Nocturnal Spotlight Surveys for Monitoring Scripps's Murrelets in At-Sea Congregations at Anacapa Island, California

Concealed nest sites, mostly inaccessible breeding habitats, and nocturnal colony visitation have long hindered studies of Scripps's Murrelets (Synthliboramphus scrippsi); but conspicuous and seasonally predictable at-sea congregations adjacent to nesting areas provide a valuable index for asse...

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Published inMonographs of the Western North American Naturalist Vol. 7; no. 1; pp. 306 - 320
Main Authors Whitworth, Darrell L, Carter, Harry R
Format Journal Article
LanguageEnglish
Published Provo Brigham Young University 2014
Monte L. Bean Life Science Museum, Brigham Young University
Western North American Naturalist
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Abstract Concealed nest sites, mostly inaccessible breeding habitats, and nocturnal colony visitation have long hindered studies of Scripps's Murrelets (Synthliboramphus scrippsi); but conspicuous and seasonally predictable at-sea congregations adjacent to nesting areas provide a valuable index for assessing murrelet colony size and population trends at all 12 breeding islands. We developed a boat-based nocturnal spotlight survey for counting murrelets in at-sea congregations at Anacapa Island, California. A high-intensity spotlight was used to count murrelets during standard surveys conducted on 2 parallel transects (1.9 km each) located 200 m (“inshore”) and 500 m (“offshore”) from shore. We conducted 130 standard surveys over 58 nights in 2001–2006. Difficulties estimating densities with strip transects and distance sampling led to use of raw counts as the best index for assessing population trends. Standard counts averaged 136 (SD 94) murrelets per survey (range 0–470). Strong correlations were noted among counts within nights, but consistent trends were not evident. We also noted a strong correlation between maximum counts on consecutive survey nights but much more variation in counts over the breeding season (annual CV range 27%–92%). Annual maximum counts occurred from 42 days before to 32 days after mean egg-laying dates. Round-island counts ranged from 29 to 564 murrelets during 12 surveys conducted along a 19.2-km transect circumnavigating Anacapa Island. Strong correlations between inshore and offshore standard counts and between standard and round-island counts indicated that major local shifts in distribution did not occur; instead, varying proportions of the murrelet population returned to the Anacapa Island congregation each night. Increases in standard counts from 2001 to 2006 and a positive correlation between standard counts and the annual number of clutches in monitored plots suggested an increase in the murrelet population after eradication of black rats (Rattus rattus) in 2002, but limited posteradication survey data were not sufficient to detect significant popu lation trends. Intensive surveys (minimum of 10 nights each year) over at least 3 consecutive years per decade are recommended to track the progress of the Scripps's Murrelet population and to validate rates of population growth observed in small nest plots on Anacapa Island.
AbstractList Concealed nest sites, mostly inaccessible breeding habitats, and nocturnal colony visitation have long hindered studies of Scripps's Murrelets (Synthliboramphus scrippsi); but conspicuous and seasonally predictable at-sea congregations adjacent to nesting areas provide a valuable index for assessing murrelet colony size and population trends at all 12 breeding islands. We developed a boat-based nocturnal spotlight survey for counting murrelets in at-sea congregations at Anacapa Island, California. A high-intensity spotlight was used to count murrelets during standard surveys conducted on 2 parallel transects (1.9 km each) located 200 m (“inshore”) and 500 m (“offshore”) from shore. We conducted 130 standard surveys over 58 nights in 2001–2006. Difficulties estimating densities with strip transects and distance sampling led to use of raw counts as the best index for assessing population trends. Standard counts averaged 136 (SD 94) murrelets per survey (range 0–470). Strong correlations were noted among counts within nights, but consistent trends were not evident. We also noted a strong correlation between maximum counts on consecutive survey nights but much more variation in counts over the breeding season (annual CV range 27%–92%). Annual maximum counts occurred from 42 days before to 32 days after mean egg-laying dates. Round-island counts ranged from 29 to 564 murrelets during 12 surveys conducted along a 19.2-km transect circumnavigating Anacapa Island. Strong correlations between inshore and offshore standard counts and between standard and round-island counts indicated that major local shifts in distribution did not occur; instead, varying proportions of the murrelet population returned to the Anacapa Island congregation each night. Increases in standard counts from 2001 to 2006 and a positive correlation between standard counts and the annual number of clutches in monitored plots suggested an increase in the murrelet population after eradication of black rats (Rattus rattus) in 2002, but limited posteradication survey data were not sufficient to detect significant popu lation trends. Intensive surveys (minimum of 10 nights each year) over at least 3 consecutive years per decade are recommended to track the progress of the Scripps's Murrelet population and to validate rates of population growth observed in small nest plots on Anacapa Island.
Concealed nest sites, mostly inaccessible breeding habitats, and nocturnal colony visitation have long hindered studies of Scripps's Murrelets (Synthliboramphus scrippsi); but conspicuous and seasonally predictable at-sea congregations adjacent to nesting areas provide a valuable index for assessing murrelet colony size and population trends at all 12 breeding islands. We developed a boat-based nocturnal spotlight survey for counting murrelets in at-sea congregations at Anacapa Island, California. A high-intensity spotlight was used to count murrelets during standard surveys conducted on 2 parallel transects (1.9 km each) located 200 m ("inshore") and 500 m ("offshore") from shore. We conducted 130 standard surveys over 58 nights in 2001–2006. Difficulties estimating densities with strip transects and distance sampling led to use of raw counts as the best index for assessing populations trends. Standard counts averaged 136 (SD 94) murrelets per survey (range 0–470). Strong correlations were noted among counts within nights, but consistent trends were not evident. We also noted a strong correlation between maximum counts on consecutive survey nights but much more variation in counts over the breeding season (annual CV range 27%–92%). Annual maximum counts occurred from 42 days before to 32 days after mean egg-laying dates. Round-island counts ranged from 29 to 564 murrelets during 12 surveys conducted along a 19.2-km transect circumnavigating Anacapa Island. Strong correlations between inshore and offshore standard counts and between standard and round-island counts indicated that major local shifts in distribution did not occur; instead, varying proportions of the murrelet population returned to the Anacapa Island congregation each night. Increases in standard counts from 2001 to 2006 and a positive correlation between standard counts and the annual number of clutches in monitored plots suggested an increase in the murrelet population after eradication of black rats (Rattus rattus) in 2002, but limited posteradication survey data were not sufficient to detect significant population trends. Intensive surveys (minimum of 10 nights each year) over at least 3 consecutive years per decade are recommended to track the progress of the Scripps's Murrelet population and to validate rates of population growth observed in small nest plots on Anacapa Island. Durante mucho tiempo, los sitios de anidación ocultos, hábitats donde la reproducción es difícil y las visitas nocturnas a las colonias han obstaculizado los estudios sobre las aves de la especie Synthliboramphus scrippsi, pero las congregaciones conspicuas y estacionalmente predecibles en el mar, adyacentes a las áreas de anidación, constituyen un valioso parámetro para analizar el tamaño de la colonia y las tendencias de la población en 12 islas de reproducción. Realizamos conteos nocturnos desde embarcaciones de los individuos en congregaciones que se sitúan en el mar, en la Isla Anacapa, California. Utilizamos una luz de alta intensidad para hacer el muestreo durante los conteos "estándar" que realizamos en dos áreas transversales paralelas (1.9 km cada una) ubicadas a 200 m ("cerca de la costa") y 500 m ("en el agua") de la costa. Llevamos a cabo 130 conteos estándar durante 58 noches entre el año 2001 y el año 2006. Debido a que era difícil realizar estimaciones de las muestras a distancia y de la densidad del Método de transecto de banda, utilizamos el conteo en crudo como el mejor parámetro para analizar las tendencias de la población. Los conteos estándar promediaron 136 ± 94 aves por muestreo (rango = 0–470). Observamos una fuerte relación entre los conteos durante las noches, pero no detectamos tendencias significativas. Observamos una relación entre los conteos máximos durante las noches consecutivas que duró la investigación, sin embargo se registró una variación muy alta en los conteos correspondientes a la temporada de reproducción (Coeficiente de variación anual = 27%–92%). Los conteos máximos anuales se registraron desde 42 días antes hasta 32 días después de las fechas promedio en que las aves ponían los huevos. Los conteos en "toda la isla de reproducción" oscilaron entre 29 y 564 individuos durante 12 muestreos que se realizaron a lo largo de 19.2 km que circunnavega la Isla Anacapa. Las fuertes relaciones entre los conteos estándar cerca de la costa y en el agua, y entre los conteos estándar y en toda la isla de reproducción indicaron que no ocurrieron desplazamientos locales significativos en la distribución, sino que diferentes proporciones de la población aparentemente regresaban a la congregación de la Isla Anacapa cada noche. Los aumentos de los conteos estándar, entre los años 2001 y 2006, y la relación positiva entre los conteos estándar y la cantidad anual de puestas de huevos en terrenos monitoreados sugieren que se produjo un aumento en la población luego de la erradicación de ratas negras (Rattus rattus) en el año 2002; sin embargo, 6 años no fueron suficientes para detectar tendencias significativas en la población. Recomendamos realizar estudios intensivos (durante 10 noches cada año, como mínimo) durante por lo menos 3 años consecutivos por cada década para hacer el seguimiento del avance de la población de Synthliboramphus scrippsi y confirmar los índices de crecimiento poblacional que se observaron en pequeños terrenos con nidos en la Isla Anacapa.
Concealed nest sites, mostly inaccessible breeding habitats, and nocturnal colony visitation have long hindered studies of Scripps's Murrelets (Synthliboramphus scrippsi); but conspicuous and seasonally predictable at-sea congregations adjacent to nesting areas provide a valuable index for assessing murrelet colony size and population trends at all 12 breeding islands. We developed a boat-based nocturnal spotlight survey for counting murrelets in at-sea congregations at Anacapa Island, California. A high-intensity spotlight was used to count murrelets during standard surveys conducted on 2 parallel transects (1.9 km each) located 200 m ("inshore") and 500 m ("offshore") from shore. We conducted 130 standard surveys over 58 nights in 2001-2006. Difficulties estimating densities with strip transects and distance sampling led to use of raw counts as the best index for assessing population trends. Standard counts averaged 136 (SD 94) murrelets per survey (range 0-470). Strong correlations were noted among counts within nights, but consistent trends were not evident. We also noted a strong correlation between maximum counts on consecutive survey nights but much more variation in counts over the breeding season (annual CV range 27%-92%). Annual maximum counts occurred from 42 days before to 32 days after mean egg-laying dates. Round-island counts ranged from 29 to 564 murrelets during 12 surveys conducted along a 19.2-km transect circumnavigating Anacapa Island. Strong correlations between inshore and offshore standard counts and between standard and round-island counts indicated that major local shifts in distribution did not occur; instead, varying proportions of the murrelet population returned to the Anacapa Island congregation each night. Increases in standard counts from 2001 to 2006 and a positive correlation between standard counts and the annual number of clutches in monitored plots suggested an increase in the murrelet population after eradication of black rats (Rattus rattus) in 2002, but limited posteradication survey data were not sufficient to detect significant popul ation trends. Intensive surveys (minimum of 10 nights each year) over at least 3 consecutive years per decade are recommended to track the progress of the Scripps's Murrelet population and to validate rates of population growth observed in small nest plots on Anacapa Island.
Abstract_FL Durante mucho tiempo, los sitios de anidación ocultos, hábitats donde la reproducción es difícil y las visitas nocturnas a las colonias han obstaculizado los estudios sobre las aves de la especie Synthliboramphus scrippsi, pero las congregaciones conspicuas y estacionalmente predecibles en el mar, adyacentes a las áreas de anidación, constituyen un valioso parámetro para analizar el tamaño de la colonia y las tendencias de la población en 12 islas de reproducción. Realizamos conteos nocturnos desde embarcaciones de los individuos en congregaciones que se sitúan en el mar, en la Isla Anacapa, California. Utilizamos una luz de alta intensidad para hacer el muestreo durante los conteos “estándar” que realizamos en dos áreas transversales paralelas (1.9 km cada una) ubicadas a 200 m (“cerca de la costa”) y 500 m (“en el agua”) de la costa. Llevamos a cabo 130 conteos estándar durante 58 noches entre el año 2001 y el año 2006. Debido a que era difícil realizar estimaciones de las muestras a distancia y de la densidad del Método de transecto de banda, utilizamos el conteo en crudo como el mejor parámetro para analizar las tendencias de la población. Los conteos estándar promediaron 136 ± 94 aves por muestreo (rango = 0–470). Observamos una fuerte relación entre los conteos durante las noches, pero no detectamos tendencias significativas. Observamos una relación entre los conteos máximos durante las noches consecutivas que duró la investigación, sin embargo se registró una variación muy alta en los conteos correspondientes a la temporada de reproducción (Coeficiente de variación anual = 27%–92%). Los conteos máximos anuales se registraron desde 42 días antes hasta 32 días después de las fechas promedio en que las aves ponían los huevos. Los conteos en “toda la isla de reproducción” oscilaron entre 29 y 564 individuos durante 12 muestreos que se realizaron a lo largo de 19.2 km que circunnavega la Isla Anacapa. Las fuertes relaciones entre los conteos estándar cerca de la costa y en el agua, y entre los conteos estándar y en toda la isla de reproducción indicaron que no ocurrieron desplazamientos locales significativos en la distribución, sino que diferentes proporciones de la población aparentemente regresaban a la congregación de la Isla Anacapa cada noche. Los aumentos de los conteos estándar, entre los años 2001 y 2006, y la relación positiva entre los conteos estándar y la cantidad anual de puestas de huevos en terrenos monitoreados sugieren que se produjo un aumento en la población luego de la erradicación de ratas negras (Rattus rattus) en el año 2002; sin embargo, 6 años no fueron suficientes para detectar tendencias significativas en la población. Recomendamos realizar estudios intensivos (durante 10 noches cada año, como mínimo) durante por lo menos 3 años consecutivos por cada década para hacer el seguimiento del avance de la población de Synthliboramphus scrippsi y confirmar los índices de crecimiento poblacional que se observaron en pequeños terrenos con nidos en la Isla Anacapa.
Author Whitworth, Darrell L
Carter, Harry R
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Snippet Concealed nest sites, mostly inaccessible breeding habitats, and nocturnal colony visitation have long hindered studies of Scripps's Murrelets...
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StartPage 306
SubjectTerms Aerial locomotion
Animal populations
Birds
Breeding
Breeding of animals
Density estimation
Histograms
Islands
Ornithology
Population size
Population trends
Sea birds
Spotlights
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Title Nocturnal Spotlight Surveys for Monitoring Scripps's Murrelets in At-Sea Congregations at Anacapa Island, California
URI http://www.bioone.org/doi/abs/10.3398/042.007.0123
https://www.jstor.org/stable/24870239
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