Blue Whale (Balaenoptera Musculus) 5-Year Review

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Blue Whale (Balaenoptera Musculus) 5-Year Review Blue Whale (Balaenoptera musculus) 5-Year Review: Summary and Evaluation Photo Credit: Peter Duley, Northeast Fisheries Science Center, NOAA Fisheries, under permit #17355. National Marine Fisheries Service Office of Protected Resources Silver Spring, MD November 2020 5-YEAR REVIEW Blue Whale (Balaenoptera musculus) 1. GENERAL INFORMATION 1.1 Reviewers Lead Regional or Headquarters Office: Heather Austin, Office of Protected Resources, 301-427-8422. Cooperating Science Center: Nancy Young, Alaska Fisheries Science Center, National Marine Mammal Laboratory, 206-526-4297. 1.2 Methodology used to complete review A 5-year review is a periodic analysis of a species’ status conducted to ensure that the listing classification of a species as threatened or endangered on the List of Endangered and Threatened Wildlife and Plants (List) (50 CFR 17.11 – 17.12) is accurate. The 5-year review is required by section 4(c)(2) of the Endangered Species Act of 1973, as amended (ESA) and was prepared pursuant to the joint National Marine Fisheries Service (NMFS) and the U.S. Fish and Wildlife 5-year Review Guidance and template (NMFS and USFWS 2006). The NMFS Office of Protected Resources led the 5-year review in collaboration with Alaska Fisheries Science Center staff and input from other NMFS regional offices and science centers. This 5-year review was accomplished through the development of the National Marine Fisheries Service (NMFS) Revised Recovery Plan for the blue whale (NMFS 2020). The Revised Recovery Plan is a revision to the 1998 Recovery Plan. We rely on the Revised Recovery Plan because it represents the best scientific and commercial data on the status and threats to the blue whale. In addition, the 1998 Recovery Plan did not contain recovery criteria. Information was updated as part of the development of the aforementioned Revised Recovery Plan, based on peer-reviewed publications, government and technical reports, conference papers, workshop reports, dissertations, and theses. We gathered information through January 2020. The information on the blue whale (Balaenoptera musculus) biology and habitat, threats, and conservation efforts was summarized and analyzed based on ESA section 4(a)(1) factors (see Section 2.0) and the recovery criteria identified in the Revised Recovery Plan to determine whether a reclassification or delisting may be warranted (see Section 3.0). 1.3 FR Notice citation announcing initiation of this review NMFS initiated a 5-year review of the blue whale on October 12, 2018 (83 FR 51665). Six public comment letters, including literature citations were received and incorporated as appropriate in this review. 2 2. REVIEW ANALYSIS 2.1 Application of the 1996 Distinct Population Segment (DPS) policy1 The ESA defines a species as including any subspecies of fish or wildlife or plants, and any DPS of any species of vertebrate fish or wildlife that interbreeds when mature. The blue whale is not currently listed as a DPS. The subspecific taxonomy is an area of continued research and is still being defined. Please refer to the NMFS Revised Recovery Plan for further information (NMFS 2020). Since the species was listed, studies of intraspecific variability and life history characteristics supports the identification of five subspecies currently recognized by the Society for Marine Mammalogy (NMFS 2020). B. m. musculus (Linnaeus, 1758) is the northern blue whale (North Atlantic and North Pacific Oceans); B. m. intermedia (Burmeister, 1871) is the Antarctic blue whale, sometimes referred to as the “true” blue whale; B. m. brevicauda (Ichihara 1966) is the pygmy blue whale, generally occurring in the sub-Antarctic southern Indian Ocean and the southwestern Pacific Ocean (Ichihara 1966; Rice 1977); B. m. indica (Blyth, 1859) is the northern Indian Ocean blue whale; and there is a recently recognized, unnamed subspecies that generally occurs off Chile and annually migrates to waters off Peru, Ecuador, and up to the Galapagos Islands (Hucke-Gaete et al. 2018) in the southeastern Pacific Ocean (Branch et al. 2007, Committee on Taxonomy 2016). 2.2 Review Summary In this section, we present new information under each of the five listing factors obtained as part of development of the Revised Recovery Plan for the blue whale (NMFS 2020). We also provide a brief summary of the Revised Recovery Plan and explain why the species meets the definition of endangered outlined in Section 3.0. Please refer to the Revised Recovery Plan (NMFS 2020) for a thorough discussion on the species status including biology, habitat, threats, and management efforts. Factor A: The present or threatened destruction, modification, or curtailment of a species’ habitat or range. No new information was found pertaining to Factor A. Factor B: Overutilization for commercial, recreational, or educational purposes. No new information was found pertaining to Factor B. 1 To be considered for listing under the ESA, a group of organisms must constitute a “species,” which is defined in section 3 of the ESA to include “any subspecies of fish or wildlife or plants, and any distinct population segment (DPS) of any species of vertebrate fish or wildlife which interbreeds when mature.” NMFS and USFWS jointly published a policy regarding the recognition of DPSs of vertebrate species under the Endangered Species Act (61 FR 4722, February 7, 1996). “DPS” is not a scientifically defined term; it is a term used in the context of ESA law and policy. Furthermore, when passing the provisions of the ESA that give us authority to list DPSs, Congress indicated that this provision should be used sparingly. We have discretion with regard to listing DPSs and, in order to be consistent with the directive of the Congressional report that followed the introduction of the DPS language in the ESA to identify DPSs sparingly, we will generally not, on our own accord, evaluate listings below the taxonomic species or subspecies level if the best available information indicates that the species or subspecies is in danger of extinction throughout all or a significant portion of its range. We should only identify DPSs if there is an overriding conservation benefit to the species. 3 Factor C: Disease or Predation. The Revised Recovery Plan for the blue whale (NMFS 2020) did not identify recovery criteria for factor C: Disease or Predation, because there were no data to indicate this factor was a potential threat to blue whale recovery. However, in this section we provide updated information from studies related to factor C. Parasites have been known to cause major health issues for a number of cetaceans and can cause severe complications to respiratory and urinary systems (Prieto et al. 2012). For example, blue whales infected with the giant nematode Crassicauda boopis suffer from chronic inflammatory reactions of the blood vessels which drain the kidneys, and can cause complete vascular occlusion and kidney failure (Lambertsen 1990). Whale calves and juveniles typically suffer the heaviest parasite burdens following transplacental infection of the developing whale fetus, with potential whale-to-whale transmission post-partum. Additionally, nutritionally stressed juveniles and newly weaned calves in particular may be vulnerable to the effects of this parasitic nematode (Lambertsen 1990). More recently, several species of helminth parasites were found to infect the gastrointestinal tract of blue whales in the Gulf of California within the Eastern North Pacific population. Records of helminth parasites were found in 100 blue whale fecal samples, collected during the winter from 1993-2014 (Flores-Cascante et al. 2019). Blue whale feces had 18.2% of adult acanthocephalans (Bolbosoma sp.) and a very high percentage of helminth egg prevalence (100%), and showed similar helminth egg intensity independent of sex, age class, reproductive status over several time scales (same day and year and between years) (Flores-Cascante et al. 2019). Additionally, Diphyllobothrium sp. eggs have been identified in blue whale feces (Flores-Cascante et al. 2019). Within the Northern Indian Ocean population, de Vos et al. (2018) revealed the presence of acanthocephalan endoparasites within the stomach and intestines of blue whales. Acanthocephalan infections have been shown to cause changes in host phenotype of other cetacean species, impacting host behavior and immunity (Gunalan et. al. 2013). This is the first record of Acanthocephala in blue whales within the Northern Indian Ocean and highlights the need for future studies on both the ecto- and endoparasitic flora and monitoring of health of blue whales in regards to management and conservation. However, parasites are not known to have any population-level effects for any blue whale population. Thus further research is required to assess whether and to what extent parasites impact blue whales. Factor D: The inadequacy of existing regulatory mechanisms. No new information was found pertaining to Factor D. Factor E: Other natural or manmade factors affecting its continued existence. x Ship strikes have been evaluated, and, if determined by NMFS to be impeding blue whale recovery, measures have been taken to minimize effects. Following this evaluation and where effects to specific management units are known, management unit specific measures have been taken to minimize effects. (Potential threat discussed in Recovery Plan section H.1.2). x Entanglement with fishing gear has been evaluated, and, if determined by NMFS to be impeding blue whale recovery, measures have been taken to minimize effects. Following this evaluation and where effects to specific management units are known, management 4 unit specific measures have been taken to minimize effects. (Potential threat discussed in Recovery Plan section H.1.3). Ship Strikes As noted in the Revised Recovery Plan for the blue whale, some blue whale populations are likely more vulnerable than others to ship strikes, largely based on differences in distribution relative to shipping traffic (NMFS 2020). However, some blue whale populations are vulnerable to ship strikes due in large part to coastal populations which seasonally reside in feeding grounds that overlap with shipping routes, such as off southern California.
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