Exploration for porphyry-style copper mineralisation near Llandeloy

Exploration for porphyry-style copper mineralisation near Llandeloy Exploration for porphyry-style copper mineralisation near Llandeloy

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(Table 2, no. 251, contains elevated levels of some chalcophile elements (Pb, Mo, As) which are perhaps indicative of weak epigenetic mineralisation. The erratic level of alkalis is considered to reflect alteration seen in thin section, but no regional pattern could be discerned with variation within one outcrop as great as across the whole area. Rock geochemistry, based on available outcrop sampling therefore failed to give any clear indication of the presence of disseminated mineralisat ion, a conclusion which agreed with the stream sediment sampling, but was in distinct contrast to the findings of a soil sampling survey and subsequent drilling. Stream sediment survey A stream sediment survey was carried out in the catchment of the Solfach, partly to look for indications of mineralisation and partly as an orientation study, to test the effectiveness of drainage sampling as a mineral exploration technique in this area of low relief with incised drainage, thick drift cover, sluggish streams and extensive contamination. Sampling and analysis Thirty five sites (Figs. 3, 4) were sampled for water stream sediment and panned concentrates. Stream sediment was wet-sieved at site to pass 100 mesh BSS (0.15 mm) using a minimum of water to retain the clay St. Brides Bey Figure 3 Location of drainage survey anomalies fraction. Samples were dried in the laboratory prior to grinding in a ball mill for 30 minutes. A 0.5 g split was analysed for Cu, Pb and Zn by atomic absorption spectro-photometry (AAS) following digestion in hot concentrated nitric acid for one hour. was determined by X-ray fluorescence spectrometry (XRF) followi~~g grinding of a 12 g subsample in a Itemat mill with 'elvacitel binder and pelletising. A further range of elements was determined by optical emission spectroscopy (OES). Detection limits were approxi- mately 1 ppm for Be; 2 pprn for As; 3 pprn for Cu; 5 ppm for Pb, B, Zn, Y and Sn; 10 ppm for V, Cr, Co and Ni; 20 ppm for Zr; SO pprn for Mn; 100 pprn for Ba and 0.5% for Fe. Constant volume panned concentrates of about 50 g were made at site from about 4 kg of -8 mesh BSS (2 mm) stream sediment. Following drying, a 12 g subsample was ground in a Itemat mill with 3g of 'elvacitel binder for five minutes prior to pelletising and analysis by XRF for a range of elements. Detection limits were 2 pprn for Mo and As; 3 pprn for Th and Zn; 5 pprn for Ni; 6 pprn for Mn and Cu; 9 ppm for Sn; 11 ppm for Sb; 13 pprn for Pb; 21 ppm for Ce and 27 pprn for Ba. A 30 ml water sample was collected in a plastic screw top bottle and acidified in the field with 0.3 ml perchloric acid. The sample was subsequently analysed by AAS for Cu and Zn without further sample preparation. Detection limits were approximately 0.02 ppm. Sample site showing tin content of panned

- 28 St. Brides Bay -

(Table 2, no. 251, contains elevated levels of some<br />

chalcophile elements (Pb, Mo, As) which are perhaps<br />

indicative of weak epigenetic <strong>mineralisation</strong>. The erratic<br />

level of alkalis is considered to reflect alteration seen in<br />

thin section, but no regional pattern could be discerned<br />

with variation within one outcrop as great as across the<br />

whole area.<br />

Rock geochemistry, based on available outcrop<br />

sampling there<strong>for</strong>e failed to give any clear indication of<br />

the presence of disseminated mineralisat ion, a<br />

conclusion which agreed with the stream sediment<br />

sampling, but was in distinct contrast to the findings of a<br />

soil sampling survey and subsequent drilling.<br />

Stream sediment survey<br />

A stream sediment survey was carried out in the<br />

catchment of the Solfach, partly to look <strong>for</strong> indications<br />

of <strong>mineralisation</strong> and partly as an orientation study, to<br />

test the effectiveness of drainage sampling as a mineral<br />

exploration technique in this area of low relief with<br />

incised drainage, thick drift cover, sluggish streams and<br />

extensive contamination.<br />

Sampling and analysis<br />

Thirty five sites (Figs. 3, 4) were sampled <strong>for</strong> water<br />

stream sediment and panned concentrates. Stream<br />

sediment was wet-sieved at site to pass 100 mesh BSS<br />

(0.15 mm) using a minimum of water to retain the clay<br />

St. Brides Bey<br />

Figure 3 Location of drainage survey anomalies<br />

fraction. Samples were dried in the laboratory prior to<br />

grinding in a ball mill <strong>for</strong> 30 minutes. A 0.5 g split was<br />

analysed <strong>for</strong> Cu, Pb and Zn by atomic absorption<br />

spectro-photometry (AAS) following digestion in hot<br />

concentrated nitric acid <strong>for</strong> one hour. was determined<br />

by X-ray fluorescence spectrometry (XRF) followi~~g<br />

grinding of a 12 g subsample in a Itemat mill with<br />

'elvacitel binder and pelletising. A further range of<br />

elements was determined by optical emission<br />

spectroscopy (OES). Detection limits were approxi-<br />

mately 1 ppm <strong>for</strong> Be; 2 pprn <strong>for</strong> As; 3 pprn <strong>for</strong> Cu; 5 ppm<br />

<strong>for</strong> Pb, B, Zn, Y and Sn; 10 ppm <strong>for</strong> V, Cr, Co and Ni;<br />

20 ppm <strong>for</strong> Zr; SO pprn <strong>for</strong> Mn; 100 pprn <strong>for</strong> Ba and 0.5%<br />

<strong>for</strong> Fe.<br />

Constant volume panned concentrates of about 50 g<br />

were made at site from about 4 kg of -8 mesh BSS<br />

(2 mm) stream sediment. Following drying, a 12 g<br />

subsample was ground in a Itemat mill with 3g of<br />

'elvacitel binder <strong>for</strong> five minutes prior to pelletising and<br />

analysis by XRF <strong>for</strong> a range of elements. Detection<br />

limits were 2 pprn <strong>for</strong> Mo and As; 3 pprn <strong>for</strong> Th and Zn;<br />

5 pprn <strong>for</strong> Ni; 6 pprn <strong>for</strong> Mn and Cu; 9 ppm <strong>for</strong> Sn;<br />

11 ppm <strong>for</strong> Sb; 13 pprn <strong>for</strong> Pb; 21 ppm <strong>for</strong> Ce and 27 pprn<br />

<strong>for</strong> Ba.<br />

A 30 ml water sample was collected in a plastic screw<br />

top bottle and acidified in the field with 0.3 ml<br />

perchloric acid. The sample was subsequently analysed<br />

by AAS <strong>for</strong> Cu and Zn without further sample<br />

preparation. Detection limits were approximately<br />

0.02 ppm.<br />

Sample site showing tin content of panned<br />

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