3. Age Structured Models Flashcards
What is the Beverton-Holt Model?
- Widely used
* Widely used in evaluation of fish populations
* Helps to predict the number of new individuals (recruits) that will join the population, based on the number of parent fish (spawners)
* Particulary useful in regions such as North Atlantic, where many important fish species spawn once a year and then die, making the model a good fit for these life cycles - Follow each year class from recruitment to virtual disappearance
* “year class” is a group of fish spawned in the same year.
* The model allos us to track number of surviving individuals in each year class
* Provides valuable insight into the survival and mortality rates at different ages, who are key factors in managing the sustainability of the fish population. - Annual catch = catch from all year classes in the population
* The number of fish caught per year includes fish caught from every year classes in the population.
* Reflect that commercial fishing target a range of ages (both young and old) - Discrete time (year, month, quarter), but continuous time mortality, originally continuous-time growth (now usually age-specificc)
a) Discrete time:
Time is divided into distinct, separate intervals or units. This might be a year, month or quarter. For instance, certain type of fish spawns once a year during the spring
b) Continuous time:
Time is not divided into separate intervals, but flows continuously. For example, growth and mortality (death), which can occur at any time and aren’t necessarily time specific.
Give an intuitive explanation of the Beverton-Holt equation
- No*e^-(F+M): Number of fish that survive at years end
- No-N0*e^-(F+M): Fish that died during that year
- F/(F+M): Fraction that died because of fishing
Beverton-Holt Model: Can fishing mortality be > 1?
Yes
No*e^-1 = 0.367879
With instantaneous mortality = 1 over one year there would still be 37% of the fish left!
Beverton-Holt Model: How high F would it take to catch all the fish before the year is over?
Would need a very big F.
See Document!
Beverton-Holt Model: How do you get catch in weight?
Multiply by weight at age
Not quite correct, because fish grow over time, and the higher F the earlier they are fished and the lower is the average weight
As fish grow over time, the size that fish reach before being caught will depend on the intensity of fishing. If the fishing mortality rate (F) is high, fish are more likely to be caught at a younger age, when they are smaller. This leads to a lower average weight of fish in the catch compared to a situation where fishing mortality is low and fish have time to grow to a larger size before they are caught.
So, while you can estimate the total catch in weight by multiplying the number of fish caught at each age by their average weight at that age, this estimate won’t be accurate if it doesn’t account for the effect of fishing mortality on the average weight of the fish. This effect is due to the fact that high fishing pressure tends to skew the age structure of the population towards younger, smaller fish.
Beverton-Holt Model: Annual Catch
Sum of catch from all year classes in a
population
[SEE DOCUMENT FOR FORMULA]
h* = age of recruitment to the population
h** = oldest surviving year class
s = selection parameter
N0,h: determined by previous life history
F = fising mortality, assumed constant over
the period
M = natural mortality, assumed constant (mostly)
Basic idea of Beverton-Holt
The basic idea is that there’s a relationship between the number of adult fish (the “stock”) and the number of baby fish, or “recruits,” that are added to the population each year. This relationship is influenced by the environment, predation, disease, and other factors.
Beverton: Density Dependence:
The model assumes that when the adult population is low, there is less competition for resources, so a higher proportion of the baby fish survive. However, as the adult population gets larger, competition increases and a smaller proportion of the baby fish survive. This is a concept known as “density dependence.”
Beverton: Assumptions
The Beverton-Holt model assumes that the environment is stable and that the rate of survival of the baby fish is solely determined by the number of adult fish.
Q: What is age-structured models?
These models are used to study the dynamics of fish populations considering the age structure of the population. These models are crucial in understanding fish population dynamics and informing sustainable fishing practices. This is because fish at different ages or stages have different survival rates, reproductive rates, and are differently affected by fishing.
Q: What is the Beverton-Holt model?
The Beverton-Holt model is a type of recruitment model that describes the relationship between the spawning stock biomass (adult population size) and the recruitment (new additions to the population). The equation is as follows:
R=aS/(1+S/K)
- R represents recruitment, the number of new individuals added to the population.
- S represents the spawning stock biomass, the total weight of sexually mature fish in the population.
- a, K are parameters of the model, usually determined by fitting the model to empirical data.
The key feature of the Beverton-Holt model is that it assumes density-dependent survival, which means that as the number of adult fish increases, each individual offspring has a lower probability of survival. This model results in an asymptotic relationship between spawning stock and recruitment, where increasing the spawning stock beyond a certain point does not result in a substantial increase in recruitment.
Q: What is the Ricker Model?
The Ricker model is another widely used model in fishery science. It includes a term for density-dependent mortality, which can cause populations to exhibit fluctuations or even chaotic dynamics under certain conditions. The equation is as follows:
R=aSexp(-bS)
- R is the recruitment,
- S is the spawning stock,
- a, b are parameters of the model, usually determined by fitting the model to empirical data.
In the Ricker model, recruitment initially increases with spawning stock size but eventually decreases when the spawning stock size gets too large. This is because the model assumes that as the population grows, the resources per individual decrease leading to a decline in survival and hence recruitment. This leads to an inverted-U shaped curve, unlike the Beverton-Holt model.
Q: Importance of age-structured models in Fisheries Management?
Important as they allow us to understand how different levels of fishing pressure might affect the population in the long term. They can be used to estimate the maximum sustainable yield (MSY), the largest yield (or catch) that can be taken from a species’ stock over an indefinite period under constant environmental conditions.
Fishery scientists and managers can use these models to predict how changes in fishing mortality, fishing gear, or fishing methods might affect the yield and the age structure of the population. They can also be used to understand how measures such as fish quotas or limiting the number of fishing days could affect the population.
Remember that these models are simplifications of complex biological systems, and the real-world behavior of fish populations may be influenced by many other factors not included in these models (e.g., environmental variability, interactions with other species, changes in growth rates or natural mortality rates, etc.)
Q: What is the difference between the Beverton-Holt model and the Ricker model?
- Both describe the relationship between the spawning stock biomass and the recruitment (i.e., the addition of new young fish to the population).
- However, they make different assumptions about how population dynamics work, leading to different predicted relationships between spawning stock size and recruitment.
Beverton-Holt Model:
This model assumes density-dependent survival. As the number of adult fish increases, each individual offspring has a lower probability of survival. This is often due to increased competition for resources. As a result, the model predicts that recruitment will increase with spawning stock size, but at a decreasing rate. Beyond a certain point, increasing the spawning stock size doesn’t lead to much increase in recruitment. The relationship between spawning stock size and recruitment is asymptotic (i.e., it approaches but never reaches a limit).
The equation for the Beverton-Holt model is: R = aS / (1 + S/K)
Here, R is recruitment, S is the spawning stock, and a and K are parameters.
Ricker Model:
This model includes density-dependent mortality. This model assumes that at low population sizes, recruitment will increase with spawning stock size. However, when the population gets too large, resources per individual decrease and survival rates decline, causing recruitment to decrease. This leads to an inverted-U shaped relationship between spawning stock size and recruitment, which can even lead to population fluctuations or chaotic dynamics under certain conditions.
The equation for the Ricker model is: R = aS * exp(-bS)
Here, R is recruitment, S is the spawning stock, and a and b are parameters.
In summary, the main difference between the two models lies in their assumptions about how spawning stock size affects recruitment. The Beverton-Holt model predicts an asymptotic relationship, where recruitment plateaus at high spawning stock sizes, while the Ricker model predicts an inverted-U shaped relationship, where recruitment can decline at high spawning stock sizes due to density-dependent mortality.
Explain how age-structured models are used in fisheries management and discuss their limitations.
Age-structured models are used in fisheries management to predict the behavior of fish populations over time, considering both biological factors (e.g., growth, mortality, and reproduction) and human factors (e.g., fishing pressure). These models account for differences in fish survival, growth, and reproduction at different ages, providing a nuanced understanding of population dynamics. However, they have limitations, including reliance on several simplifying assumptions (e.g., constant natural mortality rate, no age errors), dependency on accurate data which is often hard to get, and inability to fully account for environmental variability or human behavior changes. Age-structured models also typically ignore spatial structure, potentially leading to misleading conclusions about stock status and optimal harvest levels.