ANNUAL STOCK ASSESSMENT AND FISHERY EVALUATION REPORT HAWAII ARCHIPELAGO FISHERY ECOSYSTEM PLAN 2017 t f a r D Western Pacific Regional Fishery Management Council 1164 Bishop St., Suite 1400 Honolulu, HI 96813 PHONE: (808) 522-8220 FAX: (808) 522-8226 www.wpcouncil.org The ANNUAL STOCK ASSESSMENT AND FISHERY EVALUATION REPORT for the HAWAII ARCHIPELAGO FISHERY ECOSYSTEM 2017 was drafted by the Fishery Ecosystem Plan Team. This is a collaborative effort primarily between the Western Pacific Regional Fishery Management Council, NMFS-Pacific Island Fisheries Science Center, Pacific Islands Regional Office, and the Division of Aquatic Resources (HI) Department of Marine and Wildlife Resources (AS), Division of Aquatic and Wildlife Resources (Guam), and Division of Fish and Wildlife (CNMI). This report attempts to summarize annual fishery performance looking at trends in catch, effort and catch rates as well as provide a source document describing various projects and activities being undertaken on a local and federal level. The report also describes several ecosystem considerations including fish biomass estimates, biological indicators, protected species, habitat, climate change, and human dimensions. Information like marine spatial planning and best scientific information available for each fishery are described. This report provides a summary of annual catches relative to the Annual Catch Limits establishetd by the Council in collaboration with the local fishery management agencies. f Edited By: Marlowe Sabater, Asuka Ishizaki, Rebecca Walker, Sylvia Spalding, and Thomas a Remington WPRFMC r D This document can be cited as follows: WPRFMC, 2018. 2017 Annual Stock Assessment and Fishery Evaluation Report for the Hawaii Archipelago Fishery Ecosystem Plan. Sabater, M., Ishizaki, A., Walker, R., Remington, T., Spalding, S. (Eds.) Western Pacific Regional Fishery Management Council. Honolulu, Hawaii 96813 USA. ii The Western Pacific Regional Fishery Management Council acknowledges the valuable contributions of the following Plan Team members for drafting sections of this report: Hawaii Division of Aquatic Resources: Reginald Kokubun, Hal Koike, and Ryan Okano NMFS Pacific Islands Fisheries Science Center: Justin Hospital, Ivor Williams, Joe O’Malley, Brett Taylor, Michael Parke, Phoebe Woodworth-Jefcoats, John Marra, Tom Oliver, Frank Parrish, T. Todd Jones, Kirsten Leong, and Minling Pan. NMFS Pacific Islands Regional Office: Melanie Brown and Sarah Ellgen Pacific Islands Regional Planning Body: Sarah Pautzke The Council also acknowledges the staff of the NMFS PIFSC Western Pacific Fisheries Information Network (WPacFIN) for providing the technical support to generate the data t summaries. f The Council would like to thank the following individuals for their contributions to the report: Catherine Pham, Dawn Golden, and Lennon Thomas a r D iii Annual SAFE Report for the Hawaii Archipelago FEP Table of Contents t f a This page was intentionally left blank. r D iv Annual SAFE Report for the Hawaii Archipelago FEP Table of Contents EXECUTIVE SUMMARY As part of its five-year fishery ecosystem plan (FEP) review, the Council identified the annual reports as a priority for improvement. The former annual reports have been revised to meet National Standard regulatory requirements for the Stock Assessment and Fishery Evaluation (SAFE) reports. The purpose of the report is twofold: to monitor the performance of the fishery and ecosystem to assess the effectiveness of the FEP in meeting its management objectives, and to the structure of the FEP living document. The reports are comprised of three chapters: fishery performance, ecosystem considerations, and data integration. The Council will iteratively improve the annual SAFE report as resources allow. The fishery performance section of this report presents descriptions of Hawaiian commercial fisheries including deep-7 bottomfish, non-deep-7 bottomfish, coral reef, crustacean, and mollusk and limu management unit species (MUS). The data collection systems for each fishery are explained. The fishery statistics are organized into summaryt dashboard tables showcasing the values for the most recent fishing year and the percent change between short-term (10-year) and f long-term (20-year) averages. Time series for historical fishing parameters, top species catch by gear, and total catch values by gear are also provided. For 2017 catch in Hawaii, none of the a evaluated MUS exceeded their associated annual catch limits (ACL), allowable biological catch (ABC) values, or overfishing limits (OFL). Note that ACLs were not specified for Kona crab, non-Deep 7 bottomfish, or coral reef ecosystem management unit species because the National Marine Fisheries Service (NMFS) had recently acquired new information that require additional r environmental analyses to support the Council’s ACL recommendations for these MUS. Recent average catch for the Main Hawaiian Island Deep 7 bottomfish stock complex (266,550 lbs.) D accounted for 87.1% of its prescribed ACL (306,000 lbs.). In 2017, the Main Hawaiian Island deep-7 bottomfish fishery was characterized by maintaining a decreasing trend in fishing effort and participation relative to measured averages. Though the number of fish caught and the weight also showed a decrease, effort and participation were decreasing such that CPUE for the fishery reflected an increase CPUE relative to short- and long-term averages. The deep 7 catch was mostly from the deep sea handline. The non-deep 7 bottomfish fishery was mostly dominated by uku (Aprion virescens) with a smaller contribution from white ulua (Caranx ignobilis). The fishery participation and effort were relatively consistent with short-term values and showed a slight increase in comparison with 20-year averages. The total number and pounds of non-Deep 7 bottomfish caught were up overall in 2017. Non-deep 7 species were landed using the deep-sea handline, inshore-handline, and troll method. The deep-sea handline method had interannual increases in participation, effort, catch, and CPUE. The inshore handline showed the same pattern of increasing participation, effort, and catch, though associated CPUE was slightly less. In contrast, while troll with bait had interannual decreases in all evaluated parameters except for CPUE, the comparisons with the short- and long-term averages showed stable effort and participation with increases in catch and CPUE. The coral reef ecosystem management unit species (CREMUS) finfish fishery, in general, exhibited a decline in fishing participation, effort, and catch from 2016 and decadal averages. The CREMUS fishery is dominated by inshore handline that lands coastal pelagic species, followed by purse seine, lay gill net, and seine net that lands schooling and coastal pelagic species. Inshore handline had relatively low values for effort, participation, catch, and CPUE in v Annual SAFE Report for the Hawaii Archipelago FEP Table of Contents 2017. Purse seine also showed a general decrease in the monitored parameters. In contrast, lay gill net had an increase in catch and CPUE in comparison with short- and long-term averages, while effort and participation were slightly lower. Seine net was showing an increase in effort from 2016; though catch and CPUE were on par with short-term averages, they were much less than the values noted for long-term averages an increase in catch and CPUE. The last major gear used was the spear that showed a general decline in 2017 for all monitored parameters. In 2017, the crustacean fishery showed an overall decline. Considering the crustacean management unit species evaluated, participation and catch in the fishery for deep water shrimp (Heterocarpus laevigatus) were not disclosed due to data confidentiality despite having shown an increase in catch and CPUE last year. Kona crab and lobsters statistics were all down in 2017. Monitoring for invertebrate fisheries for mollusks and limu was generally focused on hand harvest, spear, and inshore handline. Hand picking for invertebrates showed a general decline for opihi and opihi’alina, with an increase for lime kohu. Spearing ftor day octopus had an increase in effort, participation, catch, and CPUE from last year, though CPUE was on par with short- and long-term averages. Other octopus landed using the inshorfe handline also showed an increase in CPUE despite the overall decline in effort, participation, and catch values. a Ecosystem considerations were added to the annual SAFE report following the Council’s review of its fishery ecosystem plans and revised management objectives. Fishery independent ecosystem survey data, human dimensions, protected species, climate and oceanographic, r essential fish habitat, and marine planning information are included in the ecosystem considerations section. D Fishery independent ecosystem survey data was acquired through visual surveys conducted in Main Hawaiian Islands (MHI), Northwest Hawaiian Islands (NWHI), American Samoa, Pacific Remote Island Area, Commonwealth of Northern Mariana Islands, and Guam. This report illustrates the mean fish biomass for the reef areas within these locations. Additionally, the mean reef fish biomass and mean size of fishes (>10 cm) for the MHI and NWHI are presented by sampling year and reef area. Finally, the reef fish population estimates for each study site within MHI and NWHI are provided for hardbottom habitat (0-30 m). This year for the Main Hawaiian Islands, a section was added showing life history parameters for a handful of species of both coral reef fish and bottomfish. These parameters include maximum age, asymptotic length, growth coefficient, hypothetical age at length zero, natural mortality, age at 50% maturity, age at sex switching, length at which 50% of a fish species are capable of spawning, and length of sex switching are provided The socioeconomics section outlines the pertinent economic, social, and community information available for assessing the successes and impacts of management measures or the achievements of the Fishery Ecosystem Plan for the Hawaiian Archipelago. It meets the objective “Support Fishing Communities” adopted at the 165th Council meeting; specifically, it identifies the various social and economic groups within the region’s fishing communities and their interconnections. The section begins with an overview of the socioeconomic context for the region, and then provides a summary of relevant studies and data for Hawaii, followed by summaries of relevant studies and data for each fishery within the Main Hawaiian Islands, and concludes with relevant vi Annual SAFE Report for the Hawaii Archipelago FEP Table of Contents socioeconomic data trends including commercial pounds sold, revenues, and prices. There were no new data reported for neither the crustacean nor the precious coral fisheries in the Main Hawaiian Islands. Considering the Hawaiian bottomfish fishery, the price for bottomfish management unit species stayed relatively stable at approximately $6/lb. in 2017 ($7.41/lb. for Deep-7; $4.03/lb. for non-Deep-7), while the most recently calculated average cost of a bottomfish trip was approximately $253. For the coral reef fishery in the area, the price of coral reel management unit species also remained relatively steady at $3.63/lb. in 2017, while the average cost of a spearfishing trip was notably cheaper than bottomfishing in the Main Hawaiian Islands at $159. The protected species section of this report summarizes information and monitors protected species interactions in fisheries managed under the Hawaii FEP. These fisheries generally have limited impacts to protected species, and currently do not have federal observer coverage. Consequently, this report tracks fishing effort and other characteristics to detect potential changes to the level of impacts to protected species. Fishery pertformance data contained in this report indicate that there have been no notable changes in the fisheries that would affect the f potential for interactions with protected species, and there is no other information to indicate that impacts to protected species have changed in recent years. a The climate change section of this report includes indicators of current and changing climate and related oceanic conditions in the geographic areas for which the Western Pacific Regional Fishery Management Council has responsibility. In developing this section, the Council relied on r a number of recent reports conducted in the context of the U.S. National Climate Assessment including, most notably, the 2012 Pacific Islands Regional Climate Assessment and the Ocean and Coasts chapter of the 2014 repoDrt on a Pilot Indicator System prepared by the National Climate Assessment and Development Advisory Committee. The primary goal for selecting the indicators used in this report is to provide fisheries-related communities, resource managers, and businesses with climate-related situational awareness. In this context, indicators were selected to be fisheries relevant and informative, build intuition about current conditions in light of changing climate, as well as provide historical context and recognize patterns and trends. The atmospheric concentration of carbon dioxide (CO ) trend is increasing exponentially with the time series 2 maximum at 406.53 ppm. The oceanic pH at Station Aloha, in Hawaii has shown a significant linear decrease of -0.0386 pH units, or roughly a 9% increase in acidity ([H+]) since 1989. The year 2017 had relatively low temperature anomalies, with values not surpassing two degree heating weeks in area surrounding the Main Hawaiian Islands. The East Pacific hurricane season saw 18 named storms in 2017, nine of which were hurricanes and four major. The north central Pacific, conversely, had no storms over the course of 2017. This year, the climate change section was updated with information on storm-force winds as well as an additional indicator for precipitation. The essential fish habitat (EFH) review section of this report is required by the Hawaii Archipelago FEP and National Standard 2 guidelines, and includes cumulative impacts on essential fish habitat in the U.S. Western Pacific region. The National Standard 2 guidelines also require a report on the condition of the habitat. In the essential fish habitat review section of 2017 annual SAFE report, a literature review of the life history and habitat requirements for each life stage of four reef-associated crustaceans species regularly landed in U.S. Western Pacific commercial fisheries was presented. This review included information on two species of spiny vii Annual SAFE Report for the Hawaii Archipelago FEP Table of Contents lobster, (Panulirus marginatus and Scyllarides squammosus), scaly slipper lobster (Scyllarides squammosus), and Kona crab (Ranina ranina). The most up to date information on species distribution, fisheries status, and life history are summarized. This section is also meant to address any Council directives toward its Plan Team; however, there were no Plan Team directives in 2017. The marine planning section of this report tracks activities with multi-year planning horizons and begins to track the cumulative impact of established facilities. Development of the report in later years will focus on identifying appropriate data streams. In the Hawaii Archipelago, alternative energy development and military activities are those with the highest potential fisheries impact. The Bureau of Ocean Energy Management received four nominations of commercial interest for its Call Areas northwest and south of Oahu, all of which are in the area identification and environmental assessment stage of the leasing process. The Department of Defense is released a draft environmental impact statement regarding activities entitled “Hawaii-Southern California Training and Testing” in October 2017; these activities will liketly impact fishing access and fish habitat. f The data integration chapter of this report is still under development. The Council hosted a Data a Integration Workshop in late 2016 with a goal of identifying policy-relevant fishery ecosystem relationships. The archipelagic data integration chapter currently explores the potential association between fishery parameters and precipitation, primary productivity, and temperature- derived variables. A contractor has recently completed these analyses, and intial results of r exploratory analyses are included for the first time in 2017. The commercial coral reef fisheries of the Main Hawaiian Islands generally showed weak associations with the environmental parameters evaluated. No connectioDn was discovered between sum of the coral reef fisheries in the region with sea surface temperature, though the weke (i.e. goatfish of the family Mullidae) taxa group had a positively-significant statistical relationship with the variable. No general associations were discovered between precipitation and akule or opelu. Lastly, the relationship between the sum of the commercial reef fisheries in the Main Hawaiian Islands and the concentration of fluorometric chlorophyll-a integrated over the top 200 meters of the water column was determined to be statistically significant in a negative fashion. In line with these results, the taape taxa group showed the strongest significant relationship with the same environmental variable, also negative. A non-metric multidimensional scaling analysis showed that, while the evaluation was not able to identify any significant levels of association between expanded creel catch data and a swath of environmental parameters, the first axis, responsible for explaining 94% of the variance, showed the strongest relationships with salinity (negative) and pH (positive). In continuing forward with associated analyses and presentation of results for the data integration chapter, the Plan Team suggested several improvements to implement in the coming year: standardizing and correcting values in CPUE time series, incorporating longer stretches of phase lag, completing comparisons on the species-level and by dominant gear types, incorporating local knowledge on shifts in fishing dynamics over the course of the time series, and utilizing the exact environmental data sets presented in the ecosystem consideration chapter of the annual report. Implementation of these suggestions will allow for the preparation of a more finalized version of the data integration chapter in the coming year. viii Annual SAFE Report for the Hawaii Archipelago FEP Table of Contents The 2018 Archipelagic Plan Team had the following recommendations with respect to this report: Regarding the monitoring of the management unit species, the Archipelagic Plan Team recommends the Council to direct staff to work with the Territory fishery agencies to identify and resolve issues with regards to real-time accurate reporting, such as regulatory gaps, and potential solutions, such as mandatory licensing and reporting (e.g. log books). Regarding the development and improvement of data collection systems in the short term, the Archipelagic Plan Team recommends the Council to support these processes by exploring the options of: a dedicated port sampler to conduct a full census of the bottomfish catch, the improvement and expansion of Commercial Receipt Books, and improvements in the timeliness of the data transcription. Regarding the carry-over provision of the 2016 National Standatrd 1, the Archipelagic Plan Team recommends the Council direct staff to explore the application of the carry-over provision in the Council’s control rules. f Regarding the evaluation 2017 catch relative to 2017a ACLs, the Archipelagic Plan Team recommends retaining the ACL at 60 lbs. for CNMI slipper lobster. The CNMI slipper lobsters recent three-year average of catch amounting to 130 lbs. exceeded its ACL of 60 lbs. The slipper lobster fishery is tracked through the Commercial Receipt Books. The increase in catch can likely be attributed to the implementation rof the Territory Science Initiative, designed to improve the data submitted to the Commercial Receipt Books. In 2017, seven invoices and five fishermen reported the sale of slipper lobsters,D which were zeroes in years prior to 2016. Regarding the improvement of identifying precious coral essential fish habitat, the Archipelagic Plan Team endorses the Plan Team Precious Coral Working Group Report, and they recommend that the Council direct staff to develop an analysis of options to redefine EFH/HAPC for Council consideration for an FEP amendment. Regarding the research priorities, the Archipelagic Plan Team adopts the changes proposed by the Social Science Planning Committee to the Human Communities section of the Council’s MSRA five-year research priorities. ix Annual SAFE Report for the Hawaii Archipelago FEP Table of Contents Table of Contents Executive Summary ...................................................................................................................v Acronyms and Abbreviations ..................................................................................................xx 1 FISHERY PERFORMANCE ............................................ Error! Bookmark not defined. 1.1 Deep-7 BMUS ................................................................................................... 24 1.1.1 Fishery Descriptions .......................................................................................... 24 1.1.2 Data Collection Systems .................................................................................... 24 1.1.3 Time Series Statistics ......................................................................................... 26 1.1.4 Top 4 Species per Gear Type ............................................................................. 28 1.1.5 Catch Parameters by Gear.................................................................................. 33 1.2 Non Deep-7 BMUS ........................................................................................... 36 1.2.1 Fishery Descriptions .......................................................................................... 36 t 1.2.2 Dashboard Statistics ........................................................................................... 36 1.2.3 Time Series Statistics ...............................f.......................................................... 37 1.2.4 Top Two Species per Gear Type ....................................................................... 39 1.2.5 Catch Parameters by Gear...............a................................................................... 44 1.3 CREMUS Finfish ............................................................................................... 48 1.3.1 Fishery Descriptions .......................................................................................... 48 1.3.2 Dashboard Statistics ........................................................................................... 48 r 1.3.3 Time Series Statistics ......................................................................................... 50 1.3.4 Top 4 Species per Gear Type ............................................................................. 51 D 1.3.5 Catch Parameters by Gear.................................................................................. 60 1.4 Crustacean .......................................................................................................... 65 1.4.1 Fishery Descriptions .......................................................................................... 66 1.4.2 Dashboard Statistics ........................................................................................... 66 1.4.3 Time Series Statistics ......................................................................................... 67 1.4.4 Top 4 Species per Gear Type ............................................................................. 68 1.4.5 Catch Parameters by Gear.................................................................................. 76 1.5 Mollusk and Limu .............................................................................................. 79 1.5.1 Fishery Descriptions .......................................................................................... 79 1.5.2 Dashboard Statistics ........................................................................................... 79 1.5.3 Time Series Statistics ......................................................................................... 80 1.5.4 Top Four Species per Gear Type ....................................................................... 81 1.5.5 Catch Parameters by Gear.................................................................................. 87 1.6 Precious Corals Fishery ..................................................................................... 89 1.6.1 Fishery Descriptions .......................................................................................... 89 1.6.2 Dashboard Statistics ........................................................................................... 89 1.6.3 Other Statistics ................................................................................................... 89 1.7 Hawaii Marine Recreational Fishing survey ..................................................... 90 1.7.1 Fishery Descriptions .......................................................................................... 90 1.7.2 Non-Commercial Data Collection Systems ....................................................... 90 1.8 Administrative and regulatory actions ................ Error! Bookmark not defined. x