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In This Article

  • Summary
  • Abstract
  • Introduction
  • Protocol
  • Representative Results
  • Discussion
  • Acknowledgements
  • Materials
  • References
  • Reprints and Permissions

Summary

This is a protocol to model the size spectrum (scaling relationship between individual mass and population density) for combined fish and invertebrate data from wadable streams and rivers. Methods include: field techniques to collect quantitative fish and invertebrate samples; lab methods to standardize the field data; and statistical data analysis.

Abstract

The size spectrum is an inverse, allometric scaling relationship between average body mass (M) and the density (D) of individuals within an ecological community or food web. Importantly, the size spectrum assumes that individual size, rather than species’ behavioral or life history characteristics, is the primary determinant of abundance within an ecosystem. Thus, unlike traditional allometric relationships that focus on species-level data (e.g., mean species’ body size vs. population density), size spectra analyses are ‘ataxic’ – individual specimens are identified only by their size, without consideration of taxonomic identity. Size spectra models are efficient representations of traditional, complex food webs and can be used in descriptive as well as predictive contexts (e.g., predicting responses of large consumers to changes in basal resources). Empirical studies from diverse aquatic ecosystems have also reported moderate to high levels of similarity in size spectra slopes, suggesting that common processes may regulate the abundances of small and large organisms in very different settings. This is a protocol to model the community-level size spectrum in wadable streams. The protocol consists of three main steps. First, collect quantitative benthic fish and invertebrate samples that can be used to estimate local densities. Second, standardize the fish and invertebrate data by converting all individuals to ataxic units (i.e., individuals identified by size, irrespective of taxonomic identity), and summing individuals within log2 size bins. Third, use linear regression to model the relationship between ataxic M and D estimates. Detailed instructions are provided herein to complete each of these steps, including custom software to facilitate D estimation and size spectra modeling.

Introduction

Body size scaling relationships, such as the positive association between body mass and metabolic rate, are well-known at the individual organism level and are now being studied at higher levels of organization1,2,3. These allometric relationships are most often power-law functions of the form Y = aMb, where Y is the variable of interest (e.g., metabolism, abundance, or home range size), M is the body mass of a single or average individual, b is a scaling coefficient, and a is a constant. For statistica....

Protocol

All methods described here have been approved by the Institutional Animal Care and Use Committee (IACUC) of Virginia Commonwealth University.

1. Collection and processing of fish samples

  1. Isolating fishes within the study reach to create a closed fish assemblage
    1. Identify the upstream and downstream (direction is relative to a surveyor facing ‘upstream’ and against the water current) ends of the study reach then mark the ends .......

Representative Results

Exemplar results, including original field data, are presented for Slaunch Fork, West Virginia, a small stream in southern West Virginia. Additional size spectra model results are also presented for two other streams in the same region: Camp Creek and Cabin Creek, West Virginia. These are the three study sites included in McGarvey and Kirk17, but data presented here are from new samples collected in May 2015. A fully worked, manual example of the size spectra modeling process is included for the S.......

Discussion

This ataxic size spectra protocol can be used to quantify and model size structure within communities of stream fishes and invertebrates. Previous size spectra studies in stream ecosystems have ranged from basic descriptive research39,40 to comparisons along a longitudinal river profile41 and among distinct biogeographic regions42. Seasonal comparisons have been performed43,

Acknowledgements

Funding for this work was provided by the National Science Foundation (grant DEB-1553111) and the Eppley Foundation for Scientific Research. This manuscript is VCU Rice Rivers Center contribution #89.

....

Materials

NameCompanyCatalog NumberComments
Chest wadersMultiple optionsn/aPersonal protective equipment for use during electrofishing. Do NOT use 'breatheable' waders as electrical current will pass through them.
Rubber lineman's glovesMultiple optionsn/aPersonal protective equipment for use during electrofishing.
Dip nets with fiberglass polesMultiple optionsn/aUsed to capture stunned fishes during electrofishing.
Backpack electrofishing unitSmith-Root; Halltech; Midwest Lake Management; Aqua Shock Solutionswww.smith-root.com; www.halltechaquatic.com; https://midwestlake.com; https://aquashocksolutions.com/Backpack electrofishers are currently manufactured and distributed by four independent companies in North America. Prices and warranty/technical support are the most important factors in choosing a vendor.
Block nets/seines (×2)Duluth Netshttps://duluthfishnets.com/Necessary length will depend on stream width. 3/8 inch mesh is recommended.
Cam-action utility straps with 1 inch nylon webbing (×4)Multiple optionsn/aUsed to secure/anchor block nets. Available at auto supply, hardware, and department stores.
Large tent stakes (×4)Multiple optionsn/aUsed to secure/anchor block nets. Available at camping and department stores.
5 gallon plastic buckets (×5)Multiple optionsn/aUsed to hold and transport fish during electrofishing. Available at hardware and paint supply stores.
10-20 gallon totes (×3)Multiple optionsn/aUsed as livewells, sedation tanks, and recovery bins for captured fishes. Available at hardware and department stores.
Battery powered 'bait bucket' aeration pumpsCabelasIK-019008Used to aerate fish holding bins during field processing.
Fish anesthesia (Tricaine-S)Syndelwww.syndel.comUsed to sedate fishes for field processing. Tricaine-S is regulated by the U.S. Food and Drug Administration.
Folding camp table and chairsCabelasIK-518976; IK-552777Used to process fish samples.
Pop-up canopyMultiple optionsn/aUsed as necessary for sun and rain protection.
Fish measuring boardWildco3-118-E40Used to measure fish lengths.
Battery powered field scale with weighing dishMultiple optionsn/aUsed to weigh fishes. Must weigh be accurate to 0.1 or 0.01 grams.
Clear plastic wind/rain baffleMultiple optionsn/aUsed to shield scale in rainy or windy conditions. Must be large enough to cover the scale and a weighing dish.
White plastic or enamel examination traysMultiple optionsn/aTrays are essential for examining fishes in the field.
Stainless steel forcepsMultiple optionsn/aForceps are helpful when examining small fishes and in transfering invertebrates to specimen jars.
Hand magnifiersMultiple optionsn/aMagnification is often helpful when identifying fish specimens in the field.
Fish identification keysn/an/aLaminated keys that are custom prepared for specific locations are most effective.
Datasheets printed on waterproof paperRite in the Rainn/aWaterproof paper is essential when working with aquatic specimens.
Retractable fiberglass field tapesLufkinn/aUsed to measure stream channel dimensions.
Surber sampler or Hess samplerWildco3-12-D56; 3-16-C52Either of these fixed-area benthic samplers will work well in shallow streams with gravel or pebble substrate.
70% ethanol or isopropyl alcoholMultiple optionsn/aUsed as invertebrate preservative.
Widemouth invertebrate specimen jars (20-32 oz.)U.S. Plastic Corp.67712Any widemouth plastic jars will work but these particular jars are durable and inexpensive.

References

  1. Peters, R. H. . The ecological implications of body size. , (1983).
  2. Brown, J. H., Gillooly, J. F., Allen, A. P., Savage, V. M., West, G. B. Toward a metabolic theory of ecology. Ecology. 85 (7), 1771-1789 (2004).
  3. Marquet, P. A., et al.

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