phalaris arundinacea control and riparian restoration within
TRANSCRIPT
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Phalaris arundinacea Control and Riparian Restoration Within Agricultural
Watercourses in King County, Washington
Lizbeth Seebacher
University of Washington
Botanic Gardens
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Project DescriptionProject Description
Main goals of the project:Main goals of the project:
Investigate ways to avoid or minimize agricultural Investigate ways to avoid or minimize agricultural maintenance related impacts on maintenance related impacts on salmonidsalmonid habitat.habitat.
Determine the effects of agricultural watercourse Determine the effects of agricultural watercourse maintenance projects on riparian vegetation, inmaintenance projects on riparian vegetation, in--stream erosion, fish habitat, and water quality.stream erosion, fish habitat, and water quality.
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Individual research projects included: Individual research projects included:
Water Quality (DO and temperature differences Water Quality (DO and temperature differences between vegetation types)between vegetation types)Sediment/Erosion Control (first flush, erosion control Sediment/Erosion Control (first flush, erosion control techniques)techniques)LWD (can LWD create hydraulic diversity in these LWD (can LWD create hydraulic diversity in these systems?)systems?)Riparian Vegetation (RCG control techniques)Riparian Vegetation (RCG control techniques)Fish Biology (utilization of these watercourses, Fish Biology (utilization of these watercourses, stomach contents)stomach contents)MacroinvertebrateMacroinvertebrate communities (differences between communities (differences between vegetation types?)vegetation types?)
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Phalaris arundinacea (reed canarygrass) History
Description – clonal C3 grass, long-lived perennial, up to 2.2m tall, highly rhizomatous….
Distributed throughout northern temperate regions
Hybrid of a native genotype and an introduced cultivar.
Why was it introduced?Agronomy, hay and pasture crop, especially on boggy land
Reclaim marshes and wetlands for cattle
Erosion control along drainage canals
Controlling weeds!
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Problems caused by reed canarygrass
Produces dense monocultures, altering habitat diversity and structure
Out-competes native species, reducing biodiversity
Excessive above and below ground biomass
Alters hydrology, impacting fish utilization and invertebrate assemblages
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Methods of controlCard board, black plastic and other weed fabricsMulch, alone or on top of fabricsShading Mowing, tilling and grazingBurning HerbicideFloodingMicro and macronutrient manipulationCompetition by nativesor other non-indegenousspecies
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Dredging and hydroseeding
2 years later
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Weed fabric with planted willow, red osier dogwood and oceanspray
2 years later
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Mowing, cardboard and mulch
After just one season
Mowing and willow stakes
After one year
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Why these methods have generally not been successful…
Reed canarygrass (RCG) possesses:
Substantial carbohydrate storage within the rhizomes, gives new culms the ability to push up lighter weight weed fabrics
Ability to return very early in season
Competitive pattern of above ground and below ground parts
Excessive above and below ground biomass
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Bred to be drought tolerant, therefore, not only blankets riparian areas, but moves into nearby fields, etc.
Tolerates inundationClonal species, transfer photosynthates to
portions of clone under shaded conditionsMorphology plasticityProlific seed producer, seed viability rate
determined to be ~98%
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Objectives
The objectives of the riparian vegetation enhancement section of this project include:
a) finding a BMP protocol for the effective control of reed canary grass, and
b) determining a method for providing native ground cover and woody riparian vegetation that is vigorous, shade producing and provides habitat for insects that constituteprey for salmonids.
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King County
Agricultural Production
Districts(APD’s)
3 sites located within 2 APD’s
Agriculture siteLivestock siteNatural site
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Agriculture SiteSammamish APDWoodinville, Washington
Pilot project
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Livestock SiteSammamish APDWoodinville/Redmond, Washington
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Natural SiteSnoqualmie APDDuvall, Washington
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Field project methodology and treatment design
ControlHogfuel/RCG Barrier
Hogfuel/willowRCG Barrier
1.5 meters
2.5meters
Mowed RCG
PlantingsBurlap fabricCompost, 25cmBurlap fabric
Mowed RCG
Willow stakesBurlap fabricHogfuel, 25cmBurlap fabric
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What the “RCG barrier” and hogfueltreatments will provide:
Heavy, dense material on top of mowed reed canarygrassAllow for a 3 canopy layer planting scheme for shading of seeds and rhizomesHogfuel is very dense and heavy, potentially allelopathic, and reduces nitrogen
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Questions
1) Will the following treatments negatively affect the re-growth of reed canarygrass?
RCG barrier densely planted with native speciesHog fuel densely planted with Salix sitchensisHog fuel placed on top of RCG and below the RCG barrier
2) Is Scirpus microcarpus an effective competitor with reed canarygrass?
3) How long will the reed canarygrass rhizomes need to be covered with a weed block fabric to deplete the rhizome carbohydrate reserves?
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Planting Scheme for RCG barrier
Scirpus microcarpus(Small-fruited bulrush)
Rubus spectabilis(Salmonberry)
Lonicera involucrata(Black twinberry)
Ribes bracteosum(Stink currant)
Symphoricarpos albus(Common snowberry)
Rubus parviflorus(Thimbleberry)
Cornus stolonifera(Red-osier dogwood)
Salix sitchensis(Sitka willow)
Watercourse
Moving upland
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Agricultural Site - Year 2005
0
200
400
600
800
1000
1200
1400
1600
Control RCG Barrier HF/Willows HF/ RCG Barrier
Treatment
RC
G S
tem
Co
un
tStem Count Results
Two way ANOVA over all sites Treatment * Site interaction p=.043
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Livestock Site - Year 2005
0
100
200
300
400
500
600
Control RCG Barrier HF/Willows HF/ RCG Barrier
Treatment
RC
G S
tem
Co
un
t
Stem Count Results
Treatment * Site interaction p=.043Two way ANOVA over all sites
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Natural Site - Year 2005
0
200
400
600
800
1000
1200
1400
Control RCG Barrier HF/Willows HF/ RCG Barrier
Treatment
RC
G S
tem
Co
un
tStem Count Results
Two way ANOVA over all sites Treatment * Site interaction p=.043
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Agriculture Site VegetationPercent Cover
Salix sitchensis
Rubus spectabilis
Scirpus m icrocarpus
Lonicera involucrata
Ribes bracteosum
Sym phoricarpus albus
Rubus parviflorus
Cornus stolonifera
Phalaris arundinacea
Bare ground
Hogfuel/RCG Barrier treatmentAverage of 3 replicates / 6 quadratsclosest to the watercourse
Twinberry RCG
Salmonberry
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Livestock Site VegetationPercent Cover
Salix sitchensis
Rubus spectabilis
Scirpus m icrocarpus
Lonicera involucrata
Ribes bracteosum
Sym phoricarpus albus
Rubus parviflorus
Cornus stolonifera
Phalaris arundinacea
Bare ground
Hogfuel/RCG Barrier treatmentAverage of 3 replicates / 6 quadratsclosest to the watercourse
Small fruited bulrush
SalmonberryRCG
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Hogfuel/RCG Barrier treatmentAverage of 3 replicates
Natural Site VegetationPercent Cover
Salix sitchensis
Rubus spectabilis
Scirpus m icrocarpus
Lonicera involucrata
Ribes bracteosum
Sym phoricarpus albus
Rubus parviflorus
Cornus stolonifera
Phalaris arundinacea
Bare ground
TwinberryRCG
Willow
SnowberryThimbleberry
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RCG and SFB at 22 Weeks
HSM/HN LSM/LN
HSMLN
RCG/RCG
HSMLN
SFB/RCG
HSMHN
RCG/RCG
HSMHN
SFB/RCG
LSMLN
RCG/RCG
LSMHN
RCG/RCG
LSMLN
SFB/RCG
LSMHN
SFB/RCG
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LSM = Low Soil MoistureHSM = High Soil MoistureLN = Low NitrogenHN = High Nitrogen
R = RCG vs. RCGS = RCG vs. SFB
RCG Dry Weight
0
10
20
30
40
50
R/LSMLN
S/LSMLN
R/HSMLN
S/HSMLN
R/LSMHN
S/LSMHN
R/HSMHN
S/HSMHN
Treatment
gra
ms
Moisture * Nitrogen interaction p=.002
Three way ANOVA
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0
5
10
15
20
25
gram s
R/LSMLN
R/LSMHN
R/HSMLN
R/HSMHN
S/LSMLN
S/LSMHN
S/HSMLN
S/HSMHN
T reatm ent
RCG Dry Weight
Above
Below
LSM = Low Soil MoistureHSM = High Soil MoistureLN = Low NitrogenHN = High Nitrogen
Allocation of Resources
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LSM = Low Soil MoistureHSM = High Soil MoistureLN = Low NitrogenHN = High Nitrogen
0
5
10
15
20
25
grams
LSM LN LSM HN HSM LN HSM HN
Treatment
Scirpus microcarpus dry weight
above
below
Allocation of Resources
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Multiple canopy layersRecommended species –
Scirpus microcarpus, Rubus spectabilis, Lonicera involucrata, Salix sitchensis, Cornus stolonifera, Rubus parviflorus
If using willow stakes alone, try additional species, not just willow sp. (willow borer)
Thicker fabric in place of burlap (jute)Place hogfuel when possible
Conclusions / Recommendations
Willow borer
Cryptorhynchuslapathi
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Acknowledgements
Committee members – Major advisor - Dr. Sarah Reichard, practicality advisor – Dr. Kern Ewing, financial advisor -Dr. Brad Gaolach, Dr. Liz Van Volkenburg and GSR - Dr. Martha Groom
Funding source - King County Department of Natural Resources and Parks, Water and Land Resources Division
Landowners – Tom Quigley and Olympic Nursery staff, Dave Olney, Claire Thomas
Numerous field assistants – Doug Schmidt, Jennifer Brennan, Andrea Holmes, Kate Cueno…
Students and staff at the UWBG
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MethodsRandomized block design, with 3 treatments (plus control) within 3 blocks (or replicates) chosen randomly at each of the 3 sites.
Reed canarygrass mowed, rhizome barrier placed around 1.5x2.5 meter plots.
Three treatments applied at each site.
The stems of any returning RCG counted and recorded biweekly during the growing season.
Data Analysis conducted utilizing a one way ANOVA.
Percent cover of vegetation recordedat the end of the second growing season to determine survival andcompetitive efficacy of planted nativespecies with RCG.
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Competition study
Bare-root RCG and small fruited bulrush (SFB) of similar size # of nodes will collected. Above ground biomass clipped at 10cm, and weighed.
12 RCG and 4 SFB randomly chosen, planted in 2 gallon pots and placed in the greenhouse at UWBG for 22 weeks.
Treatments - competition (RCG vs. SFB), high and low soil moisture, high and low nitrogen
Watered and fertilized (NH4 NO3) weekly
RCG and SFB harvested, washed, determined dry weight of above & below biomass of RCG and sample of SFB
Analyzed utilizing a 3 way ANOVA.
HSMLN
RCG/RCG
HSMLN
SFB/RCG
HSMHN
RCG/RCG
HSMHN
SFB/RCG
LSMLN
RCG/RCG
LSMHN
RCG/RCG
LSMLN
SFB/RCG
LSMHN
SFB/RCG