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Flowering Rush - Center for Invasive Plant Management

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<strong>Flowering</strong> <strong>Rush</strong><br />

An <strong>Invasive</strong> Aquatic Macrophyte<br />

Infesting the Columbia River Basin<br />

Peter Rice, University of Montana,<br />

Virgil Dupuis & Alvin Mitchell, Salish Kootenai College


<strong>Flowering</strong> <strong>Rush</strong><br />

(Butomus umbellatus)<br />

•umbel shaped cluster<br />

of ~30 flowers<br />

•3 whitish pink petals &<br />

3 similar sepals<br />

•green leaves are<br />

triangular in cross<br />

section<br />

•leaf tips may be<br />

spirally twisted<br />

•strongly rhizomatous


(c) Gary Fewless<br />

Rhizome fragmentation is primary mechanism<br />

of dispersal and reproduction


<strong>Flowering</strong> <strong>Rush</strong> (Butomus umbellatus)<br />

East Bay Flathead Lake MT


Eurasian<br />

Origin


North American Invasion<br />

• circa 1895-1905 St. Lawrence River region<br />

•1949 Snake River Idaho (Idaho Falls)<br />

Infested Counties in WA, OR, ID, MT, WY<br />

•1964 Flathead Lake (north shore: Peaceful Bay)


• Fully Submerged Form at 10-20 ft depths<br />

• Emergent Form at 0-10 ft depths<br />

• Shoreline Form at surface groundwater table


Inflorescence Bulblets<br />

Rhizome Buds & Fragments<br />

Seed<br />

Rhizome Bulblets


Diploid Triploid<br />

self-compatible self-sterile within clones<br />

prolific flowering infrequent flowering<br />

high seed production low production of sterile<br />

seeds<br />

prolific bulblet<br />

production (rhizome &<br />

inflorescence)<br />

primary dispersal is by<br />

vegetative structures<br />

2 karotypes<br />

inflorescence bulblet<br />

production not evident<br />

disperses only by<br />

rhizome fragmentation


Buoyant Rhizome Fragments


Rhizome Fragments on<br />

Unvegetated Littoral Zone Sediments


Pre<strong>for</strong>med Roots and Large Carbohydrate Reserve Quickly Anchor Fragments In Sediments<br />

Apr 30, 2009


Kerr Dam<br />

1 st (1964)<br />

Peaceful<br />

Bay<br />

Flathead Lake<br />

Known Infestations<br />

Flathead Lake<br />

Partial Survey<br />

Data Through<br />

10/13/2008


<strong>Invasive</strong>s of Wetlands & Shoreline<br />

(Displacing Native <strong>Plant</strong>s)


Shoots Emerging in Late March/Early April


<strong>Flowering</strong> <strong>Rush</strong> Displacing Native Bulrush<br />

(March to May Emergence Be<strong>for</strong>e Natives)


Kerr Dam Induced Low Pool in Spring<br />

Favors <strong>Flowering</strong> <strong>Rush</strong> Over Native Macrophytes


Flathead River Above Kerr Dam<br />

Bottom Barrier


Robust Triploid<br />

Dispersing Out of Flathead Lake<br />

Lateral<br />

Rhizome<br />

Bud


Kerr Dam Spillway from Flathead Lake to River


Flathead Lake Is On<br />

a Northerly Reach of<br />

the Columbia River<br />

System<br />

American Falls


Dispersal Down the Columbia River System<br />

• Kerr Dam into Flathead and Clark Fork Rivers (MT)<br />

• Thompson Falls, Noxon, Cabinet Reservoirs (MT)<br />

• 165 Miles & Into Lake Pend Oreille (ID)<br />

• Snake River Aberdeen-Springfield Canal Irrigation<br />

Systems (ID)


Perma Bridge<br />

~ 2.5 Infestation per Mile on Flathead River


Flathead River Above Paradise MT<br />

Incipient <strong>Flowering</strong> <strong>Rush</strong> Infestation


American Falls<br />

Infestations<br />

at the<br />

Headwaters of<br />

the Southerly<br />

Reach of the<br />

Columbia<br />

River System


Aberdeen-Springfield Canal System<br />

(Spills to Snake River at American Falls ID)


Aberdeen-Springfield Canal System<br />

(Spills to Snake River at American Falls ID)


Aberdeen-Springfield Canal System<br />

(Spills to Snake River at American Falls ID)<br />

Chaining to Reduce <strong>Flowering</strong> <strong>Rush</strong>


Aberdeen-Springfield Canal System<br />

(Spills to Snake River at American Falls ID)<br />

Chaining Induces Rhizome Fragmentation & Dispersal


Aberdeen-Springfield Canal System<br />

(Spills to Snake River at American Falls ID)


Pablo Reservoir Irrigation Lift Station<br />

Flathead Lake/River<br />

<strong>Flowering</strong> <strong>Rush</strong> Colony


Flathead Valley Pablo Reservoir Irrigation Canal<br />

6.7 Million Acres Irrigated by<br />

Withdrawals From<br />

Columbia River System


Fishing Access Site Boat Ramp


Prop Fowling Stalls Motors & Facilitates Dispersal<br />

(c) BASF Corporation. Photo by Mitch Kezar


Private Boat Docks Surrounded by <strong>Flowering</strong> <strong>Rush</strong><br />

(c) BASF Corporation. Photo by Mitch Kezar<br />

Not Only A Nuisance But Also a Contributing Factor in Dispersal


(c) BASF Corporation.<br />

Photo by Mitch Kezar<br />

Ideal Habitat <strong>for</strong> Great Pond Snails<br />

(Lymnaea stagnalis)<br />

Host <strong>for</strong> Swimmer’s Itch<br />

(schistosome cercarial dermatitis)<br />

Trematode Parasite (Trichobilharzia ocellata)


USFWS North Shore<br />

Water Fowl Production Area<br />

Constructed Dynamic Gravel Beaches<br />

Dampened Wave Action<br />

<strong>Flowering</strong> <strong>Rush</strong> Now Filling In Wetland


Obvious Negative Impacts<br />

•Displacement of Native <strong>Plant</strong> Communities<br />

•Formation of Monotypic Vegetation<br />

•Loss of Open Water Recreation<br />

•Irrigation Impediment<br />

Higher Level Impacts Have Not Been Assessed<br />

•Increases in Water Temperatures<br />

•Nutrient Releases<br />

•Sediment Transport & Deposition<br />

•Food Chain Alterations / Native Fisheries


Infesting<br />

Previously Unvegetated Littoral Zones<br />

Will Induce<br />

Trophic & Ecosystem Cascades


Uni<strong>for</strong>m Infestations Lack Structural Diversity <strong>for</strong> Support of Multiple Species<br />

Underwater View<br />

(c) BASF Corporation.<br />

Photo by Mitch Kezar


Macrophytes Increase Water Temperatures<br />

Northern Pike Spawning<br />

Over Vegetation Beds<br />

Cooper 2008


Macrophyte Nutrient Releases<br />

Triggers Algae Blooms<br />

Van Eeckhout and Quade1994; James et. al. 2003


Accretion of Sediments


Sediment Transport & Deposition (Lotic & Lentic)


Vegetated vs. Open Water<br />

Littoral Zone


These Introduced Piscivorous Fish<br />

Are Adapted to Vegetated Habitats<br />

(Dibble et al 1997)<br />

Native Salmonids Are Open Water Species


Occluded Mouth of Dayton Creek<br />

Historic Spawning Habitat For<br />

Adfluvial Cutthroats


Spatial Model:<br />

SPOT/10’ Lakebed<br />

on<br />

NAIP/Land<br />

Dayton Creek Delta<br />

Bright Red is<br />

<strong>Flowering</strong> rush


Schultz 2006<br />

Yellow Perch Prefer<br />

<strong>Flowering</strong> <strong>Rush</strong><br />

coontail flowering rush cattail bulrush<br />

Black Bullhead<br />

Yellow Perch


Native Cutthroat<br />

Native Bull Trout<br />

Cautionary Hypotheses<br />

Introduced Yellow Perch Yellow Perch Eggs on Vegetation<br />

Gregory & Powels 1985<br />

Introduced Lake Trout


Native Cutthroat<br />

Native Bull Trout<br />

Lake Trout Expand as Perch Prey Base Habitat Increases<br />

Magnifying Incidental Predation on Native Salmonids?<br />

Introduced Yellow Perch Yellow Perch Eggs on Vegetation<br />

Gregory & Powels 1985<br />

Introduced Lake Trout


Bass Predation of Salmonids<br />

Tabor 1993, Fritts & Peasrsons 2004, Bonar et al. 2005


Bass Predation of Salmonids<br />

Tabor 1993, Fritts & Peasrsons 2004, Bonar et al. 2005


Northern Pike Spawning in Macrophyte Beds<br />

(Macrophytes Increase Water Temperatures &<br />

Reduce Predation of Northern Pike Eggs & Juveniles)<br />

Cooper 2008


Montana Fish, Wildlife &<br />

Parks<br />

Radio Tag Study<br />

of<br />

Northern Pike Distribution<br />

in the<br />

Upper Flathead River


<strong>Flowering</strong><br />

<strong>Rush</strong><br />

Dominates<br />

Sloughs Being<br />

Used by<br />

Northern Pike<br />

Fennon Slough<br />

Mill Creek Slough


Northern Pike Predation of Salmonids<br />

McMahon & Bennett 1996


Northern Pike Bioenergetics Study<br />

Bull Trout** & Cutthroats* Are<br />

Being Significantly Depredated<br />

by Northern Pike<br />

Prey items<br />

Season WCT* BULL**<br />

Winter 686 380<br />

Spring 2,015 2,922<br />

Summer 9,428 0<br />

Fall 1,250 156<br />

Totals 13,379 3,457<br />

Muhlfeld et al. (2008)


Traditional Obstacles to Salmonid Restoration<br />

4H’S:<br />

Harvest, Hatcheries,<br />

Hydrosystem, and Habitat alteration


Spatial Modeling Suggests<br />

Lake Littoral Zones<br />

Will Be Converted to<br />

Northern Pike Habitat


4H’S: harvest, hatcheries, the hydrosystem,<br />

and habitat alteration<br />

& PREDATION by PISCIVOROUS EXOTICS<br />

Sanderson et al 2009<br />

Muhlfeld et al 2008


<strong>Flowering</strong> <strong>Rush</strong> Rhizome Dispersal<br />

May Convert 8.8% of Flathead Lake to Densely Vegetated Habitat


CLASS SUSCEPTIBILTY ACRES<br />

0-10’ DEPTH 5,823<br />

Organic Extreme 544<br />

Silt High 3,062<br />

Vegetation High 101<br />

Saturated Soil/Water High? 657<br />

Sand Medium to Low? 972<br />

Cobble/Gravel Low 489<br />

10-20’ DEPTH Varied est. 8,735<br />

WETLANDS Medium 1,536<br />

Results From Spatial Modeling of Lakebed Sediments & <strong>Flowering</strong> <strong>Rush</strong> Distribution


Initial Result<br />

Spatial Modeling<br />

Habitat<br />

Size<br />

Acres<br />

Current Susceptible<br />

Infested*<br />

Acres<br />

Maximum<br />

Acres<br />

% of<br />

Lake<br />

0-10’ Littoral 5,823 >1,039 4,364 3.5<br />

10-20’ Littoral 8,375 ?>1,000 6,546 5.3<br />

14,558 ?>2,039 10,910 8.8<br />

% Current & Susceptible >14 75<br />

Wetlands 1,536 100 ? 1,536<br />

*dense infestations with high cover value<br />

NAIP Spatial Model <strong>for</strong> East Bay


Current Project Objectives<br />

Salish Kootenai College, Salish & Kootenai Tribes, University of Montana<br />

•Mapping Flathead Lake<br />

•Spatial modeling to predict spread and in<strong>for</strong>m<br />

management decisions (Flathead Lake)<br />

•Phenology in relation to management options<br />

•Herbicide and hand digging trials<br />

•Karyotyping various CRB infestations<br />

•In<strong>for</strong>ming Columbia River system managers<br />

of threat


Where to Go Next?<br />

• Northwest Power & Conservation Council has<br />

regional scale interest in the integrity of the<br />

Columbia River System<br />

• Submit a New System-Wide Proposal<br />

• Four NW States as Partners:<br />

• Agencies, Tribes, Universities<br />

• Salish Kootenai College & CS&K Tribes Lead


Northwest Power & Conservation Council<br />

Fish & Wildlife Program<br />

New System-Wide Proposal Rationle<br />

• 31 Dams on the Columbia River<br />

System<br />

•Fast Flow Through System<br />

Was Converted to Extensive<br />

Impounded Littoral Zones<br />

Suitable <strong>for</strong> Macrophytes<br />

• 6.7 Million Acres Irrigated from<br />

Columbia R.<br />

• Native Salmonid Restoration &<br />

Maintenance a Programmatic Goal


System-Wide / Multi-Partner<br />

Comprehensive Scientific Assessment<br />

• Main Stem Survey<br />

• Water Level <strong>Management</strong> &<br />

Invasion Success<br />

• Reproductive Phenology &<br />

Rhizome/Seed Dispersal<br />

• Higher Trophic Level Impacts<br />

• Sediment Deposition &<br />

Transport<br />

• Control Methods<br />

• Professional Awareness<br />

• Strategic Plan <strong>for</strong> CRB


Still a Early Detection Rapid Response Opportunity<br />

Flathead Lake<br />

L. Pend Oreille<br />

• Flathead Lake<br />

~2,000 ac<br />

• Thompson Falls<br />

~28 ac (12.5% FoO)<br />

• Noxon<br />

~46 ac (0.6% FoO)<br />

• Cabinet<br />

Present (


: Columbia River System<br />

<strong>Flowering</strong> rush<br />

Eurasian watermilfoil


Questions & Comments?<br />

<strong>Flowering</strong> rush Photos by Alvin Mitchell & Dave Boldt SKC, Sue Ball CSKT, Steve Howser Aberdeen ID,<br />

Peter Rice UM, Chris Eckert Queens University, Gary Fewless University of Wisconsin, Mike Kezar BASF

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