Understanding the drivers of expert opinion when classifying species as extinct.

The criteria as laid out by the International Union for the Conservation of Nature (IUCN) Red List are the gold standard by which the extinction risk of a species is assessed and where appropriate biological extinctions are declared. However, unlike all other categories, the category of extinct lacks a quantitative framework for assigning this category. Given its subjective nature, we surveyed expert assessors working on a diversity of taxa to explore the attributes they used to declare a species extinct. Using a choice experiment approach, we surveyed 674 experts from the IUCN Species Survival Commission specialist groups and taskforces. Data availability, time from the last sighting, detectability, habitat availability, and population decline were all important attributes favored by assessors when inferring extinction. Respondents with red-listing experience assigned more importance to the attributes data availability, time from the last sighting, and detectability when considering a species extinction, whereas those respondents working with well-known taxa gave more importance to the time from the last sighting. Respondents with no red-listing experience and those working with more well-known taxa (i.e., mammals and birds) were overall less likely to consider species extinct. Our findings on the importance assessors place on attributes used to declare a species extinct provide a basis for informing the development of specific criteria for more accurately assessing species extinctions.

Los criterios establecidos por la Unión Internacional para la Conservación de la Naturaleza (UICN) son la regla de oro con la cual se evalúa el riesgo de extinción de una especie y en donde se declaran las extinciones biológicas. Sin embargo, como con todas las demás categorías, la categoría "extinto" carece de un marco de trabajo cuantitativo para asignar esta categoría. Dada su naturaleza subjetiva, pedimos a los asesores expertos que trabajan con la diversidad de taxones que exploraran los atributos que usan para declarar extinta a una especie. Mediante un experimento de elección, sondeamos a 674 expertos de los grupos especialistas y de trabajo de la Comisión de Supervivencia de Especies de la UICN. La disponibilidad de datos, el tiempo desde la última detección, la detectabilidad, la disponibilidad del hábitat y la declinación poblacional fueron atributos importantes que los asesores favorecieron al inferir las extinciones. Los respondientes con experiencia con la lista roja les asignaron mayor importancia a los atributos de disponibilidad de datos, tiempo desde la última detección y detectabilidad cuando consideraron la extinción de una especie, mientras que los respondientes que trabajan con taxones conocidos le dieron más importancia al tiempo desde la última detección. En general fue menos probable que los respondientes sin experiencia con la lista roja y aquellos que trabajan con los taxones más conocidos (es decir, mamíferos y aves) consideraran extinta a una especie. Nuestros descubrimientos sobre la importancia que los asesores colocan sobre los atributos utilizados para declarar extinta a una especie proporcionan una base para orientar el desarrollo de criterios específicos para evaluar de manera más acertada las extinciones de las especies.

Assessing conservation status with extensive but low-resolution data: Application of frequentist and Bayesian models to endangered Athabasca River rainbow trout.

Use of extensive but low-resolution abundance data is common in the assessment of species at-risk status based on quantitative decline criteria under International Union for Conservation of Nature (IUCN) and national endangered species legislation. Such data can be problematic for 3 reasons. First, statistical power to reject the null hypothesis of no change is often low because of small sample size and high sampling uncertainty leading to a high frequency of type II errors. Second, range-wide assessments composed of multiple site-specific observations do not effectively weight site-specific trends into global trends. Third, uncertainty in site-specific temporal trends and relative abundance are not propagated at the appropriate spatial scale. A common result is the propensity to underestimate the magnitude of declines and therefore fail to identify the appropriate at-risk status for a species. We used 3 statistical approaches, from simple to more complex, to estimate temporal decline rates for a designatable unit (DU) of rainbow trout in the Athabasca River watershed in western Canada. This DU is considered a native species for purposes of listing because of its genetic composition characterized as >0.95 indigenous origin in the face of continuing introgressive hybridization with introduced populations in the watershed. Analysis of abundance trends from 57 time series with a fixed-effects model identified 33 sites with negative trends, but only 2 were statistically significant. By contrast, a hierarchical linear mixed model weighted by site-specific abundance provided a DU-wide decline estimate of 16.4% per year and a 3-generation decline of 93.2%. A hierarchical Bayesian mixed model yielded a similar 3-generation decline trend of 91.3% and the posterior distribution showed that the estimate had a >99% probability of exceeding thresholds for an endangered listing. We conclude that the Bayesian approach was the most useful because it provided a probabilistic statement of threshold exceedance in support of an at-risk status recommendation.

El uso de datos extensivos, pero de baja resolución, de la abundancia es una práctica común en la evaluación del estado de riesgo de una especie con base en los criterios cuantitativos de declinación establecidos por la Unión Internacional para la Conservación de la Naturaleza (UICN) y la legislación nacional sobre especies en peligro extinción. Dicha información puede ser problemática por tres razones: primero, el poder estadístico para rechazar la hipótesis nula de ningún cambio es frecuentemente bajo debido a un tamaño pequeño de la muestra y a la elevada incertidumbre del muestreo, lo que resulta en una frecuencia elevada de errores de tipo II; segundo, las evaluaciones de amplia variedad compuestas de varias observaciones específicas de sitio no sopesan efectivamente las tendencias específicas de sitio dentro de las tendencias globales; y tercero, la incertidumbre en las tendencias temporales específicas de sitio y en la abundancia relativa no se propagan a la escala espacial apropiada. Un resultado común del uso de esta información es la propensión a subestimar la magnitud de las declinaciones, y por lo tanto equivocarse en la identificación del estado de riesgo apropiado para la especie. Usamos tres estrategias estadísticas, de simples a más complejas, para estimar las tasas de declinación temporal para una unidad designable (UD) de trucha arcoíris en la cuenca del río Athabasca al oeste de Canadá. Esta UD es considerada una especie nativa por razones de listado debido a su composición genética, caracterizada como >0-95 de origen nativo de frente a la continua hibridación introgresiva con poblaciones introducidas a la cuenca. El análisis de las tendencias de abundancia de 57 series de tiempo con un modelo de efectos fijos identificó 33 sitios con tendencias negativas, pero sólo dos fueron estadísticamente significativas. En contraste, un modelo lineal mixto de jerarquías sopesado por abundancia específica de sitio proporcionó una estimación de declinación en toda la UD de 16.4% año−1 y una declinación a tres generaciones de 93.2%. Un modelo bayesiano de jerarquías produjo una tendencia de declinación a tres generaciones de 91.3% y la distribución posterior mostró que el estimado tuvo una probabilidad >99% de exceder los umbrales para la categorización como especie en peligro. Concluimos que la estrategia bayesiana fue la más útil porque proporcionó una afirmación probabilística de la superación del umbral a favor de una recomendación de categorizar el estado como en riesgo.

A strategy for the next decade to address data deficiency in neglected biodiversity.

Measuring progress toward international biodiversity targets requires robust information on the conservation status of species, which the International Union for Conservation of Nature (IUCN) Red List of Threatened Species provides. However, data and capacity are lacking for most hyperdiverse groups, such as invertebrates, plants, and fungi, particularly in megadiverse or high-endemism regions. Conservation policies and biodiversity strategies aimed at halting biodiversity loss by 2020 need to be adapted to tackle these information shortfalls after 2020. We devised an 8-point strategy to close existing data gaps by reviving explorative field research on the distribution, abundance, and ecology of species; linking taxonomic research more closely with conservation; improving global biodiversity databases by making the submission of spatially explicit data mandatory for scientific publications; developing a global spatial database on threats to biodiversity to facilitate IUCN Red List assessments; automating preassessments by integrating distribution data and spatial threat data; building capacity in taxonomy, ecology, and biodiversity monitoring in countries with high species richness or endemism; creating species monitoring programs for lesser-known taxa; and developing sufficient funding mechanisms to reduce reliance on voluntary efforts. Implementing these strategies in the post-2020 biodiversity framework will help to overcome the lack of capacity and data regarding the conservation status of biodiversity. This will require a collaborative effort among scientists, policy makers, and conservation practitioners.

Una Estrategia para la Siguiente Década para Enfrentar la Deficiencia de Datos de la Biodiversidad Ignorada Resumen La medida del avance hacia los objetivos internacionales para la biodiversidad requiere información sólida sobre el estado de conservación de las especies, la cual proporciona la Lista Roja de Especies Amenazadas de la Unión Internacional para la Conservación de la Naturaleza (UICN). Sin embargo, los grupos más hiperdiversos, como los invertebrados, las plantas y los hongos, carecen de datos y capacidad, particularmente en regiones megadiversas o de endemismo alto. Las políticas de conservación y las estrategias de biodiversidad dirigidas hacia el cese de la pérdida de biodiversidad para el 2020 necesitan ser adaptadas para solucionar estas insuficiencias de información para después del año 2020. Diseñamos una estrategia de ocho puntos para cerrar las brechas existentes en los datos mediante la reactivación de la investigación exploratoria en el campo sobre la distribución, abundancia y ecología de las especies; la vinculación más cercana entre la investigación taxonómica y la conservación; la mejora a las bases de datos mundiales sobre biodiversidad mediante la presentación obligatoria de datos espacialmente explícitos para las publicaciones científicas; el desarrollo de una base mundial de datos espaciales sobre las amenazas para la biodiversidad para facilitar las valoraciones de la Lista Roja de la UICN; la automatización de las preevaluaciones mediante la integración de datos de distribución y datos de amenazas espaciales; el desarrollo de la capacidad en la taxonomía, la ecología y el monitoreo de la biodiversidad en países con una gran riqueza de especies o endemismos; la creación de programas de monitoreo de especies para los taxones menos conocidos; el desarrollo de suficientes mecanismos de financiamiento para reducir la dependencia de los esfuerzos voluntarios. La implementación de estas estrategias en el marco de trabajo para la biodiversidad posterior al 2020 ayudará a superar la falta de capacidad y datos con respecto al estado de conservación de la biodiversidad. Lo anterior requerirá de un esfuerzo colaborativo entre científicos, formuladores de políticas y practicantes de la conservación.

Using cumulative human-impact models to reveal global threat patterns for seahorses.

Understanding threats acting on marine organisms and their conservation status is vital but challenging given a paucity of data. We studied the cumulative human impact (CHI) on and conservation status of seahorses (Hippocampus spp.)-a genus of rare and data-poor marine fishes. With expert knowledge and relevant spatial data sets, we built linear-additive models to assess and map the CHI of 12 anthropogenic stressors on 42 seahorse species. We examined the utility of indices of estimated impact (impact of each stressor and CHI) in predicting conservation status for species with random forest (RF) models. The CHI values for threatened species were significantly higher than those for nonthreatened species (category based on International Union for Conservation of Nature Red List). We derived high-accuracy RF models (87% and 96%) that predicted that 5 of the 17 data-deficient species were threatened. Demersal fishing practices with high bycatch and pollution were the best predictors of threat category. Major threat epicenters were in China, Southeast Asia, and Europe. Our results and maps of CHI may help guide global seahorse conservation and indicate that modeling and mapping human impacts can reveal threat patterns and conservation status for data-poor species. We found that for exploring threat patterns of focal species, species-level CHI models are better than existing ecosystem-level CHI models.

Uso de Modelos de Impacto Humano Acumulativo para Revelar los Patrones de Amenaza Mundial para Hipocampos Resumen El entendimiento de las amenazas que actúan sobre los organismos marinos y su estado de conservación es de suma importancia pero a la vez un gran reto debido a la insuficiencia de datos. Estudiamos el estado de conservación y el impacto humano acumulativo (CHI, en inglés) que existe sobre los hipocampos (Hippocampus spp.)- un género de peces marinos raro y escaso de datos. Construimos modelos lineales aditivos con el conocimiento de expertos y conjuntos de datos espaciales relevantes para evaluar y mapear el CHI de los doce estresantes antropogénicos que afectan a las 42 especies de hipocampos. Examinamos la utilidad que tienen los índices de impacto estimado (el impacto de cada estresante y cada CHI) para la predicción del estado de conservación de las especies usando modelos de bosque azaroso (RF, en inglés). Los valores del CHI para las especies amenazadas fueron considerablemente más altos que aquellos obtenidos para las especies no amenazadas (categoría basada en la Lista Roja de la Unión Internacional para la Conservación de la Naturaleza). De esto derivamos modelos RF de alta certeza (87% y 96%), los cuales pronosticaron que cinco de las 17 especies deficientes de datos estaban amenazadas. Las prácticas de pesca demersal con una captura accesoria elevada y la contaminación fueron los mejores pronosticadores de la categoría de amenaza. Los principales epicentros de amenaza se ubicaron en China, el sureste asiático y en Europa. Nuestros resultados y mapas de CHI pueden ayudar a guiar la conservación mundial de hipocampos y también indican que el modelado y el mapeo de de los impactos humanos pueden revelar los patrones de amenaza y el estado de conservación de las especies deficientes de datos. Descubrimos que para explorar los patrones de amenaza de especies focales, son mejores los modelos de CHI a nivel de especie que los ya existentes modelos de CHI a nivel de ecosistema.

Predictability of demographic rates based on phylogeny and biological similarity.

Lack of demographic data for most of the world's threatened species is a widespread problem that precludes viability-based status assessments for species conservation. A commonly suggested solution is to use data from species that are closely related or biologically similar to the focal species. This approach assumes similar species and populations of the same species have similar demographic rates, an assumption that has yet to be thoroughly tested. We constructed a Bayesian hierarchical model with data on 425 plant species to predict demographic rates (intrinsic rate of population growth, recruit survival, juvenile survival, adult survival, and fecundity) based on biological traits and phylogenetic relatedness. Generally, we found small effects of species-level traits (except woody polycarpic species tended to have high adult survival rates that increased with plant height) and a weak phylogenetic signal for 4 of the 5 demographic parameters examined. Patterns were stronger in adult survival and fecundity than other demographic rates; however, the unexplained variances at both the species and population levels were high for all demographic rates. For species lacking demographic data, our model produced large, often inaccurate, prediction intervals that may not be useful in a management context. Our findings do not support the assumption that biologically similar or closely related species have similar demographic rates and provide further evidence that direct monitoring of focal species and populations is necessary for informing conservation status assessments.

Trait-based prediction of extinction risk of small-bodied freshwater fishes.

Small body size is generally correlated with r-selected life-history traits, including early maturation, short-generation times, and rapid growth rates, that result in high population turnover and a reduced risk of extinction. Unlike other classes of vertebrates, however, small freshwater fishes appear to have an equal or greater risk of extinction than large fishes. We explored whether particular traits explain the International Union for Conservation of Nature (IUCN) Red List conservation status of small-bodied freshwater fishes from 4 temperate river basins: Murray-Darling, Australia; Danube, Europe; Mississippi-Missouri, North America; and the Rio Grande, North America. Twenty-three ecological and life-history traits were collated for all 171 freshwater fishes of ≤120 mm total length. We used generalized linear mixed-effects models to assess which combination of the 23 traits best explained whether a species was threatened or not threatened. We used the best models to predict the probability of 29 unclassified species being listed as threatened. With and without controlling for phylogeny at the family level, small body size-among small-bodied species-was the most influential trait correlated with threatened species listings. The k-folds cross-validation demonstrated that body size and a random effect structure that included family predicted the threat status with an accuracy of 78% (SE 0.5). We identified 10 species likely to be threatened that are not listed as such on the IUCN Red List. Small body size is not a trait that provides universal resistance to extinction, particularly for vertebrates inhabiting environments affected by extreme habitat loss and fragmentation. We hypothesize that this is because small-bodied species have smaller home ranges, lower dispersal capabilities, and heightened ecological specialization relative to larger vertebrates. Trait data and further model development are needed to predict the IUCN conservation status of the over 11,000 unclassified freshwater fishes, especially those under threat from proposed dam construction in the world's most biodiverse river basins.

Orchid conservation in the biodiversity hotspot of southwestern China.

Xishuangbanna is on the northern margins of tropical Asia in southwestern China and has the largest area of tropical forest remaining in the country. It is in the Indo-Burma hotspot and contains 16% of China's vascular flora in <0.2% of the country's total area (19,690 km(2) ). Rapid expansion of monoculture crops in the last 20 years, particularly rubber, threatens this region's exceptional biodiversity. To understand the effects of land-use change and collection on orchid species diversity and determine protection priorities, we conducted systematic field surveys, observed markets, interviewed orchid collectors, and then determined the conservation status of all orchids. We identified 426 orchid species in 115 genera in Xishuangbanna: 31% of all orchid species that occur in China. Species richness was highest at 1000-1200 m elevation. Three orchid species were assessed as possibly extinct in the wild, 15 as critically endangered, 82 as endangered, 124 as vulnerable, 186 as least concern, and 16 as data deficient. Declines over 20 years in harvested species suggested over-collection was the major threat, and utility value (i.e., medicinal or ornamental value) was significantly related to endangerment. Expansion of rubber tree plantations was less of a threat to orchids than to other taxa because only 75 orchid species (17.6%) occurred below the 1000-m-elevation ceiling for rubber cultivation, and most of these (46) occurred in nature reserves. However, climate change is projected to lift this ceiling to around 1300 m by 2050, and the limited area at higher elevations reduces the potential for upslope range expansion. The Xishuangbanna Tropical Botanical Garden is committed to achieving zero plant extinctions in Xishuangbanna, and orchids are a high priority. Appropriate in and ex situ conservation strategies, including new protected areas and seed banking, have been developed for every threatened orchid species and are being implemented.

Extinction in a hyperdiverse endemic Hawaiian land snail family and implications for the underestimation of invertebrate extinction.

The International Union for Conservation of Nature (IUCN) Red List includes 832 species listed as extinct since 1600, a minuscule fraction of total biodiversity. This extinction rate is of the same order of magnitude as the background rate and has been used to downplay the biodiversity crisis. Invertebrates comprise 99% of biodiversity, yet the status of a negligible number has been assessed. We assessed extinction in the Hawaiian land snail family Amastridae (325 species, IUCN lists 33 as extinct). We did not use the stringent IUCN criteria, by which most invertebrates would be considered data deficient, but a more realistic approach comparing historical collections with modern surveys and expert knowledge. Of the 325 Amastridae species, 43 were originally described as fossil or subfossil and were assumed to be extinct. Of the remaining 282, we evaluated 88 as extinct and 15 as extant and determined that 179 species had insufficient evidence of extinction (though most are probably extinct). Results of statistical assessment of extinction probabilities were consistent with our expert evaluations of levels of extinction. Modeling various extinction scenarios yielded extinction rates of 0.4-14.0% of the amastrid fauna per decade. The true rate of amastrid extinction has not been constant; generally, it has increased over time. We estimated a realistic average extinction rate as approximately 5%/decade since the first half of the nineteenth century. In general, oceanic island biotas are especially susceptible to extinction and global rate generalizations do not reflect this. Our approach could be used for other invertebrates, especially those with restricted ranges (e.g., islands), and such an approach may be the only way to evaluate invertebrates rapidly enough to keep up with ongoing extinction.

Determining decision thresholds and evaluating indicators when conservation status is measured as a continuum.

Categorization of the status of populations, species, and ecosystems underpins most conservation activities. Status is often based on how a system's current indicator value (e.g., change in abundance) relates to some threshold of conservation concern. Receiver operating characteristic (ROC) curves can be used to quantify the statistical reliability of indicators of conservation status and evaluate trade-offs between correct (true positive) and incorrect (false positive) classifications across a range of decision thresholds. However, ROC curves assume a discrete, binary relationship between an indicator and the conservation status it is meant to track, which is a simplification of the more realistic continuum of conservation status, and may limit the applicability of ROC curves in conservation science. We describe a modified ROC curve that treats conservation status as a continuum rather than a discrete state. We explored the influence of this continuum and typical sources of variation in abundance that can lead to classification errors (i.e., random variation and measurement error) on the true and false positive rates corresponding to varying decision thresholds and the reliability of change in abundance as an indicator of conservation status, respectively. We applied our modified ROC approach to an indicator of endangerment in Pacific salmon (Oncorhynchus nerka) (i.e., percent decline in geometric mean abundance) and an indicator of marine ecosystem structure and function (i.e., detritivore biomass). Failure to treat conservation status as a continuum when choosing thresholds for indicators resulted in the misidentification of trade-offs between true and false positive rates and the overestimation of an indicator's reliability. We argue for treating conservation status as a continuum when ROC curves are used to evaluate decision thresholds in indicators for the assessment of conservation status.

Offsets and conservation of the species of the EU habitats and birds directives.

Biodiversity offsets are intended to achieve no net loss of biodiversity due to economic and human development. A variety of biodiversity components are addressed by offset policies. It is required that loss of protected species due to development be offset under the EU Habitats and Birds Directives in Europe. We call this type of offset a species-equality offset because the offset pertains to the same species affected by the development project. Whether species equality can be achieved by offset design is unknown. We addressed this gap by reviewing derogation files (i.e., specific files that describe mitigation measures to ensure no net loss under the EU Habitats and Birds Directives) from 85 development projects in France (2009-2010). We collected information on type of effect (reversible vs. irreversible) and characteristics of affected and offset sites (i.e., types of species, total area). We analyzed how the type of effect and the affected-site characteristics influenced the occurrence of offset measures. The proportion of species targeted by offset measures (i.e., offset species) increased with the irreversibility of the effect of development and the conservation status of the species affected by development (i.e., affected species). Not all effects on endangered species (International Union for Conservation of Nature Red List) were offset; on average, 82% of affected species would be offset. Twenty-six percent of species of least concern were offset species. Thirty-five percent of development projects considered all affected species in their offset measures. Species richness was much lower in offset sites than in developed sites even after offset proposals. For developed areas where species richness was relatively high before development, species richness at offset sites was 5-10 times lower. The species-equality principle appears to have been applied only partially in offset policies, as in the EU directives. We suggest the application of this principle through offsets is highly important for the long-term conservation of biodiversity in Europe. Compensaciones y Conservación de las Especies de las Directivas de Hábitats y Aves de la UE.

Avifauna en fragmentos de Bosque Mesófilo de Montaña y vegetación secundaria en el municipio de Huatusco, Veracruz / Birds in patches of cloud forest and secondary forest in the municipality of Huatusco, Veracruz

RESUMEN El Bosque Mesófilo de Montaña (BMM) del centro de Veracruz, México, representa un paisaje alterado por actividades antrópicas, por lo que es necesario evaluar el potencial evolutivo y adaptativo de las aves refugiadas en el sitio, las cuales se enfrentan a un paisaje con un gradiente heterogéneo. El objetivo de este estudio fue determinar la diversidad de aves en fragmentos de BMM y vegetación secundaria (VS), en el predio Finca La Pastoría, Huatusco, Veracruz, así como, asociar su presencia y/o alimentación a cada hábitat evaluado. Se identificaron las especies y número de individuos en 14 sitios de observación de aves, con el método de muestreo basado en conteo por puntos con radio fijo de 30 m. Se registraron 100 especies pertenecientes a 33 familias y 15 órdenes. En el BMM se identificaron 916 individuos, correspondientes a 89 especies, y en VS 331 individuos de 54 especies, encontrando diferencias significativas de diversidad de aves entre coberturas de muestreo. Destacan los registros de Dendrortyx barbatus, Leptotila verreauxi y Vireo griseus, por ser endémicas. La primera está clasificada en peligro de extinción, mientras que la segunda se encuentra sujeta a protección especial y la tercera amenazada. También se registraron Pionus senilis, especie amenazada; Falco peregrinus, Micrastur semitorquatus, Passerina ciris, Psarocolius montezuma, Myadestes occidentalis y Amazona albifrons, sujetas a protección especial. Este estudio brinda información sobre cómo la avifauna hace uso diferencial de dos coberturas de vegetación, la cual puede servir para generar estrategias sustentables para el manejo y conservación del bosque.

ABSTRACT The Cloud Forest (CF) in central Veracruz, Mexico, represents a landscape that has been altered by anthropic activities. Therefore, it is necessary to evaluate the evolutionary and adaptive potential of the birds sheltered in the site, which face a landscape with a heterogeneous gradient. The objective of the study was to describe the diversity of birds in fragments of CF and secondary vegetation (VS), in the property "Finca La Pastoría", Huatusco, Veracruz. The species and number of individuals in 14 bird watching sites were identified, with the sampling method based on counting points with a fixed radius of 30 m. 100 species from 33 families and 15 orders were recorded. In the CF, 916 individuals were identified, corresponding to 89 species, and in VS 331 individuals of 54 species, finding significant differences in bird diversity between sampling coverages. The records of Dendrortyx barbatus, Leptotila verreauxi and Vireo griseus stand out for being endemic and classified as endangered and threatened, respectively. Furthermore, Pionus senilis, a threatened species, as well as Falco peregrinus, Micrastur semitorquatus, Passerina ciris, Psarocolius montezuma, Myadestes occidentalis and Amazona albifrons, subject to special protection, were also recorded. This study provides information on how the birds make differential use of two vegetation covers, which can be used to generate sustainable strategies for forest management and conservation.

Biogeography and conservation of the herpetofauna of the Upland Pine-Oak Forests of Honduras / Biodiversidad y conservación de la herpetofauna de los Bosques de Pino-Roble de la Altiplanicie de Honduras

The upland pine-oak forest herpetofauna constitutes the smallest segment distributed in the major habitat types in Honduras, due to its occurrence at moderate elevations in relatively inhospitable environments, compared to more mesic habitats in the country. This segment, however, is subject to considerable environmental threat as a consequence of annual burning and logging. Of the 356 herpetofaunal species known from Honduras, 105 are known from these habitats. These forests occur throughout much of the mountainous interior of Honduras. They are subject to the Intermediate Dry climate. Four salamanders, 27 anurans, four turtles, 29 lizards, and 41 snakes comprise the herpetofauna. These species are partitioned into restricted, widespread, and peripheral distributional categories. They can be allocated to eleven broad distributional categories, with most belonging to the category containing species whose ranges extend from somewhere in Mexico north of the Isthmus of Tehuantepec to somewhere in South America. The large majority are terrestrial forest inhabitants, arboreal forest inhabitants, terrestrial pondside species, or terrestrial forest pondside species. Most species are judged common, with the next largest group considered to be of infrequent occurrence, and the smallest group of rare occurrence. Upland pine-oak forest species are distributed among four ecophysiographic areas, with the greatest number of species being found in the Southeastern Uplands. Construction of a CBR diagram illustrates that the herpetofaunas of the Northwestern and Northeastern Uplands, the Northeastern Uplands and Southeastern Uplands, and the Southeastern Uplands and Southwestern Uplands are about equally related to one another. The greatest significance of the upland pine-oak forest herpetofauna lies in the relatively high percentage of members presently possessing stable populations, indicating their apparent greater ability to resist anthropogenic habitat...

La herpetofauna de los bosques de pino-roble del altiplano constituye el segmento más pequeño distribuido en los habitats principales de Honduras, debido a su ocurrencia a elevaciones moderadas en ambientes relativamente inhóspitos, especialmente comparados a los ambientes más húmedos de país. Este segmento, sin embargo, está sujeto a una amenaza ambiental considerable, debido a las quemas anuales y a la tala de árboles. De las 356 especies de herpetofauna conocidas en Honduras, 105 son de estos habitats. Esta clase de bosques es prevalente en gran parte del interior montañoso de Honduras. Están sujetos al clima Seco Intermedio. La herpetofauna consiste de 4 salamandras, 27 anuros, cuatro tortugas, 29 lagartijas, y 41 serpientes. Estas especies se clasifican en categorías de distribución restrictas, extensas, y periféricas. Es posible colocar estas especies en once categorías de distribución, con la mayoría encontrándose en la categoría que contiene las especies cuyos rangos se extienden desde alguna parte de México al norte del Istmo de Tehuantepec hasta alguna parte de Suramérica. La gran mayoría son habitantes terrestres del bosque, habitantes arbóreos del bosque, especies terrestres de la orilla de estanques de agua, o especies terrestres del bosque encontradas a la orilla de estanques de agua. La mayoría de las especies se consideran comunes, con el próximo grupo más grande considerado como de ocurrencia poco frecuente, y el grupo más pequeño de rara ocurrencia. Las especies de bosques de pino y roble del altiplano están distribuidas en cuatro áreas ecofisiográficas, con el mayor número de especies encontradas en los altiplanos del sureste. La creación de un diagrama de Coeficientes de Semejanza Biogeográfica (CBR por sus siglas en inglés) ilustra que la herpetofauna de los altiplanos del noroeste y del nordeste, la de los altiplanos del nordeste y del sureste, y la de los altiplanos del sureste y del suroeste, están relacionadas...

Diversidad y estado de conservación de primates en las Sierras de Contamana, Amazonía peruana

Este trabajo contiene información del inventario, abundancia y estado de conservación de las especies de primates que habitan en los bosques de las Sierras de Contamana. Hemos registrado 87 grupos correspondientes a 11 especies. De ellas, Saguinus mystax Spix, Ateles chamek Humboldt, Cebus apella Linnaeus y Lagothrix poeppigii Schinz fueron las más avistadas con 14, 13, 13 y 11 grupos, respectivamente. El rango de variación del tamaño de grupo resultaron similares a los registrados para otras áreas, con excepción de A. chamek, cuyos grupos en la mayoría de los casos estuvieron compuestos por más de 16 individuos. En el área de estudio, las poblaciones más abundantes correspondieron al Cacajao calvus ucayalii Thomas (479 individuos/100 km), L. poeppigii (178,5 individuos/100 km) y A. chamek (148,2 individuos/100 km). los mayores avistamientos ocurrieron en los bosques de terraza alta (46%) y de colina baja (27%), constituyéndose así en los hábitats de mayor uso por los primates. Entre las especies registradas, C. calvus ucayalii y S. mystax aún no están protegidas en ninguna de las actuales áreas naturales protegidas del Perú.

This paper provides information on the diversity, abundance and conservation status of primates species that inhabit the forests of the Sierras de Contamana. We recorded 87 groups corresponding to 11 species. Saguinus mystax Spix, Ateles chamek Humboldt, Cebus apella Linnaeus and Lagothrix poeppigii Schinz were the most frequently sighted with 14, 13, 13 and 11 groups, respectively. The variation of group size was similar to those of groups in other areas, except for A. chamek whose groups in most of the cases consisted of more than 16 individuals. In the study area, highest population were observed for Cacajao calvus ucayalii Thomas (479 individuals / 100 km), L. poeppigii (178,5 individuos/100 km) and A. chamek (148,2 individuos/100 km). Most sightings occurred in high terrace forests (46%) and low hill forests (27%), constituting the habitats most frequently used by primates. Among the recorded species, C. calvus ucayalii and S. mystax are not still protected in any of the current protected natural areas of Peru.