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Field

quantification

of

wetting–drying

cycles

to

predict

temporal

changes

of

soil

pore

size

distribution

G.

Bodner

*

,

P.

Scholl,

H.-P.

Kaul

DepartmentofCropSciences,DivisionofAgronomy,UniversityofNaturalResourcesandLifeSciences,BOKUVienna,GregorMendelStraße33,A-1190Vienna,Austria

1. Introduction

Hydraulic properties of the soil depend on texture and structure.Inthesaturatedandnear-saturatedrangesoilstructure essentiallycontrolsthetwofundamentalrelationsforwaterflow, i.e.theretentionandhydraulicconductivityfunctions(Cresswell etal.,1992).Soilstructuralporosityisahighlydynamicproperty that respondstovarious external factorsof environmental and human nature. Therefore knowledge of spatial and temporal variabilityofsoilhydraulicpropertiesisfundamentaltoaccurately

describeprocesseslikewaterinfiltrationandstorage(vanEsetal.,

1999).

In a tillage experiment, Schwen et al. (2011) showed that seasonalvariabilityofhydraulicpropertieswashigherthantillage induced variability. Bodner et al. (2008) studied the effect of different cover crop canopy and residue coverageon hydraulic propertiesandfoundsignificantoverwinterdecreaseinhydraulic conductivityandflowweightedporeradiusforalltreatments.The effect was more pronounced in bare soil. Also, irrigation can introduce strong temporal changes of hydraulic properties dependingonsoiltype andirrigationmethod(Angulo-Jaramillo

etal.,1997;Zengetal.,2013).

The role of environmental influences on soil structure formation wasreviewedbyHorn andSmucker(2005).Inarid, semi-aridandsubhumidregionswetting–drying(WD)cyclesare essentialforsoilaggregation(DalalandBridge,1996).Intensity, number and duration of swelling and shrinkage cycles were identifiedaskeyprocessesofaggregateformationandstrength. Capillaritywasthedrivingfactorofsoilaggregationupondrying, whilerewettingincreasedstructuralinstability(Pengetal.,2007;

Ladoetal.,2004).

ARTICLE INFO

Articlehistory:

Received15February2013 Receivedinrevisedform25April2013 Accepted7May2013

Keywords:

Wetting–dryingcycles Soilporesizedistribution Spectralanalysis Temporalvariability Tensioninfiltrometer

ABSTRACT

Wetting–drying(WD)cyclessubstantiallyinfluencestructurerelatedsoilpropertiesandprocesses. MoststudiesonWDeffectsarebasedoncontrolledcyclesunderlaboratoryconditions.Ourobjective wasthequantificationofWDcyclesfromfieldwatercontentmeasurementsandtheanalysisoftheir relationtothetemporaldriftinthesoilporesizedistribution.Parameters oftheKosugihydraulic propertymodel(rm,Kosugi,sKosugi)werederivedbyinverse optimization fromtensioninfiltrometer

measurements.SpectralanalysiswasusedtocalculateWDcycleintensity,numberanddurationfrom watercontenttimeseries.WDcycleintensitywasthebestpredictor(r2=0.53–0.57)forthetemporal

driftinmedianporeradius(rm,Kosugi)andporeradiusstandarddeviation(sKosugi).Atlowersoilmoisture

conditionstheeffectofcycleintensitywasreduced.AbivariateregressionmodelwasderivedwithWD intensityandameteorological indicatorfordryingperiods(ET0,climaticwaterbalancedeficit) as

predictorvariables. This model showed that WDenhanced macroporosity (higherrm,Kosugi) while

decreasingporeheterogeneity(lowersKosugi).AdryingperiodwithhighcumulativevaluesofET0ora

strongclimaticwaterbalancedeficitonthecontraryreducedrm,KosugiwhileslightlyincreasingsKosugi

duetohigherfrequencyatsmallporeradiusclasses.Thetwoparameterregressionmodelwasappliedto predictthetimecourseofsoilporesizedistributionparameters.Theobservedsystemdynamicswas capturedsubstantiallybetterbythecalculatedvaluescomparedtoastaticrepresentationwithaveraged hydraulic parameters. The study showed that spectral analysis is an adequate approach for the quantificationoffieldWDpatternandthatWDintensityisakeyfactorforthetemporaldynamicsofthe soilporesizedistribution.

ß2013TheAuthors.PublishedbyElsevierB.V.

Abbreviations:WD,wetting–drying;PSD,poresizedistribution;f,totalporosity; us, water content atsaturation; ur, residual watercontent;hm,Kosugi, median pressurehead;rm,Kosugi,medianporeradius;sKosugi,poreradiusstandarddeviation.

*Correspondingauthor.Tel.:+431476543331;fax:+431476543342. E-mailaddress:[email protected](G.Bodner).

ContentslistsavailableatSciVerseScienceDirect

Soil

&

Tillage

Research

j o urn a l hom e pa g e :ww w . e l se v i e r. c om / l oca t e / st i l l

0167-1987ß2013TheAuthors.PublishedbyElsevierB.V.

http://dx.doi.org/10.1016/j.still.2013.05.006

Open access under CC BY-NC-ND license.

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SoilporositywasfoundtoincreaseaftertheapplicationofWD cycles(Piresetal.,2005).Piresetal.(2009)observedanevolution frommassivestructurestostructureswithagreatnumberoflarge and connected pores after WD cycles. Also the pore size distribution(PSD) is modified in response to internal capillary stresses.Sartorietal.(1985)andPagliaietal.(1987)discussedthe overallinfluenceofWDcyclesontotalporosity,poreshapeand poresizedistribution.Theirresultsdemonstrateanincreaseinthe volume of pores in the range of 30

m

m to 1mm and strong modificationsinshapeandsizedistribution.

Anincreaseincoarseporesduringdryingwasdescribedasa consequenceofcrackandmicrocrackformation(BruandandProst,

1987;Hornetal.,2002;SeguelandHorn,2006).Piresetal.(2005)

alsofoundanincreaseinthenumberofmicroporesandmesopores with subsequent WD cycles. Sarmah et al. (1996) however observeda decreasein water infiltration rateafter WD cycles. Thiswasprobablyduetotheslakingandcollapseofaggregates.

Also Phogat and Aylmore (1989) found a decrease in

macro-porosity after cycles of soil wetting and subsequent drying. Macroporesaregenerallymoresensitivetosoildeformationthan microporesbecauseoflowerporerigidity(Kutı´leketal.,2006). However,Braudeauetal.(2004)suggestedthatshrinkagecapacity ofmacropores can alsobe less thanthat of micropores due to smallercapillarystressesinlargepores.

Pengetal.(2007)conductedadetailedlaboratorystudyonpore

changesundervaryingWDcycleintensityand number.Intense WDcyclesenhancedthevolumeoflargeporesmarkedlyinmost soils they analyzed. Their data also suggested higher pore heterogeneity with increasing cycle number. However, if soils weresubjectedtointenseWD cycles,thefrequency dependent effectfaded.Severalauthorsshowedthattheimpactofthefirst WD cycle on soil structure is greatest and decreases with subsequentcycles(Basmaetal.,1996;Tripathyetal.,2002;Leij etal.,2002).Theeffecthoweveralsodependsontheinitialstateof soil(pre-shrinkagestress;BaumgartlandHorn,1999).

MostquantitativeknowledgeonWDeffectsonsoilproperties hasbeenobtainedfromlaboratoryexperimentwithsoilsamples subjecttocontrolledcycles.Butalsoinfieldexperimentsseveral authorsreferredtoWDasmajorinfluenceonhydraulicproperty andsoilstructurechanges (e.g.Mapaet al.,1986;Pagliaietal.,

2004;Mubaraketal.,2009).Amaingapinourcurrentknowledge

istounderstand how irregularcyclestypicallyoccurring under fieldconditionsmodifyhydraulicproperties.Aquantificationof the natural WD pattern in field experiments would be highly necessaryinordertobetterunderstandtheirroleasadriverfor hydraulicpropertyand soilstructuredynamicsina naturalsoil environment.Thiscouldhelptobridgeprocessbased understand-ingfromlaboratoryworkandqualitativefieldobservations.

Theobjectiveofourstudythereforewastodevelopamethodto quantifytheWDpatternfromfieldsoilwatercontenttimeseries usingspectralanalysis. Wethen analyzedtherelationbetween WDandtemporalchangesofKosugi’sretentioncurveparameters thatcapturetheshapeoftheporesizedistribution.Finallyouraim was to test a regression model to predict the time course of Kosugi’sporeparametersfromenvironmentalvariables.

2. Materialsandmethods 2.1. Fieldexperiment

A field experiment was conducted over three years (2009– 2012) to study factors underlying temporal changes in soil hydraulic properties. The experiment is described in detail by

Bodneretal.(2013).Inshort,itwaslocatedonanarablefieldnear

Raasdorf,LowerAustria(488140N,168350E,156masl).Themain experimental factor was three differentpost-harvest soil cover

treatments.Forthepresentevaluation,weaverageddatafromall plots(n=9)asourfocuswasonthemeantemporaldynamicsat thesite. Climaticallythelocationischaracterizedbysub-humid conditions (pannonic) with an average annual precipitation of 525mm,ameanannualtemperatureof9.88C,andameanrelative humidityof75%.Weatherdatawererecordedbyanautomated weatherstation(AdconTelemetryGmbH,Austria)directlyonthe field.Fig.1showsrainfall,temperatureandreference evapotrans-piration(ET0)forthethreeexperimentalyears.

Thesoilis classifiedas ChernozemintheWRB(IUSS,2007). BasicsoilpropertiesaregiveninTable1.

Soilwatercontentwasmonitoredcontinuouslyineachplotby capacitance sensors (CProbe, Adcon Telemetry GmbH, Austria) installedviaaccesstubes.Sensorswerepreviouslynormalizedand comparedtogravimetricreferencesamples.Fig.2showsthesoil waterdynamicsintheuppersoillayer(5cmsoildepth)whichwas usedfortheanalysisofWDcycles.

2.2. Determinationofsoilporesizedistributionparameters Soil pore size distribution parameters were determined by inverse analysis of tension infiltrometer data. Infiltration mea-surementswereconductedtwelvetimesbetweenSeptember2009 andJuly2012.Allmeasurementswereperformedusingatension infiltrometer (Soil Measurement Systems Inc., Tucson, AZ) and takenat thesoil surfacewhere moststructural dynamicswere expected.DetailsofmeasurementaregiveninBodneretal.(2013). The inverseanalysisof infiltrationmeasurementsrequires a numericalsolutionoftheRichardsequationforDarcianflowina radial symmetric 2D domain. We followed the procedure presented by Sˇimu˚nek et al. (1998). Soil water retention was described by the model of Kosugi (1996) which is based on a lognormalporesizedistribution.SoilwaterretentionSe(h)isgiven by

SeðhÞ¼0:5Erfc logðh=ðhffiffiffi m;KosugiÞÞ 2

p

s

Kosugi !

(1) whereSeistheeffectivesaturationcorrespondingtoð

u



u

rÞ=ð

u

s

u

rÞ with

u

(cm3cm3) being volumetric water content,

u

r

(cm3cm3)residualwatercontentand

u

s(cm3cm3)saturation

watercontent.Erfcisthecomplementaryerrorfunction,hm,Kosugi

(cm)themedianpressureheadofthesoilwaterretentioncurve whereSe(hm,Kosugi)=0.5,and

s

Kosugithestandarddeviationofthe

log-transformedpressurehead.Themedianporeradius(rm,Kosugi)

canbecalculatedfromhm,KosugiusingtheYoung–Laplaceequation.

Parameter estimation is done by minimizing the objective functionasdefinedbySˇimu˚nekandvanGenuchten(1996)using theprogramHYDRUS2D/3D(Sˇimu˚neketal.,2006)whichappliesa Levenberg–Marquardtnonlinear minimization algorithm. Initial parameter estimates were derived from the texture based

Fig. 1. Monthly averaged precipitation, air temperature and reference evapotranspiration(ET0)attheexperimentalsite.

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pedotransfer function Rosetta (Schaap et al., 2001) (input parameters:soiltextureandbulkdensity).Toreducetheamount ofunknownvariables,

u

rwasfixedto0.067cm3cm3,aspredicted

byRosetta.

u

svalues weresetequal totalporosity fromsample

cylindermeasurements, and Ks was used fromdirect Wooding

analysisofinfiltrationdata(Sˇimu˚neketal.,1998;Bodneretal., 2013).Theremainingparameters

s

Kosugi,andhm,Kosugiwerethen

estimatedinversely.

2.3. Quantificationofwetting–dryingcycles

WDcycleswerequantifiedbyspectralanalysisofsurfacenear soil water content time series (5cm soil depth) using theSAS procedurePROCSPECTRA(SAS/STAT,2009).Spectralanalysisisa statisticalmethodthatcandiscerncyclicpatternsinasoilproperty

(Nielsen and Wendroth, 2003; Si, 2008). We quantified the

intensity of WD cycles by spectral density and calculated the numberofcyclesfromspectralwavelength(cycleduration)via Ncycles¼

pi

D

ti;iþi

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whereNcyclesisthenumberofwetting–dryingcycles,pi(days)is

thewavelengthofaspectralpeakand

D

ti,i+1(days)isthelengthof

the analyzed time series. Fig. 3 exemplifies our approach to quantificationofWDcycles.

Beforeapplyingspectralanalysisdataaredetrendedbylinear regression of water content vs. time (Worrall and Burt, 1998,

Fig.3a). For eachperiod it istested ifthe detectedspectraare differentfromrandomscattering(whitenoise)byaFisher’sKappa andBartlett’sKolmogorov–Smirnovstatisticswhichareavailable intheSASspectralprocedure.

Spectralanalysisthenproducesestimatesofspectraldensities byafiniteFouriertransformwhichdecomposesthedataseriesinto a sum of sine and cosine waves of different amplitudes and wavelengths(Eq.(3)): xt¼ a0 2 þ Xm k¼1

½akcosð

v

ktÞþbksinð

v

ktÞ (3)

Herextisthevalueofatimeseriesattimet,misthenumberof

frequencies intheFourier decomposition(m¼n=2ifnis even, m¼n1=2ifnisodd,wherenisthenumberofobservationsin thetimeseries),a0isthemeanterm(2x),akandbkarethecosine

andsinecoefficientsrespectivelyand

v

karetheFourier

frequen-cies (

v

k¼2

p

k=n). The periodogram of amplitude at each frequencykisgivenby Jk¼ n 2ða 2 kþb2kÞ (4)

Fig. 3b gives an example of a periodogram with spectral densitiesfor thedetrendedseries.Thewhitenoise spectrumas wellasthe95%confidencelimitforpeakssignificantlydiffering fromwhite noiseare calculatedfollowing Torrence and Compo

(1998).Theperiodogramcanbeinterpretedascontributionofthe

kthharmonic

v

ktothetotalsumofsquaresinthedecomposition

of theprocess.Thusa highspectral densityquantifiesa strong cyclicdeviationfromthemeanofthetimeseries.Fig.3cshowsthe wavefunctionofthedominantspectrumfortheexampleseries,i.e. thesumofcosineandsinecomponentsweightedbyakandbkat

frequency 0.161 over time. When summing up all significant spectraaccordingtoEq.(4)thereconstructedtimeseriesshownin

Fig. 3d is obtained. To reduce volatility of the periodogram, generally spectraare smoothed usinge.g. a moving average to obtainthefinalspectraldensityestimates(SAS/STAT,2009).We appliedathirdordermovingaverage forsmoothingthe period-ograms.

2.4. Statisticalanalysesandmodeling

Statisticalanalysesofthedatacomprised(i)analysisofvariance ofsoilporesizedistributionparameters,(ii)regressionanalysisof therelationbetweenporeparametersandWDpattern,and(iii) evaluation of a regression based predictivemodel for thetime courseofsoilporesizedistributionparameters.

2.4.1. Analysisofvariance

Soilhydraulicparameters(

s

Kosugiandrm,Kosugi)weresubmitted

to an analysis of variance to determine periods of significant temporaldrift.WeusedtheMIXEDprocedureinSAStoproperly considerrepeated measurementsover time. PROCMIXED com-putesWald-typeF-statisticsusinggeneralizedleastsquares(GLSE) basedonrestrictedmaximumlikelihoodestimatesofthevariance components(Littelletal.,1998).Incaseofsignificantdifferencesin theWald-F-statisticforp<0.05,treatmentmeanswerecompared usinga two-sidedt test.Toaccountfortheserialcorrelationof non-randomized repeated measures on thesame experimental unit,i.e.measurementdate,anadequatecorrelationmodelwasfit tothedatabasedontheAkaikeInformationCriterion(Piephoetal.,

2004).

2.4.2. Regressionmodel

Regression analysis was used to determine the relation betweentemporaldriftinsoilporesizedistributionparameters andWDcharacteristics.Theobjectivewastoobtainapredictive model for hydraulic parameter change over time driven by independent environmental variables. TheSAS procedure PROC REGwiththeRSQUAREselectionmethodwasusedtofindsubsets Table1

Soilpropertiesoftheexperimentalfield. Horizon Depth(cm) Sand(kgkg1

) Silt(kgkg1

) Clay(kgkg1

) TextureUSDA Corg(kgkg1) Fieldcapacity(cm3cm3) Wiltingpoint(cm3cm3)

A 0–40 0.19 0.57 0.24 SiL 0.025 0.32 0.15

AC 40–55 0.23 0.54 0.23 SiL 0.015 0.27 0.10

C >55 0.22 0.62 0.16 SiL 0.008 0.25 0.07

Fig.2.Soilwatercontentinthesurfacenearsoillayer(5cmsoildepth).Grayarea showsthestandarddeviation(n=9),verticaldottedlinesindicatemeasurement datesandnumbersdefineperiodsbetweeninfiltrationmeasurements.Arrows showperiodsoffrozensoil.Gapsareduetosensorremovalduringharvestand seedingoperations.

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of independent variables that best predicted the hydraulic parameters.We restrictedtounivariate andbivariatemodelsin ordertoavoidover-parameterizationandensuremodel interpret-ability.

BesideWDindicators(cycleintensity,numberandduration), someotherenvironmentalvariableswereincluded.Alongertime interval is likely to show higher temporal change. Thus the influence of the length of time separating two measurements (

D

ti,i+1)wastested.Theinitialvalueatticanalsoinfluencethe

subsequentdriftascertainhydraulicpropertyconfigurations(e.g. astatewithmoremacropores)mightbelessstableandtherefore undergohigher change. Therelation between initial value and subsequentdriftwasthereforeanalyzed.Alsohighersoilmoisture couldincreasestructuralinstabilityresultinginhighertemporal drift. This was tested by the influence of initial and average moisture. Beside a cyclic WD pattern, also a general trend of wettingor dryingcaninfluences hydraulic properties.Moisture trend,calculatedastheslopeofalinearregressionthroughwater contentvs.timebetween,andmeteorologicalindicatorsofwetting vs.dryingperiods(cumulativevaluesofET0,rainfallandclimatic

waterbalancedeficit)wereincluded.Theclimaticwaterbalance deficitwascalculatedasthecumulativesumofrainfallminusET0

overtime.

2.4.3. Modelapplicationandevaluation

The regressionmodel obtained fromtheaboveanalysis was then used to predict the temporal dynamics of pore size distribution parameters at a weekly time step. An initial soil watercontentseriesofthreeweekswasusedtoensureasufficient lengthofthetimeseriesforspectralanalysis.Thereaftertheseries wasincreasedstepwisewiththesubsequentsevendaysofwater contentmeasurements.Amainquestionwasatwhichvaluethe thresholdsfordrivingvariablesshouldbesetthatdeterminewhen hydraulicparametersareupdated.Wecalibratedthesethresholds based on the values which separated periods of statistically significantvs.non-significantdriftinmeasuredporeparameters.

Comparing measured and predicted parameters using varying thresholdsrevealedthatmeanvaluesattheperiodsofsignificant change in measured hydraulic parameters were the most appropriatetresholds.Wheneverthesethresholdswereachieved, soilhydraulicparameterswereupdatedbytheregressionmodel. Afterwardsanalysisrestarted withthesubsequentthree weeks dataasinitialtimeseries.

Thefunctional formofthetemporal driftbetween two data points cannot beanswered fromourdata. We applieda cubic hermite spline interpolation between data points using the MATLAB pchip-function to obtain a continuous time course of poreparameters.

Themodelwasevaluatedwithdifferentgoodnessoffitindices. Rootmeansquarederror(RMSE)isadimensionalsquaredstatistic fordifferencebetweenmeasuredandmodeledvalues.Modeling efficiency(EF)andtheindexofagreement(d)arebothextensions ofthecommonr2statisticsofregressionlines.EFcangeteither positiveornegativevalues,1beingtheupperlimit,whilenegative infinityis thetheoreticallower bound.EF values lower than 0 resultfroma worsefit thantheaverage of measurements.The valuesoftheindexofagreementliebetween0and1,with1being theupperlimit. Finally theslope andr2 between modeledand

measuredvaluesisindicated.Allindiceswerecalculatedusingthe IRENEsoftware(Filaetal.,2003).

3. Resultsanddiscussion

3.1. Temporalvariabilityofsoilporesizedistributionparameters

Table2givesasummaryoftheparametersofKosugi’sretention

modelobtainedbyinverseparameteroptimizationfromtension infiltrometermeasurements.Wefocusontheparameters describ-ing theshape of thepore sizedistribution (rm,Kosugi,

s

Kosugi). A

companionpaperofBodneretal.(2013)alsodemonstratedthat

u

s

showedonlyminortemporalchangesatsite. Thereforewejust consideredtheshapeparametersofKosugi’sretentionmodel. Fig.3.Spectralanalysisofwatercontenttimeseries.(a)Detrendingoftheinitialseries,(b)spectraldensityperiodogramoftheserieswithwhitenoisespectrumand95% confidencelimits,(c)wavefunctionofthedominantspectrum,and(d)reconstructedtimeseriesfromallsignificantspectra.

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Sˇimu˚nek et al. (1998) demonstrated that in the dry range retentioncurvesfrominverseestimationdeviatedfromlaboratory measurementswithapressureplateextractor.Theyshowedthat the inversely estimated curves could better reproduce a field measuredinfiltrationprocessinaforwardsimulation.Therefore weconsidertheinverseestimatesfromfielddataappropriateto describehydraulicproperties,particularlyforthestructuralrange whichwearestudyinghere.

Hayashi et al. (2006) demonstrated that Kosugi’s pore

parametersareproperindicatorsforstructuralporosity.Ahigh rm,Kosugifora givensoiltextureclassrevealstheimportanceof

macroporosity.Anarrowporesizedistribution(low

s

Kosugi)with

a high frequency of the dominant pore radius class is characteristic for less structured soils. Sˇimu˚nek (2006) gives Kosugi parameters fora range of texture classes. The average values we obtained by parameter optimization (hm,Kosugi

126.5cm,

s

Kosugi 1.98) were between those of sandy loams

(hm,Kosugi27.4cm,

s

Kosugi1.26)andsiltyloams(hm,Kosugi325.9cm,

s

Kosugi2.30)indicated by Sˇimu˚nek(2006). Wenoticethatthe

averagehm,Kosugi(126.5cm) hastobecalculateddirectlyfrom

the optimization results as for mathematical reasons ð1=nÞPð1=xÞ6¼1=ð1=nPxÞ

ð Þitcannotberecalculated fromthe

averagerm,KosugigiveninTable2.Thecoefficientofvariationwas

higherforrm,Kosugicomparedto

s

Kosugi.Thetemporalfactorwas

the dominant contribution to the overall variance and was significantforbothhydraulicparameters.Inaverage

s

Kosugialso

differed among soil cover treatments. However there was no interactionofthetreatmentmaineffectwithtime.Thereforethe useofmeanvaluesateachmeasurementpointprovidedagood representation of the soil specific parameter range and the temporaldynamicsatthesite(Fig.4).

FromFig.4atendencyofoverwinterincreaseofrm,Kosugiand

aconcomitantdecreasein

s

Kosugicanbeobserved.Over-winter

freezing–thawing has been described to induce aggregate breakdown(Oztas andFayetorbay,2003)whichwouldexplain structure homogenization as expressed by the reduction of

s

Kosugi. Unger (1991) described soil loosening over winter

leadingtohigheraggregatemeanweightdiameterandreduced bulk density. These processes could result in higher macro-porosityasobservedinourmeasurements.Duringthesummer monthadecreasingtrendinrm,Kosugiandanincreasein

s

Kosugi

could beobserved. This mightbe related tocapillary induced soilshrinkage reducingthemedianradius ofporeswhilepore heterogeneity increased by formation of microfissures (Leij etal.,2002).Duringtherestoftheseason,periodsofincreaseas well as decrease in hydraulic parameters were found with a particularly pronounced change between spring and early summer2010.

3.2. Wetting–dryingdynamics

Laboratoryexperimentsdemonstratedthedominantinfluence ofWDcyclesonhydraulicproperties(e.g.Pengetal.,2007).Also field studies with simulated rainfall and subsequent drying

(Mubarak et al., 2009) reported strong effects of WD. Under

naturalconditionsthecyclicpatternismorecomplexandirregular comparedtoinducedWD.Thisischallengingwhenstudyingthe impact on field soil properties.We appliedspectral analysis of watercontenttimeseriestoquantifycycleintensity,numberand duration fromspectral densityand wavelength.Fig.5givesthe spectraldensityperiodogramsshowingthecyclicpatternduring eachperiodbetweenhydraulicpropertymeasurements.

Allperiodshadcycleswithspectrasignificantlydifferentfrom whitenoise.Fig.5clearlyshowsthatthevalueofspectraldensity expressedthestrengthoftemporalfluctuationsofwatercontent (cf. period 1 vs. period 9). Periods with both low and high frequency water content fluctuations resulted in bimodal to multimodalspectralperiodograms(cf.periods7and8),although the secondary spectral peaks were frequently below the 95% confidencelimit(cf.period7).

Periodonetofiveaswellasperiod11hadadominantspectral peakatthelowestFourierfrequency,indicatingthattherewasone dominant WDcycle. Periodone had the lowestcycle intensity which is obviousregarding thelow water contentfluctuations. Periodthreetofiveand period11 onthecontraryhadallhigh spectralpeaksindicatinganintenseWDcycle.

Periodsixtotenshoweddominantspectraathigherfrequency, representingcyclesof shorter durationwith repeatedWD over time.Forexampleperiodeighthadamarkedbimodalperiodogram correspondingtotwo(firstpeak)andseven(secondpeak)cyclesof similarintensitythatoccurredduringthisperiod.

ThestrongestcycleintensitieswerefoundbetweenApriland June 2010and between November2011and April 2012.These periods were characterized by frequent rainfall events which Table2

Resultsofanalysisofvarianceforsoilhydraulicparameters.

rm,Kosugi(mm) sKosugi Statisticssummary Mean 0.077 1.98 SD 0.078 0.58 CV% 100.8 29.1 Levelofsignificance Coverage(C) NS * Time(T) *** *** Replicate(R) NS NS CT NS NS RT NS NS NSisnonsignificant. * Significantatp<0.05. *** Significantatp<0.001.

Fig.4.TemporalvariabilityoftheparametersfromKosugi’s(1996)waterretention model. Statistical comparison indicates if changes between two consecutive measurementdatesaresignificantatp<0.05(ns

nonsignificant,*significantat p<0.05,**significantatp<0.01,***significantatp<0.001).

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partially explained the intensity of the WD pattern (r2=0.51,

p=0.01).DuringOctober2010toJune2011therewereperiods withahighnumberofcycles(highfrequencyfluctuations).This season was substantially drier than the long-term average (176.6mmvs.360.5mm).Howevertherewasnometeorological variableotherthanthenumberofrainevents,whichhadonly anintermediater2,toreliablypredictthecyclicbehaviorofsoil

WD.Spectralanalysisthusprovidesauniquedrivingparameter for the analysis of soil processes and properties under field conditions.

3.3. Wetting–dryinginducedchangeinsoilporesizedistribution In a recent study of Bodner et al. (2013) on the same experiment,theydemonstratedthatwithin-seasonvariabilityof theporesizedistributionwasstronglyrelatedtoWD,while over-season dynamics were mainly influenced by soil mechanical disturbanceandcroprotation.

Following quantification of the WD pattern, we therefore analyzeditspredictivepowerfortemporalchangesinKosugi’sPSD parameters.BesideWD,alsotheinfluenceof(i)initialvaluesofthe respective hydraulic variable, (ii) different length of periods between two measurements, and (iii) other moisture related parameters (moisture trend, average moisture, initialmoisture, cumulativerain,ET0,climaticwaterbalancedeficit)wastested.

Table3showstheresultsofregressionanalysis.Forthebivariate

case,onlythebestmodelforeachparameterisreported. WDwasthebestsinglepredictorvariableforthetemporaldrift in both hydraulic parameters. Changes in rm,Kosugi were also

significantly influenced by the climatic water balance deficit. AlthoughtherewasnodirecteffectofaveragesoilmoistureonWD cycle intensity(r2=0.04), it can still modify its impacton soil

properties (Watts et al., 1996). We therefore introduced the averagesoilmoistureasaweightingfactor.Theconsistentincrease inr2confirmedtheassumptionthatWDeffectsonporeparameters

arestronglymediatedbytheprevailingmoistureconditions,with Fig.5.SpectraldensityperiodogramsofWDcyclesfortheperiodsbetweenhydraulicpropertymeasurements.Theunderlyingdetrendedwatercontentseriesisshowninthe rightcornerofeachperiodogram.

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decreasingimpactunderlowmoistureconditions.Wealsotested otherweightingfactorsforWDintensitysuchascyclenumberand cycleduration.Theunderlyingassumptionwasthatmorefrequent or longer cycles had a stronger impact. However this did not improvethepredictivepowerofcycleintensityalone.Itconfirms thedominantinfluenceofcycleintensityonporesizedistribution parameters,whilecyclenumberand durationbeingof subordi-natedimportance(Pengetal.,2007).

Asexpectedbivariateregressionmodelsachievedahigherr2

(cf. Table 3). The intercept in the bivariate models was

non-significant, while both predictor variables were significant. Therefore weused zero-interceptmodels.Beside the higherr2, the bivariate models also allow a better interpretation of the distinct variables driving increase vs. decrease in hydraulic parameters.Fig.6 showstheregressionmodelswithhighestr2

forthetemporaldriftintheKosugiparameters.

The change in PSD predicted by the regression models is resumedinFig.7.IntenseWDcyclesincreasedthemedianpore radius (+8.0% per unit cycle intensity), while the pore radius

standarddeviationdecreased(3.5%perunitcycleintensity).A prolongeddryperiod(indicatedbyahighET0andahighclimatic

waterbalancedeficitrespectively)ledtoareductionofthemedian pore radius(3.0% per10mm decreasein thewater balance deficit), whileslightlyincreasingporeradiusstandarddeviation (+1% per 10mm increase in cumulative ET0) with a higher

frequencyoffinepores.

AlsoPengetal.(2007)reportedageneralincreaseinporosity

(between2.6and16.5%dependingonclaycontent)withWDcycle intensityandhighestchangesinthemacroporefraction.Onthe otherhandLeijetal.(2002)showedthatdryingreducedstructural porosity due to aggregate coalescence. They also reported an increaseinfineporefrequency.Ourmodelsuggeststhatthecyclic patternofWDdrivestheformationofstructural(macro)porosity, whilecapillarydrivenaggregatecoalescenceisthepredominant processduringageneraldryingphaseincreasingtheamountof smallerporeclassesattheexpenseofmacropores.

We want to point out that theeffect of WD is expectedto strongly interact with other drivers of changes in structural porositysuchastillage.Aloosesoilaftertillagewillshowdifferent responsetorepeatedWDcomparedtoamorestableno-tillsoil (e.g.Pagliaietal.,2004).Alsodifferentsoiltextureswillrespond differentlytoWDasshownbyPengetal.(2007).

3.4. Predictionofporesizedistributionparameters

Theregressionmodelswereusedtopredictthetimecourseof Kosugi’sporeparameters.WDwascalculatedfromwatercontent data by spectral analysis with a weekly time step. ET0 and

cumulative water balance were obtained from meteorological data.Thethresholdvalueforthemoistureweightedcycleintensity wasset tosixfor both

Ds

Kosugi and

D

rm,Kosugi.Periods of

non-significantchangeinKosugiparametershadanaverageweighted cycle intensity of 3.8, while those periods showing significant changes had an intensityof 6.3. Thussix seemed a reasonable intensitythresholdtoupdatethehydraulicparametersbasedon theregressionmodel.ThresholdsforcumulativeET0weresetat

100mm (

Ds

Kosugi) and for climatic water balance deficit at

50mm (

D

rm,Kosugi). Fig. 8 shows the predicted temporal

dynamicsofthehydraulicparameterscomparedtotherangeof measureddata.

Generally thehydraulicpropertydynamicswerereproduced satisfactorilybythemodelwithaslighttendencytounderestimate themeasuredvalues.Amajordeviationbetweenthemodeledtime course and observed values occurred during autumn 2011 (measurement point in November 2011) where the model did notcapturethedecreaseinrm,Kosugiandtheincreasein

s

Kosugi.The

autumnseason2011wasparticularlydry(47.8mmvs.107.8mm long-term average rainfall). It is likely that the ET0-based

meteorologicalvariablesinourmodeldidnotsufficientlyreflect soilsurfacedryingandconcomitanthydraulicparameterdriftin thisperiod.

The deviationbetween themeasurement pointin December 2009andthemodeledtimecourseismainlyrelatedtotheproblem ofinterpolation.Themodelpredicatedthefirstupdateinhydraulic parametersforthe3rdFebruary2010withWDcyclehigherthan the set threshold. When linking the initial values with the calculateddatapointsatthisdatebyacubic splinehowever,it wasnotpossibletocapture theprolonged periodofunchanged poreparametersinthebeginning.Asmentionedabove,ourmodel isnotabletopredicttheexactfunctionalbehaviorbetweentwo datapoints.

Table4givesthegoodnessoffitindicesbetweenmeasuredand

calculatedhydraulicparameters.

Inhydrologicalmodelinggenerallystatichydraulicparameters areused.Theindiceshowevershowedclearlythatthecalculated Table3

Regressionmodelstopredictchangesinsoilhydraulicpropertyparameters.(Bold valuesindicatemodelswithallpredictorvariablesbeingsignificant.).

rm,Kosugi sKosugi Initialvalue 0.20 0.10 Periodlength 0.03 0.04 Cycleintensity 0.43 0.50 Cyclenumber <0.01 <0.01 Cycleduration 0.04 <0.01

Cycleintensityweighted 0.53 0.57

Averagemoisture 0.33 0.22

Initialmoisture 0.01 0.08

Sumrain >0.01 0.04

SumET0 0.18 0.18

Rain-ET0 0.43 0.10

Intensityweighted+rain-ET0 0.81 0.50

Intensityweighted+sumET0 0.74 0.78

Fig.6.Bivariateregressionmodelsbetweenenvironmentaldrivingforcesandthe temporaldriftintheparametersofKosugi’shydraulicpropertymodel.

(8)

hydraulicparametersareabetterrepresentationoftheobserved dynamicbehaviorthanusingaveragevalues.Amodelingefficiency (EF)greater0 indicates that theagreement between thesingle measuredandestimatedvaluesisbetterthanusingtheaverageof measurement.Thevaluesof0.58and0.60forEFthereforeconfirm thesubstantialimprovementin capturingthesystemdynamics when using dynamic parameters predicted by our model. This confirmstheconclusionofSchwenetal.(2011)thatthereliability ofwater transportsimulation couldbeimprovedwhen usinga dynamicinsteadofastatichydraulicpropertydescription. 4. Conclusions

Thisstudypresentsa quantificationofWD cyclesfromfield water content time series using spectral analysis. The method allowsextractingthebasiccharacteristicsofWD(cycleintensity, numberandduration)fromthecomplexandirregularpatternthat is typicallyobservedunder fieldconditions. WDcycleintensity was strongly related to thetemporal drift in the median pore radius and pore radius standard deviation of Kosugi’s water retentionmodel.ThisconfirmslaboratoryfindingsthatWDcycle intensityisadominantdrivingfactorofstructuralporositywhich isalsovalidunderfieldconditions.Theeffectofcycleintensitywas mediatedbysoilmoisture,withdrysoilreducingitsimpactonthe hydraulic parameters. Using a bivariate regression model we showed that WD intensity increased macroporosity while de-creasing pore heterogeneity. During a general drying phase, expressedinourmodelbyahighcumulativeET0orhighclimatic

waterbalancedeficit,themedianporeradiuswasreducedwhile poreheterogeneityincreasedduetohigherfrequencyofsmallpore radiusclasses.Thisprobablyreflectstheeffectofcapillarydriven aggregatecoalescence.Wedemonstratedthattemporalchangesin pore size distribution could be predicted from environmental variables. The modeled values captured the observed system dynamics substantiallybetterthan a static representationwith averaged parameters.Time seriesof water content or pressure head are frequently measured in hydrological field studies. Spectral analysis provides a method tomake additional use of suchmeasurementsbyextractingquantitativeinformationonthe Fig.7.DynamicsoftheporesizedistributiondrivenbywettinganddryingindicatorsaspredictedbytheregressionmodelsinFig.6.

Fig.8.Timecourseofsoilhydraulicparameters,predictedbytheregressionmodels showninFig.7,comparedtotherangeofmeasuredvalues(meansSD).

Table4

Goodnessoffitindicesformeasuredandpredictedhydraulicpropertyparameters.

rm,Kosugi sKosugi RMSE 0.035 0.29 EF 0.58 0.60 d 0.89 0.88 r2 (slope) 0.84(0.89) 0.86(0.96)

(9)

WDpattern.OurstudyconfirmedthatWDisanimportantdriverof within-seasonvariabilityofstructurerelatedsoilpropertiesand processes. Therefore the application of spectral analysis can enhance our understanding of pore and aggregate temporal dynamicsunder fieldconditions and provideanimportantlink tolaboratoryinvestigations.Furtherinvestigationscouldusethis methodforquantitativelyassessingtheinteractionsofWDwith otherrelevantfactorsdrivingtemporalchangesinthesoilporesize distributionsuchastillage,irrigationandcroprotation.

Acknowledgement

The present study was funded by the Austrian Science Foundation (FWF) by grant number P 21836-B16. The authors aregratefulforthefinancialsupportprovidedtotheirwork. References

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