Quercus hinckleyi
C.H.Mull.
Pays · région · aire protégée · écorégion · biome
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Calcul du tissu écologique de Quercus hinckleyi.
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Liste rouge IUCN
CR · En danger critiquecritères C2a(ii)↘Décroissante- Évaluation
- 2017 · v3.1
- Altitude
- 1000 – 1400 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Because Q. hinckleyi has reproduced in a vastly clonal manner within its current distribution, including clones stretching 30 m across, there has been much confusion regarding actual population size, number of distinct individuals, and age of individuals.
Backs et al. (2015) began to understand some of these questions through a genetic analysis of the species, which covers all known Hinckley's Oak occurrence locations. Leaf samples were collected from all shrub clumps present at two areas, about 60 km apart. Two small sites (3 km apart) near Shafter, Texas, made up the first area, just northwest of Big Bend Ranch State Park. The other collection area, located in the eastern half of Big Bend State Park, has been labeled the 'Solitario' locality and is composed of one small group and one larger group. This protected site is in the area where Muller described the original type location. A total of 204 ramets (individuals) were sampled, and microsatellites were used to genotype these collections. From this total, which represents all known Q. hinckleyi occurrences currently, 123 unique genotypes were identified, with multiple trials and probability statistics providing reasonable certainty in these calculations. High clonality was determined at the two Shafter sites, with only seven unique genotypes among 58 ramets sampled, which leaves 116 unique genotypes at the Solitario location. But surprisingly, overall, these remnant populations of Q. hinckleyi exhibit strong population differentiation, and do not act as fringe pioneers with founder effects or genetic bottlenecks.
It is still difficult to determine the number of mature individuals (population size) for this species due to its clonal, clumping nature. But, during her sampling in search of unique genotypes Backs collected from 204 individuals, and reports that about 200 is a reasonable estimate for the total number of mature individuals currently (J. R. Backs pers. comm. 2016).
Backs et al. (2015) began to understand some of these questions through a genetic analysis of the species, which covers all known Hinckley's Oak occurrence locations. Leaf samples were collected from all shrub clumps present at two areas, about 60 km apart. Two small sites (3 km apart) near Shafter, Texas, made up the first area, just northwest of Big Bend Ranch State Park. The other collection area, located in the eastern half of Big Bend State Park, has been labeled the 'Solitario' locality and is composed of one small group and one larger group. This protected site is in the area where Muller described the original type location. A total of 204 ramets (individuals) were sampled, and microsatellites were used to genotype these collections. From this total, which represents all known Q. hinckleyi occurrences currently, 123 unique genotypes were identified, with multiple trials and probability statistics providing reasonable certainty in these calculations. High clonality was determined at the two Shafter sites, with only seven unique genotypes among 58 ramets sampled, which leaves 116 unique genotypes at the Solitario location. But surprisingly, overall, these remnant populations of Q. hinckleyi exhibit strong population differentiation, and do not act as fringe pioneers with founder effects or genetic bottlenecks.
It is still difficult to determine the number of mature individuals (population size) for this species due to its clonal, clumping nature. But, during her sampling in search of unique genotypes Backs collected from 204 individuals, and reports that about 200 is a reasonable estimate for the total number of mature individuals currently (J. R. Backs pers. comm. 2016).
Menaces identifiées(7 menaces classées CMP-IUCN)
11_1Habitat shifting & alterationCausing/Could cause fluctuationsWhole (>90%)Ongoing1_3Tourism & recreation areasCausing/Could cause fluctuationsMinority (<50%)Ongoing2_3_4Scale Unknown/UnrecordedCausing/Could cause fluctuationsMinority (<50%)Ongoing4_1Roads & railroadsCausing/Could cause fluctuationsMinority (<50%)Ongoing8_2_1Unspecified speciesCausing/Could cause fluctuationsMajority (50-90%)Ongoing8_2_2Named speciesCausing/Could cause fluctuationsMinority (<50%)Ongoing8_2_2Named speciesCausing/Could cause fluctuationsMinority (<50%)Ongoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Simply the species' very small, fragmented current range is a threat to its existence, but The State of Texas has acquired the majority of land containing Hinckley's Oak, decreasing the spatial component of concern. Hybridization with Q. pungens and Q. vaseyana should be noted as a possible future threat, but does not seem to be extensive at this time (U.S. Fish and Wildlife Service 2008, Backs et al. 2016). Certainly genetic threats should be considered for this small population as well (Backs et al. 2015). With the current reproduction method overwhelmingly clonal, continued diversification of genotypes and population of new areas are stunted. Finally, if unique genotypes are not being added to the population, Q. hinckleyi will have limited adaptation capabilities and face an even greater threat from climate change.
This general question propelled Backs et al. (2015) to carry out genetic analysis of all known Q. hinckleyi populations: if this species with a small and fragmented distribution has the common negative symptoms of such a situation (low levels of genetic variability, inbreeding, and limited gene flow)? Microsatellites were used to genotype 204 ramets (individuals), whose leaves were gathered from all three known occurrences. Next, eight loci were analyzed and used to determine levels of genetic variability, population structure, and clonal growth. Results were not entirely as expected, which is good news for Quercus hinckelyi. Genetic diversity was high and no evidence was found of inbreeding. It was determined that there are two distinct subpopulations. The two smallest sites sampled did exhibit extensive cloning, with only seven unique genotypes out of 58 individuals sampled, although the other sites seem to have been reproducing sexually because there is less clonal presence. This cloning does stunt the number of unique individuals, but "allelic diversity and levels of heterozygosity across the metapopulation are comparable to nonthreatened oak species" (Backs et al. 2015). Many believe that Q. hinckleyi's clonal reproduction may actually be an adaptive response to habitat fragmentation and environmental change. This clonality may have ultimately saved the relict species from extinction by helping it preserve a greater number of individual genotypes through the limitation of genetic drift, introgression, and swamping.
But, cloning likely cannot protect the species indefinitely. Although acorns were found at the larger sites within Big Bend Ranch State Park and there appears to be evidence of recruitment, there is no current evidence of recruitment at the smaller Shafter site. This prevents continued diversification of genotypes, as well as the species' ability to populate new areas by the natural transportation of acorns. Also, Handel observed in 1985 that as clones increase in size, flowers become surrounded with more of the same genetic entity and therefore may produce less viable seed. This is especially true for oaks, since it is generally believed that self-pollination is not successful. As the climate shifts and landscapes change, Q. hinckleyi will have a difficult time adapting without the formation of new genotypes. It is not known why sexual reproduction at the Shafter site is so rare. Backs et al. (2015) theorized that "human-induced habitat degradation, poor regeneration from seed coupled with limited number of genets... wildlife and insect predation... genetic barriers to seed production because of the limited number of genotypes available for crossing... [and] plant and seed predation" all affect this species' ability to recruit new individuals sexually.
This general question propelled Backs et al. (2015) to carry out genetic analysis of all known Q. hinckleyi populations: if this species with a small and fragmented distribution has the common negative symptoms of such a situation (low levels of genetic variability, inbreeding, and limited gene flow)? Microsatellites were used to genotype 204 ramets (individuals), whose leaves were gathered from all three known occurrences. Next, eight loci were analyzed and used to determine levels of genetic variability, population structure, and clonal growth. Results were not entirely as expected, which is good news for Quercus hinckelyi. Genetic diversity was high and no evidence was found of inbreeding. It was determined that there are two distinct subpopulations. The two smallest sites sampled did exhibit extensive cloning, with only seven unique genotypes out of 58 individuals sampled, although the other sites seem to have been reproducing sexually because there is less clonal presence. This cloning does stunt the number of unique individuals, but "allelic diversity and levels of heterozygosity across the metapopulation are comparable to nonthreatened oak species" (Backs et al. 2015). Many believe that Q. hinckleyi's clonal reproduction may actually be an adaptive response to habitat fragmentation and environmental change. This clonality may have ultimately saved the relict species from extinction by helping it preserve a greater number of individual genotypes through the limitation of genetic drift, introgression, and swamping.
But, cloning likely cannot protect the species indefinitely. Although acorns were found at the larger sites within Big Bend Ranch State Park and there appears to be evidence of recruitment, there is no current evidence of recruitment at the smaller Shafter site. This prevents continued diversification of genotypes, as well as the species' ability to populate new areas by the natural transportation of acorns. Also, Handel observed in 1985 that as clones increase in size, flowers become surrounded with more of the same genetic entity and therefore may produce less viable seed. This is especially true for oaks, since it is generally believed that self-pollination is not successful. As the climate shifts and landscapes change, Q. hinckleyi will have a difficult time adapting without the formation of new genotypes. It is not known why sexual reproduction at the Shafter site is so rare. Backs et al. (2015) theorized that "human-induced habitat degradation, poor regeneration from seed coupled with limited number of genets... wildlife and insect predation... genetic barriers to seed production because of the limited number of genotypes available for crossing... [and] plant and seed predation" all affect this species' ability to recruit new individuals sexually.
Habitats préférentiels (classification IUCN)
3_5Shrubland - Subtropical/Tropical Dry★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
In 1992, the U.S. Fish and Wildlife Service published the Hinckley's Oak Recovery Plan. The criterion for removal from the endangered list was to "attain at least 20 viable self-sustaining populations in at least 4 geographically distinct population centres and attain a total of at least 10,000 individual plants. Demonstrate population viability at recovery levels for 10 consecutive years." Within the species' five year review - which did not occur until 2008 - it was found that little new information about Q. hinckleyi had been collected and few recovery actions had been implemented. The strongest outcome at that point was the attainment of the Solitario location by the State of Texas, within Big Bend Ranch State Park, which had prior private control (U.S. Fish and Wildlife Service 2008). But, through their 2015 and 2016 studies, Backs et al. list the fulfilment of three high priority tasks within the recovery plan: "#3212 to assess genetic viability and needs, and #3231 to determine types of reproduction and contribution to population" (Backs et al. 2015), and #3213 to assess incidence of (and potential threat from) hybridization with nearby Quercus species and develop management strategies to address any problems (Backs et al. 2016). It may also be that the 1992 recovery plan needs revisions, in the case of the removal-criterion proving impossible and/or lacking definition.
Moving forward, all of Q. hinckleyi's limited locations should be protected in order to preserve their comparatively extensive genetic diversity. Human impact should be limited, while studies are needed regarding the species' reproductive biology, reaction to climate change, and health following reintroduction of other threatened native species such as the Desert Bighorn Sheep (Ovis canadensis). If more is known about the effects of "self-fertilization, local outcross pollination, and inter-population outcrossing" on Hinckley's Oak, increasingly successful conservation actions can be taken. This may include hand pollination and/or trans-locating some individuals. Finally, it is possible that other isolated populations exist within Texas and adjacent Mexico. Collaborative efforts should be initiated with the aim to locate further potential pockets, placing these areas under protection as well (Backs et al. 2015).
The species is located within three ex situ sites globally, but there are currently no specimens present in the recently-formed Quercus Multi-site Collection, as part of American Public Garden Association's Plant Collections Network (BGCI 2016).
Moving forward, all of Q. hinckleyi's limited locations should be protected in order to preserve their comparatively extensive genetic diversity. Human impact should be limited, while studies are needed regarding the species' reproductive biology, reaction to climate change, and health following reintroduction of other threatened native species such as the Desert Bighorn Sheep (Ovis canadensis). If more is known about the effects of "self-fertilization, local outcross pollination, and inter-population outcrossing" on Hinckley's Oak, increasingly successful conservation actions can be taken. This may include hand pollination and/or trans-locating some individuals. Finally, it is possible that other isolated populations exist within Texas and adjacent Mexico. Collaborative efforts should be initiated with the aim to locate further potential pockets, placing these areas under protection as well (Backs et al. 2015).
The species is located within three ex situ sites globally, but there are currently no specimens present in the recently-formed Quercus Multi-site Collection, as part of American Public Garden Association's Plant Collections Network (BGCI 2016).
Actions de conservation (4)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection3_2Species recovery3_4_1Captive breeding/artificial propagation5_2Policies and regulations
Stress écologiques (12)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_3_1Hybridisation2_3_1Hybridisation2_3_7Reduced reproductive success2_3_7Reduced reproductive success2_3_7Reduced reproductive success
Priorités de recherche (3)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology2_1Species Action/Recovery Plan
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Nearctic
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Shrub - small
Références bibliographiques (8)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2020. The IUCN Red List of Threatened Species. Version 2020-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 13 June 2020).
- IUCN. 2017. The IUCN Red List of Threatened Species. Version 2017-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 14 September 2017).
- BGCI. 2016. PlantSearch. London: Botanic Gardens Conservation International Available at: <a href="www.bgci.org/plant_search.php">www.bgci.org/plant_search.php</a>.
- Backs, J.R., Martin T. and Ashley, M.V. 2016. Using Genetic Analysis to Evaluate Hybridization as a Conservation Concern for the Threatened Species Quercus hinckleyi CH Muller (Fagaceae). <i>International Journal of Plant Sciences</i> 177(2): 122-131.
- Backs, J.R., Martin T., Klein, M. and Ashley, M.V. 2015. Genetic analysis of a rare isolated species: A tough little West Texas oak, Quercus hinckleyi C.H. Mull. <i>The Journal of the Torrey Botanical Society</i> 142(4): 302-313.
- U.S. Fish and Wildlife Service, Trans-Pecos Sub-Office. 2008. Hinckley Oak (Quercus hinckleyi) 5-Year Review. Alpine, TX.
- Handel, S.N. 1985. The intrusion of clonal growth patterns on plant breeding systems. <i>The American Naturalist</i> 125(3): 367–384.
- U.S. Fish and Wildlife Service. 1992. Hinckleyi Oak (Quercus hinckleyi) Recovery Plan. U.S. Fish and Wildlife Service, Albuquerque, New Mexico. 39 pp.
Évaluateurs & contributeurs (3)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Beckman, E.
contributor
Backs, J.
evaluator
Oldfield, S.
⚠ 1 erratum publié après l'évaluation.
Beckman, E. 2017. Quercus hinckleyi (errata version published in 2020). The IUCN Red List of Threatened Species 2017: e.T30955A176953830. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s