danielle kreeger, josh moody, kurt cheng and dave busheksummit+presentati… · water quality and...
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Blue Collar Bivalves, Water Quality and Project ROI
Danielle Kreeger, Josh Moody, Kurt Cheng and Dave Bushek
Bivalves of the Delaware
Crassostrea virginica
Elliptio complanata
Geukensia demissa
Alasmidontaheterodon
Mya arenaria
Anodonta implicata
Mytilus edulis
Ensis directus
Mercenaria mercenaria
Leptodea ochracea
Nature’s Benefits (Natural Capital)
Shellfish for Cleaner Water
Start
3 Hours
FreshwaterMussels
RibbedMussels Oysters
Freshwater Mussels: most imperiled
Oysters: prone to disease and salinity
Ribbed Mussels: losing marsh habitat
Bivalve Population Declines
Shellplanting for OystersPropagate and Reintroduce Mussels
Riparian Restoration
Fish Passage Restoration
Water Quality & Flow Management
•
Monitoring & Research
Living Shorelines
Tech to Restore Shellfish Now Exists
Living Shorelines
Funding and Capacity are Limited
http://delawareestuary.org/science_programs_state_of_the_estuary_treb.asp
Which Species is Best?
8
Which Tactic is Best?
Species Comparison
9
• Physiological Capacity
• Population Carrying Capacity
• Ecological Barriers
• Policy Barriers
• Willingness to Pay
Bivalve Feeding Physiology
Goal: satisfy nutritional demands from seston supply
Organismal Needs:Energy (C)Essential biochemicalsVariation: ‐ seasonal
‐ ontogenetic
Environmental Constraints:Food Quantity and QualityTemperatureVariation: ‐ seasonal
‐ spatial
Feeding Rate Comparison
Approach:
• Natural Diets • Consistent Methods (30 yrs)• Seasonal experiments • Ambient temperatures
GametogenesisConditioning
Seasonal Physiology Cycle
Feeding Rate Comparison10 Species – fresh, brackish, salt
ConditioningOregonMussels
AlleghenyMussels
BrandywineMussels
New JerseyAsian Clams
Cheng 2015
Canary Creek
Ribbed Mussels
Kreeger 1986;
Moody 2016
Kreeger1986
Kreeger and Howard 2011 Kreeger 2001 Kreeger and Gatenby 2002
Clearance Rates – Temperatures >20oCC
lear
ance
Rat
e (L
h-1
g-1
±SE
)
0 .0
0.5
1.0
1.5
2.0
Freshwater M usselN on-N ative C lamSaltwater Species
Marg. fa
lc.
Anod. calif.
Gonid. ang.
n=47
n=6
Lasmi. c
ost.
Elip. c
omp.Elip
. dilit
.
Act. lig
am.
Corb. fl
um.Geuk.
dem.
n=34
n=20
n=20
n=16
n=23
n=25 n=
25
n=90
n=20
n=11
9 Species: 0.5 ‐ 1.6 L/hr/g
Cle
aran
ce R
ate
(L h
-1 g
-1 ±
SE)
0 .0
0 .5
1 .0
1 .5
2 .0
F reshwa te r M usse lN on -N a tive C lamS a ltw a te r S pe c ies
Marg. fa
lc.
Anod. calif.
Gonid. ang.
n= 47
n=38
Anod. ore
g.
Corb. fl
um.Geuk.
dem.
n=23
n=13
n=80
n=25 n=
25
n=3n=
15
n=8
Crass
. virg
.
7 Species: 0.3 ‐ 1.6 L/hr/g
Clearance Rates – Temperatures 15 ‐ 20oC
Cle
aran
ce R
ate
(L h
-1 g
-1 ±
SE)
0 .0
0 .5
1 .0
1 .5
2 .0
F re s h w a te r M u s s e lN o n -N a tive C la mS a ltw a te r S p e c ie s
Marg. fa
lc.
Anod. calif.
Gonid. ang.
n = 4 7
n=38
Anod. ore
g.
Corb. fl
um.
Geuk. dem.
n=31
n=5
n=26
n=25 n=
25
n=56
n=12
n=1
6 Species: 0.1 ‐ 0.8 L/hr/g
Clearance Rates – Temperatures < 15oC
Month
2 3 4 5 6 7 8 9 10 11 120
30
60
90
120
150
180
0
20
40
60
80
100
TSS
(mg/
L)O
rganic Content
(%)
Seston Composition Highly Variable
Filtration Rates – Temperatures >20oC
8 Species: 1 ‐ 314 mg/hr/g
Filtr
atio
n R
ate
(mg
h-1 g
-1 ±
SE)
0
50
200
300Freshwater M usse lN on-N ative C lamSaltwater Species
Marg. fa
lc.
Anod. calif.
Gonid. ang.
n=38
Ellip. d
il.
Corb. fl
um.Geuk.
dem.
n=20
n=6
n=26 n=
23
n=90
n=11
n=20
n=20
Lasmig. c
ost.
Actin. li
g.
n=16
Physiological Findings
18
• Clearance rates of water were comparable among freshwater, brackish and marine species when normalized for body size and temperature
• Filtration rates of particles and associated pollutants depends largely on particle abundance and composition
• Models of biofiltration services can be constructed with data on:• Body Size and Abundance (Dry Tissue Mass)• Temperature (Season)• Seston Composition (TSS, %Organics, Nutrients)
Shellfish Strategies
19
• Increase suitable habitat e.g. oyster shellplanting, stream bed stabilization
• Enhance population abundance e.g. hatchery propagation, reseeding
• Alleviate stressors e.g. flows for salinity control, stormwater
• Improve growing conditions e.g. remove dams, sustain food quality
Considerations
20
• Track Record of Success How sustainable are the outcomes?Would carrying capacity be exceeded?
• Geospatial NichesWhat is the nexus between pollutants and species niches?Where would shellfish enhancements be most effective?
• Policy and Interest BarriersAre there restrictions on commercial species?Is there sufficient interest in noncommercial species?
• Cost
Three Case Studies
21
Alewife floaters Anodonta implicata
Ribbed musselsGeukensia demissa
Oysters Crassostrea virginica
Alewife Floaters
22
A functional co‐dominant in tidal Delaware River
Anodontaimplicata
Population Biomass by Species Densities up to 100 per square meter
=10 tons dry TSS per hectare per year
Physiologically‐Based BioFiltration Estimates
Bed Clearance
Rate
TSS Filtration
(L hr‐1 g DTW‐1)
(gal day‐1
g DTW‐1)(gal day‐1)
(kg DW day‐1)
Site 1 4,230 23,163 74,210 411,867 7.8
Site 2 18,648 477,389 992,074 5,506,008 104.2
Site 3 13,983 256,560 241,151 1,338,387 25.3
Site 4 35,525 1,662,570 586,163 3,253,202 61.6
Total 72,386 2,419,682 1,893,597 10,509,464 198.9
0.875 5.55
LocationArea (m2)
Number Tissue Weight (g)
Clearance Rate
Kreeger et al. 2013
Freshwater mussels in tidal Delaware River
Alewife Floaters
24
Investment in Mussel Hatchery
• Produces 500,000 seed per year• Seed are stocked into impaired streams• Survival ~90%, lifespan >30 years, normal growth• Cost is $400,000 per year (once operational)
See poster by Kurt Cheng
Alewife Floaters
25
Predicted Outcomes: Seston Filtration
~1,000 tons per year by Yr 16
Year2 4 6 8 10 12 14 16TS
S Fi
ltrat
ion
(tons
per
yea
r)
0
200
400
600
800
1000
Stream seeding starts
Year0 5 10 15 20 25 30
TSS
Filtr
atio
n (c
um. t
ons)
0
5000
10000
15000
20000
25000
30000
Stream seeding starts
>30,000 tons TSS by Yr 30
TSS TSS
Alewife Floaters
26
Predicted Outcomes: Nitrogen Filtration
~78,000 lbs/yr by Year 30 >870,000 total lbs by Year 30
Year0 5 10 15 20 25 30pN
Filt
ratio
n (c
um. p
ound
s)0
200000
400000
600000
800000
Stream seeding starts
Year0 5 10 15 20 25 30pN
Filt
ratio
n (p
ound
s/ye
ar)
0
20000
40000
60000
80000
Stream seeding starts
pN pN
Alewife Floaters
27
Return on Investment ?
• Healthy mussel bed >400 pounds N per ha/yr
• No established N market in Delaware River Basin
• TSS removal would cost $400 per ton (dry weight)
• Nitrogen removal would cost $14 per pound
• ROI analyses ignore many ecological benefits
Ribbed Mussels
28
A functional dominant of salt marshes
Mussel tissue biomass exceeds 200 kg per hectare
Concentrated along edge
TSS Removal
• 92.6 metric tons per hectare per year
Particulate Nitrogen Removal
• > 1,000 lbs N per hectare per year
Moody et al. In Prep.
Ribbed Mussels
Losing:69,518 mussels per day8.4 mil L/d filtration capacity
Marsh loss in Delaware Estuary
Ribbed Mussels
Living Shorelines with Ribbed Mussels
May 2010 June 2011June 2010
Shell Bags Packed with Mussels
Dual Benefits of Living Shorelines:
• Stem loss of marsh & associated services
• Boost shellfish services along edge
32
ROI?• Healthy mussel bed >1,000 pounds N per ha/yr
• Typical shellfish‐based living shorelines cost $20‐200 per linear foot (assume $100/ft)
• Assume 100 m LS protects 1 ha of marsh
• Preservation of N services costs $31 per pound N
• Edge restoration will lower this price
• ROI analyses ignore many ecological benefits
Ribbed Mussels
Oysters
33
A functional dominant of Delaware Bay
Form large reefs in many areas
Subtidal mainly, some intertidal
Oysters
34
Shellplanting very effective: 25:1 commercial ROI
Oysters
35
Shellfish Breakwaters also appear very effective:
See poster by Spencer Roberts
Three Case Studies
36
Alewife floaters Anodonta implicata
Ribbed musselsGeukensia demissa
OystersCrassostrea virginica
Pro• Effective• Opportunity• Intercept
pollutants
• Effective• Opportunity• Dual benefits• Filter bacteria
• Effective• Opportunity• Industry
support
Con• Carrying
capacity?• Low interest• No hatchery
• Low interest• No hatchery
investment
• Dermo• Policy bans• Industry
conflicts
Summary
37
• Freshwater and saltwater bivalves filter water similarly•Most populations are in decline and deserve protection• Enhancing all native species can boost water quality• Future Needs:
o Research on the fate of filtered pollutants (gross vs. net)o Research on carrying capacity in changing climateo Studies of habitat suitability & restoration R & Do Support for hatcheries and implementationo Studies of ROI
CTUIR Freshwater Mussel Project
Healthy Bivalves = Healthy Estuaries
Kreeger
Thank You!
39
Danielle KreegerScience Director(302) 655-990, x104 │ DelawareEstuary.org
Connecting people, science, and naturefor a healthy Delaware River and Bay
Bonus Slides
40
Absorption EfficienciesAb
sorp
tion
Effic
ienc
y (%
)
0
2 0
4 0
6 0
8 0
Marg
. falc.
Anod. calif.
Gonid. ang.
Actin. li
g.
n=24
n=20
n=19
n=25
n=85n=17
n=36
Lasmig. c
ost.
Ellip. d
il.
7 Species: 36 – 66%Not much variation among species
Absorption Efficiencies
Food use increases with food quality
34 44 54 64 74 84 940
20
40
60
80
100n=209, 6 species
Seston Organic Content (%)
Abs
orpt
ion
Effic
ienc
y (%
)
Ammonia Excretion versus Nutritional Status
Bivalves likely remineralizemore N in eutrophicestuaries
More work is needed
Bioavailable N in Seston
Mytilus edulis
Kreeger & Langdon 1993