Estuaries
Vol. 19, No.4, p. 769-777
December 1996
Reproductive Conditions of the Atlantic
Sturgeon (Acipenser oxyrinchus) in the
Hudson River
J.
J.
S. I. DOROSHOV
D.
G. WATSON
S. MOORE
G. P.
J.
LINARES
P. VAN EENENNAAM 1
MOBERG
University of California
Animal Science Department
Davis, California 95616
ABSTRACT: Ninety-four prespawning adult Atlantic sturgeon (Acipenser oxyrinchus) were sampled in the Hudson River
for age, sex, body size, gonad weight, fecundity, mature oocyte size, and plasma concentrations of gonadotropins, sex
steroids, and vitellogenin during the spring spawning migrations in 1992 and 1993. In males, the age and total length
ranged from 12 yr to 19 yr and from 133 em to 204 em and in females from 14 yr to 36 yr and from 197 em to 254 em.
The majority of males were 13-16 yr old, and females were 16-20 yr old. Some females had residual atretic ovarian
bodies, presumably remaining from a previous spawning and indicating iteroparity. Pre-ovulatory condition was recognized by migration of the germinal vesicle or by germinal vesicle breakdown and by significantly elevated plasma gonadotropins, progesterone, and vitellogenin. All pre-ovulatory females were captured upriver from Hudson River kilometer
136. Individual fecundity ranged from 0.4 million to 2.0 million eggs and oocyte diameter from 2.4 mm to 2.9 mm, and
both characters exhibited a significant (p < 0.05) positive relationship with female body size. Iteroparous females,
tentatively identified by the presence of atretic bodies remaining in the ovary from a previous spawning, had significantly
(p < 0.05) higher fecundity and produced larger eggs, compared with females spawning presumably for the first time.
Introduction
tists since the last century (Ryder 1888; Dean 1893,
1894). More recent reviews were published by Vladykov and Greeley (1963), Magnin (1964), Murawski and Pacheco (1977), Hoff (1980), Van Den
Avyle (1984), Smith (1985), and Gilbert (1989).
The Hudson River Atlantic sturgeon was studied
by Dovel and Berggren (1983) and Young et aI.
(1988). These works gave insight into sturgeon biology, population structure, and fishery management. However, there is very little information on
reproductive development. Smith (1985) provided
fecundity data on the South Carolina Atlantic sturgeon, and Huff (1975) described the ovarian
stages of the Gulf sturgeon (Acipenser oxyrinchus desotoi) in Florida. To our knowledge, there is no information available on reproductive hormones
and metabolites in Atlantic sturgeon.
Our objective was to characterize reproductive
conditions of the spawning population in the Hudson River in relation to age and body size. The
study was part of a larger project aimed to investigate gametogenesis and reproductive hormones
of Atlantic sturgeon during marine and freshwater
life.
The Atlantic sturgeon (Acipenser oxyrinchus) is a
valuable chondrostean species of the eastern coast
of North America. It was historically abundant and
supported a significant fishery including production of caviar (Murawski and Pacheco 1977). However, in most rivers the harvest collapsed during
the early 1900s. In addition to overfishing, industrialization contributed to the population decline
by river damming and pollution. In spite of these
factors, the Hudson River and its estuary still remain one of the major spawning and nursery
grounds for the Atlantic sturgeon. Since 1983 commerciallandings of sturgeon in New York have decreased in the Hudson River and increased in the
coastal waters (Brandt 1988). Resource agencies
are concerned with these trends and are trying to
regulate the fishery to protect the remaining sturgeon population.
The biology, fishery, and artificial propagation of
Atlantic sturgeon has attracted attention of scien1 Corresponding author; tele 916/752-2058; fax 916/7520175.
© 1996 Estuarine Research Federation
769
770
J. P. Van Eenennaam et al.
HUDSON RIVER
Catskill
>-
182 Kilometers
MA
CT
Kingston
>- 148
Hyde Park
•
136
NY
セキ。イエウ ・カ。hMョッエ イc
Tappanzee---::::....=--
NJ
ermen « RKM 64) set their nets (mesh size 3546 em) to the bottom with heavy weights on each
end. The nets were checked daily during slack tide.
The upriver (RKM 64 and upstream) fishermen set
their nets (mesh size 25-35 em) for 15-40 min depending on tide and river traffic, in the shipping
channel at a depth of 12-25 m. Fish collection and
sampling were affected by selectivity of fishing gear
and duration of the commercial fishing season
which lasted from May 15 to July 9, 1992 and from
May 15 to June 15, 1993. However, the large number of Atlantic sturgeon sampled during two consecutive years provides representative data for characterization of the spawning population.
TISSUE SAMPLING
Mter capture, sturgeon were either sampled on
the boat, or on shore during cleaning and processing. Fork length (FL) and total length (TL)
were measured (±0.1 em) in all fish. When possible, total body weight (BW) (±100 g) and gonad
weight (GW) (±l.0 g) were also measured. Samples of the gonadal tissue were excised from the
mid-portion of the gonad and fixed in buffered
formalin. Five subsamples of oocytes from mature
females were collected and weighed (±O.OOOI g)
for fecundity estimates. Blood samples were collected from the caudal vein with heparinized vacutainers, and plasma was separated by centrifugation and stored frozen. One pectoral finray was
removed for ageing.
LABORATORY PROCEDURES
Fig. 1. The Hudson River. Arrows indicate location of Atlantic sturgeon captures.
Materials and Methods
FISH COLLECTION
Ninety-four Atlantic sturgeon (28 females and 66
males) were sampled from the Hudson River commercial fishery during May-July 1992 and MayJune 1993, in the area between Hudson River kilometer (RKM) 45 and 182. Only two sampled fish
were immature: one male (age 9 years, RKM 137)
and one female with previtellogenic ovaries (age
15 years, RKM 64). The remainder were broodfish
in prespawning,spawning or recently spent gonadal conditions. The locations of capture sites are
shown in Fig. l.
Eight commercial fishermen assisted in collecting fish. The fishermen used anchor gill nets that
were 15-100 m long and 2.5-4.0 m deep, with a
stretch bar mesh of 25-46 em. Nets were set perpendicular to the river flow. The downriver fish-
Gonadal Development
The ovary of sturgeon on the spawning grounds
typically contains three clutches of ovarian follicles:
small oocytes in the endogenous growth phase with
undifferentiated chorion; slightly enlarged previtellogenic oocytes with no yolk platelets in the cytoplasm; and large, darkly pigmented oocytes to be
ovulated during spawning. We analyzed the latter
clutch. Oocyte diameter (n = 20) was measured
using a darkfield dissecting microscope with camera lucida, digital image analyzing tablet (Nikon
Microplan II), and a microcomputer interface (accuracy 0.01 mm). Whole oocytes, fixed in buffered
formalin, were bisected with a razor blade along
the animal-vegetal axis and examined under a dissecting scope with a fiber optic illuminator. Distance of the germinal vesicle from the inner border of the oocyte chorion and oocyte diameter
were used to calculate Polarization Index (PI) (distance from chorion divided by oocyte diameter), a
morphologic criterion of oocyte ripeness (Dettlaff
et al. 1993).
The gonads of prespawning Atlantic sturgeon females ate hypertrophied and open to the coelome.
Reproductive Conditions of Atlantic Sturgeon
Ovarian folds contain a distinct clutch oflarge, uniformly sized, pigmented oocytes, contributing 8090% of the total ovarian mass. Fecundity was measured using a gravimetric method similar to that
described by Bishai et al. (1974) and Keenlyne et
al. (1992). The oocytes were counted in five-six
subsamples (1-6 g wet weight) from different parts
of the ovaries of ten females. The subsamples were
cut fragments of the whole ovary (somatic tissue
and germ cells), weighed (±0.1 mg), and fixed in
10% phosphate-buffered formalin. All pigmented
oocytes were separated and counted in each subsample. The measurement unit was the number of
oocytes per 1 g of the ovarian tissue (wet weight).
Coefficients of variation among subsamples (within
female) ranged from 3.1% to 6.5% (mean =
4.6%). Variation between females was 12.9%
(mean ± SD: 107 ± 14 oocytes g-l, n = 10). Low
variability among subsamples indicates reliable estimation of sturgeon fecundity. Ovarian weight and
oocyte diameter measurements were available for
six other females, but no sUbsamples for fecundity
were taken. Their fecundity was reconstructed by
dividing ovarian weight by "one oocyte weight"
(i.e.,l g numbec 1 of ooeytes) calculated from the
regression equation: oocyte weight = 0.00869 0.01313 X oocyte diameter (p < 0.05, r 2 = 0.81)
that was established from females sampled for fecundity.
Iteroparity of females was tentatively evaluated
by the presence of atretic ovarian bodies containing dark pigment. Our recent observations with repeatedly spawned domestic white sturgeon, Acipenser transmontanus, indicate that these atretic follicles were derived from the oocytes that failed to
ovulate during the previous spawning. Ryder
(1888) described this follicle in Atlantic sturgeon
as "degenerating ova with the pigment granules
not aggregated at the surface, but irregularly distributed throughout the substance of the yolk
mass." Faleeva (1965) reported the presence of
similar atretic follicles in mature sterlet, Acipenser
ruthenus. All gonads in this study were examined
histologically (5-j.Lm paraffin sections stained by periodic acid Schiff stain). The description of histological stages and gametogenesis is not included in
this paper. Some ovarian stages were previously described by Huff (1975) in the closely related Gulf
sturgeon.
Plasma Vitellogenin and Reproductive
Hormones
Total plasma calcium concentrations, reflecting
concentrations of plasma vitellogenin (Vg), were
measured by atomic absorption spectrophotometry (Perkin-Elmer spectrophotometer, 422.7 A
wavelength, with a calcium hollow cathode lamp).
771
For validation, plasma samples from eight fish were
analyzed by an enzyme-linked immunosorbent assay (ELISA) with polyclonal rabbit antibody to purified Vg of white sturgeon (Linares-Casenave et al.
1994). The assay format was similar to that developed for siberian sturgeon by Cuisset et al. (1991).
The Vg level exhibited a strict linear relationship
with total plasma calcium measured in the same
samples. We used the linear regression Vg = 42.98
X calcium - 4136.65 (r2 = 0.97) to calculate plasma vitellogenin concentrations in the remaining
females with known concentrations of plasma calcium.
Plasma testosterone and estrogen (E2) were
measured by the radioimmunoassays (RIA) of Gay
and Kerlan (1978) and England et al. (1974), respectively (antisera were provided by G. D. Niswender). The RIA for testosterone is cross-reactive with
ll-ketotestosterone and reflects total plasma androgens (A). Two sturgeon gonadotropins (GTH-1
and GTH-2) were measured by RIAs developed for
white sturgeon by Moberg et al. (1991). The
l7a,2013-dihydroxy-4-pregnen-3-one (17a,2013DHP) was measured by the RIA of Scott et al.
(1982), and the antibody was a gift from Y Nagac
hama (National Institute of Basic Biology, Okazaki,
Japan). The following modifications were made in
the assay. Endogenous plasma-binding proteins
were denatured by addition of a 10-fold excess of
100% ethanol, the sample was centrifuged, and the
supernatant decanted, blown to dryness with an air
stream, and reconstituted in a phosphate-buffered
saline, 0.1 % gel, pH 7.6 to the original sample volume. Four thousand counts per minute (CPM) of
tritium label per assay tube was used. Recovery of
tritiated 17a,2013-DHP from spiked serum samples
was 90%. The assays detection limits were 20.00 ng
ml- 1 for A, 0.05 ng ml- 1 for E2, 0.90 ng ml- 1 for
GTH-1, 1.90 ng ml- 1 for GTH-2, 0.12 ng ml- 1 for
17a,2013-DHP, and 300 j.Lg ml- 1 for Vg.
Age Determination
Age was determined from cross sections (0.2-0.6
mm) of base portions of dried pectoral finrays. Sections polished with increasing grades of wet-dry
sandpaper were mounted on slides and examined
under a dissecting microscope with camera lucida
and digital image analyzer (Nikon Microplan II)
with a fine-point light cursor that was used to count
the annuli and trace their continuity throughout
the section plane. In reading and counting annuli
we followed guidelines of Cuerrier (1951), Probst
and Cooper (1954), Semakula and Larkin (1968),
Sokolov and Akimova (1976), and Brennan and
Cailliet (1991). Ageing was initially conducted on
85 fish by three independent readers who counted
annuli on three replicate finray sections of each
772
J. P. Van Eenennaam et al.
54
TABLE 1. Body size, gonadosomatic index, and age of Atlantic
sturgeon. Data are means, standard deviation, and sample size
in parentheses. All means between the sexes are significantly
different (p :5 0.05).
Females
Fork length (cm)
194.0 :!: 14.9 (28)
Total length (cm)
217.9 :!: 15.8 (28)
Body weight (kg)
72.7 :!: 20.3 (22)
Condition factor (%) 0.94 :!: 0.11 (22)
Gonadosomatic
index (%)
13.84 :!: 5.72 (16)
Age (year)
20:!: 5
(27)
Males
161.7
181.5
37.3
0.83
:!:
:!:
:!:
:!:
14.3
15.4
7.5
0.08
(66)
(66)
(48)
(48)
48
42
セ
36
()
>z
30
::>
24
w
0
w
cc
L1.
18
12
3.97 :!: 1.13 (42)
15 :!: 2
(66)
6
oL-O--------'---------100-115
fish. Agreement between the readers was observed
in 33-40% of all cases, and agreement within ± 1
yr was obtained for 84% of all fish. Maximum disagreement of 3 yr was observed in four fish (5%)
and it was limited to older fish exhibiting some
erosion at the periphery of the finray section, and
in rare cases, in the center of the section (first annulus). Following this procedure and discussion of
disagreements, ageing was completed by the senior
author. Based on our work with semi-anadromous
white sturgeon, ageing of Atlantic sturgeon is more
accurate, and we subjectively estimate the potential
error of 1-2 yr for fish ranging in age from 15 yr
to 30 yr. Ageing of younger fish is more accurate,
with very rare exceptions of the erosion of the first
annulus.
Data Analysis
Individual condition factor was calculated as 100
X BWg/FLcm3, gonadosomatic index (GSI) as 100
X GW/BW. Data were analyzed by descriptive statistics, analysis of variance, and simple linear regressions. Significant differences between sample
means were examined by the Student t-test (two
samples) or the Fisher PLSD test (multiple sampies). A contingency table with a Fisher Exact
Probability test was used to examine proportions
of iteroparous females in different age groups. All
comparisons were considered significant at p <
0.05. SAS software (SAS Institute) was used for statistical processing.
Results
REPRODUCTIVE CONDITIONS OF THE
SPAWNING POPULATION
The majority (56%) of mature males were
caught during the first 10 d of June, and 82% of
the females during the first, second, and third
weeks of June. The second year sampling period
was reduced by new regulations that restricted
commercial fishing on the Hudson River to May
15 through June 15, 1993. Capture of spent males
in early June and the presence of ovulatory and
spent females during the first and third weeks of
115·130
130·145
145-160
160-175
175·190
190-215
215-230
FORK LENGTH (eM)
_
B!iIJ
MALES (N-66)
FEMALES (N-2B)
Fig. 2. Fork length distribution in the spawning cohorts of
Atlantic sturgeon.
June indicate that the breeding season of Atlantic
sturgeon in the Hudson River extends from late
spring to early summer. In 1992, fishermen reported the first capture of a ripe female on May
21 (RKM 101), and the last capture onJuly 9 (RKM
76).
Data on body size, condition factor, gonadosomatic index, and age of broodfish are summarized
in Table 1. Females are larger and older fish, compared to males. Body weight ranged from 47 kg to
125 kg in females and from 27 kg to 53 kg in
males. The females had a significantly higher condition factor and gonadosomatic index, the latter
range was 7-25% in females and 1-6% in males.
Length and age histograms show substantial differences between the sexes, with different modal
classes in males and females (Figs. 2 and 3). Age
of all fish ranged from 12 yr to 36 yr, with approximately a 6 yr overlap between the two sexes. No
males older than 19 yr and no females younger
than 14 yr were present in our collection.
45
40
36
31
セ
>z
()
w
::>
0
27
23
w
18
L1.
14
cc
5
oL-_-----"L.....IL-llOLJ
6
8
__
10 12 14 16 18 20 22 24 26 28 30 32 34 36
AGE (Years)
_
MALES (N-66)
B!iIJ
FEMALES (N-27)
Fig. 3. Age distribution in the spawning cohorts of Atlantic
sturgeon. The X-axis labels indicate the upper age class limit.
773
Reproductive Conditions of Atlantic Sturgeon
0,12 , - - - - - - - - - - - - - - - - - - - - - - - - ,
0,10
0.08
T
!
IT
i'
セ
T
III
___________ セ
M ェ ャセ
0.06
PRE-OVULATORY
.
«
2.68
w
2.61
e
0
I-
w
a:
2.46
«
::;
2.39
0
0.00 L-----'_---L_--'--_-'----_.L..-.----'_---L_--'--__-'------l
32
48
64
80
96
112
128
144
0
::J
I-
OVULATORY
0
0
2.32 '----'_.....L_--'--_-'----_'-------'_---L_--'--_-'------l
160
170
176
182
HUDSON RIVER KILOMETERS
Fig. 4. The relationship between individual oocyte polarization index (mean and standard deviation) and capture site of
Atlantic sturgeon females in the Hudson River. The spaces between the horizontal dotted lines approximate different stages
of maturity as determined by the position of germinal vesicle in
the oocytes. Two females with mature oocytes (germinal vesicle
breakdown) are assigned PI = O.
The ovaries of 18 females were close to final
ovarian maturation, with polarized oocytes and advanced migration of the germinal vesicle. Two females had matured oocytes (germinal vesicle
breakdown). Four ripe females near final ovarian
maturation were kept alive and induced to ovulate
in the hatchery (personal communication, Jerre
Mohler, United States Fish and Wildlife Service,
Lamar, Pennsylvania). Three other sampled females had spent ovaries and one was immature, in
a previtellogenic phase of ovarian development.
No overripe females with atretic oocytes have been
found in this study. All males were mature, with
many males releasing milt during capture and handling on the boat.
Seventeen females were examined for PI of the
oocyte. Dettlaff et al. (1993) considered a PI below
0.07 as a threshold for oocyte maturation and ovulation in Russian sturgeon. The PI of Atlantic sturgeon females was 0.056 ± 0.030 (mean ± standard
deviation, n = 17). Plot of individual PI against the
distance of female capture from the river mouth is
shown in Fig. 4. The majority of females caught
around RKM 136 and upstream were within the
ovulatory threshold zone, or in the process of
spawning. One fish had freely flowing ovulated
eggs and another had matured oocytes still attached to the ovary. In contrast, the oocytes of all
four females caught between RKM 45 and RKM 64
were in a less advanced stage, with PI higher than
0.07. At this stage the sturgeon female does not
respond with ovulation to hormonal injections and
the oocytes do not mature in vitro under stimulation with progesterone (Dettlaff et al. 1993). It appears that females enter the Hudson River with incomplete germinal vesicle migration, which occurs
0
2.54
0
0
-----------------------!Hi--16
0
0
>-
{)
!
o
Rsq .. 0.65
2.75
::;
lJ
y - 1.0643 + .0078x
2.83
P<O.OOO5
a:
w
Iw
1. IlI Tl•
0,04
0.02
2,90
UNDERGOING
POLARIZATION
188
194
200
206
212
218
224
230
FORK LENGTH (CM)
Fig. 5. The relationship between mean oocyte diameter and
female fork length in the spawning cohorts of Atlantic sturgeon
in the Hudson River.
rapidly as fish move to the spawning grounds.
These data also suggest that spawning grounds of
Atlantic sturgeon in the Hudson River are located
upstream from the tidal saltwater front.
The diameter of mature oocytes in sturgeon females ranged from 2.38 mm to 2.88 mm, and the
relationship between oocyte diameter and fork
length of females was significant (Fig. 5). Individual and relative (number of oocytes per kg of body
weight) fecundity ranged from 0.4 million to 2.0
million and 7 thousand to 22 thousand, respectively, and exhibited a significant linear increase with
fork length of females (Fig. 6).
To examine the effect of iteroparity on fecundity
and mature oocyte size, the females were grouped
into four age classes, and proportion of presumably iteroparous fish in each group was determined by the presence of atretic ovarian bodies in
histological sections (Table 2). The difference in
the proportions of iteroparous females between
the youngest (15-17 yr) and the oldest (24-29 yr)
2,10
0
Y - -5,888,552 + 35,580x
1.88
>-
P<O.OOO5
1.66
l-
ez
0"
::J
0
Rsq '" 0.78
1.43
0
w c:
u.
0
..J=
1.21
0
0.99
セ
;;
e
""
0.77
0.54
0.32
GM ⦅ G⦅ MlZ ⦅N N lM⦅NlM セGM ⦅ G⦅
170
_
176
182
188
194
200
206
__'__....L-_.L-----'
212
218
224
230
FORK LENGTH (CM)
Fig. 6. The relationship between individual fecundity and
female fork length in the spawning cohorts of Atlantic sturgeon
in the Hudson River.
774
J. P. Van Eenennaam et al.
TABLE 2. Iteroparity, body size, and reproductive parameters of Atlantic sturgeon females in different age groups. Data are means
and standard deviations. Means with different letters are significantly different (p s 0.05).
Age (yr)
15-17 (n
Iteroparity (proportion)
Fork length (em)
Body weight (kg)
Fecundity (million)
Relative fecundity
(thousand kg-I)
Oocyte diameter (mm)
= 4)
18-20 (n
= 5)
21-23 (n
= 3)
24-29 (n
セ
3)
0.00
184.2 a ::t: 6.4
55.0 a:!: 7.3
0.49 a ::t: 0.10
0.40
191.3 a :!: 8.8
71.4 ab ::t: 9.1
1.00 b ::t: 0.26
0.67
206.2 b:!: 1.9
82.9 b::t: 14.8
1.58 c::t: 0.35
1.00
213.3 b :!: 9.2
89.7 b::t: 21.2
1.67 c::t: 0.31
8.92 a :!: 1.78
2.53 a ::t: 0.12
14.02 b :!: 2.91
2.54 a ::t: 0.08
19.02 c:!: 0.80
2.67 ab ::t: 0.05
18.89 c :!: 2.83
2.78 b::t: 0.12
fish was statistically significant (Fisher's Test, 2 X
2, p = 0.029), although the multiple-test comparison for all four groups did not show significant
difference (4 X 2, p = 0.066). Relative fecundity
and oocyte diameter significantly increased with
age and assumed iteroparity (Table 2). Data suggest that females reach their peak of egg production when they are older than 20 yr and spawn
repeatedly.
REPRODUCTIVE HORMONES, VITELLOGENIN, AND
PLASMA CALCIUM
Plasma concentrations of reproductive hormones, vitellogenin and calcium in the Atlantic
sturgeon males and females are shown in Table 3.
The females were subdivided into three distinct
groups: gravid (with germinal vesicle intact), ovulating (mature oocytes and flowing eggs), and
spent. Males exhibited low concentration of estrogen, moderate concentrations of gonadotropins
(GTH-1 and GTH-2), and were similar with gravid
females in plasma androgens and 17a,2013-DHP.
They had no detectable vitellogenin in circulation,
and their total plasma calcium was at the basal level
of 80-120 J,.Lg ml- I . Females exhibited elevated concentrations of estrogen, gonadotropic hormones,
vitellogenin, and calcium. In the ovulating females,
concentrations of androgens and estrogen decreased, but concentrations of GTH-1, GTH-2,
17a,2013-DHP, vitellogenin, and calcium increased
significantly compared with gravid females. The
spent female (only one recently spawned fish was
sampled) exhibited a decrease in sex steroids, calcium, and vitellogenin levels.
Discussion
Capture records support observations of Dovel
and Berggren (1983) that males migrate to the
spawning grounds earlier than females and probably spend a longer time in the river than females.
Classen (1944) indicates that peak migration ofthe
males in European Atlantic sturgeon (Acipenser sturio) occurs about 2-3 wk before migration of the
females. Our observations on sturgeon captured
with gill nets as well as anecdotal information from
fishermen, indicate that there are always a few resident males in the spawning areas, but when a ripe
female is captured, the number of captured males
also increase. Similar patterns of aggregation of
several males and one female at spawning were observed in Atlantic sturgeon by Dean (1893) in the
Delaware River.
The male and female cohorts differ in age and
size composition, which was documented by Dovel
and Berggren (1983) for the Hudson River and by
Smith (1985) for the mid-Atlantic population. The
difference in average age between the two sexes in
our study was 5 yr, and the mean body weight of
females compared to males was almost twice higher. The youngest reproductively active (recently
spent) female in our study was 14 yr old, but the
majority of ripe females were similar in age (20 yr)
TABLE 3. Plasma concentrations of androgens, estradiol, gonadotropins (GTH-l, GTH-2), 17a,20[:l-dihydroxy-4-pregnen-3-one
(17a,20[:l-DHP), total calcium, and vitellogenin in Atlantic sturgeon. Data are means, standard deviation, and sample size in parentheses. Means with different letters are significantly different (p s 0.05).
Androgens (ng ml- I )
Estradiol (ng ml- I)
GTH-l (ng ml- I )
GTH-2 (ng ml- I)
17a,20[:l-DHP (ng ml- I )
Calcium (fLg ml- 1)
Calculated vitellogenin (fLg ml- 1 )
a
b
126.83
0.33
3.37
1.73
0.50
105
Not available.
Below detection level (300 fLg ml- I ).
a ::t: 62.52
a ::t: 0.15
a ::t: 1.95
a :!: 1.67
a ::t: 0.27
a:!: 9
N.D.b
(51)
(51)
(46)
(46)
(17)
(47)
(4)
11 1.56 ab ::t: 35.02
5.10 b ::t: 4.05
11.15 b ::t: 10.06
10.98 b :!: 13.77
0.24 a ::t: 0.24
156 b :!: 38
2,516 a ::t: 1,204
Spent female
Ovulating females
Gravid females
Males
(10)
(10)
(9)
(9)
(8)
(10)
(10)
56.63 b::t: 38.59
1.99 c ::t: 1.32
25.88 c ::t: 8.48
38.28 c::t: 12.26
3.70 b::t: 3.09
244 c:!: 131
6,533 b ::t: 5,824
(4)
(4)
(4)
(4)
(4)
(4)
(4)
18.40 (1)
0.60 (1)
NN
NN
1.32 (1)
127
(1)
1,322
(1)
Reproductive Conditions of Atlantic Sturgeon
and body size with previous observations of Dovel
and Berggren (1983). In the South Carolina fishery, mature females ranged from 10 yr to 30 yr in
age and from 145 yr to 233 cm in FL (Smith et al.
1984).
Differences in age and size between sexes may
be explained by younger maturity age and possibly,
annual reproductive cycles of males, whereas the
females may have greater individual variation in
age at maturity and longer than 1-yrovarian cycles.
In addition, the females may have an extended life
span, determined by a longer duration of reproductive processes and the importance of larger
body size for efficient egg production. Holcik et al.
(1989) indicated that males of European Atlantic
sturgeon are sexually active for a period of 8 yr
whereas the reproductive life of females is extended to 30 yr. Both European and North American
Atlantic sturgeon are fast growing and relatively
short-lived species compared with other anadromous chondrosteans. However, because of the long
history of the caviar fishery, the proportion of
large and old females may be reduced at present
time, compared to historic records indicating the
average TL of gravid females to be 264 cm (Ryder
1888) .
Previous descriptions of Atlantic sturgeon spawning grounds in the rivers were based on captures
of ovulating and spent females. Borodin (1925) reported that sturgeon in the Delaware River gathered for spawning in an area with swift current and
a hard clay bottom. The ovulating females in our
study were captured in the area of RKM 136. The
majority of ripe and spent females and males were
captured between RKM 136 and 182, and the PI
of the oocytes in ripe females as well as their plasma levels of reproductive hormones and metabolites implicate this part of the river as a major
spawning area. Dovel and Berggren (1983) suggested that Atlantic sturgeon spawn between Croton Point (RKM 55) and Hyde Park (RKM 136).
Our observations suggest that spawning grounds of
Atlantic sturgeon in Hudson River are located further upstream, between Hyde Park and Catskill. It
should be noted that the most upstream tidal salt
front in the Hudson River reaches RKM 98 (Dovel
and Berggren 1983), and chondrostean embryos
and larvae are more sensitive to low salinity than
other bony fish, due to water intake by the early
embryo (Zotin 1953) and lower osmolality of maternal body fluids (McEnroe and Cech 1985). In
addition, the egg and larval dispersal strategy of
sturgeon (Dettlaff et al. 1993) may require that a
sufficient portion of the tidal river downstream
from the spawning site remain fresh water
throughout the spawning season.
Our estimates of fecundity in the Hudson River
775
females are in general agreement with other reports for North American Atlantic sturgeon (Ryder
1888; Vladykov and Greeley 1963; Smith 1985) and
are very similar to data for European Atlantic sturgeon (Holcik et al. 1989). The preliminary data
suggest a significant increase in fecundity and mature oocyte size with age, body size, and iteroparity
of females. Higher fecundity of older iteroparous
females may lend support to a fishery regulation
based on a lower and upper size limit, as it is practiced on the Columbia River (Hanson 1992), with
the maximum size to protect large fecund females
from harvest. However, such regulations should be
approached with caution since it may result in selective pressure on reproduction.
Published information on reproductive endocrinology of chondrosteans is fragmentary, with most
observations limited to cultured white and siberian
sturgeon (Moberg et al. 1991; Pelissero and LeMenn 1991; Moberg and Doroshov 1992; Pavlick
et al. 1993). Plasma concentrations of sex ウエ・イッゥ、セ
in the Atlantic sturgeon were similar with domestic
broodstocks of white and siberian sturgeon during
the reproductive season. Concentration of gonadotropins increased 3-4 times at ovulation (Table
3), particularly GTH-2 which we believe is involved
in final ovarian maturation. The identity of the
maturation-inducing hormone is not known in
chondrosteans (Dettlaff et al. 1993), but 17a 2013DHP was a potent inducer of in vitro oocyte maturation in white sturgeon (Lutes 1985). The female Atlantic sturgeon with ovulated or matured
oocytes had significantly elevated plasma concentration of this hormone, and ripe males also exhibited detectable concentrations (Table 3). The
potential role of this hormone as a natural egg and
sperm maturation steroid in chondrostean species
deserves further investigation.
Ripe and ovulating females of Atlantic sturgeon
had relatively high plasma concentrations ofestrogen, vitellogenin, and calcium (Table 3) compared
to wild white sturgeon in which vitellogenesis ceases sometime before spawning (Chapman et al.
1987; Doroshov et al. 1991). This difference may
relate to the season of spawning migration in these
two species. The white sturgeon migrate up the river during the late fall and winter and complete
ovarian vitellogenesis 1-3 mo before spawning.
North American Atlantic sturgeon and the closely
related European species (Holcik et al. 1989) migrate in rivers during spring and summer seasons,
and may complete vitellogenesis shortly before
spawning. The cessation of vitellogenin uptake by
the oocyte before ovulation and a long half-life of
circulating vitellogenin in chondrosteans result in
elevation of plasma vitellogenin and total calcium
in the ovulated females (Table 3).
776
J. P. Van Eenennaam et at.
In conclusion, our data describe normal reproductive conditions of the spawning population of
Atlantic sturgeon in the Hudson River as indicated
by ovarian development, gonadal hormonal levels,
fecundity, and the absence of females with overripe
eggs or atresia in the advanced clutch of pigmented ovarian follicles. Normal reproductive development in sturgeon is important but not the only
factor determining the success of natural recruitment. The Hudson River and estuary provided excellent conditions for reproduction of the Atlantic
sturgeon as indicated by its historically large population, topography of the river bed, availability of
spawning substrate, high river flow, and significant
production of zooplankton essential for larval survival (Moran and Limburg 1985; Dettlaff et al.
1993). Regulation of river flow, combined with
dredging, diking, pollution, and climatic fluctuations could change the qualities and carrying capacities of Atlantic sturgeon spawning and larval
habitats in the Hudson River. Maintenance of sturgeon spawning and nursery habitat in the Hudson
Estuary deserves special consideration in management of the Atlantic sturgeon.
ACKNOWLEDGMENTS
This research was supported and funded by the Hudson River
Foundation (grant number 007/91A). We would like to thank
all the Hudson River fishermen who assisted in fish collection
and sampling: Ian Burliuk, Jim Carey, Tucker Crawford, Cal
Greenburg, Everett Nack, Steve Nack, Jon Powell, Ian Powell,
and Ian Reed. Without their support and enthusiasm, this research would not have been possible. We appreciate the assistance of Thomas Lake who provided valuable advice and help
during organization of the sampling program, and assistance
from staff at the Hudson River Foundation and the Riverkeeper
field station. Dr. Y Nagahama, National Institute of Basic Biology, Okazaki, Japan, provided the antibody for the 17a,2013-dihydroxy-4-pregen-3-one assay. Special thanks to Robert Boyle
who inspired this study.
LITERATURE CITED
BISHAI, H. M., M. M. ISHAK, AND W. LABIB. 1974. Fecundity of
the mirror carp, Cyprinus carpio L., at the Serow fish farm
(Egypt). Aquaculture 4:257-265.
BORODIN, N. 1925. Biological observations on the Atlantic sturgeon, Acipenser sturio. Tmnsactions ofthe American Fisheries Society
55:184-190.
BRANDT, R. E. 1988. An overview of Atlantic sturgeon in New
York state. Prepared for the Atlantic State Marine Fisheries
Commission. Atlantic Sturgeon Workshop, Norfolk, Virginia.
BRENNAN, J. S. AND G. M. CAILLIET. 1991. Age determination
and validation studies of white sturgeon, Acipenser tmnsmontanus, in California, p. 209-234. In P. Williot (ed.), Acipenser.
Actes du Premier Colloque International sur l'Esturgeon.
Centre National du Machinisme Agricole du Genie Rural des
eaux et des Forets, France.
CHAPMAN, F. A., R. L. SWALLOW, AND S. I. DOROSHOV. 1987.
Ovarian cycle of white sturgeon (Acipenser tmnsmontanus), p.
196. In D. R. Idler, L. W. Crim, andJ. M. Walsh (eds.), Proceedings of the Third International Symposium on Reproductive Physiology ofFish. Memorial University of Newfoundland, St. John'S, Newfoundland, Canada.
CLASSEN, T. E. A. 1944. Estudio bio-estadistico del esturion 0
slodo del guadalquiver (Acipenser sturio L.). Trabajos # 19, Ministerio de Marina, Instituto Espanol de Oceanografia, Spain.
CUERRIER, J. P. 1951. The use of pectoral fin rays for determining age of sturgeon and other species of fish. Canadian Fish
Culturist 11: 10-18.
CUISSET, B., C. PELISSERO, F. LEMENN, AND J. NUNEZ-RoDRlGUEZ.
1991. ELISA for sturgeon vitellogenin, p. 107-111. In P. Williot (ed.), Acipenser: Actes du Premier Colloque International
sur l'Esturgeon. Centre National du Machinisme Agricole du
Genie Rural des eaux et des Forets, France.
DEAN, B. 1893. Notes on the spawning conditions of the sturgeons. Zoologischer Anzeiger 16:473-475.
DEAN, B. 1894. Recent experiments in sturgeon hatching on
the Delaware River. United States Fish Commission Bulletin 13:
335-339.
DETTLAFF, T. A., A. S. GINSBURG, AND O. I. SCHMALHAUSEN. 1993.
Sturgeon Fishes. Developmental Biology and Aquaculture.
Springer-Verlag, New York.
DOROSHOV, J. N., J. P. VAN EENENNAAM, F. A. CHAPMAN, AND S.
I. DOROSHOV. 1991. Histological study of the ovarian development in wild white sturgeon, Acipenser tmnsmontanus, p.
129-135. In P. Williot (ed.), Acipenser. Actes du Premier Colloque International sur l'Esturgeon. Centre National du
Machinisme Agricole du Genie Rural des eaux et des Forets,
France.
DOVEL, W. L. AND T. J. BERGGREN. 1983. Atlantic sturgeon of
the Hudson estuary, New York. New York Fish and GameJournal
30:140-172.
ENGLAND, B. G., G. D. NISWENDER, AND A. R. MIDGLEY, JR. 1974.
Radioimmunoassay of estradiol-1713 without chromatography.
Journal of Clinical Endocrinology and Metabolism 38:42-50.
FALEEVA, T. I. 1965. Analysis of atresia of the fish oocytes with
reference to the adaptive importance of this phenomenon.
Journal of Ichthyology 5:455-470.
GAY, V. L. AND J. T. 'KERLAN. 1978. Serum LH and FSH following
passive immunization against circulating testosterone in the
intact male rat and in orchidectomized rat bearing subcutaneous silastic implants of testosterone. Archives ofAndrology 1:
257-266.
GILBERT, C. R. 1989. Species profiles: Life histories and environmental requirements of coastal fishes and invertebrates
(Mid-Atlantic Bight). Atlantic and shortnose sturgeons. United States Fish and Wildlife Service Biological Report
82(11.122). United States Army Corps of Engineers TR
EL-82-4. Washington D.C.
HANSON, D. L. 1992. White Sturgeon Management Framework
Plan. Pacific States Marine Fisheries Commission. Portland,
Oregon.
HOFF, J. G. 1980. Review of the present status of the stocks of
the Atlantic sturgeon, Acipenser oX.Vl'hynchus (Mitchill). Southeastern Massachusetts University, National Marine Fishery
Service Report. North Dartmouth, Massachusetts.
HOLCIK, J., R. KiNZELBACK, L. I. SOKOLOV, AND V. P. VASIL'EV.
1989. Acipenser sturio Linnaeus, 1758, p. 367-394. In J. Holcik
(ed.), The Freshwater Fishes of Europe, Vol. I, Part II. General Introduction to Fishes Acipenseriformes. Verlag, Wiesbaden, Germany.
HUFF, J. A. 1975. Life history of Gulf of Mexico sturgeon, Acipenser oxyrhynchus desoti, in the Suwannee River, Florida. Florida Department of Nat).lral Resources, Marine Research Publication 16, St. Petersburg, Florida.
'KEENLYNE, K. D., E. M. GROSSMAN, AND L. G. JENKINS. 1992.
Fecundity of the pallid sturgeon. Tmnsactions of the American
Fisheries Society 121:139-140.
LINARES-CASENAVE, J., K. J. KROLL, J. P. VAN EENENNAAM, AND S.
I. DOROSHOV. 1994. Development and application of an enzyme-linked immunosorbent assay for the detection of plasma
vitellogenin in the white sturgeon broodstock, p. 165-169. In
Reproductive Conditions of Atlantic Sturgeon
D. D. Mackinlay (ed.), High Performance Fish. Proceedings
of an International Fish Physiology Symposium. University of
British Columbia in Vancouver. Fish Physiology Association,
Vancouver, British Columbia, Canada.
LUTES, P. B. 1985. Oocyte maturation in white sturgeon, Acipenser transmontanus; some mechanisms and applications, p.
87-92. In F. P. Binkowski and S. I. Doroshov (eds.), North
American Sturgeons: Biology and Aquaculture Potential. Dr.
W. Junk Publishers, Dordrecht, The Netherlands.
MAGNIN, E. 1964. Croissance en longeur de trois esturgeons
d'Amerique du Nord: Acipenser oxyrhynchus Mitchill, Acipenser
fulvescens Raffinesque, et Acipenser lYrevirostris LeSueur. Verhandlungen - Internationale Vereinigung fur Theoretische und Angewandte Limnologies 15:968-974.
McENROE, M. AND J. J. CECH, JR. 1985. Osmoregulation in juvenile and adult white sturgeon, p. 23-30. In F. P. Binkowski
and S. I. Doroshov (eds.), North American Sturgeons: Biology
and Aquaculture Potential. Dr. W. Junk Publishers, Dordrecht, The Netherlands.
MOBERG, G. P. AND S. I. DOROSHOV. 1992. Reproduction in cultured white sturgeon (Acipenser transmontanus). National Oceanic and Atmospheric Administration Technical Report, National Marine Fisheries Service 106:99-104.
MOBERG, G. P.,J. G. WATSON, H. PAPKOFF, KJ. KROLL, AND S. I.
DOROSHOV. 1991. Development of radioimmunoassays for
two sturgeon gonadotropins, p. 11-12. In A. P. Scott, J. P.
Sumpter, D. E. Kime, and M. S. Rolfe (eds.), Proceedings of
the Fourth International Symposium on the Reproductive
Physiology of Fish, Sheffield, England.
MORAN, M. A. AND K E. LIMBURG. 1985. The Hudson River
Ecosystem, p. 6-39. In K E. Limburg, M. A. Moran, and W.
H. McDowell (eds.), The Hudson River Ecosystem. SpringerVerlag, New York.
MURAWSKI, S. A. AND A. L. PACHECO. 1977. Biological and fisheries data on Atlantic sturgeon, Acipenser oxyrhynchus (Mitchill). Technical Series Report Number 10. Sandy Hook Laboratory, National Marine Fisheries Service, National Oceanic
and Atmospheric Administration, United States Department
of Commerce, Highlands, New Jersey.
PAVLICK, R. J. JR., J. G. WATSON, AND G. P. MOBERG. 1993. Influence of exogenous testosterone on the synthesis and secretion of two sturgeon gonadotropins in sexually undifferentiated Acipenser transmontanus, p. 18. In Abstract Bulletin of
the International Symposium on Sturgeons, September 6-11,
1993. Moscow, Russia.
PELISSERO, C. AND F. LE MENN. 1991. Evolution of sex steroid
levels in males and first time maturing females of siberian
sturgeon (Acipenser baeri) reared in a French fish farm, p. 8797. In P. Williot (ed.), Acipenser. Actes du Premier Colloque
777
International sur l'Esturgeon. Centre National du Machinisme Agricole du Genie Rural des eaux et des Forets, France.
PROBST, R. T. AND E. L. COOPER. 1954. Age, growth and production of the lake sturgeon (Acipenser fulvescens) in the lake
Winnebago region, Wisconsin. Transactions of the American
Fisheries Society 84:207-227.
RYDER, J. A. 1888. The sturgeon and sturgeon industries of the
eastern coast of the United States, with an account of experiments bearing upon sturgeon culture. United States Fish Commission Bulletin 20:231-328.
SCOTT, A. P., E. L. SHELDRICK, AND A. P. F. FLINT. 1982. Measurement of 17, 2013-Dihydroxy-4-pregnen-3-one in plasma of
trout (Salmo gairdneri Richardson): Seasonal changes and response to salmon pituitary extract. General and Comparative
Endocrinology 46:444-451.
SEMAKULA, S. N. AND P. A. LARKIN. 1968. Age, growth, food, and
yield of white sturgeon (Acipenser transmontanus) of the Fraser
River, British Columbia. Journal of the Fisheries Research Board of
Canada 25:2589-2602.
SMITH, T. I. J. 1985. The fishery, biology, and management of
Atlantic sturgeon, Acipenser oxyrhynchus, in North America. Environmental Biology ofFishes 14:61-72.
SMITH, T. I. J., D. E. MARCHETTE, AND G. F. ULRICH. 1984. The
Atlantic sturgeon fishery in South Carolina. North American
Journal ofFisheries Management 4:164-176.
SOKOLOV, L. I. AND N. V. AKIMOVA. 1976. Age determination of
the Lena River sturgeon, Acipenser baeri. Journal of Ichthyology
16:773-778.
VAN DEN AVll.E, M. J. 1984. Species profiles: Life histories and
environmental requirements of coastal fishes and invertebrates (South Atlantic)-Atlantic Sturgeon. United States Fish
and Wildlife Service, FWS/OBS-82/11.25. United States Army
Corps of Engineers, TR EL-82-4. Washington, D.C.
VLADYKOV, V. D. AND J. R. GREELEY. 1963. Order Acipenseridae.
Fishes of the Western North Atlantic. Sears Foundation of
Marine Research, Yale University, New Haven, Connecticut.
YOUNG,J. R., T. B. HOFF, W. P. DEY, ANDJ. G. HOFF. 1988. Management recommendations for a Hudson River Atlantic sturgeon fishery based on an age-structured population model,
p. 353-365. In C. L. Smith (ed.), Fisheries Research in the
Hudson River. Proceedings of a Conference Sponsored by the
Hudson River Environmental Society. State University of New
York Press, Albany, New York.
ZOTIN, A. I. 1953. Consumption of water by developing Acipenserid eggs from the environment. Doklady Akademii Nauk
89:377-380.
Received for consideration, May 5, 1994
Accepted for publication, November 28, 1994