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Species Distribution Modeling of Carnivorous Plants Worldwide
Forecasting how carnivorous plant species will respond to climatic change is a key issue in their conservation and management but presents a number of challenges. These challenges derive from interactions between the relatively simplistic statistical methods typically used to forecast species responses to climatic change, which to date have been limited mainly to species distribution models (“SDMs) and particular aspects of the ecology of carnivorous plants, including their rarity, habitat specialization, and limited dispersal ability. The small ranges and oftentimes low local abundance of carnivorous plants provide few occurrence records, which increase the potential for poorly or over-fitted SDMs and misspecification of relationships with their “optimal” environments. The unique habitats in which carnivorous plants often grow also are difficult to characterize using the basic temperature and precipitation data that often undergird SDMs. Rather, habitats in which carnivorous plants are common often are decoupled from broader climatic patterns (e.g., many retain high soil moisture even during seasonal drought) and may be associated with frequent disturbance. Last, dispersal limitation also may constrain range shifts of carnivorous plants as the climate changes. These three issues raise two related questions that are critical for understanding and forecasting the future of carnivorous plants. First, to what extent are current carnivorous plants distributions constrained by climate; and second, how readily, if at all, might carnivorous plants disperse to colonize new habitat as it becomes climatically suitable? We estimated the vulnerability of carnivorous plants to climatic change in light of challenges identified with SDMs in general and their particular application to these unique species. We combined two approaches: “ensembles of small models”, which attempt to deal with the challenges of fitting SDMs for data-limited species; and “bioclimatic velocity”, which is
Projected distribution of invasive plant species in the tropical Andes under climate change
<p>Distribution maps of 11 invasive species now and in the future (2040-70). The projections were the result of the assembly of three algorithms: Adaptive Boosting (AdaBoost), Boosted Regression Trees (BRT), and Extreme Gradient Boosting (XGBoost). Future projections were made for three global circulation models and three climate change scenarios, each with low (SSP126), medium (SSP370), and high (SSP585) levels of carbon emission.</p> <p>Habitat suitability and presence/absence maps are also included. The threshold for establishing a species as present was determined to be the value that maximized the TSS. </p> <p>For more information, see the article accompanying the dataset by González-Trujillo et al. Mapping the threat: Projecting invasive plant distribution in the tropical Andes under climate change</p> <p>List of modeled invasive plant species and their known impacts in the tropics.</p> <table> <tbody> <tr> <td> <p><strong>Species </strong></p> </td> <td> <p><strong>Biogeographic origin</strong></p> </td> <td> <p><strong>Impacts </strong></p> </td> <td> <p><strong>References</strong></p> </td> <td> <p><strong>GBIF data (DOIs)</strong></p> </td> </tr> <tr> <td> <p><em>Acacia decurrens </em></p> </td> <td> <p>Australian</p> </td> <td> <p>Create regular layers of litter on the ground, inhibit or redirect successional processes, inhibit the expression of seed banks, and limit resource supply, leading to displacement of native plants and animals and increasing the frequency of fires.</p> </td> <td> <p> (Cárdenas López et al., 2017; Le Maitre et al., 2011)</p> </td> <td> <p>https://doi.org/10.15468/dl.mjyxhw</p> </td> </tr> <tr> <td> <p><em>Acacia melanoxylon</em></p> </td> <td> <p>Australian</p> </td> <td> <p>Alter the structure and function of their ecosystems, thereby displacing their native flora. It also causes soil erosion and alters hydrological cycles, negatively affecting agriculture.</p> </td> <td> <p>(Kumschick and Jansen, 2023; Le Maitre et al., 2011)</p> <p> </p> </td> <td> <p>https://doi.org/10.15468/dl.4cugnk</p> </td> </tr> <tr> <td> <p><em>Arundo donax</em></p> <p><em> </em></p> </td> <td> <p>Holarctic</p> </td> <td> <p>Alter<em> </em>the natural vegetation structure, outcompete native plant species and diminish the diversity and abundance of animals such as arthropods and birds. It also drives out soil, fuels forest fires, displaces native species, and increases the invasion of ticks that affect livestock.</p> </td> <td> <p>(Cárdenas López et al., 2017; Girotto et al., 2021; Lambert et al., 2010)</p> </td> <td> <p>https://doi.org/10.15468/dl.bfep4t</p> </td> </tr> <tr> <td> <p><em>Genista monspessulana</em></p> </td> <td> <p>Holarctic</p> </td> <td> <p>Alter fire regime and nutrient cycling displace native species and decrease native diversity by forming dense monospecific stands. It also facilitates the establishment of other invasive species and produces seeds that are toxic to livestock and humans.</p> </td> <td> <p>(Cárdenas López et al., 2017; Herrera et al., 2016; Pauchard et al., 2008)</p> </td> <td> <p>https://doi.org/10.15468/dl.gyhnxh</p> </td> </tr> <tr> <td> <p><em>Hedychium coronarium </em></p> </td> <td> <p>Indo-Malesian</p> </td> <td> <p>Alter hydrological and nutrient cycles in soil. It forms thickets that suppress the successional and regeneration processes of native species, thus affecting the native flora and crops.</p> </td> <td> <p>(Cárdenas López et al., 2017; Costa et al., 2019)</p> </td> <td> <p>https://doi.org/10.15468/dl.6z2jgb</p> </td> </tr> <tr> <td> <p><em>Melinis minutiflora</em></p> </td> <td> <p>African</p> </td> <td> <p>Increases the occurrence of fires, displaces native species, and alters soil properties and decomposition. It also inhibits the growth of native species.</p> </td> <td> <p>(Cárdenas López et al., 2017; Nogueira et al., 2019; Sandoval et al., 2022)</p> </td> <td> <p>https://doi.org/10.15468/dl.fsqwsv</p> </td> </tr> <tr> <td> <p><em>Pteridium aquilinum</em></p> </td> <td> <p>Holarctic</p> </td> <td> <p>Alter vegetation success processes affect crops and cause livestock poisoning. It also produces acids that inhibit root growth in native and cultivated species.</p> </td> <td> <p> (Berget et al., 2015; Cárdenas López et al., 2017; Valdez-Ramírez et al., 2020)</p> <p> </p> </td> <td> <p>https://doi.org/10.15468/dl.sp4uuv</p> </td> </tr> <tr> <td> <p><em>Ricinus communis</em></p> </td> <td> <p>African</p> </td> <td> <p>Alter vegetation success processes affect crops and cause livestock poisoning. It also produces acids that inhibit root growth in native and cultivated species.</p> </td> <td> <p>(Cárdenas López et al., 2017; Sandoval et al., 2022; Silva and Fabricante, 2022)</p> </td> <td> <p>https://doi.org/10.15468/dl.dhbphb</p> </td> </tr> <tr> <td> <p><em>Senecio madagascariensis</em></p> </td> <td> <p>African</p> </td> <td> <p>Alter soil nutrient cycles, damage to agricultural crops, and outcompete native species. It also contains substances that are toxic to both animals and humans. </p> </td> <td> <p>(Wijayabandara et al., 2021)</p> </td> <td> <p>https://doi.org/10.15468/dl.7e8eyx</p> </td> </tr> <tr> <td> <p><em>Thunbergia alata</em></p> </td> <td> <p>African</p> </td> <td> <p>Displace native species and reduce habitat heterogeneity, thereby affecting the structure and function of native ecosystems.</p> </td> <td> <p>(Cárdenas López et al., 2017; Quijano-Abril et al., 2021)</p> </td> <td> <p>https://doi.org/10.15468/dl.g9zybc</p> </td> </tr> <tr> <td> <p><em>Ulex europeaus</em></p> </td> <td> <p>Holarctic</p> </td> <td> <p>Dry soil and increase the occurrence of fires. Inhibits vegetative growth, including pastures in agricultural and livestock lands.</p> </td> <td> <p>(Anderson and Anderson, 2009; Cárdenas López et al., 2017)</p> </td> <td> <p>https://doi.org/10.15468/dl.6642q9</p> </td> </tr> </tbody> </table>
Fig. 30 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 30 (continued on next page). Distribution of the lutko species group fritillaries in combination with the distribution of known and suspected species of host plants from the genus Phlomoides Blume. = Melitaea lutko Evans, 1932; = M. timandra timandra Coutsis & Oorschot, 2014; = M. timandra binaludica subsp. nov.; = M. shahvarica sp. nov.; = M. mimetica mimetica Higgins, 1940; = M. mimetica delerei Heidemann, 1954;? = unconfirmed findings of M. timandra; = M. timandra with an unclear subspecies status; = Phlomoides regeliana (Aitch. & Hemsl.) Adylov, Kamelin & Makhm.; = Phlomoides boissieriana (Regel) Adylov, Kamelin & Makhm.; = Phlomoides laciniata (L.) Kamelin & Makhm.; = Phlomoides labiosiformis (Popov) Adylov, Kamelin & Makhm.; = Phlomoides loasifolia (Benth.) Kamelin & Makhm.; = Phlomoides molucelloides (Bunge) Salmaki; = Phlomoides acaulis (Beck ex Rech.f.) Salmaki; = Phlomoides labiosa (Bunge) Adylov, Kamelin & Makhm. A. Pakistan, Chitral, Chaghbini CGNP, alt. 2700–3000 m. B. Pakistan, Khyber Pakhtunkhwa, Drosh. C. Pakistan, Khyber Pakhtunkhwa, Keon Nullah. D. Pakistan, Khyber Pakhtunkhwa, Malakand. E. Pakistan, Khyber Pakhtunkhwa, Birmoglasht. F. Turkmenistan, Badkhyz, Kepeli, alt. 700 m. G. Turkmenistan, Badkhyz, Kyzyl-Jar, alt. 700 m. H. Turkmenistan, Kushka, alt. 700 m. I. Turkmenistan, Murgab river, Sary-Yazy, alt. 300 m. J. Turkmenistan, 30 km E of BairamAli, Zahmet, alt. 240 m. K. Turkmenistan, Bairam-Ali, alt. 230 m. L. Turkmenistan, Kara-Kum desert, 30 km W of Mary, alt. 200 m.M. Turkmenistan, Dushak, alt. 250 m.N. Turkmenistan, Chaacha, alt. 400 m. O. Turkmenistan, Bakharden, alt. 200 m. P. Iran, Khorossan Razavi, Kuh-e-Binalud Mts, Qadamgah area, Gerina, alt. 2000 m. Q. Iran, Khorasan Razavi, Kuh-e-Binalud Mts, 15 km SW of Zoshk, alt. 2300– 2500 m. R. Iran, S Khorosan, 75 km N of Birjant, Sedeh, alt. 1500 m. S. Iran, S Khorosan, 35 km N of Birjant, alt. 1500 m. T. Afghanistan, Bamian, Band-e-Amir, Dzhudoi-Kvak Gorge, alt. 3200 m. U. Afghanistan, Bamian, Band-e-Amir, Hazarajat, alt. 3000–3200 m. V. Afghanistan, Bamian, Koh-iBaba Mts, Joshanak, alt. 2800 m. W. Afghanistan, Heart, Qala-i-Naw, Kashka pass. X. Iran, Semnan, Shahvar Mt., alt. 2200–2500 m. Y. Turkmenistan, Kara-Kala, Monjukly Ridge, 300–700 m. Z. Iran, Golestan, E Maraveh Tappeh, N Ghazan Ghayeh, Palizan Mts. A". Pakistan, Balochistan, Quetta, Urak, alt. 2500 m. B". Pakistan, Balochistan, Ziarat, alt. 2500 m. C". Pakistan, Balochistan, Khojak, alt. 1700 m. D". Pakistan, Balochistan, Zaghum, alt. 1600 m; E". Pakistan, Punjab, Gawar, alt. 500 m. F". Pakistan, Balochistan, Sheik Wazil, alt. 1600 m. G". Afghanistan, Bamian, Hushkak, alt. 2700–2800 m. H". Afghanistan, Bamian, Punjub Distr., 10 km NE of Varas, alt. 2400 m. I". Afghanistan, Ghor, 17 km E of Changcharan, 15 km S of Bandi-Ali, Gazak Mts, alt. 2400 m. J". Afghanistan, Ghor, Bayan Range, 15 km S of Changcharan, Kindival valley, alt. 2700 m. K". Afghanistan, Bamiyan, Kohi-Baba Mts, Panjao, alt. 3000 m. Afghanistan, Bamiyan, Koh-i-Baba Mts, Shah-tu-Kotal, alt. 4000 m. L". Afghanistan, Kapisa, Pandshir valley, alt. 2200–2800 m. M". Afghanistan, Kabul. N". Iran, Tehran, Elburz Ridge, Demavend Mt., Ask, alt. 1800 m. O". Iran, Semnan, Foulad Mohaleh, alt. 2200 m. P". Pakistan, Punjab, Murree.
Fig. 29 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 29.Differences in the structure of valva and aedeagus of the lutko species group.A. Melitaea shahvarica sp. nov. B, D, H. M. timandra binaludica subsp. nov. C–E. M. mimetica Higgins, 1940. F. M. lutko Evans, 1932. G. M. timandra timandra Coutsis &van Oorschot, 2014. A. Iran, Semnan Prov., Shahrud area, S macroslope of Shahvar Mts, alt. 2200–2400 m. B. Iran, Rezavi Khorassan Prov., Kuh-e-Binalud Mts, Dorrud v. vicinity, alt. 2430 m. C. Afghanistan, Bamian Prov., Punjub Distr., 10 km NE of Varas v., alt. 2400 m. D. Afghanistan, Band-i-Amir, Hazarajat. E. Pakistan, Balochistan, Quetta, Urak, alt. 2400– 2700 m. F. Pakistan, Chitral, Gol National Park, alt. 2700 m. G. Turkmenistan, Sary-Yazy, alt. 700 m. H. Iran, Rezavi Khorassan Prov., Kuh-e-Binalud Mts, Dorrud v. vicinity, alt. 2430 m.
Fig. 28 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 28.Eggs and caterpillars of Melitaea shahvarica sp. nov. in nature and in the laboratory.A–B. Freshly laid eggs under a leaf of a host plant, May 2018, Iran, Shahvar Mt., alt. 2200 m. C–D. IV–V instar caterpillars on the leaves of the host plant Phlomoides molucelloides (Bunge) Salmaki, July 2019, Iran, Shahvar Mt., alt. 2500 m. E. I instar caterpillars in the laboratory, Moscow, May 2018. F. VI instar caterpillars during diapause, Moscow, October 2018.
Fig. 18. Male genitalia and harpe. A–C in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 18. Male genitalia and harpe. A–C. Melitaea shahvarica sp. nov. D–E. M. lutko Evans, 1932. F–I. M. mimetica Higgins, 1940. A–C. Iran, Semnan Prov., Shahrud area, S macroslope of Shahvar Mts, alt. 2200–2400 m. D–E. Pakistan, Chitral, Chaghbini, CGNP [Chitral Gol National Park], alt. 2700 m. F–G. Afghanistan, Bamian Prov., Punjub Distr., 10 km. NE Varas v., alt. 2400 m. H–I. Afghanistan, Bamian Prov., Panjub Distr., 10 km. NE Varas vil., alt. 2400 m.
Fig. 8 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 8. Distribution of Melitaea mimetica Higgins, 1940. For a description of the symbols with letters, see Fig. 30. = M. mimetica mimetica Higgins, 1940; = M. mimetica delerei Heidemann, 1954.
Fig. 14 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 14. Distribution of Melitaea timandra timandra Coutsis & van Oorschot, 2014, M. timandra binaludica subsp. nov. and M. shahvarica sp. nov. For a description of the points by letters, see Fig. 30. = Melitaea timandra timandra; = Melitaea timandra binaludica subsp. nov.; = Melitaea shahvarica sp. nov.;? = unconfirmed finds of Melitaea timandra; = Melitaea timandra with uncertain subspecies status.
Fig. 17 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 17. Male genitalia (without aedeagus) in dorsal projection. A–C. Melitaea timandra timandra Coutsis & van Oorschot, 2014. D–I. M. timandra binaludica subsp. nov. A–C. S Turkmenistan, SaryYazy, alt. 300 m. D –F. Iran, Rezavi Khorassan Prov., Kuh-e-Binalud Mts, Dorrud v. vicinity, alt. 2430 m. G. Iran, Horossan Prov., 35 km N of Birjant t. H. Afghanistan, Bamian Prov., Band-e-Amir, alt. 3200 m. I. Central Afghanistan, Bamian Prov., Band-e-Amir, Dzhudoi-Kvak Gorge, alt. 3200 m.
Fig. 24 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 24. First instar caterpillar of Melitaea shahvarica sp. nov. A. Head, bottom view. B. Head, front view. C–D. Head, lateral view. E–F. Caterpillar, lateral view.
Fig. 6 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 6. Adults of M. mimetica Higgins, 1940. A –H. UPS. I –P. UNS. A–B, I–J. ♂, Pakistan, Balochistan, Quetta, Urak, alt. 2400–2700 m. C, K. ♂, Afghanistan, Ghowr Prov., Bayan Range, 15 km S of Chagcharan, Kindival vall. D, L. ♂, Afghanistan, Bamian Prov., Punjub Distr., 10 km NE of Varas v., alt. 2400 m. E–F, M–N. ♀, Pakistan, Balochistan, Quetta, Urak, alt. 2400–2700 m. G, O. ♀, Central Afghanistan, Bamian Prov., 8 km S of Bamian, Koh-e-Baba Mts, Dara-e-Khushkak, alt. 2930 m. H, P. ♀, Afghanistan, Bamian Prov., Punjub Distr., 10 km NE of Varas v., alt. 2400 m. B, J photos by Dr Eckweiler).
Fig. 5 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 5. Distribution of M. lutko Evans, 1932. For a description of the dots with letters see Fig. 30.
Fig. 4 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 4. Female genitalia (without the anal papillae, copulatory bursa, and anterior and posterior apophyses). A–D. M. shahvarica sp. nov., Iran, Semnan Prov., Shahrud area, S macroslope of Shahvar Mts, alt. 2200–2400 m. E. M. lutko Evans, 1932, Chitral Gol National Park, Chitral, Pakistan, alt. 2700 m. F–I. M. mimetica Higgins, 1940. F. Pakistan, Balochistan, Quetta, Urak, alt. 2400– 2700 m. G–H. Afghanistan, Bamian Prov., Punjub Distr., 10 km NE of Varas v., alt. 2400 m. I. Central Afghanistan, Ghor Prov., 17 km E of Changcharan, 15 km S of Bandi-Ali, Gazak Mts, alt. 2400 m.
Fig. 13 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 13. Biotopes and biology of Melitaea timandra timandra Coutsis & van Oorschot, 2014. A. Bumpycellular overgrown sands on the left bank of the Murgab River, alt. 300 m, April 1993, the habitat of M. timandra timandra. B. Phlomoides regeliana (Aitch. & Hemsl.) Adylov, Kamelin & Makhm. – host plant for M. timandra timandra. The female laying eggs is visible under the leaves of the plant. C. The female of M. timandra timandra is ovipositing on the soil under the host plant leaf. D. Egg clutch of M. timandra timandra on the basal leaf rosette of Ph. regeliana.
Fig. 16 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 16. Male genitalia (without aedeagus) in dorsal projection. A–C. Melitaea shahvarica sp. nov. D–H. M. mimetica Higgins, 1940. I. M. lutko Evans, 1932. A–C. Iran, Semnan Prov., Shahrud area, S macroslope of Shahvar Mts, alt. 2200–2400 m. D. Pakistan, Balochistan, Quetta, Urak, alt. 2400– 2700 m. E. Afghanistan, Bamian Prov., 10 km S of Bamian t., Hushkak v. vicinity, alt, 2700– 2800 m. F. Central Afghanistan, Ghor Prov., 17 km E of Changcharan, 15 km S of Bandi-Ali, Gazak Mts, alt. 2400 m. G. Afghanistan, Bamian Prov., Punjub Distr., 10 km NE of Varas v., alt. 2400 m. H. Afghanistan, Ghor Prov., 16 km E of Changcharan, Bandi-Ali v. vicinity, alt. 2400 m. I. Pakistan, Chitral, Chaghbini CGNP [Chitral Gol National Park], alt. 2700 m.
Fig. 3 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 3. Male genitalia (a = valva; b = aedeagus). A–G. Melitaea mimetica Higgins, 1940. H–I. M. lutko Evans, 1932. A. Pakistan, Balochistan, Quetta, Urak, alt. 2400–2700 m. B. Pakistan, Balochistan, Quetta, Urak, alt. 2400–2700 m. C. Central Afghanistan, Ghor Prov., 17 km E Changcharan, 15 km S of Bandi-Ali, Gazak Mts, alt. 2400 m. D. Central Afghanistan, Ghor Prov., 17 km E of Changcharan, 15 km S of Bandi-Ali, Gazak Mts, alt. 2400 m. E. Afghanistan, Bamian Prov., 10 km S of Bamian t., Hushkak v. vicinity, alt. 2700–2800 m. F. Afghanistan, Bamian Prov., Punjub Distr., 10 km NE of Varas v., alt. 2400 m. G. Central Afghanistan, Ghor Prov., 17 km E of Changcharan, 15 km S of Bandi-Ali, Gazak Mts, alt. 2400 m. H. Chitral Gol National Park, Chitral, Pakistan, alt. 2700 m. I. Chitral Gol National Park, Chitral, Pakistan, alt. 2700 m.
Fig. 7 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 7. Eggs of Melitaea mimetica Higgins, 1940, Afghanistan, Ghor Prov., 16 km E of Changcharan, Bandi-Ali v. vicinity, alt. 2400 m. A–C. Lateral view. D–F. View from above. G–I. Micropile area.
Fig. 10 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 10. Male genitalia (a = valva; b = aedeagus). A–F. Melitaea timandra timandra Coutsis & van Oorschot, 2014. G–O. M. timandra binaludica subsp. nov. A–C. S Turkmenistan, Sary-Yazy, alt. 300 m. D. Paratype, Turkmenistan, Badhyz Reserve, Kepeli. E–F. S Turkmenistan, Sary-Yazy, alt. 300 m. G–L. Iran, Rezavi Khorassan Prov., Kuh-e-Binalud Mts, Dorrud v. vicinity, alt. 2430 m. M. Central Afghanistan, Bamian Prov., Band-e-Amir, Dzhudoi-Kvak Gorge, alt. 3200 m. N. Bande-Amir, Hazarajat, Afghanistan. O. Afghanistan, Bamian Prov., Band-e-Amir, alt. 3200 m.
Fig. 12 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 12. Eggs of Melitaea timandra timandra Coutsis & van Oorschot, 2014, S. Turkmenistan, SaryYazy. A–C. Lateral view. D–F. View from above. G–I. Micropile area.
Fig. 2 in Review of the fritillary species systematically close to Melitaea lutko Evans, 1932 (Lepidoptera: Nymphalidae) with analysis of their geographic distribution and interrelations with host plants
Fig. 2. Adults of Melitaea lutko Evans, 1932 and M. timandra binaluduca subsp. nov. A–H. UPS. I–P. UNS. A, I. M. lutko, ♂, Chitral Gol National Park, Chitral, Pakistan, alt. 2700 m. B, J. M. timandra binaluduca subsp. nov., ♂, Iran, S Khorasan Prov., 35 km N Birjant t. C, K. M. timandra binaluduca subsp. nov., ♂, Central Afghanistan, Bamian Prov., Band-e-Amir, Dzhudoi-Kvak Gorge, alt. 3200 m. D, L. M. timandra binaluduca subsp. nov., ♂, Afghanistan, Bamian Prov., Band-e-Amir, alt. 3200 m. E, M. M. lutko, ♀, Chitral Gol National Park, Chitral, Pakistan, alt. 2700 m. F, N. M. timandra binaluduca subsp. nov., ♂, Iran, Mazandaran Prov., S macroslopes of Albors Mts, 80 km SE of Sari, 5 km NE Foulad Mahhaleh v., E slopes of Sultan Kuh Mt., alt. 2000 m. G, O. M. timandra binaluduca subsp. nov., ♀, Afghanistan, Bamian Prov., Band-e-Amir, alt. 3200 m. H, P. M. timandra binaluduca subsp. nov., ♀, Central Afghanistan, Bamian Prov., Band-e-Amir, Dzhudoi-Kvak Gorge, alt. 3200 m.
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Allen Brain Atlas
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OpenNeuro
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