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Tamarisk Control
on the Colorado River
Justin Beckett, Connor Lambert, Jesse Morris, & Brandon White
Background
A shrub like tree
scale-like leaves
deciduous foliage
spreads by seed and
adventitious roots
grows along riparian
areas
Background
Native across Europe and Asia
Introduced in the 1800’s for shade, windbreak,
ornamental
Escaped cultivation
Primarily occurs in the Southwest US
became a dominant species along the
Colorado River in 1963
Why Control it?
Competitive advantages include:
can use unsaturated soil water
high transpiration rates
alters soil salinity
can tolerate an extreme range of conditions
Forms monocultures
Displaces native vegetation
changes wildlife habitat
General Goals and Objectives
Restore riparian areas
Improve ecological
function
Improve wildlife habitat
Increase water yield
Specific Goals and Objectives
Reduce Tamarisk
cover/abundance
Reduce fuel loads
Increase biological
diversity
Increase native species’
cover/richness
Considerations
Time
Reseeding
Soil salinity
Water table
Cost
Environmental Concerns
● unfortunately, salt cedar infests
riparian areas- habitat that is very
sensitive and vulnerable
Treatments Overview
-Herbicide
-Mechanical
-Biological
-Fire
Herbicide: 3 Methods
Method 1: Broadcast
Method 2: Cutting
Method 3: Plowing
Image Courtesy of www.tractorbuynet.com
Herbicides
triclopyr- low toxicity to most animals- but may
affect ducks, quails, trout
tebuthiuron- may contaminate groundwater, kill
fish
hexazinone- contaminates groundwater, non-
selective
imazapyr- soil active, non-selective
Mechanical
-Cutting
-Shredding
-Chaining
-Discing
-Mowing
Problem:
Tamarisk sprouts
back, so if done alone
mechanical
treatments are not
very effective.
Fire
-Clears the ground,
reduces fuels and
competition
-Induces tamarisk
sprouting
Photo Courtesy of www.fs.fed.us
Mechanical & Fire
Most mechanical treatments still
requires burning/herbicide
Burning- all problems usually
associated with it- may be harder
to burn in wetter areas
erosion!
Rapid changes to aquatic
ecosystems
The Bea[e]tles!!
The northern tamarisk beetle-
unknown if any negative ecological
effects
can be very successful
•Stage 1: Egg
•Stage 2: Larvae
•Stage 3: Pupa (on the ground)
•Stage 4: Immerge as adults
•Stage 5: Diapause
So bad… it’s good?
Tamarisk has taken over areas in the Grand
Canyon so extensively, it is prime nesting
habitat
the tamarisk beetle has defoliated and killed
acres upon acres
Southwestern Willow Flycatcher
Endangered Species Act- the greater good?
has tamarisk become habitat for other species?
The Plan
-Integrated Pest Management Plan:
1. In the early spring, broadcast triclopyr
2. Allow the herbicide time to work its way into the soil, where it is active and
begin weakening the trees.
3. After a week, release Diorhabda beetles throughout the site, and allow them
to proliferate and weaken the tamarisk trees over time. May take up to four
years to kill trees.
4. Monitor growth, density, water and soil quality
5. Follow up with spot treatments of herbicide as needed
Sources
Tamarisk Removal in Grand Canyon National Park: Changing the Native–Non-native Relationship as
a Restoration Goal
Belote, R. Travis; Makarick, Lori J; Kearsley, Michael J. C; Lauver, Chris L
Ecological Restoration, 2010, Vol.28(4), pp.449-459, 2010
Vegetation Response Following Invasive Tamarisk ( Tamarix spp.) Removal and Implications for
Riparian Restoration
Harms, Rebecca S.; Hiebert, Ron D.
Restoration Ecology, 2006, Vol.14(3), pp.461-472, 2006
Ecological strategies for managing tamarisk on the C.M. Russell National Wildlife Refuge, Montana,
USA
Lesica, Peter; Miles, Scott
Biological Conservation, 2004, Vol.119(4), pp.535-543, 2004
Planning Riparian Restoration in the Context of Tamarix Control in Western North America
Shafroth, Patrick B.; Beauchamp, Vanessa B.; Briggs, Mark K.; Lair, Kenneth; Scott, Michael L.; Sher,
Anna A.
Restoration Ecology, 2008, Vol.16(1), pp.97-112, 2008
http://www.gcrg.org/docs/gtslib/Tamarisk-Leaf-Beetle-Life-Cycle.pdf
Bean D.W. et al. DJ, Kazmer, K. Gardner, D.C. Thompson, B. Reynolds, J.C. keller, J.F. Gaskin. Molecular Genetic
and Hybridization Studies of Diorhabda spp. Released for Biological Control of Tamarix. Invasive Plant Science and Management:
January-March, Vol. 6, No. 1, pp. 1-15.
Acharya, K. , S. Sueki ,B. Conrad , T L. Dudley , D W. Bean ,J. C. Osterberg . Life History Characteristics of
Diorhabda Carinulata Under Various Temperatures. Environmental Entemology 2013 42: 564- 571.
http://www.discovermoab.com/tamarisk.htm
http://www.tucson.ars.ag.gov/unit/publications/PDFfiles/827.pdf

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Tamarisk

  • 1. Tamarisk Control on the Colorado River Justin Beckett, Connor Lambert, Jesse Morris, & Brandon White
  • 2. Background A shrub like tree scale-like leaves deciduous foliage spreads by seed and adventitious roots grows along riparian areas
  • 3. Background Native across Europe and Asia Introduced in the 1800’s for shade, windbreak, ornamental Escaped cultivation Primarily occurs in the Southwest US became a dominant species along the Colorado River in 1963
  • 4.
  • 5. Why Control it? Competitive advantages include: can use unsaturated soil water high transpiration rates alters soil salinity can tolerate an extreme range of conditions
  • 6. Forms monocultures Displaces native vegetation changes wildlife habitat
  • 7. General Goals and Objectives Restore riparian areas Improve ecological function Improve wildlife habitat Increase water yield
  • 8. Specific Goals and Objectives Reduce Tamarisk cover/abundance Reduce fuel loads Increase biological diversity Increase native species’ cover/richness
  • 10. Environmental Concerns ● unfortunately, salt cedar infests riparian areas- habitat that is very sensitive and vulnerable
  • 12. Herbicide: 3 Methods Method 1: Broadcast Method 2: Cutting Method 3: Plowing Image Courtesy of www.tractorbuynet.com
  • 13. Herbicides triclopyr- low toxicity to most animals- but may affect ducks, quails, trout tebuthiuron- may contaminate groundwater, kill fish hexazinone- contaminates groundwater, non- selective imazapyr- soil active, non-selective
  • 14. Mechanical -Cutting -Shredding -Chaining -Discing -Mowing Problem: Tamarisk sprouts back, so if done alone mechanical treatments are not very effective.
  • 15. Fire -Clears the ground, reduces fuels and competition -Induces tamarisk sprouting Photo Courtesy of www.fs.fed.us
  • 16. Mechanical & Fire Most mechanical treatments still requires burning/herbicide Burning- all problems usually associated with it- may be harder to burn in wetter areas erosion! Rapid changes to aquatic ecosystems
  • 17. The Bea[e]tles!! The northern tamarisk beetle- unknown if any negative ecological effects can be very successful •Stage 1: Egg •Stage 2: Larvae •Stage 3: Pupa (on the ground) •Stage 4: Immerge as adults •Stage 5: Diapause
  • 18. So bad… it’s good? Tamarisk has taken over areas in the Grand Canyon so extensively, it is prime nesting habitat the tamarisk beetle has defoliated and killed acres upon acres Southwestern Willow Flycatcher Endangered Species Act- the greater good? has tamarisk become habitat for other species?
  • 19. The Plan -Integrated Pest Management Plan: 1. In the early spring, broadcast triclopyr 2. Allow the herbicide time to work its way into the soil, where it is active and begin weakening the trees. 3. After a week, release Diorhabda beetles throughout the site, and allow them to proliferate and weaken the tamarisk trees over time. May take up to four years to kill trees. 4. Monitor growth, density, water and soil quality 5. Follow up with spot treatments of herbicide as needed
  • 20. Sources Tamarisk Removal in Grand Canyon National Park: Changing the Native–Non-native Relationship as a Restoration Goal Belote, R. Travis; Makarick, Lori J; Kearsley, Michael J. C; Lauver, Chris L Ecological Restoration, 2010, Vol.28(4), pp.449-459, 2010 Vegetation Response Following Invasive Tamarisk ( Tamarix spp.) Removal and Implications for Riparian Restoration Harms, Rebecca S.; Hiebert, Ron D. Restoration Ecology, 2006, Vol.14(3), pp.461-472, 2006 Ecological strategies for managing tamarisk on the C.M. Russell National Wildlife Refuge, Montana, USA Lesica, Peter; Miles, Scott Biological Conservation, 2004, Vol.119(4), pp.535-543, 2004
  • 21. Planning Riparian Restoration in the Context of Tamarix Control in Western North America Shafroth, Patrick B.; Beauchamp, Vanessa B.; Briggs, Mark K.; Lair, Kenneth; Scott, Michael L.; Sher, Anna A. Restoration Ecology, 2008, Vol.16(1), pp.97-112, 2008 http://www.gcrg.org/docs/gtslib/Tamarisk-Leaf-Beetle-Life-Cycle.pdf Bean D.W. et al. DJ, Kazmer, K. Gardner, D.C. Thompson, B. Reynolds, J.C. keller, J.F. Gaskin. Molecular Genetic and Hybridization Studies of Diorhabda spp. Released for Biological Control of Tamarix. Invasive Plant Science and Management: January-March, Vol. 6, No. 1, pp. 1-15. Acharya, K. , S. Sueki ,B. Conrad , T L. Dudley , D W. Bean ,J. C. Osterberg . Life History Characteristics of Diorhabda Carinulata Under Various Temperatures. Environmental Entemology 2013 42: 564- 571. http://www.discovermoab.com/tamarisk.htm http://www.tucson.ars.ag.gov/unit/publications/PDFfiles/827.pdf

Editor's Notes

  1. Justin
  2. Connor http://extension.usu.edu/files/publications/publication/AG_Weeds_2006-01.pdf
  3. http://www.tucson.ars.ag.gov/unit/publications/PDFfiles/827.pdf