5
Acacia koa in Hawai‘i: Facing the Future Proceedings of the 2016 Symposium, Hilo, HI: www.TropHTIRC.org, www.ctahr.hawaii.edu/forestry 30 SILVICULTURE STAND MANAGEMENT OF KOA: THINNING AND FERTILIZATION Travis Idol, Ph.D. (University of Hawai‘i at Mānoa Department of Natural Resources and Environmental Management), Paul Scowcroft (USDA Forest Service, Institute of Pacific Islands Forestry), J.B. Friday (University of Hawai‘i at Mānoa Department of Natural Resources and Environmental Management) In many areas of Hawai‘i, Acacia koa (koa) has been naturally regenerated through soil scarification or other disturbances such as fire, resulting in single-age cohorts of dense but patchy stands. Managing these stands for timber production usually includes thinning to maintain growth potential and prevent suppression through intraspecific competion. Other treatments, such as fertilization or grass control, may have additional positive effects on the selected trees ("crop trees"). A growing body of research offers insights into responses to thinning and other treatments for dense, naturally-regenerated koa stands. Scowcroft and Stein (1986) studied a 10-year-old koa stand on Maui situated at 1100 m above sea level (asl) on nutrient-poor soil that received on average 2500 mm mean annual precipitation (MAP). Stand density at 10 years was 2100 stems ha 1 and a majority of trees were considered dying or weak. Experimental treatments included thinning to 50% residual density and fertilization with N-P-K (10-30-10) at 460 kg ha -1 and MgSO4 at 170 kg ha -1 . Thinning significantly increased stand relative growth rate for the first 2-3 years, until an outbreak of koa looper moth (Scotorhythra paludicola) defoliated the stand. Fertilization had no significant independent or additional effect to thinning. Pearson and Vitousek (2001) studied a 9-year-old koa stand on Hawai‘i Island situated at 1500 m asl on a 2000-3000 year-old lava flow soil (Mauna Loa) that received on average 2500 mm MAP. Stand density was 16,000 stems ha -1 with a basal area of 21 m 2 ha -1 . Experimental treatments included thinning to 50% residual basal area and fertilization with 70 kg ha -1 of nitrogen (N) as ammonium nitrate. Thinning increased mean annual stem diameter (DBH) increment from 0.4 to 1.1 cm. Fertilization had no significant independent or additional effect to thinning.

2016 Koa Symposium Proceedings Final 8 7 17 symposium 2016...stand on Maui situated at 1100 m above sea level ... 750 kg ha-1 of phosphorus (P) ... crown area requirement of trees

Embed Size (px)

Citation preview

AcaciakoainHawai‘i:FacingtheFutureProceedingsofthe2016Symposium,Hilo,HI:www.TropHTIRC.org,www.ctahr.hawaii.edu/forestry

30

SILVICULTURE

STANDMANAGEMENTOFKOA:THINNINGANDFERTILIZATION

TravisIdol,Ph.D. (UniversityofHawai‘iatMānoaDepartmentofNaturalResources

andEnvironmentalManagement),PaulScowcroft(USDAForestService,Instituteof

PacificIslandsForestry),J .B.Friday(UniversityofHawai‘iatMānoaDepartmentof

NaturalResourcesandEnvironmentalManagement)

InmanyareasofHawai‘i,Acaciakoa(koa)hasbeennaturallyregeneratedthroughsoilscarification

orotherdisturbancessuchasfire,resultinginsingle-agecohortsofdensebutpatchystands.

Managingthesestandsfortimberproductionusuallyincludesthinningtomaintaingrowth

potentialandpreventsuppressionthroughintraspecificcompetion.Othertreatments,suchas

fertilizationorgrasscontrol,mayhaveadditionalpositiveeffectsontheselectedtrees("crop

trees").

Agrowingbodyofresearchoffersinsightsintoresponsestothinningandothertreatmentsfor

dense,naturally-regeneratedkoastands.ScowcroftandStein(1986)studieda10-year-oldkoa

standonMauisituatedat1100mabovesealevel(asl)onnutrient-poorsoilthatreceivedon

average2500mmmeanannualprecipitation(MAP).Standdensityat10yearswas2100stems

ha1andamajorityoftreeswereconsidereddyingorweak.Experimentaltreatmentsincluded

thinningto50%residualdensityandfertilizationwithN-P-K(10-30-10)at460kgha-1andMgSO4

at170kgha-1.Thinningsignificantlyincreasedstandrelativegrowthrateforthefirst2-3years,

untilanoutbreakofkoaloopermoth(Scotorhythrapaludicola)defoliatedthestand.Fertilization

hadnosignificantindependentoradditionaleffecttothinning.

PearsonandVitousek(2001)studieda9-year-oldkoastandonHawai‘iIslandsituatedat1500m

aslona2000-3000year-oldlavaflowsoil(MaunaLoa)thatreceivedonaverage2500mmMAP.

Standdensitywas16,000stemsha-1withabasalareaof21m2ha-1.Experimentaltreatments

includedthinningto50%residualbasalareaandfertilizationwith70kgha-1ofnitrogen(N)as

ammoniumnitrate.Thinningincreasedmeanannualstemdiameter(DBH)incrementfrom0.4to

1.1cm.Fertilizationhadnosignificantindependentoradditionaleffecttothinning.

AcaciakoainHawai‘i:FacingtheFutureProceedingsofthe2016Symposium,Hilo,HI:www.TropHTIRC.org,www.ctahr.hawaii.edu/forestry

31

Inthesamelocation,Scowcroftetal.(2007)studieda23-year-oldkoastand.Standdensitywas

approximately900stemsha-1.Experimentaltreatmentsincludedthinningaroundselectedcrop

trees(alltreeswithoverlappingortouchingcrowns),herbicidegrasscontrol,andfertilizationwith

750kgha-1ofphosphorus(P)astriplesuperphosphate.Thefullcombinationoftreatments

resultedinasignificantincreaseinannualDBHincrementfrom0.5to1.09cm.Thisdifferencewas

duetoasignificantdeclineinDBHincrementovertimeinthecontrolplotsvsnodifferenceover

timeinthefullytreatedplots.

Bakeretal.(2008)studied30-year-oldkoastandsonHawai‘iIslandsituatedat1500maslona

1500-300year-oldlavaflowsoil(MaunaLoa)thatreceivedonaverage1200mmMAP.

Experimentaltreatmentsincludedthinningaroundselectedcroptreestodifferentsetdistances,

representingresidualstanddensitiesfrom900to200stemsha-1,andherbicidegrasscontrol.After

3years,stemDBHincrementwastwiceasgreatwiththinningto900stemsha-1andalmost4times

asgreatat200stemsha-1.Grasscontrolhadnosignificantindependentoradditionaleffect.

Idoletal.(2017)studieda9year-oldkoastandsituatedonHawai‘iIslandat1500maslonadeep

ashsoil(MaunaKea)thatreceivedonaverage2000mmMAP.Experimentaltreatmentsincluded

thinningaroundselectedcroptreestoaresidualstanddensityof500stemsha-1(4.5-mradius),

fertilizationwith600kgha-1ofPastriplesuperphosphate,andherbicidegrasscontrol.Thinning

increasedannualstemDBHincrementfrom1.0to2.0cm.Fertilizationandgrasscontrolhadno

significantindependentoradditionaleffectonDBHincrement.Forthinnedtrees,Pfertilization

significantlyincreasedheightgrowthfrom0.5to1.0mover2years.Gapclosureafterthinning

progressedataratethatwasprojectedtoresultinfullcanopyclosureafterapproximately5years.

Conclusionsandrecommendationsfromthisstudyincludethefollowing:

1.Thetimeoffirstthinningshouldtakeplaceat6-8yearsofage,dependinguponinitialdensityand

averagecroptreesize.

2.Croptreeselectionthinningisrecommendedtofocuseffortsontreeswiththebesttimber

potential.Thethinningintensity(radius)shouldbeaswideaspracticable,uptotheexpected

crownarearequirementoftreesatthefirstcommercialthinningorharvest.

3.ThinningatayoungageshouldapproximatelydoublestemDBHincrement,maintaininggrowth

potentialoftreesinotherwiseoverstockedstands.

AcaciakoainHawai‘i:FacingtheFutureProceedingsofthe2016Symposium,Hilo,HI:www.TropHTIRC.org,www.ctahr.hawaii.edu/forestry

32

4.FertilizationwithPisrecommendedatarateofatleast500kgha-1.Thisappearstobemore

importantforolderstands,buttheremaybeimprovementsinheightgrowthevenforyounger

stands.

5.Giventhegreaterexpenseofthinningvsfertilizationandthepotentialincreaseinheightgrowth,

repeatedPfertilizationmayimprovethecanopydominanceofcroptreesandreduceoreliminate

theneedforadditionalpre-commercialthinningasthinnedgapsclosein.

Figure1:A12-year-oldpotentialcroptreeonMaunaKearespondswithhealthycrowndevelopment

fouryearsafterrelease

AcaciakoainHawai‘i:FacingtheFutureProceedingsofthe2016Symposium,Hilo,HI:www.TropHTIRC.org,www.ctahr.hawaii.edu/forestry

33

Figure2:Alllessvigorousorforkedtreeswerefelledwithina15-footradiusofeachpotentialcroptree

inthisstudyina9-year-oldstandonMaunaKea.

Figure3:Theyoungkoastandontheleftwasregeneratedbyscarificationbybulldozerandfencingto

excludecattle.Ahealthyseedbankhadbeenbuiltupinthesoilbytheremainingoverstorykoatrees

inthesepasturesonMaunaKea.

AcaciakoainHawai‘i:FacingtheFutureProceedingsofthe2016Symposium,Hilo,HI:www.TropHTIRC.org,www.ctahr.hawaii.edu/forestry

34

References

Baker,P.J.,Robinson,A.P.,Ewel,J.J.,2008.SuddenandsustainedresponseofAcaciakoacroptrees

tocrownreleaseinstagnantstands.CanadianJournalofForestResearch38,656-666.

Idol,T.W.,MartinezMorales,R.,Friday,J.B.,Scowcroft,P.G.2017.Precommercialreleasethinningof

potentialAcaciakoacroptreesincreasesstemandcrowngrowthindense,8-year-oldstandsin

Hawai'i.ForestEcologyandManagement392:105-114.

Pearson,H.L.,Vitousek,P.M.,2001.Standdynamics,nitrogenaccumulation,andsymbioticnitrogen

fixationinregeneratingstandsofAcaciakoa.EcologicalApplications11,1381-1394.

Scowcroft,P.G.,Friday,J.B.,Idol,T.W.,Dudley,N.,Haraguchi,J.,Meason,D.,2007.Growthresponse

ofAcaciakoatreestothinning,grasscontrol,andphosphorusfertilizationinasecondaryforestin

Hawai‘i.ForestEcolManage239,69-80.

Scowcroft,P.G.,Stein,J.D.,1986.StimulatinggrowthofstagnatedAcaciakoabythinningand

fertilizing.ResearchNote-PacificSouthwestForestandRangeExperimentStation,USDAForest

Service,8pp.