NEWFOUNDLAND REGION GROUNDFISH OVERVIEW

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DFO Science Stock Status Report A2-19 (1998) NEWFOUNDLAND REGION GROUNDFISH OVERVIEW Background In Newfoundland, Science Branch of the Department of Fisheries and Oceans is responsible, either directly or indirectly, for advising on the status of numerous groundfish stocks extending from Davis Strait in the north to off the south coast of Newfoundland in the south. In this area, there are 5 cod stocks (2GH, 2J3KL, 3M, 3NO and 3Ps), 5 redfish stocks (SA2+3K, 3LN, 3M, 3O and Unit 2), 4 American plaice stocks (SA2+3K, 3LNO, 3M and 3Ps), 3 witch flounder stocks (2J3KL, 3NO and 3Ps), 2 Greenland halibut management areas (SA+1 and SA2+3KLMNO), 2 haddock stocks (3LNO and 3Ps), 1 yellowtail flounder stock (3LNO), 1 pollock stock (3Ps), 2 roundnose grenadier stocks (SA+1 and SA2+3) as well as a portion of the 3NOPs4VWX Atlantic halibut stock. In addition, there is a fishery for lumpfish, as well as relatively new fisheries for monkfish and skates. These latter two came under quota management for the first time in 1995. Scientific information on the above stocks is provided either through the DFO Science Branch regional review process and the FRCC, or the Scientific Council of NAFO. Quotas are set by the NAFO Fisheries Commission for 3NO and 3M cod, 3LN and 3M redfish, 3LNO and 3M American plaice, 3LNO yellowtail flounder, 3NO witch flounder and SA2+3KLMNO Greenland halibut. The NAFO Scientific Council also reviews the Canadian assessment of 2J3KL cod on an annual basis. Greenland halibut and roundnose grenadier in SA+1 are managed bilaterally by Denmark, on behalf of Greenland, and Canada. Quotas for the other stocks are set by the Minister of the Department of Fisheries and Oceans based on recommendations of the FRCC. The Newfoundland Region Stock Status Reports contain information only for those stocks for which the FRCC provides direct catch recommendations to the Minister. Information on the stocks evaluated and managed by NAFO is contained in separate documentation; the reports of the NAFO Scientific Council. Detailed technical information on each of the stock assessments can be found in the research documents listed with each stock report. Technical information for the NAFO stocks is available through the NAFO SCR Document series. The Groundfish Fisheries Cod traditionally dominated catches in Newfoundland waters, but with the decline of this resource, catches of other species have come to exceed those of cod. Significant reductions in catches of a number of different species and stocks has occurred since 1994 as a result of reduced fishing effort in the NAFO Regulatory Area (NRA). For Canadian managed stocks, groundfish catches were dominated by 3O redfish in 1997. In 1997, the only directed fisheries on 'traditional' species were for Greenland halibut in SA+1 and SA2+3KLMNO; cod in 3M; redfish in 3LN, 3M, 3O and Unit 2; and witch flounder in 3Ps. There was also a catch of about 8 metric tonnes of witch flounder taken from the 2J3KL stock in the July 1998

NRA by international fleets although the fishery on this Canadian managed resource was closed to Canadians. There is a moratorium on fishing the 2J3KL witch flounder stock in the NAFO Regulatory Area for 1998 imposed by the Fisheries Commission of NAFO. Reported Catches (t) 7, 6, 5, 4, 3, 2, 1, all countries 1977 198 1983 1986 1989 1992 1995 Gadoids Redfish Flatfish Directed fisheries for redfish in 3LN are not permitted for 1998, a closure also put in place by the Fisheries Commission of NAFO. A limited yellowtail flounder fishery (4, metric tonnes) is permitted by the Fisheries Commission in divisions 3NO for 1998. Canadian fisheries for 'non-traditional' species such as lumpfish, monkfish, wolffish, white hake, winter (blackback) flounder and skates continued in 1997. Background to Groundfish Reviews This overview provides an update on the status of 2GH cod, 3LNO and 3Ps haddock, 3Ps pollock, SA2+3K and 3Ps American plaice, 3Ps witch, SA2+3K redfish, as well as winter (blackback) flounder, wolffish (catfish), lumpfish and monkfish. These stocks will not be formally assessed this year but their status has been updated by the responsible assessment scientists. Cod in Div. 2J3KL and Subdivision 3Ps were assessed during a zonal assessment meeting in early 1998 (DFO Stock Status Reports A2-1 (1998) and A2-2 (1998) respectively). Div. 3O redfish and Unit 2 redfish will be reviewed in detail during a zonal meeting scheduled for early October. Skates and white hake will be reviewed regionally in early October. Stock Status Reports for all of these will be available following the assessments. Information on the status of stocks assessed by NAFO, as well as the 1998 advice of Scientific Council, is available in the report of the June 1998 meeting (NAFO SCS Doc. 98/17). Offshore Research Surveys As indicated in past Overview documents (Anon., 1996; Anon., 1997), the Newfoundland Region has recently changed to using the Campelen 18 shrimp trawl with 'rock-hopper' foot gear for its research surveys. This gear provides better information on young fish as well as other species such as crab and shrimp. Concurrent with the gear change, there was also a reduction in the duration of the standard tow from 3 minutes to 15 minutes. Different fishing gear will catch different sizes and quantities of fish species. Therefore, before being able to relate catches from surveys using the new survey trawl and 15 minute tow duration to those made in the past using the previous survey trawl (Engel) and 3 minute tow duration, it was necessary to conduct comparative fishing experiments. These experiments were described in some detail in the 1996 Overview (Anon. 1996). 2

Conversion factors are now available for the 'traditional' species, and are being applied to research vessel data. Data conversion has been completed for some stocks/species but is ongoing for others. For the most, conversions have not been completed for species not undergoing full reviews in 1998. It must also be noted that it is not possible to develop conversion factors for 'nontraditional' species at this time. Groundfish Resource Status The 'traditional' groundfish resources in the waters around Newfoundland continue to be at, or very near historical low levels. For Canadian managed stocks with TAC's still in place, reduced TAC's were imposed for 1995, and further reductions occurred for 1996 and 1997. For 1998 the TAC for 3Ps witch flounder has been increased to 65 metric tonnes. The Unit 2 redfish quota was increased to 11, metric tonnes for 1998. For the NAFO-managed groundfish stocks including those of Flemish Cap, directed fisheries are permitted only for 3M cod, Greenland halibut and 3LNO yellowtail flounder in 1998. Divisions 2GH Cod No directed fishing has been permitted on this stock since 1996. There has been no reported catch since 1991. A research survey in 1997 covering most of the area in the 2-1,5 meter depth range located no significant concentrations of cod. The survey biomass for Div. 2GH in the area surveyed was only about 1, metric tonnes. As in 1996, the survey coverage and timing were probably more appropriate for Greenland halibut than cod in that cod may have been inshore of the surveyed area at the time of the survey. Without appropriate survey coverage/timing or other inshore activity it will remain unknown if concentrations of cod exist shoreward of the 2 meter contour. Nonetheless, it appears that the stock remains at a low level compared to earlier periods. 1, 9, 8, 7, 6, 5, 4, 3, 2, 1, 196 1965 197 1975 198 1985 199 1995 Canadian Others TACs Divisions 3LNO Haddock Management advice was that there be no directed fishing, and by-catch be limited to 1 tons for both 1996 and 1997. For 1998 a closure on directed fishing remains in place. Reported catch for 1997 was 19 metric tonnes; 95% of this taken in 3O. The low catches in recent years are partially due to the moratoria on cod and flatfish stocks in the 3LNO area first imposed in 1994 by NAFO, as well as reduced haddock by-catch limits. In 1994 and 1995 the spring research survey index was low with estimates being similar to those of the 197's. The survey index increased sharply in 1997 compared to 1996. But, it should be noted that this increase was due to one large catch of large prespawning fish (97% of the abundance and 98% of the biomass). No juvenile haddock were caught during the 1997 survey. Preliminary analysis indicates that the spring 1998 3LNO survey located much fewer haddock. 3

6, 5, 4, 3, 2, 1, 1996-98 with Campelen; earlier not converted 1973 1978 1983 1988 1993 1998 91% ftom 1 large set 35, 3, 25, 2, 15, 1, 5, 1996-98 with Campelen; earlier not converted 1972 1975 1978 1981 1984 1987 199 1993 1996 3Ps This stock will not begin to recover unless there is good recruitment. Subdivision 3Ps Haddock Catches of haddock in 3Ps since 196 have been mainly in the 1, to 2, metric tonne range, but increased to 7,5 metric tonnes in 1985 before falling below 1, metric tonnes after 199. Reported catch for 1997 was only 69 metric tonnes. No directed fishing and by-catch restrictions have been in place for a number of years. For 1998 there is again no directed fishery allowed. Research vessel surveys have been conducted by Canada since 1972. The trawl index of haddock biomass from these surveys was low from 1972 to 1982, peaked in 1985 due to the presence of the relatively strong 1981 year class, but then declined again to low levels. The 1996 survey found very few haddock and the 1997 survey found even less. The 1998 3Ps survey results suggested some increase but biomass is still at a low level when compared the mid to late 198's. There were no reports of by-catch in the 1997 cod fishery. Without recruitment, this stock will not increase. Subdivision 3Ps Pollock Reported landings of pollock increased to 439 metric tonnes in 1996, over four times the bycatch limit for that year. In 1997 there was again no directed fishing permitted but the bycatch limit was increased to 1,5 metric tonnes so as to not impede the re-opened cod fishery. Reported catch for 1997 was 59 metric tonnes. The pelagic nature of pollock has always led to questions as to whether research vessel surveys give a reliable index of abundance or biomass. Keeping these uncertainties in mind, the relative biomass index was low in the 197's, then gradually increased until 1989. Since then it declined again to pre-198 levels. Estimates have remained low in the 199's. Even with the change to Campelen gear with a presumed catchability greater than the Engel, the index for 1996-1998 was only about 7% of the average of the 198's. The 1998 estimate at only 5 metric tonnes is the lowest on record. 4

9, 8, 7, 6, 5, 4, 3, 2, 1, 1977 198 1983 1986 1989 1992 1995 1998 3Ps Campelen in 1996-98; earlier not converted Survey Relative Biomass Index 14, 12, 1, 8, 6, 4, 2, 1978 1983 1988 1993 3K 1995-97 with Campelen; earlier not converted 2J Pollock have never been a major component of the commercial fishery in NAFO Subdiv. 3Ps. The fishery is opportunistic, and based on the occurrence and survival of yearclasses against great odds in the extreme north of their range. There may also be occasional migration into the area from further south. Subarea 2 + Division 3K American Plaice Catch from this stock was only about 8 metric tonnes in 1997, the third consecutive year in which the catch has been less than 25 metric tonnes. Research vessel surveys continue to show that the stock is at a very low level. In Div. 2J and 3K combined, the biomass index declined by over 95% between 1982-83 and 1992-94. The 1995 to 1997 surveys were conducted with the new Campelen trawl gear, known to have a much higher catchability of small American plaice. Therefore the survey biomass indices in Div. 2J and Div. 3K for 1995 to 1997 are not directly comparable with previous values. However, even with this change in survey gear, the divisions 2J3K biomass index in the most recent 3 years is only about 1-15% of the peak values seen in 1982-83. There is no trend in the biomass estimates from 1995 to 1997. Surveys in Div. 2GH in 1996 and 1997 indicate very low biomass of American plaice in these areas, at less than 1% of the level in Div. 2J3K combined. Given the current stock size estimates from the surveys, there continues to be no optimism about recovery of this stock in the short or medium term. Subdivision 3Ps American Plaice Catches from this stock remain well below the historic average, but have increased from 76 metric tonnes in 1995 to 23 metric tonnes in 1997. Most of the catch is taken as by-catch in other fisheries, such as that for Subdiv. 3Ps witch flounder. Research vessel survey information shows that this stock is at a very low level. The 1993-95 survey biomass estimates were only 1% of those in the mid-198's. The surveys in 1996 to 1998, conducted using the Campelen trawl, also gave very low biomass estimates relative to the 198's even though the catchability is greater with this gear than with the Engel trawl. 5

Survey Relative Biomass Index 7, 6, 5, 4, 3, 2, 1, Newfoundland Region 198 1983 1986 1989 1992 1995 1998 1996-97 are Campelen; earlier not yet converted The outlook for this stock remains pessimistic, given the current low stock size, and the lack of recruitment indicated by the surveys. In the short to medium term, there continues to be no prospect for stock rebuilding. Subdivision 3Ps Witch Flounder This fishery has remained open, with a 5 metric tonne TAC in 1997, and 65 metric tonnes for 1998. The catch has been less than the TAC in the last 4 years; in the range of 25 to 4 metric tonnes. In 1997, 289 metric tonnes were taken. By-catch of other species (cod, American plaice) remains a problem in this fishery. The survey biomass index has been highly variable over time, fluctuating between years but with little in the way of longer term trends. The survey biomass index was below average but relatively stable from 1993 to 1995 and within the range of previous estimates. The 1996-98 surveys were done with the new Campelen gear so results are not directly comparable with those of the previous surveys. It has been shown that catchability with the Campelen gear is higher than with the Engel. There is an increasing trend in the biomass estimates from 1996 to 1998. However this may reflect growth of individuals since estimates of abundance remained stable during the same period. Survey Relative Biomass Index 16, 14, 12, 1, 8, 6, 4, 2, 1976 1979 1982 1985 1988 1991 1994 1997 Catches at the level of the current TAC are not likely to cause a decline in this stock. Subarea 2 + Division 3K Redfish There has not been constant directed effort on this stock since 199 when 2,4 metric tonnes were landed. Landings declined to 28 metric tonnes in 1991 and have been 15 metric tonnes or less in each year from 1992 through 1997. Estimates of discarded redfish, taken as bycatch in shrimp fisheries, declined from 386 metric tonnes in 1992 to 11 metric tonnes in 1994. Estimates from the 1995-97 shrimp fisheries have not been compiled to date. Results from research vessel surveys in Div. 2J and 3K suggest the resource was at an historically low level in 1994. The 1995-97 survey estimates cannot at this time be compared directly with the historical series because data conversion is not yet complete. Although the Campelen trawl has resulted overall in a higher catchability than before, the estimates for 1995-97 are still very low, less than 1% of the 1978-88 average. 6

Survey Relative Biomass Index 8, 7, 6, 5, 4, 3, 2, 1, 1995-97 with Campelen; earlier not yet converted 1978 1981 1984 1987 199 1993 1996 3K 2J Lumpfish Roe Landings (t) 3,5 3, 2,5 2, 1,5 1, 5 1976 1979 1982 1985 1988 1991 1994 1997 3K 3L 3P This stock remains at a low level. Recruitment has been very poor since the year classes of the early 197's. There are no indications that the status of the stock will change in a positive way in the foreseeable future. Lumpfish in Divisions 3K, 3L and 3P Lumpfish roe landings from divisions 3K, 3L and 3P were approximately 5 metric tonnes from 1977 to 1984. They reached a high of 3, metric tonnes in 1987 then declined to an average of 2, metric tonnes from 1988 to 1994. There was a decline to 1, metric tonnes in 1995 and 1996. The landings increased to 2, metric tonnes with 3Ps at an all time high of 1,6 metric tonnes in 1997. The lumpfish fishery is exclusively on prespawning mature females and therefore the spawning stock is vulnerable to overexploitation. Since the cod moratorium there has been an increase in fishers entering this fishery. This fishery is regulated by effort controls. There have been reductions in numbers of nets allowed as well as duration of the fishery in recent years These reductions in effort over time were imposed as a result of indications of stock declines, particularly in divisions 3K and 3L. Research vessel surveys are not considered to be representative of the stock due to the seasonal migratory pattern of this species. There is insufficient new data available to determine the current status of this resource. Catfish (Wolffish) in Divisions 2J, 3K, 3L, 3N, 3O and 3Ps Historically, catfish have mainly been taken as by-catch in other fisheries. During the 198's catches exceeded 1, metric tonnes in most years. They declined after 1991 when many fisheries were closed. Reported catch was only 23 metric tonnes in 1996, but increased to 165 metric tonnes in 1997. For spotted wolfish, the research survey biomass index remains at a low level. The data suggest some increase in 1996 and 1997, and again in 1998 for 3LNOPs combined but this may be due, at least in part, to the change in gear used. 7

Nonetheless, the estimates remain very much below those observed in the 198's. 3, 25, 2, 15, 1, 5, Spotted Catfish Campelen conversions not made.1995-97 for 2J3K; 1996-97 for 3LNOPs 1977 198 1983 1986 1989 1992 1995 1998 3Ps 3O 3N 3L 3K 2J For striped wolfish, the survey biomass index also remains at a relatively low level, although the overall decline has not been as great as occurred with spotted wolffish. 4, 35, 3, 25, 2, 15, 1, 5, Striped Catfish Campelen conversions not made.1995-97 for 2J3K; 1996-97 for 3LNOPs 1977 198 1983 1986 1989 1992 1995 1998 3Ps 3O 3N 3L 3K 2J Winter (Blackback) Flounder in Divisions 3K, 3L and 3Ps Catches increased in 1994 and 1995 to 1,568 and 1,37 metric tonnes respectively, but declined again in 1996 and 1997 to 561 and 46 metric tonnes respectively, similar to levels observed in the late 198's and early 199's. It is unknown whether these declines represent a decline in the resource or a decrease in fishing effort. Blackback flounder is rarely observed in research vessel catches as it is generally restricted to less than 6 m water depth. Thus, lack of data make it impossible to determine trends in biomass or examine other biological characteristics. The distribution of reported landings suggest that it is widespread along the coast. Monkfish in Divisions 3L, 3N, 3O and 3Ps A directed trawl Fishery for monkfish began in 1991, and almost 4 metric tonnes were taken that year. Catches gradually increased with the development of this fishery, to about 1, metric tonnes in 1994, but the 1995 catch fell to only 16 metric tonnes under a quota restriction of 2 metric tonnes. The same quota level was in place for 1996 when 255 metric tonnes were landed. The 1997 catch increased to 475 metric tonnes although the quota remained at 2 metric tonnes. 7, 6, 5, 4, 3, 2, 1, 1996-98 with Campelen; earlier years not converted. 1977 198 1983 1986 1989 1992 1995 1998 3Ps 3O The survey biomass index showed a dramatic increase from 1995 to 1996, but declined again in 1997. Because of the change in fishing gears beginning in 1996, it is not possible to interpret the most recent survey data. If catchability is greater with the Campelen, then this resource may be declining. 8

The Environment Annual air temperatures over most of the northwest Atlantic were cooler in 1997 compared to 1996. They were however, warmer than normal over the Labrador Sea. Sea ice generally arrived later and left early resulting in a shorter duration then usual, although the extent was greater than in 1996. The number of icebergs reaching the Grand Banks was higher than in 1996 but still about 6% lower than during the early 199's. At Station 27 off St. John's, temperatures over all depths were near normal or above normal throughout the water column during winter months. In April the surface waters became cooler than normal and this cooler water extended into May. from 1961-9 mean 3 2 1-1 -2-3 Station 27 Surface -4 45 5 55 6 65 7 75 8 85 9 95 It gradually extended deeper to reach 1 meters by October. During fall, temperatures in the upper layers were near normal, while bottom temperatures were near normal throughout the year. mean 2 1.5 1.5 -.5-1 Station 27 Bottom -1.5 45 5 55 6 65 7 75 8 85 9 95 9 Summer salinity values continue to be below the long term average. During the summer of 1997, the area of the cold intermediate layer (CIL) on the Newfoundland shelf was below normal, continuing the declining trend from 1995. Core temperatures were near normal within the CIL. Off the south coast, the relatively cold conditions which began around the mid- 198's have moderated somewhat, even though below normal bottom temperatures continued through 1996. There was some cooling again in 1997 although temperatures warmed to near normal late in the year in inshore areas. Outlook Overall, there are no signs of recovery for stocks examined in this overview. Many of the species are relatively long lived and will require a number of years following the next good recruitment before these year-classes would begin to contribute to the spawning stock biomass. An exception to the above is witch flounder in Subdivision 3Ps which appears to be stable or increasing somewhat at the current catch levels. For More Information Research Documents: Colbourne, E. 1998. Oceanographic conditions in the Newfoundland region during 1997. DFO Atl. Fish. Res. Doc. 98/29 Drinkwater, K.F., E. Colbourne and D. Gilbert. 1998. Overview of environmental conditions in the northwest Atlantic in 1997. NAFO SCR Doc. 98/638.

Reports: Anon. 1996. Newfoundland Region Overview. DFO Science Stock Status Report 96/43E. Anon. 1996. Divisions 2GH cod. DFO Science Stock Status Report 96/44E. Anon. 1996. Divisions 3LNO haddock. DFO Science Stock Status Report 96/46E. Anon. 1996. Subarea 2+3K redfish. DFO Science Stock Status Report 96/47E. Anon. 1996. Subarea 2+3K American plaice. DFO Science Stock Status Report 96/48E. Anon. 1996. Subdivision 3Ps haddock. DFO Science Stock Status Report 96/82E. Anon. 1996. Subdivision 3Ps pollock. DFO Science Stock Status Report 96/83E. Anon. 1996. Subdivision 3Ps American plaice. DFO Science Stock Status Report 96/84E. Anon. 1996. Subdivision 3Ps witch flounder. DFO Science Stock Status Report 96/85E. Anon. 1996. Divisions 3L, 3N, 3O and 3Ps skates. DFO Science Stock Status Report 96/86E. Anon. 1996. Monkfish in Divisions 3L, 3N, 3O and 3Ps. DFO Science Stock Status Report 96/89E. Anon. 1996. White hake in Divisions 3L, 3N, 3O and 3Ps. DFO Science Stock Status Report 96/9E. Anon. 1996. Catfish (wolffish) in Divisions 2J, 3K, 3L, 3N, 3O and 3Ps. DFO Science Stock Status Report 96/91E. Anon. 1996. Blackback (winter) flounder in Divisions 3K, 3L and 3Ps. DFO Science Stock Status Report 96/92E. Anon. 1997. Newfoundland Region. DFO Science Stock Status Report A2-19 (1997). Anon. 1997. Report of Scientific Council 4-19 June 1997. NAFO SCS Doc. 97/14. Anon. 1998. Divisions 2J3KL cod. DFO Science Stock Status Report A2-1 (1998). Anon. 1998. Subdivision 3Ps cod. DFO Science Stock Status Report A2-2 (1998). Contact: Bruce Atkinson Tel. (79) 772-252 Fax. (79) 772-4188 e-mail: atkinson@athena.nwafc.nf.ca This report is available: Science Branch Dept. of Fisheries and Oceans Newfoundland Region P.O. Box 5667 St. John's NF A1C 5X1 (79) 772-4355 e-mail address: gperry@athena.nwafc.nf.ca Internet address: http://www.nwafc.nf.ca 1