persistence of forage fish ‘hot spots’ and its association with foraging steller sea lions in...
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Persistence of forage fish ‘hot spots’ Persistence of forage fish ‘hot spots’ and its association with foraging and its association with foraging
Steller sea lions in southeast AlaskaSteller sea lions in southeast Alaska
Scott M. GendeScott M. Gende
National Park Service, Glacier Bay Field Station, 3100 National Park Service, Glacier Bay Field Station, 3100 National Park, Juneau, Alaska, USA; National Park, Juneau, Alaska, USA;
[email protected][email protected]
Michael F. SiglerMichael F. Sigler
National Marine Fisheries Service, Alaska Fisheries National Marine Fisheries Service, Alaska Fisheries Science Center, Auke Bay Laboratory, Juneau, Alaska, Science Center, Auke Bay Laboratory, Juneau, Alaska,
1. Identify aggregations of pelagic fish prey in space and time.
2.Examine whether these prey ‘hot spots’ persist within and across seasons.
3.Examine which characteristics of prey aggregations are associated with predator aggregations.
4.Model foraging effort (efficiency) as it varies with these characteristics.
Objectives:Objectives:
Upper Lynn canal, Upper Lynn canal, southeast Alaskasoutheast Alaska
~40 linear km~40 linear km
Methods:Methods:
1. Hydroacoustic surveys for 1. Hydroacoustic surveys for pelagic prey conducted June 2001-pelagic prey conducted June 2001-May 2004May 2004
2. Periodic midwater trawls to 2. Periodic midwater trawls to sample prey energy and confirm sample prey energy and confirm echo soundecho sound3. Concurrent observations of top 3. Concurrent observations of top predators including Steller sea lions predators including Steller sea lions and humpback whalesand humpback whales
4. Transformed data from 4. Transformed data from estimates of biomass to energy estimates of biomass to energy densities integrated across the densities integrated across the water columnwater column5. Blocked data into tenths of a 5. Blocked data into tenths of a latitudinal minute such that each latitudinal minute such that each ‘block’ constituted approximately ‘block’ constituted approximately 1.83 km)1.83 km)
Methods:Methods:
1. Hydroacoustic surveys for 1. Hydroacoustic surveys for pelagic prey conducted June 2001-pelagic prey conducted June 2001-May 2004May 2004
2. Periodic midwater trawls to 2. Periodic midwater trawls to sample prey energy and confirm sample prey energy and confirm echo soundecho sound3. Concurrent observations of top 3. Concurrent observations of top predators including Steller sea lions predators including Steller sea lions and humpback whalesand humpback whales
4. Transformed data from 4. Transformed data from estimates of biomass to energy estimates of biomass to energy densities integrated across the densities integrated across the water columnwater column5. Blocked data into tenths of a 5. Blocked data into tenths of a latitudinal minute such that each latitudinal minute such that each ‘block’ constituted approximately ‘block’ constituted approximately 1.83 km)1.83 km)
Methods:Methods:
1. Hydroacoustic surveys for 1. Hydroacoustic surveys for pelagic prey conducted June 2001-pelagic prey conducted June 2001-May 2004May 2004
2. Periodic midwater trawls to 2. Periodic midwater trawls to sample prey energy and confirm sample prey energy and confirm echo soundecho sound3. Concurrent observations of top 3. Concurrent observations of top predators including Steller sea lions predators including Steller sea lions and humpback whalesand humpback whales
4. Transformed data from 4. Transformed data from estimates of biomass to energy estimates of biomass to energy densities integrated across the densities integrated across the water columnwater column5. Blocked data into tenths of a 5. Blocked data into tenths of a latitudinal minute such that each latitudinal minute such that each ‘block’ constituted approximately ‘block’ constituted approximately 1.83 km)1.83 km)
Methods:Methods:
1. Hydroacoustic surveys for 1. Hydroacoustic surveys for pelagic prey conducted June 2001-pelagic prey conducted June 2001-May 2004May 2004
2. Periodic midwater trawls to 2. Periodic midwater trawls to sample prey energy and confirm sample prey energy and confirm echo soundecho sound3. Concurrent observations of top 3. Concurrent observations of top predators including Steller sea lions predators including Steller sea lions and humpback whalesand humpback whales
4.4. Blocked data into tenths of a Blocked data into tenths of a latitudinal minute such that each latitudinal minute such that each ‘block’ constituted approximately ‘block’ constituted approximately 1.83 km1.83 km5. Transformed data from 5. Transformed data from estimates of biomass to energy estimates of biomass to energy densities integrated across the densities integrated across the water columnwater column
Methods:Methods:
1. Hydroacoustic surveys for 1. Hydroacoustic surveys for pelagic prey conducted June 2001-pelagic prey conducted June 2001-May 2004May 2004
2. Periodic midwater trawls to 2. Periodic midwater trawls to sample prey energy and confirm sample prey energy and confirm echo soundecho sound3. Concurrent observations of top 3. Concurrent observations of top predators including Steller sea lions predators including Steller sea lions and humpback whalesand humpback whales
5. Transformed data from 5. Transformed data from estimates of biomass to energy estimates of biomass to energy densities integrated across the densities integrated across the water columnwater column
kJ x 10kJ x 1066/km/km22
4. Blocked data into tenths of a 4. Blocked data into tenths of a latitudinal minute such that each latitudinal minute such that each ‘block’ constituted approximately ‘block’ constituted approximately 1.83 km)1.83 km)
Results:Results:
Strong seasonal variation in prey energy Strong seasonal variation in prey energy density; consistent across three yearsdensity; consistent across three years
0
5,000
10,000
15,000
20,000
25,000
30,000
JUN
AUGO
CTDEC
FEBAPR
JUN
AUGO
CTDEC
FEBAPR
JUN
AUGO
CTDEC
FEBAPR
Avera
ge e
nerg
y d
en
sit
y in
stu
dy
are
a
(Million
s k
J/km
2)
2001 2004
0
5,000
10,000
15,000
20,000
25,000
30,000
JUN
AUGO
CTDEC
FEBAPR
JUN
AUGO
CTDEC
FEBAPR
JUN
AUGO
CTDEC
FEBAPR
Cold winter months (Nov-Feb) are Cold winter months (Nov-Feb) are hothot
Avera
ge e
nerg
y d
en
sit
y in
stu
dy
are
a
(Million
s k
J/km
2)
2001 2004
SeasonSeasonal haul-al haul-outout
> 20000
10000-20000
5000-10000
1000-5000
1-1000
Prey energy density and SSL locations: Prey energy density and SSL locations: Nov 03Nov 03
>70%>70%
50-70%50-70%
30-50%30-50%10-30%10-30%
<<10%10%
Prey energyPrey energy % of SSL% of SSL
SeasonSeasonal haul-al haul-outout
> 20000
10000-20000
5000-10000
1000-5000
1-1000
Prey energy density and SSL locations: Prey energy density and SSL locations: Dec 03Dec 03
>70%>70%
50-70%50-70%
30-50%30-50%10-30%10-30%
<<10%10%
Prey energyPrey energy % of SSL% of SSL
SeasonSeasonal haul-al haul-outout
> 20000
10000-20000
5000-10000
1000-5000
1-1000
Prey energy density and SSL locations: Prey energy density and SSL locations: Jan 04Jan 04
>70%>70%
50-70%50-70%
30-50%30-50%10-30%10-30%
<<10%10%
Prey energyPrey energy % of SSL% of SSL
SeasonSeasonal haul-al haul-outout
> 20000
10000-20000
5000-10000
1000-5000
1-1000
Prey energy density and SSL locations: Prey energy density and SSL locations: Feb 04Feb 04
>70%>70%
50-70%50-70%
30-50%30-50%10-30%10-30%
<<10%10%
Prey energyPrey energy % of SSL% of SSL
SeasonSeasonal haul-al haul-outout
> 20000
10000-20000
5000-10000
1000-5000
1-1000
Prey energy density and SSL locations: Prey energy density and SSL locations: Mar 04Mar 04
>70%>70%
50-70%50-70%
30-50%30-50%10-30%10-30%
<<10%10%
Prey energyPrey energy % of SSL% of SSL
SeasonSeasonal haul-al haul-outout
> 20000
10000-20000
5000-10000
1000-5000
1-1000
Prey energy density and SSL locations: Prey energy density and SSL locations: Apr 04Apr 04
>70%>70%
50-70%50-70%
30-50%30-50%10-30%10-30%
<<10%10%
Prey energyPrey energy % of SSL% of SSL
SeasonSeasonal haul-al haul-outout
> 20000
10000-20000
5000-10000
1000-5000
1-1000
Prey energy density and SSL locations: Prey energy density and SSL locations: May 04May 04
>70%>70%
50-70%50-70%
30-50%30-50%10-30%10-30%
<<10%10%
Prey energyPrey energy % of SSL% of SSL
SeasonSeasonal haul-al haul-outout
Proportion of surveys where above Proportion of surveys where above average prey densities were located: average prey densities were located:
winter months (Nov-Feb)winter months (Nov-Feb)
>70%
60-70% 50-60%
SeasonSeasonal haul-al haul-outout
>70%
60-70% 50-60% 20-30%
Proportion of surveys where above average Proportion of surveys where above average prey densities were located: prey densities were located: non-winter non-winter
months (Mar-Oct)months (Mar-Oct)
SeasonSeasonal haul-al haul-outout
Prey persistence relative to locations of Prey persistence relative to locations of foraging sea lions: foraging sea lions: winterwinter
>70%
60-70% 50-60%
Prey persistence
>40% 30-40% 20-30%
Foraging SSL
0%
10%
20%
30%
40%
50%
0% 10% 20% 30% 40% 50% 60% 70%
Persistence (Proportion of surveys patch was hot)
Pro
port
ion
of
mon
ths s
ea lio
ns
fou
nd
fora
gin
g w
ith
in p
atc
hWinter: R2 = 0.41
0%
10%
20%
30%
40%
50%
0% 10% 20% 30% 40% 50% 60% 70%
Non-winter: R2 = 0.01
0%
10%
20%
30%
40%
50%
0% 10% 20% 30% 40% 50% 60% 70%
Pro
port
ion
of
mon
ths s
ea lio
ns
fou
nd
fora
gin
g w
ith
in p
atc
hPersistence: R2 = 0.41
Average Density (Proportion of surveys patch was hot)
0%
10%
20%
30%
40%
50%
- 5,000 10,000 15,000 20,000 25,000
Density: R2 = 0.36
1.1. Are prey aggregated in time and Are prey aggregated in time and space?space?• Overwintering herring schools result in high Overwintering herring schools result in high
prey aggregations Nov-Feb and occur in prey aggregations Nov-Feb and occur in consistent locations.consistent locations.
2.2. Do these prey ‘hot spots’ persist?Do these prey ‘hot spots’ persist?• The probability of encountering a high The probability of encountering a high
concentration of prey exceeded 70% for some concentration of prey exceeded 70% for some areasareas
3.3.Do predators respond to this Do predators respond to this persistence?persistence?• Strong relationship (during the winter) between Strong relationship (during the winter) between
sea lion distribution and distribution of prey. sea lion distribution and distribution of prey. However, it appears that sea lion’s response is However, it appears that sea lion’s response is strongest in areas with highest prey strongest in areas with highest prey persistence, not necessarily highest densitypersistence, not necessarily highest density
So So what?what?
A foraging effort model:A foraging effort model:
How will foraging effort of sea How will foraging effort of sea lions vary with density or lions vary with density or persistence of prey hot spots?persistence of prey hot spots?
xxx
TT11 TT22 TT33 ....T....T1010
Prey distribution: High density, low Prey distribution: High density, low persistencepersistence
xxx
Low density, low Low density, low persistencepersistence
xxx
Low density, high Low density, high persistencepersistence
PersistencePersistence
LowLow HigHighh
0
6
12
18
24
30
10 9 8 7 6 5 4 3 2 1Fora
gin
g E
ffort
Fora
gin
g E
ffort
Prey density = Prey density = HighHigh
Random walkRandom walkBayesian foragerBayesian forager
0
6
12
18
24
30
10 9 8 7 6 5 4 3 2 1
Prey density = Prey density = MidMid
PersistencePersistence
LowLow HigHighh
PersistencePersistence
LowLow HigHighh
0
40
80
120
160
10 9 8 7 6 5 4 3 2 1
Prey density = Prey density = LowLow
Density may not be Density may not be the only the only characteristic of prey characteristic of prey aggregations that are aggregations that are important to important to predators; predators; persistence may be persistence may be just as important, just as important, particularly for those particularly for those that do not have the that do not have the ability to search large ability to search large areas efficiently.areas efficiently.
Special thanks to : Dave Csepp, JJ Volldenweider, and Jamie Womble. This project funded by the Auke Bay Laboratory, National Marine Fisheries Service