This function calculates the Fishing-in-Balance (FiB) Index of fisheries landings for \(j\) areas and \(i\) years.
fishingInBalance(land, TL.table, minTL = 0, TE = 0.1, base.start,
base.end, years)
A dataframe of commercial landings data with columns YEAR
,
ID
, SPECIES
and CATCH
. YEAR
indicates the year
the landing was recorded, ID
is an area code indicating where the
landing was recorded, SPECIES
is a numeric code indicating the
species landed, and CATCH
is the corresponding landed weight.
A dataframe with columns SPECIES
and the corresponding
TL_LAND
(trophic level). Entries in the SPECIES
column should
be the unique values of species codes in land
(or a subset thereof).
Other columns in TL.table
are ignored.
The minimum trophic level of species to include. Default is
minTL = 0
.
Trophic efficiency. Default is TE = 0.1
, i.e., a trophic
efficiency of 10%.
Year indicating the beginning of the baseline period. The
average landings and average mean trophic level of the landings over the
baseline period are used as baseline values to calculate FiB (see Details).
land
must include data for the baseline period.
Year indicating the end of the baseline period. The average
landings and average mean trophic level of the landings over the baseline
period are used as baseline values to calculate FiB (see Details).
land
must include data for the baseline period.
A vector of years for which to calculate indicator.
Returns a dataframe with three columns: ID
, YEAR
, and
FishinginBalance
.
If there are no observations in land for spatial scale \(j\) and year
\(i\), indicator value is set to NA
.
Fishing-in-Balance (FiB) Index: $$FiB = log(Y_k*(1/TE)^{TL_k}) - log(Y_0 * (1/TE)^{TL_0})$$ where \(Y\) is the catch, \(TL\) is the mean trophic level in the catch, \(TE\) is the transfer efficiency, \(k\) is any year, and 0 refers to any year used as a baseline. By default, \(TE\) is set to 0.10 (Pauly and Christensen 1995).
This indicator captures changes in fishing strategies and their impact on system productivity: a positive FiB index indicates that the fishery has expanded and/or bottom-up effects are occurring, and there is more catch than expected, while a negative FiB index indicates it is likely that the fishing impact is so high that the ecosystem function is impaired and the ecosystem is less productive owing to excessive fishery removals (Pauly et al., 2000).
Bundy A, Gomez C, Cook AM. 2017. Guidance framework for the selection and evaluation of ecological indicators. Can. Tech. Rep. Fish. Aquat. Sci. 3232: xii + 212 p.
Pauly D, Christensen V, Walters C. 2000. Ecopath, Ecosim, and Ecospace as tools for evaluating ecosystem impact of fisheries. ICES J Mar Sci 57:697 706
Other resource potential indicators: allPotential
,
resourcePotential
# NOT RUN {
data(land)
data(species.info)
fishingInBalance(land, TL.table = species.info, minTL = 0, TE = 0.1,
base.start = 2014, base.end = 2015, years = c(2014:2019))
# }
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