selenium as an indicato elemenr int geochemical …

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SELENIUM AS AN INDICATOR ELEMENT IN GEOCHEMICAL EXPLORATION TAPIO KOLJONEN KOLJONEN, TAPIO 1977: Selenium as an indicator element in geochemical exploration. Bull. Geol. Soc. Finland, 49 (2): 85—88. Selenium is always present in sulphide ores and can be used as an indicator element in the geochemical exploration of those ores. Being an anion selenium also gives information, e.g., about ore type, that cannot be obtained through the analysis of cations alone. When sulphides weather in acid soils selenium is oxidized to elemental form or to selenite, it is adsorbed onto colloids, and migrates with difficulty. Therefore, high selenium contents occur in colloid-rich sediments in restricted areas near sulphide mineralizations. The mineralizations can be located by analysing such sediments as gossan, till, lake and river sediment, and organic- and iron-rich layers in podzolic soil. Selenium content is increased also in vegetation grow- ing on selenium-rich soils but the increase observed has been small. When the pH of sediments is neutral or nearly neutral, e.g., in calcareous areas, selenium is oxidized to selenate, which form easily dissolves, and the anomaly near sulphide mineralizations is not as distinct as in acid soils. Tapio Koljonen, Department of Geology and Mineralogy, University of Helsinki, P.O. Box 115, SF-00171 Helsinki 17, Finland. (Address until 2. 11. 1979: University of Dar es Salaam, Department of Geology, P.O. Box 35602, Dar es Salaam, Tanzania.) Introduction Selenium replaces sulphur diadochially and hence is always present in sulphide ores and a common by-product when such ores are mined. Their geochemistries coincide in many respects since the ionic radii of Se and S are similar. In magmatic processes Se is more strongly enriched than S into late differen- tiates, together with elements such as As, Sb, Hg, and Ag, and is commonly found in high temperature volcanic emanations. Se partly separates from S is sedimentary processes where it is oxidized to elemental form or to selenite, while S is oxidized predominantly to sulphate. Geochemical exploration is usually based on the anomalous contents of cations. Se is one of the few anions that can be widely used. Its use as an indicator element has been increasing of late with the development of instrumental analytical methods (e.g. Crenschaw and Lakin 1974, Schnepfe 1974, Terada et al. 1975). When the concentration of Se in sulphide ores and nearby soils is 0.5 ppm or higher, it can be measured easily. The present report is based on earlier studies related to the general geochemistry

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Page 1: SELENIUM AS AN INDICATO ELEMENR INT GEOCHEMICAL …

SELENIUM AS AN INDICATOR ELEMENT IN GEOCHEMICAL EXPLORATION

TAPIO K O L J O N E N

KOLJONEN, TAPIO 1977: Selenium as an indicator element in geochemical exploration. Bull. Geol. Soc. Finland, 49 (2): 85—88. Selenium is always present in sulphide ores and can be used as an indicator element in the geochemical exploration of those ores. Being an anion selenium also gives information, e.g., about ore type, that cannot be obtained through the analysis of cations alone. When sulphides weather in acid soils selenium is oxidized to elemental form or to selenite, it is adsorbed onto colloids, and migrates with difficulty. Therefore, high selenium contents occur in colloid-rich sediments in restricted areas near sulphide mineralizations. The mineralizations can be located by analysing such sediments as gossan, till, lake and river sediment, and organic- and iron-rich layers in podzolic soil. Selenium content is increased also in vegetation grow-ing on selenium-rich soils but the increase observed has been small. When the pH of sediments is neutral or nearly neutral, e.g., in calcareous areas, selenium is oxidized to selenate, which form easily dissolves, and the anomaly near sulphide mineralizations is not as distinct as in acid soils. Tapio Koljonen, Department of Geology and Mineralogy, University of Helsinki, P.O. Box 115, SF-00171 Helsinki 17, Finland. (Address until 2. 11. 1979: University of Dar es Salaam, Department of Geology, P.O. Box 35602, Dar es Salaam, Tanzania.)

Introduction

Selen ium replaces su lphur diadochial ly and hence is a lways p resen t in su lphide ores and a common by-p roduc t w h e n such ores a re mined. The i r geochemistr ies coincide in m a n y respects since the ionic radi i of Se and S are s imilar . In magmat ic processes Se is more s t rongly enr iched than S into l a te d i f f e r e n -tiates, toge ther w i th e lements such as As, Sb, Hg, and Ag, and is commonly found in h igh t e m p e r a t u r e volcanic emanat ions . Se pa r t l y separa tes f r o m S is s ed imen ta ry processes w h e r e it is oxidized to e lementa l f o r m or to

selenite, whi le S is oxidized p redominan t ly to su lphate .

Geochemical explora t ion is usual ly based on the anomalous contents of cations. Se is one of the f e w anions t h a t can be widely used. Its use as an indicator e lement has been increas ing of la te w i t h the deve lopment of i n s t r u m e n t a l analyt ica l methods (e.g. Crenschaw and Lak in 1974, Schnepfe 1974, Te rada et al. 1975). W h e n the concent ra t ion of Se in su lphide ores and n e a r b y soils is 0.5 p p m or h igher , it can be measu red easily.

The p resen t r epo r t is based on ear l ier s tudies re la ted to the genera l geochemis t ry

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86 Tapio Koljonen

Table 1. Selenium content in some uranium ores, iron-rich oxidate sediments, and iron ores, mostly from Finland.

No. Sample Locality Se ppm

1 Uranium mineralization (pitchblende) in quartzite. U 3.8 °/o Eno, Paukkajanvaara 0.35

2 Uranium mineralization (pitchblende) in metadia-base. U 3.1 °/o Eno, Paukkajanvaara 0.41

3 Quartzite Eno, Paukkajanvaara 0.15 4 Carbonaceous shale, uranium ore. U 0.03 %> Sweden, Billingen 1.12 5 Cossan, containing jarosite Eno, Otravaara 21.0 6 Gossan, containing jarosite Eno, Otravaara 9.5 7 Gossan, containing jarosite Eno, Otravaara 5.3 8 Gossan, containing jarosite Eno, Otravaara 4.5 9 Gossan, containing jarosite Eno, Otravaara 4.3

10 Gossan Eno, Otravaara 1.7 11 Sand, cemented with Fe-hydroxides Eno, Otravaara 1.7 12 Gossan Eno, Otravaara 0.4 13 Iron ore, sedimentary USSR, Krivoi Rog 0.3 14 Oolitic iron ore BRD, Harzburg 0.2 15 Mn-rich iron ore, sedimentary Ylistaro, Vittinki 0.2 16 Hematite ore, magmatic Kemijärvi, Raajärvi 0.1

of selenium. The detai led resul ts h a v e been publ ished e l sewhere (Koljonen 1973a, b, c; 1974a, b, c; 1975a, b). In this paper the p rop-ert ies of Se tha t have proven use fu l in geo-chemical explora t ion are repor ted , toge ther wi th a f e w new analyses.

Sulphide ores

The most impor t an t su lphide ores in F in -land appea r to be h y d r o t h e r m a l or exha la -t ive - sed imenta ry in origin (cf., K a h m a 1973). Se len ium is enr iched into volcanic emana t ions and Se content is high, about 1—50 ppm in the economical ly most i m p o r t a n t su lphide ores. High Se content in sulphides can thus be t aken as an indicator of h y d r o t h e r m a l or igin or sed imenta t ion f r o m volcanic emanat ions . Th rough m e a s u r e m e n t of Se the ore type m a y be recognized even such indicator e lements as Cu, Co, W, and Zn are absent .

The average content of se lenium in the Ear th ' s crus t is 0.05 ppm. The content is in-creased in the rocks a round ore bodies and even in the igneous rocks cu t t ing the ore. The increase in igneous rocks is not easily

detected, however , because of the analyt ica l di f f icul t ies encountered .

In sed imen ta ry sulphides the S/Se ra t io is 30 000—50 000 in m a g n i t u d e and in Outo-k u m p u - t y p e ores and in carbonaceous schists 2 000—10 000 (Koljonen 1975b). The Se con-t en t in carbonaceous schists, l ike t h a t in su lphide ores, is about 10 ppm. The content is h igh because Se, as a nu t r ien t , is collected by organisms and also enr iched wi th organic de t r i tus du r ing sedimenta t ion .

Uranium ores

Selenium and u r a n i u m are prec ip i ta ted by organisms and organic colloids and a re o f t en found together in s ed imen ta ry rocks, e.g., in Paleozoic slates in Sweden (Table 1, No. 4).

Se seems to be enr iched wi th U in both sed imen ta ry and magmat i c ores. Häkli , Vuo-rela inen, and S a h a m a (1965) f o u n d n e w selenides in albi te diabases conta ining U, and Se is also enr iched in the small U ores found in quar tz i tes in Eno, S.E. F in land (Table 1, Nos. 1—3).

U explora t ion is most ly carr ied out by ana -

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Selenium as an indicator element in geochemical exploration 87

lyzing for U or measur ing the radia t ion. How-ever, increased Se content in rocks, e.g., in carbonaceous schists and sediments , indicates a reas f avo rab le for prospect ing.

Gossans

Se is enr iched into oxida te sediments and fo rms insoluble iron-selenites. I t is t he re fo re presen t in the wea the r ing products of sul-phide ores even w h e n most cations and S have been leached out (Table 1, Nos. 5—12). Through the analysis of Se in rus ty w e a t h e r -ing produc ts gossans can be ident i f ied and easily dis t inguished f r o m common oxida te sediments (cf., e.g., Kol jonen et al. 1976) and iron ores (Table 1, Nos. 13—16). Se concen-t ra t ion is usual ly h igher in s ed imen ta ry than in magmat ic i ron ores, because in exogenic processes Se in enr iched to iron hydrox ides and in endogenic processes to sulphides.

Sediments

Aroud sulphide ores, Se content is increased in all sediments conta ining colloids. In acid soils, such as podzols, Se behaves as a resist-ate, and the content is increased in till, clay, organic-r ich lake sediments — g y t t j a s and dys — and in podzols in top soil and the i ron-r ich B-horizon.

Vegetation

In Se-r ich areas, especially in the USA, p lan t species t ha t accumula te Se have been used as indicator p lan t s in u r a n i u m explo-ra t ion.

Se genera l ly migra tes wi th d i f f icu l ty in F innish soils and thus f a r no p lan t has been f o u n d to be an accumula tor . The concent ra-tion in dr ied p lants g rowing nea r or upon su lphide- r ich rocks is about 10 °/o of t ha t found in soil. The content nea r su lphide minera l iza t ions is increased b u t t h e increase is small .

In Ca-r ich soils the mobi l i ty of Se increases because of its oxidat ion and g rea te r solubil i ty. Se is more avai lable to p lan t consumpt ion than in podzolic soils and the contens is in-creased in vegetat ion. Subs tan t i a t ing this a re the Se poisonings observed in cat t le t ha t have consumed se leni ferous p lants in calcareous areas; e.g., in I re land (Walsh et al. 1951).

Dissussion

In acid soils Se is oxidized to e lementa l f o r m (Se3" Se°) and, behaving as a resistate, is adsorbed on colloids. In wea the r ing rock containing bases (e.g., s k a r n rocks) Se is oxi-dized to seleni te (Se° - > SeO:i

2") more readi ly than in podzolic soils (Kol jonen 1975a). If considerable iron is p resen t as in su lphide ores, seleni te is bound to the wea the r ing produc ts and does not mig ra t e even w h e n most cations and su lphur a re depleted in soils. Because of the low mobil i ty of Se in most F innish soils, anomalous ly high contents are found in res t r ic ted a reas nea r su lphide min-eral izat ions. For explora t ion purposes Se m a y analysed advan tageous ly in such colloid-rich sediments as i ron hydroxides , organic r ich soils, and tills. Se len ium anomalies in vege-ta t ion nea r sulphide mineral iza t ion seem to be weak .

An indicat ion of ore type m a y be achieved by de te rmin ing the S/Se rat io.

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88 Tapio Koljonen

References

Crenshaw, G. L. and Lakin, H. W. (1974) A sen-sitive and rapid method for the determination of trace amounts of selenium in geologic materials. J. Res. U.S. Geol. Surv. 2: 483—487.

Häkli, T. A., Vuorelainen, J., and Sahama, Th. G. (1965) Kitkaite (NiTeSe), a new mineral from Kuusamo, northeast Finland. Am. Min. 50: 581—586.

Kahma, A. (1973) The main metallogenic features of Finland. Geol. Surv. Finland, Bull. 265.

Koljonen, T. (1973a) Selenium in certain igneous rocks. Bull. Geol. Soc. Finland 45; 9—22.

— (1973b) Selenium in certain metamorphic rocks. Bull. Geol. Soc. Finland 45: 107—117.

— (1973c) Selenium in certain sedimentary rocks. Bull. Geol. Soc. Finland 45: 119—123.

— (1974a) Selenium in certain Finnish sediments. Bull. Geol. Soc. Finland 46: 15—21.

— (1974b) Behavior of selenium in silicic vein rocks and near granitic contacts. Bull. Geol. Soc. Finland 46: 133—138.

— (1974c) Selenium uptake by plants in Finland. Oikos 25: 353—355.

— (1975a) The behavior of selenium in Finnish soils. Ann. Agric. Fenn. 14: 240—247.

— (1975b) Behavior of selenium and sulfur in Svecokarelian sulfide-rich rocks. Bull. Geol. Soc. Finland 47; 25—31.

—, Lahermo, P., and Carlson, L. (1976) Origin, mineralogy, and chemistry of manganiferous and ferruginous precipitates found in sand and gravel deposits in Finland. Bull. Geol. Soc. Finland 48: 111—135.

Schnepfe, M. M. (1974) Spectrofluorimetric pro-cedure using 2,3-naphthalenediamine for deter-mining selenium in rocks. J. Res. U.S. Geol. Surv. 2: 631—636.

Terada, K., Ooba, T., and Kiba, T. (1975) Sepa-ration and determination of selenium in rocks, marine sediments and plankton by direct evolution with the bromide-condensed phos-phoric acid reagent. Talanta 22: 41—49.

Walsh, T., Fleming, G. A., O'Connor, R., and Sweeney, A. (1951) Selenium toxicity associated mith an Irish soil series. Nature 168: 881.

Manuscript received April 24, 1977.