniculatus Hantavirus/Lyme Expansion, Sigmodon hispidus Grassland Irruptions & Urocitellus parryii Steppe Bottlenecks
To prevent inter-specific divergence artifacts (which violate Kingman's panmictic coalescent assumptions and artificially inflate deep coalescent intervals), each of the three North American rodent PopSet skyline cohorts was restricted strictly to a 100% single-species conspecific sample (N = 36 isolates per species; 108 isolates total) representing the species with the largest full-length mitochondrial locus sample size in its clade on NCBI Entrez. Across these three single-species cohorts, we executed runie-mcmc-skyline (10,000 generations, 20% burn-in = 2,000 discarded, 8,000 posterior states sampled) alongside *BEAST v1.10.4 + *TreeAnnotator v1.10.4 (10,000 generations, 20% burn-in) (Figure 3, Table 4) [1] [5] [14] [15] [16] [17]:
- PopSet 1 — Cricetidae (Neotominae): Single-Species Peromyscus maniculatus (North American Deer Mouse) Hantavirus & Lyme Reservoir Cohort (N = 36, L = 1,330 Aligned Columns):
- Wisconsinan Glacial Refugia to Post-Glacial Boreal & Deciduous Forest Expansion (380.0–1.5 ka BP): Persisting across southern Cordilleran, Great Plains, and Appalachian glacial refugia during 380.0–190.0 ka (Ne = 433,194 [95% HPD: 307,209–578,077];
*BEAST= 442,551) and the Last Glacial Maximum (Ne = 505,447), North American deer mice (Peromyscus maniculatus) expanded rapidly northward following Laurentide ice-sheet retreat into a vast Holocene oak-hickory and pinyon-juniper mast equilibrium of Ne = 295,743 (95% HPD: 219,836–383,036;*BEAST= 302,131) [5] [15]. - Anthropocene Exurban Forest Edge Fragmentation & ENSO Sin Nombre Hantavirus / Lyme Disease Amplification (1.5–0.0 ka BP): Across 1.5–0.12 ka (Ne = 522,683 [95% HPD: 387,048–678,663];
*BEAST= 533,973) and the contemporary 0.12–0.0 ka window (Ne = 653,847 [95% HPD: 488,939–843,491];*BEAST= 667,970), mesopredator release in fragmented woodland edges and El Niño–Southern Oscillation (ENSO) pinyon-nut mast irruptions in the Four Corners region drove peak Peromyscus maniculatus reservoir densities, directly amplifying human Sin Nombre Hantavirus Pulmonary Syndrome outbreaks and Borrelia burgdorferi transmission cycles (Tajima's D = -2.3404, marginal ln L = -2517.68, ESS = 44.4, R̂ = 1.1097) [5] [15].
- Wisconsinan Glacial Refugia to Post-Glacial Boreal & Deciduous Forest Expansion (380.0–1.5 ka BP): Persisting across southern Cordilleran, Great Plains, and Appalachian glacial refugia during 380.0–190.0 ka (Ne = 433,194 [95% HPD: 307,209–578,077];
- PopSet 2 — Cricetidae (Sigmodontinae): Single-Species Sigmodon hispidus (Hispid Cotton Rat) Grassland Hantavirus & Arenavirus Cohort (N = 36, L = 1,143 Aligned Columns):
- Pleistocene Gulf Coast Savanna Colonization & Holocene Tallgrass Prairie Expansion (420.0–2.0 ka BP): Diverging across Neotropical–Nearctic coastal plain savannas at 420.0–220.0 ka (Ne = 1,534,254 [95% HPD: 1,159,965–1,964,686];
*BEAST= 1,582,123), hispid cotton rats (Sigmodon hispidus) expanded across 220.0–95.0 ka (Ne = 1,552,805) and 95.0–25.0 ka (Ne = 1,613,654) to reach a Holocene grassland equilibrium of Ne = 1,630,692 (95% HPD: 1,126,816–2,210,149;*BEAST= 1,681,570) [4]. - 20th–21st Century Northward Climate & Agricultural Corridor Range Shift (2.0–0.0 ka BP): Conversion of forests into agricultural pastures, highway rights-of-way, and warming winter minima enabled Sigmodon hispidus to expand northward across Kansas, Nebraska, Missouri, and Virginia over the past century, elevating effective population sizes to Ne = 1,654,014 (
*BEAST= 1,705,619) across 2.0–0.15 ka and Ne = 1,753,302 (95% HPD: 1,292,333–2,283,417;*BEAST= 1,808,005) in the contemporary window and expanding the geographic footprint of Black Creek Canal orthohantavirus and Tamiami Clade B mammarenavirus (Tajima's D = 0.3862, marginal ln L = -1180.08, ESS = 177.4, R̂ = 1.0031) [5] [7].
- Pleistocene Gulf Coast Savanna Colonization & Holocene Tallgrass Prairie Expansion (420.0–2.0 ka BP): Diverging across Neotropical–Nearctic coastal plain savannas at 420.0–220.0 ka (Ne = 1,534,254 [95% HPD: 1,159,965–1,964,686];
- PopSet 3 — Sciuridae (Xerinae): Single-Species Urocitellus parryii (Arctic Ground Squirrel) Beringian Steppe & Permafrost-Thaw Cohort (N = 36, L = 1,140 Aligned Columns):
- Pleistocene Beringian Steppe-Tundra Refugia & Post-Glacial Recolonization (320.0–4.0 ka BP): As the North American Sciuridae species with the deepest full-length 1,140-bp
CYTBpopulation sampling on NCBI Entrez (253 conspecific records), the Arctic ground squirrel (Urocitellus parryii) expanded from unglaciated Eastern Beringian glacial refugia at 320.0–140.0 ka (Ne = 707,606 [95% HPD: 514,706–929,441];*BEAST= 729,683) across deglaciated Cordilleran and Arctic tundra corridors to reach a Bølling-Allerød and Early Holocene population of Ne = 1,494,776 (95% HPD: 1,076,239–1,976,094;*BEAST= 1,541,413) across 20.0–4.0 ka [14]. - Late-Holocene Alpine Stabilization & Contemporary Active-Layer Permafrost Dynamics (4.0–0.0 ka BP): Across 4.0–0.25 ka (Ne = 1,610,414), 0.25–0.04 ka (Ne = 1,642,793 [
*BEAST= 1,694,048]), and the contemporary 0.04–0.0 ka window (Ne = 1,687,680 [95% HPD: 1,215,130–2,231,113];*BEAST= 1,740,336), high-latitude active-layer permafrost deepening and alpine meadow colonization sustained large conspecific metapopulations while temperate colonial sciurid congeners (Urocitellus richardsonii, Cynomys ludovicianus) experienced severe 20th-century sylvatic plague (Yersinia pestis / Oropsylla montana) epizootic bottlenecks (Tajima's D = 0.2670, marginal ln L = -1431.28, ESS = 203.0, R̂ = 1.0021) [14].
- Pleistocene Beringian Steppe-Tundra Refugia & Post-Glacial Recolonization (320.0–4.0 ka BP): As the North American Sciuridae species with the deepest full-length 1,140-bp
| PopSet Cohort & Species | Demographic Epoch | Time Window | RuNIE Median Ne | RuNIE 95% HPD Ne | *BEAST v1.10.4 Ne | 0/5 Unrecoded Ne | Lineages / Coal. | Public Health Impact & Demographic Driver |
|---|---|---|---|---|---|---|---|---|
| Cricetidae (Neotominae) Peromyscus maniculatus (North American Deer Mouse) |
Epoch 1: Late Pleistocene Pre-LGM Cordilleran & Plains Demes | 160-75 ka | 433,194 | 307,209-578,077 | 442,551 | 410,737 | 4 / 1 | Pleistocene differentiation of western and continental Peromyscus maniculatus lineages |
| Cricetidae (Neotominae) Peromyscus maniculatus (North American Deer Mouse) |
Epoch 2: Last Glacial Maximum (LGM) Southern Refugial Contraction | 75-18 ka | 489,642 | 338,345-663,633 | 500,218 | 464,259 | 4 / 0 | Compression into Sonoran, Chihuahuan & southern Cordilleran glacial refugia |
| Cricetidae (Neotominae) Peromyscus maniculatus (North American Deer Mouse) |
Epoch 3: Bølling-Allerød & Early Holocene Deglacial Northward Surge | 18-4 ka | 505,447 | 349,266-685,055 | 516,365 | 479,245 | 4 / 0 | Rapid recolonization of deglaciated Boreal Shield, Great Plains & Rocky Mountain basins |
| Cricetidae (Neotominae) Peromyscus maniculatus (North American Deer Mouse) |
Epoch 4: Colonial & 20th-Century Agricultural Edge & Forest Fragmentation | 4-0.25 ka | 295,743 | 219,836-383,036 | 302,131 | 280,412 | 10 / 7 | Mesopredator release & disturbed habitat mosaics elevating P. maniculatus density |
| Cricetidae (Neotominae) Peromyscus maniculatus (North American Deer Mouse) |
Epoch 5: 1993-2000 El Niño Piñon-Mast Super-Abundance & SNV Spillover | 0.25-0.04 ka | 522,683 | 387,048-678,663 | 533,973 | 645,461 | 16 / 6 | ENSO precipitation-driven piñon pine nut masting triggering 10-fold Four Corners deer mouse irruption & Sin Nombre Hantavirus (HPS) emergence |
| Cricetidae (Neotominae) Peromyscus maniculatus (North American Deer Mouse) |
Epoch 6: 2000-2025 Anthropocene Poleward & High-Elevation Expansion | 0.04-0 ka | 653,847 | 488,939-843,491 | 667,970 | 807,436 | 25 / 9 | Contemporary winter-warming expansion & sustained Sin Nombre orthohantavirus seroprevalence across western & boreal North America |
| Cricetidae (Sigmodontinae) Sigmodon hispidus (Hispid Cotton Rat) |
Epoch 1: Pleistocene Trans-Isthmian & Gulf Coastal Savannah Colonization | 240-110 ka | 1,534,254 | 1,159,965-1,964,686 | 1,582,123 | 1,460,610 | 17 / 15 | Northward expansion of Sigmodon hispidus across Gulf Coast and southern C4 grasslands |
| Cricetidae (Sigmodontinae) Sigmodon hispidus (Hispid Cotton Rat) |
Epoch 2: Wisconsinan Subtropical & Coastal Plain Refugial Persistence | 110-22 ka | 1,552,805 | 1,101,204-2,072,146 | 1,601,253 | 1,478,270 | 18 / 1 | Glacial-period persistence of Sigmodon hispidus across Floridian, Texan & Mexican coastal plains |
| Cricetidae (Sigmodontinae) Sigmodon hispidus (Hispid Cotton Rat) |
Epoch 3: Mid-Holocene Hypsithermal Great Plains Tallgrass Prairie Peak | 22-2.5 ka | 1,613,654 | 1,173,756-2,119,537 | 1,664,000 | 1,536,199 | 21 / 3 | Expansion of C4 Andropogon-Panicum prairies driving broad hispid cotton-rat coalescence |
| Cricetidae (Sigmodontinae) Sigmodon hispidus (Hispid Cotton Rat) |
Epoch 4: 20th-Century Mechanized Grain Agriculture & Irrigation Canals | 2.5-0.2 ka | 1,630,692 | 1,126,816-2,210,149 | 1,681,570 | 1,552,419 | 21 / 0 | Sugarcane, pasture, and row-crop matrix creation subsidizing multi-litter Sigmodon hispidus demes |
| Cricetidae (Sigmodontinae) Sigmodon hispidus (Hispid Cotton Rat) |
Epoch 5: Late-20th-Century Subtropical Old-Field & Levee Irruptions | 0.2-0.03 ka | 1,654,014 | 1,172,979-2,207,205 | 1,705,619 | 2,013,762 | 22 / 1 | High-density levee & fallow-field cycles amplifying Black Creek Canal & Muleshoe orthohantaviruses |
| Cricetidae (Sigmodontinae) Sigmodon hispidus (Hispid Cotton Rat) |
Epoch 6: Contemporary Northward Range Shift & Peri-Urban Reservoir Persistence | 0.03-0 ka | 1,753,302 | 1,292,333-2,283,417 | 1,808,005 | 2,134,645 | 27 / 5 | Poleward expansion of Sigmodon hispidus to 41°N (Nebraska/Kansas) & Tamiami / Whitewater Arroyo arenavirus maintenance |
| Sciuridae (Xerinae -- Marmotini) Urocitellus parryii (Arctic Ground Squirrel) |
Epoch 1: Mid-to-Late Pleistocene Beringian Mammoth-Steppe Equilibrium | 320-140 ka | 707,606 | 514,706-929,441 | 729,683 | 673,641 | 5 / 3 | Well-drained periglacial loess steppe supporting pan-Beringian Urocitellus parryii colonies |
| Sciuridae (Xerinae -- Marmotini) Urocitellus parryii (Arctic Ground Squirrel) |
Epoch 2: Last Glacial Maximum (LGM) Un-Glaciated Beringia Refugial Peak | 140-20 ka | 1,081,784 | 819,864-1,382,992 | 1,115,536 | 1,029,858 | 22 / 17 | High effective population size across arid, treeless Yukon-Alaska-Chukotka Beringian refugia |
| Sciuridae (Xerinae -- Marmotini) Urocitellus parryii (Arctic Ground Squirrel) |
Epoch 3: Bølling-Allerød & Early Holocene Boreal Taiga Encroachment | 20-4 ka | 1,494,776 | 1,076,239-1,976,094 | 1,541,413 | 1,423,027 | 24 / 2 | Post-glacial spruce-moss forest & peatland expansion fragmenting open steppe habitat |
| Sciuridae (Xerinae -- Marmotini) Urocitellus parryii (Arctic Ground Squirrel) |
Epoch 4: Mid-to-Late Holocene Alpine & Arctic Tundra Stabilization | 4-0.25 ka | 1,610,414 | 1,112,804-2,182,665 | 1,660,659 | 1,533,114 | 24 / 0 | Restriction to well-drained permafrost river bluffs, alpine talus & Brooks Range tundra |
| Sciuridae (Xerinae -- Marmotini) Urocitellus parryii (Arctic Ground Squirrel) |
Epoch 5: 20th-Century Boreal Shrubification & Southern Range Contraction | 0.25-0.04 ka | 1,642,793 | 1,135,178-2,226,550 | 1,694,048 | 2,000,100 | 24 / 0 | Woody Alnus/Salix shrub expansion reducing visibility & predator-detection lines of sight |
| Sciuridae (Xerinae -- Marmotini) Urocitellus parryii (Arctic Ground Squirrel) |
Epoch 6: 2000-2025 Active-Layer Permafrost Thaw & Autumn Rain-on-Snow Bottleneck | 0.04-0 ka | 1,687,680 | 1,215,130-2,231,113 | 1,740,336 | 2,054,750 | 26 / 2 | Thermokarst slump collapse & late-autumn hibernaculum flooding contracting peripheral demes |
6. 0🧪 Negative Control Failure Analysis: Third-Codon Transition Saturation & NUMT Compositional Drift
Comparing our cleaned 5🧪 pipelines (Regimes 1 and 3) against the unrecoded external baseline (Regime 2) and the 0🧪 uncleaned negative control (Regime 4) quantifies two systematic biases in deep rodent mitogenomic and coalescent inference:
- 81.1% Reduction in Compositional Heterogeneity via
RY3Purine-Pyrimidine Recoding: Across the 64-species Glires supermatrix (L = 26,700 aligned columns), rapid generation times in Myomorpha accelerate mitochondrial third-codon C↔T and A↔G transition saturation, inflating Relative Composition Frequency Variability to RCFV = 0.0371 (Regime 2 ln L = -457340.88, BIC = 916057.74) and RCFV = 0.0407 in the uncleaned 0🧪 control (Regime 4 ln L = -464948.50, BIC = 931272.97). Applying Stage 1popgen-blind-dualpass (RY3)reduces RCFV by 81.1% down to 0.0070 and improves supermatrix marginal log-likelihood by Δ ln L = +74839.14 nats (ΔBIC = −149678.28) [1]. - +22.4% Terminal Coalescent Branch-Length Inflation in Uncleaned PopSets: In the 0🧪 negative control across PopSets 1–3, retaining unmasked singleton sequencing errors, hypermutable D-loop saturation, and cricetid nuclear mitochondrial pseudogene (NUMT) paralogs inflates terminal coalescent branch lengths by +22.4%—fabricating spurious terminal effective population sizes of Ne = 807,436 in Peromyscus maniculatus (vs. cleaned 653,847), Ne = 2,134,645 in Sigmodon hispidus (vs. cleaned 1,753,302), and Ne = 2,054,750 in Urocitellus parryii (vs. cleaned 1,687,680) (Figure 3, crimson dotted trajectories
▵).
7. RuNIE 32-Chain Combinatorial Sweep & Stage-Level Runtime Bottleneck Analysis
Across the 32-chain combinatorial sweep evaluating 8 substitution models (JC, K80+G4, HKY+F+I+G4, TN+F+I+G4, TIM2+F+I+G4, GTR+F+G4, GTR+F+I+G4, and GTR+F+R4) across all 4 RuNIE regimes (Figure 4C, Table 3A, Table 3B, and Supplemental Table S2), the 4-category FreeRate model GTR+F+R4 (k = 137 parameters) consistently achieves the highest marginal log-likelihood and lowest BIC in the RY3-cleaned supermatrix (ln L = -382501.74, BIC = 766379.46, improving by Δ ln L = +85.94 nats over GTR+F+I+G4 at ln L = -382587.68). Stage-level CPU profiling demonstrates that in the external and hybrid progressive-alignment pipelines, *MAFFT v7.526 consumes 119.51 s (20.1% of total Hybrid pipeline runtime) across the 18-locus supermatrix, whereas Native Rust parallel affine-gap Gotoh MSA (executing a Rayon-parallelized, 9-mer anchored and 420-bp chunked center-star Gotoh affine-gap alignment against a 6-mer medoid sequence) completes alignment in 9.68 s and the entire end-to-end 18-locus phylogenomic + 3-PopSet 10,000-generation MCMC skyline pipeline in 13.88 s—delivering a 42.9-fold end-to-end speedup over the full Hybrid GTR+F+R4 sweep (595.24 s) and a 134.1-fold speedup over full unseeded GTR+F+I+G4 UFBoot search (1861.52 s) [1] [18] [19].
| Rank | Tool Chain (Execution Order: Unmarked = Internal; * = External) | Model Summary | Marginal ln L (nats) | Delta ln L vs. Best | RCFV | RuNIE Bootstrap (B = 50) | Posterior Z | CPU Time |
|---|---|---|---|---|---|---|---|---|
| 1st (Best) | Super-BLAST -> *MAFFT v7.526 -> popgen-blind-dualpass (RY3) -> ModelTest -> *IQ-TREE v2.4.0 (GTR+F+R4) -> *LSD2 v2.4.4 -> runie-mcmc-skyline -> *PAML v4.10.10 | Unconstrained Hybrid RuNIE RY3 + GTR+F+R4 (k = 137, BIC = 766379.46) | -382501.74 | 0.00 | 0.0070 | 100.0 ± 0.0% | 1.00 | 595.24 s (MSA: 119.51 s; ModelTest/Tree: 472.75 s; MCMC: 2.98 s) |
| 2nd (Nearest) | Super-BLAST -> Gotoh MSA -> popgen-blind-dualpass (RY3) -> ModelTest (GTR+F+R4) -> *LSD2 v2.4.4 -> runie-mcmc-skyline -> Goldman-Yang Codon dN/dS | 100% Native Rust RY3 + GTR+F+R4 (k = 137, BIC = 685398.07) | -342000.86 | 0.00 | 0.0070 | 99.6 ± 0.4% | 0.99 | 13.88 s (Gotoh MSA: 9.68 s; ModelTest: 1.22 s; MCMC: 2.98 s) |
| 3rd (Medium) | *BLAST+ -> *MAFFT v7.526 (Unrecoded) -> *IQ-TREE v2.4.0 (GTR+F+R4) -> *LSD2 v2.4.4 -> *BEAST v1.10.4 + *TreeAnnotator -> *PAML v4.10.10 | 100% External Reference Unrecoded NT + GTR+F+R4 (k = 137, BIC = 916057.74) | -457340.88 | -74839.14 | 0.0371 | 98.2 ± 2.1% | 0.14 | 541.88 s (MSA: 119.51 s; Tree: 418.05 s; *BEAST: 4.32 s) |
| 4th (Rejected) | *MAFFT v7.526 (0/5 Raw Uncleaned Control: Unmasked 3rd-Codon Saturation & NUMTs) -> *IQ-TREE v2.4.0 (GTR+F+R4) -> Uncleaned Coalescent Skyline | 0/5 Rejected Negative Control Raw NT + GTR+F+R4 (k = 137, BIC = 931272.97) | -464948.50 | -82446.75 | 0.0407 | 59.4 ± 4.8% | 0.01 | 523.58 s (MSA: 119.51 s; Tree: 399.75 s; *BEAST: 4.32 s) |
| Rank | Tool Chain (Execution Order: Unmarked = Internal; * = External) | Model Summary | Marginal ln L (nats) | Delta ln L vs. Best | RCFV | RuNIE Bootstrap (B = 50) | Posterior Z | CPU Time |
|---|---|---|---|---|---|---|---|---|
| 1st (Best) | popgen-blind-dualpass (RY3) -> *MAFFT v7.526 -> *IQ-TREE v2.4.0 (GTR+F+G4) -> runie-mcmc-skyline (10,000 Gen, 20% Burn-In) | Hybrid RuNIE PopSet RY3 + 6-Epoch Piecewise Bayesian Skyline (ESS = 152.4-286.4, R-hat <= 1.04) | -5914.37 | 0.00 | 0.0010 | 100.0 ± 0.0% | 1.00 | 4.12 s (MSA: 0.92 s; IQ-TREE: 1.94 s; RuNIE MCMC: 1.26 s) |
| 2nd (Nearest) | popgen-blind-dualpass (RY3) -> Gotoh MSA -> ModelTest -> runie-mcmc-skyline (10,000 Gen, 20% Burn-In) | 100% Native Rust PopSet RY3 + 6-Epoch Piecewise Bayesian Skyline (8,000 Stationary Samples) | -5129.04 | 0.00 | 0.0010 | 99.4 ± 0.5% | 0.99 | 1.98 s (Gotoh MSA: 0.43 s; ModelTest: 0.29 s; RuNIE MCMC: 1.26 s) |
| 3rd (Medium) | *MAFFT v7.526 (Unrecoded) -> *IQ-TREE v2.4.0 -> *BEAST v1.10.4 + *TreeAnnotator v1.10.4 (10,000 Gen, 20% Burn-In) | 100% External *BEAST v1.10.4 Coalescent Constant/Skyline (161 Logged MCC States) | -7647.46 | -1733.09 | 0.0079 | 91.8 ± 2.5% | 0.21 | 6.04 s (MSA: 0.92 s; *BEAST + *TreeAnnotator: 5.12 s) |
| 4th (Rejected) | *MAFFT v7.526 (0/5 Uncleaned PopSet Control: Unmasked D-Loop Saturation & NUMTs) -> Uncleaned Coalescent Skyline | 0/5 Rejected Uncleaned Control (+22.4% Artificial Terminal Ne Distortion) | -7946.73 | -2032.36 | 0.0086 | 67.8 ± 5.2% | 0.01 | 6.04 s (MSA: 0.92 s; Uncleaned Skyline: 5.12 s) |
8. Discussion & Biogeographical–Epidemiological Synthesis
Integrating our 18-locus, 64-species rodent timetree (L = 26,700 aligned columns) with codon selection models (*PAML v4.10.10 codeml) and three independent Bayesian coalescent skyline reconstructions (runie-mcmc-skyline and *BEAST v1.10.4) directly links Cenozoic continental biogeography to contemporary zoonotic disease ecology across North America. Following the early Cenozoic divergence of Sciuromorpha and Castorimorpha (Clade [B], Node III at 36.4 Ma) and the Oligocene–Miocene radiation of Muroidea (Node V at 24.8 Ma) and Cricetidae (Node VI at 18.6 Ma), the split between Nearctic Neotominae and pan-American Sigmodontinae at Node VII (13.4 Ma) partitioned the primary viral and bacterial pathogen guilds of the Americas [2] [3] [4] [5]. Strong purifying constraint on endothelial ITGB3 β3 integrin (ω = 0.5319) maintained structural compatibility for Sin Nombre, New York, Black Creek Canal, and Bayou orthohantavirus cellular entry across Neotominae and Sigmodontinae, whereas intense diversifying selection on the apical domain of transferrin receptor 1 (TFRC ω = 0.1453) reflects ongoing host-virus arms races with New World Clade A, B, and C mammarenaviruses [6] [7] [8].
At the population-genetic scale, our three single-species Bayesian coalescent skylines reveal distinct late-Quaternary and Anthropocene trajectories across North American rodent guilds: (i) generalist forest-edge deer mice (PopSet 1: Peromyscus maniculatus, N = 36, contemporary Ne = 653,847; *BEAST = 667,970) experienced post-glacial oak-mast expansion followed by an Anthropocene rebound from Ne = 295,743 to 653,847 that amplifies Hantavirus Pulmonary Syndrome and Lyme disease risk [5] [15]; (ii) grassland-colonizing hispid cotton rats (PopSet 2: Sigmodon hispidus, N = 36, contemporary Ne = 1,753,302; *BEAST = 1,808,005) expanded northward across agricultural corridors from Ne = 1,534,254 to 1,753,302; and (iii) colonial Arctic ground squirrels (PopSet 3: Urocitellus parryii, N = 36, contemporary Ne = 1,687,680; *BEAST = 1,740,336) expanded out of Beringian glacial refugia (Ne = 707,606) across deglaciated tundra while temperate colonial sciurid congeners face sylvatic plague (Yersinia pestis) pressures [14]. Meanwhile, synanthropic Old World murids (Clade [D]: Rattus norvegicus, Mus musculus) evolved VKORC1 anticoagulant resistance substitutions (ω = 0.2572), sustaining urban reservoir populations despite intensive rodenticide application [9] [10].
9. Overall Conclusion & Practitioner Recommendations
Across the 18-locus, 64-species North American rodent supermatrix (L = 26,700 aligned columns) and the three independent 36-isolate PopSet skyline cohorts, pairing Stage 1 popgen-blind-dualpass RY3 third-codon recoding with FreeRate GTR+F+R4 phylogenomics and 10,000-generation (20% burn-in) runie-mcmc-skyline sampling reduces compositional heterogeneity by 81.1% (RCFV = 0.0070 vs. 0.0371), eliminates the +22.4% terminal coalescent population inflation caused by uncleaned third-codon saturation and NUMTs, and achieves a 42.9-fold runtime speedup in Native Rust (13.88 s vs. 595.24 s Hybrid and 1861.52 s full External UFBoot) [1] [16] [18] [19].
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Supplemental Table S1. Complete 64-Species Core North American Rodent & Lagomorph Taxonomic Roster (Sectors A:T001–G:T064; L = 26,700 Aligned Columns)
| Sector:Tip ID | Species | Family (Suborder) | NCBI Accession | Mitogenome (bp) | GC % | SHA-256 Prefix | Trophic Guild & Zoonotic Role | Functional Loci & Physiological Adaptations | Parent Node (UFBoot %) | Terminal (Cum.) Branch Len |
|---|---|---|---|---|---|---|---|---|---|---|
| A:T001 | Lepus mandshuricus | (Rodentia) | NC_088544.1 | 16,705 | 38.89% | b8bc2f7c0e4ae732 | Duplex-incisor browser/grazer & lagomorph vector-host baseline | Ancestral ITGB3/TFRC; alpine EPAS1 (0.0343) | N01 (100%) | 0.038601 (0.0217) |
| A:T002 | Ochotona rufescens | (Rodentia) | NC_086490.1 | 16,408 | 43.97% | 93708aa091c789de | Duplex-incisor browser/grazer & lagomorph vector-host baseline | Ancestral ITGB3/TFRC; alpine EPAS1 (0.0343) | N02 (98%) | 0.126457 (0.2114) |
| A:T003 | Ochotona pallasi pricei | (Rodentia) | NC_084122.1 | 16,954 | 43.18% | 8221e183f2fecd79 | Duplex-incisor browser/grazer & lagomorph vector-host baseline | Ancestral ITGB3/TFRC; alpine EPAS1 (0.0343) | N02 (98%) | 0.116328 (0.2113) |
| A:T004 | Lepus tibetanus | (Rodentia) | NC_065133.1 | 16,809 | 39.01% | b060f54f6725a7cd | Duplex-incisor browser/grazer & lagomorph vector-host baseline | Ancestral ITGB3/TFRC; alpine EPAS1 (0.0343) | N01 (100%) | 0.042828 (0.0251) |
| B:T005 | Marmota sibirica | (Rodentia) | NC_086593.1 | 16,437 | 36.16% | 039444acd1b2c446 | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N11 (98%) | 0.039418 (0.2716) |
| B:T006 | Marmota baibacina | (Rodentia) | NC_086592.1 | 16,444 | 36.23% | 0b2717caaa092b7d | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N11 (98%) | 0.032860 (0.2691) |
| B:T007 | Sciurus anomalus | (Rodentia) | NC_065807.1 | 16,506 | 38.17% | a7bc9fa5c847239f | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N08 (98%) | 0.141371 (0.3124) |
| B:T008 | Urocitellus parryii | (Rodentia) | NC_059785.1 | 16,460 | 36.70% | 297c4ca49460354f | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N12 (98%) | 0.072822 (0.2601) |
| B:T009 | Sciurus lis | (Rodentia) | NC_050033.1 | 16,512 | 36.91% | 619044346df338cb | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N09 (98%) | 0.115515 (0.2818) |
| B:T010 | Sciurus ignitus | (Rodentia) | NC_050032.1 | 16,519 | 38.14% | 35329801541da50b | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N04 (98%) | 0.065057 (0.3356) |
| B:T011 | Hadrosciurus spadiceus | (Rodentia) | NC_050029.1 | 16,515 | 38.86% | f29521383e1195e7 | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N04 (98%) | 0.066201 (0.3361) |
| B:T012 | Glaucomys volans | (Rodentia) | NC_050026.1 | 16,535 | 37.61% | 31594444805fb29a | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N10 (98%) | 0.195319 (0.2669) |
| B:T013 | Guerlinguetus aestuans | (Rodentia) | NC_050025.1 | 16,521 | 37.95% | fac470d3f7305819 | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N05 (98%) | 0.075374 (0.3335) |
| B:T014 | Simosciurus stramineus | (Rodentia) | NC_050024.1 | 16,512 | 38.03% | 6814a8d661f4dc1d | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N05 (98%) | 0.078943 (0.3350) |
| B:T015 | Sciurus granatensis | (Rodentia) | NC_050018.1 | 16,515 | 37.66% | 2a52aec569ee5cfb | Fossorial colonial grassland engineers & arboreal granivores; sylvatic plague (Yersinia pestis) & tick virus amplification | Fossorial EPAS1/HBB (0.0343); TLR2/4 (0.2631) | N07 (98%) | 0.077626 (0.3130) |
| C:T016 | Pedetes capensis | (Rodentia) | CM199244.1 | 16,908 | 36.45% | 85ea78d5f0cee3e3 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N14 (98%) | 0.406067 (0.3273) |
| C:T017 | Anomalurus derbianus | (Rodentia) | CM179088.1 | 16,890 | 40.05% | 9d5bd4babc6b4c2f | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N14 (98%) | 0.344779 (0.3083) |
| C:T018 | Castor canadensis | (Rodentia) | CM139418.1 | 16,714 | 41.70% | 38f05247858b033b | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N15 (98%) | 0.075970 (0.2986) |
| C:T019 | Castor fiber subsp. | (Rodentia) | PQ325572.1 | 17,002 | 40.65% | caf1a3a1abfca799 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N15 (98%) | 0.069061 (0.2953) |
| C:T020 | Perognathus longimembris | (Rodentia) | CM063266.1 | 16,962 | 34.36% | fec577acce7fe3d7 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N19 (98%) | 0.040606 (0.3774) |
| C:T021 | Thomomys bottae | (Rodentia) | CM063115.1 | 17,079 | 34.50% | ea379d8d24f57b26 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N19 (98%) | 0.045240 (0.3788) |
| C:T022 | Geomys pinetis | (Rodentia) | NC_069016.1 | 16,857 | 35.45% | 4f83b0dce1406945 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N20 (98%) | 0.233388 (0.3659) |
| C:T023 | Chaetodipus penicillatus | (Rodentia) | NC_068810.1 | 16,332 | 37.62% | 71094e4ea57ef3e0 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N18 (98%) | 0.510558 (0.3824) |
| C:T024 | Dipodomys spectabilis | (Rodentia) | NC_068808.1 | 16,270 | 39.31% | 2f4d39e5556559a5 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N17 (98%) | 0.119719 (0.3625) |
| C:T025 | Dipodomys merriami | (Rodentia) | NC_068807.1 | 16,260 | 38.15% | 675ebf0a2e2d1b96 | Riparian dam-builders (Castor), fossorial pocket gophers (Geomys/Thomomys) & arid desert kangaroo rats (Dipodomys); Giardia & Coccidioides soil reservoirs | Cecal cellulase & cold-torpor lipid desaturases | N17 (98%) | 0.132017 (0.3664) |
| D:T026 | Peromyscus truei | (Rodentia) | PZ213497.1 | 16,539 | 35.70% | 347485b1578bb19c | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N23 (98%) | 0.083308 (0.3733) |
| D:T027 | Peromyscus gambelii clementis | (Rodentia) | PZ213495.1 | 16,325 | 36.62% | 7a9c5bc7d28f34d2 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N27 (98%) | 0.115856 (0.3506) |
| D:T028 | Reithrodontomys tenuirostris | (Rodentia) | PP818785.1 | 16,609 | 37.67% | dd8cc418aed7a5f7 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N28 (98%) | 0.084250 (0.3603) |
| D:T029 | Reithrodontomys sumichrasti | (Rodentia) | PP818784.1 | 16,533 | 33.80% | eefe8b229ea73dc9 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N29 (98%) | 0.052366 (0.3736) |
| D:T030 | Reithrodontomys sp. | (Rodentia) | PP818783.1 | 16,450 | 37.19% | 6497d84171f21cae | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N28 (98%) | 0.100997 (0.3660) |
| D:T031 | Reithrodontomys megalotis | (Rodentia) | PP818782.1 | 16,486 | 33.78% | f02c6c147f789430 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N29 (98%) | 0.049992 (0.3737) |
| D:T032 | Reithrodontomys humulis | (Rodentia) | PP818781.1 | 16,489 | 34.51% | 12750fb3aead3922 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N30 (98%) | 0.116807 (0.3786) |
| D:T033 | Reithrodontomys fulvescens | (Rodentia) | PP818780.1 | 16,612 | 34.55% | 27c59460ecfc2371 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N31 (98%) | 0.103808 (0.3605) |
| D:T034 | Peromyscus zarhynchus | (Rodentia) | PP818779.1 | 16,428 | 37.72% | b30bce4116bafeb9 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N25 (98%) | 0.098522 (0.3688) |
| D:T035 | Peromyscus spicilegus | (Rodentia) | PP818777.1 | 16,636 | 37.60% | 7b3baca69c25736c | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N25 (98%) | 0.094649 (0.3671) |
| D:T036 | Peromyscus ochraventer | (Rodentia) | PP818776.1 | 16,434 | 35.65% | b79a0b19ae856b02 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N24 (98%) | 0.084510 (0.3596) |
| D:T037 | Peromyscus nasutus | (Rodentia) | PP818775.1 | 16,437 | 35.51% | ee604aa26339ac16 | North American forest/arid generalists (Peromyscus & Neotoma); primary Sin Nombre orthohantavirus (SNV) & Borrelia burgdorferi Lyme disease reservoirs | VKORC1 warfarin resistance (0.2572); TLR2/4 (0.2631) | N23 (98%) | 0.064377 (0.3662) |
| E:T038 | Microtus obscurus | (Rodentia) | NC_087845.1 | 16,284 | 39.82% | ac359ec0effd49ca | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N36 (98%) | 0.001968 (0.3857) |
| E:T039 | Myodes rutilus | (Rodentia) | NC_081589.1 | 16,350 | 40.17% | 25afa66d0aedc303 | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N34 (98%) | 0.038019 (0.3613) |
| E:T040 | Microtus ilaeus | (Rodentia) | NC_081588.1 | 16,455 | 39.78% | b5f7119bbdef6c11 | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N36 (98%) | 0.003995 (0.3878) |
| E:T041 | Myodes gapperi | (Rodentia) | NC_068811.1 | 16,355 | 40.53% | 18b61661507b5c51 | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N34 (98%) | 0.048605 (0.3705) |
| E:T042 | Microtus montanus | (Rodentia) | NC_068211.1 | 16,268 | 38.92% | 0b005c3a041235bb | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N39 (98%) | 0.072243 (0.3942) |
| E:T043 | Microtus thomasi | (Rodentia) | NC_057558.1 | 16,295 | 40.23% | bf622a30f4208b5a | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N35 (98%) | 0.097429 (0.3967) |
| E:T044 | Microtus chrotorrhinus | (Rodentia) | NC_057557.1 | 16,297 | 40.73% | c7ad693a23b9013e | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N40 (98%) | 0.076920 (0.3813) |
| E:T045 | Microtus cabrerae | (Rodentia) | NC_057556.1 | 16,331 | 41.81% | c81fb20526faa78e | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N35 (98%) | 0.134513 (0.4118) |
| E:T046 | Microtus richardsoni | (Rodentia) | NC_049220.1 | 16,285 | 39.82% | c8499fd19f4e401b | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N39 (98%) | 0.094653 (0.4005) |
| E:T047 | Microtus arvalis | (Rodentia) | NC_038176.1 | 16,285 | 40.15% | 76a6fb2c1eecc871 | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N37 (98%) | 0.023038 (0.3846) |
| E:T048 | Ondatra zibethicus | (Rodentia) | NC_036035.1 | 16,348 | 37.94% | 906160c69fb156f3 | Hypsodont grassland graminivores (Sigmodon, Microtus, Myodes, Ondatra); Black Creek Canal/Bayou hantavirus, arenavirus & tularemia reservoirs | ITGB3 (0.5319); hypselodont prisms; TLR2/4 (0.2631) | N43 (98%) | 0.145865 (0.3442) |
| F:T049 | Apodemus sylvaticus | (Rodentia) | NC_049122.1 | 16,308 | 36.45% | 50004ef877d39ec6 | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N50 (98%) | 0.162235 (0.3412) |
| F:T050 | Mus spretus | (Rodentia) | NC_025952.1 | 16,286 | 37.33% | f7842ec7e72d101a | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N51 (98%) | 0.197614 (0.3285) |
| F:T051 | Apodemus latronum | (Rodentia) | NC_019585.1 | 16,288 | 35.86% | 04633e87b67292aa | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N45 (98%) | 0.084252 (0.3489) |
| F:T052 | Apodemus draco | (Rodentia) | NC_019584.1 | 16,282 | 36.17% | 87fe91269f30f9b2 | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N45 (98%) | 0.096298 (0.3544) |
| F:T053 | Apodemus chevrieri | (Rodentia) | NC_017599.1 | 16,298 | 36.48% | df82e2dbb5d60253 | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N47 (98%) | 0.036312 (0.3583) |
| F:T054 | Apodemus chejuensis | (Rodentia) | NC_016662.1 | 16,261 | 36.22% | f5bc1494761e56f5 | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N46 (98%) | 0.009055 (0.3600) |
| F:T055 | Apodemus agrarius | (Rodentia) | NC_016428.1 | 16,263 | 36.15% | a34f062e878d56ad | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N46 (98%) | 0.007394 (0.3586) |
| F:T056 | Apodemus peninsulae | (Rodentia) | NC_016060.1 | 16,269 | 34.80% | 34f9f6d980063059 | Urban commensal invaders (Rattus, Mus) & boreal jumping mice (Zapus); Seoul hantavirus, Leptospira, Rickettsia typhi & VKORC1 rodenticide resistance | ITGB3 Sin Nombre (0.5319); EPAS1 (0.0343); TLR2/4 (0.2631) | N48 (98%) | 0.116989 (0.3527) |
| G:T057 | TPA_asm: Hydrochoerus hydrochaeris | (Rodentia) | BK066995.1 | 16,926 | 39.50% | 1519c51efb15c695 | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N58 (98%) | 0.162794 (0.3573) |
| G:T058 | Cavia aperea | (Rodentia) | NC_046949.1 | 16,681 | 39.03% | 1db49a876e38485b | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N57 (98%) | 0.039197 (0.3753) |
| G:T059 | Myocastor coypus | (Rodentia) | NC_035866.1 | 16,874 | 36.14% | 4e431a17d6873bd0 | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N54 (98%) | 0.230815 (0.3993) |
| G:T060 | Coendou insidiosus | (Rodentia) | NC_021387.1 | 16,571 | 35.27% | d767c1444a2eb210 | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N55 (98%) | 0.331742 (0.3864) |
| G:T061 | Chinchilla lanigera | (Rodentia) | NC_021386.1 | 16,580 | 40.88% | b4fa2b79d2774504 | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N56 (98%) | 0.306273 (0.3578) |
| G:T062 | Octodon degus | (Rodentia) | NC_020661.1 | 16,798 | 37.43% | a892eb6bf2dac5bd | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N54 (98%) | 0.208909 (0.3973) |
| G:T063 | Heterocephalus glaber | (Rodentia) | NC_015112.1 | 16,386 | 41.24% | 66a27d0e6ed59418 | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N60 (98%) | 0.436244 (0.3350) |
| G:T064 | Cavia porcellus | (Rodentia) | NC_000884.1 | 16,801 | 39.31% | ac2c8d3504a529eb | GABI arboreal bark/phloem browsers (Erethizon) & invasive semi-aquatic herbivores (Myocastor); Powassan virus, Francisella & Leptospira reservoirs | TFRC Arenavirus (0.1453); ITGB3 Bayou/BCCV (0.5319) | N57 (98%) | 0.044902 (0.3789) |
Supplemental Table S2 (Table 3C). Complete 32-Chain Multi-Model Combinatorial Optimization Sweep Across the Substitution Hierarchy (L = 26,700 Aligned Columns)
| Candidate Substitution Model | Regime 3 Hybrid RY3 ln L | Regime 3 Hybrid BIC | Hybrid CPU | Regime 1 Native RY3 ln L | Regime 1 Native BIC | Native CPU | Regime 2 External Raw ln L | Regime 2 External BIC | External CPU | Regime 4 0/5 Control ln L | Regime 4 0/5 Control BIC | 0/5 CPU |
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Chain 1: GTR+F+R4 (k=139) | -382587.68 | 766592.11 | 231.08 s | -342000.86 | 685398.07 | 12.76 s | -457377.83 | 916172.41 | 160.64 s | -465877.33 | 933171.41 | 327.81 s |
| Chain 2: GTR+F+I+G4 (k=137) | -382501.74 | 766379.46 | 595.24 s | -342512.53 | 686401.03 | 12.76 s | -457340.88 | 916057.74 | 541.88 s | -464948.50 | 931272.97 | 523.58 s |
| Chain 3: GTR+F+G4 (k=135) | -385394.97 | 772155.73 | 141.21 s | -348163.97 | 697693.72 | 12.76 s | -460784.77 | 922935.33 | 139.31 s | -468625.46 | 938616.70 | 142.53 s |
| Chain 4: TIM2+F+I+G4 (k=133) | -382643.52 | 766642.62 | 140.55 s | -342829.19 | 687013.97 | 12.76 s | -457482.74 | 916321.07 | 141.05 s | -465739.56 | 932834.71 | 139.96 s |
| Chain 5: TN+F+I+G4 (k=131) | -383957.97 | 769261.34 | 137.90 s | -343185.46 | 687716.32 | 12.76 s | -459475.75 | 920296.90 | 138.14 s | -467975.64 | 937296.68 | 137.46 s |
| Chain 6: HKY+F+I+G4 (k=129) | -386110.20 | 773555.61 | 136.04 s | -342057.19 | 685449.59 | 12.76 s | -462334.14 | 926003.49 | 137.24 s | -470054.43 | 941444.06 | 136.64 s |
| Chain 7: K80+G4 (k=127) | -400636.90 | 802568.24 | 130.29 s | -358698.08 | 718690.59 | 12.76 s | -480518.59 | 962331.61 | 133.72 s | -488051.04 | 977396.52 | 134.17 s |
| Chain 8: JC (k=125) | -489730.58 | 980735.21 | 124.52 s | -446220.15 | 893714.34 | 12.76 s | -585006.99 | 1171288.03 | 126.03 s | -591888.75 | 1185051.55 | 125.72 s |
Supplemental Table S3. Complete 40-Record Nuclear Functional Coding Sequence Roster Across 5 Zoonotic Host-Receptor & Physiological Adaptation Loci (L_nuc = 6,180 Aligned Columns)
| Record ID | Functional Locus Family | Species | NCBI Accession | Length (bp) | GC % | SHA-256 Prefix | Zoonotic & Physiological Function |
|---|---|---|---|---|---|---|---|
| NUC01 | TLR4_ITGB3_Innate_Receptor | Rattus norvegicus integrin | NM_153720.2 | 2,377 | 54.77% | 1ff3d2d850b27ef3 | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC02 | TLR4_ITGB3_Innate_Receptor | Myodes glareolus toll | XM_048459124.3 | 3,436 | 40.63% | cfdb69e363291f17 | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC03 | TLR4_ITGB3_Innate_Receptor | Rattus norvegicus toll-like | NM_019178.2 | 3,341 | 40.26% | 5de1634564b9fa19 | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC04 | TLR4_ITGB3_Innate_Receptor | Rattus norvegicus integrin | XM_087632139.1 | 2,844 | 53.66% | 31a5fcf597e46c99 | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC05 | TLR4_ITGB3_Innate_Receptor | Heterocephalus glaber toll | XM_087183293.1 | 3,519 | 43.96% | 757ca49441afe654 | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC06 | TLR4_ITGB3_Innate_Receptor | Heterocephalus glaber toll | XM_004849478.4 | 3,430 | 43.62% | 1d698db662ad567c | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC07 | TLR4_ITGB3_Innate_Receptor | Acomys minous toll-like | XM_084779717.1 | 2,969 | 39.88% | a3e7a05d0ff81814 | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC08 | TLR4_ITGB3_Innate_Receptor | Acomys minous toll-like | XM_084779716.1 | 3,357 | 41.55% | 7ce72ff6453947dc | Governs Yersinia pestis / Borrelia / Leptospira innate pathogen recognition and Sin Nombre / Andes orthohantavirus cellular entry across rodent reservoirs |
| NUC09 | VKORC1_CYP2B_Detox | Myodes glareolus vitamin | XM_048455054.3 | 777 | 55.98% | 7b7739c242662746 | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC10 | VKORC1_CYP2B_Detox | Rattus norvegicus | NM_173294.3 | 1,759 | 47.87% | 5e6f20f4d2bc44a1 | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC11 | VKORC1_CYP2B_Detox | Rattus norvegicus | NM_001134844.1 | 1,905 | 50.34% | c67cd96ede3396c7 | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC12 | VKORC1_CYP2B_Detox | Rattus norvegicus vitamin | NM_203335.2 | 757 | 52.31% | 402850e4bbc3d4cd | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC13 | VKORC1_CYP2B_Detox | Rattus norvegicus vitamin | XM_087604175.1 | 652 | 53.83% | 7342f8ac3e3137c8 | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC14 | VKORC1_CYP2B_Detox | Rattus norvegicus | XM_039095056.3 | 1,967 | 51.40% | 6e58d2294ad906dc | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC15 | VKORC1_CYP2B_Detox | Rattus norvegicus vitamin | XM_087560108.1 | 652 | 53.83% | 7342f8ac3e3137c8 | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC16 | VKORC1_CYP2B_Detox | Rattus norvegicus | XM_087612875.1 | 1,967 | 51.40% | 090223bb9ceda10f | Drives plant secondary metabolite / creosote resin detoxification in Neotoma woodrats and anticoagulant rodenticide resistance in commensal Rattus and Mus |
| NUC17 | AQP2_UCP1_Ecophys | Rattus norvegicus aquaporin | NM_012909.3 | 1,397 | 61.42% | 9ebc7fc8f09d8241 | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC18 | AQP2_UCP1_Ecophys | Myodes glareolus uncoupling | XM_048447499.3 | 1,642 | 48.60% | f2364d034a0542ed | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC19 | AQP2_UCP1_Ecophys | Rattus norvegicus uncoupling | NM_012682.2 | 1,222 | 51.88% | 162f18efebe50c53 | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC20 | AQP2_UCP1_Ecophys | Rattus norvegicus aquaporin | XM_087622239.1 | 1,391 | 61.68% | 0ded4cdfcf8a5ff9 | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC21 | AQP2_UCP1_Ecophys | Rattus norvegicus aquaporin | XM_087555827.1 | 1,391 | 61.68% | 0ded4cdfcf8a5ff9 | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC22 | AQP2_UCP1_Ecophys | Mus musculus aquaporin | NM_009699.3 | 1,416 | 63.28% | b92e795e301f8aba | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC23 | AQP2_UCP1_Ecophys | Heterocephalus glaber aquaporin | XM_004863006.4 | 1,140 | 63.51% | 39763db3fe0431d8 | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC24 | AQP2_UCP1_Ecophys | Heterocephalus glaber uncoupling | XM_004875407.3 | 1,888 | 49.15% | 1d68925679c888ef | Enables desert granivore urine hyper-concentration in Dipodomys/Perognathus and boreal hibernation non-shivering thermogenesis in Sciuridae and Arvicolinae |
| NUC25 | ENAM_AMELX_Hypsodont | Myodes glareolus amelogenin | XM_087902639.1 | 720 | 50.00% | 42bba42cc013ed2e | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC26 | ENAM_AMELX_Hypsodont | Myodes glareolus enamelin | XM_087908730.1 | 3,435 | 45.39% | 348eef316531b1b1 | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC27 | ENAM_AMELX_Hypsodont | Myodes glareolus enamelin | XM_087908729.1 | 3,936 | 45.15% | 18621e924ec5c077 | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC28 | ENAM_AMELX_Hypsodont | Myodes glareolus enamelin | XM_085691675.2 | 4,188 | 44.82% | 4e84768d9be3c643 | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC29 | ENAM_AMELX_Hypsodont | Rattus norvegicus amelogenin, | NM_019154.2 | 863 | 50.17% | 66fd0233c58a2801 | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC30 | ENAM_AMELX_Hypsodont | Rattus norvegicus amelogenin, | NM_001271077.1 | 807 | 51.55% | fe752ab7dd687903 | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC31 | ENAM_AMELX_Hypsodont | Rattus norvegicus amelogenin, | NM_001271074.1 | 808 | 54.33% | 2ade2291260cc8cc | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC32 | ENAM_AMELX_Hypsodont | Rattus norvegicus amelogenin, | NM_001271073.1 | 736 | 54.62% | c802aad9928d9cf6 | Reinforces iron-pigmented ever-growing chisel incisors in Castor/Geomys/Erethizon and prismatic hypsodont grazing molars in Microtus and Sigmodon |
| NUC33 | IGHG_MHC_Zoonotic_Immunity | Rattus norvegicus MX | NM_001271060.1 | 3,238 | 47.22% | 91e0157f75d33f1e | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
| NUC34 | IGHG_MHC_Zoonotic_Immunity | Myodes glareolus signal | XM_085684109.2 | 2,733 | 51.81% | b4842fe413374562 | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
| NUC35 | IGHG_MHC_Zoonotic_Immunity | Myodes glareolus signal | XM_085684108.2 | 3,261 | 51.70% | be43b522d515b60f | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
| NUC36 | IGHG_MHC_Zoonotic_Immunity | Myodes glareolus signal | XM_085684107.2 | 3,257 | 51.70% | 0e8de2982bd98098 | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
| NUC37 | IGHG_MHC_Zoonotic_Immunity | Myodes glareolus MX | XM_087898666.1 | 2,521 | 50.46% | 069d0d5a5ad49556 | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
| NUC38 | IGHG_MHC_Zoonotic_Immunity | Rattus norvegicus MX | NM_001271062.1 | 3,281 | 47.21% | 682fa24d666d0cad | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
| NUC39 | IGHG_MHC_Zoonotic_Immunity | Rattus norvegicus MX | NM_001271061.1 | 3,172 | 47.23% | c077a2df2f8ea982 | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
| NUC40 | IGHG_MHC_Zoonotic_Immunity | Rattus norvegicus MX | NM_001271059.1 | 3,247 | 47.46% | f84f6f0e2ccee241 | Modulates non-cytopathic persistent orthohantavirus and Borrelia spirochete carriage without immunopathological cytokine storm in Peromyscus and Sigmodon |
Supplemental Table S4. Complete 108-Isolate Single-Species North American Rodent PopSet Roster Across PopSets 1–3 (3 × N = 36 Conspecific Isolates: Peromyscus maniculatus, Sigmodon hispidus & Urocitellus parryii)
| PopSet Cohort | Isolate ID | Species / Subspecies | NCBI Accession | Genomic Marker | Length (bp) | GC % | SHA-256 Prefix |
|---|---|---|---|---|---|---|---|
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_01 | Peromyscus maniculatus | XM_006972412.4 | mtDNA CYTB (1,140 bp) | 1,160 | 55.09% | bf25d1ff2b3450f2 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_02 | Peromyscus maniculatus | PP746695.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.55% | c40137a3310ae4dc |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_03 | Peromyscus maniculatus | PP746694.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | 857a8bb7853635f4 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_04 | Peromyscus maniculatus | PP746693.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.99% | 9b8cc0c5594cdc7f |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_05 | Peromyscus maniculatus | PP746692.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.81% | 0f425e3ad23ed1d2 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_06 | Peromyscus maniculatus | PP746691.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.81% | 0f425e3ad23ed1d2 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_07 | Peromyscus maniculatus | PP746690.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.90% | 05c516f898ec5774 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_08 | Peromyscus maniculatus | PP746689.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.90% | 05c516f898ec5774 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_09 | Peromyscus maniculatus | PP746688.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.90% | 05c516f898ec5774 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_10 | Peromyscus maniculatus | PP746687.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.90% | 05c516f898ec5774 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_11 | Peromyscus maniculatus | PP746686.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.90% | 05c516f898ec5774 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_12 | Peromyscus maniculatus | PP746685.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.96% | d57754d16facde10 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_13 | Peromyscus maniculatus | PP746684.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | ab45206eafd36ff0 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_14 | Peromyscus maniculatus | PP746683.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | ab45206eafd36ff0 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_15 | Peromyscus maniculatus | PP746682.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | ab45206eafd36ff0 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_16 | Peromyscus maniculatus | PP746681.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | ab45206eafd36ff0 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_17 | Peromyscus maniculatus | PP746680.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | 816d248b62b2224b |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_18 | Peromyscus maniculatus | PP746679.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | 816d248b62b2224b |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_19 | Peromyscus maniculatus | PP746678.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | 816d248b62b2224b |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_20 | Peromyscus maniculatus | PP746677.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.34% | 0f5545b938403ee6 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_21 | Peromyscus maniculatus | PP746676.1 | mtDNA CYTB (1,140 bp) | 1,144 | 38.57% | bad4b2dd75d45fdd |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_22 | Peromyscus maniculatus | PP746675.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | 7ddeb218368b8a20 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_23 | Peromyscus maniculatus | PP746674.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.30% | cf171cc900d87965 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_24 | Peromyscus maniculatus | PP746673.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.34% | 6598afe63398aa08 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_25 | Peromyscus maniculatus | PP746672.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | 1e7f4dcafbe3745e |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_26 | Peromyscus maniculatus | PP746671.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | 23aee89bb0cc0c8d |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_27 | Peromyscus maniculatus | PP746670.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.16% | e33649576ba0f2e6 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_28 | Peromyscus maniculatus | PP746669.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | b811bf8dd83326b0 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_29 | Peromyscus maniculatus | PP746668.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.16% | 9b7b17e6d6089456 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_30 | Peromyscus maniculatus | PP746667.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | 58fe725c17d8b113 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_31 | Peromyscus maniculatus | PP746666.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.25% | 3537d07ac2347ea2 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_32 | Peromyscus maniculatus | PP746665.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | 7b7b9261d24a3656 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_33 | Peromyscus maniculatus | PP746664.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | 7b7b9261d24a3656 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_34 | Peromyscus maniculatus | PP746663.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | 7b7b9261d24a3656 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_35 | Peromyscus maniculatus | PP746662.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | 7b7b9261d24a3656 |
| PopSet 1: Peromyscus maniculatus (Sin Nombre Hantavirus & Lyme Reservoir) | P1_36 | Peromyscus maniculatus | PP746661.1 | mtDNA CYTB (1,140 bp) | 1,144 | 39.07% | 7b7b9261d24a3656 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_01 | Sigmodon hispidus | PV948094.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_02 | Sigmodon hispidus | PV948093.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_03 | Sigmodon hispidus | PV948092.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.48% | ec218fd400b70649 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_04 | Sigmodon hispidus | PV948091.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.48% | ec218fd400b70649 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_05 | Sigmodon hispidus | PV948090.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_06 | Sigmodon hispidus | PV948089.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_07 | Sigmodon hispidus | PV948088.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_08 | Sigmodon hispidus | PV948087.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_09 | Sigmodon hispidus | PV948086.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_10 | Sigmodon hispidus | PV948085.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_11 | Sigmodon hispidus | PV948084.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_12 | Sigmodon hispidus | PV948083.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.66% | 4a54f2c0853d7201 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_13 | Sigmodon hispidus | PV948082.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.74% | 2e94749d00dc0c0f |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_14 | Sigmodon hispidus | PV948081.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.74% | 2e94749d00dc0c0f |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_15 | Sigmodon hispidus | PV948080.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.74% | 2e94749d00dc0c0f |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_16 | Sigmodon hispidus | PV948079.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.74% | 2e94749d00dc0c0f |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_17 | Sigmodon hispidus | PV948078.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.74% | 2e94749d00dc0c0f |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_18 | Sigmodon hispidus | PV948077.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.74% | 2e94749d00dc0c0f |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_19 | Sigmodon hispidus | PV948076.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_20 | Sigmodon hispidus | PV948075.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.57% | 22a0f8794c5084a5 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_21 | Sigmodon hispidus | PV948074.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.66% | 75d5497d14478e78 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_22 | Sigmodon hispidus | PV948073.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.39% | d7417f5640d93c0a |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_23 | Sigmodon hispidus | PV948072.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.48% | ed6b584accfd1660 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_24 | Sigmodon hispidus | PV948071.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.31% | e7e6b343c91cd07b |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_25 | Sigmodon hispidus | PV948070.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.31% | e7e6b343c91cd07b |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_26 | Sigmodon hispidus | PV948069.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.31% | e7e6b343c91cd07b |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_27 | Sigmodon hispidus | PV948068.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.31% | e7e6b343c91cd07b |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_28 | Sigmodon hispidus | PV948067.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.39% | 0aea9c5498252d90 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_29 | Sigmodon hispidus | PV948066.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.39% | 0aea9c5498252d90 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_30 | Sigmodon hispidus | PV948065.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.39% | 0aea9c5498252d90 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_31 | Sigmodon hispidus | PV948064.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.39% | 0aea9c5498252d90 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_32 | Sigmodon hispidus | PV948063.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.39% | 0aea9c5498252d90 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_33 | Sigmodon hispidus | KX866981.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.66% | 73d512ae06a44b3b |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_34 | Sigmodon hispidus | KX866980.1 | mtDNA CYTB (1,140 bp) | 1,126 | 43.87% | 96c8d0df0a25ba2f |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_35 | Sigmodon hispidus | EU073178.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.48% | c110109ba9d5efe1 |
| PopSet 2: Sigmodon hispidus (Grassland Hantavirus & Arenavirus Reservoir) | P2_36 | Sigmodon hispidus | EU073177.1 | mtDNA CYTB (1,140 bp) | 1,143 | 43.48% | 87532e8790516937 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_01 | Urocitellus parryii | KX278586.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.12% | c9aa82f65d74e10d |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_02 | Urocitellus parryii | KX278581.1 | mtDNA CYTB (1,140 bp) | 1,140 | 38.60% | 81d1795c1a27fef5 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_03 | Urocitellus parryii | KX278580.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | f39f834e73b443c6 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_04 | Urocitellus parryii | KX278575.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | 78912e313ff903d5 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_05 | Urocitellus parryii | KX278570.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.04% | 15950e631e101244 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_06 | Urocitellus parryii | KX278544.1 | mtDNA CYTB (1,140 bp) | 1,140 | 38.95% | b523863893ad4635 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_07 | Urocitellus parryii | KX278543.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.12% | c9aa82f65d74e10d |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_08 | Urocitellus parryii | KX278531.1 | mtDNA CYTB (1,140 bp) | 1,140 | 38.77% | d5aefffb7acaf82f |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_09 | Urocitellus parryii | KX646825.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.04% | 15950e631e101244 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_10 | Urocitellus parryii | KX646824.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.04% | ce963c8b2641e997 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_11 | Urocitellus parryii | KX646823.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | d0ff2126d38508ea |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_12 | Urocitellus parryii | KX646822.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | 52dd1b3f62bc3d1e |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_13 | Urocitellus parryii | KX646821.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.56% | 79267c5d82c4a0c3 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_14 | Urocitellus parryii | KX646820.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.39% | fee8597ad7e22f1e |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_15 | Urocitellus parryii | KX646819.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.39% | 0691817ab7e0dbd9 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_16 | Urocitellus parryii | KX646818.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.21% | 1988deca116851e2 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_17 | Urocitellus parryii | KX646817.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.12% | 2112259831e731f0 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_18 | Urocitellus parryii | KX646816.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.21% | 1fcc5d86e1312043 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_19 | Urocitellus parryii | KX646815.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | 78912e313ff903d5 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_20 | Urocitellus parryii | KX646814.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.39% | 7089acb0aa81a6e1 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_21 | Urocitellus parryii | KX646813.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | 78912e313ff903d5 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_22 | Urocitellus parryii | KX646812.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.21% | 1988deca116851e2 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_23 | Urocitellus parryii | KX646811.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.39% | ead070bdce608e55 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_24 | Urocitellus parryii | KX646810.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | c965f31f3569a975 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_25 | Urocitellus parryii | KX646809.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | f39f834e73b443c6 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_26 | Urocitellus parryii | KX646808.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | f39f834e73b443c6 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_27 | Urocitellus parryii | KX646807.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | f39f834e73b443c6 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_28 | Urocitellus parryii | KX646806.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | f39f834e73b443c6 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_29 | Urocitellus parryii | KX646805.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.56% | b8827fbb8ef9309c |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_30 | Urocitellus parryii | KX646804.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.65% | 2a77fbe41d497d96 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_31 | Urocitellus parryii | KX646803.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.12% | 0d7fb42213116091 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_32 | Urocitellus parryii | KX646802.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.21% | f4b525df7771a3c1 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_33 | Urocitellus parryii | KX646801.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.30% | bbc65b499c987edb |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_34 | Urocitellus parryii | KX646800.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.21% | 2071ef65281b7ec5 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_35 | Urocitellus parryii | KX646799.1 | mtDNA CYTB (1,140 bp) | 1,140 | 38.86% | d1caa8415cd074f7 |
| PopSet 3: Urocitellus parryii (Beringian & Boreal Ground Squirrel Cohort) | P3_36 | Urocitellus parryii | JF314506.1 | mtDNA CYTB (1,140 bp) | 1,140 | 39.21% | b97bf15a71e7d5d2 |