the influence of varying tidal exchange on the...
TRANSCRIPT
The influence of varying tidal exchange on the ecology of
Elkhorn Slough
Amy Ritter and Kerstin WassonK. Alt-Griffth, S. Connors, S. Lonhart, R. Preisler, E. Van Dyke, A. Woolfolk,
Flow regime categories
1. Full flow (no structures restricting tidal exchange)
2. Restricted flow1. Muted – during rainy season,
tidal > freshwater influence
2. Minimal – during rainy season, freshwater > tidal influence
Roadmap to talk
• Synthesis of several studies looking at how various groups of organisms respond to differences in tidal influence
• Potential mechanisms influencing biological patterns
• Implications for management
Summary of studies synthesizedThe following studies examined how assemblage and community structure varied across flow regimes in Elkhorn Slough:• Fishes and crabs - Ritter, Preisler
• Aquatic invertebrates, algae, birds, and mammals - Wasson, Lonhart, Ritter
• Shorebirds - Connors
• Aquatic/terrestrial inverts - Alt-Griffith
• Marsh ecotone plants - Wasson and Woolfolk
• Data on average fish and crab abundance • Surveyed 19 shallow-water sites throughout Elkhorn
Slough in early spring and late summer (2005)• Used seines and both large and small minnow traps (3
replicates of each) to sample fishes and crabs• Amy Ritter, Rikke Preisler
Fish + Crab Study - Ritter and Preisler
• Data on average fish and crab abundance
• Multivariate data analysis:– Multidimensional scaling
(MDS - graph)
– Analysis of similarities (ANOSIM - table):
Pairwise Tests R SignificanceGroups Statistic Level FULL, MUTED -0.071 0.690FULL, MINIMAL 0.88 0.001MUTED, MINIMAL 0.726 0.001
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
Fish + Crab Study - Ritter and Preisler
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
• Data on average fish and crab abundance • Multivariate data analysis: Multidimensional scaling• Correlations between fish and crab species and MDS
scores (> 0.45)
3-spine stickleback
Ore. shore crab
Topsmelt
Shiner surfperch
Eur. green crab
Tidewater goby
Longjawmudsucker
Staghorn sculpin
Cal. halibut
MDS 1
MDS 2
-1.0 0 1.0
Correlation with MDS 1
0.5
Correlation with
MDS 2
0
-0.75-2.0 2.00
0
-1.0
1.0
Fish + Crab Study - Ritter and Preisler
• Similarity percentages (SIMPER) resultsFULL MUTED MINIMAL
Topsmelt Topsmelt 3-spine sticklebackOre. lined-shore crab Ore. lined-shore crab Longjaw mudsuckerStaghorn sculpin Staghorn sculpin TopsmeltEuropean green crab Goby complex Tidewater goby**Goby complex* Long-jaw mudsucker
European green crab
*Goby complex: Clevelandia ios and Lepidogobius lepidus** Tidewater goby only found in 2/9 minimal flow sites
Fish + Crab Study - Ritter and Preisler
Leptocottus armatus(staghorn sculpin)
% Differences between flow regimes:
•Full vs. Muted: 5.41
•Full vs. Minimal: 8.77
•Muted vs. Min.: 9.70
*Expected if all spp contribute evenly = 100/23 = 4.35%
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
LA
0.7
2.8
4.9
7
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
Fish + Crab Study - Ritter and Preisler
Atherinops affinis(topsmelt)
% Differences between flow regimes:
•Full vs. Muted: 12.31
•Full vs. Minimal: 16.00
•Muted vs. Min.: 17.86
*Expected if all spp contribute evenly = 100/23 = 4.35%
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
AA
20
80
140
200
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
Fish + Crab Study - Ritter and Preisler
% Differences between flow regimes:
•Full vs. Muted: 7.82
•Full vs. Minimal: 20.00
•Muted vs. Min.: 20.56
Gasterosteusaculeatus(threespinestickleback)
*Expected if all spp contribute evenly = 100/23 = 4.35%
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
GA
40
160
280
400
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09
Fish + Crab Study - Ritter and Preisler
• Data on presence of multiple species of inverts, algae, birds, mammals
• Surveyed 15 sites throughout Elkhorn Slough (2005)• Used sediment cores and visual surveys of soft and
hard substrate types to quantify species presence• Kerstin Wasson, Steve Lonhart, Amy Ritter
Community Study - Wasson et al.
• Data on presence of multiple species of inverts, algae, birds, mammals
• Multivariate data analysis:
– MDS (graph)
– ANOSIM (table):Pairwise Tests R SignificanceGroups Statistic LevelFULL, MUTED 0.192 0.135FULL, MINIMAL 0.852 0.008MUTED, MINIMAL 0.828 0.008
Community Study - Wasson et al. Resemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
L Moro Cojo
Moro Cojo Railroad
Struve
S Harbor
N Harbor
Old Mouth
Porter-Blohm
S Azevedo
Whistlestop
Hidden
N MarshN Marsh Exit
N Azevedo
KirbyHudsons
2D Stress: 0.1
• Similarity percentages (SIMPER) resultsFULL MUTED MINIMAL
Amphipods Amphipods Sea lettuce complex*Polychaetes Sea lettuce complex* Water boatmenSea lettuce complex* Jap. mud snail Brackish snailAmethyst gem clam Nemerteans Black-necked stiltJapanese mud snail Red turf algaeAcorn barnacles Diadumene anemonesBay mussel complex** Polychaetes
*Sea lettuce complex: Ulva fenestrata, U. linza, and U. intestinalis**Bay mussel complex: Mytilus galloprovincialis and M. trossulus
Community Study - Wasson et al.
• Data on abundance of inverts (aquatic and terrestrial)
• Surveyed 21 sites throughout Elkhorn Slough in summer and winter (2005)
• Used astroturf collectors to sample invertebrates at the lower edge of the marsh zone
Invertebrate Study - Alt-Griffith
• Data on abundance of inverts (aquatic and terrestrial)
• Multivariate data analysis:
– MDS (graph)
– ANOSIM (table):
Pairwise Tests R SignificanceGroups Statistic LevelFULL, MUTED 0.067 0.322FULL, MINIMAL 0.243 0.009MUTED, MINIMAL 0.478 0.012
Invertebrate Study - Alt-GriffithTransform: Fourth rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
Old Mouth
Campagna
Coyote
Dominic's
Estrada
Hidden
Hudson
Hummingbird
N Harbor
Kirby
Five Fingers S Azevedo
Moro Cojo Bridge
M Azevedo
MLML Marsh
Packard Main
Porter-BlohmStruve
Crazy Cow
WhistlestopYampah
2D Stress: 0.2
• Similarity percentages (SIMPER) resultsFULL MUTED MINIMAL
Estuarine amphipod Estuar. amphipod Water boatmenBeach hopper Jap. mud snail Estuar. amphipodAmethyst gem clam Brachyceran fliesMussel shrimp/ostracods SpidersSpiders Brine fliesShore bugs Mussel shrimp/ostracodsJapanese mud snail Calif. Assiminea snail
Invertebrate Study - Alt-Griffith
• Data on average abundance of shorebirds• Visual surveys of 17 sites throughout Elkhorn
Slough• Multiple surveys conducted during spring, fall, and
winter (1999-2000)• Sarah Connors
Shorebird Study - Connors
• Data on abundance of shorebirds
• Multivariate data analysis:
– MDS (graph)
– ANOSIM (table):
Pairwise Tests R SignificanceGroups Statistic LevelFULL, MUTED 0.424 0.121FULL, MINIMAL 0.796 0.001MUTED, MINIMAL 0 0.476
Transform: Fourth rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
ES-AES-BES-CES-D
ES-EN Harbor
Old Mouth
N Strawberry
N Marsh
EstradaS Marsh
Five Fingers
W Salt ponds
E Salt ponds
Moro CojoSalinas River
Porter-Blohm
2D Stress: 0.04
Shorebird Study - Connors
• Similarity percentages (SIMPER) resultsFULL MUTED MINIMAL
Dowitcher Willet
Least sandpiper Least sandpiper Black-necked stiltWestern sandpiper Western sandpiper Least sandpiperWillet Dunlin American avocetMarbled godwit Marbled godwit Western sandpiperDunlin Dowitcher Dowitcher
Black-bellied plover
Shorebird Study - Connors
• Data on marsh plant relative abundance• 18 sites around Elkhorn Slough• 3 transects / site to assess plant assemblages and
soil parameters• Kerstin Wasson, Andrew Woolfolk
Marsh Plant Study - Wasson +Woolfolk
• Data on marsh plant relative abundance
• Multivariate data analysis:
– MDS (graph)
– ANOSIM (table):
Pairwise Tests R SignificanceGroups Statistic LevelFULL, MUTED 0.625 0.029FULL, MINIMAL 0.01 0.486MUTED, MINIMAL 0.354 0.114
Marsh Plant Study - Wasson +WoolfolkTransform: Square rootResemblance: S17 Bray Curtis similarity
FLOWFULLMUTEDMINIMAL
Azevedo Pen
Coyote
MLML Marsh
Yampah
N Azevedo
N Marsh
Whistlestop
Old Mouth
Porter-Blohm
Estrada
Crazy Cow
Struve
2D Stress: 0.12
Ecotone width* shows similar pattern as multivariate community analysis: muted flow is the outlier, with a very narrow band of ecotone
*distance from 100% cover by marsh plants to 100% by upland plants
EcotoneWidth (cm)
FULL MUTED MINIMAL0
100
200
300
400
500
600
700
800
900
1000
Marsh Plant Study - Wasson +Woolfolk
• Similarity percentages (SIMPER) resultsFULL MUTED MINIMAL
Pickleweed Pickleweed Pickleweed
Alkali heath Jointed charlock/ Wild radish
Saltgrass
Saltgrass Unidentified fescue
Fleshy jaumea Soft chess
Marsh Plant Study - Wasson +Woolfolk
Fish and crab study Community study
Invertebrate study
3 studies found significant differences in assemblage/community structure between minimal flow and
both muted/full regimes
FLOWFULLMUTEDMINIMAL
Coyote
Hudson
Hummingbird
Kirby
Packard Main
S Marsh
Old MouthEstrada
Hidden
M Azevedo
N Marsh
N Strawberry
WhistlestopCrazy Cow
Packard Pond
Porter-Blohm
S Azevedo
L Moro Cojo
Struve
2D Stress: 0.09 FLOWFULLMUTEDMINIMAL
L Moro Cojo
Moro Cojo Railroad
Struve
S Harbor
N Harbor
Old Mouth
Porter-Blohm
S Azevedo
Whistlestop
Hidden
N MarshN Marsh Exit
N Azevedo
KirbyHudsons
2D Stress: 0.1
FLOWFULLMUTEDMINIMAL
Old Mouth
Campagna
Coyote
Dominic's
Estrada
Hidden
Hudson
Hummingbird
N Harbor
Kirby
Five Fingers S Azevedo
Moro Cojo Bridge
M Azevedo
MLML Marsh
Packard Main
Porter-BlohmStruve
Crazy Cow
WhistlestopYampah
2D Stress: 0.2
1 study found significant differences in assemblage structure between full flow and minimal flow regimes only
Shorebird study
Marsh plant study
1 study found significant differences in assemblage structure only between full flow and muted flow regimes
FLOWFULLMUTEDMINIMAL
ES-AES-BES-CES-D
ES-EN Harbor
Old Mouth
N Strawberry
N Marsh
EstradaS Marsh
Five Fingers
W Salt ponds
E Salt ponds
Moro CojoSalinas River
Porter-Blohm
2D Stress: 0.04
FLOWFULLMUTEDMINIMAL
Azevedo Pen
Coyote
MLML Marsh
Yampah
N Azevedo
N Marsh
Whistlestop
Old Mouth
Porter-Blohm
Estrada
Crazy Cow
Struve
2D Stress: 0.12
02468
10121416
0
10
20
30
40
50
0
10
20
30
40
50
60
Invertebrates
1° Producers
Fishes
FULL MUTED MINIMAL
Species Richness(# spp / regime)
Freshwater/Terrestrial NON-NATIVE
Freshwater/Terrestrial NATIVE
Estuarine NON-NATIVE
Estuarine NATIVE
Marine NON-NATIVE
Marine NATIVE05
10152025303540
Birds
FULL MUTED MINIMAL
FULL MUTED MINIMAL
FULL MUTED MINIMAL
Summary of results• Multivariate showed effect of flow regime,
but differences by study/indicator– Minimal most different– Most threatened spp found in minimal
• Univariate analysis by taxon shows differences across taxa– Reduced richness in minimal for fish and inverts– In general, more freshwater influence in minimal,
more marine influence in muted
Roadmap to talk
• Synthesis of several studies looking at how various groups of organisms respond to differences in tidal influence
• Potential mechanisms influencing biological patterns
• Implications for management
Potential mechanisms behind ecological patterns across flow regimes
Structures can alter conditions upstreame.g. physical, chemical
Structures can restrict transport of organismse.g. behavior, mobility, size
A B C
C D E
X
X
A B C
C D E
AB
DE
XX
XX
Water Quality Data – Monthly volunteer “snapshot” surveys
• Muted/minimal flow sites tend to have smaller tidal range and lower rainy season salinity, and greater values of all other factors compared to full flow sites
-1.0 -0.5 0.0 0.5 1.0Correlation with MDS 1
-1.0
-0.5
0.0
0.5
1.0
Correlation with
MDS 2
DO
Salinity (dry)
NH3
NOX
pH
PO4
Salinity (rainy)Temperature
Tidal Range
Turbidity_
MDS 1
MDS2
NormaliseResemblance: D1 Euclidean distance
FLOWFULLMUTEDMINIMAL
Old Mouth
Hudsons
Kirby
Crazy Cow
L Moro Cojo
M Azevedo
N Harbor
N Marsh
Porter
Reserve BridgeSkippers
S Azevedo
S Harbor
S Marsh
Struve
2D Stress: 0.08
Roadmap to talk
• Synthesis of several studies looking at how various groups of organisms respond to differences in tidal influence
• Potential mechanisms influencing biological patterns
• Implications for management
Implications for management• Biological data supports that there is a mosaic
of habitats throughout the slough (esp. minimal are different from full flow sites )
• Mosaic increases overall biodiversity in the Slough
• Full and muted are very similar for most taxa
• While minimal has lowest species richness overall, it harbors unique species and some threatened species
TIDAL RANGE (in cm, measured on a spring tide)
0 2 7 45 88
South Azevedo Struve Pond North Marsh Whistlestop Bennett Slough
Restricted flow sites at Elkhorn Slough span a continuum of tidal exchange
TIDAL RANGE (in cm, measured on a spring tide)
0 2 7 45 88
threatened brackish speciese.g. tidewater goby, Tryonia snail
key marine visitors e.g. migratory shorebirds, commercial fish nurseries
Also a continuum of habitat use by potential conservation targets
South Azevedo Struve Pond North Marsh Whistlestop Bennett Slough
TIDAL RANGE (in cm, measured on a spring tide)
0 2 7 45 88
Low tidal exhangeLimited flushing can result in poor water quality
And a continuum of ecological concerns
, and these habitats have limited connectivity with the estuarine network, but habitats are not subject to tidal erosion
High tidal exchangeGood flushing improves water quality, and there is good connectivity, but some habitats are subject to tidal erosion
South Azevedo Struve Pond North Marsh Whistlestop Bennett Slough
TIDAL RANGE (in cm, measured on a spring tide)
0 2 7 45 88
Restricted flow sites at Elkhorn Slough span a continuum of tidal exchange
Do we want representation of all parts of this continuum for the future?In what proportion?
South Azevedo Struve Pond North Marsh Whistlestop Bennett Slough
TIDAL RANGE (in cm, measured on a spring tide)
0 2 7 45 88
Restricted flow sites at Elkhorn Slough span a continuum of tidal exchange
Straw man for even representation of entire spectrum
South Azevedo Struve Pond North Marsh Whistlestop Bennett Slough
TIDAL RANGE (in cm, measured on a spring tide)
0 2 7 45 88
Restricted flow sites at Elkhorn Slough span a continuum of tidal exchange
Straw man for “Goldilocks” model: aim for middle range, with no representation of extremes
South Azevedo Struve Pond North Marsh Whistlestop Bennett Slough
Do we want representation of the entire continuum of tidal exchange? In what proportion?
What are the key ecological values of each flow regime? Key concerns?
What are the consequences of limited connectivity between restricted and unrestricted flow sites?
How long are estuarine assemblages likely to persist in minimal flow sites managed for no tidal exchange?
Do any existing restricted exchange sites seem like they would be good models for the proposed tidal restriction project at Parson’s?