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Ryan M. Wersal, Ph.D.
                Mississippi State University
               Geosystems Research Institute

Missouri Department of Conservation Invasive Plant Workshop
Powder Valley Nature Center, Kirkwood, MO May 16th and 17th
Benefits of Aquatic Plants
 Stabilize lake sediments, reduce
  resuspension

 Increase sedimentation, reduce
  turbidity

 Provide habitat for insects, forage
  fish, fish spawning and YOY fish

 Provide food for waterfowl, other
  animals
Non-native vs. Native Community
 Myriophyllum spicatum    Vallisneria americana
  Eurasian watermilfoil        Water celery
Canopy Structure
Alligatorweed
                     (Alternanthera philoxeroides)
 Emergent perennial native to South America (Vogt et al. 1979)

 Nuisance aquatic species in over 32 countries worldwide
  (Gunasekera and Bonila 2001)


 Major problem in Southern U.S. aquatic and riparian areas
  (Kay and Haller 1982)


 Hollow stems form extensive, dense mats on water surface
  (Kay and Haller 1982)


 Impedes boat traffic, increases flood risk, clogs irrigation
  canals, harbors pathogen-carrying insects, reduces overall
  water quality and property value (Madsen 2004)
Alligatorweed distribution in the
United States by Hydrologic Units
Alligatorweed distribution in the MidSouth Region
Alligatorweed Habitat
 Nuisance in subtropical
  aquatic and wetland areas,
  can be rooted in submersed
  to moist soil, especially ditch
  and stream habitats, forms
  floating mats
   Major problem in the Ross
    Barnett Reservoir and MS
    Delta
   Potentially has two biotypes    Ross Barnett Reservoir, MS
Alligatorweed ID
 Non-native emergent perennial
  plant

 Emergent or submersed

 Stems form a tangled mass

 Leaves simple and opposite on
  stems

 Leaves elliptical

 Typically glabrous (very little if
  any hair)
Alligatorweed ID
 Several-flowered whitish
  head

 Flowers borne in leaf axils

 Flowers always on stalks up
  to 2 inches in length

 Mature seeds not known to
  occur

 Spread via vegetative growth
  and fragmentation
Alligatorweed ID
 Key identifying characteristic:
    Stems almost always hollow
Can Be Confused With:
 Sessile joyweed (Alternanthera sessilis)
    Not widespread

 Ludwigia spp.
                                             StarrImages




                                                      Kim Starr
Ecological Impacts
 Degradation of water quality

 Reduction in species diversity

 Suppresses native plant species

 Potential impacts on endangered
  species

 Alters animal communities
Lake Jackson, MS        Blue Lake, MS




Little Eagle Lake, MS   Blue Lake, MS
Human Use Impacts
 Reduces access to water

 Reduces property values

 Limits recreation

 Impedes navigation

 Increases flood duration
  & intensity
                             Lake Jackson, MS
 Human health                 Alligatorweed
Management Options
 Biological

 Chemical

 Mechanical

 Physical

 Institutional
Alligatorweed Management
Biological
  Alligatorweed flea beetle
  Stem borer moth


Chemical
  2,4-D, triclopyr, imazapyr,
  glyphosate

Mechanical - None

Physical - None
Biological Control
 Alligatorweed flea beetle
  (Agasicles hygrophila)

 Works well south of
  Vicksburg-Jackson-
  Montgomery (I-20
  corridor)
Biological Control
 Stem borer moth (Vogtia malloi)

 Active throughout MS

 May be more of an option for
  Missouri than flea beetle due to   (Photograph courtesy USDA, ARS by Willey C. Durden.)



  climate
 Typically not present near
  agricultural areas where
  insecticides are used

                                                       (Photograph courtesy USDA, ARS)
Small Scale Trials
 Imazapyr, triclopyr, glyphosate (DIA salt and IPA salt),
  imazamox, 2,4-D, diquat (maximum label rate), and
  penoxsulam (maximum label rate) offered similar effective
  control for 12 weeks

 Carfentrazone and diquat provided rapid biomass
  reduction but regrowth began within days after
  application
Field Control
 Imazapyr, 1 to 4 pints/acre
 Triclopyr, 3 to 8 quarts/acre
 2,4-D, 2 quarts/acre
 Glyphosate, 2 quarts/acre
 Non-ionic surfactant, 1 pint/acre
 In Mississippi, 2,4-D and glyphosate are being used
 alone or as a tank mix

Always read the herbicide label
Hobbs and Humphries 1995. Conserv. Biol. 9:761-770.
Other Resources
UNIVERSITY                                     PROFESSIONAL SOCIETY
Center for Aquatic and Invasive Plants         Aquatic Plant Management Society
   aquat1.ifas.ufl.edu                            www.apms.org
Mississippi State University GRI               North American Lake Management Society
   www.gri.msstate.edu                            www.nalms.org
MSU Extension Service                          GOVERNMENT
   msucares.com/pubs/publications/p1532aquat   Aquatic Plant Control Research Program
   ic.pdf                                         www.wes.army.mil/el/aqua/aqua.html
                                               USGS Aquatic Nonindigenous Species Site
FOUNDATION                                        nas.er.usgs.gov
Aquatic Ecosystem Restoration Foundation
   www.aquatics.org
Ryan Wersal, Ph.D.
Geosystems Research Institute
Box 9652
Mississippi State, MS 39762
Ph (662) 325-4595
Fax (662) 325-7692
rwersal@gri.msstate.edu

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Alligatorweed Biology Ecology and Management

  • 1. Ryan M. Wersal, Ph.D. Mississippi State University Geosystems Research Institute Missouri Department of Conservation Invasive Plant Workshop Powder Valley Nature Center, Kirkwood, MO May 16th and 17th
  • 2. Benefits of Aquatic Plants  Stabilize lake sediments, reduce resuspension  Increase sedimentation, reduce turbidity  Provide habitat for insects, forage fish, fish spawning and YOY fish  Provide food for waterfowl, other animals
  • 3. Non-native vs. Native Community Myriophyllum spicatum Vallisneria americana Eurasian watermilfoil Water celery
  • 5.
  • 6.
  • 7. Alligatorweed (Alternanthera philoxeroides)  Emergent perennial native to South America (Vogt et al. 1979)  Nuisance aquatic species in over 32 countries worldwide (Gunasekera and Bonila 2001)  Major problem in Southern U.S. aquatic and riparian areas (Kay and Haller 1982)  Hollow stems form extensive, dense mats on water surface (Kay and Haller 1982)  Impedes boat traffic, increases flood risk, clogs irrigation canals, harbors pathogen-carrying insects, reduces overall water quality and property value (Madsen 2004)
  • 8. Alligatorweed distribution in the United States by Hydrologic Units
  • 9. Alligatorweed distribution in the MidSouth Region
  • 10. Alligatorweed Habitat  Nuisance in subtropical aquatic and wetland areas, can be rooted in submersed to moist soil, especially ditch and stream habitats, forms floating mats  Major problem in the Ross Barnett Reservoir and MS Delta  Potentially has two biotypes Ross Barnett Reservoir, MS
  • 11. Alligatorweed ID  Non-native emergent perennial plant  Emergent or submersed  Stems form a tangled mass  Leaves simple and opposite on stems  Leaves elliptical  Typically glabrous (very little if any hair)
  • 12. Alligatorweed ID  Several-flowered whitish head  Flowers borne in leaf axils  Flowers always on stalks up to 2 inches in length  Mature seeds not known to occur  Spread via vegetative growth and fragmentation
  • 13. Alligatorweed ID  Key identifying characteristic:  Stems almost always hollow
  • 14. Can Be Confused With:  Sessile joyweed (Alternanthera sessilis)  Not widespread  Ludwigia spp. StarrImages Kim Starr
  • 15. Ecological Impacts  Degradation of water quality  Reduction in species diversity  Suppresses native plant species  Potential impacts on endangered species  Alters animal communities
  • 16. Lake Jackson, MS Blue Lake, MS Little Eagle Lake, MS Blue Lake, MS
  • 17. Human Use Impacts  Reduces access to water  Reduces property values  Limits recreation  Impedes navigation  Increases flood duration & intensity Lake Jackson, MS  Human health Alligatorweed
  • 18. Management Options  Biological  Chemical  Mechanical  Physical  Institutional
  • 19. Alligatorweed Management Biological Alligatorweed flea beetle Stem borer moth Chemical 2,4-D, triclopyr, imazapyr, glyphosate Mechanical - None Physical - None
  • 20. Biological Control  Alligatorweed flea beetle (Agasicles hygrophila)  Works well south of Vicksburg-Jackson- Montgomery (I-20 corridor)
  • 21. Biological Control  Stem borer moth (Vogtia malloi)  Active throughout MS  May be more of an option for Missouri than flea beetle due to (Photograph courtesy USDA, ARS by Willey C. Durden.) climate  Typically not present near agricultural areas where insecticides are used (Photograph courtesy USDA, ARS)
  • 22. Small Scale Trials  Imazapyr, triclopyr, glyphosate (DIA salt and IPA salt), imazamox, 2,4-D, diquat (maximum label rate), and penoxsulam (maximum label rate) offered similar effective control for 12 weeks  Carfentrazone and diquat provided rapid biomass reduction but regrowth began within days after application
  • 23. Field Control  Imazapyr, 1 to 4 pints/acre  Triclopyr, 3 to 8 quarts/acre  2,4-D, 2 quarts/acre  Glyphosate, 2 quarts/acre  Non-ionic surfactant, 1 pint/acre  In Mississippi, 2,4-D and glyphosate are being used alone or as a tank mix Always read the herbicide label
  • 24. Hobbs and Humphries 1995. Conserv. Biol. 9:761-770.
  • 25. Other Resources UNIVERSITY PROFESSIONAL SOCIETY Center for Aquatic and Invasive Plants Aquatic Plant Management Society aquat1.ifas.ufl.edu www.apms.org Mississippi State University GRI North American Lake Management Society www.gri.msstate.edu www.nalms.org MSU Extension Service GOVERNMENT msucares.com/pubs/publications/p1532aquat Aquatic Plant Control Research Program ic.pdf www.wes.army.mil/el/aqua/aqua.html USGS Aquatic Nonindigenous Species Site FOUNDATION nas.er.usgs.gov Aquatic Ecosystem Restoration Foundation www.aquatics.org
  • 26. Ryan Wersal, Ph.D. Geosystems Research Institute Box 9652 Mississippi State, MS 39762 Ph (662) 325-4595 Fax (662) 325-7692 rwersal@gri.msstate.edu