Taxa where post‐glacial or late‐glacial inter‐oceanic relationships were inferred (or suspected), and divergence estimates
Species | Post‐ or late‐glacial invasion | Contact region | net p‐dist. (%) | n Pac / n Atl | τ | τ / L (%) | References |
Bivalves | |||||||
Hiatella L a | NP → NWA d | NWA | 1.10 | 59/26 | Laakkonen, Strelkov, and Väinölä (2015) | ||
Hiatella L a | NP → NWA | NWA f | 0.02 | 59/48 | 0.65 | 0.10 | Laakkonen, Strelkov, and Väinölä (2015) |
Macoma balthica | NP → NEA g | NEA | 0.09 | 26/26 | 0.55 | 0.09 | Nikula, Strelkov, and Väinölä (2007) |
Macoma calcarea a | NEP/A/NWA/NEA b | 0.30 | 20/85 | 0.24 | 0.04 | This study, Layton et al. 2013 | |
Mytilus trossulus | NP → NWA/NEA g | NWA/NEA | 0.08 | 194/68 | 0.53 | 0.10 | Marko et al. 2010, this study |
Gastropods | |||||||
Acanthodoris pilosa | NA → NEP | NEP | 0.11 | 2/15 | BOLD | ||
Dendronotus venustus/frondosus | NEA → NEP | NEP | 0.51 | 2/10 | Dewaard 2017, Korshunova et al. 2019, Pola & Gosliner 2010, | ||
Ekimova et al. 2016 | |||||||
Limacina helicina | f | 0.28 | 209/138 | Abyzova et al. 2018, Chichvarkhin 2016, Shimizu et al. 2017, Hunt et al. 2010, Layton, Martel & Hebert 2014, Jennings et al. 2010 | |||
Velutina velutina | ? | 0.47 | 2/8 | BOLD | |||
Crustaceans | |||||||
Balanus crenatus | NP → NWA d/NEA d | NWA/NEA | 0.22 | 9/24 | 1.58 | 0.08 | This study |
Balanus crenatus | (NP → NWA/NEA) h | (NWA/NEA) | 0.00 | 4/57 | This study | ||
Centropages abdominalis | NA → NEP | 0.34 | 6/19 | Young 2016, BOLD | |||
Pandalus borealis | NP → ARC ← NA | ARC f | 0.70 | 5/20 | This study, BOLD, Radulovici et al 2009 | ||
Gammarus setosus a | NWP/NA | NWP | This study, BOLD, Radulovici et al 2009 | ||||
Pleopsis polyphaemoides | (NA → NEP)h | (NEP) | 0.27 | 2/20 | Durbin et al. (2008) | ||
Podon leukcartii | (NA → NEP)h | (NEP) | 0.04 | 6/12 | Durbin et al. (2008) | ||
Echinoderms | |||||||
Echinarachnius parma | NP → NWA d | 0.30 | 63/53 | 0.53 | 0.08 | This study | |
Henricia cf. oculata | NEP → NWA | 0.34 | 3/4 | Corstorphine (2010) | |||
Henricia sp. AAB9183 | NEP → NWA | NWA | 0.49 | 2/13 | Layton, Corstorphine & Hebert 2016 | ||
Henricia sp. EAC06 | NEP/NWA | Corstorphine (2010) | |||||
Strongylocentrotus droebachiensis | NP → NWA d | NWA f | 0.41 | 33/115 | 1.28 | 0.31 | Palumbi & Kessing 1991, Addison and Hart (2005), this study |
Strongylocentrotus pallidus | NP/NWA/NEA | Balakirev et al 2008, Corstophine 2010, Hardy et al. 2011 | |||||
Polychaetes | |||||||
Glycera capitata | Ber/NWA/NEA | Carr et al. (2011), Hardy et al. 2011 | |||||
Harmothoe imbricata group | NEP/ARC/NWA | NEP/ARC/NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Harmothoe rarispina CMC03 | NWA → NEP | NEP | 0.11 | 8/17 | Carr et al. (2011), BOLD | ||
Nereis pelagica CMC03 | NWA → Ber | 1/26 | Hardy et al. 2010, Carr et al. (2011), BOLD | ||||
Nereis pelagica CMC03a | Ber/NWA | NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Phyllodoce sp. CMC01a | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe baltica A | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe minuta A | Ber/ARC‐NWA | 0.55 | 4/29 | Carr et al. (2011) | |||
NEP/NEA | NEA | This study | |||||
Fishes | |||||||
Anisarchus medius a | NP → ARC ← NWA (?) | ARC | Mecklenburg et al. (2011) | ||||
Aspidophoroides monopterygius | NP c → NWA | NWA | Mecklenburg et al. (2011) | ||||
Clupea pallasii | NWP → NEA g | NEA | 0.06 | 111/242 | 2.32 | 0.21 | Laakkonen et al. (2013) |
Eumesogrammus praecisus a | NP c → ARC ← NWA | ARC f | Mecklenburg et al. (2011) | ||||
Gadus chalcogrammus (G. finnmarchicus) | NP → NEA | NEA | Ursvik et al. (2007),Gorbachev et al. 2014 | ||||
Gadus macrocephalus (G. ogac) | NP → NWA | NWA | Coulson et al. (2006) | ||||
Gymnocanthus tricuspis | NA → NP | Ber | Yamazaki et al. 2013 | ||||
Leptagonus decagonus a | NWP c → ARC ← NA | ARC f | McCusker et al. 2012, BOLD | ||||
Leptoclinus maculatus a | NP → ARC ← NA | ARC f | Mecklenburg et al. (2011) | ||||
Liopsetta glacialis | NWP → NEA b | 0.16 | 7/17 | This study, Kartavtsev et al. (2014) | |||
Lumpenus fabricii | NP → NEA | NEA e | This study, Mecklenburg et al. (2011) | ||||
Mallotus villosus | NP → ARC/NWA | NWA | Dodson et al. (2007) | ||||
Myoxocephalus scorpius a | NEA/NWA → NEP | NEP | This study, Mecklenburg et al. (2011) | ||||
Osmerus dentex | NWP → ARC/NEA | NEA | 0.22 | 4/9 | Kovpak et al. 2011, Skurikhina et al. 2013 | ||
Reinhardtius hippoglossoides a | NP/NWA/NEA | 0.06 | 5/280 | Vis et al. 1997, Kartavtsev et al. (2014) | |||
Mammals | |||||||
Phoca hispida (sspp. hispida & ochotensis)a | NEA /ARC/ NWP b | This study |
Species | Post‐ or late‐glacial invasion | Contact region | net p‐dist. (%) | n Pac / n Atl | τ | τ / L (%) | References |
Bivalves | |||||||
Hiatella L a | NP → NWA d | NWA | 1.10 | 59/26 | Laakkonen, Strelkov, and Väinölä (2015) | ||
Hiatella L a | NP → NWA | NWA f | 0.02 | 59/48 | 0.65 | 0.10 | Laakkonen, Strelkov, and Väinölä (2015) |
Macoma balthica | NP → NEA g | NEA | 0.09 | 26/26 | 0.55 | 0.09 | Nikula, Strelkov, and Väinölä (2007) |
Macoma calcarea a | NEP/A/NWA/NEA b | 0.30 | 20/85 | 0.24 | 0.04 | This study, Layton et al. 2013 | |
Mytilus trossulus | NP → NWA/NEA g | NWA/NEA | 0.08 | 194/68 | 0.53 | 0.10 | Marko et al. 2010, this study |
Gastropods | |||||||
Acanthodoris pilosa | NA → NEP | NEP | 0.11 | 2/15 | BOLD | ||
Dendronotus venustus/frondosus | NEA → NEP | NEP | 0.51 | 2/10 | Dewaard 2017, Korshunova et al. 2019, Pola & Gosliner 2010, | ||
Ekimova et al. 2016 | |||||||
Limacina helicina | f | 0.28 | 209/138 | Abyzova et al. 2018, Chichvarkhin 2016, Shimizu et al. 2017, Hunt et al. 2010, Layton, Martel & Hebert 2014, Jennings et al. 2010 | |||
Velutina velutina | ? | 0.47 | 2/8 | BOLD | |||
Crustaceans | |||||||
Balanus crenatus | NP → NWA d/NEA d | NWA/NEA | 0.22 | 9/24 | 1.58 | 0.08 | This study |
Balanus crenatus | (NP → NWA/NEA) h | (NWA/NEA) | 0.00 | 4/57 | This study | ||
Centropages abdominalis | NA → NEP | 0.34 | 6/19 | Young 2016, BOLD | |||
Pandalus borealis | NP → ARC ← NA | ARC f | 0.70 | 5/20 | This study, BOLD, Radulovici et al 2009 | ||
Gammarus setosus a | NWP/NA | NWP | This study, BOLD, Radulovici et al 2009 | ||||
Pleopsis polyphaemoides | (NA → NEP)h | (NEP) | 0.27 | 2/20 | Durbin et al. (2008) | ||
Podon leukcartii | (NA → NEP)h | (NEP) | 0.04 | 6/12 | Durbin et al. (2008) | ||
Echinoderms | |||||||
Echinarachnius parma | NP → NWA d | 0.30 | 63/53 | 0.53 | 0.08 | This study | |
Henricia cf. oculata | NEP → NWA | 0.34 | 3/4 | Corstorphine (2010) | |||
Henricia sp. AAB9183 | NEP → NWA | NWA | 0.49 | 2/13 | Layton, Corstorphine & Hebert 2016 | ||
Henricia sp. EAC06 | NEP/NWA | Corstorphine (2010) | |||||
Strongylocentrotus droebachiensis | NP → NWA d | NWA f | 0.41 | 33/115 | 1.28 | 0.31 | Palumbi & Kessing 1991, Addison and Hart (2005), this study |
Strongylocentrotus pallidus | NP/NWA/NEA | Balakirev et al 2008, Corstophine 2010, Hardy et al. 2011 | |||||
Polychaetes | |||||||
Glycera capitata | Ber/NWA/NEA | Carr et al. (2011), Hardy et al. 2011 | |||||
Harmothoe imbricata group | NEP/ARC/NWA | NEP/ARC/NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Harmothoe rarispina CMC03 | NWA → NEP | NEP | 0.11 | 8/17 | Carr et al. (2011), BOLD | ||
Nereis pelagica CMC03 | NWA → Ber | 1/26 | Hardy et al. 2010, Carr et al. (2011), BOLD | ||||
Nereis pelagica CMC03a | Ber/NWA | NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Phyllodoce sp. CMC01a | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe baltica A | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe minuta A | Ber/ARC‐NWA | 0.55 | 4/29 | Carr et al. (2011) | |||
NEP/NEA | NEA | This study | |||||
Fishes | |||||||
Anisarchus medius a | NP → ARC ← NWA (?) | ARC | Mecklenburg et al. (2011) | ||||
Aspidophoroides monopterygius | NP c → NWA | NWA | Mecklenburg et al. (2011) | ||||
Clupea pallasii | NWP → NEA g | NEA | 0.06 | 111/242 | 2.32 | 0.21 | Laakkonen et al. (2013) |
Eumesogrammus praecisus a | NP c → ARC ← NWA | ARC f | Mecklenburg et al. (2011) | ||||
Gadus chalcogrammus (G. finnmarchicus) | NP → NEA | NEA | Ursvik et al. (2007),Gorbachev et al. 2014 | ||||
Gadus macrocephalus (G. ogac) | NP → NWA | NWA | Coulson et al. (2006) | ||||
Gymnocanthus tricuspis | NA → NP | Ber | Yamazaki et al. 2013 | ||||
Leptagonus decagonus a | NWP c → ARC ← NA | ARC f | McCusker et al. 2012, BOLD | ||||
Leptoclinus maculatus a | NP → ARC ← NA | ARC f | Mecklenburg et al. (2011) | ||||
Liopsetta glacialis | NWP → NEA b | 0.16 | 7/17 | This study, Kartavtsev et al. (2014) | |||
Lumpenus fabricii | NP → NEA | NEA e | This study, Mecklenburg et al. (2011) | ||||
Mallotus villosus | NP → ARC/NWA | NWA | Dodson et al. (2007) | ||||
Myoxocephalus scorpius a | NEA/NWA → NEP | NEP | This study, Mecklenburg et al. (2011) | ||||
Osmerus dentex | NWP → ARC/NEA | NEA | 0.22 | 4/9 | Kovpak et al. 2011, Skurikhina et al. 2013 | ||
Reinhardtius hippoglossoides a | NP/NWA/NEA | 0.06 | 5/280 | Vis et al. 1997, Kartavtsev et al. (2014) | |||
Mammals | |||||||
Phoca hispida (sspp. hispida & ochotensis)a | NEA /ARC/ NWP b | This study |
IMa analysis was performed only for taxa with sample sizes n > 10 in both basins: τ is an estimate of distance in terms of the number of observed inter‐oceanic nucleotide differences, and τ / L is the relative distance (per site), from the IMa analysis. The genetically documented distribution of the invading lineage and the inferred direction of post‐glacial spread and possible intra‐generic contact regions are indicated. References for previously published sequence data are listed in Table S2.
Net distance estimates between relevant clades are indicated, if sequence data were available (n > 2 for each population). Estimates were calculated with MEGA (Tamura et al. 2013). For a subset of comparisons, the population split time estimate from the IM analysis, translated to per‐site distance units, is also given.
Boreal–arctic species with possibly continuous range through the Arctic.
Post‐glacial spread without refugial disjunction.
No sequence data (from the actual basin).
Inferred spread in the last interglacial (ca 110–130 kya).
Other intra‐species contacts (not related to trans‐Arctic dispersal).
Contacts of late‐glacial lineages.
Instances where hybridization has been documented.
Suspected anthropogenic invasion.
Taxa where post‐glacial or late‐glacial inter‐oceanic relationships were inferred (or suspected), and divergence estimates
Species | Post‐ or late‐glacial invasion | Contact region | net p‐dist. (%) | n Pac / n Atl | τ | τ / L (%) | References |
Bivalves | |||||||
Hiatella L a | NP → NWA d | NWA | 1.10 | 59/26 | Laakkonen, Strelkov, and Väinölä (2015) | ||
Hiatella L a | NP → NWA | NWA f | 0.02 | 59/48 | 0.65 | 0.10 | Laakkonen, Strelkov, and Väinölä (2015) |
Macoma balthica | NP → NEA g | NEA | 0.09 | 26/26 | 0.55 | 0.09 | Nikula, Strelkov, and Väinölä (2007) |
Macoma calcarea a | NEP/A/NWA/NEA b | 0.30 | 20/85 | 0.24 | 0.04 | This study, Layton et al. 2013 | |
Mytilus trossulus | NP → NWA/NEA g | NWA/NEA | 0.08 | 194/68 | 0.53 | 0.10 | Marko et al. 2010, this study |
Gastropods | |||||||
Acanthodoris pilosa | NA → NEP | NEP | 0.11 | 2/15 | BOLD | ||
Dendronotus venustus/frondosus | NEA → NEP | NEP | 0.51 | 2/10 | Dewaard 2017, Korshunova et al. 2019, Pola & Gosliner 2010, | ||
Ekimova et al. 2016 | |||||||
Limacina helicina | f | 0.28 | 209/138 | Abyzova et al. 2018, Chichvarkhin 2016, Shimizu et al. 2017, Hunt et al. 2010, Layton, Martel & Hebert 2014, Jennings et al. 2010 | |||
Velutina velutina | ? | 0.47 | 2/8 | BOLD | |||
Crustaceans | |||||||
Balanus crenatus | NP → NWA d/NEA d | NWA/NEA | 0.22 | 9/24 | 1.58 | 0.08 | This study |
Balanus crenatus | (NP → NWA/NEA) h | (NWA/NEA) | 0.00 | 4/57 | This study | ||
Centropages abdominalis | NA → NEP | 0.34 | 6/19 | Young 2016, BOLD | |||
Pandalus borealis | NP → ARC ← NA | ARC f | 0.70 | 5/20 | This study, BOLD, Radulovici et al 2009 | ||
Gammarus setosus a | NWP/NA | NWP | This study, BOLD, Radulovici et al 2009 | ||||
Pleopsis polyphaemoides | (NA → NEP)h | (NEP) | 0.27 | 2/20 | Durbin et al. (2008) | ||
Podon leukcartii | (NA → NEP)h | (NEP) | 0.04 | 6/12 | Durbin et al. (2008) | ||
Echinoderms | |||||||
Echinarachnius parma | NP → NWA d | 0.30 | 63/53 | 0.53 | 0.08 | This study | |
Henricia cf. oculata | NEP → NWA | 0.34 | 3/4 | Corstorphine (2010) | |||
Henricia sp. AAB9183 | NEP → NWA | NWA | 0.49 | 2/13 | Layton, Corstorphine & Hebert 2016 | ||
Henricia sp. EAC06 | NEP/NWA | Corstorphine (2010) | |||||
Strongylocentrotus droebachiensis | NP → NWA d | NWA f | 0.41 | 33/115 | 1.28 | 0.31 | Palumbi & Kessing 1991, Addison and Hart (2005), this study |
Strongylocentrotus pallidus | NP/NWA/NEA | Balakirev et al 2008, Corstophine 2010, Hardy et al. 2011 | |||||
Polychaetes | |||||||
Glycera capitata | Ber/NWA/NEA | Carr et al. (2011), Hardy et al. 2011 | |||||
Harmothoe imbricata group | NEP/ARC/NWA | NEP/ARC/NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Harmothoe rarispina CMC03 | NWA → NEP | NEP | 0.11 | 8/17 | Carr et al. (2011), BOLD | ||
Nereis pelagica CMC03 | NWA → Ber | 1/26 | Hardy et al. 2010, Carr et al. (2011), BOLD | ||||
Nereis pelagica CMC03a | Ber/NWA | NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Phyllodoce sp. CMC01a | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe baltica A | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe minuta A | Ber/ARC‐NWA | 0.55 | 4/29 | Carr et al. (2011) | |||
NEP/NEA | NEA | This study | |||||
Fishes | |||||||
Anisarchus medius a | NP → ARC ← NWA (?) | ARC | Mecklenburg et al. (2011) | ||||
Aspidophoroides monopterygius | NP c → NWA | NWA | Mecklenburg et al. (2011) | ||||
Clupea pallasii | NWP → NEA g | NEA | 0.06 | 111/242 | 2.32 | 0.21 | Laakkonen et al. (2013) |
Eumesogrammus praecisus a | NP c → ARC ← NWA | ARC f | Mecklenburg et al. (2011) | ||||
Gadus chalcogrammus (G. finnmarchicus) | NP → NEA | NEA | Ursvik et al. (2007),Gorbachev et al. 2014 | ||||
Gadus macrocephalus (G. ogac) | NP → NWA | NWA | Coulson et al. (2006) | ||||
Gymnocanthus tricuspis | NA → NP | Ber | Yamazaki et al. 2013 | ||||
Leptagonus decagonus a | NWP c → ARC ← NA | ARC f | McCusker et al. 2012, BOLD | ||||
Leptoclinus maculatus a | NP → ARC ← NA | ARC f | Mecklenburg et al. (2011) | ||||
Liopsetta glacialis | NWP → NEA b | 0.16 | 7/17 | This study, Kartavtsev et al. (2014) | |||
Lumpenus fabricii | NP → NEA | NEA e | This study, Mecklenburg et al. (2011) | ||||
Mallotus villosus | NP → ARC/NWA | NWA | Dodson et al. (2007) | ||||
Myoxocephalus scorpius a | NEA/NWA → NEP | NEP | This study, Mecklenburg et al. (2011) | ||||
Osmerus dentex | NWP → ARC/NEA | NEA | 0.22 | 4/9 | Kovpak et al. 2011, Skurikhina et al. 2013 | ||
Reinhardtius hippoglossoides a | NP/NWA/NEA | 0.06 | 5/280 | Vis et al. 1997, Kartavtsev et al. (2014) | |||
Mammals | |||||||
Phoca hispida (sspp. hispida & ochotensis)a | NEA /ARC/ NWP b | This study |
Species | Post‐ or late‐glacial invasion | Contact region | net p‐dist. (%) | n Pac / n Atl | τ | τ / L (%) | References |
Bivalves | |||||||
Hiatella L a | NP → NWA d | NWA | 1.10 | 59/26 | Laakkonen, Strelkov, and Väinölä (2015) | ||
Hiatella L a | NP → NWA | NWA f | 0.02 | 59/48 | 0.65 | 0.10 | Laakkonen, Strelkov, and Väinölä (2015) |
Macoma balthica | NP → NEA g | NEA | 0.09 | 26/26 | 0.55 | 0.09 | Nikula, Strelkov, and Väinölä (2007) |
Macoma calcarea a | NEP/A/NWA/NEA b | 0.30 | 20/85 | 0.24 | 0.04 | This study, Layton et al. 2013 | |
Mytilus trossulus | NP → NWA/NEA g | NWA/NEA | 0.08 | 194/68 | 0.53 | 0.10 | Marko et al. 2010, this study |
Gastropods | |||||||
Acanthodoris pilosa | NA → NEP | NEP | 0.11 | 2/15 | BOLD | ||
Dendronotus venustus/frondosus | NEA → NEP | NEP | 0.51 | 2/10 | Dewaard 2017, Korshunova et al. 2019, Pola & Gosliner 2010, | ||
Ekimova et al. 2016 | |||||||
Limacina helicina | f | 0.28 | 209/138 | Abyzova et al. 2018, Chichvarkhin 2016, Shimizu et al. 2017, Hunt et al. 2010, Layton, Martel & Hebert 2014, Jennings et al. 2010 | |||
Velutina velutina | ? | 0.47 | 2/8 | BOLD | |||
Crustaceans | |||||||
Balanus crenatus | NP → NWA d/NEA d | NWA/NEA | 0.22 | 9/24 | 1.58 | 0.08 | This study |
Balanus crenatus | (NP → NWA/NEA) h | (NWA/NEA) | 0.00 | 4/57 | This study | ||
Centropages abdominalis | NA → NEP | 0.34 | 6/19 | Young 2016, BOLD | |||
Pandalus borealis | NP → ARC ← NA | ARC f | 0.70 | 5/20 | This study, BOLD, Radulovici et al 2009 | ||
Gammarus setosus a | NWP/NA | NWP | This study, BOLD, Radulovici et al 2009 | ||||
Pleopsis polyphaemoides | (NA → NEP)h | (NEP) | 0.27 | 2/20 | Durbin et al. (2008) | ||
Podon leukcartii | (NA → NEP)h | (NEP) | 0.04 | 6/12 | Durbin et al. (2008) | ||
Echinoderms | |||||||
Echinarachnius parma | NP → NWA d | 0.30 | 63/53 | 0.53 | 0.08 | This study | |
Henricia cf. oculata | NEP → NWA | 0.34 | 3/4 | Corstorphine (2010) | |||
Henricia sp. AAB9183 | NEP → NWA | NWA | 0.49 | 2/13 | Layton, Corstorphine & Hebert 2016 | ||
Henricia sp. EAC06 | NEP/NWA | Corstorphine (2010) | |||||
Strongylocentrotus droebachiensis | NP → NWA d | NWA f | 0.41 | 33/115 | 1.28 | 0.31 | Palumbi & Kessing 1991, Addison and Hart (2005), this study |
Strongylocentrotus pallidus | NP/NWA/NEA | Balakirev et al 2008, Corstophine 2010, Hardy et al. 2011 | |||||
Polychaetes | |||||||
Glycera capitata | Ber/NWA/NEA | Carr et al. (2011), Hardy et al. 2011 | |||||
Harmothoe imbricata group | NEP/ARC/NWA | NEP/ARC/NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Harmothoe rarispina CMC03 | NWA → NEP | NEP | 0.11 | 8/17 | Carr et al. (2011), BOLD | ||
Nereis pelagica CMC03 | NWA → Ber | 1/26 | Hardy et al. 2010, Carr et al. (2011), BOLD | ||||
Nereis pelagica CMC03a | Ber/NWA | NWA | Carr et al. (2011), Hardy et al. 2011 | ||||
Phyllodoce sp. CMC01a | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe baltica A | Ber/ARC‐NWA | Carr et al. (2011) | |||||
Pholoe minuta A | Ber/ARC‐NWA | 0.55 | 4/29 | Carr et al. (2011) | |||
NEP/NEA | NEA | This study | |||||
Fishes | |||||||
Anisarchus medius a | NP → ARC ← NWA (?) | ARC | Mecklenburg et al. (2011) | ||||
Aspidophoroides monopterygius | NP c → NWA | NWA | Mecklenburg et al. (2011) | ||||
Clupea pallasii | NWP → NEA g | NEA | 0.06 | 111/242 | 2.32 | 0.21 | Laakkonen et al. (2013) |
Eumesogrammus praecisus a | NP c → ARC ← NWA | ARC f | Mecklenburg et al. (2011) | ||||
Gadus chalcogrammus (G. finnmarchicus) | NP → NEA | NEA | Ursvik et al. (2007),Gorbachev et al. 2014 | ||||
Gadus macrocephalus (G. ogac) | NP → NWA | NWA | Coulson et al. (2006) | ||||
Gymnocanthus tricuspis | NA → NP | Ber | Yamazaki et al. 2013 | ||||
Leptagonus decagonus a | NWP c → ARC ← NA | ARC f | McCusker et al. 2012, BOLD | ||||
Leptoclinus maculatus a | NP → ARC ← NA | ARC f | Mecklenburg et al. (2011) | ||||
Liopsetta glacialis | NWP → NEA b | 0.16 | 7/17 | This study, Kartavtsev et al. (2014) | |||
Lumpenus fabricii | NP → NEA | NEA e | This study, Mecklenburg et al. (2011) | ||||
Mallotus villosus | NP → ARC/NWA | NWA | Dodson et al. (2007) | ||||
Myoxocephalus scorpius a | NEA/NWA → NEP | NEP | This study, Mecklenburg et al. (2011) | ||||
Osmerus dentex | NWP → ARC/NEA | NEA | 0.22 | 4/9 | Kovpak et al. 2011, Skurikhina et al. 2013 | ||
Reinhardtius hippoglossoides a | NP/NWA/NEA | 0.06 | 5/280 | Vis et al. 1997, Kartavtsev et al. (2014) | |||
Mammals | |||||||
Phoca hispida (sspp. hispida & ochotensis)a | NEA /ARC/ NWP b | This study |
IMa analysis was performed only for taxa with sample sizes n > 10 in both basins: τ is an estimate of distance in terms of the number of observed inter‐oceanic nucleotide differences, and τ / L is the relative distance (per site), from the IMa analysis. The genetically documented distribution of the invading lineage and the inferred direction of post‐glacial spread and possible intra‐generic contact regions are indicated. References for previously published sequence data are listed in Table S2.
Net distance estimates between relevant clades are indicated, if sequence data were available (n > 2 for each population). Estimates were calculated with MEGA (Tamura et al. 2013). For a subset of comparisons, the population split time estimate from the IM analysis, translated to per‐site distance units, is also given.
Boreal–arctic species with possibly continuous range through the Arctic.
Post‐glacial spread without refugial disjunction.
No sequence data (from the actual basin).
Inferred spread in the last interglacial (ca 110–130 kya).
Other intra‐species contacts (not related to trans‐Arctic dispersal).
Contacts of late‐glacial lineages.
Instances where hybridization has been documented.
Suspected anthropogenic invasion.
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