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View of Chloride and sulphate solutions as extractants for soil P: III Effect of increasing sulphate concentration on P desorption 

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JOURNALOFTHESCIENTIFIC AGRICULTURAL SOCIETY OFFINLAND MaataloustieteellinenAikakauskirja

Voi. SS:363-369, 1983

Chloride and sulphate solutions

as extractants

for

soil P 111

Effect of increasing sulphate

concentration on P

de- sorption

HELINÄ HARTIKAINEN and MARKKU YLI-HALLA

Department

of

Agricultural Chemistry, University

of

Helsinki, 00710Hel-

sinki 71

Abstract. Theeffect ofincreasingsulphateconcentrationonPdesorption wasstudied in 102mineral

soil sampleswith; a) solutions ofaconstantionicstrengthI=o.l adjustedwithKCI andb) 0.1 Mand0.033 Msulphatesolutionsof differentionicstrengths. Further, the efficiency of chloride andsulphatesolutions of equalanionconcentration(0.1 M)was compared.

Ataconstantionicstrength, Pdesorptionwasenhancedasthesulphateconcentration of theextractant increased. Even despite amuch higher ionicstrength the extraction power of the K2S04solution was greaterthan thatof the KCI solution ofthesameanion concentration. Comparisonof the0.1 Mand0.033 M K2SO, solutions revealedin 53 soilsamples the extractabilityofPtobe depressedby anincreasein sulphate concentration(and ionic strength).In 49 samples,on the contrary,the0.1 M K2S04solution

extracted equalor greaterPamountsthan did the0.033 M K2S04.It wasobserved that the lower theP coverageonthe oxide surfaces in the soil was, the moreobviously thepromoting effect ofincreasing sulphate concentration overruled the depression inducedby increasing ionic strength, and the more superiorthe K2S04 solutionwas ascompared totheKCI solution.

Introduction

Indifferentanions depress the desorption of P from soilto solution (RYDEN

and SYERS 1975). The ionic strength created by sulphate is, however, found

not todecrease the desorptionas much as the same ionic strength createdby chloride (HARTIKAINEN and YLI-HALLA 1982a).

WIKLANDER and ANDERSSON (1974) have demonstrated the mobiliza- tion of P under field conditions to be promoted in autumn when the ionic strength is diminished. Their analyses ofsoil solution showed that in spring, after fertilization, the concentration of cations and anions at field capacity

was91—97 mmol/1,atwilting pointas highas 211 —307mmol/1. Fertilization caused a high concentration of Cl' ions,the ratio of Cl'to SO4 being about

10:1.

InFinland, a common fertilization practiceis toaddpotassiumtothe soil as KCI. For instance, the fertilizers sold during the period of July 1979 to

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June 1980 corresponded to the addition of Cl 44 kg/ha on an average,

whereas that ofS(mainly asK2S04and superphosphate)was only 13kg/ha.

Thus, the chloride-sulphate ratio can be expectedto be high at least inthe beginningofthe growth season which is usually dry and noleaching occurs.

In earlier papers (HARTIKAINEN and YLI-HALLA 1982 a and b) dealing with the extractability of soil P, the ionic strength of the extractants was

composed solely of K2S04 or KCI. The purpose of the present additional studywas toelucidate the effect of differentsulphate concentrations as well

as chloride-sulphate ratio in the extractants on P desorption from soil.

Further, chloride andsulphate solutions of equalanionic concentrationswere

briefly compared.

Materials and methods

The soilmaterial, 102 mineral soil samples, was the same described in the previous papers by

HARTIKAINEN and YLI-HALLA(1982 aand b).

SoilP was extracted withsolutions of differentconcentrations ofsulphate.Theextractants,equal in ionic strength(1=0.1),weremarked withroman numerals accordingtotheincreasing sulphate portions, and they had thefollowingconcentrations of salts:

solution K2S04cone. KCIcone.

I 0.100M

0.067M 0.033 M II

111 IV

0.011 M 0.022 M 0.033M

The effect ofaveryhigh sulphateconcentration wasstudiedbyextractingthesoils witha 0.1M K2S04 solutioncorresponding tothe ionic strength of0.3.

The soil-solutionratio was 1:60 (w/v) and desorption time 18hours. The soil suspensions were

centrifuged and filtered throughamembranefilter of0.2pm pore size.ThepHofthe clearextractantswas

measured and the solutionswereanalyzed forPbyamolybdenumbluemethod(ANON. 1969)and forCa byanatomic absorption spectrophotometer (acetylene-nitrous oxideflame).

ThetwopreviouspapersbyHARTIKAINENandYLI-HALLA(1982aandb)wereaimedatfindingoutsoil properties whichcontroltheeffectiveness ofvarious salt solutionsasextractantsforsoilP.Therefore the

soil sample materialwas divided into threecategories accordingto the order of efficiencyof different

solutions todesorb P. In the presentstudy, where attention was focused on the effect of sulphate concentration,thisgroupingseemed togiveno advantage. Thus,the conventional division accordingto soiltexturewasused.

Results

The effect of anion concentration on P desorption was studied by extractingthe soilsamples withK2S04andKCI solutionsoftheequalanionic concentration 0.1 M. The amounts ofP desorbed(mg/kg) from various soil textural classesare presented, with the confidencelimits at the95 % level,in thefollowing tabulation:

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KCI (1=0.1) K2S04(1=0.3) Heavy clays (n=l7)

Coarser clays (n=sl) Non-clay soils (n=34)

1.89±0.79 8.04±3.26 9.46±5.13

3.70±1.34 10.30±3.69 11.70±5.88

The results show theaverage desorption by theK2S04solution to have

been somewhatgreater. These solutions were, however, inequal in the con-

centration of potassium. Thus, in order to elucidate more accurately the effect of varying sulphateconcentrations on P desorption,itwas necessary to

eliminate the influence of cation exchange reactions. Therefore the ionic strength was adjusted to the constant level ofI=o.l.

Table 1 shows that, inspite of different anion and cation compositions, thesalt solutions ofthesame ionic strength exchanged equalquantities ofCa.

P desorption, on thecontrary, was enhancedasthe sulphateconcentration in the extractants increased (Table 2). This appeared in all the soil groups, but

very distinctly in the heavy clay soils. The increase in P desorption at each

step of the sulphate concentration was statistically significant at the confi- dence level of 99.9 %. Only in the heavy clay soils, where the quantities dissolved werelowand thus somewhat unreliable,the differencebetween the quantities dissolved by the solutions I and II remained statistically insignifi-

cant. In a given soil, an increase inthe P desorption at every concentration step was ofthe same magnitude.

As can be seen inTable 3,the extractants differed tosome extent in their acidity: the higher the sulphate concentration, the higher the pH value. The data show that generally thepH oftheextractdid notmarkedly deviatefrom that ofthe initial salt solution. However, in the heavy cla}r soils the leachate tended tobe a little more acid than the extracting solution.

Table 1. Ca(mg/kg) exchanged by solutions of differentSO] concentrations at ionic strength I=o.l Means withconfidencelimitsat95 %level.

Caexchanged by sulphatesolutions of

OM 0.011 M 0.022 M 0.033 M

Heavy clays 2250+393 2211 ±328 2216±324 2203±355

Coarserclays 1715±156 1720±155 1716±153 1720±156

Non-claysoils 1298±178 1319±184 1315±185 1272±195

Table2. P (mg/kg) extracted with solutions of different SO,’ concentrations at ionic strength I=o.l Means with confidence limitsat95 % level.

Pextracted withsulphate solutions of

OM 0.011 M 0.022 M 0.033 M

Heavy clays 1.9±0.8 2.2+1.2 2.7±1.4 3.0±1.4

Coarserclays 8.0±3.3 8.7±3.4 9.6±3.6 10.7±3.9

Non-claysolis 9.5±5.1 10.0+5.4 10.7±5.6 12.5±6.1

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Table3. pH of theextracts. Meanswithconfidence limitsat95% level.

pH of theextractsobtained by sulphate solutions of

OM 0.011 M 0.022 M 0.033 M

(pH 5.25) (pH 5.30) (pH 5.35) (pH5.45)

Heavyclays 5.02±0.22 5.04±0.23 5.11±0.22 5.2010.22

Coarserclays 5.2010.14 5.2310.15 5.3110.15 5.4010.14

Non-clay soils 5.1310.21 5.2910.21 5.3510.20 5.3410.19

In order toget somefurther informationabout the efficiencyofconcen-

trated sulphate solutions as extractants, the P quantities dissolved by 0.1 M K2S04 (1=0.3, above tabulation) and 0.033 M K2S04 (I=o.l, Table 2) were

compared. The data reveal that the solution of higher sulphateconcentration

tended to enhance desorption in heavy clay soils and to depress it in other textural classes.A closer examination showed, however,that in 49 outof 102 samples the markedincrease inionicstrength had eitherno effect whatsoever

or a promoting effect on the extractability of P. The result suggests the depressive effect of increasing ionic strength tohave been counteracted by

somefactors. These soil samples wererelatively poor in secondary phosph-

ates as compared to their content of sorption components. The differences between P amounts dissolved by 0.1 M and 0.033 M K2S04 were foundto

correlate closely with the molarratio ofNH4F-P and oxalate solubleAl, the

value of r being —0.86::!;':: (n=lo2). The correlation coefficient with the

molar ratio of NaOH-P/Fe was much lower(r= —o.s3***).

Discussion

Earlier tests of HARTIKAINEN and YLI-HALLA (1982 a and b) showed a

K2S04solutiontobe moreeffectiveas extractantforP thanaKCI solutionof the same ionic strength. In both solutions, a moderate increase in ionic strength reduced P desorption from soils rich in secondary phosphates but did not affect that from soils of lower P coverage on oxide surfaces. In the present study, the comparison of KCI and K2S04 solutions equal inanion

concentration (0.1 M) gavefurtherevidence ofthesuperiority ofthesulphate solution: inspite of much higher ionic strength,more P was extracted from all the soil groups. The result suggeststhat the effect ofthegreater extraction

power exceeded the depressive effect ofthe increased ionic strength.

The cation species and concentration are known to affect P desorption (HELYAR et al. 1976, BARROW and SHAW 1979). Therefore the effect of sulphate concentration was investigated also at a constant ionic strength (1=0.1). All the solutions of differentratios of CI7S04

exchanged equal quantities of Ca2+, whereas P desorption was enhanced as the sulphate concentration wasraised.

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The pH of the extraction solution somewhat increased with increasing sulphate concentration but hardly affected the extraction ability of sulphate solution. Sulphate is assumed to be sorbed as HS04 anion to the oxide surface(HINGSTON etal. 1972). If this occurred, theprotonation of sulphate would raise thepH ofthe solution. Theincrease inpH canbe expected tobe the greater, the higher the sulphate concentration is, because all the salt solutions obviously exchanged equal quantities of H+ ions to the solution.

However, especially inthe heavy clay soils,the mean pHofthe leachatewas lower than that ofthe extractantand the decreasewas ofthe samemagnitude

at every sulphate concentration step.

Thefacts discussed above allow toconclude that thedifference betweenP

amounts extracted by 0.1 M and 0.033 M K2S04 solutions isa net effect of three forces. Firstly, increasing ionic strength depresses desorption.

Secondly, increasing sulphate concentration enhances desorption. Thirdly, the cationic composition in leachatesis not equal,whichcauses anadditional effect, too. Apparently,the resultant being positive ornegative is dependent

on soil properties.

It is interesting tonotice thatinsoils ofhighP coverage on oxidesurfaces the net result of these reactions is a reduction in P extractability. In these soils,sulphate seems to behave like any indifferentanion when itsconcentra- tion israised. If a direct ligand exchange between sulphate and phosphate occurred, an increase in the sulphate concentration of the extractant would inevitably, according to the law of mass action, promote P desorption.

However, the observation made was just the reverse, which suggests the depressive effect of increasing ionic strength tobe dominating. On the other hand, in soils poor in phosphates, especially on the

A 1 oxide

surfaces, P

desorption is enhanced by an increase in sulphate concentration. In these soils,the extraction power of sulphateseems tobe able tooverrule the ionic strength action.

Similarly, thesuperiority ofK2S04solution ascompared toKCI solution dependson the waycomparison is made. In the soils oflow P coverage, the difference betweenP quantities dissolved in K2S04and KCI solutions ofthe same anion concentration gives the impression of a K2S04 solution to be even more superior than if the comparison is made on equal ionic strength basis. On the other hand, in the soils of high P coverage the comparison at

equal anion concentration lessens the apparent effectiveness of the K2S04

solution. Thus, when comparing the solutions at anion concentrationbasis, thedifferenceinthe extraction ability seems tobemoredecisively dependent

on soil properties.

The dissimilarresponse of the soil samples to increasing sulphate con- centration can be explained by the conclusions reached by HARTIKAINEN

and YLI-HALLA (1982 a and b). Hence, in soil samples of high P coverage

thereareonly sparselyH2O ligands exchangeable by sulphate. Consequently, sulphate is not able tomake the charge near the oxide surface more negative and to displace phosphate by increasing therepulsion. Further, owingtothe minor anion exchange, the ionic strength of an outer solution is hardly affected. On the otherhand, in the soils of low P coverage, ligand exchange

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between H2Ogroups and sulphatemaybe possible, leading tochanges inthe charge properties near the oxide surface.

The results of thepresent studyare in accord with the evidence of some

potexperiments:sulphatepromotesthe Puptakeby plants (e.g. SALONENet

al. 1968,MANCHANDA etal. 1982).Further studies are needed, however, to prove whether these findings are consequences ofincreased phosphatecon- centration in soil solution.

Acknowledgement.The authors wish tothanktheMaj and TorNesslingFoundation forsupporting thisstudy financially.

References

ANON. 1969.Juoma-jatalousveden tutkimusmenetelmät.Elintarviketutkijain Seura. 169p.Helsinki.

BARROW,N.J.&SHAW,T.C.1979.Effects of ionicstrengthandnatureof the cationondesorptionof phosphatefromsoil,J.Soil Sci.30;53—65.

HARTIKAINEN, H.&YLI-HALLA, M. 1982a.Chloride and sulphate solutionsasextractantsfor soil P. I. Effect ofionicspeciesandionicstrengthonP desorption.J.Scient.Agric. Soc.Finl.54;287- 296.

& YLI-HALLA, M. 1982 b. 11. Dependence of the relative extraction power of chloride and

sulphatesolutionson some soilproperties. J.Scient.Agric.Soc. Eini. 54: 297-304.

HELYAR, K. R., MUNNS,D. N.& BURAU, R. G. 1976. Adsorption ofphosphate by gibbsite. I.

Effects ofneutralchloride saltsof Ca, Mg,Na andK. J. Soil Sci.27; 307-314.

HINGSTON,F.J.,POSNER,A. M.&QUIRK,J.P. 1972.Anionadsorption by goethiteandgibbsite.

I. The role of the protonindetermining adsorption envelopes.J.Soil Sci.23; 177-192.

MANCHANDA,H. R„ SHARMA, S.K.&BHANDARI, D. K. 1982.Responseofbarleyandwheatto phosphorus inthe presence ofchloride andsulphate salinity.Plantand Soil 66:233-241.

RYDEN, J.C.&SYERS,J.K. 1975.Rationalization of ionicstrength andcationeffects onphosphate sorption bysoils.J.SoilSci. 26: 395—406.

SALONEN, M.,TÄHTINEN, H.,JOKINEN, R, & KERÄNEN, T. 1968. Kipsi moniravinteisten

lannoitteidenosana. Astiakokeidentuloksiavuosilta1961-65. Summary: Gypsumas aconstituent

of multi-nutrient fertilizer.Ann. Agric.Fenn. 7; 111-116.

WIKLANDER, L. &ANDERSSON, A. 1974.Thecomposition of the soil solution as influenced by fertilization and nutrient uptake. Geoderma 11:157-166.

MsreceivedMay6, 1983

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SELOSTUS

Kloridi- jasulfaattiliuokset maan fosforin uuttajina

111 Kasvavan sulfaattikonsentraation vaikutus P:n uuttumiseen Helinä Hartikainen ja Markku Yli-Halla

Helsingin yliopiston maanviljelyskemian laitos,00710Helsinki 71

Sulfaattikonsentraation vaikutusta fosforin uuttumiseen selvitettiin 102kivennäismaanäyt-

teen aineistolla. Näytteitä uutettiin neljällä K2S04 -liuoksella, joissa sulfaattikonsentraatio vaihteli0-0.033M ja joiden ionivahvuus oli säädetty 0.1 :ksi KCI-lioksella. Lisäksi selvitettiin fosforin uuttumista0.1 M ja0.033M K2S04-liuoksiin, joiden ionivahvuutta ei säädetty. KCl:n ja K2S(D4:n uuttotehoa verrattiinkäyttämällä liuoksia, joissa anionikonsentraatio oli 0.1 M, muttaliuosten ionivahvuudet olivat erisuuruiset.

lonivahvuuden ollessa vakio maanäytteistä uuttui fosforia sitä enemmänmitä korkeampi oli uuttoliuoksen sulfaattikonsentraatio. Puhtailla 0.033 M ja0.1 M K2S04-liuoksilla saadut tulokset osoittivat, ettävahvempi sulfaattiliuos uutti fosforia53 näytteestä vähemmän ja49 näytteestä jokoenemmän tai yhtä paljon kuin laimeampi liuos.

Tuloksista voitiin päätellä ionivahvuuden kasvun vähentävän ja sulfaattikonsentraation kasvun lisäävän P:n uuttumista. Liuoksen ionivahvuuden ja sulfaattikonsentraation samanai- kaisen kasvamisen nettovaikutus fosforin uuttumiseen riippuu maan ominaisuuksista. loni- vahvuuden suurenemisen aiheuttama desorption väheneminen näyttää olevan sitä vallitse- vampi, mitä korkeampi on maan Al-oksidipolymeerien fosforinkyllästysaste. Näytteissä,

joissaNLLF-liukoisen fosforin suhde oksalaattiuuttoiseen aluminiumiin oli pieni, sulfaatti- konsentraation kasvu lisäsi desorptiota enemmän kuin ionivahvuuden kasvu sitä vähensi.

Vaikka 0.1 M KCI-liuoksen ionivahvuus oli kolmasosa 0.1 M K2S04-liuoksen ionivahvuu- desta,sulfaattiliuos oli tehokkaampi P:n uuttaja. Erot uuttumisenmäärässäolivat sitäsuurem-

mat,mitä alhaisempi maanäytteenfosforinkyllästysaste oli.

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