| Issue |
Knowl. Manag. Aquat. Ecosyst.
Number 427, 2026
Freshwater ecosystems management strategies
|
|
|---|---|---|
| Article Number | 5 | |
| Number of page(s) | 15 | |
| DOI | https://doi.org/10.1051/kmae/2026001 | |
| Published online | 02 February 2026 | |
Research Paper
Application, development and opportunities of Remote Underwater Video for freshwater fisheries management
1
Water@Leeds, School of Biology, Faculty of Biological Sciences, Leeds, LS2 9JT, UK
2
South African Institute for Aquatic Biodiversity (SAIAB), Makhanda 6139, South Africa
3
South African National Biodiversity Institute, Cape Town, South Africa
4
School for Climate Studies, Stellenbosch University, Stellenbosch, South Africa
5
Ecosystems and Ocean Sciences, Pacific Region, Fisheries and Oceans Canada, Sidney, BC V8L 4B2, Canada
6
School of Life Science, University of Wollongong, Wollongong, NSW 2522, Australia
7
APEM Limited, International House, International Business Park, Southampton SO18 2RZ, UK
8
Department of Zoology and Entomology, Rhodes University, Makhanda, 6139, South Africa
9
Department of Ichthyology and Fisheries Science, Rhodes University, Makhanda, 6139, South Africa
* Corresponding author: This email address is being protected from spambots. You need JavaScript enabled to view it.
; This email address is being protected from spambots. You need JavaScript enabled to view it.
Received:
3
November
2025
Accepted:
3
January
2026
Remote Underwater Video (RUV) is a promising tool for progressing the future of freshwater fisheries monitoring and management. While uses have previously been focused on marine systems there has been a rise in application for freshwaters. Given the potential for coordinated geographical research using RUVs it is essential that standardised methodologies are described and promoted. We therefore conducted a systematic literature review which returned 185 publications that discussed using RUVs in freshwater environments. These publications used RUVs to measure: abundance, species richness, length-frequency, spawning/mating, behaviour, migration, foraging, size, habitat use, species presence and nesting. There were taxonomic and geographic biases in the results, with commercial salmonid fisheries the primary focus and 49% of published research was performed in North and Central America. While some research has investigated best practices, there are numerous gaps including: determining optimal deployment time in different systems/species compositions, determining suitable acclimation time for behavioural analysis and ascertaining the costs and benefits of using bait as an attractant and stereo-camera for photogrammetry. Until these gaps are addressed, we recommend a cautious set of standards for freshwater RUVs deployment which includes using a standard action camera, recording at ≥30 fps with a resolution of 1080p for 60 minutes. This will ensure that data are broadly comparable between studies. Current bottlenecks in methodology uptake relate to data storage, processing time and cost but this may be overcome with the optimisation of computer vision and machine learning. There are broad opportunities to develop RUV application into a powerful tool for freshwater fisheries management, invasive species detection, and ethological observations if standardised and findability, accessibility, interoperability, and reusability (FAIR) workflows are followed.
Key words: RUV / novel tools / biodiversity monitoring / baited remote underwater video / method standardisation / ethology
© M. Harwood et al., Published by EDP Sciences 2026
This is an Open Access article distributed under the terms of the Creative Commons Attribution License CC-BY-ND (https://creativecommons.org/licenses/by-nd/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited. If you remix, transform, or build upon the material, you may not distribute the modified material.
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