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Salt Marsh Integrity Assessment Program in USFWS region 5

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<strong>Salt</strong> <strong>Marsh</strong> <strong>Integrity</strong> <strong>Assessment</strong> <strong>Program</strong><br />

<strong>in</strong> <strong>USFWS</strong> Region 5<br />

SusanC. Adamowicz; Neckles, Hilary;<br />

Guntenspergen, Glenn; Shriver, Greg; Taylor, Jan


Background<br />

• <strong>USFWS</strong> Region 5 National<br />

Wildlife Refuges<br />

• Refuge purposes…..<br />

– Threatened &<br />

Endangered Species<br />

– Migratory Birds<br />

– Wilderness<br />

– Shorebirds & Wad<strong>in</strong>g Birds<br />

– Encourage Natural<br />

Diversity<br />

– Conservation of Wetlands


Background cont.<br />

• US FWS has series of unrelated research<br />

projects but no common basel<strong>in</strong>e assessment<br />

Fundulus heteroclitus Length (mm)<br />

Before After 1 yr After 2+ yr<br />

Konisky et al. 2004


Background cont.<br />

• Desire for more<br />

<strong>in</strong>formed<br />

management<br />

decision mak<strong>in</strong>g<br />

at local and<br />

<strong>region</strong>al level<br />

Scott Kahan<br />

Refuge<br />

Manager<br />

Regional<br />

Refuge<br />

Chief<br />

Regional<br />

Director<br />

Wendi Weber<br />

Regional Natural<br />

Resources Chief<br />

Refuge<br />

Biologist<br />

Jan Taylor


Structured<br />

Decision<br />

Mak<strong>in</strong>g<br />

PrOACT<br />

Problem Def<strong>in</strong>ition<br />

Objectives<br />

Action alternatives<br />

Consequences (Predictive model)<br />

Trade-offs/Optimization (Solution algorithm)<br />

Monitor<strong>in</strong>g<br />

Reference: Smart Choices by Hammond, Keeney, and Raiffa


PrOACT<br />

Problem Def<strong>in</strong>ition:<br />

• Identify <strong>in</strong>dicators of salt marsh <strong>in</strong>tegrity that are<br />

effective across large geographic <strong>region</strong>s, responsive to<br />

a wide range of threats, and feasible to implement<br />

with<strong>in</strong> fund<strong>in</strong>g and staff<strong>in</strong>g constra<strong>in</strong>ts of the NWRS<br />

• Management/restoration decisions made for a given<br />

refuge at 3- to 5-year time scales,<br />

• The ecological and geographic focus of this exercise<br />

was historically brackish and sal<strong>in</strong>e marshes dom<strong>in</strong>ated<br />

by halophytic vegetation <strong>in</strong> FWS Region 5 (Northeast)


PrOACT<br />

• Objectives:<br />

Biological Diversity<br />

and <strong>Integrity</strong><br />

Obligate <strong>Salt</strong><br />

<strong>Marsh</strong> Breed<strong>in</strong>g<br />

Birds<br />

Nonbreed<strong>in</strong>g<br />

Wetland Birds<br />

Native<br />

Nekton<br />

Community<br />

Native Veg<br />

Community<br />

Trophic<br />

Structure<br />

Tidal Regime<br />

and Hydrology<br />

Environmental<br />

Health<br />

Herbicide<br />

Applied Dur<strong>in</strong>g<br />

Mgt.<br />

Ma<strong>in</strong>ta<strong>in</strong><br />

<strong>Marsh</strong> Area


<strong>Salt</strong> <strong>Marsh</strong> <strong>Integrity</strong> Objectives Hierarchy<br />

Biological Diversity and <strong>Integrity</strong> (0.5)<br />

Environmental Health (0.5)<br />

Obligate <strong>Salt</strong><br />

<strong>Marsh</strong> Breed<strong>in</strong>g<br />

Birds (0.10)<br />

Nonbreed<strong>in</strong>g<br />

Wetland Birds<br />

(0.10)<br />

Native Nekton<br />

Community<br />

(0.09)<br />

Native Veg<br />

Community<br />

(0.12)<br />

Trophic Structure<br />

(0.09)<br />

Tidal Regime and<br />

Hydrology (0.22)<br />

Ma<strong>in</strong>ta<strong>in</strong> <strong>Marsh</strong><br />

Area (0.22)<br />

Herbicide Applied<br />

Dur<strong>in</strong>g Mgt.<br />

(0.06)<br />

Birds/po<strong>in</strong>t<br />

Ave ABDU w<strong>in</strong>ter<br />

abundance<br />

Nekton Density<br />

(#/m2) (0.045)<br />

% cover native<br />

spp.<br />

<strong>Marsh</strong> spiders<br />

per m2<br />

Flood<br />

Duration (0.11)<br />

Relative change<br />

marsh surface<br />

elevation<br />

P<strong>in</strong>ts<br />

Nekton Species<br />

Richness (0.045)<br />

Sal<strong>in</strong>ity (0.11)<br />

Objective<br />

Measureable Attribute


Desire for “Rapid” Assessement<br />

Method<br />

Intensive<br />

• Obligate <strong>Marsh</strong> Bird Nest<strong>in</strong>g<br />

Success<br />

• Vegetation Quadrats<br />

• Nekton Throw Traps& Ditch<br />

Nets<br />

• Groundwater Wells<br />

• GIS<br />

“Rapid”<br />

• Bird Po<strong>in</strong>t Counts/Callback<br />

• Vegetation Transects<br />

• Veg: Visual Community ID<br />

• M<strong>in</strong>now Traps<br />

• Water Level Loggers<br />

• GIS


Rapid Method “F<strong>in</strong>al” List<br />

Historical condition and geomorphic sett<strong>in</strong>g<br />

Landscape_position<br />

• Landscape position: 1 (mar<strong>in</strong>e), 2 (middleestuary),<br />

3 (upper-estuary)<br />

• Shape: 1 (expansive meadow), 2 (narrow<br />

fr<strong>in</strong>g<strong>in</strong>g marsh)<br />

• Fill/fragmentation: 1 (no), 2 (low), 3 (mod),<br />

4 (severe)<br />

• Tidal flush<strong>in</strong>g: 1 (well flushed),<br />

2 (moderately flushed), 3 (poorly flushed)<br />

• Aquatic edge: 1 (low), 2 (mod), 3 (high)<br />

• Ditch Density: 1 (no), 2 (low), 3 (mod),<br />

4 (severe)


Rapid Method “F<strong>in</strong>al” List cont.<br />

Surround<strong>in</strong>g land-use<br />

• % agricultural land <strong>in</strong> 150 m buffer *<br />

(area of buffer/area of MSU)<br />

• % natural land <strong>in</strong> 150 m buffer * (area<br />

of buffer/area of MSU)<br />

• % natural land <strong>in</strong> 1 km buffer * (area<br />

of buffer/area of MSU)<br />

• Ratio of open water area :<br />

vegetation area


Rapid Method “F<strong>in</strong>al” List cont.<br />

<strong>Marsh</strong> surface elevation<br />

• Elevation to NAVD88<br />

Tidal range/groundwater level<br />

• % of Time <strong>Marsh</strong> Surface Flooded<br />

• Mean Flood Depth (cm)<br />

Sal<strong>in</strong>ity<br />

• Surface water sal<strong>in</strong>ity (@ nekton sites)


Rapid Method “F<strong>in</strong>al” List cont.<br />

Vegetation community<br />

• Species richness us<strong>in</strong>g rapid po<strong>in</strong>t<br />

<strong>in</strong>tercept method on transects<br />

• % Cover Visual Estimations of<br />

– Brackish Terrestrial Border<br />

Community<br />

– Open Water<br />

– Pannes, Pools, & Creeks<br />

– High <strong>Marsh</strong> Community<br />

– Low <strong>Marsh</strong> Community<br />

– <strong>Salt</strong> <strong>Marsh</strong> Terrestrial Border<br />

community<br />

– Upland Community<br />

– Invasive Plant Species


Rapid Method “F<strong>in</strong>al” List cont.<br />

Nekton community<br />

(throw trap, ditch nets)<br />

• Nekton Density<br />

• Nekton Species Richness<br />

• Fundulus heteroclitus length (mm)<br />

Breed<strong>in</strong>g bird community<br />

Po<strong>in</strong>t Count Surveys<br />

• Willet Abundance<br />

• Tidal <strong>Marsh</strong> Obligate Abundance<br />

• Call-broadcast surveys: Clapper Rail,<br />

Willet, <strong>Salt</strong>marsh Sparrow, Seaside<br />

Sparrow


Tidal Regime Influence Diagram<br />

Plant<strong>in</strong>g<br />

Vegetation<br />

Spray<br />

Phrag<br />

<strong>Marsh</strong><br />

Elevation<br />

Flood Duration<br />

(% Time<br />

Flooded )<br />

Sea Level<br />

Rise<br />

Dredge<br />

Spoil<br />

Deposition<br />

Freshwater<br />

Input<br />

Sediment<br />

Traps<br />

Divert<br />

freshwater<br />

Tidal<br />

Exchange<br />

with Bay /<br />

Ocean<br />

Flood Depth<br />

(above marsh<br />

surface)<br />

Tidal<br />

Regime &<br />

Hydrology<br />

Increase<br />

culvert size<br />

Excavate<br />

Channels<br />

Tidal Creek<br />

Density<br />

Sal<strong>in</strong>ity<br />

Goal<br />

<strong>Marsh</strong><br />

Mgmt for<br />

Mosquitoes<br />

Action<br />

Ditch Density<br />

Effect<br />

Measured<br />

Attributes


Alternatives and Consequence Table:<br />

Raw Scores (s ij )<br />

Objectives<br />

Unit Management Action 1 2 3 … 8 9 10<br />

I Current Status 15 200 50 … 0 1 0<br />

I<br />

(A) Excavate old ditch, <strong>in</strong>stall new<br />

culvert under road<br />

19 500 70 … 0 1 0<br />

I (B) Treat Phragmites <strong>in</strong> WUI zone 17 550 65 … 0 1 10<br />

… … …<br />

II (A) DE Bay dredge spoil deposition … …<br />

II<br />

(B) Excavate Old Slaughter Creek<br />

…<br />

…<br />

… … …<br />

III (C) + (D) + (F) … … 0<br />

Slide Courtesy of Jim Lyons


Multi-attribute Utility Theory<br />

utility<br />

Example: Tidal marsh obligate birds<br />

1.00<br />

0.90<br />

0.80<br />

0.70<br />

0.60<br />

0.50<br />

0.40<br />

0.30<br />

0.20<br />

0.10<br />

0.00<br />

0 5 10 15<br />

Score for tidal marsh obligate birds<br />

utility<br />

Example: Nekton density<br />

1.00<br />

0.80<br />

0.60<br />

0.40<br />

0.20<br />

0.00<br />

0.0000 0.0020 0.0040 0.0060 0.0080<br />

Score for Nekton density<br />

Management<br />

Benefit<br />

( ) ∑<br />

10<br />

U Action =<br />

i j =<br />

1<br />

w<br />

Utility functions for illustration purposes only. See spreadsheet for actual utility functions.<br />

Slide Courtesy of Jim Lyons<br />

j<br />

u<br />

ij


Multi-attribute Utility Theory<br />

utility<br />

Example: Tidal marsh obligate birds<br />

1.00<br />

0.90<br />

0.80<br />

0.70<br />

0.60<br />

0.50<br />

0.40<br />

0.30<br />

0.20<br />

0.10<br />

0.00<br />

0 5 10 15<br />

Score for tidal marsh obligate birds (birds / po<strong>in</strong>t)<br />

utility<br />

Example: Nekton density<br />

1.00<br />

0.80<br />

0.60<br />

0.40<br />

0.20<br />

0.00<br />

0.0000 0.0020 0.0040 0.0060 0.0080<br />

Score for Nekton density (# / m^2)<br />

Management<br />

Benefit<br />

( ) ∑<br />

10<br />

U Action =<br />

i j =<br />

1<br />

w<br />

Utility functions for illustration purposes only. See spreadsheet for actual utility functions.<br />

Slide Courtesy of Jim Lyons<br />

j<br />

u<br />

ij


Consequence Table: Utility (u ij )<br />

Objectives<br />

Unit Management Action 1 2 3 … 8 9 10<br />

I Current Status u 1,1 u 1,2 u 1,3 … u 1,8 u 1,9 u 1,10<br />

I<br />

(A) Excavate old ditch, <strong>in</strong>stall new culvert<br />

under road<br />

u 2,1 u 2,2 u 2,3 … u 2,8 u 2,9 u 2,10<br />

I (B) Treat Phragmites <strong>in</strong> WUI zone … …<br />

… … …<br />

II (A) DE Bay dredge spoil deposition … …<br />

II<br />

(B) Excavate Old Slaughter Creek<br />

…<br />

…<br />

… … …<br />

III (C) + (D) + (F) … … u i,j<br />

Slide Courtesy of Jim Lyons


Pareto Efficiency Frontier<br />

8<br />

Conservation Benefit<br />

7<br />

6<br />

5<br />

22<br />

17<br />

16<br />

18<br />

23<br />

13 14<br />

8 9<br />

6<br />

7<br />

24 29<br />

25<br />

34<br />

20<br />

19<br />

15<br />

10<br />

35<br />

4<br />

2<br />

1<br />

Current<br />

Status<br />

3<br />

4<br />

2<br />

0 100 200 300 400 500<br />

Cost over 15 years Slide (x Courtesy $1000) of Jim Lyons


Examples of Data Gathered:<br />

2009 pilot study<br />

Grape Nelson OMWM<br />

Sal<strong>in</strong>ity Mean SD Mean SD Mean SD<br />

Rapid_Sal<strong>in</strong>ity 39 17 nd . 14 1<br />

Vegetation community<br />

Spp Richness 3 4 6<br />

RA_Brack_Terr_Border np . np . np .<br />

RA_Open_Water np . 5 4 np .<br />

RA_Pannes_Pools_Creeks 23 10 8 7 15 17<br />

RA_High_<strong>Marsh</strong> 75 14 69 13 81 13<br />

RA_Low_<strong>Marsh</strong> 31 38 30 13 15 17<br />

RA_<strong>Salt</strong>_<strong>Marsh</strong>_Terr_Border np 6 3 np<br />

RA_Upland np 16 19 np<br />

Invasive species<br />

RA_Invasives np 8 9 3<br />

Nekton community<br />

Spp Richness 5 nd 1<br />

Density 16 1 nd 25 35<br />

Fundulus_Length 40 17 nd 36 16<br />

Breed<strong>in</strong>g bird community<br />

Willet_Abundance 3 4 15 11 15 10<br />

TMO_Abundance 4 3 9 5 12 6<br />

Data from Neckles et al. 2011, draft


2012 Implementation Sites<br />

Moosehorn NWR<br />

Ma<strong>in</strong>e Coastal Island NWR<br />

Rachel Carson NWR<br />

Parker River NWR<br />

RI Complex NWR<br />

Stewart B. McK<strong>in</strong>ney NWR<br />

Long Island Complex NWR<br />

Forsythe NWR<br />

Bombay Hook NWR<br />

Prime Hook NWR<br />

Ch<strong>in</strong>coteague NWR


2012 Data Analysis<br />

• Summary of number of po<strong>in</strong>ts, samples etc.<br />

– 11 National Wildlife Refuges from Ma<strong>in</strong>e to Virg<strong>in</strong>ia<br />

– A m<strong>in</strong>imum of<br />

• 34 salt marsh units<br />

• 680 nekton stations<br />

• 102 bird stations<br />

• 102 vegetation transects and community plots<br />

• 34 water level loggers deployed for at least 1 complete<br />

tidal cycle (spr<strong>in</strong>g and neap tide sequence)


Acknowledgements<br />

Field Crews from 12<br />

National Wildlife Refuges<br />

<strong>in</strong> 2008, 2009, 2012<br />

Project Developers: <strong>USFWS</strong>,<br />

USGS, Univ DE


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