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Ecologically Based Management of Salt Cedar K. George Beck Bioag Science & Pest Management Colorado State University
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References Sheley, R.L., T.J. Svejcar, & B.D. Maxwell. 1996. A theoretical framework for developing successional weed management strategies on rangeland. Weed Technology 10:766-773 Sheley, R.L., S. Kedzie-Webb, & B.D. Maxwell. Integrated weed management on rangeland. in R.L. Sheley & J.K. Petroff, eds. Biology & Management of Noxious Rangeland Weeds p 57-68
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Ecologically Based Weed Management Develop strategies based upon current understanding of succession –Recognizes plant communities dynamic –Use technology to enhance natural processes & mechanisms that regulate vegetation change –Direct weed infested communities on trajectory to more desirable community
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Causes of Succession Site availability Differential species availability Differential species performance Successional weed management exploits these causes
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Successional Weed Management Components Mgmt component: –Designed disturbance –Controlled colonization –Controlled species performance Succession cause: –Site availability –Differential species availability –Differential species performance
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Ecological Opportunities for Weed Management Controlled colonization Controlled performance Designed disturbance Undesired plant community Desired plant community Time
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Successional Weed Mgmt: Treatment Examples Designed Disturbance Controlled Colonization Controlled spp Performance
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Biological Control of Salt Cedar Several speakers to address this issue –biocontrol can be controlled colonization and controlled species performance components of successional weed mgmt
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Reference Brock, J.H. 1994. Tamarix spp. (Salt Cedar), an invasive exotic woody plant in arid and semi-arid riparian habitats in western USA. p.27-44 In L.C. de Waal, L.E. Child, P.M. Wade, and J.H. Brock, eds. Ecology and management of invasive riverside plants. John Wiley & sons, West Sussex, England.
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Physical or Mechanical Control Fire: –not effective for controlling salt cedar readily resprouts from crown at rate of 3 to 4 M per year –20 A fire in UT summer 1975 1 year later fire effects observable but with surface of lush green salt cedar regrowth over entire area 1978 salt cedar fully recovered
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Physical or Mechanical Control Fire: –UT research repeat burning during spring, summer, fall for 2 years no effective control because of regrowth from crowns
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Physical or Mechanical Control Shredding, rollerchopping, chaining: –all designed to decrease canopy of target species and ideally decrease plant density fails to do so on salt cedar
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Physical or Mechanical Control Grubbing: –cutting individual plants to a depth of more than 20 cm deep also does not work well on salt cedar regrowth evident following this technique within 6 to 12 months
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Physical or Mechanical Control Root plowing: –using horizontal blade more than 20 cm deep controlled 40% of salt cedar in NM must repeat operations to achieve greater control –In AZ, 1 M long ripper blades set 1 M apart & pulled with D9 crawler kept portion of Salt River nearly free of SC for 10 yr must repeat at about 10 month intervals
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Physical or Mechanical Control Flooding (Inundation): –inundation of established SC 24 to 36 months caused 99% control flooding during growing season –inundation also prevents seedling establishment –established SC withstood root crowns flooded for 98 days total submersion for 70 days
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Reference Duncan, K.W. and K.C. McDaniel. 1998. Saltcedar (Tamarix spp.) management with imazapyr. Weed Technology 12:337-344.
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Chemical Control First chemicals used: –2,4-D, 2,4,5-T, & silvex controlled topgrowth regrowth always occurred –2,4,5-T & silvex banned 1983
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Chemical Control Triclopyr (Garlon 3A): –used to treat individual plants –fairly effective –1.5% solution v/v in 300 gallons total spray solution per acre!! Thorough coverage necessary May best timing, August also good
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Chemical Control Imazapyr (Arsenal): –Treating individual plants: 1% v/v solution in water sprayed to wet,but not to drip –generally 90% control –best control in August or September (99%) –control less when sprayed in April or October an expensive treatment
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Salt Cedar Mortality 1% Solution Arsenal May JunJulAugSepOct Individual plants treated
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Chemical Control Imazapyr (Arsenal) + glyphosate (Roundup or Rodeo) individual plants: –often imazapyr & glyphosate tank-mixed decrease treatment expense –0.5 + 0.5% v/v solution + 0.25% NIS controlled 95% of SC regardless of date of application during growing season –glyphosate at 2% v/v only 32% control
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Chemical Control NMSU guidelines treating individual plants: –young or regrowth SC < 4 M tall easier to trt & better control –trt areas root plowed, mowed, or cleared or where SC starting to invade –trt areas < 160 trees/A –glyphosate+imazapyr 0.5 + 0.5% v/v + 0.25% nis comparable to 1% v/v imazapyr –spray foliage to wet, especially terminal ends of branches –allow 2 full seasons before follow-up trts
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Chemical Control “Broadcast” - carpet roller: –imazapyr + glyphosate 0.125 + 0.125% or imazapyr at 0.125% controlled 85 & 92% of SC 2 YAT mortality dropped to 32% when solution decreased to 0.1 + 0.1% –glyphosate alone 0.5%, 5% mortality –imazapyr alone 0.25%, 94% mortality
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Chemical Control “Broadcast” - carpet roller: –good because only contacts target vegetation understory protected –many plants went untreated decreased with increased operator experience –treat only plants < 3 M tall
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Chemical Control Aerial applications: –NMSU evaluated fixed wing 1993 & 1994; data 2 YAT compared imazapyr at 0.75 lb ai/A to mixtures of imazapyr and glyphosate control ranged from 66% (imazapyr 0.75 lb) to 87% (0.5 + 0.5 lb imazapyr + glyphosate)
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Fixed Wing Treatments Imazapyr & Glyphosate Ima 0.75 I+G 0.25+0.5 I+G 0.38+0.38 I+G 0.38+0.5 I+G 0.5+0.5 Data taken 2 YAT
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Chemical Control Aerial applications: –aircraft fit with conventional raindrop nozzles delivered 7 gpa –when changed to microaire nozzles at 3 gpa control decreased 10 to 15% –Upshot - higher gallonage important for coverage & to penetrate canopy
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Chemical Control Aerial applications: –also found helicopter applications caused highly variable control 31-90% with no apparent rate response –generally taller trees harder to control –trees with higher number of stems harder to control
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Tree Ht & Stem Number Influences Control Stem numbers 1-4; 5-9; 10-19; >20 Tree ht
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Reference Taylor, J.P. and K.C. McDaniel. 1998. Restoration of Saltcedar (Tamarix spp.)-infested floodplains on the Bosque del Apache National Wildlife Refuge. Weed Technology 12:345- 352.
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Ecologically Based SC Mgmt Designed disturbance: –root plowing –pile & burn Controlled colonization: –spot trt SC regrowth imazapyr or imazapyr + glyphosate individual trees experience shows plowing, burning, spray better than spray, chain or burn, spray cost about 1/3 as much –planted many native spp
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Ecologically Based SC Mgmt Controlled species performance: –drip irrigation –ultimately mimic natural flooding by controlled water manipulations while stimulates SC recruitment, experience shows that remains minor component of overall flora
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Summary These are just examples –many treatment combinations that work Always: –know starting composition plant community; –know what composition trying to achieve; –thru designed disturbance, controlled colonization, controlled species performance put succession on trajectory to achieve desirable plant community
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