Fisheries Research 94 (2008) 123–132
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The nascent recovery of the Georges Bank haddock stock
Jon Brodziak∗, Michele L. Traver, Laurel A. Col
Northeast Fisheries Science Center, 166 Water Street, Woods Hole, MA 02543, United States
Received 30 October 2007
Received in revised form 19 March 2008
Accepted 27 March 2008
World-wide many ﬁsh stocks have been depleted by overﬁshing. In this study, we describe the nascent
recovery of the Georges Bank haddock stock. This mainstay of the New England groundﬁsh ﬁshery was
overﬁshed for decades prior to mid-1990s and experienced long-term declines in spawning biomass and
recruitment. The stock was considered to have collapsed in the early-1990s when a lawsuit by the Con-
servation Law Foundation led the New England Fishery Management Council (NEFMC) and the National
Marine Fisheries Service (NMFS) to take actions to cease overﬁshing and to recover Georges Bank haddock
and other groundﬁsh stocks. Under restrictive management measures, stock size increased 10-fold from
1995 to 2005. In 2003, an exceptionally abundant year class (YC) was produced. Although this YC may
rebuild the haddock stock to pre-1930s abundance if properly ﬁshed, monitoring changes in life history
parameters and recruitment will be important for sustaining stock recovery. Mean weights and sizes at
age of adult haddock have decreased in recent years, and compensatory responses of haddock growth and
recruitment to changes in stock density are assessed. We discuss some remaining challenges to managing
this recovering transboundary resource in a dynamic multispecies ﬁshery.
Published by Elsevier B.V.
Rebuilding depleted marine ﬁshery resources in the U.S. is
mandated by the Sustainable Fisheries Act. This law requires
that management measures prevent overﬁshing and achieve BMSY,
the stock size that produces maximum yield, for the purpose of
achieving optimum yields. However, reducing ﬁshing mortality
and implementing successful rebuilding plans for depleted ﬁsh-
ery resources has proven to be challenging in practice (Rosenberg
et al., 2006). Nowhere in the U.S. has this been more apparent
than in the New England region, where there have been ongoing
controversies over stopping overﬁshing and rebuilding ﬁsheries
The Georges Bank haddock (Melanogrammus aegleﬁnus)stock
(Fig. 1) was the mainstay of the New England groundﬁsh ﬁshery
in the mid-20th century. Annual haddock landings from Georges
Bank averaged 46kt during 1931–1960 (Fig. 2), roughly 100 million
pounds a year. Foreign distant water and domestic ﬂeets severely
overharvested the stock in the 1960s, and by the early-1970s,
Georges Bank haddock stock size and annual yield had dropped to
record lows (Figs. 2 and 3). The stock experienced a brief recovery
∗Corresponding author. Currentaddress: Paciﬁc Islands Fisheries Science Center,
2570 Dole Street, Honolulu, HI 96822-2326, United States. Tel.: +1 808 983 2964;
fax: +1 808 983 2902.
E-mail address: Jon.Brodziak@NOAA.GOV (J. Brodziak).
in the late-1970s when two strong year classes (YCs) (1975 and
1978) were produced. By the mid-1980s, however, the stock had
again declined due to chronic overﬁshing. U.S. landings of Georges
Bank haddock declined more than 100-fold in 30 years, falling
from 52.918 kt in 1965 to a record low of 0.218kt in 1994–1995
(Fig. 2). By the early-1990s, the stock was again at record-low
abundance and was considered to be collapsed (NEFSC, 1994). In
effect, this productive stock was overﬁshed for several decades
prior to mid-1990s (Brodziak and Link, 2002) and as a result, expe-
rienced long-term declines in spawning biomass and recruitment
(Brodziak et al., 2001).
Management of New England groundﬁsh stocks has been the
subject of legal disputes for over 20 years. The U.S. and Cana-
dian maritime border dispute over territorial waters in the Gulf
of Maine-Georges Bank region was decided by the International
Court in 1984. The settlement established the Hague Line demar-
cating the maritime border between U.S. and Canadian ﬁshing areas
on Georges Bank. In this case, the U.S. lost access to the produc-
tive Northeast Peak of Georges Bank, an important haddock ﬁshing
area. As a result, the Georges Bank haddock stock is a transboundary
resource shared by the U.S. and Canada (Christie, 1987). The east-
ern Georges Bank haddock management unit is jointly managed
by the two countries (Fig. 1) while the U.S. manages the western
Georges Bank management unit. In May 2004, a formal quota shar-
ing agreement between Canada and the U.S. was implemented to
share the harvest of the transboundary eastern Georges Bank had-
dock management unit. This agreement includes total allowable
0165-7836/$ – see front matter. Published by Elsevier B.V.
124 J. Brodziak et al. / Fisheries Research 94 (2008) 123–132
Fig. 1. The geographic range of the Georges Bank haddock stock off New England (enclosed by solid red lines) showing the western and eastern management units along
with the Hague Line demarcating the boundary between U.S. and Canadian waters and four year-round groundﬁsh closed areas (CA): CA I, CA II, the Nantucket Lightship CA,
and the Western Gulf of Maine (WGOM) CA. (For interpretation of the references to color in this ﬁgure legend, the reader is referred to the web version of the article.)
catch quotas for each country as well as in-season monitoring of
the catch of haddock on eastern Georges Bank.
Another dispute arose in 1991 when the National Marine Fish-
eries Service (NMFS) was sued by the Conservation Law Foundation
(CLF) to cease overﬁshing of New England groundﬁsh stocks,
including Georges Bank haddock. As a direct result of this lawsuit,
the New England Fishery Management Council (NEFMC), which has
advisory authority to put forward ﬁshery management measures
for approval by NMFS, agreed to three large-scale area closures on
Georges Bank and in Southern New England. The three areas closed
were Closed Area I, Closed Area II, and the Nantucket Lightship
Closed Area (Fig. 1). These areas were closed to all ﬁshing gears that
were capable of catching groundﬁshes, including otter trawls, gill-
nets, longlines, and scallop dredges. Year-round closed areas were
established in the Western Gulf of Maine in 1998 and on Cashes
Ledge in 2002 to reduce ﬁshing mortality on Gulf of Maine cod. Indi-
vidual vessels were allocated a baseline number of days at sea based
on their recorded ﬁshing history. Thus, restrictive management
measures were imposed on the U.S. groundﬁsh ﬁshery in the mid-
1990s toreduce ﬁshing mortality on groundﬁsh stocks, in particular
Atlantic cod, haddock, and yellowtail ﬂounder on Georges Bank.
These management measures were effective for some ground-
ﬁsh stocks like Georges Bank haddock, but not for others. In
particular, the Gulf of Maine and Georges Bank Atlantic cod stocks
Fig. 2. Trends in commercial catch biomass (shaded area, kt) and ﬁshing mortality
(solid line, average for ages 4–7) for Georges Bank haddock from 1931 to 2004.
J. Brodziak et al. / Fisheries Research 94 (2008) 123–132 125
Fig. 3. Trends in Georges Bank haddock spawning biomass (SB, solid line) during
1931–2004 and recruitment (R, solid bar) during 1931–2005 along with projected
spawning biomass (median and interquartile range) during 2005–2009 and pro-
jected recruitment (average plus one standard error) during 2006–2009 under the
Amendment 13 stock rebuilding plan.
continued to experience overﬁshing through the late-1990s. The
lack of progress in reducing ﬁshing mortality on cod led the CLF
and four other environmental organizations to sue NMFS again in
1999. In this lawsuit, the Plaintiffs asserted that NMFS was not in
compliance with its legal mandate to cease overﬁshing (reduce F
to or below FMSY) on Atlantic cod and other groundﬁsh stocks. The
environmental organizations prevailed in this lawsuit. As a result,
the U.S. District Court for the District of Columbia required that
NMFS and the NEFMC complete Amendment 13 (NEFMC, 2003,
see below), a comprehensive plan to end overﬁshing on all New
England groundﬁsh stocks.
In this study we describe the nascent recovery of the Georges
Bank haddock stock. Research survey and stock assessment data
are used to assess changes in stock status and population dynamics
from the 1930s to the present. We focus special attention on the
exceptional 2003 year class and consider the conﬂuence of factors
that led to increased stock productivity. Mean weights and sizes at
age of adult haddock have decreased in recent years and compen-
satory responses of haddock growth and recruitment to changes in
stock density are also assessed. We discuss some remaining chal-
lenges to managing this recovering transboundary resource in a
changing multispecies ﬁshery.
Research survey data from the Northeast Fisheries Science Cen-
ter (NEFSC) autumn and spring bottom trawl surveys were used
to index the relative abundance at age, growth, weight at length,
and spatial distribution of haddock. The NEFSC has conducted bot-
tom trawl surveys of the NE continental shelf ecosystem since
the 1960s (Grosslein, 1969; Azarovitz, 1981); the autumn bottom
trawl survey began in 1963 and the spring bottom trawl survey
began in 1968. These standardized survey data include indices
of cohort abundance for GB haddock in autumn for 1963–2005
and in spring for 1968–2005 (Brodziak et al., 2006). They also
include size-at-age data for individual cohorts since 1961, individ-
ual weight-at-length data since 1992, and spatial distribution data
since 1963. In addition, the Canadian Department of Fisheries and
Oceans (DFO) initiated a winter bottom trawl survey on Georges
Bank in 1986. This survey also provides age-speciﬁc number per
tow indices for Georges Bank haddock during 1986–2004 (Van
Eeckhaute and Brodziak, 2004). Together, these surveys track the
relative abundance of year classes for estimation of stock size and
ﬁshing mortality and are used to compare the abundance, growth,
condition factor, and spatial distribution of the 2003 YC in compar-
ison to other cohorts of Georges Bank haddock.
We collected data from recent stock assessments of the Georges
Bank haddock stock (Brown and Munroe, 2000; Brodziak et al.,
2006) to document changes in stock abundance and ﬁshery impacts
through time. The most recent stockassessment provided estimates
of spawning biomass, recruitment, and ﬁshing mortality through
calendar year 2004 (Brodziak et al., 2006). These estimates were
derived from tuned virtual population analysis (VPA) as in Brown
and Munroe (2000) and Brodziak et al. (2006). These data were
also used to evaluate the association between survival ratios and
spawning through time. Fishery mean weights at age of haddock
were collected from Clark et al. (1982) and Brodziak et al. (2006) to
assess changes in mean weight across cohorts through time.
The research survey and stock assessment data were analyzed
to assess changes in stock status and population dynamics from the
1930s to the present. Research survey data were used to ﬁt cohort-
speciﬁc von Bertalanffy growth curves during 1961–1996 using
the likelihood method of Kimura (1980). Allometric length–weight
parameters were ﬁtted to research survey weight-at-age data from
1992 to 2002 using the low-bias estimator of Hayes et al. (1995).
Spearman rank correlations between annual Georges Bank had-
dock commercial ﬁshery weights at age (age-2 through age-9+)and
spawning biomass were calculated to investigate the associations
between ﬁsh weight and biomass density. Associations between
haddock recruitment strength on Georges Bank and in the Gulf of
Maine (Fig. 1) were assessed using the Spearman correlation coef-
ﬁcient between VPA estimates of recruitment and age-1 survey
abundance indices from the Gulf of Maine. Similarly, the associ-
ation between the NEFSC autumn survey age-0 haddock survey
index and VPA estimates of recruitment was evaluated using the
Spearman correlation coefﬁcient. The odds of achieving recruit-
ment above its 1931–2005 median value when spawning biomass is
over 75 kt were evaluated using Fisher’s exact test applied to a 2×2
contingency table of stock-recruitment data using the approach of
Brodziak et al. (2001).
3.1. Survey abundance indices
The NEFSC spring and autumn abundance indices exhibit sim-
ilar trends through time (Fig. 4). Autumn indices declined from
record highs in the 1960s to low levels in the early-1970s. The
Fig. 4. U.S. and Canadian research survey abundance indices for Georges Bank had-
126 J. Brodziak et al. / Fisheries Research 94 (2008) 123–132
spring and autumn indices both increased in the mid-1970s due
to the strong 1975 and 1978 year classes and then declined in the
early 1980s. Both U.S. and Canadian abundance indices were low
from the mid-1980s to the mid-1990s and have since increased.
The NEFSC autumn survey age-0 haddock index exhibited a signiﬁ-
cant positive rank correlation with estimated recruitment (R=0.83,
P< 0.001). Overall, the survey indexseries show a consistent pattern
of a rapid increase in haddock abundance since 2000.
3.2. Spawning biomass
During 1931–1960, Georges Bank haddock biomass was rela-
tively high, averaging 102kt (Fig. 3). Spawning biomass increased
in the late-1950s through early 1960s coincident with the impo-
sition of a minimum trawl mesh size of 4.5in. in 1954 (Graham,
1952), the ﬁrst regulatory measure applied to the haddock ﬁshery.
The increase in mesh from an average of about 2.5 in. undoubt-
edly reduced the wasteful discard of undersized haddock that had
diminished ﬁshery productivity since the 1930s(Herrington, 1935).
The reduction in juvenile mortality is believed to have been an
important factor in building haddock spawning biomass to roughly
200 kt in 1962, the highest ever observed.
Georges Bank haddock spawning biomass changed substan-
tially during the next four decades. While spawning biomass
remained relatively high during the mid-1960s averaging 132kt
during 1963–1968 (Fig. 3), it subsequently declined to a near-
record low of 15 kt in 1973 due to overﬁshing. Spawning biomass
almost doubled to an average of 48kt during 1975–1984 with
the production of two large year classes. Spawning biomass then
declined again to average about 23kt during 1985–1994, reach-
ing a record low of 15 kt in 1993. During the mid-1990s, spawning
biomass began to increase and averaged 50 kt during 1995–2000.
Since 2001 spawning biomass has approached levels observed
in the 1960s and averaged 115 kt during 2001–2004. Spawning
biomass increased by 22% from 96 kt in 2001 to 117 kt in 2004.
Despite marked increases in recent years, however, spawning
biomass in 2004 was still less than 50% of the rebuilding target
of BMSY = 250.3 kt.
Recruitment of Georges Bank haddock also ﬂuctuated substan-
tially during 1931–2005 (Fig. 3). Recruitment was relatively high
and stable during 1931–1960, averaging 75 million age-1 recruits
(Fig. 3). Recruitment during 1961–1968 averaged 93 million ﬁsh and
was dominated by the exceptional 1963 year class (462 million age-
1 ﬁsh). Recruitment declined to average only 8 million ﬁsh during
1969–1974 and subsequently increased to average 26 million ﬁsh
during 1975–1984 primarily due to the strong 1975 (106 million)
and 1978 (84 million) year classes. Recruitment declined again to
average only 8 million ﬁsh during 1985–1994. In the mid-1990s,
recruitment steadily increased to average 22 million ﬁsh during
1995–2000. Since 2001, recruitment has averaged 179 million ﬁsh.
In particular, the 2003 YC is the highest recruitment on record,
with an estimated size of 789 million age-1 ﬁsh. Bootstrap anal-
ysis indicates that the CV on the size of this cohort at age-2 at the
start of 2005 (645 million ﬁsh) was about 41%. Thus, although the
2003 YC is very abundant, its absolute magnitude remains uncer-
3.4. Fishery yield
The Georges Bank haddock stock has been commercially
exploited since the 19th century with stock assessment informa-
tion beginning in 1931 (Fig. 2). Since then, the ﬁshery for Georges
Bank haddock has gone through sevenperiods: (1) the initial expan-
sion from 1904 to 1923 when annual nominal catches averaged
17.4kt; (2) the rapid expansion and decline during 1924–1930 when
catches averaged 73.2 kt; (3) the 30-year period of ﬁshery sta-
bility during 1931–1960 when annual catch averaged 46.3kt; (4)
the rapid expansion and decline during 1961–1968 when catches
averaged 73.0kt; (5) the pre-Hague line ﬁshery during 1969–1984
when catches averaged about 13.5 kt; (6) the ﬁshery nadir during
1985–2000 when catches averaged only 5.6kt; and (7) the nascent
recovery from 2001 to 2004 when annual catches have increased
to average 13.7kt per year. Catches have increased each year since
1995 with the exception of 2003 as the stock has been rebuild-
ing under restrictive management measures in the Georges Bank
region. In 2004, total commercial catch was 17.6 kt, over sevenfold
larger than the lowestrecorded catch taken in 1995 but less than 1/3
of the yield sustained during 1931–1960. Thus, ﬁshery yields have
not increased as rapidly as stock size, in part due to restrictions on
the bycatch of cod.
3.5. Fishing mortality
Fishing mortality on Georges Bank haddock has also changed
substantially through time. The ﬁshing mortality (F) rateon Georges
Bank haddock was relatively high with a long-term decline dur-
ing 1931–1960 (Fig. 2). Since 1963, Fhas ranged from less than
0.1 to over 0.6 (Fig. 2). Fwas high during the 1960s averaging
0.52 during 1963–1968 and subsequently declined to a low of
0.06 in 1974. Fincreased substantially in the mid-1980s and aver-
aged 0.35 during 1985–1994. Fishing mortality declined in the
mid-1990s and has remained below the overﬁshing threshold of
FMSY = 0.26 since 1995. In particular, the 1995–2004 decade is the
longest continuous period of time that the Georges Bank had-
dock stock has not been experiencing overﬁshing since the early
Cohort-speciﬁc growth curves based on research survey size-at-
age data show that the exceptional 1963 YC grew slower than the
average cohort-speciﬁc growth pattern during 1961–1996 (Fig. 5).
Predicted curves indicate that mean lengths at ages 2 and 3 were
about 15% lower than average for the 1963 YC. In comparison, the
strong 1975 YC, which was about 1/4 of the size of the 1963 YC,
exhibited close to average growth through its lifetime. This suggests
Fig. 5. Observed mean size at age and 80% conﬁdence interval for the 2003 Georges
Bank haddock year class collected during NEFSC during autumn20 03 through spring
2007 in comparison to von Bertalanffy estimates growth curves for the 1963 and
1975 year classes and the 1961–1996 average growth curve. Age-1 on the x-axis
corresponds to the observation of the 2003 YC at age-1 during spring 2004.
J. Brodziak et al. / Fisheries Research 94 (2008) 123–132 127
Fig. 6. Observed weight at length (solid dot) and 95% conﬁdence interval along with average length (OBS) of the 2003 Georges Bank haddock year class during the NEFSC
(a) autumn 2003, (b) spring 2004, (c) autumn 2004, (d) spring 20 05, (e) autumn 2005, and (f) spring 2006 surveys in comparison to the average length–weight curves (solid
line) during NEFSC autumn and spring surveys during 1992–2002.
that strong year classes of Georges Bank haddockmay have a typical
growth pattern whereas exceptional year classes on the order of
200 million or more age-1 ﬁsh may experience density-dependent
growth with a smaller mean size at age.
Mean size at age of the 2003 YC has been well-below average
since it was ﬁrst observed in autumn 2003 (Fig. 6), and it appears
to be smaller than that exhibited by the 1963 YC, the previous
record YC (486 million age-1 ﬁsh). The slower growth of the 2003
YC indicates it will begin to recruit to the ﬁshery at age-4 in 2007,
instead of the typical pattern of recruitment to the ﬁshery at age-3.
In particular, if the 2003 YC has a similar growth pattern as the
1963 YC, then it will reach the U.S. minimum legal commercial
size of 48 cm at least 1 year later than an average cohort. This sug-
gests that density-dependent growth will delay the availability of
the 2003 YC to be landed in the commercial ﬁshery by at least 1
3.7. Weight at length
Allometric length–weight relationships show that the excep-
tional 2003 YC had signiﬁcantly lower mean weight at length
than the recent average length–weight relationship for 1992–2002
(Fig. 6). The condition factor of the 2003 YC at age-0 was near or
slightly below the recent average during autumn 2003 (Fig. 6a). The
percentage of the age-0 autumn 2003 samples with below average
weight at length was 71%with a 95% conﬁdence interval (CI) of (66%,
75%). At age-1 in spring 2004, the condition factor of the 2003 YC
was also signiﬁcantly lower than average (Fig. 6b) and the propor-
tion of age-1 spring 2004 samples with below average weight was
97% with a CI of (93%, 99%). Similarly, during autumn 2004 through
autumn 2005, the condition factor of the 2003 YC was signiﬁcantly
below average. The percentages of the 2003 YC samples with below
average weight at length during autumn 2004, spring 2005, and
128 J. Brodziak et al. / Fisheries Research 94 (2008) 123–132
Fig. 7. Trends in Georges Bank haddock commercial ﬁshery mean weights at age
(kg) for age classes 3–7 (solid lines with numbered circle indicating age class) along
with trends in spawning biomass (dashed line), 1931–2004.
autumn 2005 NEFSC surveys were 93% (CI of (89%, 96%)), 94% (CI of
(91%, 96%)), and 87% (CI of (83%, 90%)). Overall, the condition fac-
tor of the 2003 YC has been consistently below average, suggesting
that intraspeciﬁc competition for food may be limiting growth of
To investigate this possibility, the food habits of the 2003 YC
were opportunistically sampled during the NEFSC autumn 2003
and spring 2004 surveys to discern whether the diet composition
was anomalous. Analyses of over 1000 stomachs indicated that the
diet composition of the 2003 YC was not atypical and consisted pri-
marily of gammarids, caprellids, and other small crustaceans (see,
for example, Brodziak, 2005). The observation of a normal diet of
the 2003 YC combined with its low observed condition factor sug-
gested that a reduced per capita ration was likely the cause of its
smaller weight at length, on average.
3.8. Fishery mean weights at age
Commercial ﬁshery mean weights at age ﬂuctuated syn-
chronously across ages throughout the 1930s–1960s (Fig. 7). Mean
weights at age increased substantially in the 1970s when spawn-
ing biomass declined. Weights at age for age classes 5–7 gradually
declined through the from peak values in the early 1970s to long-
term average in the 2000s. In contrast, weights at age for age classes
3 and 4 were more stable during the 1980s–1990s but also show
a sharp decline in recent years. Overall, the trends in spawning
biomass and mean weights appeared to suggest an association of
increasing weight at age with declining adult biomass.
Correlation analyses indicated there was a strong positive asso-
ciation between changes in weight at age between age classes
(Fig. 8). Correlations () among weight-at-age values were positive
and ranged from a low of =0.46 to a high of = 0.92. In contrast,
there was a negative association between means weights at age
and spawning biomass (Fig. 8). Signiﬁcant negative associations
were detected between spawning biomass and mean weights at
Fig. 8. Scatterplots of Georges Bank haddock commercial ﬁshery mean weights at age for age-2 (Age2)through age-8 (Age8) and age-9 and older (Age9) along with spawning
biomass (SB) during 1931–2004.
J. Brodziak et al. / Fisheries Research 94 (2008) 123–132 129
Fig. 9. Spatial distribution of the 1963 and 2003 year classes of Georges Bank haddock in the Georges Bank–Gulf of Maine regioncaptured at age-0 during the 1963 and 2003
NEFSC autumn bottom trawl surveys.
age-2 through age-9+ (P<0.001), with negative rank correlations
ranging from R=−0.66 to −0.75. Overall, changes in commercial
ﬁshery weight at age were inversely related to changes in spawn-
ing biomass, indicating possible density-dependence in haddock
3.9. Spatial distribution
Spatial distribution plots of the 1963 and 2003 year classes at
age-0 (Fig. 9) show that the 2003 YC had a more southwesterly dis-
tribution than the comparably abundant 1963 YC. In particular, the
distance between the centroids of distribution of the 2003 and 1963
YCs was about 177km. In 1963, age-0 haddock were abundant in the
Gulf of Maine, but in 2003, they were largely absent. This difference
in abundance of age-0 haddock in the Gulf of Maine and Georges
Bank is atypical since recruitment of Georges Bank haddock was
signiﬁcantly positively correlated with NEFSC age-0 survey catch
number per tow in the Gulf of Maine during 1963–2004 (R= 0.53).
This suggested that haddock recruitment strength in the Gulf of
Maine and Georges Bank regions was typically synchronous, but
that this pattern did not occur in 2003.
3.10. Survival ratios
Survival ratios of Georges Bank haddock, as indexed by recruit-
ment per spawning biomass, have ﬂuctuated about an average of
0.70 recruits per kg (R/S) during 1931–2004 (Fig. 10). Survival ratios
averaged 0.76 R/S with a standard error of 0.06 during 1931–1960
when spawning biomass averaged 102 kt. Since then survival ratios
have declined 13% on average to 0.66 R/S with a standard error
of 0.18 during 1961–2004 when spawning biomass averaged 64 kt.
Although the decline in survival ratios since the 1960s is not statisti-
cally signiﬁcant, it may reﬂect an important change in productivity
of the Georges Bank haddock stock. Similarly, the coefﬁcient of vari-
ation of survival ratios during 1961–2004 (27%) was over threefold
higher than during 1931–1960 (8%) indicating that variability in
early life history survival has also increased in recent decades.
Since 1961, three strong year classes (>100 million recruits) had
survival ratios of roughly 3 or more; these were the 1963, 1975,
and 2003 year classes (Fig. 10). Each of these year classes experi-
enced high survival during early life history stages, suggesting the
inﬂuence of favorable environmental conditions for large recruit-
ment events. Regardless, a positive association between spawner
130 J. Brodziak et al. / Fisheries Research 94 (2008) 123–132
Fig. 10. Annual survival ratios of Georges Bank haddock, indexed by the number
of recruits per kilogram of spawning biomass, along with the average survival ratio
(dashed line) during 1931–2004.
abundance and survival ratios was also suggested since survival
ratios average 0.82 when spawning biomass is over 75kt in com-
parison to only 0.59 (−28%) when spawning biomass is less than
3.11. Stock–recruitment relationship
Spawner abundance is clearly an important determinant of
Georges Bank haddock recruitment strength (Fig. 11). Analyses of
stock–recruitment data indicate that spawning stock size affects
recruitment of Georges Bank haddock (Brodziak and Legault, 2005;
Brodziak et al., 2001; NEFSC, 2002). In particular, Brodziak et al.
(2001) found that when spawning stock biomass is above 82 kt, the
odds of recruitment being above average is 20 times greater than
when biomass is below that level and the average YC size is ﬁvefold
higher using data from 1931 to 1998.
In a subsequent analysis, the Working Group on the Re-
evaluation of Reference Points for New England Groundﬁsh
determined that an appropriate productivity threshold for Georges
Bank haddock was 75kt of spawning biomass (NEFSC, 2002).
Using this cutoff and the most recent stock assessment data, aver-
age recruitment at high spawning biomass (>75kt) is 94 million
age-1 ﬁsh (Fig. 11) while average recruitment is about 20 mil-
lion ﬁsh at low spawning biomass (<75kt). The odds of achieving
recruitment above its 1931–2005 median value when spawning
Fig. 11. Relationship between Georges Bank haddock recruitment strength (age-1
ﬁsh) and spawner abundance (kt) during 1931–2004 along with mean recruitment
() above and below the threshold spawner abundance of 75kt.
biomass is over 75 kt are 23 times greater than when spawning
biomass is less than 75 kt. This difference is statistically signiﬁcant
(P< 0.001) based on Fisher’s exact test applied to the 2 ×2 contin-
gency table of stock–recruitment data. Furthermore, the average
spawning biomass that produced the 12 large year classes of over
100 million age-1 ﬁsh since 1931 was 110kt. Of these 12 YCs, the
smallest was the 1975 year class which wasproduced by a spawning
biomass of 22 kt. The remainder of the large haddock YCs (the 1936,
1939, 1940, 1948, 1950, 1952, 1958, 1959, 1962, 1963 and 2003)
were all produced by spawning biomasses of greater than 75 kt.
This underscores the importance of maintaining adequate spawner
abundance on the productivity of the Georges Bank haddock stock.
3.12. Biological reference points
Biological reference points provide benchmarks for determin-
ing whether Georges Bank haddock are being overﬁshed or are
in an overﬁshed condition. Georges Bank haddock are currently
managed according to the U.S. Sustainable Fisheries Act of 2007
(NOAA, 2007) which requires that ﬁshery conservation and man-
agement measures prevent overﬁshing and rebuild depleted stocks
to biomasses consistent with producing maximum sustainable
yield (MSY). Overﬁshing occurs wheneverﬁshing mortality exceeds
a threshold that jeopardizes the reproductive capacity of a stock to
produce maximum sustainable yield. For Georges Bank haddock,
spawning biomass (BMSY) and the ﬁshing mortality to produce MSY
(FMSY)areBMSY = 250.3 kt and FMSY = 0.26 (NEFSC, 2002). Guide-
lines to the Act also specify that an overﬁshed resource is one
that has been reduced below a minimum stock size threshold.
For Georges Bank haddock, the minimum stock size threshold
is one-half the biomass needed to produce MSY (BMSY). That
is, the overﬁshed threshold (BTHRESHOLD) for Georges Bank had-
dock is BTHRESHOLD = (1/2)BMSY =125.2kt. The overﬁshing threshold
(FTHRESHOLD) for Georges Bank haddock is FTHRESHOLD =FMSY = 0.26. It
is possible for a stock to be classiﬁed as overﬁshed (due to previous
overharvesting) even though the annual harvest rate is below the
overﬁshing threshold. This has been the case for haddock, which
has been rebuilding under low ﬁshing mortality rates in recent
3.13. The recovery plan
The formal rebuilding plan for Georges Bank haddock adopted
in Amendment 13 calls for ﬁshing at the overﬁshing threshold
FMSY = 0.26 during 2004–2008 (NEFMC, 2003). In 2009, the ﬁshing
mortality would be reduced marginally to FREBUILD = 0.245, a value
projected to produce at least a 50% chance that spawning biomass
will meet or exceed BMSY =250.3 kt in 2014. This rebuilding strategy
is subject to change in 2008 if observed progress towards rebuilding
spawning biomass or reducing ﬁshing mortality is not consistent
with the projected rebuilding trajectory.
To measure progress towards stock recovery, the projected
Amendment 13 rebuildingtrajectory for Georges Bank haddock was
compared to VPA estimates of spawning biomass and ﬁshing mor-
tality in 2004. Haddock has an adaptive rebuilding plan in which
the ﬁshing mortality to rebuild the stock is equal to the overﬁsh-
ing threshold during 2004–2008, i.e., FREBUILD =FMSY = 0.26, and in
2009 the rebuilding Fwill be adjusted to meet the goal of achieving
BMSY by 2014. Median spawning biomass for the haddock rebuilding
trajectory (SBREBUILD) was projected to be 130 kt in 2004. In compar-
ison, the 80% conﬁdence interval for SB2004 was (98, 139)kt. Thus,
the SBREBUILD value falls within the probable range of the VPA esti-
mate of SB2004. Similarly, the 80% conﬁdence for F2004 was (0.21,
0.31) and the FREBUILD =0.26 value falls within the probable range
of the VPA estimate of F2004. Overall, 2004 estimates of spawning
J. Brodziak et al. / Fisheries Research 94 (2008) 123–132 131
biomass and ﬁshing mortality indicate that Georges Bank haddock
is on the path to stock recovery.
In addition, projected increases in Georges Bank haddock
spawning biomass from the most recent assessment (Fig. 3;
Brodziak et al., 2006) suggest that the spawning biomass will likely
reach BMSY in a few years. If this projection is realized, the Georges
Bank haddock stock will have been rebuilt in less than the legally
mandated 10-year time horizon.
The Georges Bank haddock stock responded positively to
changes in ﬁshing mortality during the 1990s. Under persistent
overﬁshing in the 1980s, Georges Bank haddock spawning biomass
declined almost 80% from 67 kt in 1980 to less than 15 kt in 1993.
Since 1994, spawning biomass has increased substantially as ﬁsh-
ing mortality decreased. By 2003, spawning biomass had increased
to 132kt, the highest abundance of adult spawners since 1966
and over a ninefold increase since 1993. Even though stock size
has increased markedly in recent years, the Georges Bank haddock
stock was still considered to be overﬁshed in 2004 since spawning
biomass was less than one-half of the rebuilding target. Nonethe-
less, estimates of stock size indicate that the stock is on the path
to recovery and projections indicate that the stock is likely to be
rebuilt in a few years.
One of the challenges facing U.S. ﬁshery management is the
question of how to access a recovering haddock stock with year-
round groundﬁsh closures. Several innovative gear designs have
been developed to reduce the catch of cod in otter trawl gear.
These so-called haddock separator trawls are now a requirement
for participation in the haddock Special Access Program in the east-
ern Georges Bank haddock management area. Another innovative
development was the use of fabricated baits by hook and line ﬁsh-
ermen. Experimental data show that using the fabricated bait to
target haddock also reduced the bycatch of cod to acceptable lev-
els. This innovation allowed for the developmentof a Special Access
Program for hook and line ﬁshermen to ﬁsh for haddock in Closed
Area I. This, in turn, provided an economic opportunity for small-
vessel operators who previously only targeted cod using traditional
baits like squid, mackerel, or herring. Overall, the innovation of the
ﬁshing industry may help it to survive through lean times when
many New England groundﬁsh stocks are still well below their
Recruitment of Georges Bank haddock also displayed a positive
response to reduced ﬁshing mortality. Recruitment averaged only 8
million age-1 recruits per year during 1980–1993. Since 1994, aver-
age recruitment has increased over 10-fold to about 87 million ﬁsh.
Further, prospects remain positive for continued high recruitment
since spawning biomass is currently above the 75kt threshold.
Recent U.S. and Canadian assessments and research survey data
provide empirical support to the assessment model estimates that
the 2003 year class is exceptionally abundant. If this exceptional
cohort can be protected from excessive discarding and high ﬁshing
mortality, it has the potential to rebuild the Georges Bank had-
dock spawning biomass to over its estimated BMSY of 250 kt in
the near future. This would be a remarkable change in resource
abundance given that spawning biomass reached a record low of
15kt in 1993.
Recruits per spawner data shows that survival ratios for Georges
Bank haddock were relatively low from the late-1960s to early-
1990s in comparison to historic ratios during the 1930s–1960s. The
impact of the large-scale area closures, reductions in ﬁshing effort,
and trawl mesh size increases during the 1990s appears to have had
a positive effect on recruits per spawning biomass (R/SB). During
1980–1993, R/SB averaged about 0.33 recruits per kilogram. Since
1994, average R/SB, excluding the exceptional 2003 year class, has
increased to 0.46 recruits per kilogram. Further increases in R/SB
may still occur since, at least historically, the expected value of R/SB
was higher. Overall, the recent increases in R/SB indicate that sur-
vival ratios are approaching the historical average of about 0.76
recruits per kilogram observed during 1931–1960, despite recent
decreases in ﬁsh size at age. If the recent increases in recruitment
and survival can be sustained, it is possible that historical yields on
the order of 50 kt per year may be achievable.
The exceptional 2003 haddock year class was inﬂuenced by pos-
itive maternal and environmental conditions. Haddock spawning
biomass in 2003 was the highest since 1967. Further, the spawn-
ing biomass of repeat spawners (age-5 and older) was 56.9kt in
2003, the highest observed since 1968. High spawning output
from a broad age structure of mature spawners combined with
favorable environmental conditions to produce very high early life
history survival. One favorable environmental condition appears to
have been the geostrophic currents caused by southwesterly wind
stresses during spring 2003 which led to the southerly distribu-
tion of age-0 haddock in the Mid-Atlantic Bight during the autumn
NEFSC survey, similar to that observed in 1987 (Polachek et al.,
1992). This wind pattern would be expected to enhance retention
of haddock eggs and larvae on Georges Bank and improve survival
of the 2003 YC (Fig. 10). In addition, a strong fall phytoplankton
bloom in 2002 appears to have been a key factor in the formation
of the 2003 YC (Friedland et al., in press). In this case, an increase
in the quantity and quality of haddock reproductive output would
be expected due to enhanced adult feeding conditions.
Our analyses of haddock size at age and condition factor indicate
that the 2003 year class is experiencing compensation in growth
rate. The pattern of density-dependent growthof the 20 03 YC needs
to be considered in near-term management measures. If this YC
was heavily targeted in 2006, many of the ﬁsh would have been
below the U.S. legal minimum size of 48 cm. Based on our analyses,
the potential for high discard rates appears to have been substan-
tial. For Canadian ﬁshermen, this issue is less of a concern because
Canada does not impose a minimum haddock size and the Cana-
dian ﬁshermen are mandated to bring in all of their catch to count
against their TAC. Regardless, setting an appropriate minimum size
is important for U.S. ﬁshery management giventhe observed reduc-
tions in mean length at age of recent Georges Bank haddock cohorts
and the apparent density-dependent growth of this stock (Brodziak
and Link, in press).
One of the striking aspects of the haddock stock is the threshold
in productivity that appears around 75–85 kt of spawning biomass.
There are several hypotheses that may explain whysuch a threshold
might exist including expansion of spawning activity in space and
time to hedge risks of egg and larval survival, fecundity increases
more than linearly with weight at age for older haddock, improved
egg quality due to higher proportions of multiple spawning females
in the stock, increased chances of secondary fertilization due to
adequately sized spawning aggregations, and more eggs to escape
opportunistic zooplankton predators. Of these, the two hypotheses
that are most readily testable are the questions of increased fecun-
dity at older ages and improved egg quality from older females
(Berkeley et al., 2004). While there was a small-scale cooperative
research effort to estimate haddock fecundity in 2005, there is no
long-term research effort to assess changes in fecundity through
time. While it is not surprising in this era of reduced scientiﬁc bud-
gets that there is a lack of funding for expanding fecundity research
initiatives, we believe investigating the importance of parental con-
dition is an important research topic that needs to be addressed.
The challenges of joint management of the transboundary
Georges Bank haddock stock became evident in 2005. While the
132 J. Brodziak et al. / Fisheries Research 94 (2008) 123–132
Canadian ﬁshery took its allocated share of the total TAC, the U.S.
ﬁshery on eastern Georges Bank was closed in August 2005 because
the Atlantic cod bycatch TAC was projected to be taken. Protection
of the depleted Georges Bank cod stock required that some U.S.
haddock yield had to be forgone. This situation may continue to
occur in the near future until the cod stock begins to show signs
of recovery as well. Overall, ﬁshery closures due to restrictions on
cod bycatch may also contribute to faster rebuilding of the Georges
Bank haddock stock.
One of the salient points of the nascent haddock recovery is that
ﬁshery management can work. Keeping ﬁshing mortality below the
overﬁshing threshold can produce tangible economic beneﬁts in
the near term. Instead of writing off the haddock stock in the mid-
1990s, the New England ﬁshery management system responded
with restrictive measures that reduced ﬁshery mortality on this
stock. The realization that depleted stocks can recover needs to
be taken to heart by skeptical resource stakeholders (Saﬁna et
al., 2005). Hopefully, Georges Bank haddock stock will not be an
isolated case and other New England groundﬁsh stocks, such as
Georges Bank cod, will recover despite recent declines in stock
productivity (Shelton et al., 2006).
We thank Drs. E. Brooks and C. Needle for their helpful com-
ments on the draft manuscript. We thank our colleagues in the
NEFSC Ecosystems Survey Branchfor their assistance and also thank
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