Shrimp fisheries
Shrimp fisheries data were derived from electronic logbooks
and
dealer records for the period 2014-2021. Landings and revenues are reported per trip and
were matched to multiple VMS fishing pings. Fishing pings were identified using speed
filters and logic rules. Dealer records provide trip-level landings. Landings and
revenues
for each electronic logbook ping were calculated by distributing trip-level values
uniformly
to each fishing ping, the most common method used in marine spatial planning (Chollett
et
al. 2022). Unmatched revenues and landings (corresponding to fishing activity carried
out
by vessels without transponders, or when transponders were off) were distributed evenly
among fishing pings for that year. All revenue data were reported in 2021 dollars using
the
implicit price deflator by the U.S. Bureau of Economic Analysis. Full information for
this
dataset can be found in Chollett & O’Farrell (2022). Shrimp fisheries data were
mapped
over a 10x10 km grid and over Coastal Fisheries statistical areas (Atkinson et al.
2021).
Reef fish
fisheries
Reef fish fisheries data are available from 2007 to 2021. In the GoM
reef fish are fished using multiple gears: bottom longline, handlines and bandit reels,
diving, buoys, gillnets, trolling, cast nets and traps. Only bottom longline, handlines
and
bandit reels have been mapped at high spatial resolution using Vessel Monitoring System
(VMS) data that have been linked to logbooks. Spatial information for the other
fisheries is
only available at the spatial scale of Coastal Fisheries statistical areas (Atkinson et
al.
2021), through self-reported fishing locations in logbooks.
Data for reef fish fisheries using bottom longlines, handlines and bandit reels were
mapped in the FIP using VMS positions that have been linked to logbook data to extract
landings and revenues. Fishing pings were identified using a supervised classification
method implemented in Random Forests (Breiman 2001). Landings and revenues are
reported per trip and were matched to multiple VMS fishing pings. Landings and revenues
for each VMS ping were calculated by distributing trip-level values uniformly to each
fishing ping. Unmatched revenues and landings were distributed evenly among fishing
pings for that year. All revenue data were reported in 2021 dollars using the implicit
price
deflator by the U.S. Bureau of Economic Analysis. This dataset was first described by
O’Farrell et al. (2017) and is fully described in O’Farrell et al. (in press). Bottom
longline,
handline and bandit reel reef fish fisheries data were mapped over a 10 x10 km grid and
over Coastal Fisheries statistical areas (Atkinson et al. 2021).
Data for reef fish fisheries without linked positional data (caught using diving, buoys,
gillnets and trolling) were mapped in the FIP using the self-reported Coastal Fisheries
statistical areas available in the logbooks (Atkinson et al. 2021). Revenues have been
adjusted to 2021 dollars using the implicit price deflator by the U.S. Bureau of
Economic
Analysis. Coastal Cast nets and Traps are small fisheries with little fishing effort,
have
no
non-confidential data at the statistical fishing area level if we apply the rule of
three
and
were not mapped.
Highly migratory
species fisheries
Highly migratory species (HMS) are fished using
multiple gears: pelagic longline, bandit, bottom longline, buoys, gillnet, green stick
tuna,
handlines, ottertrawl, pairtrawl, and rod and reel, but pelagic longline is by far the
largest
fishery in the GoM, accumulating almost 90% of logbook records from 2013 to 2021.
HMS fisheries data caught using pelagic longlines are available in the FIP from 2015 to
2021, when revenues data are available. Total revenue estimates were calculated by
George Silva (NOAA’s NMFS), and are not available for specific species or species
groups. For this dataset, landings and revenues are reported per set and coincide with a
self-reported coordinate. We summarized total landings and revenues data into Coastal
Fisheries statistical areas (Atkinson et al. 2021). Revenues have been adjusted to 2021
dollars using the implicit price deflator by the U.S. Bureau of Economic Analysis.
Although
this fishery has been recently mapped using high-spatial resolution VMS data, the data
for
the fishery in the GoM is too sparse and 10 x10 km grids would involve loosing about
half
of the data and were not considered here.
Headboat
fisheries
In the Gulf, information for headboats targeting reef fish is available
from 2015 to 2021. In headboats recreational fishers carry more than six passengers for
half or full day trips and fishers pay by the “head” (Fitzpatrick et al. 2017). Data
have
been
collected in the Gulf by the Beaufort Laboratory of the National Marine Fisheries
Service,
Southeast Fisheries Science Center (SFSC) since 1986, with an electronic logbook
system since 2013 and economic data added in 2014 (Carter and Liese 2017, Fitzpatrick
et al. 2017). For each trip, logbooks collect information on date and duration of the
trip,
geographic location of fishing activity, number of individuals of each caught species
that
were kept, the number of crew, number of non-fishing passengers, gallons of fuel used
and price paid per gallon of fuel, among others (Fitzpatrick et al. 2017). For this
fishery,
only data on location, date and net revenue pr trip were provided, and therefore there
are
no associated landings, species or port information.
Revenue was estimated by NOAA’s SFSC (Social Science Research Group, Recreational
Fisheries) as the price per angler hour multiplied by the number of anglers and trip
hours.
Net revenue was estimated as the revenue obtained minus fuel and crew costs, with fuel
costs equalling gallons used multiplied by the price per gallon, and crew costs
calculated
as trip duration multiplied by wage per hour and number of crew. All information was
extracted from logbooks except the price per angler hour and wage which were estimated
from additional documentation1
In the FIP all revenue data were reported in 2021 dollars using the implicit price
deflator
by
the U.S. Bureau of Economic Analysis. Headboat fisheries data were mapped over a 10
x10 km grid and over Coastal Fisheries statistical areas (Atkinson et al. 2021).
1 https://repository.library.noaa.gov/view/noaa/12007
Confidentiality
issues
US fisheries data are subject to strict confidentiality. To protect the identity of any
single
fisher, data presented to the public should conform a criteria called “rule of three”,
where
locations with less than three different vessels fishing are excluded (filtered) from
the
final
dataset. In all products in the FIP, records that did not meet the rule of three (<=
three
unique vessels targeting a grid cell) were removed, therefore all the layers include
only
non-confidential data.
Applying the rule of three implies loosing some information (Figure 1). The consequences
are likely to depend on the specific fishery or data subset. In general, the higher the
density of the data the less data loss. We quantified the percentage of data removed due
to applying the rule of three in each layer included in the FIP. All values can be found
in
the
tables at the end of this document.
Figure 1. In the figure, a grid overlays hypothetical fishing pings. Fishing pings have
different colors to represent different vessels. The same set of pings is shown in each
panel. When producing a grid and applying the rule of three, some cells and fishing
pings
are lost (right). For this hypothetical dataset, 11% of the pings are lost due to the
rule
of
three.
Confidentiality
tables
Table 1. Percentage of data loss (percentage of fishing pings lost) after applying the
rule
of
three to shrimp fisheries.
Layer
Description
10 km
% data
lost
Statistical
areas
% data lost
Overall Overall Landings
Total landings (pounds) for the entire time
series (2007-2021)
0.1789
0.0054
Overall Revenues
Total revenues (USD) for the entire timeseries (2007-2021)
0.1789
0.0054
Species Landings Brown shrimp
Total landings (pounds) for brown shrimp
0.1789
0.0054
Revenues Brown shrimp
Total revenues (USD) for brown shrimp
0.1789
0.0054
Landings White shrimp
Total landings (pounds) for white shrimp
0.1789
0.0054
Revenues White shrimp
Total revenues (USD) for white shrimp
0.1789
0.0054
Landings Seabobs
Total landings (pounds) for seabobs
0.1789
0.0054
Revenues Seabobs
Total revenues (USD) for seabobs
0.1789
0.0054
Landings Rock shrimp
Total landings (pounds) for rock shrimp
0.1789
0.0054
Revenues Rock shrimp
Total revenues (USD) for rock shrimp
0.1789
0.0054
Landings Trachypenaeus
Total landings (pounds) for trachypenaeus
0.1789
0.0054
Revenues
Trachypenaeus
Total revenues (USD) for trachypenaeus
0.1789
0.0054
Landings Pink shrimp
Total landings (pounds) for pink shrimp
0.1789
0.0054
Revenues Pink shrimp
Total revenues (USD) for pink shrimp
0.1789
0.0054
Landings Royal red
shrimp
Total landings (pounds) for royal red shrimp
0.1789
0.0054
Revenues Royal red
shrimp
Total revenues (USD) for royal red shrimp
0.1789
0.0054
Time Period Landings 2007-2014
Total landings (pounds) for the period 2007
to 2014
0.5557
0.0974
Revenues 2007-2014
Total revenues (USD) for the period 2007 to
2014
0.5557
0.0974
Landings 2015-2021
Total landings (pounds) for the period 2015
to 2021
0.3207
0.0062
Revenues 2015-2021
Total revenues (USD) for the period 2015 to
2021
0.3207
0.0062
State Landings Florida
Total landings (pounds) for vessels from
Florida
1.8754
0.2788
Revenues Florida
Total revenues (USD) for vessels from
Florida
1.8754
0.2788
Landings Alabama
Total landings (pounds) for vessels from Alabama
1.8401
0.0095
Revenues Alabama
Total revenues (USD) for vessels from
Alabama
1.8401
0.0095
Landings Mississippi
Total landings (pounds) for vessels from
Mississippi
5.4603
0.5359
Revenues Mississippi
Total revenues (USD) for vessels from
Mississippi
5.4603
0.5359
Landings Louisiana
Total landings (pounds) for vessels from
Louisiana
0.8153
0.1655
Revenues Louisiana
Total revenues (USD) for vessels from
Louisiana
0.8153
0.1655
Landings Texas
Total landings (pounds) for vessels from
Texas
0.0748
0.0118
Revenues Texas
Total revenues (USD) for vessels from Texas
0.0748
0.0118
Table 2. Percentage of data loss (percentage of fishing pings lost) after applying the
rule of
three to bottom longline, bandit and handline reef fish fisheries.
Layer
Description
10 km
% data
lost
Statistical
areas
% data lost
Overall Overall Landings
Total landings (pounds) for the entire time
series (2007-2021)
0.2112
0.014
Overall Revenues
Total revenues (USD) for the entire timeseries (2007-2021)
0.2112
0.014
Species Landings Red Snapper
Total landings (pounds) for Red Snapper
0.2112
0.014
Revenues Red Snapper
Total revenues (USD) for Red Snapper
0.2112
0.014
Landings Mid-depth snapper group
Total landings (pounds) for Mid-depth snapper group
0.2112
0.014
Revenues Mid-depth snapper group
Total revenues (USD) for Mid-depth
snapper group
0.2112
0.014
Landings Shallow-water snapper group
Total landings (pounds) for Shallow-water snapper group
0.2112
0.014
Revenues Shallow-water snapper group
Total revenues (USD) for Shallow-water snapper group
0.2112
0.014
Landings Shallow-water grouper group
Total landings (pounds) for Shallow-water grouper group
0.2112
0.014
Revenues
Shallow-water grouper group
Total revenues (USD) for Shallow-water grouper group
0.2112
0.014
Landings Deep-water grouper group
Total landings (pounds) for Deep-water grouper group
0.2112
0.014
Revenues Deep-water grouper group
Total revenues (USD) for Deep-water grouper group
0.2112
0.014
Revenues Tilefishes group
Total revenues (USD) for Tilefishes group
0.2112
0.014
Revenues Tilefishes group
Total revenues (USD) for Tilefishes group
0.2112
0.014
Revenues Jacks group
Total revenues (USD) for Jacks group
0.2112
0.014
Revenues Jacks group
Total revenues (USD) for Jacks group
0.2112
0.014
Revenues Triggerfishes group
Total revenues (USD) for Triggerfishes group
0.2112
0.014
Revenues Triggerfishes group
Total revenues (USD) for Triggerfishes group
0.2112
0.014
Revenues Grunts and porgies group
Total revenues (USD) for Grunts and porgies group
0.2112
0.014
Revenues Grunts and porgies group
Total revenues (USD) for Grunts and porgies group
0.2112
0.014
Revenues Coastal pelagics group
Total revenues (USD) for Coastal pelagics group
0.2112
0.014
Revenues Coastal pelagics group
Total revenues (USD) for Coastal pelagics group
0.2112
0.014
Time Period Landings 2007-2014
Total landings (pounds) for the period 2007
to 2014
0.5251
0.0275
Revenues 2007-2014
Total revenues (USD) for the period 2007 to
2014
0.5251
0.0275
Landings 2015-2021
Total landings (pounds) for the period 2015
to 2021
0.6193
0.0077
Revenues 2015-2021
Total revenues (USD) for the period 2015 to
2021
0.6193
0.0077
State Landings Florida
Total landings (pounds) for vessels from
Florida
0.2012
0.0159
Revenues Florida
Total revenues (USD) for vessels from
Florida
0.2012
0.0159
Landings Alabama
Total landings (pounds) for vessels from Alabama
6.584
2.8109
Revenues Alabama
Total revenues (USD) for vessels from
Alabama
6.584
2.8109
Landings Mississippi
Total landings (pounds) for vessels from
Mississippi
24.6902
1.0891
Revenues Mississippi
Total revenues (USD) for vessels from
Mississippi
24.6902
1.0891
Landings Louisiana
Total landings (pounds) for vessels from
Louisiana
3.0254
0.4506
Revenues Louisiana
Total revenues (USD) for vessels from
Louisiana
3.0254
0.4506
Landings Texas
Total landings (pounds) for vessels from
Texas
3.3964
0.1001
Revenues Texas
Total revenues (USD) for vessels from Texas
3.3964
0.1001
Table 3. Percentage of data loss (percentage of fishing records lost) after applying the rule
of three into statistical areas to other reef fish fisheries. “NA” indicates no fisheries data for
that particular subset.
Layer
Description
Diving
Buoys
Gillnet
Trolling
Overall Overall Landings
Total landings (pounds) for the entire time
series (2007-2021)
8.8318
21.1111
13.8518
2.8719
Overall Revenues
Total revenues (USD) for the entire timeseries (2007-2021)
8.8318
21.1111
13.8518
2.8719
Species Landings Red Snapper
Total landings (pounds) for Red Snapper
8.8318
21.1111
13.8518
2.8719
Revenues Red Snapper
Total revenues (USD) for Red Snapper
8.8318
21.1111
13.8518
2.8719
Landings Mid-depth snapper group
Total landings (pounds) for Mid-depth snapper group
8.8318
21.1111
13.8518
2.8719
Revenues Mid-depth snapper group
Total revenues (USD) for Mid-depth
snapper group
8.8318
21.1111
13.8518
2.8719
Landings Shallow-water snapper group
Total landings (pounds) for Shallow-water snapper group
8.8318
21.1111
13.8518
2.8719
Revenues Shallow-water snapper group
Total revenues (USD) for Shallow-water snapper group
8.8318
21.1111
13.8518
2.8719
Landings Shallow-water grouper group
Total landings (pounds) for Shallow-water grouper group
8.8318
21.1111
13.8518
2.8719
Revenues
Shallow-water grouper group
Total revenues (USD) for Shallow-water grouper group
8.8318
21.1111
13.8518
2.8719
Landings Deep-water grouper group
Total landings (pounds) for Deep-water grouper group
8.8318
21.1111
13.8518
2.8719
Revenues Deep-water grouper group
Total revenues (USD) for Deep-water grouper group
8.8318
21.1111
13.8518
2.8719
Revenues Tilefishes group
Total revenues (USD) for Tilefishes group
8.8318
21.1111
13.8518
2.8719
Revenues Tilefishes group
Total revenues (USD) for Tilefishes group
8.8318
21.1111
13.8518
2.8719
Revenues Jacks group
Total revenues (USD) for Jacks group
8.8318
21.1111
13.8518
2.8719
Revenues Jacks group
Total revenues (USD) for Jacks group
8.8318
21.1111
13.8518
2.8719
Revenues Triggerfishes group
Total revenues (USD) for Triggerfishes group
8.8318
21.1111
13.8518
2.8719
Revenues Triggerfishes group
Total revenues (USD) for Triggerfishes group
8.8318
21.1111
13.8518
2.8719
Revenues Grunts and porgies group
Total revenues (USD) for Grunts and porgies group
8.8318
21.1111
13.8518
2.8719
Revenues Grunts and porgies group
Total revenues (USD) for Grunts and porgies group
8.8318
21.1111
13.8518
2.8719
Revenues Coastal pelagics group
Total revenues (USD) for Coastal pelagics group
8.8318
21.1111
13.8518
2.8719
Revenues Coastal pelagics group
Total revenues (USD) for Coastal pelagics group
8.8318
21.1111
13.8518
2.8719
Time Period Landings 2007-2014
Total landings (pounds) for the period 2007
to 2014
8.4287
57.6923
17.603
3.4778
Revenues 2007-2014
Total revenues (USD) for the period 2007 to
2014
8.4287
57.6923
17.603
3.4778
Landings 2015-2021
Total landings (pounds) for the period 2015
to 2021
10.5795
30.4688
22.8417
4.0679
Revenues 2015-2021
Total revenues (USD) for the period 2015 to
2021
10.5795
30.4688
22.8417
4.0679
State Landings Florida
Total landings (pounds) for vessels from
Florida
6.8990
20.6704
1.3908
1.8430
Revenues Florida
Total revenues (USD) for vessels from
Florida
6.8990
20.6704
1.3908
1.8430
Landings Alabama
Total landings (pounds) for vessels from Alabama
NA
100
100
18.1347
Revenues Alabama
Total revenues (USD) for vessels from
Alabama
NA
100
100
18.1347
Landings Mississippi
Total landings (pounds) for vessels from
Mississippi
NA
NA
NA
100
Revenues Mississippi
Total revenues (USD) for vessels from
Mississippi
NA
NA
NA
100
Landings Louisiana
Total landings (pounds) for vessels from
Louisiana
100
NA
100
6.5858
Revenues Louisiana
Total revenues (USD) for vessels from
Louisiana
100
NA
100
6.5858
Landings Texas
Total landings (pounds) for vessels from
Texas
NA
NA
NA
100
Revenues Texas
Total revenues (USD) for vessels from Texas
NA
NA
NA
100
Table 4. Percentage of data loss (percentage of fishing records lost) after applying the rule
of three into statistical areas to highly migratory species fisheries. “NA” indicates no
fisheries data for that particular subset.
Layer
Description
% data lost
Overall Overall Landings
Total landings (pounds) for the entire time series (2015-2021)
0.6893
Overall Revenues
Total revenues (USD) for the entire timeseries (2015-2021)
0.6893
State Landings Florida
Total landings (pounds) for vessels from
Florida
1.1851
Revenues Florida
Total revenues (USD) for vessels from
Florida
1.1851
Landings Alabama
Total landings (pounds) for vessels from Alabama
100
Revenues Alabama
Total revenues (USD) for vessels from
Alabama
100
Landings Mississippi
Total landings (pounds) for vessels from
Mississippi
100
Revenues Mississippi
Total revenues (USD) for vessels from
Mississippi
100
Landings Louisiana
Total landings (pounds) for vessels from
Louisiana
0.4557
Revenues Louisiana
Total revenues (USD) for vessels from
Louisiana
0.4557
Landings Texas
Total landings (pounds) for vessels from
Texas
100
Revenues Texas
Total revenues (USD) for vessels from Texas
100
Table 5. Percentage of data loss (percentage of fishing records lost) after applying the rule
of three to headboat fisheries. “NA” indicates no fisheries data for that particular subset.
Layer
Description
% data lost
Overall Overall Net Revenues– 10 km grid
Total net revenues (USD) for the entire time series (2015-2021)
12.3578
Overall Net Revenues– statistical grid
Total net revenues (USD) for the entire time series (2015-2021)
0.7612
Fishing territories
Although the sea can look like an open landscape without boundaries, fishers' extraction of its resources is highly clustered in space, and different fishing communities have well defined fishing territories they target. Knowledge of fishing territories can be used to identify where fishing occurs, to quantify site fidelity, competition, temporal shifts in use, to assess the effects of management measures, and to allow rapid-response assessments of vulnerability of fishing-dependent communities to environmental shocks.
Fishing territories were estimated from detailed Vessel Monitoring System data that provides the position of each vessel at intervals of about 1 hour, which has been linked to logbook records recording associated counties of landing. Here, territories are identified at the spatial resolution of Counties.
Fishing territories were delineated using polygons that outline the areas where 95% of that community’s vessel activity occur in their entire fishing history.
For reef fishing (longline, handline and bandit reel), territories span the period 2007-2021. The maps were created using a Local Convex Hull method that constructs small minimum convex polygons (hulls) for each fishing position and its neighbors, and then merging the hulls together, therefore taking spatial autocorrelation into account (Getz et al. 2007). Here, we set the parameter k (the number of neighbors) to the square root of the number of observations, which is commonly advised (Signer et al. 2015, Noonan et al. 2019). This method has shown to be the most appropriate to estimate fishing territories in fishing data (Chollett et al, in review).
For shrimp, territories describe the fishery for the period 2014-2021. The maps were created using a Kernel Density Estimation method that aggregates all fishing effort into grids, and then generates a surface using a non-parametric method based on a smoothing parameter h. Kernel results are extremely sensitive to the choice of the smoothing parameter. Here, we used the automatic method smoothed cross validation (Duong 2022) to calculate a bivariate h. This method has shown to be appropriate to estimate communities-at-sea in fishing data when datasets are large (Chollett et al, in review).
All maps were aggregated at the “community” level, and represent the collective grounds of all fishers for that County. To protect data confidentiality, only communities consisting of more than three vessels were mapped.
References
Atkinson S, Judge M, Orhun R. 2021. Coastal Fisheries Logbook Program Metadata.
SEDAR74-DW-3. SEDAR. North Charleston, SC. 17 pp. Available at:
https://sedarweb.org/documents/sedar-74-dw-03-coastal-fisheries-logbook-program-
metadata/
Breiman L. 2001. Random forests. Machine Learning. 45: 5-32.
Carter DW, Liese C. 2017. Summary of economic data collected by the Gulf of Mexico and
South Atlantic Headboat Logbooks: 2015. NOAA Technical Memorandum NMFS-SEFSC-
703. Miami, Florida. 34 pp.
Chollett I, O’Farrell S., Perruso L., McPherson M., Matitski A. In review. Delineating
fishing territories for marine resource management.
Chollett I, O’Farrell S. 2022. Gulf of Mexico shrimp fishery: linking ELB and dealer data
to map landings and revenues. Report presented to NOAA SFSC. West of Ireland. 13 pp.
Chollett I, Perruso L, O’Farrell S. 2022. Toward a better use of fisheries data in
spatial planning. Fish and Fisheries. 23: 1136-1149.
Duong T. 2022. ks: Kernel Smoothing. R package version 1.14.0. https://CRAN.R-project.org/package=ks
Fitzpatrick EE, Williams EH, Shertzer KW, Siegfried KI, Craig JK, Cheshire RT, Kellison
GT, Fitzpatrick KE, Brennan K. 2017. The NMFS Southeast Region Headboat Survey:
History, methodology, and data integrity. Marine Fisheries Review. 79(1):1-27.
Getz WM, Fortmann-Roe S, Cross PC, Lyons AJ, Ryan SJ, Wilmers CC. 2007.
LoCoH: Nonparameteric Kernel methods for constructing home ranges and utilization distributions.
PLoS One. 2(2): e207.
Noonan MJ, Tucker MA, Fleming CH, Akre TS, Alberts SC, Ali AH, Altmann J, Antunes PC, Belant JL, Beyer D, Blaum N. 2019. A comprehensive analysis of autocorrelation and bias in home range estimation. Ecological Monographs. 89(2):e01344.
O’Farrell S, Sanchirico JN, Chollett I, Cockrell M, Murawski SA, Watson JT, Haynie A,
Strelcheck A, Perruso L. 2017. Improving detection of short-duration fishing behaviour
in vessel tracks by feature engineering of training data. ICES Journal of Marine Science.
74(5):1428-36.
O’Farrell S, Perrruso L, Sanchirico JN, Chollett I. In press. Linking real world
fisheries datasets for mapping of revenue from fishing grounds to dependent communities.
Canadian Journal of Fisheries Sciences.
Signer J, Balkenhol N, Ditmer M, Fieberg J. 2015.
Does estimator choice influence our ability to detect changes in home-range size?.
Animal Biotelemetry. 3:1-9.