Editorial Type:
Article Category: Research Article
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Online Publication Date: 18 Dec 2024

Effect of Turbidity on Survival and Growth of Juvenile Devils River Minnow (Dionda diaboli) Fed Chironomid Larvae

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Page Range: 659 – 671
DOI: 10.1643/i2023049
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The Devils River Minnow (Dionda diaboli) is a federally endangered species endemic to spring-fed tributaries of the Rio Grande drainage of Mexico and western Texas. Its occurrence in spring-fed stream habitats suggests that increased turbidity could negatively affect its survival in the wild. We used a laboratory experiment to assess the effect of turbidity (0 NTU: control; 10 NTU: low; 50 NTU: moderate; and 100 NTU: high) on time to initiate foraging, feed conversion ratio (FCR), specific growth rate (SGR), and condition coefficient for juvenile D. diaboli fed on a diet of chironomids, a pollution-tolerant invertebrate. Our results showed that increased turbidity significantly affected time to initiate foraging, but not the amount of food consumed, growth, body condition, and survival. Thus, although short-term exposure to turbidity conditions negatively affected feeding behavior, the treatments were not sufficient to cause significant differences in physiological performance and growth, suggesting D. diaboli may be resistant to short-term pulse increases in turbidity in its natural habitat. In this study, D. diaboli fed on chironomids had low average juvenile survivorship (27%) by the end of 12 weeks, with decreased growth and weight beginning by week 4 and 6, respectively. Thus, although increased turbidity did not directly affect D. diaboli, if elevated turbidity causes alteration of food resources toward pollution-tolerant macroinvertebrates, the species could be negatively affected. These results provide important information on the impacts of turbidity on the long-term conservation of D. diaboli, though further studies are needed to examine the species response to combined impacts of turbidity, droughts, non-native species invasions, and altered habitat.

Copyright: © 2024 by the American Society of Ichthyologists and Herpetologists
Fig. 1.
Fig. 1.

Boxplot showing measured turbidity levels for each turbidity treatment (n = 84 in each case). Values connected by the same letters are not significantly different (Tukey HSD test).


Fig. 2.
Fig. 2.

Boxplot showing time to initiate foraging (s) over time for the four treatments (n = 3 in each case). Values connected by the same letters are not significantly different (Tukey HSD test).


Fig. 3.
Fig. 3.

Line graph showing (A) mean length, (B) mean weight, and (C) mean fish number per aquarium over time for the four turbidity treatments (n = 3 in each case). Error bars are omitted for clarity.


Fig. 4.
Fig. 4.

Histograms showing lengths of fish at 0 weeks for the various treatments.


Fig. 5.
Fig. 5.

Histograms showing lengths of individual fish at 12 weeks for the various treatments.


Fig. 6.
Fig. 6.

Histograms showing weights of dead fish for various treatments throughout the experimental period.


Received: 03 Jul 2023
Accepted: 18 Nov 2024
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