Age and Growth of Klamath River Green Sturgeon (Acipenser medirostris)

Prepared by:

Rodney J. Nakamoto

U. S. Forest Service

Redwood Sciences Laboratory

1700 Bayview Drive

Arcata, California 95521

and

Tom T. Kisanuki

Greg H. Goldsmith

U. S. Fish and Wildlife Service

Coastal California Fish and Wildlife Office

1125 16th Street

Arcata, California 95521

Funded by:

U.S. Fish and Wildlife Service

Klamath River Fishery Resource Office

12 15 South Main Street, Suite 212

Yreka, California 96097

Project # 93-FP-13

January 31, 1995
Age and Growth of Klamath River

Green Sturgeon (Acipenser medirostris)

Rodney J. Nakamoto

U. S. Forest Service

Redwood Sciences Laboratory

1700 Bayview Drive

Arcata, California 95521

Tom T. Kisanuki

Greg H. Goldsmith

U. S. Fish and Wildlife Service

Coastal California Fish and Wildlife Office

1125 16th Street

Arcata, California 95521

Funded by:

U.S. Fish and Wildlife Service

Klamath River Fishery Resource Office

1215 South Main Street, Suite 212

Yreka, California 96097

Project # 93-FP-13

January 31, 1995
The mention of trade names of commercial products in this report does not

constitute endorsement by the U.S. Forest Service or the U.S. Fish and

Wildlife Service.
LIST OF TABLES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..*.................ii

LIST OF FIGURES . . . . . . . . . . . . . . . . . . . . . ..*.................................... iii

ABSTRACT .. . . . .. . . . . . . . . . . . . . . . . . .. . . . ..*......... iV

INTRODUCTION. . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . .1

STUDY AREA . . . . . . . . . . . . . ..*...........................*....................... 2

METHODS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..*........................2

Field Procedures . . . . . . . . . . . . . . . . . . . . . . . . . ..*...........................* 2

Beach Seining . . . . . . . . . . . . . . . . . . . . . . . . . .2

Net Harvest Monitoring . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..*...........4

Laboratory Procedures . . . . . . . . . . ...*..................................*.. 5

RESULTS . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . 5

DISCUSSION . . . . . . . . . . . . ... . . . . . . . . . . . . . . . . . . . 11

RECOMMENDATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ..*........*..........15

LITERATURE CITED . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 18
LIST OF TABLES

1. Regression equations developed for the relationship

between fork length (fl, cm) and total length

(tl, cm) of green sturgeon (Acipenser medirostris,

Ayers) measured from the Klamath River, California,

1990-1993 . . . . . . . . . . . . . . . . . . . . . . . . . . . ..*............................ 6
LIST OF FIGURES

Figure

1. Map of the Klamath River and Yurok Indian Reservation

depicting sample reacher . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3

2. Mean and range of length at age for sturgeon aged using

the Optical Pattern Resoulution System (OPRS) and microfiche reader. Estimates using the microfiche reader are

the average of two independent readingas . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8

3.

4.

5.

6.

7.

Length-frequency distribution (5 cm groupings) for male,

female, and unknown sex green sturgeon measured from the

Klamath River, California, 1990-993 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9

Length-age relationship for male, female, juvenile, and

unknown sex green sturgeon measured from the Klamath

River, California, 1990-1993 . . . . . . . . . . . . . . . . ..*................... 10

Length-frequency distributions of green sturgeon measured

as part of the beach seining and Native American gill net

harvest monitoring activities conducted by the U.S. Fish

and Wildlife Service, Arcata, California, in the Klamath

River for periods 1979-1982 and 1990-1993............................12

Mean, range, and sample size for total lengths of male

and female green sturgeon measured from the Klamath River,

California, 1980-1982 and 1990-1993 . . . . . . . ..*..................... 13

Mean length at age for green sturgeon measured from the

Klamath River, California, between 1980-1982 and 1990-1993........16

iii
During 1990 through 1993, green sturgeon (Acipenser medirostris) pectoral

fin rays and biological data were collected as part of the Native American

gill net harvest monitoring program and beach seining program conducted by the

U.S. Fish and Wildlife Service (USFWS), Coastal California Fish and Wildlife

Office (CCFWO), in the Klamath River, California. These data were utilized

jointly by the U.S. Forest Service,Redwood Sciences Laboratory (RSL) and

CCFWO to assess the age and growth of Klamath River green sturgeon. This

project was funded by the Klamath River Basin Fisheries Task Force, a program

funded through the USFWS' Klamath River Fisheries Resource Office, in Yreka,

California.

Pectoral fin rays from 154 green sturgeon were sectioned and aged by two

independent readers. Thirty-four percent of the age estimates differed by

lees than two years. Sixty-six percent differed by less than five years. The

irregular shape of the fin ray combined with close spacing and discontinuity

of the circuli and incorporation of secondary fin rays contributed

significantly to the variability in age estimates between readers. Upstream

migrant female green sturgeon were less numerous, older, and longer than male

sturgeon.

Green sturgeon harvest and life history data suggest that male sturgeon

become sexually mature sometime after reaching 120 centimeter (cm) total

length; while female sturgeon mature after attaining approximately 145 cm

total length. The results suggest that green sturgeon life history can be

divided into three general phases: 1) freshwater juveniles (~3 years old);

coastal migrants (3-13 years old for females and 3-9 years old for males; and

adults (213 years old for females and 2;9 years old for males).

i v
During 1992, the U.S. Fish and Wildlife Service, Coastal California Fish

and Wildlife Office (CCFWO), and the U.S. Forest Service, Redwood Science

Laboratory (RSL) were jointly funded through the Klamath River Basin Fisheries

Task Force to conduct an age and growth investigation on green sturgeon

(Acipenser medirostris) from the Klamath River. This Task Force wan created

under the provision of the passage of the 1986 Klamath River basin

Conservation Area Fishery Restoration Program (P.L. 99-552). This public law

was initiated to restore the anadromous fish stocks of the Klamath River

basin, and to offset the effects of dams, floods, timber harvest, mining, and

other detrimental impacts (Klamath River Basin Fisheries Task Force 1991).

Within California, green sturgeon have been reported in the Sacrmento,

Eel, Klamath and Trinity river systems. Presently, green sturgeon have

disappeared from the Eel River. Green sturgeon tend to spend much of their

life in the ocean (Chadwick 1959, Miller 1972), returning to freshwater

streams to spawn. Tagging information suggests that there is significant

interchange among green sturgeon populations along the Pacific Coast (Chadwick

1959). Klamath and Trinity river green sturgeon are unique in that they

represent the only California population which migrate significant distances

upstream (Fry 1973). Currently, information pertaining to green sturgeon

biology is scarce (Houston 1988). The USFWS has identified green sturgeon as

one of five stocks of special concern due to their depressed stock status

(USFWS 1988). Further, Moyle (1989) identified green sturgeon in California

as a species of uncertain status needing additional investigation.

Basic information pertaining to the ecology of any fishery population is

essential for effective management. The scarcity of information pertaining to

green sturgeon ecology is a significant barrier to developing an effective

management plan for this species. The objectives of this study were to:

1. Define the age composition of sturgeon harvested in the 1990-1993

Klamath River gill net fishery.

2. Define the age composition of green sturgeon captured incidentally

in CCFWO's 1989-1990 beach seining project in the Klamath River

estuary.

3. Provide descriptive growth data on Klamath River green sturgeon.

4. Determine the utility of pectoral fin ray sections in estimating

age of green sturgeon.

the
5. Examine the utility of using Optical Pattern Recognition System

(OPRS) for age and growth interpretation work of green sturgeon.

6. Expand the current biological database on green sturgeon.

The Klamath River originates in Oregon and flows in a southwesterly

direction into California. The Klamath River drains approximately 14,400

square kilometers (kd) and 26,000 km2 in Oregon and California, respectively.

Iron Gate Dam on the Klamath River at river kilometer (rkm) 306, and Lewiston

Dam on the Trinity River (rkm 179) represent the upper limits of anadromous

Salmonid migration in these basins.

The Klamath River has historically supported large runs of anadromous

fish such as chinook salmon (Oncorhvnchus tshawvtscha), steelhead trout (p.

mykiss), eulachon (Thaleichthys pacificus), Pacific lamprey (Entosphenus

tridentata), and smaller runs of coho salmon (O. kisutch) and green sturgeon

Acipenser medirostris). These fisheries have significantly contributed to

subsistence, sport, and commercial fisheries in California. Generations of

Native Americans have utilized fishing grounds in the Klamath River basin.

Salmon, steelhead, and sturgeon have historically provided the mainstay of the

Native American economy and culture in the area (Bearss, 1981).

Field Procedures

Sturgeon data and biological samples were collected from the mouth of the

Klamath River, upstream 70 rkm to the river's confluence with the Trinity

River, at Weitchpec, CA. The Klamath River flows through the Yurok Indian

Reservation throughout this distance (Figure 1). The data and samples were

collected in conjunction with the Native American gill net harvest monitoring

and beach seining activities conducted by the CCFWO, Arcata, California,

during the 1990-1993 seasons.

Beach Seininq. The beach seining program in the Klamath River estuary

was conducted to target the adult run of fall chinook salmon. This program

was terminated after the 1990 season. During the 1990 season the sampling

period extended from July 23 to October 2. Seining times for the 1990 season

varied daily to target the tidal period from before slack low tide to

immediately after the slack low tide. Seining schedules were conducted during

daylight hours. Sturgeon catch during the beach seining operation was

2
\Tenver Creek

Monitoring boundries

Yurok Indian Reservation boundary

Middle

Klamath

Area

... * ‘. ‘.

. -e- _I --.A‘. . .

%

-.

9 ‘.

. .

4 . . .

0; ‘. :

i __ Johnson 1

-.. -. ‘.

., Pecwan Creek : ‘.

\

-.

‘. . . .

Upper

Klamath

Area

Trinity River-\

Figure 1. Map of the Klamath River and Yurok Indian Reservation depicting

sampling reaches.

3
largely dependent on the physical characteristics of the seining site. Those

sites which were characterized as off-channel, slow-water habitats favored

sturgeon capture. A 150 meter (m) x 6 m beach seine net with a 5.4 cm bar

mesh bag section was deployed with a jet boat, and retrieved to shore using

gas-powered winches. Eight net sets were made each sampling day. Captured

sturgeon were identified to species, measured for fork and total length,

weighed, tagged with a Peterson disc tag, and a pectoral fin was excised prior

to release. Fins were stored in plastic bags and frozen prior to conducting

laboratory processing and analyses.

Net Harvest Moitoring. Coastal California Fish and Wildlife Office

staff monitored the spring and fall Native American gill net fishery which

target anadromous salmonids and sturgeon in the Klamath River. Detailed

descriptions of the monitoring methodology are available in USFWS (1992). The

spring monitoring period generally begins in early April, and concludes in

mid-July. The number of sturgeon captured was generally dependent on spring

flows. High spring flows hamper the operation of the Native American gill

nets resulting in lower harvest rates and therefore fewer sturgeon available

to measure. The fall fishery monitoring begins in mid-July, and usually ends

in latter September, although in some years, dependent upon fishing quotas,

has extended into October and November. Gill net harvest information was

collected by CCFWO crews from three contiguous areas (estuary, middle Klamath,

and upper Klamath) of the Klamath River on the Yurok Indian Reservation

(Figure 1). The estuary area was defined as the lower 6 rkm, from the mouth

to the U.S. Highway 101 bridge. The middle Klamath area is from the 101

bridge to Surpur Creek, a distance of 27 rkm. The upper Klamath area

constitutes the final 33 rkm, beginning at Surpur Creek and ending at the

confluence with the Trinity River, at Weitchpec, CA.

During periods of allowed fishing, CCFWO crews surveyed gill net

fishermen in the estuary at two hour intervals. Native American fishers were

interviewed during each time stratum to obtain information on the number of

each fish species caught, the type and number of nets fished, and the number

of hours fished. Those fishes made available by the fishers for examination

were identified to species, measured, weighed, examined for identification

characteristics (fin-clips, tags, etc), and sampled for scales (salmonids) or

pectoral fin rays (sturgeon). The fins were transported to the laboratory and

frozen until processing. Sex determinations were made based on examination of

gonads. In those cases when the gonads were not available for examination the

sex was listed as unknown.

The fishery was monitored four to five days per week in the middle and

upper Klamath areas during the allowed fishing period. CCFWO crews

interviewed Native American fishers for netting effort and biological

information, in the manner previous described.

4
Laboratory Procedures

Frozen pectoral fin rays were thawed in boiling water, and defleshed with

a stiff brush. The leading fin ray was isolated, and allowed to air dry. The

fin rays were mounted on plywood strips and thin-sectioned using a lapidary

saw (Raytec, Jem Saw Model 45), in accordance to methods described by Brennan

and Cailliet (1989). The fin ray sections were then adhered to a glass

microscope slide using clear nail polish.

The fin ray sections were examined with a microfiche reader equipped with

a 30x lens. Banding patterns on the fin ray sections were interpreted in

accordance to criteria outlined by Brennan and Cailliet (1989). It was

assumed that the combination of one translucent (formed during the summer) and

one opaque (formed during the winter) band represented a single years growth.

The authors examined the fin sections independently and assigned numerical

values to indicate the number of summer growth (annular) bands for each

individual fish.

A Optical Pattern Resolution System/t-m (OPRS, BioSonics 1985) was employed

to determine the feasibility and utility of this system in interpreting green

sturgeon fin ray sections. This system utilizes a Ikegami (model ICD-4422)

video camera linked to a Olympic BH2 microscope via a Olympic MTV-3 coupler.

The camera interfaces with Biosonics OPRS software based on a 386 microcomputer. Prepared fin ray sections were placed in the microscope and the

image was projected onto a video monitor. A reference line was drawn from the

center to the posterio-lateral margin of the fin ray section and the software

was allowed to select annular locations based on differential light

transmission between winter and summer growth bands. The locations of each of

the selected annuli were evaluated by the operator. All measurements for a

particular fin ray were stored as records in a computer file.

Between 1990 and 1993, 243 sturgeon were measured as part of the Native

American gill net harvest monitoring program and 30 sturgeon were measured as

part of the beach seining program on the Klamath River. Regression equations

were developed for the relationship between fork length and total length for

males, females, and males and females combined (Table 1). Examination of P

statistics and correlation coefficients for the equations suggested that the

combined male and female equation best explained this relationship.

The leading pectoral fin ray from 154 of the 243 sturgeon collected

between 1990 and 1993 was prepared for age and growth assessment. Ages were

assigned to 148 sturgeon by two independent readers. Thirty-four percent of

the two age estimates differed by less than two years. Sixty-six percent of

S
Table 1. Regression equations developed for the relationship between fork length (fl

and total length (tl, cm) of green sturgeon (Acipenser medirostris, Ayers) measured 

the Klamath River, 1990-193.

Sex n Model r2 p

Male 58 tl = -2.0878 + 1.1202(fl) 0.99 0.0001

Female 33 tl = -8.3060 + 1.1597(fl) 0.95 0.0001

Combined/1 91 tl = -4.6131 + 1.1374(fl) 0.98 0.0001

6
the ago estimates differed by less than 5 years. The average difference

between ago assignments war 4 year8 (range O-19 years). The mean of readings

assigned by reader 1 (21 years, range 1-45 years) was 1 year greater than the

mean of readings assigned by reader 2 (22 years, range 2-54 years).

Age assignments for 115 of the 148 sturgeon were also made using the OPRS

system. The average age assigned by the OPRS system was 29 years (range 1-72

years). Age assignments by the OPRS

age assignments using the microfiche

system were consistently older than the

reader. OPRS age assignments averaged 8

years greater than the average age assignment using the microfiche reader.

Total length variation within a given age war greater for those sturgeon aged

using the OPRS system compared to those aged using the microfiche (Figure 2).

In addition, the OPRS results suggested that between ages 1-9 total length

(tl) remains nearly static. Greater magnification, image clarity, and the

computer enhanced ability of the OPRS system to differentiate between light

and dark banding patterns may have resulted in the counting of false or

incomplete annuli which resulted in the greater variability in the length-age

relationship. Due to the greater variability in the data noted for the OPRS

readings and the poor relationship at young ages, the average of the two

microfiche readings will be used for further discussions of age.

Weight information was collected in conjunction with fork length (fl)

data for 56 males, 31 females and 23 individuals of undetermined sex. Male

sturgeon averaged 58 kilogram8 (kg) (range 20-112 kg) while female sturgeon

averaged 94 kg (range 29-148 kg). The relationship between fork length and

weight, and total length and weight were described by:

weight = -27.9903 + 0.0039(fork length')

n = 90

r& .85

p < 0.0001

weight = -20.0434 + 0.0027(total length

n = 110

r& .58

p < 0.0001

Sex was determined for 165 individuals between 1990-1993. Female

sturgeon were less abundant, older, and significantly longer than male

sturgeon (Figures 3, 4). Female sturgeon averaged 32 years old (range 22-46

years) while males averaged 23 years old (range 9-45 years).

Sturgeon <60 mm tl were collected primarily during the beach seining

operations within the Klamath River estuary. The beach seining operation was

discontinued after the 1990 season. During 1990, 27 small green sturgeon were

captured. These fish averaged 52 mm tl (range 32-66 mm tl). Age estimates

for these individuals indicated that these individuals averaged 3 years old

(range l-4 years old). Previous years' data indicate that within the

7
Age (years)

Figure 2. Mean and range of length at age for sturgeon aged using the Optical

Pattern Resolution System (OPRS) and microfiche reader. Estimates using the

microfiche reader are the average of two independent readings.
“a3,

171-17s swq I

176-180 *‘”

181-165 *w; l

186-190 3196-20020102t%206-2102ll-21s

216220

221-225226-230231-235

236240241-245246-250

251-255

-260!
300-I

275-.

250-. 0

225-. 0

z 200- .

s 175, 5 .

g) 150- a

o, 8

5 125- .

g loo-.

75'.

50-A A ' riA

25-. 0 I - I - " ' I - n - a - n - ' 1

0 5 10 15 20 25 30 35 40 45 50

Age (years)

Figure 4. Length-age relationship for male, female, juvenile, and unknown sex green

sturgeon measured from the Klamath River, California, 1990 - 1993.

10
Klamath River estuary the abundance of these small sturgeon peaks between July

and September. Juveniles generally spend up to 3 years in freshwater prior to

migrating to sea, primarily during the summer-fall period (Em m ett et al. 1991,

USFWS).

A conspicuous lack of individuals measuring between 71-115 mm was

observed in the length-frequency distribution for sturgeon collected between

1990 and 1993 (Figure 5). Similar length-frequency distributions were

obtained by the USFWS (1982, Figure 5). Previously published information

suggests that individuals within this size range are migratory marine

residents and seldom venture into freshwater.

We further examined data collected on 610 green sturgeon measured in the

Klam ath River between 1980 and 1993. Previously published information

indicates that green sturgeon can reach 230 cm fl (256 cm tl) and 159 kg

(Hoyle 1976). However, they seldom exceed 130 cm fl (144 cm tl) and 45 kg

(Skinner 1962). Within this study, 431 of the 610 individuals exceeded 130 cm

fl (mean 160 cm , range 132 -233 cm).

We compared the lengths of male and female sturgeon measured between

1980-1982 to those measured between 1990-1993 (Figure 6). The results

demonstrate that the patterns noted between 1990-1993 were l similar to those

noted between 1980-1982. Female sturgeon were generally larger and less

numerous than male sturgeon.

DISCUSSION

Significant difficulties were encountered in aging the pectoral fin ray

sections. The annular patterns consisted of alternating dark and translucent

bands. The wide dark bands result from the abundant formation of connective

tissue during the summer, converted later to bone tissue; the narrow

translucent bands correspond to the period of metabolic inactivity during the

winter (Brennan and Cailliet 1991). Examination of the prepared fin ray

sections using a microfiche reader revealed that annular patterns within the

sections were extremely difficult to differentiate. The irregular shape of

the fin ray combined with close spacing and discontinuity of the circuli and

incorporation of secondary fin rays made confident age assessment difficult.

These difficulties have been encountered by other researchers (Roussow 1957,

USFWS 1983, Brennan and Cailliet 1989). The observed variability in sturgeon

size at each age appears to be characteristic of sturgeon studies (Semakula

and Larkin 1968, Kolhorst et al. 1980, USFWS 1983). Kolhorst et al. (1980)

suggested that size variation at each age may be real. The reduced growth

rates of older fish and prespawning age fish, formation of spawning checks,

long migrations or adverse environmental conditions may contribute to

decreased ability to accurately assess age from pectoral fin ray sections

11
10

9

8

7

6

5

4

3

2

1

0

-

-

-

I

-

I

-

I

-

-

-

-

-

-

-

I

-

m

-

10

9

8

7

6

5

4

1979-1982

n=187

19904993

n=154

Figure 5. Length-frequency distributions of green sturgeon measured as part of

the beach seining and Native American net harvest monitoring monitoring activities

conducted by the U.S. Fish and Wildlife Service, Arcata, California, in the Klamath

River for periods 1979-l982 and 1990-l993.

12
29

47

fj

30

I

“‘]]

34 24

1

23

I

36

I,

0

L

11

100 ' 1980 1981 1982 1990 1991 1992 1993

Year

Figure 6. Mean, range, and sample size for total lengths of male and female

green sturgeon measured in the Klamath River, California, 1980-l982 and

1990-1993.

13
(Roussow 1957, Sokolov and Malyutin 1978, Kolhorst et al. 1980, Keenlyne and

Jenkins 1993, Rein and Beamesderfer 1994).

The relative rarity of males between ages 3-9 years and females between

the ages of 3-13 years suggests that these individuals spend relatively little

time in freshwater. Within the Klamath River these individuals are usually

observed between July and October (USFWS 1982, 1983, 1992). Previous reports

have documented the marine migratory behavior of subadult and adult green

sturgeon. Green sturgeon tagged in San Pablo Bay were recovered as far north

as Gray’s Harbor and as far south as Santa Cruz (Chadwick 1959; Miller 1972).

Roedel (1941) reported the capture of a green sturgeon weighing 3.3 kg

offshore between the towns of Huntington Beach and Newport, CA. Chadwick

(1959) concluded that there is considerable interchange between green sturgeon

populations along the Pacific Coast.

Females under 145 cm tl did not appear in the record. The smallest

female sturgeon sampled between 1990 and 1993 was 148 cm tl. Size selectivity

of the gill net would not preclude capture of females smaller than 145 cm tl

as individuals under this size are commonly caught. The absence of small

females in the harvest suggests that either prior to reaching 145 cm tl

gonadal development was insufficient to determine sex or that females return

to freshwater sometime after reaching 145 cm tl. This length would correspond

to an age of about 13 years old. Males generally appeared in the harvest

record after reaching 120 cm tl (8 years old). The size at which males mature

is questionable as the gill net sampling efficiency is biased toward

individuals greater than 120 cm tl. In addition, sex determination was based

on gonadal observations. In many cases individual sturgeon less than 120 cm

tl may have been caught but due to their small size they were released. In

these cases, the observers would not have been able to determine sex.

Although the length frequency distribution suggests that male sturgeon may

begin spawning sometime after reaching 120 cm tl, this conclusion is

tentative; male sturgeon may become reproductively active prior to reaching

120 cm tl.

The data suggests that male green sturgeon may become reproductively

mature at a younger age than female green sturgeon. Differences in age at

first spawning between sexes have been noted for other sturgeon species.

Semakula and Larkin (1968) noted that the age at first spawning for white

sturgeon (Acioenser transmontanus) from the Frasier River is 11-22 years

(81-137 cm tl) for males and 11-34 years (81-231 cm tl) for females. Roussow

(1957) reported age at first spawning for lake sturgeon (Acioenser fulvescens)

in Canada varied between 12-19 years and 14-23 years for males and females,

respectively. Keenlyn and Jenkins (1993) reported that male pallid sturgeon

mature at ages 5-7 years while females may begin spawning sometime after 17

years old.

14
The use of pectoral fin rays for estimating the age of sturgeon was not a

precise method. However, these results do not totally discount the utility of

this method. Comparison of the length-age relationship reported by the USFWS

(1983) to the relationship obtained in the herein reveals that the

relationehips are very similar (Figure 7). The similarity in the

relationships adds more strength to the utility of pectoral fin ray analysis.

The pectoral fin ray analysis offers a simple and practical tool for fisheries

managers. The pectoral fin rays can be obtained without sacrificing the

sturgeon. Green sturgeon are a long-lived species, with a life span of

several decades. Age estimates for nearly 70% of the individuals differed by

less than 5 years. The results of this study and previously published

information suggest that green sturgeon life history can be divided into three

general phases: 1) freshwater juveniles years old), 2) coastal marine

migrants (3-9 years for males, 3-13 years for females) and 3) adults. Further

research aimed at investigating spawning periodicity, fecundity, survival, and

the degree to which adults may use rivers other than their natal rivers for

reproduction is needed in order to effectively manage this long-lived species.

The OPRS system may be a valuable tool for green sturgeon age assessment.

The computer assisted technology offers a fast and precise means of fin ray

interpretations. In contrast to the microfiche, the OPRS may over-estimate

the age of sturgeon. This was attributed to the acute discriminatory

abilities of the OPRS system. Additional experimentation and calibration may

be necessary to fully utilize this technology for age analyses of sturgeon fin

rays. The utility of this system should be further explored.

The use of pectoral fin rays in this study for estimating the age of

sturgeon was not a precise method. However, the observed variability

between age estimates does not totally discount the utility of this method.

The use of fin rays offers a simple and practical tool for fishery managers.

The fin rays can be obtained without sacrificing the sturgeon. The fin rays

are readily sectioned, and most managers possess the skills necessary to

perform the age interpretation work. Green sturgeon are long-lived, with a

life span of several decades. Age determination increased in difficulty with

increased age of the sturgeon. At present, fin ray analysis is the most

readily available method of estimating sturgeon age. This method in

conjunction with biological data is extremely useful for estimating the age at

which these fish become reproductively mature.

The use of a high quality lapidary saw with

is imperative for producing precise, thin cross

this study was marginal, and had to be modified

15

a micro-adjustable feed ramp

sections. The saw utilized in

with a " home-made" feed
250

200

- 1980-1982

-+- 1990-1993

l

1 0 2 0 3 0

Age (years)

Figure 7. Mean length at age for green sturgeon sampled from the Klamath

River, California, between 1980-l982 and 1990-1993.

16
mechanism. We found it difficult to produce consistant cross sections, thus

necessitating repeated l efforts. The inability of the operator to smoothly

feed the fin rays stemmed from the inferior mechanism.

Initiation of sturgeon tagging programs in order to provide validation

for aging techniques, and information pertaining to the recurrence of l spawning

and dispersion along the Pacific coast would be helpful. Application of

external tags in conjunction with biological markers (much as tetracycline)

would allow age validation, and provide empirical information on growth rates,

and migration characteristics. The external tags would help identify whether

Answers to these questions would have profound implications for the future of

would prevent work duplication and promote comparable data.

Are there distinct populations of green sturgeon, or o

gill net fishery i

defining potentially distinct Pacific coast populations. Green sturgeon are

yet most 

ensure that annular formation was complete.

Rein and Beameederfer (1994) noted that within the Columbi

of 

rays 

assumed to be highly migratory

rivers

sturgeon age and siz

sturgeon management.

length-weight data

limitations.

stock identification work on green sturgeon would be very helpful towards the

integrated approach to share research needs and costs. This coordination

long-term information is necessary to monitor any potential changes in the

collection of fin ra

Continuation of data collection in conjunction with the Native American

There is considerable need to understand the biolog

In conjunction with age and growt

should be collected either before May or after July in order to better

 and bays

government agencies are constrained by budgetary and personnel

We 

,

recommend

and whether green sturgeon utilize multiple nata

,

s 

e 

s

recommended

e

composition,

x 

y 

r

 that fishery managers coordinate, and utilize an

samples 

atios

,

.

,

are 

and 

 and sex ratio.

may 

On-going data needs include collectio

they utilizing multiple natal streams?

h 

increase the 

gonadal

17

assessment work, conducting genetic

 development and fecundity.

accuracy 

Consideration 

ne common gene pool?

y of 

a 

of 

green sturgeon,

River 

age estimation.

l 

of 

system,

waters.

the timing

n 

 fin

This

of
Bearss, B.C. 1981. Historical resourcs study - Hoopa-Yurok fisheries suit,

Hoopa Valley Indian Reservation - Del Norte and Humboldt Counties,

California. Denver Service Center. Denver, Colorado. 443 pp.

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Brennan,

program manual. Vestion 1.10. 3670 Stone Way North, Seattle,

Washington 98103.

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techniques for white sturgeon in California. Transactions of the

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and Game 45:297-301.

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.

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estuaries Volume II: Species life history summaries. ELMR

8. NOAA/NOS Strategic Environmental Assessments Division,

XD, 329 p.

west coast

Rep. No.

Rockville,

Houston, J. J. 1988. Status of the green sturgeon, Acipenser medirostris, in

Canada. Canadian Field Naturalist 102:286-290.

Keenlyn, K. D. and L. G. Jenkins. 1993. Age at sexual maturity of the pallid

sturgeon. Transactions of the American Fisheries Society 122:393-

396.

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Klamath River basin conservation area fishery restoration program.

USFWS. Yreka, CA.

Kohlhorst, D. W., L. W. Miller, and J. J. Orsi. 1980. Age and growth of

white sturgeon collected in the Sacramento-San Joaquin Estuary,

California: 1965-1970 and 1973-1976. California Fish and Game

66:83-95.

18
Miller, L. W. 1972. Migrations of sturgeon tagged in the Sacramento-San

Joaquin Estuary. California Fish and Game 58:102-106.

Hoyle, P.B. 1976. Inland fishes of California. University of California

Press,; Berkeley, Los Angeles, London. 405 pp.

Moyle, P.B., J.E. Williams, and B.S. Wikramanayake. 1989. Fish species of

special concern in California. California Department of Fish and

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7337. 222 pp.

Rein, T. A. and R. C. Beamesderfer. 1994. Accuracy and precision of white

sturgeon age estimates from Pectoral fin rays. Transactions of the

American Fisheries Society 123~255-265.

Roedel, P. M. 1941. A sturgeon in southern California waters. California

Fish and Game 27:191-197.

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periodicity. Journal Fisheries Research Board Canada 14:553-572.

Semakula, S. N. and P. A. Larkin. 1968. Age, growth, food, and yield of the

white sturgeon (Acipenser transmontanus) of the Fraser River,

British Columbia. Journal Fisheries Research Board Canada

25:2589-2602.

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structure and characteristics of

Acipenser baeri, in the spawning

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Features of the population

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grounds of the Lena River. Journal

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1982. Fisheries Assistance Office, Arcata,

1983. Fisheries Assistance Office, Arcata, California. 133

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report

Arcata, California. 73 pp.

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1990 & 1991. Coastall California Fishery Resource Office,

20