PROGRESS REPORT State: NEW HAMPSHIRE Grant: F-61-R-21/F16AF0163 Grant Title: NEW HAMPSHIRE S MARINE FISHERIES INVESTIGATIONS Project 2: MARINE RECREATIONAL FISHERIES MONITORING Job 1: MONITORING OF THE RAINBOW SMELT RESOURCE AND WINTER ICE FISHERY Objective: To annually monitor the resource of Rainbow Smelt Osmerus mordax and its fishery in the Great Bay Estuary system. Period Covered: April 1, 2017 - March 31, 2018 ABSTRACT There was no winter ice fishery for Rainbow Smelt Osmerus mordax during the winter of 2016 2017 due to poor ice conditions. There is no data from the 2016 2017 season to include in this report for the examination of long-term catch and effort trends. INTRODUCTION New Hampshire's Great Bay Estuary traditionally provides a winter recreational and commercial Rainbow Smelt fishery. In 1977, complaints from anglers concerning the quality of the fishery led to an investigation by the New Hampshire Fish & Game Department (NHFG). Length and age data were obtained from the catch of anglers during the winter fishery. These data were compared with earlier studies of Rainbow Smelt in the Great Bay area (Warfel et al. 1943; Krochmal 1949). When an absence of age-2 Rainbow Smelt was observed in 1977, indicating possible recruitment problems, an emergency closure to the taking of Rainbow Smelt was enacted except during the winter ice fishery. The management decision reduced fishing mortality and protected the spawning run, while providing the opportunity to obtain information by creel survey. This action was followed by a 5-year study of the Rainbow Smelt resource and fishery from 1979 to 1983 under Federal Aid Project F-36-R. The results of that study illustrated a general decline in CPUE (fish/hour). Only one year out of five had a normal age distribution (more age-2 fish than older age classes) in the F-61-RII-1_17_AR Page 61
winter ice fishery. The egg deposition was, at best, one-sixth of the level considered to be optimal, roughly 13 eggs/cm 2 (Rothschild 1961; McKenzie 1964). A statewide fisheries management plan for Rainbow Smelt was written in 1981 (NHFG 1981). The objectives for the sea-run Rainbow Smelt portion of the management plan were: 1. Maintain or increase the sea-run population of Rainbow Smelt 2. Provide for a sea-run recreational Rainbow Smelt fishery 3. Provide for a sea-run commercial Rainbow Smelt fishery Management measures implemented following development of the plan included closure of the fishery to net and weir harvesters from March 1 to December 15, a daily possession limit of 10 liquid quarts, and implementation of a Rainbow Smelt egg transfer program. When data from the 2014 smelt creel survey indicated that CPUE had fallen to the lowest level on record, management measures were taken to reduce the harvest in subsequent years. Beginning in 2015 the daily possession limit became 4 liquid quarts. To evaluate the effectiveness of the management measures and detect trends in resource abundance, a creel survey of the recreational ice fishery has been conducted annually (except 1983 1986), coastal harvest logbooks have been used to monitor bow net harvest of Rainbow Smelt (See Project III-2), and a Rainbow Smelt egg deposition survey was conducted annually from 1979 to 2007. The egg deposition survey was terminated in 2007 because of poor correlation with the catch data; it was reinstated in 2014 under Project I-2 with updated procedures. PROCEDURE The winter Rainbow Smelt Fishing Creel Survey is conducted from roughly ice-in to ice-out, which normally occurs between the months of December and March. Four areas of major Rainbow Smelt angling activity have been identified and surveyed throughout the project period: the Lamprey, Squamscott, Oyster Bellamy rivers, as well as Great Bay proper. The survey was designed using a random schedule of two-hour survey periods between 0600 and 2400 hours. Locations are weighted by relative fishing effort from previous years and then randomly selected. After a location is selected, the AM and PM tide is alternated by day and an offset is randomly assigned. Times that fall outside of two hours before or five hours after the high tide are eliminated due to the lack of fishing activity around low tide. At least one survey is scheduled for each day of the week with supplemental surveys added to ensure each location is surveyed at least once F-61-RII-1_17_AR Page 62
during each weekday period and once during a weekend. Additionally, beginning in 2009, an instantaneous count method was conducted during each day of the winter ice fishery. The counts are obtained separately from the creel survey activities by driving to each of the four locations and counting the number of anglers actively participating in the fishery after the creel survey is completed. All anglers, or a subsample, are interviewed for catch and effort (hours fished) information during an assigned survey. The information collected is expanded by strata (weekend/weekday, location, and month) to provide estimates of catch, effort, and CPUE by month and location. Length and sex information, weight measurements, and scales for aging are taken weekly (when available) from samples of angler harvest. Scales are double aged using a QImaging microscopy camera and Image-Pro software, and according to methods described by Bailey (1964). RESULTS There was insufficient ice cover to support fishing effort for Rainbow Smelt on the Great Bay Estuary during the 2016 2017 winter season. There was no documented fishing which resulted in no data for inclusion in long-term trends (Tables 2.1-1 through 2.1-3) or analysis. No Rainbow Smelt were measured and no scale samples for ageing were taken (Table 2.1-4). DISCUSSION A lack of ice cover during the 2016 2017 winter Rainbow Smelt fishing season resulted in an absence of fishing effort. There is no data from the 2016 2017 season for inclusion in the time series or to examine for long-term catch and effort trends in this report. F-61-RII-1_17_AR Page 63
REFERENCES Bailey, M.M. 1964. Age, growth, maturity, and sex composition of the American Smelt of western Lake Superior. Trans. Am. Fish. Soc. 93: 382 395. Krochmal, S.B. 1949. Ecology of the Smelt, Osmerus mordax (Mitchell), in Great Bay New Hampshire. Master s Thesis. Univ. N.H., Durham. 78pp. McKenzie, R.A. 1964. Smelt life history and fishery in the Miramichi River, New Brunswick. Fish. Res. Bd. Can. Bull. #144. 77pp. New Hampshire Fish and Game Department (NHFG), 1981. Fisheries Management Plan For Rainbow Smelt (Osmerus mordax). Appendix I. New Hampshire Fish and Game Department, Concord Rothschild, B.J. 1961. Production and survival of eggs of the American Smelt, Osmerus mordax (Mitchill), in Maine. Trans. Am. Fish. Soc. 90: 42 48. Warfel, H.E., T.P. Frost, and W.H. Jones. 1943. The Smelt, Osmerus mordax, in Great Bay, New Hampshire. Trans. Am. Fish. Soc. 72: 257 262. F-61-RII-1_17_AR Page 64
Table 2.1-1. Estimates of catch and effort with associated proportional standard error (PSE) and CPUE for the marine recreational Rainbow Smelt ice fishery in New Hampshire during fishing years 1978 through 2017. a Estimated Estimated Months of Ice-on Angler Angler harvest Estimated harvest a CPUE Year fishery index # trips hours hours PSE (number) harvest PSE (kg) (fish/hr) 1978 D-M NA 3,085 6,654 20.5 33,336 19.6 1,512 4.8 1979 D-M NA 10,256 33,044-225,090-10,210 6.8 1980 J-M NA 2,644 6,314 14.6 4,469 32.0 203 0.4 1981 D-F NA 17,047 40,659 17.4 148,606 27.7 6,741 3.3 1982 J-M NA 10,879 23,803 14.6 11,472 34.3 520 0.4 1983 1984 1985 1986 No survey conducted No survey conducted No survey conducted No survey conducted 1987 J-M NA 19,732 28,041 10.1 163,555 46.7 7,419 6.0 1988 J-M NA 22,952 38,564 12.0 200,157 20.7 9,079 5.0 1989 D-M NA 22,942 45,503 10.6 477,208 13.9 21,646 10.3 1990 D-M NA 16,839 45,905 7.8 301,783 15.6 13,689 5.1 1991 J-F NA 9,105 18,338 15.0 49,486 23.4 2,245 2.7 1992 D-M 1,284 11,767 24,618 11.1 34,848 15.1 1,581 1.4 1993 D-M 1,134 11,684 23,120 11.3 82,772 16.1 3,754 3.5 1994 D-M 1,704 16,445 32,745 9.8 97,077 15.2 4,403 3.0 1995 J-M 726 11,880 23,780 12.1 251,184 24.2 11,393 10.6 1996 D-M 1,698 20,114 40,654 10.6 204,767 15.8 9,288 5.0 1997 D-M 774 5,957 12,379 14.4 32,426 33.9 1,471 2.6 1998 D-F 540 2,213 4,191 22.3 8,619 28.0 391 1.9 1999 J-F 894 4,701 8,834 15.8 22,386 16.0 1,016 2.5 2000 D-M 1,302 10,843 20,837 11.3 84,203 11.9 3,819 4.0 2001 D-M 1,872 14,877 28,909 12.1 162,397 14.9 7,366 5.6 2002 2003 D-M 1,848 17,519 33,653 10.8 169,103 11.0 7,670 5.0 2004 D-F 1,272 11,637 21,630 11.4 91,654 16.0 4,157 4.2 2005 J-M 1,440 6,544 12,288 13.7 48,987 13.7 2,222 3.9 2006 2007 J-M 1,158 7,799 15,153 13.8 33,975 13.7 1,541 2.2 2008 D-M 1,560 5,052 9,403 23.1 34,280 19.3 1,555 3.7 2009 J-M 1,548 3,716 14,649 8.3 36,911 29.0 1,430 2.5 2010 D-F 1,092 2,121 8,286 10.3 29,867 33.8 2,211 3.6 2011 D-M 1,398 3,269 11,886 12.4 65,331 20.2 3,361 5.5 2012 2013 2014 D-M 1,698 1,014 3,694 13.5 1,078 38.2 88 0.3 2015 J-M 600 187 723 16.8 202 35.7 15 0.3 2016 2017 Prior to 2009, the estimated total harvested weight of fish was 1/10 the catch estimate. Beginning in 2009, the weight measurements taken during sampling were used to calculate harvest weight (pounds converted to kg). F-61-RII-1_17_AR Page 65
Table 2.1-2. Fishing effort by area (percent of total trips) for the marine recreational Rainbow Smelt ice fishery in New Hampshire during fishing years 1978 through 2017. Year Great Bay Lamprey R. 1978 69.8 17.8 12.3 NS NS 3,085 1979 Survey data unavailable 1980 92.1 7.4 0.5 NS NS 2,644 1981 31.1 46.7 4.8 NS 17.3 17,047 1982 37.9 45.1 3.2 NS 13.8 10,879 1983-1986 No recreational fishing survey conducted 1987 34.1 10.3 6.2 NS 49.5 19,732 1988 25.4 14.7 10.2 NS 49.8 22,952 1989 33.9 8.8 11.4 NS 45.9 22,942 1990 19.6 29.2 4.4 0.0 46.8 22,933 1991 27.5 31.5 7.6 1.6 31.8 9,105 1992 30.5 35.8 2.3 NS 31.4 11,767 1993 7.4 15.4 20.5 NS 56.7 11,684 1994 34.7 10.3 16.2 NS 38.7 16,445 1995 28.9 12.2 13.9 NS 45.0 11,880 1996 21.3 14.5 16.1 NS 48.1 20,114 1997 26.5 4.8 33.3 NS 35.4 5,957 1998 0.2 12.6 68.1 NS 19.1 2,213 1999 8.7 6.6 50.0 NS 33.8 4,701 2000 12.6 18.4 22.4 2.6 43.8 10,843 2001 7.6 16.2 8.5 NS 68.3 14,877 2002 2003 12.7 7.9 16.5 0.0 62.8 17,519 2004 14.7 5.6 14.9 NS 64.8 11,637 2005 16.8 5.5 27.3 NS 50.4 6,544 2006 2007 25.9 0.3 10.8 NS 63.1 7,799 2008 13.7 0.0 16.7 NS 69.6 5,052 2009 12.6 4.2 17.1 NS 66.0 3,716 2010 33.4 1.3 14.2 NS 51.1 2,121 2011 7.4 4.5 22.6 NS 65.5 3,269 2012 2013 2014 11.2 0.8 4.6 NS 83.4 1,014 2015 2.1 0.0 10.2 NS 87.7 187 2016 2017 NS = Not surveyed due to zero effort. Oyster R. Bellamy R. Winnicut R. Depot Rd. Squamscott R. Total trips F-61-RII-1_17_AR Page 66
Table 2.1-3. Rainbow Smelt catch by area (percent of total catch) for the marine recreational Rainbow Smelt ice fishery in New Hampshire during fishing years 1978 through 2017. Year Great Bay Lamprey R. 1978 99.0 0.8 0.2 NS NS 197,989 1979 73.5 1.9 4.8 19.8 NS 225,090 1980 2.6 89.0 6.3 2.1 NS 21,278 1981 52.1 15.7 5.8 0.3 26.1 413,944 1982 61.7 17.6 1.2 NS 19.5 60,430 1983-1986 No recreational fishing survey conducted 1987 18.3 5.5 3.5 NS 72.7 334,755 1988 6.5 13.7 7.2 NS 72.6 281,365 1989 9.7 10.0 7.6 NS 72.8 493,452 1990 7.4 38.8 0.1 0.0 53.0 342,205 1991 28.5 16.7 20.4 0.5 33.8 96,370 1992 25.4 47.6 0.4 NS 26.7 43,287 1993 0.4 10.8 28.5 NS 60.2 87,393 1994 32.6 5.1 22.7 NS 39.6 93,708 1995 10.9 14.5 12.9 NS 61.7 238,888 1996 7.0 16.2 11.3 NS 65.5 192,356 1997 45.2 0.3 20.6 NS 33.9 31,433 1998 0.0 6.9 85.3 NS 7.8 7,254 1999 0.9 4.1 44.0 NS 51.0 22,386 2000 6.4 29.9 21.7 1.4 40.6 84,203 2001 2.8 12.7 3.0 NS 81.5 162,397 2002 2003 5.3 4.6 14.4 NS 75.7 169,103 2004 6.3 4.0 7.5 NS 82.2 91,654 2005 22.0 7.5 29.4 NS 41.0 48,987 2006 2007 25.6 0.1 8.4 NS 65.9 33,975 2008 4.1 0.0 17.3 NS 78.5 34,280 2009 31.2 3.2 13.6 NS 52.1 36,911 2010 41.8 0.0 4.8 NS 53.5 29,737 2011 8.2 0.4 14.6 NS 76.8 65,331 2012 2013 2014 1.2 0.0 0.0 NS 98.8 1,078 2015 11.8 0.0 0.0 NS 88.2 202 2016 2017 NS = Not surveyed due to zero effort. Oyster R. Bellamy R. Winnicut R. Depot Rd. Squamscott R. Total catch F-61-RII-1_17_AR Page 67
Table 2.1-4. Percent age distribution of harvested Rainbow Smelt from the marine recreational Rainbow Smelt ice fishery in New Hampshire during fishing years 1987 through 2017 (sexes combined). Percent at age Year Age-1 Age-2 Age-3 Age-4 Age-5+ Sample size 1987 a 0.0 45.6 45.8 8.0 0.6 327 1988 a 0.0 58.6 31.1 9.8 0.5 428 1989 a 0.0 59.6 32.3 6.9 1.2 495 1990 a 0.0 40.8 52.5 6.3 0.5 608 1991 a 0.0 30.8 49.4 16.1 3.7 354 1992 a 0.0 57.1 29.5 12.4 1.0 597 1993 No age data collected 1994 b 0.0 33.7 62.5 3.1 0.7 512 1995 b 0.0 33.3 55.4 10.5 0.9 521 1996 b 0.0 42.6 41.7 13.4 2.3 756 1997 b 0.0 18.6 65.6 14.5 1.3 209 1998 b 0.0 80.9 10.9 6.2 1.9 171 1999 b 0.0 40.9 52.6 6.2 0.3 306 2000 b 0.0 57.2 27.0 14.1 1.7 596 2001 b 0.2 15.8 59.2 19.8 5.0 682 2002 2003 b 0.0 66.8 28.7 3.9 0.6 810 2004 b 0.0 27.7 59.8 11.9 0.6 537 2005 b 0.0 82.9 10.6 6.0 0.5 490 2006 2007 b 0.0 44.3 43.3 11.9 0.4 329 2008 b 0.9 36.5 27.5 29.3 5.9 290 2009 b 0.2 14.0 46.6 31.7 7.4 463 2010 b 0.6 25.5 47.4 22.1 4.5 344 2011 b 0.1 56.5 30.0 11.6 1.9 529 2012 2013 2014 b 1.6 22.9 48.2 26.6 0.7 119 2015 b 0.0 39.4 53.7 2.9 4.0 37 2016 2017 a Raw age distrubution from biological samples. b Calculated by weighting the sample distribution by catch estimates. F-61-RII-1_17_AR Page 68