american samoa commercial fisheries … samoa commercial fisheries biosampling program rose atoll...
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American Samoa Commercial Fisheries Biosampling Program
Rose AtollManu’a
Tutuila
Independent Samoa
Vailulu’uSeamount Tongan Trench
The Samoan Archipelago
Congress funds NMFS to expand data requirements consistent with Magnuson-Stevens Act
Fisheries Science initiatives has funded Commercial Fish Biosampling
Goals of Biosampling: (1) to obtain life history data (2) size and age-specific population structure; (3) stock identity data
Philosophy: (1) non-aggressive; (2) minimal impact; (3) non-competitive
Background
U.S. Department of Commerce| National Oceanic and Atmospheric Administration |NOAA Fisheries | Page 5
Stock Assessment computer model:Pounds of fish next yr =
Pounds of fish this yr + Recruits + Growth – Death (natural fishery)
ABUNDANCE• Fishery data
(CPUE)• Non-fishery data
BIOLOGY• Includes life
history
CATCH• Commercial• Recreational• Subsistence
How many fish can we catch next year, based on the biology of the fish?Stock assessment also describes current and past abundance & stock status.
Challenges of AS creel programs Very limited species level identification Limited staff capacity for species ID, management
issues Creel survey protocol implementation issues ‘Representative’ sampling issues Low fisheries participation, esp. night spearfishing L-W coefficients were not AS specific Very limited life history data collections, analyses
A.
Age (years)
0 10 20 30 40
Fork
Len
gth
(mm
)
0
50
100
150
200
250
Model coral reef fishes
Acanthurus nigricans / A. Samoa: sex-specific Von Bertalanffy growth model
0
20
40
60
80
100
120
140
160
180
200
0 5 10 15 20 25 30
Age (years)
Fork
Len
gth
(mm
)
Female
Male
Imm
VB parameters: Females: n = 318, Linf = 169.6, K = 1.14, to = -0.165Males: n = 174, Linf = 163.2, K = 1.19, to = -0.165
Ctenochaetus striatus
Acanthurus nigricans
Life History Data for pone Ctenochaetus striatus
Lab Biosampling provides life history data such as growth rate, longevity, timing of spawning and length-at-first maturity.
a. Recruits
Substratum Regression
coefficient (β)
p
Rubble 0.32 <0.01*
b. Juveniles
Substratum Regression
coefficient (β)
p
Algae - 0.26 <0.05*
c. Adults
Substratum Regression
coefficient (β)
p
Coralline Algae 0.27 < 0.05*
Relationship between the abundance of (a) recruits, (b) juvenile, (c) adult and percent cover of each substratum type.
Recruits Juveniles Adults
Recruits -
Juveniles 0.17 -
Adults -0.23* -0.03
Spearman rank correlation analysis of the Ctenocheatusstriatus size categories. Significant correlations are highlighted in bold (p < 0.05).
Size and Age Data for Cephalopholis urodeta
(Ochavillo et al., in prep)
0.00
2.00
4.00
6.00
8.00
Ofu-Olosega Tau Tutuila
Islands
Age
(yea
rs)
Cephalopholis urodeta
0102030405060708090
100110120130140150160170180190200210220230240250260
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18
Age
Tota
l len
gth Female
Female VBGFMaleMale VBGF
Fast early growth, asymptotic
Relatively low longevity
Inter-island demographic differences
Hire and capacitate a staff member to identify the catch to species level
Develop and field-test logistics to collect length-and-weight-data from commercial fisheries (Field Biosampling)
Develop a protocol for collecting and processing otolith, gonads and fin clips (Lab Biosampling)
Regularly evaluate lessons learned and make recommendations for improvement
Objectives of Biosampling
Biosampling Program Timeline August 2009, the PIFSC and the Council organized a
biosampling workshop at the Guam Fisherman’s Co-op Association (GFCA) in Hagatna, Guam.
In an October 2010 workshop held at the LHP Lab in Aiea, Hawaii
Biosamplers in American Samoa began regular sampling of reef and bottom fish at the FagatogoMarket in Pago Pago, October 2010
In Feb-March 2012, fish ID workshop in Bishop Museum
Milestones We have 7 DMWR staff trained to identify fish
species ID of catch
We work with 15 spearfishermen, 6 bottomfishingboats, and 2 handlining fishermen.
Measured over 216,000 fish lengths, over 209,000 lbs fish
Collected almost almost 4,000 otoliths and gonads from 10 fish species for life-history data; and over 200 fin slips for barcode of life project.
Collected AS specific L-W coefficients
Species level fish catch summaries
Protocol (Field Biosampling) For spearfishing, sampling was conducted bet 4 to 7
AM For bottomfishing, sched is more variable Saturdays is always covered Each fisherman is the sampling unit Separated trolling vs bottomfishing in mixed fishing Each fish and inverts ID to species and measured Staff used audio recorders, recoded to computer Audio files are archived following PIFSC protocols Ice supplied, documentation
Protocol Fish and inverts measured to nearest cm For octopus-head length; for lobsters-carapace length L-W measurements; eventually L only if ‘enough’ data Data entry/management customized PIFSC-WestPACFIN maintained software, database,
support Field Biosampling Database and Lab Biosampling
Database Labeling, preservation, and archival protocols for
extracted gonads and otoliths
Lab Protocol (Lab Biosampling) Species, length, weight, sex, gonad weight, tag Specimen labeled (A=American Samoa, 3 letters for
tech name, sequence number) Visual gonad categorization (male, female, unid) Gonad weight to 0.01 g X-section of central gonad or whole gonad preserved Sagittae otoliths extracted (2, 1.5, 1, 0.5, 0 categories) Otoliths stored in vials with cotton balls Targeted 20 specimens per species per month Target sizes: sizes represented; opportunistic on large
sizes; small sizes from focused collections
Lab Protocol (Fin clips) 5 specimen per species Fishing ground, length, weight 2 digital photos taken from each specimen Photo taken with fish atop measuring board Fish facing left Fins spread as much as possible Specimen labeled following protocols (A=American
Samoa, 3 letters for tech name, sequence number)
Life history species for AS Lethrinus xanthochilus Lethrinus rufolineatus Lutjanus gibbus Myripristis berndti Myripristis amaena Myripristis murdjan Naso unicornis Sargocentron spiniferum Sargocentron tiere Scarus rubroviolaceus Criteria: Top species landing, preference, available size
ranges
What Biosampling Data Are Collected:
Name of fishermanDateArea fishedNumber of hours fishingCar or boat?How many fisherman in boatHow much bait used (bottomfishing)How much fuel usedHow much ice (supplied)All species (length, weight)Gonads and otoliths of target species
Top fish species caught (number) by commercial spearfishing
Species Total %1 Acanthurus lineatus 79,305 54.92 Ctenochaetus striatus 6,554 4.53 Naso lituratus 5,573 3.94 Sargocentron tiere 5,300 3.75 Chlorurus japanensis 4,555 3.26 Naso unicornis 3,563 2.57 Scarus rubroviolaceus 3,179 2.28 Panulirus pencillatus 2,975 2.19 Scarus oviceps 2,590 1.8
10 Myripristis berndti 2,177 1.511 Acanthurus nigricans 2,153 1.512 Epinephelus melanostigma 1,674 1.213 Myripristis amaena 1,664 1.214 Acanthurus guttatus 1,662 1.115 Panulirus sp. 1,648 1.1
species %1 Acanthurus lineatus 28.32 Parrotfishes 25.33 Ctenochaetus striatus 8.94 Unicornfishes 7.65 Panulirus penicillatus 6.26 Reef fishes (unknown) 6.07 Inshore groupers 4.58 Squirrelfishes 2.89 Acanthurus xanthopterus 2.2
10 Acanthurus nigrofuscus 0.711 Naso lituratus 0.6
Creel SurveyBiosampling
Top fish species caught (number) by commercial bottomfishing
Species Grand Total %1 Lutjanus kasmira 5558 27.1 2 Lethrinus rubrioperculatus 4102 20.0 3 Lethrinus xanthochilus 1974 9.6 4 Lutjanus gibbus 1879 9.2 5 Aprion virescens 865 4.2 6 Variola albimarginata 821 4.0 7 Lutjanus rufolineatus 529 2.6 8 Lethrinus harak 302 1.5 9 Sphyraena forsteri 280 1.4
10 Lethrinus amboinensis 229 1.1 11 Pristipomoides flavipinnis 225 1.1 12 Sargocentron spiniferum 191 0.9 13 Aphareus rutilans 173 0.8 14 Lutjanus fulvus 170 0.8 15 Lutjanus monostigma 166 0.8
Species Pounds Price/Lb. Value
BMUS
Blue lined snapper 427 $2.73 $1166
Ruby snapper (ehu) 374 $4.41 $1649
Flower snapper (gindai) 41 $2.75 $113
Gray jobfish 200 $3.42 $684
Pink snapper (opakapaka) 265 $3.02 $802
Silverjaw jobfish (lehi) 71 $3.37 $240
Longtail snapper (onaga) 146 $2.82 $412
Goldflag jobfish 51 $3.70 $188
Yellow-edged lyretail 3 $3.00 $9
Redgill emperor 389 $3.40 $1323
Black jack 79 $2.94 $231
Giant trevally 18 $3.50 $64
BMUS SUBTOTALS 2064 $3.33 $6882
OTHER
Bottomfishes (unknown) 10987 $2.88 $31695
Yellow margined snapper 8 $3.75 $28
Brown jobfish 33 $2.95 $99
Humpback snapper 975 $3.44 $3356
Onespot snapper 117 $3.75 $438
Twinspot/red snapper 44 $2.95 $130
Groupers 125 $3.27 $409
Flagtail grouper 2 $3.75 $7
Peacock grouper 20 $3.75 $74
Emperors 1059 $3.70 $3918
Species Weight SummariesSpeciesName Total (lbs)
1 Acanthurus lineatus 101,856
2 Scarus rubroviolaceus 9,026
3 Naso unicornis 8,005
4 Chlorurus japanensis 5,666
5 Naso lituratus 4,612
6 Panulirus pencillatus 4,293
7 Lethrinus xanthochilus 3,948
8 Lethrinus rubrioperculatus 3,706
9 Ctenochaetus striatus 3,575
10 Aprion virescens 3,281
11 Panulirus sp. 3,160
12 Lutjanus gibbus 3,133
13 Lutjanus kasmira 2,633
14 Scarus oviceps 2,473
15 Chlorurus microrhinos 1,924
16 Sargocentron tiere 1,912
17 Epinephelus melanostigma 1,662
18 Scarus frenatus 1,549
19 Actinopyga mauritiana 1,398
20 Acanthurus xanthopterus 1,314
Sargocentron tiereFish Sampled in American Samoa March 2011-January 2013
AirportAloauAmouliAuasiAunuu
Avau-NuuuliFagaaluFagasaFailoloFogagogoLauliiMasefauTulaVaitogi
Distinct spear fishing areas
Multivariate statistical analyses of fish species assemblages indicated that these are highly distinct fishing grounds.
TaputapuAunuuFagaaluLauliiTula
Distinct bottomfishing areas
Multivariate statistical analyses of fish species assemblages indicated that these are highly distinct fishing grounds.
"Var1"; LS MeansWilks lambda=.37655, F(104, 1381.3)=2.0240, p=.00000
Effective hypothesis decompositionVertical bars denote 0.95 confidence intervals
AirportAloau
AmouliAuasi
AunuuAvau-Nuuuli
FagaaluFagasa
FailoloFogagogo
LauliiMasefau
TulaVaitogi
Var1
-2
-1
0
1
2
3
4
5
Pan
uliru
s pe
nici
llatu
s
"Var1"; LS MeansWilks lambda=.37655, F(104, 1381.3)=2.0240, p=.00000
Effective hypothesis decompositionVertical bars denote 0.95 confidence intervals
AirportAloau
AmouliAuasi
AunuuAvau-Nuuuli
FagaaluFagasa
FailoloFogagogo
LauliiMasefau
TulaVaitogi
Var1
-1.5
-1.0
-0.5
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
Chl
orur
us m
icro
rhin
os
"Var1"; LS MeansWilks lambda=.37655, F(104, 1381.3)=2.0240, p=.00000
Effective hypothesis decompositionVertical bars denote 0.95 confidence intervals
AirportAloau
AmouliAuasi
AunuuAvau-Nuuuli
FagaaluFagasa
FailoloFogagogo
LauliiMasefau
TulaVaitogi
Var1
-0.5
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
5.0
Nas
o un
icor
nis
Biosampling statistics
Coral reef fishery stock assessmentWhat are the exploitation rates for various species?
Species mean length k maximum min Lmax Linfinity M ZExploitati
on
(cm) age (yrs) Rate (%)
Acanthurus lineatus 19 0.7 18 10 22 25 0.23 0.42 44.2
Acanthurus nigricans 17.5 1.7 25 10 24 26 0.17 1.34 87.4
Ctenochaetus striatus 18 0.9 34 10 17 22 0.12 0.45 72.4
Chlorurus microrhinos 36.6 0.3 17 18 59 65 0.25 0.38 35.0
Scarus rubroviolaceus 34.8 0.59 8 21.5 55 61 0.53 1.00 47.3
Naso unicornis 34.7 0.49 30 17 83.5 90 0.14 1.50 90.6
Size limits can also be derived from yield-per-recruit analyses using M, k, lc, Linf.
Issues and Challenges Biosampling was too successful but filled a gnawing
data gap Competed with existing creel program, highlighted
deficiencies of existing creel Unsustainable, need to explore sustainability Needed regular review Data quality issues (some expected): gonad IDs, length
discrepancies, species IDs Accumulated a lot of high quality data that remain
unanalyzed
Issues and Challenges Biosampling succeeded based on its objectives Biosampling eventually filled in on some other
objectives: Attempt to integrate it to existing creel Data is now used for data-poor methods such as PSA Length-based assessment is largely unexplored but
precedented Data could be used to independently corroborate
existing creel survey data
Fa’afaetai tele lava!
David Hamm and Kimberly Lowe, and staffNOAA Pacific Islands Fisheries Science Center
Bob Humphries
Dr. Ruth Matagi-Tofiga, Director DMWR
TeeJay Letalie, Auvaa Soonaolo, Poasa TofaeonoAlama Tua, Ekueta Schuster, Faleselau Tuilagi
Numerous fishermen who have supported BiosamplingMamani and Talavou
Scientific/Technical Do the laboratory and market sampling programs apply an
appropriate suite of methods to sample collection and analysis? Yes
Are the sample collection and analytical processes of the laboratory sampling program peer-reviewed, efficient, effective and clearly described? The samples collection for the life history could be improved.
Are the territorial field and laboratory teams appropriately trained in the skills necessary for executing the program protocols? Yes. The field ID of gonad sex was expected to be fraught esp for sex-changers. But the histo would correct this.
How are the species collected for life history determined? Are those species appropriate for management purposes? DMWR proposed the species based on criteria.
Data Are the data collection protocols clearly articulated, streamlined,
efficient and appropriate to the data collected? Are there improvements that could be effectively implemented within current resources? For Field Biosampling: it was not clear at what point data was enough. For Lab Biosampling: the size collection probably needed some guidance. For Fin Clips: could be more focused perhaps on problematic species identifications.
Do data confidentiality concerns exist and how are they accommodated? Are data review, quality control, data integrity, transparency, confidentiality, and PII, etc. treated appropriately? This needs improvement. Data review irregular, data quality control could be more improved although program included some flags.
What fisheries management research questions are the data being collected for? Are the samples collected and the analytical process used relevant to the management or research questions being asked? Is the data collection appropriately designed to meet the management needs? Objectives were met but management research questions were not inclusive at the onset.
Communication Are effective working relationships in place with vendors
and fishermen so that staff are able to obtain access to measure and take samples of fish at the landing sites and at vendor sites? Yes, definitely.
Is the communication between, territorial and federal bio-sampling staff effective and at the appropriate level to meeting the needs of territorial and federal mandates? Communication needs to be improved, lapses most probably due to heavy workload of agencies involved.
Are the results of the bio-sampling work communicated to stakeholders and the public? Very limited.
Opportunities Are there existing opportunities for leveraging that
should be pursued but are not currently? E.g., data management systems, training opportunities? The Biosampling Program generated a lot of data that are still unexplored: (a) length-based stock assessment; (b) spatial analyses of CPUE and identifying environmental correlates to coral reef productivity; (c) analyses to determine ‘effective’ sampling; (d) independent corroboration of creel survey data.
Questions to Territorial Agencies Describe your agency’s fisheries management mandates. Assessment of
fisheries and stock status and habitats; catch and size limits What are your agency’s management and monitoring priorities around
meeting those mandates? Creel survey programs and habitat monitoring programs; stock assessments in collaboration with federal agencies; limited resources for life-history projects.
How does the bio-sampling program support those priorities? L-W coeffficients, life-history data (size at maturity, average length, longevity, etc.); average length data
Does the agency currently use data collected in the bio-sampling program and how are those data used? The data are most utilized in data-poor assessments such as PSA at the moment. We expect more data analyses in the future.
Describe your agency’s process or participation in the selection of priority species. We collaborated with PIFSC in species selection.
Describe your agency’s activities, role, and technical capacity in the scientific/technical and data management/analysis aspects of the bio-sampling program, e.g., collecting data, quality control, logistics, man-hours. Activities mainly focused in communicating with fishermen, field sampling, gonad and otolith extraction, data encoding, data quality control, logistics. We expect to be more involved in gonad histology analyses and foresee collaboration in analytics.