modification of soil structure of sand tailings: i...
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PenanikaJ. Tcop. Agric. Sc;. 18(2),83-88(1995) ISSN,012lHi128© Universiti Pertanian Malaysia Press
Modification of Soil Structure of Sand Tailings: I. Preliminary Study on theEffect of Organic Amendment and Iron on Soil Aggregation
A. M. MOKHTARUDDIN and M. NORHAYATIDepartment of Soil Science, Faculty of Agriculture,
Universiti Pertanian Malaysia, 43400 UPM Serdang,Selangor, Malaysia
Keywords: structure, sand tailings, amendment, aggregation
ABSTRAK
Keberkesanan efluen kiln.ng keln.pa sawit kering yang mengandungi 14 % karbon organik dan In.rutan besi daln.mmenggaln.kkan pengaggregatan di tanah pasir bekas lombong dikaji. Penambahan besi atau efluen ki/ang keln.pasawit kering pada kadar 20 dan 60 t hal tidak memberikan kesan bermi ke atas pengaggregatan dan kestabilantanah pasir. Pada kadar 100 thai, efluen kiln.ng keln.pa sawit memberikan kesan bermi ke atas kestabiln.naggregat. Dengan penambahan 0.1 % Fe, kadar eflum kilang keln.pa sawit kering yang diperlukan untukpengstabilan dapat diturunkan hampir separuh. Watau bagaimanapun darjah pengaggregatan masih rendah (%pengaggregatan > 2 mm - 5.6%). 1ni mungkin disebabkan kandungan pasir sangat halus dan kelodak adatahrendah iaitu hanya 5.8% dan ketiadaan lempung daln.m tanah pasir bekas lombm'g itu. Hasil kajian inimencadangkan untuk pembaihan struktur tanah pasir bekas lombong dengan menggunakan pembaik tanah,kehadiran juzukjuzuk tanah halus iaitu lempung dan kelodak dan/atau pasir halus datam hadar yang mencukupiadalah sangat perlu. Kehadirannya akan menyebabkan pembentukan stmktur yang kbih baik bagi tanah pasiroleh pemhaik lanah dan seterusnya l1U!71Jebabkan pembaikan ekonomi air dan nutrien lanah itu.
ABSTRACf
The effectiveness of dried palm oil mill effluent (decanter cake), which contains 14 % organic carbon, and ironsolution in promoting aggregation in sand tailing soil was determ;ned. The addition of iron (JT decanter cakeat rates oj 20 and 60 t h«l had no significant effect on the aggregation and stability of the sand. At a higherrate of 100 t h«l, decanter cake gave a significant effect on aggregate stability. With the addition of 0.1 % Fe,the rate of decanter cake application for effective stabilization was reduced to almost half. However, generally theextent of aggregatian was law (% aggregation>2mm was only 5.6%). This could be due to the low amount ofvery fine sand and sil~ amaunting to only 5.8%, and the absence oj clay in the sand tailings. It is postuln.tedthat an improvement in the soil structure of sandy tailings using amendments essentially requires the presence offine soil fractions viz. cln.y and silt and/or very fine sand in suffuient amounts. Their presence will kad to bettersoil structure Jonnation in the sand tailings by the amendments and hence to better water and nutrient economyof the soil.
INTRODUCTION
Large tracts of land are laid waste after tinmining opecations. In 1984, the total hectareageof tin mining lands in Peninsular Malaysia wasapproximately 113,700 ha (Chan, 1990). Eightypercent of this is sand tailings on which it isdifficult 10 establish vegetation because of theabsence of organic matter and the predominance of coarse materials leads to excessive drain-
age, low water and nutrient retention capacitiesand high surface tempecalUres (Lim et al., 1981;Shamshuddin et ai, 1986; Mokhtaruddin andWan Sulaiman, 1990).
Rehabilitation of sand tailings for agriculture can be based on three approaches. Theseare: improvement in soil \lIater economy by soilstructurization; raising the fertility status andreducing leaching losses by organic amendments;
A. M. MOKHTARUDDIN AND M. NORHAYATI
and lowering sUlface temperatures by mulching.Structurization can be achieved by adding organic matter. In Malaysia, palm oil mill effluent(POME), of which Malaysia produced about 18million tonnes in 1990. can be a potential sourceof organic matter. POME, if not utilized, cancause environmental pollution. The use of POMEto improve the physical conditions of mineralsoils has been reported by many authors (Lim etal., 1983; Wan Sulaiman et al., 1981) but its useto improve the structure of sandy soil is littlestudied. Besides organic matter, polyvalent metals such as iron (Fe) are knmvn to promoteaggregation and stability of soils (Deshpande etaL, 1968; Krishna Murti and Rengasamy, 1976).Further Mokhtamddin (1983) showed that interaction of organic matter and Fe has a synergisticeffect in improving aggregate stability.
The objective of this paper is to evaluate theeffectiveness of POME, alone or in combination\vith Fe, as a soil conditioner to promote soilaggregate formation in sand tailings.
MATERIALS AND METHODS
Soil
Sand tailings used were collected from theUniversiti Pertanian Malaysia tin-tailing researcharea. Particle size distribution was determinedusing the pipette method of Day (1965). Organic carbon content was determined by the wetdigestion method of Walkley and Black (Allison,1965). Free iron oxide was determined by thedithionite-citric-bicarbonate (DCB) method ofMehra and Jackson (1960). Soil pH was measured from 1:2.5 soil/water suspensions. The results are presented in Table 1.
Palm Oil Mill Effluent
The type of POME used was the decanter-driedraw POME (decanter cake). The decanter cakewas analysed for its nutrient and carbon contents. Nitrogen was determined by the normalKjeldahl method and P, K, Ca, Mg and Fe by thedry ashing method (Sharifuddin and Dynoodt,1981). The amount of N, P and K was measuredusing an autoanaIyser. and Ca, Mg and Fe withan atomic absorption spectrophotometer. Organic carbon was determined by the wet digestion method ofWalk1ey and Black (Allison, 1965).The results are presented in Table 2. Ferroussulphate was used as a source of Fe.
Experimentation
Air-dried sand «2mm, I020 g) in three replicates were treated with 0, 10.5. 31.4 and52.3 g of decanter cake which correspondedto an application rate of 0, 20, 60 and 100 tha· l . The sand-decan ter cake mixtures werethoroughly mixed and then sprayed with a0.1 % iron solution (ferrous sulphate) or distilled water (0% Fe) until field capacity.Samples were placed in a plastic bag andincubated for 48 hours at ambienttemperatures. After incubation they were airdried. The extent of aggregation was evaluated by the dry sieving technique. In the drysieving, 100 g of air-dried sample was placedon a nest of sieves with 8.00, 4.75, 2.80, 2.00,1.00, 0.50 and 0.30 mm openings. The sieveswere shaken manually in circular motion tentimes. Aggregates remaining on each sievewere weighed. The extent of aggregation wasexpressed as the fraction of air-dried aggregates >2mm (% aggregation> 2mm). Theaggregate stability was determined by the wetsieving technique of Yoder (1936). A 100 g ofair-dried sample «2mm) was placed on a 0.5mm size sieve. The sieve was shaken up anddown in water at a frequency of 40 oscillations per minute for 30 minutes. The heightof oscillations was 4 em. The aggregates remaining on tht7 sieve were dried and weighed.The aggregate stability was expressed as percent water-stable aggregates >0.5mm(%WSA>0.5mm) (Bryan, 1969).
RESULTS AND DISCUSSION
Extent of Aggregation
The sand tailings contain more than 99% sandand trace amounts of clay with negligible veryfine sand and silt fractions (Table 1), which areknmvn to act as the skeleton in aggregate formation (Emerson, 1959). This together withthe very low contents of organic matter andfree iron oxides made the sand tailingsstructureless.
Percent Aggregation > 2mm
Percent aggregation of the sand tailings 'was notaffected by the addition of iron or decanter cake(Table 3). Possible causes were (a) the lack ofvery fine sand and silt fractions which hinderthe formation of aggregates, and (b) the inert
84 PERTANlKAJ. TROP. AGRIC. SCI. VOL. 18 NO.2 1995
STRUCTIJRAL MODIFICATION OF SA1'1D TAILINGS BY ORGANIC AMENDMENT
TABLE IParticle size distribution and some of thechemical properties of the sand tailings
Content 1.14 0.17 0.99 1.19 0.24 0.139 14.4%
TABLE 2Carbon and nutrient contents of decanter cake
Fraction
Coarse sandMedium sandFine sandVery fine sandClaypHCarbonFree iron oxides
Tr = Trace
Element N p
Size (rom)
> 0.500.25 . 0.500.10 - 0.250.05 • 0.002
< 0.002
K Ca Mg
%
17.436.540.9
0.2Tr5.420.15Tr
Fe C
QUARTZ
Fig. 1: POSJibie !x:mds belWMn clay domains. organic: matter and sand parlicles in an aggregate. QuamOrganic Mauer-Quart, {Q-OM-Ql. {A/terEmer3on, /977{
A Quart'--&ganic Matter-Qua'" (Q:-OM-QIB Qua"'--&gani<: Matler-Cln)' Domain (Q:-OM-C]C Cia)' Domain-Organic: Matter-Polivalent Metal-Clay
Domain (C-OM-P-C]D Cla), Domain Edge-Clay Domain Face fC-C}
nature of the sand tailings. which contained morethan 99% sand, making the iron or decanter cakeineffective in promoting aggregation. Figure 1indicates that although the binding of quartzpartides by organic matter (Q-OM-Q) might havetaken place. the binding seemed weak and couldnOt resist the dry sieving process.
In combination with iron, only the highestrate of decanter cake application (IOO I ha-I )
showed a significant effect on the percent aggregation (Table 3).
Percent Water-stable Aggregates >O.5mm(%WSA>O.5mm)
Table 4 shows the effect of iron, decanter cakeand their combination on aggregate stabiltyo As
TABLE 3Comparison between mean percent aggregation of control and treaunems using LSD test
Treaunent
Control0.1% Fe20 t hao
! decanter cake60 t hao
! decanter cake100 t haol decanter cake20 t hao1 decanter cake + 0.1 % Fe60 t hao1 decanter cake + 001 % Fe100 t haol decanter cake + 0.1% FeLSD (5%)LSD (1%)
Mean % aggregationa
4.34.04.04.36.05.75.3
11.3
Difference from contro1b
-o.3n>-0.301
0.30'
1.70 •
1.401
1.0JU
7.0"4.366.05
a Average of 3 replicationsb ** = Significant at 1% le\·el. * = Significant at 5% le\'el, os = Not significant
PERTANlKAJ. TROP. AGRIC. SCI. VOL. 18 NO.2, 1995 85
A M. MOKHTARUDDIN AND M. NORHAYATI
TABLE 4Comparison between mean percent WSA > 0.5 mm of control and each of the treatments using LSD test
Treaunent
CoIlU·ot0.1% Fe20 t ha·1 decanter cake60 t ha-' decanter cake100 t ha-1 decanter cake20 t ha-' decanter cake + 0.1 % Fe60 t ha-' decanter cake + 0.1 % Fe100 t ha'\ decanter cake + 0.1 % FeLSD (5%)LSD (1 %)
Mean % aggregation> 2 mm~
23.321.723.024.733.027.333.333.7
Difference from conrrolb
1.6'".Q.3'"l.4ru
9.7""4.0m
10.0"lOA'·6.559.09
;I Average of 3 replicationsb ** = Significant at 1% level, * = Significant at 5% level, os "'" NO( significam
with percent aggregation, aggregate stability wasnot significantly affected by the addition of Fe.The addition of decanter cake at the rate of 20and 60 t ha·' slightly increased the stability of theaggregates but the increase was not significant. Atthe highest rate of 100 t ha·1
, decanter cake gavea significant increase in aggregate stability. This isin accordance with the known fact that organicmatter in adequate amounts is needed for theformation of water-stable aggregates. In combination with iron, the higher rates of decanter cakeapplication (60 and 100 t ha·') gave a significantincrease in the aggregate stability but the lowestrate of 20 t ha·' did not. It appears that theaddition of 0.1 % Fe was able to reduce theamount of decanter cake required for effectivestabilization implying that the interaction of ironand organic matter was partly responsible in aggregate stabilization in sandy soils. Giovanniniand Sequi (1976) suggested that iron fonns blidging between organic polymers (-OM-P-OM-),wbich binds the sand particles more strongly.
The above findings suggest that the combination of decanter cake and iron has a greatereffect than the decanter cake or iron alone onthe stability of aggregates in sandy tailings. However, the overall extent of aggregation resultingfrom this treatment was still low (average %aggregation> 2mm is 5.6%, Table 2). Previouswork has demonstrated a similar effect in thatthe addition of organic amendments to sandysoils failed to give positive response to the aggregation and stability of these soils (Lim et aL,1983; Othman el al., 1990). On the other hand,
when similar experiments were carried out onmineral soils, a significant increase in aggregation and stability was noticed (Mokhtaruddin,1983; Mokhtaruddin and Wan Sulaiman, 1987).
Figure 1 clearly shows that for good aggregation in the sand tailings, the presence of clay,silt and very fine sand fractions is indispensible.Clay particles is a well knmvn cementing material binding the skeletal materials, such as veryfine sand, together into aggregates (Peterson,1946; Kemper and Koch, 1966; Dixon, 1991).
CONCLUSION
Iron and organic matter are known as excellentaggregating and stabilizing agents in soils.Nevertheless,this smdy shows that the additionof iron or decaotered dried raw POME (decanter cake) at 20 and 60 t ha·' to the sandtailings (which complised more than 99% sand)had no effect on aggregation and stability. Athigher rates (100 t ha·'), decanter cake had apositive effect 00 aggregate stability. In combination with iron, the rate of decanter cakeapplication can be reduced to 60 t ha- I foreffective stabilization. However, the overall extent of aggregation resulting from the lattertreatment was low (% aggregation > 2mm =
5.6%). The most probable explanation was thelack of very fine sand and silt fractions, whichact as skeleton in the formation of aggregates,and the absence of claro which interacts withorganic polymer and polyvalent metal to form astrong bond. It is therefore postulated that thepresence of fine fractions in sufficient quantity
86 PERTANlKAJ. TROP. AGRIC. SCI. VOL. 18 NO.2 1995
STRUCTURAL MODIFICATION OF SAND TAILINGS BY ORGANIC AMENDMENT
is a prerequisite for soil structure improvementor development in sand tailings using amendments.
ACKNOWLEDGEMENT
The authors would like to record their utmostappreciation to Universiti Pertanian Malaysia andNational Council for Scientific Research andDevelopment of Malaysia for financial and technical support under the Intensification of Research Priority Areas (IRPA) Project No: 1-07-05
048 002).
REFERENCES
A!.uSOl", L.E. 1965. Organic carbon. In C.A. Blacket aL, (ed.) Methods of Soil Analysis. Part 2.Agronomy 9. ASA, Madison, Wisconsin, USA.p. 1367-1378.
BRYAN, R.B. 1969. The development, use and efficiency of indices of soil erodibility. Geoderma 2:5-26.
CHAN, Y.K. 1990. Tin mining land: an overview ofthe current situation in Peninsular Malaysia.Paper presented in the National Seminar on Exmining Land and Eris soil: Prospect and Profit.Kejora Management Services, ]5-]6 October1990, Kuala Lumpur.
DAY, P.R 1965. Particle fraction and particle sizeanalysis. In G.A. Black et al.,(ed.) Methods ofSoil Anal)'sis. Pan]. Agronomy 9. ASA, MadisionWisconsin, USA. p. 545-566.
DESHPANDE, T.L., DJ. GREENlAND, and J.P. QUIRK.1968. Changes in soil properties associated\'lith the removal of iron and aluminium oxides. fournal of Soil Sciellee 19: 102-108.
DIXON, J.B. 1991. Roles of clays in soils. AppliedCIa)' Scirnee, p. 489-503.
E~l£RSON, lA'.\V. 1959. The struCLUre of soil crumbs.Journal of Soil Scirnee 10: 235-243.
GIOVANINNI, G. and P. SEQUI. 1976. Iron and aluminium as cementing substances of soil aggregates. Journal of Soil Scirnce 4: 140-147.
KEMPER, W.D. and EJ. KOCH. 1966. AggregoteSiabilil)' of Soils from W«Iern US. and Calloda.USDA Tech. Bulletin 1355.
KRIsHNA MURTI, G.S.R., and P. RE~GASA.'IY. 1976.Role of amorphous minerals in aggregation offerruginous soils of India. Meded. Landb. Gent41: 407-420.
LIM, KH., L. MAENE, G. MAEssCHALK, and w.H. WANSULAIr.L.s.N. 1981. Reclamation of Tin Tailings jorAgriculture in Mala)'sia. Technical Bulletin, Faculty of Agriculture, Universiti Pertanian Malaysia, Serdang. pp. 61.
LIM, KH., BJ. Wooo, A.C. L<J, W.H. W,"~ SUlAJMAN,and S. MOHAMED. 1983. Land application ofdigested POME supernatant on oil palm usinga flatbed system. Prec. Seminar on Land Application of Palm Oil and Rubber Factory Effluents. (KH. Lim, A.T. Bachik and Y.C.Poon) Kuala Lumpur. Malaysian Society ofSoil Science. p. 163-169.
MEHRA, O.P., and M.L. JACKSON. 1960. Iron oxideremoval from soils and clays by dithionitecitrate sysIems buffered with sodium bicarbonate. Proc. 7th ConJ. Cla)'S and Cia)' Mineralsp. 317-327.
MOKHTARUDDll", A.M. 1983. Aggregation and StaMlityof Ultisols and Oxisols in Peninsular Mala)'sia.Thesis D. Agr. Sci., University of Gent, Belgium.
MOKHTARUDDIN, A.M. and W.H. \\-TAN SUWMAN. 1987.The use of palm oil mill effiuent in slopestabilization. Proceedings International Conference on Steepland Agriculture in the Humid Trapics(T.H. Tay, A.M. Mokhtaruddin and A.B. Zahari,eds.), Kuala Lumpur. p. 332-351.
MOKHTARUDDll", A.M. and W.H. WA'i SULo\1~lAN. 1990.Characteristics and improvement of ex-miningland. Paper presenIed in The National Seminaron Ex-mining Land and Eris Soil: Prospect andProfit. Kejora Management Setvices, 15-16 October 1990, Kuala Lumpur.
OTHMA.'i ABu BAKAR, A\DNUDDL"i YUSOFF, ABDUL RAsHID
AHMAD, ABo. AzIZ BIDIN, LEE CHONG SooN andLIM SOOl";G PER. 1990. Recent approach to fruittree cultivation on Sand tailing. Paper presented in The National Seminar on Ex-miningLand and Ens Soil: Prospect and Profit. KejoraManagement Services, 15-16 October 1990.Kuala Lumpur.
P£TERSON, J.B. 1946. The role of clay minerals inthe formation of soil structure. Soil Scimce 61:247-256.
SHA~iSHUDDJN, J., N.W. NIK MOKHTAR, and S.PARA.\{A,'W\'THA..'l. 1986. Morphology, mineralogy and chemistry of an ex-mining land inIpoh. Pertonika 9: 89-97.
PERTANlKAJ. TROP. AGRIC. SCI. VOL. 18 NO.2, 1995 87
A. M. MOKHTARUDDIN AND M. NORHAYATI
SHARffUDDIN. H.A.H. and R.P.F. DYNOODT. 1981. Basi<Guide to Soil and Plant Anal)'ses. Technical Bul·letin, Faculty of Agriculture, UniversitiPertanian Malaysia, Serdang_ pp. 48.
WAl' SULAI~l>\.."l. W.H., C.K MOK, S. ZuuunJ, andK.H. LIM. 1981. Improvementofdegmded landby the use of palm oil mill effiuent. ProceedingsNational Workshop on Oil Palm by Product Utiliz.ation, Kuala Lumpur. Malaysian Society of SoilScience.
YODER. RE. 1936. A direct method of aggregate analysis of soils and a study of the physical narure oferosion losses. Journal of the American Society ofAgronomy 28: 337-351.
(lUceiv,d 31 januar)' 1994; accepted 22 May 1995)
88 PERTANlKAJ. TROP. AGRlC. SCI. VOL. 18 NO. 2 1995