Serosurvey of free-ranging Amur tigers in the Russian Far East.

Wild Amur tigers (Panthera tigris altaica, n=44) from the Russian Far East were tested for antibodies to feline leukemia virus, feline corona virus (FCoV), feline immunodeficiency virus, feline parvovirus (FPV), canine distemper virus (CDV), Toxoplasma gondii, and Bartonella henselae. Antibodies to FCoV, CDV, FPV, and T. gondii were detected in 43, 15, 68, and 42% of tigers, respectively. No differences were detected in antibody prevalence estimates between tigers captured as part of a research program and those captured to mitigate human-tiger conflicts. Domestic dogs (Canis familiaris) were tested as a potential source for CDV; 16% were vaccinated against CDV and 58% of unvaccinated dogs were antibody positive for CDV. A high percentage of tigers were exposed to potential pathogens that could affect the survival of this species. We recommend continued monitoring of wild tigers throughout Asia, development of standardized sampling and postmortem examination procedures, and additional research to better understand potential domestic and wild animal sources for these pathogens.

Factors associated with pathogen seroprevalence and infection in Rocky Mountain cougars.

Serological and genetic material collected over 15 years (1990-2004) from 207 cougars (Puma concolor) in four populations in the Rocky Mountains were examined for evidence of current or prior exposure to feline immunodeficiency virus (FIV), feline parvovirus (FPV), feline coronavirus (FCoV), feline calicivirus (FCV), canine distemper virus (CDV), feline herpesvirus (FHV), and Yersinia pestis. Serologic data were analyzed for annual variation in seroconversions to assess whether these pathogens are epidemic or endemic in cougars, and to determine whether family membership, age, sex, or location influence risk of exposure. FIV and FPV were clearly endemic in the studied populations, whereas exposure to FCoV, FCV, CDV, and Y. pestis was more sporadic. No evidence was found for FHV. Age was the most consistent predictor of increased exposure risk, often with no other important factors emerging. Evidence for transmission within family groups was limited to FIV and FCoV, whereas some indication for host sex affecting exposure probability was found for FIV and Y. pestis. Overall, cougar populations exhibited few differences in terms of pathogen presence and prevalence, suggesting the presence of similar risk factors throughout the study region.

Effects of Roads and Human Disturbance on Amur Tigers.

Understanding the effects of human disturbance on endangered wildlife populations is critical to their conservation. We examined the effects of roads and human disturbance on the survivorship and foraging efficiency of Amur tigers ( Panthera tigris altaica) on and near Sikhote-Alin State Biosphere Zapovednik, Primorye Krai ( province), Russia. To evaluate the effects of roads, we estimated survivorship of radiocollared tigers and their cubs living in three types of areas: (1) areas with primary roads, (2) areas containing secondary roads, and (3) areas with minimal or no road access. We classified a tiger into one of these three treatments based on which types of roads bisected their 50% minimum convex polygon home ranges. Over a 9-year period (1991-2000), adult female survival was greatest (χ 2 = 12.2, df = 2, p = 0.002) for radiocollared tigers in roadless areas. All adult female tigers in roadless areas survived their tenure in those locations (n = 2), whereas all died or disappeared prematurely from areas with primary roads (n = 6). Cub survival was lower in areas with primary and secondary roads than in roadless areas (χ 2 = 10.9, df = 1, p < 0.009). We evaluated the effects of human disturbance at kill sites by examining 86 kills made by 15 tigers determining whether human disturbance had occurred at the kill site, and examining prey carcasses after tigers left, to estimate the percent meat eaten and whether the tiger abandoned the kill following human disturbance. Tigers undisturbed at kills consumed more meat ( Z = 3.71, p = 0.0002) from each kill than disturbed tigers did. Undisturbed tigers also spent more time at each kill site than disturbed tigers did ( Z = 2.3; p = 0.02). Abandonment of kills occurred in 63% of 24 instances when tigers were disturbed by people. Because roads decrease the survivorship and reproductive success of tigers, we recommend that in habitats managed for tigers, construction of new roads should be prohibited wherever possible and access to secondary roads (e.g., logging roads) should be reduced or prevented wherever possible. Protected areas seem to cease functioning as source populations where road access exists, and unprotected areas-the majority of Amur tiger range-cannot sustain stable populations with the increasing threat of human access to tiger habitat.

RESUMEN: Entender los efectos de la perturbación humana sobre poblaciones de vida silvestre en peligro es crítico para su conservación. Examinamos los efectos de caminos y perturbación humana sobre la supervivencia y eficiencia de forrajeo de tigres Amur ( Panthera tigris altaica) en y cerca de Biosfera Estatal Zapovednik Sikhote-Alin, Primorye Krai ( provincia), Rusia. Para evaluar los efectos de los caminos, estimamos la supervivencia de tigres con radio-collares y sus crías en áreas de tres tipos: 1) áreas con caminos primarios, 2) áreas con caminos secundarios y 3) áreas con mínimo o sin acceso de caminos. Clasificamos un tigre en uno de estos tres tratamientos con base en cuales tipos de caminos dividen el 50 % mínimo del polígono convexo de sus rangos de hogar. En un período de 9 años (1991-2000), la supervivencia de hembras adultas fue mayor (χ 2 = 12.2, g.l. = 2, p = 0.002) en tigres con radio-collar en áreas sin caminos. Todas las hembras adultas en áreas sin caminos sobrevivieron su dominio en esas localidades (n = 2), mientras que todas murieron o desaparecieron prematuramente en las áreas con caminos primarios (n = 6). La supervivencia de crías fue menor en áreas con caminos primarios y secundarios que en áreas sin caminos (χ 2 = 10.9, g.l. = 1, p < 0.009). Evaluamos los efectos de la perturbación humana en sitios de depredación mediante el examen de 86 muertes causadas por 15 tigres, determinando si había ocurrido perturbación humana en el sitio, y mediante el examen de restos de las presas después de que se alejaron los tigres, para estimar el porcentaje de carne consumida y si el tigre abandonó su presa después de una perturbación humana. Los tigres no perturbados consumieron más carne ( Z = 3.71, p = 0.0002) de cada presa que los tigres perturbados. Tigres no perturbados pasaron más tiempo con su presa que tigres perturbados ( Z = 2.3, p = 0.02). El abandono de presas ocurrió en 63 % de 24 eventos cuando los tigres fueron perturbados por humanos. Debido a que los caminos reducen la supervivencia y el éxito reproductivo de los tigres, recomendamos que en los hábitats bajo manejo para tigres, se debe prohibir la construcción de caminos donde sea posible y se debe reducir o prevenir el acceso a caminos secundarios (e. g. caminos madereros) donde sea posible. Las áreas protegidas dejan de funcionar como poblaciones fuente donde existe acceso a caminos, y las áreas no protegidas ( la mayor parte del rango de tigre Amur) no pueden sostener poblaciones estables con la incremento en la amenaza del acceso humano al hábitat de los tigres.