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the Paul S. Sarbanes Ecosystem Restoration Project at Poplar Island

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Wetland Development in Dredged<br />

M<strong>at</strong>erial <strong>at</strong> <strong>the</strong> <strong>Paul</strong> S. <strong>Sarbanes</strong><br />

<strong>Ecosystem</strong> <strong>Restor<strong>at</strong>ion</strong> <strong>Project</strong> <strong>at</strong><br />

<strong>Poplar</strong> <strong>Island</strong><br />

Doldon Moore<br />

Maryland Board of Public Works<br />

Wetlands Administr<strong>at</strong>ion<br />

27 th Intern<strong>at</strong>ional Submerged Lands Management Conference<br />

Traverse City, MI October 26-29, 2008<br />

Maryland Port Administr<strong>at</strong>ion<br />

USACE Baltimore District<br />

Maryland Environmental Service


Overview<br />

• Background<br />

• Wetland Development<br />

• Lessons Learned<br />

• Monitoring


<strong>Paul</strong> S. <strong>Sarbanes</strong> <strong>Ecosystem</strong> <strong>Restor<strong>at</strong>ion</strong><br />

<strong>Project</strong> <strong>at</strong> <strong>Poplar</strong> <strong>Island</strong><br />

• Dredged m<strong>at</strong>erial placed from Baltimore Harbor Approach<br />

Channels<br />

• <strong>Island</strong> restor<strong>at</strong>ion will re-establish <strong>the</strong> approxim<strong>at</strong>e 1847 footprint


<strong>Project</strong> Loc<strong>at</strong>ion<br />

Mid-<br />

Chesapeake Bay,<br />

Maryland<br />

Talbot County


Tilghman <strong>Island</strong><br />

<strong>Poplar</strong> <strong>Island</strong><br />

2000<br />

Coaches <strong>Island</strong><br />

Jefferson <strong>Island</strong><br />

South Central<br />

<strong>Poplar</strong> <strong>Island</strong><br />

Middle<br />

<strong>Poplar</strong> <strong>Island</strong><br />

Sunken Barges<br />

North Point<br />

South


Landmass Comparison 1847-1993


<strong>Poplar</strong> <strong>Island</strong> Specific<strong>at</strong>ions<br />

• Size: 1,140 acres<br />

• Perimeter dike: 40,000 ft<br />

• Capacity: 42 mcy<br />

• Cost: $407 million<br />

• Uplands: 570 acres (50%)<br />

• Wetlands: 570 acres (50%)<br />

• To d<strong>at</strong>e, approxim<strong>at</strong>ely 13 mcy<br />

dredged m<strong>at</strong>erial placed<br />

• <strong>Project</strong>ed placement life until 2015


<strong>Poplar</strong> <strong>Island</strong> Site Development<br />

EAST<br />

Cell 6<br />

west<br />

• 6 Large Containment Cells: 4 Wetland Cells & 2 Upland Cells<br />

• Wetland Cells Temporarily Divided via Interior Dikes<br />

• Wetland Cells- 80% Low Marsh & 20% High Marsh


• Wetland Cell “3D”<br />

• 32 acres<br />

Wetland Cell Development


Wetland Cell Development<br />

Wetland Cell Development is a<br />

Four Phase Process:<br />

• Inflow and Crust Management<br />

• Grading and Channel Development<br />

• Inlet Structure Construction<br />

• Planting


Wetland Cell Development<br />

Inflow and Crust Management: April ‘01-Nov. ‘03<br />

•0.35 million cubic yards<br />

(mcy) of dredged m<strong>at</strong>erial<br />

inflowed into Cell 3D<br />

•Crust develops from<br />

dew<strong>at</strong>ering methods<br />

•Goal was to maximize<br />

consolid<strong>at</strong>ion and achieve <strong>the</strong><br />

appropri<strong>at</strong>e elev<strong>at</strong>ions


Crust Management<br />

Desicc<strong>at</strong>ion Cracks<br />

Pontoon trencher<br />

Pontoon Excav<strong>at</strong>or


Wetland Cell Development<br />

Grading & Channel Development: Dec. ‘03-Oct. ‘04<br />

Channel Excav<strong>at</strong>ion<br />

•M<strong>at</strong>erial excav<strong>at</strong>ed from channels was redistributed by grading<br />

•High Marsh elev<strong>at</strong>ions: Approxim<strong>at</strong>ely +2.2 ft<br />

•Low marsh: Approxim<strong>at</strong>ely +1.5 ft


Wetland Cell Development<br />

Inlet Structure Construction: Dec. ’04 – Jan. ‘05<br />

Pipes allow<br />

tidal interaction<br />

Weir boards


Spillways<br />

Interior of spillway,<br />

pipes lead to <strong>the</strong><br />

Bay<br />

Spillway<br />

boarded up with<br />

weir boards


Wetland Cell Development<br />

Inlet Structure – Opening to Tidal Flow: March ‘05<br />

Removing Weir boards<br />

Cell 3D during 1 st opening<br />

•Opened to tidal flow in March to note any areas of erosion before planting<br />

•Eventually structure will be removed in addition to <strong>the</strong> road above so th<strong>at</strong><br />

tidal inlet resembles a n<strong>at</strong>ural channel


Wetland Cell Development<br />

Planting: Planning<br />

Cell 3D Fe<strong>at</strong>ures:<br />

DESIGN<br />

TREATMENTS<br />

FEATURE<br />

Wetland Species Spartina p<strong>at</strong>ens,<br />

Spartina alterniflora<br />

Density of Geese 100’ x 100’, 75’ x 75’,<br />

Fencing<br />

50’ x 50’ and 25’ x<br />

25’<br />

Wetland Plant 1’, 2’, 3’, 4’, 6’<br />

Density<br />

Addition of None, 0.5 oz., 1.0 oz.<br />

Fertilizer<br />

Method of Planting Volunteer,<br />

Contractor<br />

Type of Planting Seed, Container,<br />

Plug and Bare Root<br />

Type of Substr<strong>at</strong>e Dredged,<br />

Sandy/Dredged,<br />

Sandy<br />

USACE, 2004


Wetland Cell Development<br />

Marsh Planting: April - July 05’<br />

•Total area planted: 897,500 sq ft<br />

•Total Spartina alterniflora plugs: 312,560<br />

•Total Spartina p<strong>at</strong>ens plugs: 174,160<br />

•Planting conducted by a contractor and volunteers<br />

organized by <strong>the</strong> N<strong>at</strong>ional Aquarium in Baltimore<br />

(6 acres).


Cell 3D October 2002 Cell 3D July 2006


Cell 3D Time Sequence<br />

(view looking east)<br />

June 2005 August 2005<br />

June 2006


Monitoring Elements<br />

• Veget<strong>at</strong>ion surveys<br />

• Plant chemical composition<br />

• Photo-document<strong>at</strong>ion<br />

• Visual inspections<br />

• Soil composition


Lessons Learned<br />

Method of Planting<br />

200<br />

<strong>Poplar</strong> <strong>Island</strong> Cell 3D Stem Height<br />

October 2006<br />

•Areas planted by <strong>the</strong> volunteers<br />

had similar biomass in<br />

comparison to contractor<br />

plantings<br />

Height (cm)<br />

150<br />

100<br />

50<br />

0<br />

High Marsh<br />

Low Marsh<br />

Contractual<br />

Volunteer<br />

•Volunteers are suitable to use for<br />

marsh plantings <strong>at</strong> <strong>Poplar</strong> in<br />

terms of success<br />

Percent<br />

120<br />

90<br />

60<br />

30<br />

<strong>Poplar</strong> <strong>Island</strong> Cell 3D Percent Cover<br />

<strong>Poplar</strong> <strong>Island</strong> Cell 3D Percent Cov<br />

October 2006<br />

October 2006<br />

0<br />

High Marsh<br />

Low Marsh<br />

Contractual<br />

Volunteer<br />

UMCES, 2007


Lessons Learned<br />

Fertilizer Additions<br />

• Quadrants with no<br />

fertilizer amendments<br />

had <strong>the</strong> same, if not more<br />

biomass than <strong>the</strong><br />

quadrants with fertilizer<br />

Height (cm)<br />

180<br />

150<br />

120<br />

90<br />

60<br />

30<br />

0<br />

<strong>Poplar</strong> <strong>Island</strong> Cell 3D Stem Height<br />

July 2006<br />

High Marsh<br />

Low Marsh<br />

a<br />

• Dredged m<strong>at</strong>erial<br />

contains high amounts of<br />

ammonium and<br />

phosphorus<br />

120<br />

90<br />

No Fert.<br />

Fert.<br />

<strong>Poplar</strong> <strong>Island</strong> Cell 3D Percent Cover<br />

July 2006<br />

b<br />

• Fertilizer should not be<br />

used in future plantings<br />

Percent<br />

60<br />

30<br />

0<br />

High Marsh<br />

Low Marsh<br />

No Fert.<br />

Fert.<br />

UMCES, 2007


Lessons Learned<br />

Type of Planting, Goose Fencing Density, Planting Density<br />

•Plugs appear to be <strong>the</strong> most reliable means of marsh establishment<br />

•Proper seed prep (pre-wet, chilled seeds) may help yield better<br />

results in dredged m<strong>at</strong>erial<br />

•Seeds have a much lower cost, so we will continue to experiment<br />

with using <strong>the</strong>m<br />

•Plant spacing can be increased to 3 feet spacing except on channel<br />

edges where more erosion is likely to occur<br />

•Geese were able to fly into <strong>the</strong> 100’ X 100’ grid and pred<strong>at</strong>e on<br />

plants; <strong>the</strong> 75’ X 75’ grid for fencing will be utilized in <strong>the</strong> future


Lessons Learned<br />

Mineral Nutrition – Too much of a good thing<br />

• Sediments were characterized as having an abundance of<br />

available nitrogen (as ammonium).<br />

• In 2007 some portions of <strong>the</strong> low marsh had much less growth<br />

in comparison to 2006.<br />

• It is specul<strong>at</strong>ed th<strong>at</strong> <strong>the</strong> high nitrogen content in <strong>the</strong> dredged<br />

m<strong>at</strong>erial caused <strong>the</strong> plants to have much more above than<br />

belowground biomass; this causes lodging which can inhibit<br />

plant growth during <strong>the</strong> next growing season.<br />

• As nitrogen accumul<strong>at</strong>es in plant tissue it becomes more<br />

<strong>at</strong>tractive to bugs and fungus and may make <strong>the</strong> plants more<br />

susceptible to infection.


Lessons Learned<br />

Mineral Nutrition – Too much of a good thing<br />

• The veget<strong>at</strong>ion will<br />

gradually remove<br />

nitrogen from <strong>the</strong><br />

sediments and over<br />

time Cell 3D should<br />

have a more typical<br />

growth p<strong>at</strong>tern.<br />

•Ongoing studies will<br />

continue track<br />

progress of Cell 3D.<br />

Including tissue<br />

sampling and above<br />

and belowground<br />

biomass surveys.<br />

July 2007


• Fertiliz<strong>at</strong>ion is not needed<br />

Lessons Learned<br />

Summary<br />

•Volunteers plant just as well as contractors (with <strong>the</strong><br />

proper oversight)<br />

• Plant spacing can be increased to 3 foot spacing except on<br />

channel edges<br />

•Though plugs are more efficient <strong>at</strong> marsh establishment<br />

seeds can still be used in moder<strong>at</strong>ion to cut costs as long as<br />

<strong>the</strong>y are prepped properly<br />

•75 X 75 foot grid for goose fencing works fine<br />

•Nitrogen levels in plant tissue needs to be monitored<br />

closely as well as above to belowground biomass r<strong>at</strong>ios.


“POP”ular Destin<strong>at</strong>ion<br />

Sandpiper<br />

Gre<strong>at</strong> Blue Heron<br />

American Avocet<br />

Willet<br />

Tree Swallow<br />

Gulls<br />

Red-winged Blackbird<br />

Snowy Egret<br />

Black Skimmer


Working Group<br />

• Meet with Working Group semi-annually in May and<br />

November<br />

• HSG meets every February and in August, if needed<br />

• MSG meets in August<br />

• Electronically transmit monthly newsletters to <strong>the</strong> WG<br />

members<br />

• Communic<strong>at</strong>e with Working Group and sub-groups<br />

electronically when need advice, proposal review, or to<br />

address specific site conditions<br />

• Group members are very responsive & play an active role<br />

in site development


Framework Monitoring<br />

• Exterior sediment<br />

quality<br />

• Exterior w<strong>at</strong>er quality<br />

• Benthics – community<br />

and tissue<br />

• Discharge monitoring<br />

• Construction turbidity<br />

monitoring<br />

• Shellfish bed<br />

sediment<strong>at</strong>ion<br />

• Interior w<strong>at</strong>er quality-<br />

algae monitoring<br />

• Wetland veget<strong>at</strong>ion<br />

• Wetlands use by fish<br />

• Fisheries use of<br />

exterior proximal<br />

w<strong>at</strong>er<br />

• Wetlands use by<br />

wildlife<br />

• Bird utiliz<strong>at</strong>ion counts<br />

• Submerged aqu<strong>at</strong>ic<br />

veget<strong>at</strong>ion<br />

• Diamondback terrapin<br />

monitoring<br />

• Wetland cell soil and<br />

veget<strong>at</strong>ion


Framework Monitoring<br />

• Principal Investig<strong>at</strong>ors prepare annual reports detailing <strong>the</strong><br />

results of Framework Monitoring elements<br />

• These are summarized and included in a comprehensive<br />

Annual Report<br />

• Recommend<strong>at</strong>ions regarding changes to <strong>the</strong> monitoring<br />

elements are reviewed with <strong>the</strong> HSG every February<br />

• These recommend<strong>at</strong>ions are <strong>the</strong>n used to upd<strong>at</strong>e <strong>the</strong><br />

Adaptive Management Plan<br />

• The recommend<strong>at</strong>ions are also added to <strong>the</strong> Habit<strong>at</strong><br />

Development Framework, which is upd<strong>at</strong>ed annually and<br />

details how to develop <strong>the</strong> desired habit<strong>at</strong>


Example of Working Group<br />

Coordin<strong>at</strong>ion<br />

• One of <strong>the</strong> EIS goals is to maintain sparsely veget<strong>at</strong>ed<br />

habit<strong>at</strong> islands for colonial w<strong>at</strong>er birds, such as terns<br />

• These islands were originally constructed of oyster shell on<br />

top of sand<br />

• These shell covered islands are not staying sparsely<br />

veget<strong>at</strong>ed<br />

• A significant amount of time and effort was going into<br />

cutting down <strong>the</strong> veget<strong>at</strong>ion and applying pre-emergent<br />

emergent<br />

herbicide before <strong>the</strong> terns arrive each year<br />

• However, <strong>the</strong> veget<strong>at</strong>ion was growing back during <strong>the</strong><br />

nesting season and HSG was concerned th<strong>at</strong> this re-growth<br />

could cause nesting failure


Shell Covered Nesting <strong>Island</strong>s<br />

Shell island<br />

approxim<strong>at</strong>ely 1 year<br />

after construction<br />

Shell island in 2003,<br />

after weed-whacking


Reconstructing Nesting <strong>Island</strong>s<br />

• The maintenance issue was discussed with <strong>the</strong> HSG to<br />

determine wh<strong>at</strong> needed to be done to make <strong>the</strong> islands<br />

sparsely veget<strong>at</strong>ed and as maintenance free as possible<br />

• Looked <strong>at</strong> various substr<strong>at</strong>es and tre<strong>at</strong>ments to apply on<br />

top of <strong>the</strong> existing substr<strong>at</strong>e<br />

• Determined th<strong>at</strong> whole oyster or clam shell were not<br />

available, so group suggested pea gravel as <strong>the</strong> cover<br />

• A plan was developed where geo-textile, rock salt and pea<br />

gravel are being tested in various combin<strong>at</strong>ions on 2 of <strong>the</strong><br />

original shell covered islands<br />

• A monitoring plan was also developed to determine <strong>the</strong><br />

success of <strong>the</strong>se various tre<strong>at</strong>ments


<strong>Island</strong> Re-construction


Terns!!<br />

Final Result


Questions

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