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DTIC ADA570875: Open-Ocean Movements of a Satellite-Tagged Blainville's Beaked Whale (Mesoplodon densirostris): Evidence for an Offshore Population in Hawaii? PDF

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Aquatic Mammals 2011, 37(4), 506-511, DOI 10.1578/AM.37.4.2011.506 Short Note Open-Ocean Movements of a Satellite-Tagged Blainville’s Beaked Whale (Mesoplodon densirostris): Evidence for an Offshore Population in Hawai‘i? Robin W. Baird,1 Gregory S. Schorr,1 Daniel L. Webster,1 Sabre D. Mahaffy,1 Daniel J. McSweeney,2 M. Bradley Hanson,3 and Russel D. Andrews4 1Cascadia Research Collective, 218½ W. 4th Avenue, Olympia, WA 98501, USA E-mail: [email protected] 2Wild Whale Research Foundation, Box 139, Holualoa, HI 96725, USA 3NOAA Northwest Fisheries Science Center, 2725 Montlake Boulevard E, Seattle, WA 98112, USA 4School of Fisheries and Ocean Sciences, University of Alaska Fairbanks, and Alaska SeaLife Center, 301 Railway Avenue, Seward, AK 99664, USA In Hawaiian waters, a single stock of Blainville’s (Schorr et al., 2009). Combined with long-term beaked whale (Mesoplodon densirostris) is recog- resightings of distinctive individuals off the island nized, extending throughout the U.S. Exclusive (McSweeney et al., 2007), such results suggest the Economic Zone (EEZ) surrounding the archi- existence of an island-resident population. Mark- pelago and into adjacent international waters recapture population estimates based on photo- (Carretta et al., 2011). Abundance within the identification data suggest this island-resident entire EEZ around Hawai‘i was estimated at population is quite small, with approximately 140 2,872 individuals based on a large vessel sight- individual Blainville’s beaked whales (CV = 0.30) ing survey (Barlow, 2006), with a single on-effort using the area off the island of Hawai‘i over a 4-y sighting near the western boundary of the EEZ period (Baird et al., 2009b). (Hamilton et al., 2009). There is, however, con- While Blainville’s beaked whales are gener- siderable uncertainty associated with this estimate ally thought to be distributed throughout tropical (CV = 1.17; Barlow, 2006), and there is recent oceanic waters (Jefferson et al., 2008), research evidence that individuals documented around efforts to examine movements and spatial use the main Hawaiian Islands may not be part of an have focused on studies of animals around oceanic open-ocean population (McSweeney et al., 2007; islands (Claridge, 2004; Schorr et al., 2009; Tyack Schorr et al., 2009). Individual Blainville’s beaked et al., 2011). Nothing is known of the movements whales instrumented with satellite tags off the or habitat use of individual Blainville’s beaked island of Hawai‘i have remained strongly associ- whales in the open ocean, away from island habitats. ated with the island, primarily using slope habi- In Hawaiian waters, there have been few sightings tats for the entire duration of satellite tag trans- of Blainville’s beaked whales in the open ocean missions (up to 71 d; Schorr et al., 2009). Schorr (Carretta et al., 2011), and thus limited opportuni- et al. (2009) noted a mean distance from shore of ties to study this species in such habitats. Here, we 16.9 km (range 4.4 to 27.7 km) and a mean depth report on the movements of a Blainville’s beaked of 1,156 m (range 880 to 1,455 m) for six satel- whale satellite tagged off the island of Hawai‘i lite tagged individuals, over periods ranging from but thought to be from an open-ocean population, 15 to 71 d (median = 43 d), with from 26 to 405 rather than the resident island-associated popula- locations per individual (median = 195 locations/ tion. Using photo-identification data on this spe- individual). Although these individuals moved cies in the area since 1986 (McSweeney et al., a cumulative distance of at least 8,000 km over 2007) and sighting information from our study of the duration of their tag attachments, median odontocetes off the island since 2002 (Baird et al., distances of locations from the tagging location 2008, 2009a), we compare sighting characteristics for the different individuals ranged from 19.9 to and photo-identification results from the tagged 91.8 km, and the maximum distance any individual group with other sightings of Blainville’s beaked moved from where it was tagged was only 139 km Report Documentation Page Form Approved OMB No. 0704-0188 Public reporting burden for the collection of information is estimated to average 1 hour per response, including the time for reviewing instructions, searching existing data sources, gathering and maintaining the data needed, and completing and reviewing the collection of information. Send comments regarding this burden estimate or any other aspect of this collection of information, including suggestions for reducing this burden, to Washington Headquarters Services, Directorate for Information Operations and Reports, 1215 Jefferson Davis Highway, Suite 1204, Arlington VA 22202-4302. Respondents should be aware that notwithstanding any other provision of law, no person shall be subject to a penalty for failing to comply with a collection of information if it does not display a currently valid OMB control number. 1. REPORT DATE 3. DATES COVERED 2011 2. REPORT TYPE 00-00-2011 to 00-00-2011 4. TITLE AND SUBTITLE 5a. CONTRACT NUMBER Open-Ocean Movements of a Satellite-Tagged Blainville’s Beaked Whale 5b. GRANT NUMBER (Mesoplodon densirostris): Evidence for an Offshore Population in Hawai’i? 5c. PROGRAM ELEMENT NUMBER 6. AUTHOR(S) 5d. PROJECT NUMBER 5e. TASK NUMBER 5f. WORK UNIT NUMBER 7. PERFORMING ORGANIZATION NAME(S) AND ADDRESS(ES) 8. PERFORMING ORGANIZATION Cascadia Research Collective,218 1/2 W. 4th Avenue,Olympia,WA,98501 REPORT NUMBER 9. SPONSORING/MONITORING AGENCY NAME(S) AND ADDRESS(ES) 10. SPONSOR/MONITOR’S ACRONYM(S) 11. SPONSOR/MONITOR’S REPORT NUMBER(S) 12. DISTRIBUTION/AVAILABILITY STATEMENT Approved for public release; distribution unlimited 13. SUPPLEMENTARY NOTES 14. ABSTRACT 15. SUBJECT TERMS 16. SECURITY CLASSIFICATION OF: 17. LIMITATION OF 18. NUMBER 19a. NAME OF ABSTRACT OF PAGES RESPONSIBLE PERSON a. REPORT b. ABSTRACT c. THIS PAGE Same as 6 unclassified unclassified unclassified Report (SAR) Standard Form 298 (Rev. 8-98) Prescribed by ANSI Std Z39-18 Beaked Whale Open -Ocean Movements 507 whales and discuss the management implications side of the island of Hawai‘i (19.24° N, of our results. 156.18° W). This was the second deepest group The tag used was a location-only LIMPET sat- and fourth farthest from shore of the 29 groups ellite tag (see Andrews et al., 2008; Schorr et al., documented. A LIMPET tag was attached to 2009). Details of the tag configuration and deploy- the dorsal fin of one individual, identified as an ment system, as well as data processing, can be adult male based on the presence of erupted teeth. found in Andrews et al. (2008) and Schorr et al. Reaction to tagging consisted of a fast dive, while (2009), so they are only briefly mentioned here. none of the other individuals in the group reacted. The tag was set up to transmit 10 h/d during peri- Both left and right sides of all three individuals in ods that corresponded to the highest density of sat- the group encountered 29 April 2009 were well- ellite overpasses, with a limit of 300 transmissions photographed, and all three were distinctive, with per day. These 10 h of on-time were in four blocks numerous scars to allow for long-term individual ranging from 2 to 3 h in duration, with intervals of identification. Photos of all three were compared to 2 to 5 h in between transmission periods. Satellite a catalog of 115 distinctive individual Blainville’s locations were assessed for plausibility with the beaked whales that had been documented around Douglas Argos-filter, Version 7.06 (available at the main Hawaiian Islands (see McSweeney Alaska.usgs.gov/science/biology/spatial/douglas. et al., 2007). Neither the tagged individual, des- html). Horizontal rate of movement calculations ignated HIMd153 in our catalog, nor the other were restricted to pairs of locations from 4 to two individuals present (HIMd152 and HIMd154 24 h apart for comparison with analyses of Schorr in our catalog), had been previously documented et al. (2009). Depths and distances from shore photographically. of sightings and filtered satellite locations were Five of the 27 sightings with photo-identified determined using ArcGIS, Version 9.2 (ESRI, individuals (including the 29 April 2009 group) Redlands, CA, USA). Filtered locations were were either in depths > 2,100 m or at distances plotted in conjunction with offshore eddy sys- > 35 km from shore, and none of the photo-iden- tems using output from the Archiving, Validation, tified individuals from these groups were docu- and Interpretation of Satellite Oceanographic mented on more than one occasion (i.e., they had (AVISO) data (see www.aviso.oceanobs.com/en/ not been seen prior to or since these encounters). data/products/sea-surface-height-products/global/ Only one of the 22 sightings in less than 2,100 m index.html). AVISO data were available as weekly depth and within 35 km of shore was entirely com- means of sea surface height (SSH) at 0.25° × 0.25° posed of photo-identified individuals that had not resolution and geostrophic currents at 0.5° × 0.5° been seen on more than one occasion (i.e., did not resolution. link by association to the known resident island- Blainville’s beaked whales were encountered associated population). The high proportion of on 29 occasions during directed research sur- groups (21 of 22) documented in < 2,100 m and veys off the island of Hawai‘i from 2002 through within 35 km of shore that match the resident 2010 (see Baird et al., 2008, 2009a for methods). social network, and the lack of such matches for Sighting water depths ranged from 360 to 3,903 m the five groups documented in deeper water or (mean = 1,438 m, SD = 911 m), while distance farther from shore, suggests that individuals docu- from shore ranged from 2.1 to 48.9 km (mean = mented in very deep water or very far offshore are 11.3 km, SD = 11.9 km). Identification photos more likely to be from an open-ocean population. were available from 27 of the 29 encounters. Locations from HIMd153 were received over From these there were 92 identifications of 52 a 40-d span. After filtering, there were 109 loca- distinctive individuals, 19 of which were seen on tions on 37 different days. The distribution of more than one occasion. Of these 27 encounters, location classes (LC, an indicator of the loca- individuals from 21 of these link by association tion accuracy and number of messages received in a single social network (not shown), including by the satellite during the overpass) was similar the previously satellite tagged individuals studied (LC3 – 2.75%; LC2 – 9.17%; LC1 – 22.02%; by Schorr et al. (2009). Some of these individu- LC0 – 44.04%; LCA – 11.01%; LCB – 10.09%; als have been resighted in the area over periods of LCZ – 0.92%) to Schorr et al. (2009). The inter- up to 17 y (McSweeney et al., 2007), suggesting val between consecutive locations ranged from they are long-term residents and strongly associ- 0.38 to 36.43 h (median = 6.55 h). Over the 40 d, ated with the island. All 21 of these encounters HIMd153 moved a cumulative minimum distance that were linked by association were in depths of of 1,801 km and traveled 1,008 km from the site < 2,100 m and within 32 km of shore. of tagging (Figures 1 & 2). While covering similar On 29 April 2009, a group of three Blainville’s or greater cumulative distances, satellite-tagged beaked whales was encountered in 3,812 m water individuals from the island-associated population depth 32.3 km from shore, off the southwestern (Schorr et al., 2009) remained relatively close to 5 08 Baird et al. Figure 1. Map showing movements of HIMd153 over the 40 d of signals from the tag 1200(cid:1) m) HIMd153(cid:1) n (k 1000(cid:1) HIMd148(cid:1) o ocati 800(cid:1) HIMd025(cid:1) g l n ggi 600(cid:1) a m t e fro 400(cid:1) c n sta 200(cid:1) Di 0(cid:1) 0(cid:1) 5(cid:1) 10(cid:1) 15(cid:1) 20(cid:1) 25(cid:1) 30(cid:1) 35(cid:1) 40(cid:1) Days since tagging(cid:1) Figure 2. Distance from tagging location over time for HIMd153 and the two individuals from the island-associated population (HIMd148 and HIMd025) that had the greatest average distance from tagging locations (see Schorr et al., 2009) the sites of tagging (Figure 2). The horizontal rate 2 wks were associated with the northern edges of of movement calculated using all pairs of consecu- two cyclonic eddies, possibly moving with the tive locations obtained from 4 to 24 h apart ranged currents, although movements in the latter half from 0.17 to 8.51 km h-1 (median = 1.575 km h-1); of the track were not associated with any strong however, there was a significant negative relation- oceanographic features visible in AVISO SSH and ship between the rate of movement and the time current data (Figure 3). since tagging (regression, r2 = 0.118, p = 0.005). HIMd153 utilized depths ranging from 3,150 During the first 20 d, while the whale generally to 4,946 m (median depth = 4,702 m), on aver- travelled away from the island, the median hori- age using water four times deeper than individuals zontal rate of movement was 2.41 km h-1; while from the island resident population (Schorr et al., during the last 20 d, when the whale used a broad 2009). After the 4th d post-tagging, there were area located 900 to 1,000 km from the tagging loca- no depths associated with satellite-derived loca- tion, it was 0.99 km h-1. By comparison, the grand tions shallower than 3,500 m. The distance from mean of the median rates of horizontal movement the closest point of land in the main Hawaiian from the six groups of Blainville’s beaked whales Islands ranged from 17.6 to 573.0 km (median previously satellite tagged was 1.16 km h-1 (Schorr = 282.6 km). When the tag stopped transmitting, et al., 2009). Many of the locations during the first HIMd153 was still inside the U.S. EEZ surrounding Beaked Whale Open -Ocean Movements 509 the Hawaiian Islands, but only 60.9 km from the and reactions of beaked whales to naval sonar EEZ boundary (Figure 1). exercises. Individuals of several species of beaked Based on the depth and distance that HIMd153 whales, including Blainville’s beaked whales, was encountered from shore and the lack of any have died in association with mid-frequency link by association to the island-resident social active sonar use (Balcomb & Claridge, 2001; network, we believe this individual was not part Jepson et al., 2003; Fernandez et al., 2005). Such of the island-associated population of Blainville’s mortalities are thought to occur due to changes in beaked whales, but, rather, from an open-ocean diving behavior leading to decompression sick- population. The spatial use patterns and depths ness (Jepson et al., 2003; Fernandez et al., 2005; used by this individual differed dramatically from Cox et al., 2006; Hooker et al., 2009). The history previous Blainville’s beaked whales tagged in of prior exposure of individuals may be important Hawai‘i, moving over 900 km from where it was in understanding their responses to mid-frequency tagged in just 20 d and traveling over depths of up sonar since naïve individuals would potentially to almost 5,000 m. Although the tagged whale did show strong behavioral responses, while those not leave the EEZ in the 40 d we received loca- exposed to mid-frequency sonar on a regular basis tions from the tag, the broad ranging movements may habituate to some degree (Falcone et al., and proximity to the EEZ boundary suggest that 2009). Movement patterns of HIMd153 suggest Blainville’s beaked whales in offshore waters sur- that individuals from an open-ocean population rounding the Hawaiian Islands are likely part of a are much less likely to be regularly exposed to larger oceanic population that uses both U.S. and mid-frequency sonar use from naval exercises that international waters. Combined with the evidence typically occur in closer proximity to the islands of an island-resident population (McSweeney (Anonymous, 2008). Since open-ocean animals et al., 2007; Schorr et al., 2009), it appears that, may be naïve to sonar exposure, their reactions like many other species of odontocetes in Hawaiian and potential impacts may differ from those that waters (Chivers et al., 2007, 2010; Baird et al., have been exposed on multiple occasions through- 2008, 2009a; Andrews et al., 2010; Aschettino out their lives. et al., 2011), there is more than one population of Blainville’s beaked whale in Hawaiian waters. As well as their relevance for population struc- ture, our results have implications for exposure Figure 3. Track of the Blainville’s beaked whale tagged 29 April 2009 with sea surface height (SSH) (color) and surface cur- rents (vectors); locations during periods when SSH and current data are available are indicated by symbols: circles represent locations following intervals of > 4 h with shading indicating speed over the track from the previous location, and squares represent locations < 4 h from the prior location with no speed indicated (see text). SSH and current data are shown (in panels of varying widths depending on the distance moved, labeled in upper left of each panel) for the weeks of (a) 1 June 2009, (b) 18 May 2009, (c) 11 May 2009, (d) 4 May 2009, and (e) 27 April 2009 (from left to right). The trackline for the week of 25 May 2009 is shown, but no locations are indicated. 5 10 Baird et al. Acknowledgments patterns. Marine Mammal Science, 24, 591-612. http:// dx.doi.10.1111/j.1748-7692.2008.00200.x This research was funded primarily by the Baird, R. W., McSweeney, D. J., Schorr, G. S., Mahaffy, U.S. Navy (N45) via a contract from the Southwest S. D., Webster, D. L., Barlow, J., . . . Andrews, R. D. Fisheries Science Center; we thank Jay Barlow for (2009b). Studies of beaked whales in Hawai‘i: administering the contract funds. Improvements Population size, movements, trophic ecology, social to the tagging methods were funded by Office organization and behaviour. European Cetacean Society, of Naval Research Grant N000140811203. Special Publication 51, 23-25. Additional funds for fieldwork were provided Balcomb, K. C., & Claridge, D. E. (2001). A mass strand- by the Scripps Institution of Oceanography and ing of cetaceans caused by naval sonar in the Bahamas. the Alaska SeaLife Center. We thank Phoebe Bahamas Journal of Science, 5, 1-12. Woodworth from the Pacific Islands Fisheries Barlow, J. (2006). Cetacean abundance in Hawaiian waters Science Center for producing Figure 3, Damon estimated from a summer/fall survey in 2002. Marine Holzer of the Northwest Fisheries Science Center Mammal Science, 22, 446-464. http://dx.doi.10.1111/ for GIS analyses, and two anonymous review- j.1748-7692.2006.00032.x ers for their comments. Tagging was undertaken Carretta, J. V., Forney, K. A., Oleson, E., Martien, K., Muto, under NMFS Scientific Research Permit No. 731- M. M., Lowry, M. S., . . . Hill, M. C. (2011). U.S. Pacific 1774. marine mammal stock assessments: 2010 (NOAA- TM-NMFS-SWFSC-476). Washington, DC: National Literature Cited Oceanic and Atmospheric Administration. Chivers, S. J., Baird, R. W., McSweeney, D. J., Webster, Andrews, K. R., Karczmarski, L., Au, W. W. L., Rickards, D. L., Hedrick, N. M., & Salinas, J. C. (2007). Genetic S. H., Vanderlip, C. A., Bowen, B. W., . . . Toonen, variation and evidence for population structure in east- R. J. (2010). Rolling stones and stable homes: Social ern North Pacific false killer whales (Pseudorca crassi- structure, habitat diversity and population genetics of dens). Canadian Journal of Zoology, 85, 783-794. http:// the Hawaiian spinner dolphin (Stenella longirostris). dx.doi.10.1139/Z07-059 Molecular Ecology, 19, 732-748. http://dx.doi.10.1111/ Chivers, S. J., Baird, R. W., Martien, K. M., Taylor, j.1365-294X.2010.04521.x B. L., Archer, E., Gorgone, A. M., . . . Webster, D. L. Andrews, R. D., Pitman, R. L., & Balance, L. T. (2008). (2010). Evidence of genetic differentiation for Hawai‘i Satellite tracking reveals distinct movement patterns for insular false killer whales (Pseudorca crassidens) Type B and Type C killer whales in the southern Ross (NOAA Technical Memorandum NMFS-SWFSC-458). Sea, Antarctica. Polar Biology, 31, 1461-1468. http:// Washington, DC: National Oceanic and Atmospheric dx.doi.10.1007/s00300-008-0487-z Administration. Anonymous. (2008). Hawaii range complex final environ- Claridge, D. E. (2004). Fine-scale distribution and habitat mental impact statement/overseas environmental impact selection of beaked whales (M.Sc. thesis). University of statement. Washington, DC: U.S. Department of the Aberdeen, Aberdeen, Scotland. Navy. Retrieved September 14, 2011, from www.gov- Cox, T. M., Ragen, T. J., Read, A. J., Vos, E., Baird, R. W., support.us/navynepahawaii/Docs/Final/Vol%201/cover- Balcomb, K., . . . Benner, L. (2006). Understanding exec-ch1-ch2_HRC_FEIS-OEIS_VOL1_May08.pdf. the impacts of anthropogenic sound on beaked whales. Aschettino, J. M., Baird, R. W., McSweeney, D. J., Webster, Journal of Cetacean Research and Management, 7, 177- D. L., Schorr, G. S., Huggins, J. L., . . . West, K. L. 187. (2011). Population structure of melon-headed whales Falcone, E. A., Schorr, G. S., Douglas, A. B., Calambokidis, (Peponocephala electra) in the Hawaiian Archipelago: J., Henderson, E., McKenna, M. F., . . . Moretti, D. Evidence of multiple populations based on photo-iden- (2009). Sighting characteristics and photo-identification tification. Marine Mammal Science [Online]. http:// of Cuvier’s beaked whales (Ziphius cavirostris) near dx.doi. 10.1111/j.1748-7692.2011.00517.x San Clemente Island, California: A key area for beaked Baird, R. W., Gorgone, A. M., McSweeney, D. J., Ligon, whales and the military? Marine Biology, 156, 2631- A. D., Deakos, M. H., Webster, D. L., . . . Mahaffy, S. D. 2640. http://dx.doi.10.1007/s00227-009-1289-8 (2009a). Population structure of island-associated dol- Fernández, A., Edwards, J. F., Rodrígues, F., Espinosa de phins: Evidence from photo-identification of common los Monteros, A., Herráez, P., Castro, P., . . . Arbelo, M. bottlenose dolphins (Tursiops truncatus) in the main (2005). “Gas and fat embolic syndrome” involving a mass Hawaiian Islands. Marine Mammal Science, 25, 251- stranding of beaked whales (Family Ziphiidae) exposed 274. http://dx.doi.10.1111/j.1748-7692.2008.00257.x to anthropogenic sonar signals. Veterinary Pathology, 42, Baird, R. W., Gorgone, A. M., McSweeney, D. J., Webster, 446-457. http://dx.doi.10.1354/vp.42-4-446 D. L., Salden, D. R., Deakos, M. H., . . . Mahaffy, Hamilton, T. A., Redfern, J. V., Barlow, J., Ballance, L. T., S. D. (2008). False killer whales (Pseudorca crassi- Gerrodette, T., Holt, R. S., . . . Taylor, B. L. (2009). Atlas dens) around the main Hawaiian Islands: Long-term of cetacean sightings for Southwest Fisheries Science site fidelity, inter-island movements, and association Center cetacean and ecosystem surveys: 1986-2005 Beaked Whale Open -Ocean Movements 511 (NOAA-TM-NMFS-SWFSC-440). Washington, DC: National Oceanic and Atmospheric Administration. Hooker, S. K., Baird, R. W., & Fahlman, A. (2009). Could beaked whales get the bends? Effects of diving behav- iour and physiology on modelled gas exchange for three species: Ziphius cavirostris, Mesoplodon densirostris and Hyperoodon ampullatus. Respiratory Physiology & Neurobiology, 167, 235-246. http://dx.doi.10.1016.j. resp.2009.04.023 Jefferson, T. A., Webber, M. A., & Pitman, R. L. (2008). Marine mammals of the world: A comprehensive guide to their identification. San Diego: Academic Press. Jepson, P. D., Arbelo, M., Deaville, R., Patterson, I. A. P., Castro, P., Baker, J. R., . . . Fernández, A. (2003). Gas- bubble lesions in stranded cetaceans: Was sonar respon- sible for a spate of whale deaths after an Atlantic mili- tary exercise? Nature (London), 425, 575-576. http:// dx.doi.10.1038/425575a McSweeney, D. J., Baird, R. W., & Mahaffy, S. D. (2007). Site fidelity, associations and movements of Cuvier’s (Ziphius cavirostris) and Blainville’s (Mesoplodon den- sirostris) beaked whales off the island of Hawai‘i. Marine Mammal Science, 23, 666-687. http://dx.doi.10.1111/ j.1748-7692.2007.00135.x Schorr, G. S., Baird, R. W., Hanson, M. B., Webster, D. L., McSweeney, D. J., & Andrews, R. D. (2009). Movements of satellite-tagged Blainville’s beaked whales off the island of Hawai‘i. Endangered Species Research, 10, 203-213. http://dx.doi.10.3354/esr00229 Tyack, P. L., Zimmer, W. M. X., Moretti, D., Southall, B. L., Claridge, D. E., Durban, J. W., . . . Boyd, I. L. (2011). Beaked whales respond to simulated and actual Navy sonar. PLoS ONE, 6(3), e17009. http://dx.doi.10.1371/ journal.pone.0017009

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