<str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Third</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Invasive</strong> SpartinaChapter 4: Spartina C<strong>on</strong>trol and Managementglyphosate and crushing <strong>on</strong> firm surfaces extend <str<strong>on</strong>g>the</str<strong>on</strong>g> timeperiod well bey<strong>on</strong>d 10 years. If a more realistic andc<strong>on</strong>servative approach to modeling is used that includesgrowth and seedling inputs, <str<strong>on</strong>g>the</str<strong>on</strong>g>n <strong>on</strong>ly <str<strong>on</strong>g>the</str<strong>on</strong>g> use <str<strong>on</strong>g>of</str<strong>on</strong>g> imazapyrapproaches 100% c<strong>on</strong>trol after four years <str<strong>on</strong>g>of</str<strong>on</strong>g> treatment.Treatment cost per hectare is <strong>on</strong>ly a minor comp<strong>on</strong>ent<str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> total cost <str<strong>on</strong>g>of</str<strong>on</strong>g> a c<strong>on</strong>trol effort. Efficacy governs <str<strong>on</strong>g>the</str<strong>on</strong>g>majority <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> total cost. For example, treating 100 hectares<str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina with imazapyr or glyphosate at 38 kg/ha, wouldcost approximately $60,000/ha and $120,000/ha, respectivelyat current chemical prices. These values change dramaticallywhen <str<strong>on</strong>g>the</str<strong>on</strong>g> modeling results shown in Table 1 are factored in.To c<strong>on</strong>trol 99% <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina using imazapyr, a total <str<strong>on</strong>g>of</str<strong>on</strong>g> 130 hawould need to be treated over four years at a cost <str<strong>on</strong>g>of</str<strong>on</strong>g>approximately $78,000/ha, whereas to achieve that c<strong>on</strong>trolwith glyphosate, a total <str<strong>on</strong>g>of</str<strong>on</strong>g> 208 ha would need to be treatedover seven years at a cost <str<strong>on</strong>g>of</str<strong>on</strong>g> approximately $250,000/ha.DISCUSSIONThe objectives <str<strong>on</strong>g>of</str<strong>on</strong>g> this study were to evaluate <str<strong>on</strong>g>the</str<strong>on</strong>g> Spartinac<strong>on</strong>trol efforts in Willapa Bay and to determine if <str<strong>on</strong>g>the</str<strong>on</strong>g> efficacy<str<strong>on</strong>g>of</str<strong>on</strong>g> those efforts was sufficient to accomplish eradicati<strong>on</strong>.Developing inferences about treatment efficacy based <strong>on</strong>m<strong>on</strong>itoring data from a few sites is problematic. Unlikeresearch plots, <str<strong>on</strong>g>the</str<strong>on</strong>g>se treatment sites lack replicati<strong>on</strong> andcomplete records <strong>on</strong> all <str<strong>on</strong>g>the</str<strong>on</strong>g> envir<strong>on</strong>mental and site c<strong>on</strong>diti<strong>on</strong>s,and in general lack applicati<strong>on</strong> precisi<strong>on</strong>. Traditi<strong>on</strong>al “inhouse”m<strong>on</strong>itoring also lacks objectivity. These c<strong>on</strong>cerns wereminimized within this study by pooling data collected by animpartial party (WSU) across as many similar treatment sitesand times as possible and using a very c<strong>on</strong>servative estimate<str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>trol (percent Spartina-free quadrats). The tremendousvariability across sites found in this m<strong>on</strong>itoring effort is notatypical <str<strong>on</strong>g>of</str<strong>on</strong>g> that found in o<str<strong>on</strong>g>the</str<strong>on</strong>g>r Spartina c<strong>on</strong>trol efforts (Patten2002). Due to <str<strong>on</strong>g>the</str<strong>on</strong>g> lack <str<strong>on</strong>g>of</str<strong>on</strong>g> background data, however, <str<strong>on</strong>g>the</str<strong>on</strong>g>variati<strong>on</strong>s in this study are difficult to account for. Detaileddata collecti<strong>on</strong> <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> variables that affect Spartina c<strong>on</strong>trolefficacy, such as herbicide dry time, tidal c<strong>on</strong>diti<strong>on</strong>s, canopyquality (dirtiness, height, intactness/health, growth stage, andcl<strong>on</strong>al age), spray water quality, and sediment type (Patten2002), are usually not collected by field crews doing <str<strong>on</strong>g>the</str<strong>on</strong>g>c<strong>on</strong>trol work.Several observati<strong>on</strong>s <strong>on</strong> specific treatments should benoted. Tilling, although a superlative method formechanically c<strong>on</strong>trolling Spartina, is costly, requiring anexpensive ($250,000) amphibious tiller and is slow (~0.25ha/hr). It has a limited window during <str<strong>on</strong>g>the</str<strong>on</strong>g> winter when itworks, and unless it is preceded by summer mowing, itresults in massive seedling density <str<strong>on</strong>g>of</str<strong>on</strong>g> more than 200seedlings/m 2 . Crushing is relatively less expensive(~$40,000 to $80,000 for <str<strong>on</strong>g>the</str<strong>on</strong>g> equipment) and is faster (1-2ha/hr) than tilling, but it requires multiple crushing eventsper year. The greatest success in crushing appears to beTable 3. Years to achieve 99% Spartina-free tideland using repeated annualtreatment <str<strong>on</strong>g>of</str<strong>on</strong>g> different c<strong>on</strong>trol practices.TreatmentExtincti<strong>on</strong>coefficient±std. errormean *Calculatedtime toreach 99%Spartinafreetideflat**(years)Amount <str<strong>on</strong>g>of</str<strong>on</strong>g> 100 hameadow Spartinaremaining at <str<strong>on</strong>g>the</str<strong>on</strong>g>start <str<strong>on</strong>g>of</str<strong>on</strong>g> year 5, after 4years <str<strong>on</strong>g>of</str<strong>on</strong>g> treatmentand total amount <str<strong>on</strong>g>of</str<strong>on</strong>g>area treated duringthat time***haremainingtotal hatreatedWinter tilling 0.73±0.03 3.6 1 145Crushing <strong>on</strong>s<str<strong>on</strong>g>of</str<strong>on</strong>g>tsediment0.52±0.14 6.3 11 211Crushing <strong>on</strong>sand or firmsilt sedimentGlyphosate9 kg/haGlyphosate38 kg/haCrushing +glyphosate38 kg/haImazapyr 1.7kg/ha0.26±0.09 15.4 73 3600.31±0.06 12.5 52 3230.57±0.04 5.4 7 1920.59±0.04 5.3 6 1850.82 2.7 0.3 127* Extincti<strong>on</strong> coefficient equals <str<strong>on</strong>g>the</str<strong>on</strong>g> mean % Spartina-free quadrats for <str<strong>on</strong>g>the</str<strong>on</strong>g>given treatment.** Assumes that treatment is repeated annually, that <str<strong>on</strong>g>the</str<strong>on</strong>g> equati<strong>on</strong> log0.01/log (1- extincti<strong>on</strong> coefficient) approximates <str<strong>on</strong>g>the</str<strong>on</strong>g> system’s resp<strong>on</strong>se,and that <str<strong>on</strong>g>the</str<strong>on</strong>g>re are no inputs from spread and seedlings.*** Discrete time, logistic growth model, with growth rate parameter0.15, carrying capacity 100 ha and additi<strong>on</strong>al seedling input from outsidesources equal to 0.1% <str<strong>on</strong>g>of</str<strong>on</strong>g> carrying capacity per year. Developed by Dr.Caz Taylor, UC Davis.limited to sites with certain sediment characteristics, such asareas with young Spartina <strong>on</strong> s<str<strong>on</strong>g>of</str<strong>on</strong>g>t sediment. Crushing wellestablishedSpartina meadows with a thick root mat orSpartina <strong>on</strong> sand provides marginal c<strong>on</strong>trol. Disking is alsorelatively inexpensive and comparable to crushing, but wasproblematic in terms <str<strong>on</strong>g>of</str<strong>on</strong>g> secti<strong>on</strong>ing and uprooting large mats<str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina, which re-established in deeper tidal z<strong>on</strong>es. Thebroadcast rate <str<strong>on</strong>g>of</str<strong>on</strong>g> glyphosate, although very inexpensive,<strong>on</strong>ly provided c<strong>on</strong>trol under ideal c<strong>on</strong>diti<strong>on</strong>s (>48 hour drytime and a clean, intact canopy). These c<strong>on</strong>diti<strong>on</strong>s were rarein <str<strong>on</strong>g>the</str<strong>on</strong>g> field. The hand-sprayed rate <str<strong>on</strong>g>of</str<strong>on</strong>g> glyphosate (with orwithout previous crushing) provided fairly c<strong>on</strong>sistentc<strong>on</strong>trol, but accurate rates and cost analysis are difficult toassess. Tank mixes ranged from 5 to 8% v/v <str<strong>on</strong>g>of</str<strong>on</strong>g> product withspray volumes from 1,000 to 3,000 l/ha spray volume.Applicati<strong>on</strong> from airboats is limited to a few hectares perday. Variability in efficacy from hand applicati<strong>on</strong>s largelyreflected plants that were missed or <strong>on</strong>ly partially covered.Although large-site m<strong>on</strong>itoring data is lacking, <str<strong>on</strong>g>the</str<strong>on</strong>g> broadcast- 253 -
Chapter 4: Spartina C<strong>on</strong>trol and Management<str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Third</str<strong>on</strong>g> <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Invasive</strong> Spartinaapplicati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> imazapyr c<strong>on</strong>ducted in 2004 was relativelyinexpensive (~$600/ha), fast (>100 ha/day), and fairlyefficacious.Repeated c<strong>on</strong>trol measures c<strong>on</strong>ducted year after year <strong>on</strong><str<strong>on</strong>g>the</str<strong>on</strong>g> same site should result in an overall reducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g>Spartina at <str<strong>on</strong>g>the</str<strong>on</strong>g> site. This overall reducti<strong>on</strong> in Spartinaoccupati<strong>on</strong> over time (two years) was not evident from <str<strong>on</strong>g>the</str<strong>on</strong>g>pooled m<strong>on</strong>itoring data for ei<str<strong>on</strong>g>the</str<strong>on</strong>g>r chemical or mechanicalc<strong>on</strong>trol. These results are not inc<strong>on</strong>sistent with those foundin Puget Sound (Hacker et al. 2001). They report that sitesrequired c<strong>on</strong>sistent c<strong>on</strong>trol for four years to obtain an 86%decrease in Spartina. Most <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> sites m<strong>on</strong>itored in thisstudy were also large (>10 ha) and, according to Hacker etal. (2001), less likely to show decline in Spartina densityover time than small sites. Examples <str<strong>on</strong>g>of</str<strong>on</strong>g> this spatial scaleeffect were evident in this study. For three discrete sites thatwere smaller than five hectares and sprayed for twoc<strong>on</strong>secutive years, <str<strong>on</strong>g>the</str<strong>on</strong>g> percentage <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina-free quadratswent from 73% to 85%, 60% to 90% and 60% to 95%.Evidently <strong>on</strong> large sites, re-growth and seedling reinfestati<strong>on</strong>compensated for any additi<strong>on</strong>al c<strong>on</strong>trol achievedin subsequent years. This c<strong>on</strong>curs with results from <str<strong>on</strong>g>the</str<strong>on</strong>g>discrete time, logistic growth model. When parameters forgrowth rate are set at 0.15, seedling input at 0.01, andc<strong>on</strong>trol rates at 50%, 10 ha <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina within a 100-hamudflat would still have 50% <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina left in <str<strong>on</strong>g>the</str<strong>on</strong>g>beginning <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> third year. On <str<strong>on</strong>g>the</str<strong>on</strong>g> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r hand, when ac<strong>on</strong>trol rate <str<strong>on</strong>g>of</str<strong>on</strong>g> 73% is used and <str<strong>on</strong>g>the</str<strong>on</strong>g> parameter for outsideseedling input is reduced to 0.005, <str<strong>on</strong>g>the</str<strong>on</strong>g> site is projected to be81% Spartina-free in <str<strong>on</strong>g>the</str<strong>on</strong>g> beginning <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> third year (this issimilar to <str<strong>on</strong>g>the</str<strong>on</strong>g> 85% found at <strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> our m<strong>on</strong>itoring sites).Three major c<strong>on</strong>clusi<strong>on</strong>s can be reached from thism<strong>on</strong>itoring study. First, real world c<strong>on</strong>trol data are highlyvariable between sites and years, and tend to show resultsthat are less effective than what would be expected underideal c<strong>on</strong>diti<strong>on</strong>s. Efficacy can vary by at least 20% from <str<strong>on</strong>g>the</str<strong>on</strong>g>expected level. Sec<strong>on</strong>d, with <str<strong>on</strong>g>the</str<strong>on</strong>g> excepti<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> tilling andimazapyr, n<strong>on</strong>e <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> treatments provided efficacyanywhere near <str<strong>on</strong>g>the</str<strong>on</strong>g> level <str<strong>on</strong>g>of</str<strong>on</strong>g> that which would be required toachieve eradicati<strong>on</strong> in a reas<strong>on</strong>able time frame. Based <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g>political landscape, it is not prudent to expect funding for alarge-scale c<strong>on</strong>trol effort to go bey<strong>on</strong>d a six to eight-yeartime period. Thus, unless <str<strong>on</strong>g>the</str<strong>on</strong>g> average c<strong>on</strong>trol rate for a givenmethod can be expected to be greater than 75%, that methodhas minimal practical value. The tenfold expansi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g>Spartina in Willapa Bay during <str<strong>on</strong>g>the</str<strong>on</strong>g> last decade <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>trolefforts testifies to this maxim. <str<strong>on</strong>g>Third</str<strong>on</strong>g>, even if <str<strong>on</strong>g>the</str<strong>on</strong>g> c<strong>on</strong>trol rateis 75%, as l<strong>on</strong>g as <str<strong>on</strong>g>the</str<strong>on</strong>g>re is significant seedling input fromoutside sources, eradicati<strong>on</strong> can not be achieved. The c<strong>on</strong>trolefforts should be mounted over a scale large enough tominimize threats from new seedlings. Similarly, unless <str<strong>on</strong>g>the</str<strong>on</strong>g>sites c<strong>on</strong>tinue to be treated year after year, no appreciablegains toward eradicati<strong>on</strong> can be achieved.ACKNOWLEDGEMENT:Funding was provided by Willapa Nati<strong>on</strong>al WildlifeRefuge and Washingt<strong>on</strong> State Commissi<strong>on</strong> for PesticideRegistrati<strong>on</strong>. The discrete time, logistic growth model wasdeveloped and provided by Dr. Caz Taylor, UC Davis.REFERENCESFrid, C., W. Chandrasekara, and P. Davey, 1999. The restorati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g>mud flats invaded by comm<strong>on</strong> cordgrass (Spartina anglica)using mechanical disturbance and its effects <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> macrobenthicfauna. Aquatic C<strong>on</strong>servati<strong>on</strong>: Marine and FreshwaterEcosystems 9:47-61.Garnett, R.P., G. Hir<strong>on</strong>s, C. Evans, and D. O’C<strong>on</strong>nor. 1992. Thec<strong>on</strong>trol <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina (cord-grass) using glyphosate. Aspects <str<strong>on</strong>g>of</str<strong>on</strong>g>Applied Biology 29:359-364.Government Accounting Office. 2002. <strong>Invasive</strong> Species: Clearerfocus and greater commitment needed to effectively manage <str<strong>on</strong>g>the</str<strong>on</strong>g>problem. GAO-03-1; www.gao.gov/cgi-bin/getrpt?GAO-03-01.Hacker, S.D., D. Heimer, S. E. Hellquist, T.G. Reeder, B. Reeves,T.J. Riord<strong>on</strong>, and M.N. Dethier, 2001. A marine plant (Spartinaanglica) invades widely varying habitats: potential mechanisms<str<strong>on</strong>g>of</str<strong>on</strong>g> invasi<strong>on</strong> and c<strong>on</strong>trol. Biological Invasi<strong>on</strong>s 3: 211-217.Hedge P., L. Kriwoken and K. Patten, 2003. A review <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartinamanagement in Washingt<strong>on</strong> State, US. Journal <str<strong>on</strong>g>of</str<strong>on</strong>g> Aquatic PlantManagement 41: 82-90.Kilbride, K.M., F.L. Paveglio and C.E. Grue, 1995. C<strong>on</strong>trol <str<strong>on</strong>g>of</str<strong>on</strong>g>smooth cordgrass with Rodeo in a southwestern Washingt<strong>on</strong>estuary. Wildlife Society Bulletin 23:53-524.Major, W.W., III, C.E. Grue, J.M. Grassley and L.L. C<strong>on</strong>quest,2003. Mechanical and chemical c<strong>on</strong>trol <str<strong>on</strong>g>of</str<strong>on</strong>g> smooth cordgrass inWillapa Bay, Washingt<strong>on</strong>. Journal <str<strong>on</strong>g>of</str<strong>on</strong>g> Aquatic PlantManagement 41: 6-12.Patten, K. 2002. Smooth cordgrass c<strong>on</strong>trol with imazapyr. WeedTechnology 16: 826-832.Patten, K. 2003. The efficacy <str<strong>on</strong>g>of</str<strong>on</strong>g> mechanical treatment efforts in2001 <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> c<strong>on</strong>trol <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina in Willapa Bay in 2002. Progressreport submitted to <str<strong>on</strong>g>the</str<strong>on</strong>g> Willapa Nati<strong>on</strong>al Wildlife Refuge.(Available from <str<strong>on</strong>g>the</str<strong>on</strong>g> author via email [pattenk@wsu.edu].)Patten, K. 2004. The efficacy <str<strong>on</strong>g>of</str<strong>on</strong>g> chemical and mechanical treatmentefforts in 2002 <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> c<strong>on</strong>trol <str<strong>on</strong>g>of</str<strong>on</strong>g> Spartina in Willapa Bay in 2003.Progress report submitted to <str<strong>on</strong>g>the</str<strong>on</strong>g> Willapa Nati<strong>on</strong>al WildlifeRefuge. (Available from <str<strong>on</strong>g>the</str<strong>on</strong>g> author via email[pattenk@wsu.edu].)Patten, K. and C. Stenvall. 2002. C<strong>on</strong>trol <str<strong>on</strong>g>of</str<strong>on</strong>g> smooth cordgrass(Spartina alterniflora): a comparis<strong>on</strong> between variousmechanical and chemical c<strong>on</strong>trol methods for efficacy, cost andaquatic toxicity. Proc. <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> 11th <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong>Aquatic <strong>Invasive</strong> Species. pp. 340-350.Pritchard, G. H. (1995). Herbicide trials <strong>on</strong> Spartina. In: J.E. Rash,R.C. Williams<strong>on</strong>, and S.J. Taylor, eds. How green is yourmudflat? <str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> Australasian <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong>Spartina C<strong>on</strong>trol. Department <str<strong>on</strong>g>of</str<strong>on</strong>g> C<strong>on</strong>servati<strong>on</strong> and NaturalResources, Yarram, Victoria, pp. 66.Shaw, W. B. and D.S. Gosling. 1995. Spartina c<strong>on</strong>trol in NewZealand—an overview. In: J.E. Rash, R.C. Williams<strong>on</strong>, and S.J.Taylor, eds. <str<strong>on</strong>g>Proceedings</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> Australasian <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong>Spartina C<strong>on</strong>trol Melbourne, Australia: Victorian GovernmentPublicati<strong>on</strong>. pp. 43-60.WSDA. 1999-2003, Spartina Eradicati<strong>on</strong> Program—LegislativeReports, http://agr.wa.gov/PlantsInsects/Weeds/Spartina.- 254 -
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