Traditional fisheries advice - data flow chart

Catch Lengths Ages CPUE/Survey Indices Catch at age Assessment Prediction
#FIG 3.2
Landscape
Center
Inches
Letter  
100.00
Single
-2
1200 2
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 2175 3675 2175 2700 225 2700 225 3675 2175 3675
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 5475 5700 5475 4725 3525 4725 3525 5700 5475 5700
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 8400 7350 8400 6375 6450 6375 6450 7350 8400 7350
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 11325 7350 11325 6375 9375 6375 9375 7350 11325 7350
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 2175 5025 2175 4050 225 4050 225 5025 2175 5025
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 2175 6525 2175 5550 225 5550 225 6525 2175 6525
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 2175 8025 2175 7050 225 7050 225 8025 2175 8025
2 1 0 3 0 7 50 -1 -1 0.000 0 0 -1 1 0 2
	1 1 3.00 180.00 360.00
	 2175 3225 3525 5175
2 1 0 3 0 7 50 -1 -1 0.000 0 0 -1 1 0 2
	1 1 3.00 180.00 360.00
	 2175 4650 3525 5250
2 1 0 3 0 7 50 -1 -1 0.000 0 0 -1 1 0 2
	1 1 3.00 180.00 360.00
	 2175 6075 3525 5325
2 1 0 3 0 7 50 -1 -1 0.000 0 0 -1 1 0 2
	1 1 3.00 180.00 360.00
	 2175 7575 3375 7575
2 1 0 3 0 7 50 -1 -1 0.000 0 0 -1 1 0 2
	1 1 3.00 180.00 360.00
	 5475 7425 6450 6900
2 1 0 3 0 7 50 -1 -1 0.000 0 0 -1 1 0 2
	1 1 3.00 180.00 360.00
	 5475 5250 6450 6675
2 1 0 3 0 7 50 -1 -1 0.000 0 0 -1 1 0 2
	1 1 3.00 180.00 360.00
	 8400 6825 9375 6825
2 4 0 1 0 7 50 -1 -1 0.000 0 0 7 0 0 5
	 5325 8100 5325 7125 3375 7125 3375 8100 5325 8100
4 0 0 50 -1 0 18 0.0000 4 195 660 375 3150 Catch\001
4 0 0 50 -1 0 18 0.0000 4 255 900 300 4500 Lengths\001
4 0 0 50 -1 0 18 0.0000 4 255 570 375 6000 Ages\001
4 0 0 50 -1 0 18 0.0000 4 255 1530 375 7575 CPUE/Survey\001
4 0 0 50 -1 0 18 0.0000 4 195 795 3675 7575 Indices\001
4 0 0 50 -1 0 18 0.0000 4 255 1350 3600 5175 Catch at age\001
4 0 0 50 -1 0 18 0.0000 4 195 1350 6600 6825 Assessment\001
4 0 0 50 -1 0 18 0.0000 4 195 1155 9525 6825 Prediction\001
Traditional data flow chart of fisheries data. One or more data boxes may be missing.
Explanation
The traditional flow of information and data when an annual assessment is
conducted using high-quality data sets can be presented in a flow diagram.

%SPLITSLIDE
Measurements to be undertaken and data to be collected relates to how
this flow diagram is constructed. As seen from the diagram, the following
basic data is typically collected each year:
\begin{itemize}
\item
Catch statistics
\item
Length distributions
\item
Age determination
\item
Weights
\item
Surveys
\item
Other measurements
\end{itemize}


Details
The approaches to fish stock assessments vary considerably depending on data availability and the purpose behind the assessment. In the straight-forward case of annual assessments with annually collected age readings of high quality, the process is as follows:\\

Each year, data is collected by estimating the amount landed, along with biological sampling from the fishery and surveys. \\

Traditionally, the biological samples from the fisheries are used to compute the catches in numbers at age (along with various other important indicators such as mean weight at age).\\

The survey (or catch per unit effort from the fleet) data provides information on the relative stock status, in the form of indices of abundance. Similarly, underwater visual surveys provide indices of abundance which can in principle be used to monitor trends in abundance.\\
 
Acoustic measurements and sighting surveys (counts) of whales are of a different nature from the most common (indirect) measurements of marine animals when used as absolute abundance measures. Such direct measurements, which in principle provide absolute counts rather then indices, will not be covered in any detail, but they can also be used as indices, i.e. in the same manner as any other survey data.\\
 
The same applies to tag-return data. Such data can be extremely important, but have mainly been used to obtain information on migration between regions.\\

Many of the above monitoring methods are commonly scaled up to give an absolute measure of abundance. Thus, in principle one can scale results from an underwater visual survey to obtain an estimate of total abundance. It will be seen, however, that this is a very dangerous procedure and will almost never be recommended.\\

Most commonly the assessment process consists of annual data collection followed by data summaries for each annual data set. The data summaries are subsequently used with mathematical models of the population dynamics to estimate the state of the stock and provide advice on its utilization.\\

In many formal statistical assessment models the procedure commonly deviates a bit from the above in that the data tend to be used in less of a summary form. Thus, length distributions are typically only used in simple summary form, not raised to the catches. Each such data set is simply used as a different piece of information in a so-called likelihood function.