Editorial Type:
Article Category: Research Article
 | 
Online Publication Date: 08 Nov 2021

Environmental Influences on the Larval Density and Age-Class Distribution of Ascaphus truei near the Northern Extent of Its Range

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Page Range: 1015 – 1025
DOI: 10.1643/h2020048
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Complex environmental factors influence the distribution of species within lotic systems. This is especially apparent for amphibian species that have a multi-year larval stage. Pre-metamorphic Coastal Tailed Frogs (Ascaphus truei) are found in fast-flowing headwater streams for up to four years. Although there is considerable opportunity for the spatial redistribution of larval frogs, there is relatively little known of the habitat ecology of the various growth stages. We compared the abundance of larvae near the northern extent of the species range to a collection of environmental factors hypothesized to influence population density. We also assessed spatial segregation at various developmental stages where relatively short summers and cool climates result in a long residence for larvae. The top ranked model for larvae abundance included covariates representing the wetted width and wetted depth of the stream. Capture rates decreased in a nonlinear fashion as wetted width increased, and rates increased in streams wider than 6 m. Capture rates nonlinearly increased when stream depth exceeded 20 cm. Older larvae were associated with greater slopes than younger larvae. Our results suggest little evidence for a relationship between elevation and cohort distribution. We recommend considering micro-scale influences on the presence and movement patterns of Coastal Tailed Frog larvae within streams.

Copyright: © 2021 by the American Society of Ichthyologists and Herpetologists
Fig. 1.
Fig. 1.

Locations of the 32 streams where larvae of A. truei were surveyed and captured between mid-June and mid-November, 2014, in northwestern British Columbia, Canada. Inset illustrates the global distribution of A. truei.


Fig. 2.
Fig. 2.

Box plots of percent cover categories for larvae of A. truei surveyed in northwestern British Columbia, Canada. The black line is the median, upper and lower limits of the box are the 75th and 25th percentiles, respectively, the whiskers extend up to 1.5 times the interquartile range, and outliers are represented as points.


Fig. 3.
Fig. 3.

Histogram showing the frequency of capture rates for larvae of A. truei surveyed in northwestern British Columbia, Canada.


Fig. 4.
Fig. 4.

Coefficients and 95% confidence intervals of the top-ranked negative binomial regression models (ΔAICc < 2.0) representing environmental influences on the capture rates for A. truei in northwestern British Columbia, Canada.


Fig. 5.
Fig. 5.

Model coefficients and 95% confidence intervals of the top-ranked logistic regression models (ΔAICc < 2.0) representing environmental influences on the distribution within streams of larvae of A. truei with visible limbs compared to no visible limbs in northwestern, British Columbia, Canada.


Contributor Notes

University of Northern British Columbia, Prince George, British Columbia, Canada V2N 4Z9; Email: (CMM) cmosher0@unbc.ca; (CJJ) johnsoch@unbc.ca; and (BWM) brent.murray@unbc.ca. Send reprint requests to CMM.
BC Ministry of Forests, Lands, Natural Resource Operations, and Rural Development, Nanaimo, British Columbia, Canada V9T 6E9; Email: Melissa.Todd@gov.bc.ca.

Associate Editor: J. Kerby.

Received: 31 Mar 2020
Accepted: 27 May 2021
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