Human history with fishing highlights its practices since primitive societies.
Discovery of shell and bone middens, artifacts supporting evidence of fishing and overfishing.
Development of efficient fishing techniques:
Better boats and giant factory ships
Improved nets and trawls
Integration of remote sensing technologies
Fisheries landings have dramatically increased since 1950 but have plateaued over time.
In 2006, predictions indicated a potential collapse of fish populations by 2048, but these figures have been revised.
Presently, 37% of fished species are still classified as overexploited.
Fish and shellfish provide 16% of global animal protein consumption.
The increase in fish catch has not kept pace with fishing effort due to declining populations.
A portion of the catch is dedicated to animal feed, with decreasing percentages allocated for aquaculture as plant-based feeds have become more viable.
Fish and shellfish are renewable resources, but even low fishing pressure can lead to population crashes and near extinction.
Effective management must set limits (quotas) and establish closures to recover fish populations.
Requires detailed knowledge of species' stock sizes, life histories, and ecological behaviors.
Fish species have broad geographic ranges, often divided into relatively independent stocks based on spawning and nursery grounds.
Stocks can become genetically isolated due to geographical and temporal differences (e.g., salmon).
Monitoring of stocks involves:
Tagging fish with plastic/metal tags for tracking.
Using genetic markers or enzyme polymorphisms for identification.
Estimating stock size and age structure is crucial for sustainable management, considering fish sizes that are typically harvested.
Assessment processes include:
Sampling programs accounting for migration and spatial distribution.
Recognizing that sampling gear can influence results (e.g., net sizes).
Most fishery data sources stem from landings, yet these data can be biased as fisheries often focus on areas with higher fish density.
Important factors affecting data include:
Number of fishing vessels.
Number of personnel involved.
Types of fishing gear used.
Duration of fishing activities.
To factor in variable fishing effort, landings are expressed as CPUE.
Metrics may be misleading if fish learn to avoid fishing boats or fishing efforts decline over time.
Managers need to estimate the potential yield (kg/year) while avoiding overexploitation.
Models must consider:
Reproduction rates.
Recruitment levels.
Growth rates across different life stages.
Managers establish limits to optimize sustainable yields over multiple years, preventing stock stress.
Fishers align their efforts with optimizing production, where intermediate stock sizes can foster greater growth rates.
Regulations, such as size limits on caught individuals, help maintain sustainable fisheries:
Catching larger fish leaves more resources for younger fish.
Gathering precise measurements of population sizes, growth rates, and reproductive rates poses significant challenges, leading to uncertainties in MSY models.
Management plans tend to be species-specific which can inadvertently impact other species (e.g. bottom trawling affects cod populations).
Societal demands often push for increased fishing efforts despite sustainability issues.
Overfishing occurs when fish are harvested faster than they can reproduce, leading to stock reductions.
Increased fishing pressures can disrupt trophic structures, exemplified by the decline of cod populations in Newfoundland.
Studies indicate substantial declines in apex predator populations due to overfishing.
The biomass of top carnivores is around 10% of what it was in the 1960s.
Planktivorous fish (e.g. anchovies, sardines, menhaden) play a crucial ecological role.
Menhaden fished extensively for fertilizer has seen declines in population numbers and sizes, affecting larger fish populations.
Restrictions have allowed for some recovery of menhaden populations.
Removing fish across various trophic levels, combined with ocean warming and pollution, has led to the dominance of certain 'junk' species.
Notable increases in jellyfish populations affect zooplankton, including fish eggs.
Different fishing methods utilize various gear types, affecting catch efficiency:
Hooking Methods: Longlines with thousands of hooks used for species like tuna.
Shoreline Nets: Nets that trap fishes along coastlines.
Gill Nets: Mesh nets catching fish by gills, often resulting in bycatch.
Seine Nets: Purse seines that encircle schools of fish can unintentionally capture marine mammals.
Trawling: Bottom and pelagic trawls capture fish but can cause significant ecosystem disruption.
Baited Traps: Use in specific fishing grounds to catch mobile crustaceans.
Bycatch refers to the incidental capture of non-target species, contributing to declines in their populations.
Devices like turtle exclusion devices aim to reduce bycatch from gill nets and longlines.
Drift nets have been banned due to excessive bycatch, impacting various marine animals.
Although efficient, bottom trawling is destructive to benthic ecosystems, leading to significant bycatch and long recovery times.
This method can deplete species that are prey for targeted species and harm various marine habitats.
Biol 3711 - Fisheries