1. 2 A Case History of Fishing Regulations in Great Smoky Mountains National Park: 1934 - 2004 Matt...
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![Page 1: 1. 2 A Case History of Fishing Regulations in Great Smoky Mountains National Park: 1934 - 2004 Matt A. Kulp and Steve E. Moore Great Smoky Mountains National.](https://reader034.fdocuments.in/reader034/viewer/2022042821/56649da85503460f94a94cff/html5/thumbnails/1.jpg)
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A Case History of Fishing Regulations in
Great Smoky Mountains National Park: 1934 - 2004Matt A. Kulp and Steve E. Moore
Great Smoky Mountains National Park
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Background
• Study began as case history and summary of GRSM fishing regulations
• Original three objectives:
1) What is the fishing regulation history of GRSM?
2) Did regulations meet management goals for each time period?
3) Were various regulations effective in enhancing or influencing salmonid age structure, size structure, growth, and population dynamics over 70 years (1934-2004)?
• Rainbow trout (non-native) used in all analysis
• >1.4 million rainbow trout stocked in GRSM from 1934-1975• Mostly fingerlings up to 1945; then switched to catchables
• Part of broader study: Kulp, M.A. and S.E. Moore. 2004. A Case History in Fishing Regulations in
Great Smoky Mountains National Park: 1934-2004. North American Journal of Fisheries Management. In press.
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Methods
• Analyzed similar types of data from different regulatory periods
• Population abundance variety of time series analysis used to evaluate time trend
pre- and post-1960 groups compared with ANOVA
• Length frequency data analyzed using customized RSD’s rainbow >150mm used as “stock size”; RSD’s calculated for subsequent 25mm size groups (i.e. RSD178, RSD 203, RSD229…RSD305, etc.)
years or periods compared using Chi2 analysis
• Age structure – delineated using scales collected Parkwide
years compared using Chi2 analysis
• Annual Mortality – Catch Curves
• Annual Growth – Visual Implant tags
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General Regulations
Period Season Legal Lures Size Limit Creel Limit Notes
1934-1935 Apr-Aug Single Hook
Artificial >254mm 10 fish/day
Could keep injured
1936-1939 May-Aug Single Hook
Artificial >203mm RBT >152mm BKT
10 fish/day Could keep
injured
1940-1942 Apr-Aug Single Hook Artificial/Bait
>178mm trout
10 trout/day
Could keep injured
1943-1947 May-Aug Single Hook
Artificial >178mm All
Species 10
trout/day Could keep
injured
1948-1950 May-Aug Single Hook Artificial/Bait
>178mm trout
10 trout/day
Could keep injured
1951-1953 May-Aug Single Hook Artificial/Bait
>178mm All species
7 trout/day Could keep
injured
1954-1975 May-Aug Single Hook
Artificial >178mm All
species 5 trout/day
CANNOT keep injured
1976-1982 Apr-Oct Single Hook
Artificial >178mm 5 fish/day
1983-Today Year Round Single Hook
Artificial >178mm 5 trout/day
Eliminate Special Reg
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Population Dynamics – East Prong Little River
0
100
200
300
400
500
600
700
800
900
1,000
1930 1940 1950 1960 1970 1980 1990 2000 2010
Years
Leg
al T
rout
/ km
.
No Significant Trend Detected
Time Series Linear Regression, Exponential Smoothing, ARIMA (x,y)
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0
100
200
300
400
500
600
700
800
900
1,000
1930 1940 1950 1960 1970 1980 1990 2000 2010
Years
Leg
al T
rout
/ k
m
Population Dynamics – East Prong Little River
No Significant Difference
p = 0.73, df = 15
Pre-1960 Post-1960
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12
0
10
20
30
40
50
60
70
RSD203 RSD254 RSD305 RSD356
RSD
1930's
1940's
1950's
1980's
1990's
Size Structure (RSD’s) – East Prong Little River
Only 1940’s Significantly Greater Than 1990’s
df=3, F=11.92
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Size Structure (RSD’s) – Abrams Creek
1999 Significantly Greater Than 1985
df=5, F=20.87
0
10
20
30
40
50
60
70
80
90
100
RSD178 RSD203 RSD229 RSD254 RSD279 RSD305 RSD330
RSD
Abrams Creek 1985
Abrams Creek 1999
205mm Creel Limit
178mm Creel Limit
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Age Structure – Parkwide
NO Significant Difference
df=3, F=4.04
0
10
20
30
40
50
60
70
80
Age-1 Age-2 Age-3 Age-4
Per
cent
of
Pop
ulat
ion
(%)
.
Holloway 1945 N=928
Kulp 1993 N=107
* Injured fish
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Length at Capture – East Prong Little River
0
50
100
150
200
250
300
350
400
Age-0 Age-1 Age-2 Age-3 Age-4
Tot
al L
engt
h (m
m) .
King 1942
Holloway 1945
Kulp 1995
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Annual Mortality – Abrams Creek
Abrams Creek 1957y = -0.8545x + 5.5381
A = 58%
Abrams Creek 1994y = -0.8865x + 5.1051
A = 59%
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
5.0
Age-2 Age-3 Age-4
log e
(N
umbe
r of
Fis
h) .
• Regulations similar among two periods regulations very liberal up to 1954
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Little River 1996y = -0.8226x + 4.8373
A = 56%
Sams Creek 1998y = -1.6479x + 6.1254
A = 80%
Fish Camp 1945y = -1.1612x + 5.2555
A = 69%
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
Age-1 Age-2 Age-3
loge
(Num
ber o
f Fis
h)
Annual Mortality – Parkwide
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Limiting Factors – Food Limitation
-20
-10
0
10
20
30
40
< 177mm 178-203mm 204-229mm > 230mmMea
n W
eigh
t C
hang
e (g
)
October-April
May-September
1-Year
* Visual Implant (VI) tag data from Little River (May 1991 to Sept. 1996) N=64
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Limiting Factors – Annual Net Production
Historical Stream Salmonid Literature Review
Annual Net Production
Productivity
Range (g/m2)
Study Area
Specific Conduct. (MS/cm)
Species
Net Production
(g/m2)Authors
Low
(Infertile) < 6.0
GA
QUE
GRSM
MN/WI
N/A
10-11
10
N/A
BKT
BKT
BKT/RBT
BKT/RBT
0.31-0.72
1.5-6.6
0.45-0.62
1.3-5.8
Michaels 1974
O’Connor & Power 1976
Ensign et al. 1990
Waters et al. 1990
Medium 6.0-25.0
PA
ID
WI
MN
27
N/A
273
620
BKT
RBT/STL
BKTBNT
6.4
11.8-12.5
8.2-25.810.4-19.5
Cooper & Scherer 1967
Goodnight & Bjornn 1971
Hunt 1974
Newman and Waters 1989
High
(Fertile)
> 25.0 NZ
PA
N/A
374
BNT
BKT
54.7
33.1
Allen 1951
Cooper & Scherer 1967
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Angler Attitudes – Changes on the Horizon . . .
• Long-term involvement with sampling provided an understanding of natural variation (>12-40 people per year)
• Angler involvement in annual monitoring opened their eyes to actual size structures and densities (1 or 2 people)
• Angler understanding of regulations dispelled myths
• Once educated about regulation realities:
1. anglers policed their own ranks concerning regulation criticism
2. focused energies on more productive projects
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• Unable to detect any significant changes due to regulations during any period
Droughts and floods account for major changes
Heavy stocking may explain short-term differences observed in East Prong Little River
Results mirror those of populations outside GRSM
Summary
• Stocking of fingerling/catchable trout temporarily augmented wild population
61-90% caught in first three months
• Acid deposition impacts not apparent in low elevation streams (<875m) in this study
• Current GRSM fishing regulations more closely tied to social beliefs rather than biological data
• Food limitations and subsequent lack of productivity main limiting factor in all GRSM populations
• Angler understanding allowed to focus energies on productive partnership efforts
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Questions . . . ?
Moral of the regulation story in GRSM. . .
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