The habitats and ecology of Schinia zuni are not well understood. Most occurrences of this species are within the North Central New Mexico Valleys and Mesas and Semiarid Tablelands of the Arizona /New Mexico Plateau ecoregion (Griffith et al. 2006). This ecoregion is a mosaic of sparse semiarid grasslands and desert scrub shrublands (Ruhlman 2012).

Schinia moths are called the “flower moths” because as caterpillars they feed on buds or flowers of their host plant. In most cases, Schinia are oligophagous, meaning specialized to feed on only one genus or a few related genera of plants (Mitter et al. 1993). In Texas, many species are known in association with Asteraceae plants. Larvae are short-lived, feeding for less than a month, perhaps due to this flower-specific lifestyle (Peigler and Vinson 1988). They are also found frequently as adults on flowers, resting and feeding on nectar during daylight hours or providing pollination services at night (BugGuide 2023).

Schinia zuni was named for its type locality on the Zuni Indian Reservation (Pueblo of Zuni) (McElvare 1950), which is located in western New Mexico. It also occurs in Sandoval, Rio Arriba, and McKinley Counties, New Mexico, and in Apache County, Arizona. Occurrences in Apache and McKinley Counties are within the Navajo Nation (GBIF.org 2024). With increased survey effort, the species may be found in additional localities.

This species occurs in some semi-protected federal lands, such as the Santa Fe National Forest (GBIF.org 2024). However, there is no conservation action currently in progress for Schinia zuni. There is a critical need for research to determine the full range, population size and trends, habitats and ecology (including host plant preferences), and threats.

Threats to this species are not well understood, though threats to sympatric Lepidoptera species, including increased incidence and severity of drought due to climate change, livestock grazing, and invasive species, likely also negatively impact this species.

The Southwestern U.S. saw its driest 22-year period from 2000 to 2021, since at least 800 CE (the time period used in previous climatic reconstructions) (Williams et al. 2022). Droughts are projected to become more prolonged, severe, and common in the region under future climate change scenarios (USGCRP 2018). The impact of drought on specific Lepidoptera populations is not well understood, though advanced timing to adulthood has been observed in some butterfly species, which may lead to phenological mismatch with plant resources (Forister et al. 2018). Drought may also adversely impact larval host plants and nectar sources (Pettorelli et al. 2007, Gottfried et al. 2012).

Due to the aridity of this region, there is minimal forage for livestock, yet the region is used extensively as rangeland. Two thirds of Navajo rangelands were determined to be overgrazed as early as 1933. Drought conditions in northeastern Arizona in recent years, have further degraded rangeland by increasing wind erosion and sand-dune mobility (Rhulman 2012). Grazing has been know to degrade habitat for herbivorous insects, such as the Sacramento Mountains Checkerspot Butterfly, by reducing the health and abundance of host plants (McIntyre 2010). It often also promotes the spread of invasive species, which outcompete host plants and change the composition of vegetation communities (Souther et al. 2019).

Habitat on the Navajo Nation may be threatened by encroachment of invasive species, for example Saltcedar (Tamarix spp.) and Russian olive (Elaeagnus angustifolia) in riparian regions, and various nonnative forbs (e.g. thistles) and grasses in meadows (Mike and Talkington 2020). Because Schinia zuni has flower-feeding larvae, this habitat degradation likely threatens the abundance or establishment of this moth’s host plant, like it does for the threatened Great Basin Silverspot Butterfly (Argynnis nokomis) (Mike and Talkington 2020). Having a narrow host range, like other Schinia species (Mitter et al. 1993), may put this species at greater threat of habitat loss. However, research is needed to determine what host plants are utilized by S. zuni, and where they occur.

The population size and trend are not known for this species. It went unobserved for 60 years, until it was rediscovered by Chuck Harp in 2009 (Bettman 2012). Since 2009, over two dozen occurrences have been recorded (GBIF.org 2024). This likely indicates a historical lack of targeted surveys within this moth’s range.

• Peigler, R.S. and Vinson, S.B.. 1988. Parasitoid and hostplant records for genus Schinia (Noctuidae) in Texas. Journal of the Lepidopterists' Society 42: (144–145).
• Mike, J. and Talkington, N.. 2020. Wildlife habitat and invasive plant species prioritization. Navajo Nation Department of Fish & Wildlife Diné Native Plants Program, Window Rock, AZ .
• ITIS. 2024. Integrated Taxonomic Information System (ITIS). 2024. https://www.itis.gov/
• Ruhlman, J., Gass, L. and Middleton, B.. 2012. Arizona/New Mexico Plateau Ecoregion. U.S. Geological Survey Professional Paper 1794–A, 2012.
• Griffith, G.E., Omernik, J.M., McGraw, M.M., Jacobi, G.Z., Canavan, C.M., Schrader, T.S., Mercer, D., Hill, R. and Moran, B.C.. 2006. Ecoregions of New Mexico (color poster with map, descriptive text, summary tables, and photographs). U.S. Geological Survey (map scale 1:1,400,000), Reston, Virginia .
• GBIF.org. 2024. GBIF Occurrence Download. May 8th. https://doi.org/10.15468/dl.yta3js
• Mitter, C., Poole, R.W. and Matthews, M.. 1993. Biosystematics of the Heliothinae (Lepidoptera: Noctuidae). Annual Review of Entomology 38: (207-225).
• Pettorelli, N., Pelletier, F., von Hardenberg, A., Festa-Bianchet, M. and Côté S.D. 2007. Early onset of vegetation growth vs rapid green-up: impacts on juvenile mountain ungulates. Ecology 88: (381-390).
• McElvare, R.R.. 1950. A new heliothid from New Mexico. Bulletin of the Brooklyn Entomological Society 45: (83-84).
• BugGuide. 2023. Genus Schinia- Flower Moths. 2024. https://bugguide.net/node/view/238
• USGCRP. 2018. Impacts, Risks, and Adaptation in the United States: Fourth National Climate Assessment, Volume II. U.S. Global Change Research Program , Washington, DC, USA : (1515).
• McIntyre, J.. 2010. Habitat variables, mammal interactions, and recovery approaches important to a rare, New Mexican butterfly, Euphydryas anicia cloudcrofti (Lepidoptera: Nymphalidae). University of New Mexico, Albuquerque, NM : (115). https://digitalrepository.unm.edu/biol_etds/78
• Souther, S., Loeser, M., Crews, T.E. and Sisk, T.. 2019. Drought exacerbates negative consequences of high-intensity cattle grazing in a semiarid grassland. Ecological Applications 30: (e02048).
• Williams, A.P., Cook, B.I. and Smerdon, J.E. . 2022. Rapid intensification of the emerging southwestern North American megadrought in 2020–2021. Nature Climate Change 12: (232-234).
• Gottfried, M., Pauli, H., Futschik, A., et al. 2012. Continent-wide response of mountain vegetation to climate change. Nature Climate Change 2: (111-115).
• Forister, M.L., Fordyce, J.A., Nice, C.C., Thorne, J.H., Waetjen, D.P. and Shapiro, A.M.. 2018. Impacts of a millennium drought on butterfly faunal dynamics. Climate Change Responses 5: (9-Jan).
• Bettman, D.. 2012. The Lepidoptera Collection at the Denver Museum of Nature & Science, Denver, Colorado: Description and Holdings. Denver Museum of Nature & Science, Denver, CO .