Editorial Type:
Article Category: Research Article
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Online Publication Date: 05 Jun 2020

Neutrophil: Lymphocyte Ratios as a Measure of Chronic Stress in Populations of the Hellbender (Cryptobranchus alleganiensis) across a Habitat Quality Gradient

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Page Range: 403 – 415
DOI: 10.1643/CP-19-265
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Amphibians are currently facing widespread population declines, primarily due to the introduction of anthropogenic stressors, which have the potential to alter ecosystem dynamics and elicit long-term physiological responses resulting in overall population declines. Population assessments typically rely upon genomics, demography, and geographic isolation; however, when physiological parameters are included, mechanistic explanations for population declines can be determined. Rapid population assessments that can be related to specific microhabitat characteristics for management purposes can be achieved by implementing a chronic stress proxy, such as neutrophil: lymphocyte (N:L) ratios. As a long-lived habitat specialist, facing dramatic population declines with state and federally protected populations, the Hellbender (Cryptobranchus alleganiensis) is a good candidate species for applying N:L ratios to assess population vulnerability and habitat quality. This study used N:L ratios as a proxy of chronic stress among Hellbender populations to determine environmental variables potentially correlated with chronic stress. Additionally, comparisons of N:L ratios were made among Hellbender populations to examine applicability of this method for assessing among-population differences. Of the microhabitat variables assessed, high conductivity, low pH, and low dissolved oxygen correlated with elevated N:L ratios. In addition, N:L ratios differed significantly among Hellbender populations, which suggests the utility of N:L ratios as an indicator of population-level differences. Specifically, where traditional methods lack the ability to detect concerns, physiological assessment suggested certain populations may be of concern in regard to experiencing chronic stress. Including physiological parameters in viability and vulnerability assessments more frequently, such as the one described here, can provide evidence of population concerns earlier than traditional methods, and allow for better management strategy by elucidating specific environmental variables contributing to stress.

Copyright: © 2020 by the American Society of Ichthyologists and Herpetologists
Fig. 1.
Fig. 1.

Map of eight sites surveyed between 2017 and 2018 for Hellbenders, including North Fork Triplett Creek (NFTC) in Kentucky, Little Buffalo River (LBR), Hiwassee River (HR), Little River (LR), Doe River (DR), Tumbling Creek (TC), and Elk River (ER) in Tennessee, and South Fork New River (SFNR) in North Carolina.


Fig. 2.
Fig. 2.

Scatterplots showing multiple linear regression comparing Hellbender neutrophil: lymphocyte ratio and water characteristics for 2017. The first row of graphs depicts neutrophil: lymphocyte ratio on the y-axis and corresponding environmental variables on the x-axis; all other rows depict the relationship among water quality parameters assessed. R2 values are provided for each graph, the red line represents the overall trend line, and significant variables are indicated with an asterisk.


Fig. 3.
Fig. 3.

Scatterplots showing regressions between Hellbender neutrophil: lymphocyte ratios and conductivity (A), pH (B), and dissolved oxygen (C), in 2017.


Fig. 4.
Fig. 4.

Scatterplots showing multiple linear regression comparing Hellbender neutrophil: lymphocyte ratio and water characteristics for 2018. The first row of graphs depicts neutrophil: lymphocyte ratio on the y-axis and corresponding environmental variables on the x-axis; all other rows depict the relationship among water quality parameters assessed. R2 values are provided for each graph, the red line represents the overall trend line, and significant variables are indicated with an asterisk.


Fig. 5.
Fig. 5.

Scatterplot showing regression between Hellbender neutrophil: lymphocyte ratio and water pH observed in 2018.


Fig. 6.
Fig. 6.

Hellbender neutrophil: lymphocyte ratio in 2017 at Little River (LR; n = 4), Tumbling Creek (TC; n = 9), Hiwassee River (HR; n = 6), Little Buffalo River (LBR; n = 2), and Doe River (DR; n = 1). Letters indicate among-site differences, where sites that are significantly different have different letters, and error bars represent two standard deviations from the mean.


Fig. 7.
Fig. 7.

Hellbender neutrophil: lymphocyte ratio across 2017 and 2018 at Little River (LR; n = 8), Tumbling Creek (TC; n = 12), Hiwassee River (HR; n = 11), Elk River (ER; n = 3), North Fork Triplett Creek (NFTC; n = 4), Little Buffalo River (LBR; n = 4), Doe River (DR; n = 1), and South Fork New River (SFNR; n = 5). Letters indicate among-site differences, where sites that are significantly different have different letters, and error bars represent two standard deviations from the mean.


Contributor Notes

Department of Biology, University of Arkansas, SCEN 601, 850 W. Dickson Street, Fayetteville, Arkansas 72701; Email: arlitmer@uark.edu. Send reprint requests to this address.
Department of Natural Sciences and Mathematics, Lee University, 1120 N. Ocoee Street, Cleveland, Tennessee 37311; Email: mfreake@leeuniversity.edu.
Department of Biology, Tennessee Technological University, Pennebaker Hall #207, 1100 N. Dixie Avenue, Cookeville, Tennessee 38505.
Department of Biology, Southeastern Louisiana University, 500 W. University Avenue, Hammond, Louisiana 70402; Email: cmurray@selu.edu.

Associate Editor: C. Bevier.

Received: 10 Jul 2019
Accepted: 13 Mar 2020
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