An alternative approach to partial geochemical extractions: The Pink Leach

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1 An alternative approach to partial geochemical extractions: The Pink Leach Iain Dalrymple David Cohen Simon Gatehouse School of Biological, Earth and Environmental Sciences,

2 Location Mandamah

3 Mandamah

4 Mandamah Geology Cu-Au porphyry style mineralisation, possibly E. Silurian. Mineralisation hosted in quartz stockworks in coarse plagioclase-phyric quartz diorite. m 5 m m MACD 312 MHACD 228 m g/t Au.37 % Cu Mandamah looking North m Transported Clay Lower Saprolite Sericite-chlorite-magnetitealbite alteration Sericite-pyrite alteration

5 Mandamah Geology m of saprolite developed on the diorite. Area covered by ~5m?post Miocene clay-rich alluvium. Supergene Cu Au development at alluv-sap boundary. m 5 m m MACD 312 MHACD 228 m g/t Au.37 % Cu Mandamah looking North m Transported Clay Lower Saprolite Sericite-chlorite-magnetitealbite alteration Sericite-pyrite alteration

6 Mandamah Samples Grey to beige, massive and well sorted alluvium. >7% by weight clays and -18µm quartz fragments. Quartz and lithic fragments < 1mm. Carbonates both as cements and nodules at selected locations.

7 Mandamah Orientation Study Extensive survey performed with 5 leaches that did not display patterns of ore related metals definitively related to mineralisation. Significant variability seen in the traverses, particularly over and around structural features and the periphery of mineralisation. Subtle leaches appeared to offer the greatest variability that might be related to mineralisation., ppm 1, F mineralisation Acetate Ca Mg Ce Ba Mo Cu

8 Mandamah Orientation Study The distribution of many major and trace metals appears to be affected by the distribution of carbonates. The carbonate distribution may be a affected mineralisation but also may affect the redistribution of trace elements in the sample or extractability in the leach Mo(L) Ca(R) Pb(L) Ca(R) 45 4 acetate Mo / ppb acetate Ca / ppm acetate Pb / ppm acetate Ca / ppm

9 Mandamah Orientation Study It was concluded that we needed a weak leach that would be unaffected by local variations in the soil s capacity to consume acid or base. Buffering appeared to not offer the required control in the acetate buffer ph range. A leach was required that would be tailored for each sample while not taking an excessive amount of time or significantly affecting the natural background soil chemistry.

10 Pink Leach Theory In regions of uniform cover, local changes in a soil s buffering capacity may be a consequence of an active geochemical system. The Pink Leach is a Ca(NO 3 ) 2 based exchange leach with no chelating agents. The Pink Leach reacts all samples at the same ph irrespective of the sample alkalinity or acidity.

11 Pink Leach Chemistry Concentrated Ca(NO 3 ) 2 solution ~g/l. Neutral, acidic and alkaline Ca(NO 3 ) 2 solutions are prepared Trace concentration of phenol red in each Indicator with a ph range of 6.8 to 8.4 Equivalence point ph of 7.3 to 7.8 This indicator was chosen as ph slurries for samples distant to mineralisation at Mandamah are within this ph range and most metals are mobile This is now referred to as the PR-Ca(NO 3 ) 2 reagent.

12 Pink Leach - Method A standard solution is made at a known ph in the transition range for the indicator. Add ml of neutral PR-Ca(NO 3 ) 2 reagent to 1g of sample. The solution ph quickly equilibrates with the sample. If the solution is yellow, it is too acidic. If the solution is red, it solution is too alkaline. Acidic or alkaline PR-Ca(NO 3 ) 2 reagent is added in small measured quantities until the colour of solution matches the standard solution. The leachate is removed when the fine material flocculates, typically within 5 minutes.

13 Pink Leach - Results Addition of acid or base indicates a capacity to resist change in soil conditions Capacity to Resist Neutralization (CRN) No Sample Zones of acid generation. Zones of acid consumption

14 Pink Leach - Results Aliquot measurement is significantly different to a simple ph measurement on a slurry. ph measurements give an indication of the dominant acid-base species in a sample. The amount of acid or base required to neutralise a sample is a measure of the soil s capacity to generate base or acid. It is therefore a fundamental soil property rather than a consequence of soil solution interaction.

15 Pink Leach - Results High extractable mobile Al at all zones of non-neutrality. 14 Zones of acid generation correspond to zones of high Al extraction. Al / ppm Al(L) CRN(R) acid(r) aliq. base added aliq. base added Zones of acid consumption correspond approximately to zones of high Al extraction

16 Pink Leach - Results 6 Mo and W have a high extraction in the samples that generate acid. Mo / ppb 5 4 Mo(L) CRN(R) W / ppb W(L) CRN(R)

17 Pink Leach - Results 6 Mo and W also accumulate in the acid consumption zone between the acid generation zones. This may be a consequence of the limited directions for these elements to diffuse away. Mo / ppb W / ppb Mo(L) CRN(R) W(L) CRN(R)

18 Pink Leach - Results Au has a high extraction in the samples which generate acid. The high Au variability lies within the zone of non neutrality. Au / ppb Au(L) CRN(R) acid(r) The major Au peaks correspond to the high acid generation samples.

19 Pink Leach - Results In a selection of samples (blue), the extraction of mobile Au is related mobile Al. Local residual Au minima correspond to the alkaline generation zones Au / ppb Al / ppm

20 Pink Leach - Results In a selection of samples, the extraction of mobile Au is related mobile Al. Local residual Au minima correspond to the alkaline generation zones. 16 Residual Au / ppb Residual Au(L) acid(r) CRN(R)

21 Pink Leach Time Dependence Al quickly destabilises out of solution. Au, Mo and W also destabilise quickly out of solution, particularly over mineralisation. Patterns are obscured in a high background. Al / ppm Al / ppm brief leach long leach CRN brief leach long leach CRN minutes 4 hours

22 Pink Leach Time Dependence Al quickly destabilises out of solution. Au, Mo and W also destabilise quickly out of solution, particularly over mineralisation. Patterns are obscured in a high background. Mo / ppb Mo / ppb brief leach long leach CRN brief leach long leach CRN minutes 4 hours

23 Pink Leach Time Dependence Al quickly destabilises out of solution. Au, Mo and W also destabilise quickly out of solution, particularly over mineralisation. Patterns are obscured in a high background. W / ppb W / ppb brief leach long leach CRN brief leach long leach CRN minutes 4 hours

24 Pink Leach Time Dependence 22 Al quickly destabilises out of solution. Au, Mo and W also destabilise quickly out of solution, particularly over mineralisation. Patterns are obscured in a high background. Au / ppb Au / ppb minutes 4 hours brief leach long leach CRN brief leach long leach CRN

25 Pink Leach Other Leaches 8 The local acid-base conditions can be used to interpret the results other leaches. Fine detail which might otherwise be interpreted as variability is related to the local acid-base system. Au / ppb Mo / ppb Au acid CRN(R) Mo acid CRN(R) aliq. acid added aliq. base added aliq. base added aliq. base added

26 Pink Leach Local acid base variations are efficiently illustrated by the capacity of a sample to consume or generate acid. The theory behind this leach assumes that local acid base variations may be related to the movement of acid from an oxidising ore body at depth through local structures. This subtle leach appears to simply reverse these acid base processes.

27 Pink Leach If the background ph is different from 7.5 or a different suite of elements was targeted, an alternative indicator could be used. The acid base consumption can be used as an inexpensive field technique to screen for potential partial leach responses.

28 Pink Leach - Conclusions An understanding of how an individual sample location relates to the local geochemical system enhances the interpretability of the partial leach results. An anomalous response related to mineralisation was seen at Mandamah, where other techniques had failed.