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Geochem Evaluation of Waste Rock in Hollinger Mine

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GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Report prepared for: GOLDCORP - PORCUPINE GOLD MINES P.O. Box 70, 4315 Gold Mine Road South Porcupine, Ontario P0N 1H0 Report prepared by: ECOMETRIX INCORPORATED 6800 Campobello Road Mississauga, Ontario L5N 2L8 Ref. 07-1430 June 2008
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Page 1: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE

Report prepared for:

GOLDCORP - PORCUPINE GOLD MINES P.O. Box 70, 4315 Gold Mine Road South Porcupine, Ontario P0N 1H0

Report prepared by:

ECOMETRIX INCORPORATED 6800 Campobello Road Mississauga, Ontario L5N 2L8

Ref. 07-1430 June 2008

Page 2: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE

Original Signed By

Michael Venhuis, M.Sc., P.Geo. Project Manager

Original Signed By

Ronald V. Nicholson, Ph.D. Project Principal

Page 3: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Executive Summary

Ref. 07-1430 June 2008 i

EXECUTIVE SUMMARYA characterization study was completed for waste rock associated with the proposed open pit mining operations at the former Hollinger Mine in Timmins, ON. The investigation was focused on identifying and assessing potential environmental risks associated with waste rock from the proposed mining operation. Goldcorp collected and submitted over 80 diamond drill core samples for static testing, including metal content, Acid Base Accounting (ABA) and Synthetic Precipitate Leachate Procedure (SPLP) analyses. The samples were organized by rock type as identified by PGM geologists into groups including feldspar porphyry, mafic volcanics and various sedimentary lithologies.

The ABA results suggest that acid generation is not likely to be an issue with the waste rock generated from the proposed Hollinger Open Pit. There appears to be sufficient useful NP in all rock types to prevent acidification. Metal content analyses suggest that the key constituents of potential concern include antimony, arsenic and zinc. However, results of the SPLP tests suggest that most constituents of potential concern (COPC) appear to be relatively immobile and leachate concentrations were typically below laboratory detection limits. Arsenic and zinc have the highest leachate concentrations relative to water quality objectives and these results suggest further assessment of these COPCs.

Temporal trends in sulphate loadings from humidity cell testing on the argillite sediments are indicative of both flushing of soluble products from the rock and longer term oxidative release. The loadings of cobalt, molybdenum, selenium and zinc in the argillite sediments appear to be correlated with sulphate concentrations, and are indicative of rinsing of the rock (selenium and molybdenum) and longer term release due to oxidation (cobalt and zinc). Steady state loadings of cobalt and zinc from the argillite sediments averages about 42 and 520 kg/Mt/a, respectively, based on humidity cells with no adjustment for field conditions.

Arsenic loadings from the feldspar porphyries are indicative of flushing of residual arsenic from the surface of the rock. However, peak loading rates ranged between 2,600 and 4,680 kg/Mt/a for the two duplicate samples. The elevated arsenic levels are consistent with arsenic observations in tailings associated with the Hollinger and McIntyre mines.

Further assessment is required for the argillite sediments during the Hollinger Feasibility stage and should include evaluation of management options for the waste materials, including the potential for segregation of the various wastes, as part of the feasibility study. Volume estimates of each potential waste type should be completed to allow for estimation of the total loadings from the waste and to assist with the assessment of potential segregation strategies.

Page 4: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Table of Contents

Ref. 07-1430 June 2008 ii

TABLE OF CONTENTS

Page

EXECUTIVE SUMMARY........................................................................................................i

1.0 INTRODUCTION..................................................................................................1.1

2.0 WASTE CHARACTERIZATION AND CLASSIFICATION ..................................2.1

3.0 LABORATORY TESTING ...................................................................................3.13.1 Sample Selection .................................................................................................3.1 3.2 Humidity Cell Test Methods .................................................................................3.1 3.3 Humidity Cell Test Results ...................................................................................3.1

4.0 ENVIRONMENTAL IMPLICATIONS ...................................................................4.1

5.0 SHAFT WATER FROM THE EXISTING HOLLINGER UNDERGROUND MINE .................................................................................................................5.1

6.0 CONCLUSIONS...................................................................................................6.1

7.0 REFERENCES.....................................................................................................7.1

APPENDIX 1: Compilation of Metal, ABA and SPLP Data APPENDIX 2: Compilation of Humidity Cell Testing Data

Page 5: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Table of Contents

Ref. 07-1430 June 2008 iii

LIST OF TABLES

Table No.

2.1: Summary of Metal Contents in Waste Rock 2.2: Summary of Acid Base Accounting Results for Waste Rock 2.3: Summary of Synthetic Precipitate Leachate Procedure (SPLP) Testing Results for

Waste Rock

5.1: Summary of Hollinger Shaft Sludge Chemistry 5.2: Summary of Hollinger Shaft Water Chemistry

LIST OF FIGURES

Figure No.

2.1: Distribution of Sobek and Carbonate NP/AP with Sulphide Content in Hollinger Waste Rock Samples

2.2: Comparison of Sobek and Carbonate Neutralization Potentials

3.1: Modified Humidity Test Cell Set-up 3.2: Summary of Humidity Cell Testing Results for Selected Constituents of Concern

Page 6: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Introduction

Ref. 07-1430 June 2008 1.1

1.0 INTRODUCTION Goldcorp Canada Ltd. Porcupine Gold Mines (PGM) is currently evaluating the possibility of resuming mining operations at the former Hollinger Mine in Timmins, ON. PGM has been actively exploring the site over the past few years and has collected a substantial amount of diamond drill core. As part of the pre-feasibility study, PGM requires an assessment of the potential environmental issues related to drainage from potential waste rock associated with the open pit mine and implications for managing the waste rock.

EcoMetrix Incorporated (EcoMetrix) was retained by PGM to provide a preliminary characterization of the waste rock inventory for the proposed Hollinger Mine. The results of the investigation are intended to provide guidance for mitigation of the potential environmental issues related to drainage from waste rock, as appropriate, through classification and management of each of the waste rock types during the mining operation.

The overall objective of the program is to provide assistance with appropriate classification and management of each of the waste rock types during the mining operation. Specifically, the program was focused on identifying and assessing potential environmental concerns from waste rock from the proposed open pit mine. Once the rock types are classified in terms of potential environmental behavior, operational monitoring and management strategies will be required to provide cost effective and safe storage of waste rock for the long term.

This program involved characterization of the rock and assessment of the environmental implications of the various rock types. The data collected to date indicates that much of the waste rock will likely represent a low risk for environmental effects. However, there is potential for some of the waste rock to represent a higher risk to drainage quality. The results of the current testing assist in differentiating between the majority of low risk material and the minority of higher risk materials, and also assist in determining cost effective mitigation strategies for these higher risk rock types.

Page 7: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Waste Characterization and Classification

Ref. 07-1430 June 2008 2.1

2.0 WASTE CHARACTERIZATION AND CLASSIFICATION In 2006 a drilling program was initiated at the Hollinger Mine and carried out by PGM. Since then, PGM has submitted over 80 core samples, collected as approximately 1m sections, for static testing, including metal content, Acid Base Accounting (ABA) and Synthetic Precipitate Leachate Procedure (SPLP with 20:1 water:solids ratio).

The samples are organized by rock type identified by PGM geologists into groups including feldspar porphyries (F), mafic volcanics (VM) and various sedimentary lithologies (SS).

Results from the metal content analysis are summarized as minimum, maximum and geometric mean values in Table 2.1 and are compared to average crustal abundances for each potential constituent of concern. Results from the ABA and SPLP testing are summarized in Tables 2.2 and 2.3, respectively. Complete results as analyzed by SGS Lakefield Research Limited (SGS Lakefield) and provided by PGM are presented in Appendix 1.

Review of the ABA results (Table 2.2) suggest that the majority of rock samples will not be at risk for acid generation, with only 4 of the 80 samples (5%) categorized as possibly acid generating (Sobek-NP/AP ratios less than 2) based on criteria provided in BC Draft Guidelines (Price, 1997). An additional 4 samples exhibited ratios between 2 and 4, suggesting low potential for acid generation (Figure 2.1). All but one of these samples with low NP/AP ratios are of mafic volcanic lithology, and the other sample is a feldspar porphyry sample.

Based on the samples to date, there appears to be sufficient useful NP to prevent acidification, therefore, acid generation is not likely to be an issue with the waste rock generated from the proposed Hollinger Open Pit. This conclusion is further supported by data available from historical and current mining operations in the Timmins area (McIntyre, Hollinger, Pamour) for which there are abundant data for the historic tailings on surface in that area.

In general, carbonate NP values, which are calculated from the carbonate content of the rock material, are slightly greater than the Sobek NP values which are determined through laboratory titrations (Figure 2.2). This suggests that a small portion of the carbonate minerals either react slowly or may not provide any net neutralization capacity, as would be the case with iron or manganese carbonate.

Although the waste rock is not expected to pose an acid generation problem, assessment of metal leaching at neutral pH required consideration for the assessment and development of waste rock management strategies. The geometric mean of the arsenic content of the potential waste rock is 12.6 mg/kg, with antimony and zinc contents with geometric means of 0.4 and 148 mg/kg, respectively (Table 2.1). The geometric mean is 48 mg/kg for nickel

Page 8: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Waste Characterization and Classification

Ref. 07-1430 June 2008 2.2

and 53 mg/kg for copper. However, results of the SPLP tests (Table 2.3) suggest that most parameters appear to be relatively immobile as leachate concentrations were typically low and below laboratory detection limits, although the low concentrations may be a result of dilution due to the high water to solids ratio.

Based on screening criteria of 10x the average crustal abundance and SPLP testing, the results suggest that the key constituents of potential concern include antimony, arsenic and zinc. It is important to note that although the concentration of molybdenum in the solids is low (geometric mean=0.35 mg/kg), molybdenum was easily leached from some samples during the SPLP testing. The concentration of molybdenum leached during the tests ranged between 0.002 and 278 mg/kg. In addition, previous evaluations of mine tailings from the Hollinger area (McIntyre, former Hollinger Mine) suggest that leaching of cadmium, cobalt, copper, nickel, lead and selenium may also represent potential environmental risks. Although tailings geochemistry may be more representative of ore materials, the results from the historic mines provide an indication of constituents of potential concern that warrant further scrutiny.

Page 9: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Laboratory Testing

Ref. 07-1430 June 2008 3.1

3.0 LABORATORY TESTING As part of the pre-feasibility study for resuming mining operations at the Hollinger Mine, PGM requires an assessment of the potential environmental issues related to drainage from waste rock associated with the open pit mine. Characteristics of the waste rock have previously been investigated by PGM using ABA and SPLP testing, as described above. In order to further evaluate the waste rock at the Hollinger Mine, EcoMetrix completed laboratory studies in order to assess the leachability of metals from potential waste rock.

3.1 Sample Selection

Crushed rock samples from the 80 core segments used for the metals, ABA and SPLP analyses were delivered to EcoMetrix and divided into three composites, representing the three different rock types, feldspar porphyry (19 core samples), mafic volcanics (55 core samples) and argillite sediments (8 core samples). Each composite sample comprised of equal amounts of each core segment to create a 4kg sample. Two 1kg sub-samples of each composite were used for the humidity cell testing with the remaining composite material archived for further analysis, if required.

3.2 Humidity Cell Test Methods

The modified humidity cell test procedure involved weekly flushing and collection of leachate for analysis for the duplicate composite rock samples representing feldspar porphyries (F-1 and F-2), mafic volcanics (VM-1 and VM-2) and argillite sediments (SS-1 and SS-2). Approximately 1 kg (dry weight) of the crushed rock material was placed into the top portion of a high density polyethylene (HDPE) funnel (Figure 3.1). A layer of Nitex screen between two sheets of Whatman filter paper was placed in the bottom of the funnel, prior to rock addition, in order to retain the rock, while allowing for water to filter through. Each week, distilled water was poured over the rock and allowed to gravity drain into dedicated collection flasks. Samples were taken from the collection flasks and the conductivity and pH were measured immediately after sample collection. After sampling, the funnels were loosely covered with cellophane to prevent excessive evaporation and left undisturbed until the next sampling event. Leachate samples for metals analysis were filtered using (45 µm), acidified (nitric acid to pH < 2) and stored at 4 °C prior to submission for analysis. Samples collected for alkalinity/acidity were filtered and stored at 4°C prior to analysis. All samples were submitted to ALS Environmental Laboratories (ALS) in Mississauga, ON for analysis.

3.3 Humidity Cell Test Results

The results for the humidity cell test are presented in Figure 3.2. As the methods used for the humidity cell tests are consistent over time, the time trends for the loading rates of individual COCs are similar to the trends for concentrations, thus, loading rates are

Page 10: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Laboratory Testing

Ref. 07-1430 June 2008 3.2

presented as mg-metal/kg-tailings/week. Complete results of the humidity cell tests are provided in Appendix 2.

Although fluctuations were observed in the weekly pH measurements, the pH values of the leachate from all the samples generally ranged between 6.5 and 8.5. Some exceptions with respect to the general pH range existed during the initial stages of testing. Sample SS-2 exhibited an initial leachate pH of 6.2 on the first day of testing, while samples F-1, F-2 and VM-2 had pH values of between 8.5 and 9.0 on the first sampling event (Day 0).

Concentrations of antimony, copper, cadmium, nickel and lead in the humidity cell leachates were generally below detection limits for all samples over the course of the testing, and therefore are not discussed further in this section of the report.

The highest arsenic loading trends were observed in the feldspar porphyry samples, F-1 and F-2 (Figure 3.2), with maximum loadings of 0.092 and 0.05 mg/kg/wk, respectively, or between 2,600 and 4,680 Kg/Mt/a. All other samples had arsenic loadings less than 0.02 mg/kg/wk, with either a steady or slightly decreasing trend with time, with the exception of VM-2, which appeared to have slightly increasing trend during the first 15 weeks before exhibiting a slight decrease after 15 weeks.

Loadings of cobalt, molybdenum and selenium were generally below detection (0.0005, 0.001 and 0.005 mg/L, respectively) in all of the feldspar porphyry and mafic volcanic samples. However, concentrations were detected in the argillite sediment samples with cobalt loadings ranging between <0.0005 and 0.0016 mg/kg/wk and with no consistent trend over time. Concentrations of molybdenum were highest in the initial flushing of the humidity cells, with loadings of 0.011 and 0.007 mg/kg/wk for the SS-1 and SS-2 samples, respectively. Maximum selenium loadings of approximately 0.021 and 0.018 mg/kg/wk were observed within a few weeks of rinsing and decreased with further testing.

The loadings of zinc during the beginning of testing were below or near detection limits for the feldspar porphyry and mafic volcanic samples (F-1, F-2, VM-1 and VM-2). However, after about 15 weeks of testing, spikes in zinc loadings were observed, although the overall loading of the samples generally remained below 0.005 mg/kg/wk. Zinc loadings in the SS-1 and SS-2 samples exhibited a general increasing trend, with maximum loadings of about 0.017 and 0.012 mg/kg/wk, respectively.

Sulphate loadings were relatively constant and below 20 mg/kg/wk for the feldspar porphyry and mafic volcanic samples, with the exception of sample F-2 which exhibited increases after 14 weeks of testing (Figure 3.2). The argillite sediment samples had sulphate loadings ranging between 27 and 111 mg/kg/wk for sample SS-1 and 24 and 75 for sample SS-2. In general, sulphate loadings show an overall decreasing trend with time in the sediment samples.

Page 11: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Environmental Implications

Ref. 07-1430 June 2008 4.1

4.0 ENVIRONMENTAL IMPLICATIONS The humidity cell testing was completed to provide a screening evaluation for any potential environmental issues related to drainage from the waste rock arising from the proposed Hollinger Mine and was not corrected for field conditions. The investigation was intended to allow for identification of any additional screening of COCs and/or rock types that could be completed as part of the feasibility program for the proposed mine should results of this study suggest that environmental effects were anticipated.

The results of Humidity Cell testing in addition to the ABA results indicate that the potential risk for acid generation is low if rock is stored in large stockpiles on surface. All samples exhibited neutral pH values in the humidity cell leachate, providing no indication that the samples could go acidic during the test period. However, sulphate loadings were steady around 30 mg/kg/wk for the argillite sediments by the end of the testing period. The initial loading of sulphate is likely a result of flushing of sulphate contained on the rock as a result of oxidation during sample collection and processing (crushing) prior to testing. However, the constant loadings at the end of the testing are an indication of longer-term oxidation and suggest that sulphate is being produced and that sulphide minerals will be subject to ongoing oxidation. The sulphate loadings also suggest that other metals may be subject to ongoing release during oxidation.

Loadings of cobalt, molybdenum, selenium and zinc in the argillite sediments correlate with sulphate release, and represent both flushing of these constituents from the rock (selenium and molybdenum) and longer term release due to oxidation (cobalt and zinc). Steady-state loadings from the argillite sediment samples averaged around 0.0008 and 0.01 mg/kg/wk for cobalt and zinc, respectively, or about 42 and 520 kg/Mt/a, respectively.

Sulphate loadings from one of the two duplicate feldspar samples exhibited increases after 14 weeks, although the second duplicate sample had not yet exhibited this increasing trend in concentration at week 20. The observed increase suggests that longer-term oxidation may also be occurring for the feldspar material. However, there were no correlated metal releases observed with the increased sulphate release.

The observed trend in arsenic loadings for the feldspar material is consistent with flushing of soluble arsenic contained on the rock as a result of oxidation during sample collection and processing. In addition, the lack of correlation with sulphate in the same sample cells suggests that these concentrations have not resulted from oxidative leaching. None-the-less, peak arsenic loadings during the initial rinsing of the waste may represent an environmental concern, and should be re-assessed after waste inventories and water flow balances are better defined.

The metal loadings observed for the argillite sediments indicates a potential risk and suggests that further assessment is warranted in the feasibility study for the site to evaluate

Page 12: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Environmental Implications

Ref. 07-1430 June 2008 4.2

the management options for waste disposal. As part of the feasibility stage, an assessment of grade control should be completed, including screening of blast hole cuttings to allow for material identification and potential separation during drilling of potential metal leaching material.

Page 13: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Environmental Implications

Ref. 07-1430 June 2008 5.1

5.0 SHAFT WATER FROM THE EXISITNG HOLLINGER UNDERGROUND MINE

Concern for the water quality in the Hollinger shaft was expressed by Goldcorp personnel after excessive corrosion of the water pump was noted in 2008. The pump and associated steel parts required replacement after only one year of operation compared to the ongoing operation of a similar pump in the McIntyre shaft. Goldcorp requested that EcoMetrix assess the conditions that may be responsible for the conditions related to the pump corrosion in the Hollinger shaft. Samples of sludge were collected from the pump when it was removed for maintenance and sent for chemical analysis. Water samples from the shaft were also collected and analyzed.

The sludge sample contained approximately 39% iron and 9% sulphur (Table 5.1). The sulphur is the key to understanding the corrosion issue. It appears that the iron is corroded by the formation of FeS rather than iron oxide. The FeS is consistent with the appearance of the “black” coloured sludge.

The water samples support this hypothesis (Table 5.2). The water contains sulphate (600 to 2,700 mg/L) and therefore has a source of sulphur. Only one sample was analyzed for dissolved sulphide and that sample exhibited a concentration of 0.03 mg/L, a relatively high value for sulphide in water. In addition, the water had a neutral pH (7.4) and elevated alkalinity (460 to 580 mg/L and CaCO3). The neutral pH suggests that the water is not corrosive due to acidic conditions. The high alkalinity is consistent with sulphate reduction or the production of sulphide (dissolved or gas) during reactions between sulphate and some organic source.

It is understood that the current flow rate from the Hollinger shaft is relatively low (approximately 1,000 m3/d). This means that there is a long residence time in the shaft and adequate time for bacterial activity to mediate the sulphate reduction reactions. However, if mine dewatering is planned in the future, then greater pumping rates are anticipated and shorter residence times are expected. It is likely that greater pumping will not allow as much sulphate reduction and the potential for corrosion by this mechanism will decline. If small pumping rates are expected to continue, then stainless steel pumps or other mitigation (such as aeration of shaft water) should be considered.

Page 14: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE Conclusions

Ref. 07-1430 June 2008 6.1

6.0 CONCLUSIONS The following conclusions are based on the results of this investigation:

� ABA results indicate that the majority of the potential waste rock material is not likely to produce acid, with only 8 of the 80 samples having NP/AP ratios less than 4 and all samples exhibiting NP/AP values greater than 1;

� SPLP testing suggests that most parameters appear to be relatively immobile as leachate concentrations were typically low and below laboratory detection limits, although the low concentrations may be a result of dilution due to the high 20:1 water to solids ratio. Arsenic and zinc exhibited the highest leachate concentrations relative to water quality objectives;

� Constituents of Primary Concern include arsenic, cobalt, molybdenum, selenium and zinc;

� Temporal trends in sulphate loadings from humidity cell testing on the argillite sediments are indicative of both flushing from the rock and longer term oxidation;

� The loadings of cobalt, molybdenum, selenium and zinc in the argillite sediments appear to be correlated with sulphate concentrations, and are indicative of rinsing of the rock (selenium and molybdenum) and longer term release due to oxidation (cobalt and zinc);

� Steady state loadings of cobalt and zinc from the argillite sediments averages about 42 and 520 kg/Mt/a, respectively, based on humidity cells with no adjustment for field conditions;

� Arsenic loadings from the feldspar porphyries are indicative of flushing of residual arsenic from the surface of the rock. However, peak concentrations ranged between 2,600 and 4,680 kg/Mt/a for the two duplicate samples. The elevated arsenic levels are consistent with arsenic observations in tailings associated with the Hollinger and McIntyre mines.

� Further assessment is required for the argillite sediments during the Hollinger Feasibility stage and should include evaluation of management options for the waste material. In addition, segregation should be considered for various wastes as part of the feasibility study; and

� Volume estimates of each potential waste type should be completed to allow for estimation of the total loadings from the waste.

Page 15: Geochem Evaluation of Waste Rock in Hollinger Mine

GEOCHEMICAL EVALUATION OF WASTE ROCK – HOLLINGER MINE References

Ref. 07-1430 June 2008 7.1

7.0 REFERENCES Price, W.A. 1997. Draft Guidelines and Recommended Methods for the Prediction of Metal

Leaching and Acid Rock Drainage at Minesites in British Columbia. B.C. Ministry of Employment and Investment (note: Ministry of Employment and Investment was the former home of the present Ministry of Energy and Mines).

Page 16: Geochem Evaluation of Waste Rock in Hollinger Mine

ParameterAverage Crustal

Abundance (mg/kg) 1Minimum (mg/kg) Maximum (mg/kg)

Geometric Mean (mg/kg) 2,3

Felspar Porphyries (n=19)Antimony 0.20 0.20 2.90 0.66Arsenic 1 <2 91 15.3Cobalt 29 4.30 91.0 13.6Copper 75 1.80 96.0 10.4Iron 24,830 15,000 65,000 25,455Lead 8 2.50 178 16.6Molybdenum 1 0.08 24.0 0.44Nickel 105 7.20 91.0 26.4Selenium 0.05 <1 2 1Zinc 80 28 2500 192Mafic Volcanics (n=55)Antimony 0.20 <0.1 1.30 0.28Arsenic 1 <2 130 11.3Cobalt 29 18.0 100 38.7Copper 75 27.0 550 80.6Iron 24,830 39,000 147,000 68,945Lead 8 0.20 14 2.0Molybdenum 1 <0.05 12 0.30Nickel 105 13.0 300 60.1Selenium 0.05 <1 7 2Zinc 80 37 1800 112Sedimentary Lithologies (n=8)Antimony 0.20 0.60 2.70 1.07Arsenic 1 20 96 41.3Cobalt 29 32.0 60.0 39.2Copper 75 77 540 234Iron 24,830 30,000 108,000 67,296Lead 8 3.90 170 11.3Molybdenum 1 0.42 10 1.76Nickel 105 56 90 72.3Selenium 0.05 2 6 3Zinc 80 110 2900 978

Notes:1 - From Faure (1998) Geochemistry of Natural Waters. Prentice-Hall, Table A.10 pg. 5132 - Assumes a value equivalent to detection limit for values in data set reported less than detection3 - Bold values are more than 10 times average crustal abundance

Table 2.1Summary of Metal Contents in Waste Rock

Page 17: Geochem Evaluation of Waste Rock in Hollinger Mine

Parameter Units Minimum Maximum Geometric Mean

Feldspar Porphyries (n=19)pH --- 8.40 9.35 8.81Acid Generating Potential kg CaCO3/t 0.31 69.6 5.0Sobek Neuralization Potential kg CaCO3/t 48 284 167Carbonate Neutralization Potential kg CaCO3/t 64 331 206Sobek NP/AP --- 1.70 771 33.0Carbonate NP/AP --- 3.50 927 40.8Sulphide Sulphur % 0.01 2.23 0.16Total Sulphur % 0.06 2.72 0.24Sulphate Sulphur % <0.4 <0.4 <0.4CO2 % 2.94 19.6 10.8Mafic Volcanics (n=55)pH --- 8.44 9.86 9.21Acid Generating Potential kg CaCO3/t 0.31 65.3 3.82Sobek Neuralization Potential kg CaCO3/t 58 331 139Carbonate Neutralization Potential kg CaCO3/t 86 394 165Sobek NP/AP --- 1.30 1067 36.5Carbonate NP/AP --- 1.93 1272 43.3Sulphide Sulphur % 0.01 2.09 0.12Total Sulphur % 0.01 2.75 0.20Sulphate Sulphur % <0.4 <0.4 <0.4CO2 % 4.33 21.7 8.58Sedimentary Lithologies (n=8)pH --- 8.29 9.21 8.75Acid Generating Potential kg CaCO3/t 0.31 27 3.1Sobek Neuralization Potential kg CaCO3/t 85 263 162Carbonate Neutralization Potential kg CaCO3/t 122 310 212Sobek NP/AP --- 5.90 850 52.7Carbonate NP/AP --- 9.01 1000 68.9Sulphide Sulphur % 0.01 0.85 0.10Total Sulphur % 0.09 1.2 0.31Sulphate Sulphur % <0.4 <0.4 <0.4CO2 % 5.71 17.2 10.7

Table 2.2Summary of Acid Base Accounting Results for Waste Rock

Page 18: Geochem Evaluation of Waste Rock in Hollinger Mine

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90.

0000

20.

003

Cop

per

mg/

L0.

001

<0.0

001

0.00

160.

0004

0.4

Iron

mg/

L0.

3<0

.01

1.40

0.02

0.1

Lead

mg/

L0.

005

<0.0

002

0.00

220.

0005

40.

5M

olyb

denu

mm

g/L

0.04

0.00

019.

670.

409.

9N

icke

lm

g/L

0.02

5<0

.000

020.

0010

00.

0001

0.00

5S

elen

ium

mg/

L0.

1<0

.000

30.

0010

0.00

050.

005

Zinc

mg/

L0.

020.

003

0.25

20.

057

2.8

Sedi

men

tary

Lith

olog

ies

Ant

imon

ym

g/L

0.02

0.00

250.

0050

0.00

30.

2A

rsen

icm

g/L

0.00

5<0

.000

50.

0486

0.00

30.

6C

obal

tm

g/L

0.00

9<0

.000

010.

0002

30.

0000

40.

004

Cop

per

mg/

L0.

001

0.00

020.

0024

0.00

070.

7Iro

nm

g/L

0.3

<0.0

10.

180.

030.

1Le

adm

g/L

0.00

50.

0003

50.

0052

00.

0018

0.4

Mol

ybde

num

mg/

L0.

040.

0003

9.24

1.86

46.5

Nic

kel

mg/

L0.

025

<0.0

0002

0.00

080

0.00

010.

005

Sel

eniu

mm

g/L

0.1

<0.0

003

0.00

100.

0004

0.00

4Zi

ncm

g/L

0.02

0.00

60.

181

0.06

63.

3

Not

es:

1 - A

ssum

es a

val

ue e

quiv

alen

t to

dete

ctio

n lim

it fo

r val

ues

in d

ata

set r

epor

ted

less

than

det

ectio

n2

- Rat

ios

of le

acha

te c

once

ntra

tion

to P

rovi

ncia

l Wat

er Q

ualit

y O

bjec

tives

(PW

QO

) sho

wn

for s

cree

ning

inde

x on

ly -

ther

e ar

e no

regu

lato

ry li

mits

for S

PLP

resu

lts

Tabl

e 2.

3Su

mm

ary

of S

ynth

etic

Pre

cipi

tate

Lea

chat

e Pr

oced

ure

(SPL

P) T

estin

g R

esul

ts fo

r Was

te R

ock

Page 19: Geochem Evaluation of Waste Rock in Hollinger Mine

Sludge3-Mar-08

Antimony mg/kg <10 Arsenic mg/kg 710 Cobalt mg/kg 850 Copper mg/kg 630

Iron % 39 Molybdenum mg/kg 41

Nickel mg/kg 700 Zinc mg/kg 440

Sulphur % 8.98

Sample IDSample Date

Table 5.1Summary of Hollinger Shaft Sludge Chemistry

Page 20: Geochem Evaluation of Waste Rock in Hollinger Mine

Hol

linge

r Sha

ft Ta

nkH

ollin

ger S

haft

Tank

Hol

linge

r Sha

ft Ta

nkH

ollin

ger S

haft

Tank

Hol

linge

r Sha

ft29

-Jan

-08

5-Fe

b-08

25-F

eb-0

83-

Mar

-08

7-A

pr-0

8La

b pH

pH u

nit

7.25

7.33

7.42

7.32

7.42

Aci

dity

(pH

8.3

)m

g C

aCO

3/L

8966

.961

.652

.458

.9To

tal A

lkal

inity

mg

CaC

O3/

L58

446

046

745

545

9 S

ulph

ate

mg/

L27

2158

057

059

162

4To

tal S

ulph

ide

mg/

L0.

03TO

TAL

MET

AL S

Ant

imon

ym

g/L

<0.0

03<0

.003

<0.0

03<0

.003

Ars

enic

mg/

L0.

0061

0.05

510.

0525

0.06

530.

0633

Cob

alt

mg/

L<0

.000

50.

0163

0.01

110.

0168

Cop

per

mg/

L<0

.000

5<0

.000

5<0

.000

50.

0008

<0.0

005

Iron

mg/

L26

.412

.211

.311

.810

.1 M

olyb

denu

mm

g/L

0.00

74<0

.002

<0.0

02<0

.002

Nic

kel

mg/

L0.

0021

<0.0

005

0.00

470.

0057

0.00

36 Z

inc

mg/

L0.

0933

0.02

240.

0172

0.01

570.

0227

DIS

SOLV

ED M

ETA

LS A

ntim

ony

mg/

L<0

.003

<0.0

03<0

.003

<0.0

03 A

rsen

icm

g/L

0.00

320.

0495

0.01

570.

0144

Cob

alt

mg/

L<0

.000

50.

0161

0.01

640.

0158

Cop

per

mg/

L0.

0015

<0.0

005

<0.0

005

<0.0

005

Iron

mg/

L22

.510

.61

0.00

79 M

olyb

denu

mm

g/L

0.00

6<0

.002

<0.0

02<0

.002

Nic

kel

mg/

L0.

0041

<0.0

005

0.00

490.

0072

Zin

cm

g/L

0.07

220.

005

0.00

260.

0054

Sam

ple

Loca

tion

Sam

ple

Dat

e

Tabl

e 5.

2Su

mm

ary

of H

ollin

ger S

haft

Wat

er C

hem

istr

y

Page 21: Geochem Evaluation of Waste Rock in Hollinger Mine

0.1

1

10

100

1000

10000

0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0

Sulphide Content (%)

So

be

k N

P/A

P

Feldspar Porphyries

Argillite Sediments

Mafic Volcanics

0.1

1

10

100

1000

10000

0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0

Sulphide Content (%)

Ca

rbo

na

te N

P/A

P

Feldspar Porphyries

Argillite Sediments

Mafic Volcanics

NP/AP = 4

NP/AP = 3

NP/AP = 1

NP/AP = 4

NP/AP = 3

NP/AP = 1

EcoMetrix I N C O R P O R A T E D

Distribution of Sobek and Carbonate NP/AP with

Sulphide Content in Hollinger Waste Rock Samples

Goldcorp Canada Ltd. - Porcupine Gold Mines

April 2008 Figure 2.1

Page 22: Geochem Evaluation of Waste Rock in Hollinger Mine

EcoM

etrix

IN

CO

RP

OR

AT

ED

Co

mp

ariso

n o

f S

ob

ek a

nd

Ca

rbo

na

te

Ne

utr

aliz

atio

n P

ote

ntia

ls

Go

ldco

rp C

an

ad

a L

td.

- P

orc

up

ine G

old

Min

es

April 2008

Fig

ure

2.2

0

20

0

40

0

60

0

80

0

10

00

12

00

14

00

16

00

02

00

40

06

00

80

01

00

01

20

01

40

0

So

be

k N

P/A

P

Carbonate NP/AP

Mafic V

olc

anic

sF

eld

sp

ar

Po

rphyrie

sA

rgill

ite

Se

dim

ents

Carb

NP

= S

ob

ek N

P

Page 23: Geochem Evaluation of Waste Rock in Hollinger Mine

Tailings (inside funnel)

Connection for vacuum

Cellophane cover to

prevent evaporation

Leachate Collection Vessel

Layer of Nytex screen

between sheets of

Whatman filter paper

EcoMetrix I N C O R P O R A T E D

Modified Humidity Test Cell Set-up

Goldcorp Canada Ltd. - Porcupine Gold Mines

April 2008 Figure 3.1

Page 24: Geochem Evaluation of Waste Rock in Hollinger Mine

EcoMetrix I N C O R P O R A T E D

Summary of Humidity Cell Testing Results for

Selected Constituents of Concern

Goldcorp Canada Ltd. - Porcupine Gold Mines

April 2008 Figure 3.2

5.0

5.5

6.0

6.5

7.0

7.5

8.0

8.5

9.0

9.5

10.0

0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21

Week

pH

0

20

40

60

80

100

120

0 5 10 15 20 25

Week

Su

lph

ate

(m

g/k

g/w

k)

0

0.01

0.02

0.03

0.04

0.05

0.06

0.07

0.08

0.09

0.1

0 5 10 15 20 25

Week

Ars

en

ic (

mg

/kg

/wk)

0

0.0002

0.0004

0.0006

0.0008

0.001

0.0012

0.0014

0.0016

0.0018

0 5 10 15 20 25

Week

Co

balt

(m

g/k

g/w

k)

0

0.002

0.004

0.006

0.008

0.01

0.012

0 5 10 15 20 25

Week

Mo

lyb

den

um

(m

g/k

g/w

k)

0

0.005

0.01

0.015

0.02

0.025

0 5 10 15 20 25

Week

Sele

niu

m (

mg

/kg

/wk)

0

0.002

0.004

0.006

0.008

0.01

0.012

0.014

0.016

0.018

0 5 10 15 20 25

Week

Zin

c (

mg

/kg

/wk)

0

10

20

30

40

50

60

70

80

90

0 5 10 15 20 25

Week

Alk

alin

ity (

mg

CaC

O3/k

g/w

k)

SS-1 F-1 VM-1

SS-2 F-2 VM-2

Page 25: Geochem Evaluation of Waste Rock in Hollinger Mine

APPENDIX 1

Compilation of Metal, ABA and SPLP Data

Page 26: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDE

4146

20E

4146

88E

4165

07E

4300

13E

4468

47E

4463

35E

4463

36E

4463

37E

4463

45E

4463

66E

4463

53E

4463

54E

4463

55E

4463

56E

4463

57E

4463

58E

4463

59D

epth

From

109.

2015

4.70

96.8

032

0.00

11.0

0To

110.

2015

5.70

97.8

032

1.00

12.0

0

Lith

olog

yFP

FPFP

FPFP

Por

ph (M

T)P

orph

(MT)

Por

ph (M

T)P

orph

(MT)

Por

ph(M

T)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)U

nits

Solid

s C

onte

ntS

ilver

(Ag)

ug/g

0.26

0.37

0.23

0.30

0.30

0.36

0.47

0.35

2.3

0.89

0.59

0.45

0.41

0.70

0.64

0.81

0.44

Alu

min

um (A

l)ug

/g88

000

8900

049

000

7300

084

000

7600

067

000

7700

072

000

7900

078

000

7500

073

000

8100

081

000

7000

078

000

Ars

enic

(As)

ug/g

9116

1311

30<2

<2<2

1955

1628

3112

2423

10B

ariu

m (B

a)ug

/g30

029

022

040

025

032

016

034

028

037

060

056

039

070

019

045

028

0B

eryl

ium

(Be)

ug/g

0.8

0.9

0.6

0.9

0.8

0.8

0.6

0.9

0.9

0.9

0.8

0.8

0.9

1.0

1.1

0.5

1.1

Bor

on (B

)ug

/g17

963

107

95

139

283

511

87

78

Bis

mut

h (B

i)ug

/g0.

11<0

.06

0.26

<0.0

60.

29<0

.06

0.17

0.08

0.20

0.66

0.28

0.10

0.69

0.07

<0.0

60.

410.

08C

alci

um (C

a)ug

/g12

000

1400

019

000

3400

022

000

2700

054

000

2100

024

000

1600

019

000

2500

020

000

2700

018

000

3100

022

000

Cad

miu

m (C

d)ug

/g0.

430.

170.

100.

250.

240.

510.

320.

180.

400.

601.

30.

750.

550.

631.

71.

95.

5C

obal

t (C

o)ug

/g40

5.6

918.

66.

17.

225

4.8

4.3

1011

1117

1314

4425

Chr

omiu

m (C

r)ug

/g60

138.

417

1112

4713

9.0

7923

3794

3141

8620

Cop

per (

Cu)

ug/g

124.

82.

87.

46.

02.

996

1.8

3.3

149.

611

179.

818

8312

Iron

(Fe)

ug/g

1800

018

000

1600

024

000

2200

017

000

4700

016

000

1500

018

000

2200

025

000

4700

029

000

4000

065

000

3200

0P

otas

sium

(K)

ug/g

2100

021

000

1600

019

000

1700

013

000

9300

2400

022

000

2000

020

000

1700

020

000

2000

026

000

1300

021

000

Lith

ium

(Li)

ug/g

<5<5

525

<57

10<5

<5<5

1419

3728

2254

36M

agne

sium

(Mg)

ug/g

4500

4500

6400

1300

059

0087

0017

000

5800

4800

5300

1000

015

000

2400

014

000

1600

037

000

1600

0M

anga

nese

(Mn)

ug/g

850

600

750

440

1300

340

1300

1200

760

770

770

1400

1600

1300

2300

1900

1800

Mol

ybde

num

(Mo)

ug/g

240.

280.

240.

560.

270.

530.

560.

290.

114.

30.

200.

080.

331.

10.

260.

600.

26S

odiu

m (N

a)ug

/g31

000

3700

085

0011

000

4200

027

000

2400

021

000

2200

024

000

1900

015

000

6200

1200

065

0060

0079

00N

icke

l (N

i)ug

/g91

1018

2013

1240

7.2

9.2

2328

3876

2241

6725

Lead

(Pb)

ug/g

6.0

9.5

3.2

8.6

4.4

282.

55.

563

1434

1919

3482

5313

Ant

imon

y (S

b)ug

/g0.

60.

40.

30.

20.

52.

90.

90.

60.

40.

40.

30.

41.

50.

91.

12.

00.

8S

elen

ium

(Se)

ug/g

<1<1

<12

<11

1<1

<1<1

21

<11

11

<1Ti

n (S

n)ug

/g2.

40.

50.

40.

90.

41.

11.

30.

70.

90.

90.

70.

51.

30.

90.

70.

81.

3Ti

tani

um (T

i)ug

/g28

024

016

025

039

016

020

0035

027

038

021

019

016

023

021

015

017

0Th

aliu

m (T

l)ug

/g0.

70.

80.

30.

30.

50.

60.

20.

80.

50.

50.

50.

30.

40.

50.

50.

30.

4U

rani

um (U

)ug

/g0.

710.

590.

320.

780.

590.

810.

260.

520.

510.

500.

730.

730.

630.

790.

740.

280.

78V

anad

ium

(V)

ug/g

7021

2226

1720

8517

1640

2630

3726

3586

25Y

ttriu

m (Y

)ug

/g3.

13.

72.

55.

54.

35.

213

3.9

3.9

3.5

4.2

4.4

3.7

4.3

4.2

3.9

4.1

Zinc

(Zn)

ug/g

110

4239

8557

130

7428

100

170

650

340

290

260

730

880

2500

Page 27: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSo

lids

Con

tent

Silv

er (A

g)ug

/gA

lum

inum

(Al)

ug/g

Ars

enic

(As)

ug/g

Bar

ium

(Ba)

ug/g

Ber

yliu

m (B

e)ug

/gB

oron

(B)

ug/g

Bis

mut

h (B

i)ug

/gC

alci

um (C

a)ug

/gC

adm

ium

(Cd)

ug/g

Cob

alt (

Co)

ug/g

Chr

omiu

m (C

r)ug

/gC

oppe

r (C

u)ug

/gIro

n (F

e)ug

/gP

otas

sium

(K)

ug/g

Lith

ium

(Li)

ug/g

Mag

nesi

um (M

g)ug

/gM

anga

nese

(Mn)

ug/g

Mol

ybde

num

(Mo)

ug/g

Sod

ium

(Na)

ug/g

Nic

kel (

Ni)

ug/g

Lead

(Pb)

ug/g

Ant

imon

y (S

b)ug

/gS

elen

ium

(Se)

ug/g

Tin

(Sn)

ug/g

Tita

nium

(Ti)

ug/g

Thal

ium

(Tl)

ug/g

Ura

nium

(U)

ug/g

Van

adiu

m (V

)ug

/gY

ttriu

m (Y

)ug

/gZi

nc (Z

n)ug

/g

E44

6360

E44

6361

E44

6363

E43

1875

E43

1918

E42

9186

E42

9259

E42

9712

E43

0756

E47

1903

E41

4574

E41

4780

E41

4794

E41

6101

E41

6463

E42

8991

E42

9051

E42

9111

131.

6118

0.74

210.

5527

2.00

39.0

014

2.10

258.

0049

.60

83.2

012

7.80

122.

6545

.00

50.0

010

1.00

151.

0013

3.04

182.

0021

1.30

273.

0040

.00

142.

8525

8.98

50.6

084

.20

128.

8012

3.65

46.0

051

.00

102.

0015

2.00

Por

ph(P

LP)

Por

ph(P

LP)

Sed

SS

10S

S10

SS

8S

S8

SS

8S

S8

SS

8V

MV

MV

MV

MV

MV

MV

MV

M

0.74

1.3

0.45

0.77

1.2

0.52

0.64

0.60

0.55

4.3

0.25

0.18

0.14

0.43

0.19

0.24

0.08

0.15

7200

075

000

7400

053

000

3800

055

000

7600

064

000

8300

039

000

7000

058

000

6300

061

000

5700

075

000

6600

071

000

2330

5333

2034

3161

9639

3815

927

846

205

540

360

320

200

2024

063

040

063

021

012

012

083

4921

280

180

110

0.9

1.0

0.7

0.8

0.3

0.5

0.5

0.6

1.6

0.3

0.2

0.2

0.1

0.2

<0.1

0.6

0.4

0.4

57

513

1112

2015

67

1211

67

34

134

0.09

0.13

<0.0

60.

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0

Page 28: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSo

lids

Con

tent

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er (A

g)ug

/gA

lum

inum

(Al)

ug/g

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enic

(As)

ug/g

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ium

(Ba)

ug/g

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yliu

m (B

e)ug

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oron

(B)

ug/g

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mut

h (B

i)ug

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um (C

a)ug

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ium

(Cd)

ug/g

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alt (

Co)

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omiu

m (C

r)ug

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oppe

r (C

u)ug

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n (F

e)ug

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sium

(K)

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ium

(Li)

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nesi

um (M

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nese

(Mn)

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ium

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kel (

Ni)

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imon

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ium

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ium

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Page 29: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSo

lids

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tent

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er (A

g)ug

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inum

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enic

(As)

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ium

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yliu

m (B

e)ug

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oron

(B)

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mut

h (B

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um (C

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ium

(Cd)

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alt (

Co)

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omiu

m (C

r)ug

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oppe

r (C

u)ug

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n (F

e)ug

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sium

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ium

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nesi

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ium

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kel (

Ni)

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imon

y (S

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ium

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nium

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ium

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nium

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89

Page 30: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSo

lids

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tent

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er (A

g)ug

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inum

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enic

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ium

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yliu

m (B

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oron

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mut

h (B

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um (C

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ium

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alt (

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omiu

m (C

r)ug

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r (C

u)ug

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n (F

e)ug

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sium

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ium

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nesi

um (M

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ium

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Nic

kel (

Ni)

ug/g

Lead

(Pb)

ug/g

Ant

imon

y (S

b)ug

/gS

elen

ium

(Se)

ug/g

Tin

(Sn)

ug/g

Tita

nium

(Ti)

ug/g

Thal

ium

(Tl)

ug/g

Ura

nium

(U)

ug/g

Van

adiu

m (V

)ug

/gY

ttriu

m (Y

)ug

/gZi

nc (Z

n)ug

/g

E44

6344

E44

6348

E44

6349

E44

6350

E44

6351

E44

6352

E44

6362

E44

6365

E55

6364

E44

6346

E44

6347

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c (C

ntl)

Vol

c (C

ntl)

Vol

c/S

edV

olc/

Sed

0.20

0.18

0.17

0.28

0.16

0.18

0.26

0.15

0.34

0.20

0.19

6400

059

000

6300

063

000

6600

059

000

7000

064

000

6700

070

000

6200

010

23<2

74

415

2718

53

180

200

1624

045

250

210

110

170

170

180

0.4

0.2

0.3

0.4

<0.1

0.3

0.6

0.3

0.3

0.5

0.4

4<3

45

<3<3

86

7<3

<3<0

.06

<0.0

6<0

.06

<0.0

60.

24<0

.06

<0.0

60.

09<0

.06

<0.0

6<0

.06

5200

042

000

3500

041

000

5500

049

000

4000

069

000

6200

036

000

4100

00.

130.

130.

180.

160.

090.

140.

140.

220.

260.

100.

1336

3637

3741

3252

4037

4342

2447

5150

6239

7065

8628

2086

4469

8611

042

5996

7798

8074

000

9200

094

000

7500

083

000

8500

087

000

7800

072

000

7700

082

000

8000

7700

220

8000

2700

1000

012

000

6800

7200

5900

5900

1219

1419

3313

3629

2925

2520

000

2900

029

000

1600

032

000

1900

016

000

2600

031

000

1800

020

000

1400

1500

1300

1100

1400

1500

1300

1500

1300

1100

1300

0.32

0.24

0.22

0.29

0.08

<0.0

50.

461.

32.

20.

410.

1418

000

1300

023

000

1900

015

000

1700

019

000

1000

011

000

1500

011

000

4546

4545

6038

4966

6671

640.

81.

50.

61.

91.

80.

83.

01.

310

0.7

0.8

0.1

1.3

0.6

0.3

0.2

<0.1

0.7

0.4

0.3

0.4

0.2

22

<12

22

1<1

12

10.

40.

30.

60.

40.

20.

30.

70.

80.

50.

50.

326

025

056

0029

013

039

061

023

042

042

034

0<0

.10.

1<0

.10.

1<0

.1<0

.10.

2<0

.1<0

.10.

30.

20.

060.

050.

090.

060.

010.

060.

150.

030.

150.

060.

0695

100

120

100

120

9910

021

018

014

014

05.

96.

225

6.6

3.1

7.0

7.2

3.4

3.5

6.4

6.5

7586

120

9311

088

8213

013

011

010

0

Page 31: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDE

4146

20E

4146

88E

4165

07E

4300

13E

4468

47E

4463

35E

4463

36E

4463

37E

4463

45E

4463

66E

4463

53E

4463

54E

4463

55E

4463

56E

4463

57E

4463

58E

4463

59D

epth

From

109.

2015

4.70

96.8

032

0.00

11.0

0To

110.

2015

5.70

97.8

032

1.00

12.0

0

Lith

olog

yFP

FPFP

FPFP

Por

ph (M

T)P

orph

(MT)

Por

ph (M

T)P

orph

(MT)

Por

ph(M

T)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)U

nits

SPLP

Che

mis

try

Alu

min

um (A

l)m

g/L

2.55

2.35

0.83

0.80

0.67

0.49

50.

576

0.70

00.

686

0.49

80.

353

0.56

00.

440

0.42

10.

330

0.51

0A

rsen

ic (A

s)m

g/L

0.06

040.

0107

0.01

760.

0206

0.01

400.

0018

0.00

730.

0181

0.02

680.

0104

0.04

500.

0703

0.01

390.

0025

0.00

880.

0022

Silv

er (A

g)m

g/L

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

Bar

ium

(Ba)

mg/

L0.

933

0.87

00.

766

0.85

80.

244

0.67

30.

656

0.74

10.

694

0.66

10.

699

0.64

30.

851

0.78

20.

849

0.71

9B

eryl

ium

(Be)

mg/

L0.

0001

80.

0000

80.

0000

80.

0000

5<0

.000

04<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4B

oron

(B)

mg/

L0.

486

0.42

20.

406

0.57

10.

007

0.29

50.

251

0.26

10.

324

0.41

40.

350

0.36

50.

481

0.41

30.

393

0.43

6B

ism

uth

(Bi)

mg/

L0.

0000

5<0

.000

02<0

.000

02<0

.000

02<0

.000

02<0

.000

02<0

.000

02<0

.000

020.

0000

3<0

.000

02<0

.000

020.

0000

3<0

.000

02<0

.000

02<0

.000

020.

0000

2C

alci

um (C

a)m

g/L

6.04

7.19

7.35

5.99

9.01

7.51

7.84

8.61

7.71

5.57

6.44

4.25

7.16

5.35

7.44

5.84

Cad

miu

m (C

d)m

g/L

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

Cob

alt (

Co)

mg/

L0.

0007

000.

0002

660.

0000

820.

0001

620.

0000

360.

0000

890.

0000

920.

0001

080.

0000

980.

0000

510.

0001

080.

0001

540.

0001

050.

0000

500.

0000

570.

0000

59C

hrom

ium

(Cr)

mg/

L0.

0016

0.00

110.

0009

0.00

15<0

.000

30.

0007

0.00

100.

0005

0.00

060.

0009

0.00

080.

0019

0.00

090.

0008

0.00

070.

0008

Cop

per (

Cu)

mg/

L0.

0008

0.00

050.

0006

0.00

050.

0005

0.00

070.

0013

0.00

110.

0006

0.00

050.

0005

0.00

100.

0006

0.00

070.

0007

0.00

10Iro

n (F

e)m

g/L

0.54

0.64

0.08

0.07

<0.0

10.

070.

180.

080.

100.

070.

090.

210.

050.

040.

030.

07P

otas

sium

(K)

mg/

L<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

0.90

0.82

2.61

1.42

0.92

0.66

0.85

0.83

1.03

0.83

1.04

Lith

ium

(Li)

mg/

L1.

410.

964

1.36

1.44

1.25

<0.0

007

<0.0

007

<0.0

007

<0.0

007

0.00

220.

0011

0.00

100.

0015

<0.0

007

0.00

080.

0011

Mag

nesi

um (M

g)m

g/L

1.00

1.23

1.31

0.83

32.

222.

452.

142.

122.

733.

342.

18M

anga

nses

(Mn)

mg/

L0.

0010

40.

0000

90.

0004

00.

0001

90.

0001

20.

0012

40.

0034

90.

0108

0.00

385

0.00

353

0.00

741

0.00

874

0.00

485

0.01

290.

0020

90.

0103

Mol

ybde

num

(Mo)

mg/

L13

.411

.410

.513

.92.

150.

0006

40.

0013

20.

0007

40.

0004

10.

0002

60.

0002

20.

0002

40.

0004

20.

0002

00.

0003

70.

0002

4S

odiu

m (N

a)m

g/L

0.00

180.

0007

<0.0

007

0.00

07<0

.000

78.

786.

798.

168.

3010

.79.

398.

919.

728.

077.

688.

86N

icke

l (N

i)m

g/L

0.00

064

0.00

134

<0.0

0002

0.00

007

0.00

017

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

0.00

070.

0016

<0.0

007

<0.0

007

<0.0

007

<0.0

007

Lead

(Pb)

mg/

L0.

0021

0.00

120.

0010

0.00

250.

0014

0.00

091

0.00

064

0.00

039

0.00

154

0.00

106

0.00

072

0.00

101

0.00

081

0.00

209

0.00

045

0.00

047

Ant

imon

y (S

b)m

g/L

<0.0

03<0

.003

<0.0

03<0

.003

<0.0

030.

0004

0.00

150.

0009

0.00

130.

0033

0.00

330.

0020

0.00

170.

0029

0.00

320.

0017

Sel

eniu

m (S

e)m

g/L

0.00

08<0

.000

30.

0004

0.00

04<0

.000

3<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

Tin

(Sn)

mg/

L0.

0273

0.02

550.

0178

0.02

33<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3S

tont

ium

(Sr)

mg/

L0.

0143

0.03

520.

0432

0.04

630.

0397

0.04

790.

0487

0.03

890.

0529

0.03

710.

0439

0.04

54Ti

tani

um (T

i)m

g/L

0.01

160.

0114

0.00

360.

0024

<0.0

002

0.00

140.

0135

0.00

200.

0021

0.00

130.

0007

0.00

140.

0010

0.00

100.

0009

0.00

11Th

aliu

m (T

l)m

g/L

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

Ura

nium

(U)

mg/

L0.

0001

70.

0001

60.

0000

90.

0000

70.

0001

20.

0000

7<0

.000

020.

0001

20.

0001

00.

0000

40.

0000

20.

0000

20.

0000

40.

0000

3<0

.000

020.

0000

2V

anad

ium

(V)

mg/

L0.

0022

90.

0017

10.

0009

50.

0012

90.

0005

70.

0020

30.

0029

80.

0013

70.

0012

00.

0013

20.

0015

20.

0016

60.

0009

00.

0006

80.

0012

50.

0008

2Tu

ngst

en (W

)m

g/L

0.00

050

0.00

021

0.00

030

0.00

024

0.00

031

0.00

010

0.00

040

0.00

026

<0.0

0007

0.00

053

0.00

024

0.00

024

0.00

032

0.00

014

0.00

031

0.00

029

Yttr

ium

(Y)

mg/

L<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

40.

0000

400.

0000

370.

0000

450.

0000

450.

0000

700.

0000

470.

0000

720.

0000

600.

0000

570.

0000

330.

0000

62Zi

nc (Z

n)m

g/L

0.18

50.

152

0.13

90.

218

0.00

270.

0871

0.08

040.

0586

0.09

600.

126

0.10

90.

112

0.22

70.

215

0.21

20.

193

Page 32: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSP

LP C

hem

istr

y

Alu

min

um (A

l)m

g/L

Ars

enic

(As)

mg/

LS

ilver

(Ag)

mg/

LB

ariu

m (B

a)m

g/L

Ber

yliu

m (B

e)m

g/L

Bor

on (B

)m

g/L

Bis

mut

h (B

i)m

g/L

Cal

cium

(Ca)

mg/

LC

adm

ium

(Cd)

mg/

LC

obal

t (C

o)m

g/L

Chr

omiu

m (C

r)m

g/L

Cop

per (

Cu)

mg/

LIro

n (F

e)m

g/L

Pot

assi

um (K

)m

g/L

Lith

ium

(Li)

mg/

LM

agne

sium

(Mg)

mg/

LM

anga

nses

(Mn)

mg/

LM

olyb

denu

m (M

o)m

g/L

Sod

ium

(Na)

mg/

LN

icke

l (N

i)m

g/L

Lead

(Pb)

mg/

LA

ntim

ony

(Sb)

mg/

LS

elen

ium

(Se)

mg/

LTi

n (S

n)m

g/L

Sto

ntiu

m (S

r)m

g/L

Tita

nium

(Ti)

mg/

LTh

aliu

m (T

l)m

g/L

Ura

nium

(U)

mg/

LV

anad

ium

(V)

mg/

LTu

ngst

en (W

)m

g/L

Yttr

ium

(Y)

mg/

LZi

nc (Z

n)m

g/L

E44

6360

E44

6361

E44

6363

E43

1875

E43

1918

E42

9186

E42

9259

E42

9712

E43

0756

E47

1903

E41

4574

E41

4780

E41

4794

E41

6101

E41

6463

E42

8991

E42

9051

E42

9111

131.

6118

0.74

210.

5527

2.00

39.0

014

2.10

258.

0049

.60

83.2

012

7.80

122.

6545

.00

50.0

010

1.00

151.

0013

3.04

182.

0021

1.30

273.

0040

.00

142.

8525

8.98

50.6

084

.20

128.

8012

3.65

46.0

051

.00

102.

0015

2.00

Por

ph(P

LP)

Por

ph(P

LP)

Sed

SS

10S

S10

SS

8S

S8

SS

8S

S8

SS

8V

MV

MV

MV

MV

MV

MV

MV

M

0.35

61.

150.

346

0.23

0.07

0.24

0.33

0.34

0.44

0.21

0.44

0.34

0.52

0.18

0.24

0.59

0.36

0.94

0.03

440.

0593

0.02

33<0

.000

5<0

.000

50.

0015

0.00

140.

0228

0.04

860.

0006

0.00

16<0

.000

50.

0007

0.00

080.

0006

0.01

020.

0011

<0.0

005

<0.0

001

<0.0

001

<0.0

001

<0.0

0003

0.00

004

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

0.88

60.

948

0.83

80.

217

0.31

20.

588

0.56

20.

647

0.58

60.

590

0.66

80.

617

0.67

90.

531

0.56

20.

674

0.74

30.

178

<0.0

004

<0.0

004

<0.0

004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

0.00

006

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

0.44

00.

521

0.32

80.

013

0.23

40.

323

0.27

10.

321

0.38

20.

281

0.31

40.

248

0.37

10.

283

0.30

10.

256

0.33

70.

005

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

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0002

5.90

6.17

11.8

14.8

16.3

9.85

10.3

10.3

8.56

14.5

7.16

8.62

7.81

8.14

8.08

8.00

7.81

8.38

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0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

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0006

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0006

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0006

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0006

<0.0

0006

<0.0

0006

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0006

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0006

<0.0

0006

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0006

0.00

0036

0.00

0360

0.00

0155

0.00

0011

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0001

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0001

0.00

0070

0.00

0231

0.00

0064

0.00

0045

0.00

0007

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0001

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0001

<0.0

0001

0.00

0027

0.00

0062

0.00

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0001

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0019

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0004

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0007

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0009

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003

0.00

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0010

0.00

170.

0002

0.00

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0007

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0024

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0007

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0003

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0004

0.00

060.

0003

0.00

020.

020.

160.

18<0

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0.03

0.08

0.09

0.03

0.02

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1<0

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010.

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621.

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0.00

100.

0012

<0.0

007

2.77

1.66

2.93

2.22

1.76

0.55

53.

681.

852.

730.

952

2.19

1.39

0.64

62.

260.

954

2.42

1.76

2.42

0.00

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0.02

710.

0091

10.

0021

90.

0049

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0001

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0012

90.

0003

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0004

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0000

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979.

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0440

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0200

0.04

670.

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0013

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.000

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.000

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.000

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0001

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0014

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0008

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0001

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0002

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0008

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0008

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0003

70.

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70.

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20.

0012

00.

0006

70.

0003

80.

0028

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20.

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0006

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40.

273

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181

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0723

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90.

0937

0.07

610.

105

0.06

360.

148

0.09

070.

0913

0.08

070.

124

0.00

27

Page 33: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSP

LP C

hem

istr

y

Alu

min

um (A

l)m

g/L

Ars

enic

(As)

mg/

LS

ilver

(Ag)

mg/

LB

ariu

m (B

a)m

g/L

Ber

yliu

m (B

e)m

g/L

Bor

on (B

)m

g/L

Bis

mut

h (B

i)m

g/L

Cal

cium

(Ca)

mg/

LC

adm

ium

(Cd)

mg/

LC

obal

t (C

o)m

g/L

Chr

omiu

m (C

r)m

g/L

Cop

per (

Cu)

mg/

LIro

n (F

e)m

g/L

Pot

assi

um (K

)m

g/L

Lith

ium

(Li)

mg/

LM

agne

sium

(Mg)

mg/

LM

anga

nses

(Mn)

mg/

LM

olyb

denu

m (M

o)m

g/L

Sod

ium

(Na)

mg/

LN

icke

l (N

i)m

g/L

Lead

(Pb)

mg/

LA

ntim

ony

(Sb)

mg/

LS

elen

ium

(Se)

mg/

LTi

n (S

n)m

g/L

Sto

ntiu

m (S

r)m

g/L

Tita

nium

(Ti)

mg/

LTh

aliu

m (T

l)m

g/L

Ura

nium

(U)

mg/

LV

anad

ium

(V)

mg/

LTu

ngst

en (W

)m

g/L

Yttr

ium

(Y)

mg/

LZi

nc (Z

n)m

g/L

E42

9867

E42

9962

E43

0694

E43

0723

E43

0787

E43

0991

E43

1039

E43

1807

E44

6417

E44

6913

E44

6973

E44

7310

E44

7328

E44

7504

E44

7522

E47

1636

E47

1732

E41

4703

167.

0024

0.00

30.0

086

.00

199.

0014

.00

100.

0050

.00

219.

6062

.00

122.

0017

0.00

260.

0013

1.00

196.

0069

.00

150.

0021

0.50

168.

0024

1.00

31.0

087

.00

200.

0015

.00

101.

0051

.50

220.

6063

.00

123.

0017

1.00

261.

0013

2.50

197.

5070

.00

151.

0021

1.50

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

1

0.25

0.56

0.18

0.16

0.49

0.84

1.06

0.63

0.49

0.74

0.51

0.57

0.52

0.55

0.46

0.30

0.37

0.53

0.00

950.

0005

0.00

190.

0071

0.00

080.

0014

<0.0

005

0.00

13<0

.000

50.

0020

<0.0

005

<0.0

005

0.00

28<0

.000

5<0

.000

50.

0008

0.00

530.

0005

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

0.53

80.

263

0.55

50.

606

0.59

00.

182

0.20

40.

224

0.70

10.

232

0.58

50.

645

0.73

40.

588

0.57

40.

665

0.65

10.

692

<0.0

0004

<0.0

0004

<0.0

0004

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0004

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0004

<0.0

0004

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0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

0.00

005

<0.0

0004

0.00

007

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0004

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0004

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0004

0.26

10.

012

0.30

70.

290

0.25

40.

007

0.00

70.

012

0.30

80.

012

0.29

70.

358

0.34

80.

281

0.26

80.

342

0.31

60.

398

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

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0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

11.6

9.12

11.7

17.1

7.01

8.36

9.09

9.72

7.49

8.22

7.69

7.01

6.42

6.82

7.22

8.16

8.11

6.75

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0006

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0006

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0006

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0006

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0006

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0006

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0006

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0006

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0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

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0006

0.00

0024

<0.0

0001

0.00

0009

0.00

0047

0.00

0042

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0001

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0001

<0.0

0001

0.00

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0001

0.00

0024

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0001

0.00

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0.00

0022

0.00

0011

0.00

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<0.0

0001

0.00

0008

0.00

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.000

30.

0006

0.00

050.

0004

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003

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003

<0.0

003

0.00

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.000

30.

0006

0.00

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0010

0.00

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0006

0.00

080.

0005

0.00

130.

0005

0.00

030.

0002

0.00

020.

0005

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001

0.00

050.

0002

0.00

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.000

10.

0004

0.00

030.

0004

0.00

030.

0003

0.00

040.

0004

0.00

03<0

.01

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10.

02<0

.01

0.05

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1<0

.01

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10.

15<0

.01

0.01

0.02

0.05

0.02

0.01

<0.0

10.

010.

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

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.002

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.002

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022.

942.

851.

843.

120.

514

0.55

90.

431

1.32

1.13

2.76

0.88

30.

673

0.56

70.

625

0.72

22.

391.

520.

797

0.00

016

0.00

006

0.00

054

0.00

091

0.00

014

0.00

015

0.00

016

0.00

019

0.00

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001

0.00

007

0.00

012

0.00

009

0.00

005

0.00

005

0.00

010

0.00

006

0.00

013

8.45

1.97

8.40

7.53

6.08

1.83

1.95

3.28

8.74

1.99

6.31

8.98

8.01

6.75

6.16

8.90

9.14

8.57

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007

<0.0

007

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007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

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007

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007

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007

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007

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007

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007

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0014

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0178

0.02

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0.02

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0180

0.02

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0171

0.02

830.

0273

0.03

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0196

0.01

240.

0003

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002

0.00

080.

0004

0.00

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.000

20.

0002

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002

0.00

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20.

0004

0.00

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0028

0.00

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0005

0.00

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0004

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0008

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0005

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0004

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10.

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80.

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0021

40.

0007

30.

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0028

00.

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00.

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0.00

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0.07

360.

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0.00

280.

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0.00

330.

105

0.00

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0.12

00.

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0.09

820.

0949

0.09

130.

0854

0.14

4

Page 34: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSP

LP C

hem

istr

y

Alu

min

um (A

l)m

g/L

Ars

enic

(As)

mg/

LS

ilver

(Ag)

mg/

LB

ariu

m (B

a)m

g/L

Ber

yliu

m (B

e)m

g/L

Bor

on (B

)m

g/L

Bis

mut

h (B

i)m

g/L

Cal

cium

(Ca)

mg/

LC

adm

ium

(Cd)

mg/

LC

obal

t (C

o)m

g/L

Chr

omiu

m (C

r)m

g/L

Cop

per (

Cu)

mg/

LIro

n (F

e)m

g/L

Pot

assi

um (K

)m

g/L

Lith

ium

(Li)

mg/

LM

agne

sium

(Mg)

mg/

LM

anga

nses

(Mn)

mg/

LM

olyb

denu

m (M

o)m

g/L

Sod

ium

(Na)

mg/

LN

icke

l (N

i)m

g/L

Lead

(Pb)

mg/

LA

ntim

ony

(Sb)

mg/

LS

elen

ium

(Se)

mg/

LTi

n (S

n)m

g/L

Sto

ntiu

m (S

r)m

g/L

Tita

nium

(Ti)

mg/

LTh

aliu

m (T

l)m

g/L

Ura

nium

(U)

mg/

LV

anad

ium

(V)

mg/

LTu

ngst

en (W

)m

g/L

Yttr

ium

(Y)

mg/

LZi

nc (Z

n)m

g/L

E41

5991

E41

6050

E41

6139

E41

6152

E41

6544

E42

9326

E42

9787

E44

7184

E44

7259

E44

7267

E44

7461

E44

7481

E44

6338

E44

6340

E44

6341

E44

6339

E44

6342

E44

6343

16.8

069

.00

196.

0026

1.00

128.

7032

4.00

100.

0010

.00

56.0

013

0.50

14.7

062

.30

17.8

070

.00

197.

0026

2.00

129.

7032

5.00

101.

0011

.00

57.0

013

1.50

15.7

063

.30

VM

1V

M1

VM

1V

M1

VM

1V

M1

VM

1V

M1

VM

1V

M1

VM

1V

M1

Vol

cV

olc

Vol

cV

olc

(99F

low

)V

olc

(99F

low

)V

olc

(99F

low

)

0.31

0.16

0.30

0.25

0.27

0.31

0.59

0.25

0.49

0.50

0.85

0.28

0.49

70.

600

0.26

40.

504

0.32

50.

319

<0.0

005

0.00

760.

0173

0.00

780.

0021

<0.0

005

<0.0

005

0.00

16<0

.000

50.

0006

<0.0

005

0.00

88<0

.000

20.

0004

0.00

050.

0007

<0.0

002

<0.0

002

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

0003

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

0.54

10.

579

0.60

50.

546

0.71

10.

686

0.20

00.

621

0.72

80.

634

0.17

00.

545

0.64

90.

654

0.60

20.

669

0.66

50.

641

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

0004

0.00

009

<0.0

0004

<0.0

0004

<0.0

0004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

0.30

50.

260

0.27

20.

239

0.36

90.

283

0.00

70.

287

0.35

70.

300

0.00

50.

233

0.26

90.

262

0.28

50.

264

0.29

30.

277

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

0.00

005

0.00

002

<0.0

0002

8.57

7.99

8.17

7.59

7.41

10.2

10.5

6.84

6.80

6.82

7.55

7.69

7.47

8.91

8.92

7.61

8.41

7.39

0.00

010

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

0.00

0071

0.00

0013

<0.0

0001

<0.0

0001

0.00

0018

0.00

0017

<0.0

0001

0.00

0014

0.00

0023

0.00

0016

<0.0

0001

0.00

0018

0.00

0037

0.00

0075

0.00

0059

0.00

0058

0.00

0038

0.00

0025

0.00

060.

0005

0.00

050.

0005

0.00

090.

0006

<0.0

003

0.00

070.

0008

0.00

07<0

.000

30.

0006

0.00

050.

0005

0.00

050.

0007

0.00

050.

0005

0.00

020.

0001

0.00

080.

0002

0.00

040.

0003

<0.0

001

0.00

070.

0004

0.00

030.

0003

0.00

020.

0011

0.00

080.

0008

0.00

110.

0010

0.00

04<0

.01

<0.0

1<0

.01

<0.0

10.

01<0

.01

<0.0

1<0

.01

0.02

0.02

<0.0

1<0

.01

0.02

0.05

0.16

0.02

0.04

0.04

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

0.29

0.26

0.26

0.54

0.37

0.24

2.06

2.27

2.93

2.70

2.33

2.71

2.98

1.85

0.56

90.

645

0.81

53.

34<0

.000

7<0

.000

7<0

.000

7<0

.000

7<0

.000

7<0

.000

70.

722

0.48

60.

419

0.57

51.

780.

506

0.00

014

0.00

007

0.00

008

0.00

006

0.00

010

0.00

019

<0.0

001

0.00

009

0.00

010

0.00

007

<0.0

001

0.00

014

0.00

072

0.00

111

0.00

439

0.00

070

0.00

090

0.00

077

9.18

7.88

7.29

8.34

9.67

7.97

1.37

7.03

7.90

7.47

1.37

8.33

0.00

067

0.00

028

0.00

072

0.00

033

0.00

059

0.00

025

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

6.58

5.76

5.89

6.21

6.38

5.34

0.00

035

0.00

025

0.00

034

0.00

025

<0.0

0002

<0.0

0002

0.00

032

<0.0

0002

<0.0

0002

<0.0

0002

0.00

017

0.00

029

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

<0.0

007

0.00

080.

0010

0.00

080.

0006

0.00

050.

0009

0.00

090.

0002

0.00

04<0

.000

20.

0008

0.00

040.

0010

80.

0003

50.

0002

60.

0006

90.

0003

30.

0002

3<0

.003

<0.0

03<0

.003

<0.0

03<0

.003

<0.0

03<0

.003

<0.0

03<0

.003

<0.0

03<0

.003

<0.0

030.

0004

0.00

050.

0002

0.00

040.

0006

0.00

04<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

30.

0005

<0.0

003

0.00

030.

0005

<0.0

003

<0.0

003

<0.0

003

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

0.01

700.

0232

0.01

200.

0172

0.01

49<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

30.

0220

0.01

360.

0134

0.02

130.

0255

0.01

770.

0121

0.03

000.

0459

0.02

780.

0259

0.04

360.

0380

0.00

060.

0009

0.00

040.

0002

0.00

06<0

.000

2<0

.000

2<0

.000

20.

0009

0.00

06<0

.000

20.

0002

0.00

080.

0022

0.00

090.

0004

0.00

060.

0028

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

0.00

073

0.00

118

0.00

167

0.00

136

0.00

133

0.00

046

0.00

076

0.00

099

0.00

235

0.00

249

0.00

246

0.00

102

0.00

344

0.00

023

0.00

012

0.00

232

0.00

067

0.00

143

<0.0

0007

<0.0

0007

0.00

070

0.00

037

0.00

030

0.00

008

0.00

007

0.00

012

0.00

025

0.00

008

0.00

009

0.00

017

<0.0

0007

0.00

013

<0.0

0007

0.00

014

<0.0

0007

<0.0

0007

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

<0.0

004

0.00

0017

0.00

0045

0.00

0030

0.00

0016

0.00

0022

0.00

0033

0.07

280.

0861

0.12

20.

0525

0.10

20.

0795

0.00

350.

0806

0.13

50.

102

0.00

270.

0604

0.08

450.

0839

0.08

850.

0781

0.08

590.

0959

Page 35: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsSP

LP C

hem

istr

y

Alu

min

um (A

l)m

g/L

Ars

enic

(As)

mg/

LS

ilver

(Ag)

mg/

LB

ariu

m (B

a)m

g/L

Ber

yliu

m (B

e)m

g/L

Bor

on (B

)m

g/L

Bis

mut

h (B

i)m

g/L

Cal

cium

(Ca)

mg/

LC

adm

ium

(Cd)

mg/

LC

obal

t (C

o)m

g/L

Chr

omiu

m (C

r)m

g/L

Cop

per (

Cu)

mg/

LIro

n (F

e)m

g/L

Pot

assi

um (K

)m

g/L

Lith

ium

(Li)

mg/

LM

agne

sium

(Mg)

mg/

LM

anga

nses

(Mn)

mg/

LM

olyb

denu

m (M

o)m

g/L

Sod

ium

(Na)

mg/

LN

icke

l (N

i)m

g/L

Lead

(Pb)

mg/

LA

ntim

ony

(Sb)

mg/

LS

elen

ium

(Se)

mg/

LTi

n (S

n)m

g/L

Sto

ntiu

m (S

r)m

g/L

Tita

nium

(Ti)

mg/

LTh

aliu

m (T

l)m

g/L

Ura

nium

(U)

mg/

LV

anad

ium

(V)

mg/

LTu

ngst

en (W

)m

g/L

Yttr

ium

(Y)

mg/

LZi

nc (Z

n)m

g/L

E44

6344

E44

6348

E44

6349

E44

6350

E44

6351

E44

6352

E44

6362

E44

6365

E55

6364

E44

6346

E44

6347

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c (C

ntl)

Vol

c (C

ntl)

Vol

c/S

edV

olc/

Sed

0.36

90.

297

0.49

50.

368

0.38

20.

317

0.84

50.

546

0.47

70.

0002

0.00

06<0

.000

20.

0006

0.00

05<0

.000

20.

0022

0.00

290.

0014

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

0.66

70.

707

0.66

70.

781

0.73

30.

767

0.90

80.

646

0.65

3<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

4<0

.000

40.

295

0.27

90.

292

0.28

90.

316

0.29

10.

402

0.30

10.

289

<0.0

0002

<0.0

0002

<0.0

0002

0.00

003

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

8.04

10.1

7.44

9.03

7.85

10.2

12.0

8.18

8.65

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

<0.0

0006

0.00

0037

0.00

0028

0.00

0044

0.00

0055

0.00

0031

0.00

0017

0.00

0586

0.00

0087

0.00

0049

0.00

060.

0006

0.00

050.

0007

0.00

070.

0005

0.00

160.

0006

0.00

050.

0005

0.00

090.

0009

0.00

060.

0005

0.00

060.

0016

0.00

080.

0005

0.03

<0.0

10.

070.

060.

030.

011.

400.

110.

070.

500.

460.

270.

460.

340.

511.

070.

460.

49<0

.000

7<0

.000

7<0

.000

70.

0013

0.00

160.

0009

0.00

07<0

.000

7<0

.000

71.

312.

670.

720

2.19

1.46

2.13

2.91

0.74

00.

952

0.00

156

0.00

084

0.00

089

0.00

278

0.00

095

0.00

214

0.02

480.

0015

20.

0015

50.

0005

20.

0003

50.

0001

80.

0002

40.

0003

80.

0004

10.

0001

20.

0004

30.

0002

96.

766.

376.

066.

866.

636.

647.

837.

076.

84<0

.000

7<0

.000

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.000

7<0

.000

7<0

.000

7<0

.000

70.

0010

<0.0

007

<0.0

007

0.00

033

0.00

030

0.00

018

0.00

018

0.00

017

0.00

018

0.00

032

0.00

031

0.00

022

0.00

080.

0019

0.00

050.

0015

0.00

440.

0004

0.00

130.

0019

0.00

13<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

003

<0.0

003

<0.0

003

<0.0

003

<0.0

003

<0.0

003

<0.0

003

<0.0

003

<0.0

003

0.03

620.

0337

0.05

660.

0457

0.03

390.

0390

0.04

740.

0317

0.03

240.

0006

0.00

080.

0072

0.00

110.

0008

0.00

050.

0061

0.00

100.

0009

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

<0.0

0002

0.00

095

0.00

059

0.00

189

0.00

130

0.00

123

0.00

053

0.00

253

0.00

271

0.00

161

<0.0

0007

0.00

012

0.00

044

0.00

027

0.00

023

0.00

015

0.00

015

0.00

014

0.00

015

0.00

0018

0.00

0016

0.00

0040

0.00

0025

0.00

0021

0.00

0018

0.00

0123

0.00

0031

0.00

0034

0.08

080.

0904

0.10

00.

0969

0.12

10.

0919

0.25

20.

0996

0.08

75

Page 36: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDE

4146

20E

4146

88E

4165

07E

4300

13E

4468

47E

4463

35E

4463

36E

4463

37E

4463

45E

4463

66E

4463

53E

4463

54E

4463

55E

4463

56E

4463

57E

4463

58E

4463

59D

epth

From

109.

2015

4.70

96.8

032

0.00

11.0

0To

110.

2015

5.70

97.8

032

1.00

12.0

0

Lith

olog

yFP

FPFP

FPFP

Por

ph (M

T)P

orph

(MT)

Por

ph (M

T)P

orph

(MT)

Por

ph(M

T)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)P

orph

(PLP

)U

nits

Aci

d B

ase

Acc

ount

ing

Pas

te p

Hun

its8.

628.

998.

738.

718.

588.

409.

069.

319.

199.

358.

528.

468.

689.

238.

768.

469.

03S

obec

k N

Pt C

aCO

3/10

237

47.8

54.0

193

230

207

248

239

223

284

118

240

68.6

252

158

183

159

Car

bona

te N

Pt C

aCO

3/10

276.

764

.265

.028

5.9

274.

222

0.0

258.

428

7.5

276.

733

0.9

243.

327

5.0

91.7

289.

216

3.3

216.

716

2.5

AP

t CaC

O3/

102.

54.

25.

93.

15.

12.

96.

30.

3110

.74.

369

.613

.211

.63.

31.

32.

70.

94N

et N

Pt C

aCO

3/10

234

43.5

48.2

190

225

204

241

239

213

279

48.9

226

57.1

249

157

181

158

Sob

eck

NP

/AP

ratio

93.5

11.2

9.2

62.4

45.1

71.9

39.4

771

20.8

65.3

1.7

18.1

5.9

76.8

118

68.2

169

Car

bona

te N

P/A

Pra

tio11

0.7

15.3

11.0

92.2

53.8

75.9

41.0

927.

525

.976

.93.

520

.87.

987

.612

5.6

80.3

172.

9S

2-%

0.08

80.

140.

240.

130.

220.

120.

300.

130.

510.

212.

720.

580.

340.

140.

069

0.08

30.

065

Sul

phid

e%

0.08

0.14

0.19

0.10

0.16

0.09

0.20

<0.0

10.

340.

142.

230.

420.

370.

100.

040.

090.

03S

O4

%<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4C

(t)%

3.32

0.77

0.78

3.43

3.29

2.64

3.10

3.45

3.32

3.97

2.92

3.30

1.10

3.47

1.96

2.60

1.95

Car

bona

te%

15.8

2.94

3.06

17.5

13.9

12.7

13.7

16.3

14.4

19.6

7.79

15.1

4.87

16.1

9.28

11.8

9.13

Page 37: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsA

cid

Bas

e A

ccou

ntin

g

Pas

te p

Hun

itsS

obec

k N

Pt C

aCO

3/10

Car

bona

te N

Pt C

aCO

3/10

AP

t CaC

O3/

10N

et N

Pt C

aCO

3/10

Sob

eck

NP

/AP

ratio

Car

bona

te N

P/A

Pra

tioS

2-%

Sul

phid

e%

SO

4%

C(t)

%C

arbo

nate

%

E44

6360

E44

6361

E44

6363

E43

1875

E43

1918

E42

9186

E42

9259

E42

9712

E43

0756

E47

1903

E41

4574

E41

4780

E41

4794

E41

6101

E41

6463

E42

8991

E42

9051

E42

9111

131.

6118

0.74

210.

5527

2.00

39.0

014

2.10

258.

0049

.60

83.2

012

7.80

122.

6545

.00

50.0

010

1.00

151.

0013

3.04

182.

0021

1.30

273.

0040

.00

142.

8525

8.98

50.6

084

.20

128.

8012

3.65

46.0

051

.00

102.

0015

2.00

Por

ph(P

LP)

Por

ph(P

LP)

Sed

SS

10S

S10

SS

8S

S8

SS

8S

S8

SS

8V

MV

MV

MV

MV

MV

MV

MV

M

8.43

9.05

8.29

8.71

9.07

8.61

9.21

8.84

8.88

8.42

8.69

8.98

9.16

9.20

9.17

8.69

9.35

9.70

226

161

191

84.6

188

182

263

144

141

158

144

155

90.9

112

88.4

130

284

99.3

281.

723

5.0

237.

512

1.7

225.

823

2.5

310.

017

1.7

185.

826

8.4

158.

315

0.0

86.7

113.

310

0.8

209.

232

9.2

113.

332

.923

.44.

813

.50.

3122

.60.

316.

80.

3126

.723

.01.

92.

20.

314.

338

.89.

00.

6219

313

718

671

.118

715

926

313

814

113

212

115

388

.711

284

.191

.127

598

.76.

96.

939

.96.

360

58.

085

021

.345

55.

96.

381

.541

.336

220

.53.

431

.616

08.

610

.049

.59.

072

8.5

10.3

1000

.125

.259

9.5

10.1

6.9

79.0

39.4

365.

623

.55.

436

.618

2.8

1.85

0.89

0.19

0.54

0.09

41.

130.

093

0.34

0.22

1.22

0.97

0.08

20.

090

0.16

0.15

1.43

0.37

0.07

81.

050.

750.

150.

43<0

.01

0.72

<0.0

10.

22<0

.01

0.85

0.74

0.06

0.07

<0.0

10.

141.

240.

290.

02<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.43.

382.

822.

851.

462.

712.

793.

722.

062.

233.

221.

901.

801.

041.

361.

212.

513.

951.

3614

.411

.512

.15.

7112

.312

.117

.29.

2710

.210

.38.

308.

684.

606.

135.

197.

6818

.06.

09

Page 38: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsA

cid

Bas

e A

ccou

ntin

g

Pas

te p

Hun

itsS

obec

k N

Pt C

aCO

3/10

Car

bona

te N

Pt C

aCO

3/10

AP

t CaC

O3/

10N

et N

Pt C

aCO

3/10

Sob

eck

NP

/AP

ratio

Car

bona

te N

P/A

Pra

tioS

2-%

Sul

phid

e%

SO

4%

C(t)

%C

arbo

nate

%

E42

9867

E42

9962

E43

0694

E43

0723

E43

0787

E43

0991

E43

1039

E43

1807

E44

6417

E44

6913

E44

6973

E44

7310

E44

7328

E44

7504

E44

7522

E47

1636

E47

1732

E41

4703

167.

0024

0.00

30.0

086

.00

199.

0014

.00

100.

0050

.00

219.

6062

.00

122.

0017

0.00

260.

0013

1.00

196.

0069

.00

150.

0021

0.50

168.

0024

1.00

31.0

087

.00

200.

0015

.00

101.

0051

.50

220.

6063

.00

123.

0017

1.00

261.

0013

2.50

197.

5070

.00

151.

0021

1.50

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

VM

1

9.50

9.67

9.27

9.28

9.12

8.79

9.11

9.17

9.26

9.67

9.37

9.17

9.23

9.34

9.43

9.23

9.08

9.75

159

84.6

193

185

102

102

153

160

170

81.7

104

127

186

88.4

173

183

180

91.6

173.

310

5.8

200.

019

1.7

99.2

96.7

180.

016

5.0

188.

396

.710

7.5

134.

222

3.3

85.8

222.

520

0.8

210.

811

0.0

0.94

0.31

1.25

1.88

2.50

1.88

1.88

0.62

1.88

1.88

8.12

4.06

11.2

1.56

4.06

4.38

0.31

39.7

158

84.3

192

183

99.1

100

151

160

168

79.9

96.0

123

175

86.9

169

179

180

51.9

169

273

155

98.5

40.6

54.2

81.5

259

90.4

43.5

12.8

31.3

16.6

56.7

42.6

41.8

582

2.3

184.

434

1.4

160.

010

2.0

39.7

51.4

95.8

266.

110

0.2

51.4

13.2

33.0

19.9

55.0

54.8

45.9

680.

22.

80.

078

0.03

30.

088

0.09

00.

084

0.08

40.

068

0.03

90.

084

0.03

70.

284

0.14

60.

397

0.08

30.

170

0.17

00.

025

1.21

0.03

0.01

0.04

0.06

0.08

0.06

0.06

0.02

0.06

0.06

0.26

0.13

0.36

0.05

0.13

0.14

<0.0

11.

27<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.4<0

.42.

081.

272.

402.

301.

191.

162.

161.

982.

261.

161.

291.

612.

681.

032.

672.

412.

531.

329.

965.

6511

.611

.45.

675.

4310

.19.

5810

.75.

136.

107.

6812

.45.

0111

.811

.712

.05.

04

Page 39: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsA

cid

Bas

e A

ccou

ntin

g

Pas

te p

Hun

itsS

obec

k N

Pt C

aCO

3/10

Car

bona

te N

Pt C

aCO

3/10

AP

t CaC

O3/

10N

et N

Pt C

aCO

3/10

Sob

eck

NP

/AP

ratio

Car

bona

te N

P/A

Pra

tioS

2-%

Sul

phid

e%

SO

4%

C(t)

%C

arbo

nate

%

E41

5991

E41

6050

E41

6139

E41

6152

E41

6544

E42

9326

E42

9787

E44

7184

E44

7259

E44

7267

E44

7461

E44

7481

E44

6338

E44

6340

E44

6341

E44

6339

E44

6342

E44

6343

16.8

069

.00

196.

0026

1.00

128.

7032

4.00

100.

0010

.00

56.0

013

0.50

14.7

062

.30

17.8

070

.00

197.

0026

2.00

129.

7032

5.00

101.

0011

.00

57.0

013

1.50

15.7

063

.30

VM

1V

M1

VM

1V

M1

VM

1V

M1

VM

1V

M1

VM

1V

M1

VM

1V

M1

Vol

cV

olc

Vol

cV

olc

(99F

low

)V

olc

(99F

low

)V

olc

(99F

low

)

9.84

9.68

9.73

9.68

9.59

9.61

9.86

9.72

9.38

9.35

8.59

9.28

9.12

8.80

9.40

8.81

8.92

8.79

116

93.5

111

83.3

143

102

152

103

148

124

130

83.4

194

192

273

218

57.6

209

164.

216

0.0

146.

713

9.2

230.

011

6.7

210.

815

8.3

219.

219

7.5

156.

710

4.2

221.

718

5.8

301.

721

5.0

179.

221

2.5

22.2

56.2

15.0

65.3

35.0

60.3

28.7

47.8

10.9

14.7

0.31

7.5

5.3

12.3

2.8

0.8

0.31

2.1

94.3

37.3

96.2

17.9

108

41.3

124

54.8

138

110

130

75.9

188

180

270

217

57.3

207

5.2

1.7

7.4

1.3

4.1

1.7

5.3

2.1

13.6

8.5

421

11.1

36.4

15.6

97.4

279

186

98.5

7.4

2.8

9.8

2.1

6.6

1.9

7.3

3.3

20.1

13.4

505.

413

.941

.815

.110

7.7

268.

857

8.0

101.

20.

737

1.77

0.48

72.

271.

112.

040.

929

1.53

0.41

20.

508

0.01

40.

350.

210.

580.

120.

035

0.04

00.

081

0.71

1.80

0.48

2.09

1.12

1.93

0.92

1.53

0.35

0.47

<0.0

10.

240.

170.

400.

090.

02<0

.01

0.07

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

1.97

1.92

1.76

1.67

2.76

1.40

2.53

1.90

2.63

2.37

1.88

1.25

2.66

2.23

3.62

2.58

2.15

2.55

7.23

5.28

6.95

4.33

8.46

5.70

9.65

6.24

10.3

7.61

8.75

5.19

12.9

10.8

17.7

12.6

10.5

12.2

Page 40: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 1

Com

pila

tion

of M

etal

s, A

BA

and

SP

LP D

ata

Sam

ple

IDD

epth

From To

Lith

olog

y

Uni

tsA

cid

Bas

e A

ccou

ntin

g

Pas

te p

Hun

itsS

obec

k N

Pt C

aCO

3/10

Car

bona

te N

Pt C

aCO

3/10

AP

t CaC

O3/

10N

et N

Pt C

aCO

3/10

Sob

eck

NP

/AP

ratio

Car

bona

te N

P/A

Pra

tioS

2-%

Sul

phid

e%

SO

4%

C(t)

%C

arbo

nate

%

E44

6344

E44

6348

E44

6349

E44

6350

E44

6351

E44

6352

E44

6362

E44

6365

E55

6364

E44

6346

E44

6347

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c(9

9Flo

w)

Vol

c (C

ntl)

Vol

c (C

ntl)

Vol

c/S

edV

olc/

Sed

8.89

9.15

9.37

8.50

8.75

9.12

8.66

8.44

141

178

331

166

201

198

183

170

140.

817

3.3

394.

216

3.3

195.

822

6.7

205.

023

2.5

0.31

0.31

0.31

2.4

8.7

2.5

3.5

57.8

141

178

330

163

192

195

180

112

454

574

1067

68.9

23.1

79.1

51.9

2.9

454.

355

9.2

1271

.668

.122

.590

.758

.64.

00.

068

0.09

80.

230.

150.

310.

110.

132.

75<0

.01

<0.0

1<0

.01

0.08

0.28

0.08

0.11

1.85

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

<0.4

1.69

2.08

4.73

1.96

2.35

2.72

2.46

2.79

8.16

9.76

21.7

9.29

10.9

12.6

11.7

11.0

Page 41: Geochem Evaluation of Waste Rock in Hollinger Mine

APPENDIX 2

Compilation of Humidity Cell Testing Data

Page 42: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 2

Com

pila

tion

of H

umid

ity C

ell T

est D

ata

Para

met

erSS

-1D

ay 0

SS-1

Day

7SS

-1D

ay 1

3SS

-1D

ay 2

1SS

-1D

ay 2

8SS

-1D

ay 3

5SS

-1D

ay 4

2SS

-1D

ay 4

9SS

-1D

ay 5

5SS

-1D

ay 6

3SS

-1D

ay 7

0SS

-1D

ay 7

7SS

-1D

ay 8

4SS

-1D

ay 9

1SS

-1D

ay 9

8SS

-1D

ay 1

05SS

-1D

ay 1

12SS

-1D

ay 1

19SS

-1D

ay 1

26SS

-1D

ay 1

33SS

-1D

ay 1

40

Da y

07

1321

2835

4249

5563

7077

8491

9810

511

211

912

613

314

0W

eek

Uni

ts0

12

34

56

78

910

1112

1314

1516

1718

1920

Vol

ume

Wat

er A

dded

L2.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

001.

00V

olum

e W

ater

Rec

over

edL

1.71

1.04

1.05

0.95

0.99

0.93

0.95

0.98

1.10

0.90

1.00

0.97

0.95

0.97

0.98

0.98

0.98

0.99

1.00

1.00

1.00

pH--

-6.

627.

417.

026.

937.

526.

817.

457.

437.

518.

027.

667.

377.

727.

807.

587.

147.

607.

457.

517.

687.

19S

peci

fic C

ondu

ctan

cem

S0.

240.

200.

160.

170.

150.

110.

170.

230.

210.

150.

160.

160.

040.

120.

080.

090.

100.

090.

150.

160.

10

Aci

dity

as

CaC

03m

g/L

5N

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MN

MA

lkal

inity

as

CaC

03m

g/L

NM

7659

4038

2419

5557

4663

6322

4042

4844

4667

5045

Dis

solv

ed A

lum

inum

(Al)

mg/

L0.

060.

110.

090.

110.

090.

090.

080.

070.

090.

10.

090.

090.

070.

070.

060.

060.

060.

060.

040.

040.

05D

isso

lved

Ant

imon

y (S

b)m

g/L

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05D

isso

lved

Ars

enic

(As)

mg/

L<0

.001

0.00

40.

005

0.00

50.

003

0.00

30.

004

0.00

50.

004

0.00

40.

003

0.00

30.

002

0.00

20.

002

0.00

10.

001

0.00

1<0

.001

0.00

10.

001

Dis

solv

ed B

ariu

m (B

a)m

g/L

<0.0

10.

01<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

Dis

solv

ed B

eryl

lium

(Be)

mg/

L<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

Dis

solv

ed B

ism

uth

(Bi)

mg/

L<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

Dis

solv

ed B

oron

(B)

mg/

L<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

Dis

solv

ed C

adm

ium

(Cd)

mg/

L<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1D

isso

lved

Cal

cium

(Ca)

mg/

L31

.520

.218

.819

.618

.511

.518

.121

.219

.318

21.5

20.4

8.6

13.6

1416

.313

.513

.322

.817

.514

.8D

isso

lved

Chr

omiu

m (C

r)m

g/L

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01D

isso

lved

Cob

alt (

Co)

mg/

L<0

.000

50.

0006

0.00

110.

001

0.00

1<0

.000

50.

0009

0.00

130.

001

0.00

050.

001

0.00

1<0

.000

50.

0006

0.00

070.

0008

0.00

060.

0007

0.00

130.

0008

0.00

06D

isso

lved

Cop

per (

Cu)

mg/

L0.

001

0.00

10.

002

<0.0

01<0

.001

<0.0

010.

001

0.00

10.

002

<0.0

01<0

.001

<0.0

01<0

.001

0.00

10.

001

0.00

20.

001

0.00

2<0

.001

0.00

10.

002

Dis

solv

ed Ir

on (F

e)m

g/L

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5D

isso

lved

Lea

d (P

b)m

g/L

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01D

isso

lved

Mag

nesi

um (M

g)m

g/L

5.4

13.3

12.8

11.3

12.2

611

17.5

14.8

13.4

12.6

133.

77.

67.

410

.37.

87.

713

.68.

47.

1D

isso

lved

Man

gane

se (M

n)m

g/L

0.05

90.

052

0.07

50.

066

0.05

90.

041

0.05

30.

048

0.03

40.

032

0.03

80.

039

0.03

70.

045

0.05

10.

048

0.04

30.

046

0.06

10.

051

0.04

7D

isso

lved

Mol

ybde

num

(Mo)

mg/

L0.

011

0.01

0.00

60.

004

0.00

20.

005

0.00

20.

008

0.00

60.

003

0.00

30.

002

0.00

10.

004

0.00

20.

002

0.00

20.

002

0.00

30.

002

0.00

1D

isso

lved

Nic

kel (

Ni)

mg/

L<0

.002

0.00

30.

002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

Dis

solv

ed P

hosp

horu

s (P

)m

g/L

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5D

isso

lved

Pot

assi

um (K

)m

g/L

12.6

106

43

23

33

22

2<1

<1<1

<1<1

<1<1

<1<1

Dis

solv

ed S

elen

ium

(Se)

mg/

L0.

005

0.01

70.

018

0.02

10.

019

0.00

90.

019

0.02

10.

011

0.00

90.

007

0.00

7<0

.005

<0.0

05<0

.005

0.00

5<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

Dis

solv

ed S

ilico

n (S

i)m

g/L

0.6

1.5

1.6

1.1

0.6

0.3

0.3

11.

11

1.3

1.2

0.4

0.5

0.5

0.7

0.6

0.7

0.6

0.7

0.6

Dis

solv

ed S

ilver

(Ag)

mg/

L<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

10.

0003

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

<0.0

001

Dis

solv

ed S

odiu

m (N

a)m

g/L

7.4

3.5

1.6

0.7

0.7

0.9

<0.5

0.7

0.5

<0.5

<0.5

<0.5

<0.5

<0.5

<0.5

<0.5

<0.5

<0.5

<0.5

<0.5

<0.5

Dis

solv

ed S

tront

ium

(Sr)

mg/

L0.

080.

069

0.05

70.

060.

058

0.03

40.

072

0.08

70.

067

0.05

90.

071

0.06

80.

022

0.04

30.

045

0.05

10.

041

0.04

20.

069

0.04

80.

043

Dis

solv

ed S

ulph

ur (S

)m

g/L

3719

1621

2113

2832

1818

1417

510

1011

99

149

8D

isso

lved

Tha

llium

(Tl)

mg/

L<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3<0

.000

3D

isso

lved

Tin

(Sn)

mg/

L<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

Dis

solv

ed T

itani

um (T

i)m

g/L

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02D

isso

lved

Tun

gste

n (W

)m

g/L

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1<0

.01

<0.0

1D

isso

lved

Ura

nium

(U)

mg/

L<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

<0.0

05<0

.005

Dis

solv

ed V

anad

ium

(V)

mg/

L<0

.001

0.00

20.

001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

Dis

solv

ed Z

inc

(Zn)

mg/

L0.

004

0.00

50.

010.

008

0.00

90.

006

0.01

10.

014

0.01

60.

007

0.01

10.

011

0.00

30.

012

0.01

0.01

10.

010.

015

0.01

70.

013

0.01

2D

isso

lved

Zirc

oniu

m (Z

r)m

g/L

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04<0

.004

<0.0

04

Sul

phat

e (S

O4)

mg/

L11

157

4863

6339

8496

5454

4251

1530

3033

2727

4227

24

Page 43: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 2

Com

pila

tion

of H

umid

ity C

ell T

est D

ata

Para

met

er

Da y

Wee

kU

nits

Vol

ume

Wat

er A

dded

LV

olum

e W

ater

Rec

over

edL

pH--

-S

peci

fic C

ondu

ctan

cem

S

Aci

dity

as

CaC

03m

g/L

Alk

alin

ity a

s C

aC03

mg/

L

Dis

solv

ed A

lum

inum

(Al)

mg/

LD

isso

lved

Ant

imon

y (S

b)m

g/L

Dis

solv

ed A

rsen

ic (A

s)m

g/L

Dis

solv

ed B

ariu

m (B

a)m

g/L

Dis

solv

ed B

eryl

lium

(Be)

mg/

LD

isso

lved

Bis

mut

h (B

i)m

g/L

Dis

solv

ed B

oron

(B)

mg/

LD

isso

lved

Cad

miu

m (C

d)m

g/L

Dis

solv

ed C

alci

um (C

a)m

g/L

Dis

solv

ed C

hrom

ium

(Cr)

mg/

LD

isso

lved

Cob

alt (

Co)

mg/

LD

isso

lved

Cop

per (

Cu)

mg/

LD

isso

lved

Iron

(Fe)

mg/

LD

isso

lved

Lea

d (P

b)m

g/L

Dis

solv

ed M

agne

sium

(Mg)

mg/

LD

isso

lved

Man

gane

se (M

n)m

g/L

Dis

solv

ed M

olyb

denu

m (M

o)m

g/L

Dis

solv

ed N

icke

l (N

i)m

g/L

Dis

solv

ed P

hosp

horu

s (P

)m

g/L

Dis

solv

ed P

otas

sium

(K)

mg/

LD

isso

lved

Sel

eniu

m (S

e)m

g/L

Dis

solv

ed S

ilico

n (S

i)m

g/L

Dis

solv

ed S

ilver

(Ag)

mg/

LD

isso

lved

Sod

ium

(Na)

mg/

LD

isso

lved

Stro

ntiu

m (S

r)m

g/L

Dis

solv

ed S

ulph

ur (S

)m

g/L

Dis

solv

ed T

halli

um (T

l)m

g/L

Dis

solv

ed T

in (S

n)m

g/L

Dis

solv

ed T

itani

um (T

i)m

g/L

Dis

solv

ed T

ungs

ten

(W)

mg/

LD

isso

lved

Ura

nium

(U)

mg/

LD

isso

lved

Van

adiu

m (V

)m

g/L

Dis

solv

ed Z

inc

(Zn)

mg/

LD

isso

lved

Zirc

oniu

m (Z

r)m

g/L

Sul

phat

e (S

O4)

mg/

L

SS-2

Day

0SS

-2D

ay 7

SS-2

Day

13

SS-2

Day

21

SS-2

Day

28

SS-2

Day

35

SS-2

Day

42

SS-2

Day

49

SS-2

Day

55

SS-2

Day

63

SS-2

Day

70

SS-2

Day

77

SS-2

Day

84

SS-2

Day

91

SS-2

Day

98

SS-2

Day

105

SS-2

Day

112

SS-2

Day

119

SS-2

Day

126

SS-2

Day

133

SS-2

Day

140

07

1321

2835

4249

5563

7077

8491

9810

511

211

912

613

314

00

12

34

56

78

910

1112

1314

1516

1718

1920

2.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.69

1.10

1.07

0.95

0.98

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7.87

6.89

6.67

7.64

7.34

7.54

7.61

7.35

8.08

7.78

7.46

7.35

7.69

7.78

7.60

7.59

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7.66

7.63

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0.18

0.18

0.17

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0.14

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0.15

0.15

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MN

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19.4

16.6

18.1

16.8

18.6

16.5

18.2

17.1

16.5

18.1

20.3

19.4

16.4

19.3

19.3

20.2

18.2

14.3

20.5

20.2

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7542

4551

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3030

3030

3030

2424

3630

30

Page 44: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 2

Com

pila

tion

of H

umid

ity C

ell T

est D

ata

Para

met

er

Da y

Wee

kU

nits

Vol

ume

Wat

er A

dded

LV

olum

e W

ater

Rec

over

edL

pH--

-S

peci

fic C

ondu

ctan

cem

S

Aci

dity

as

CaC

03m

g/L

Alk

alin

ity a

s C

aC03

mg/

L

Dis

solv

ed A

lum

inum

(Al)

mg/

LD

isso

lved

Ant

imon

y (S

b)m

g/L

Dis

solv

ed A

rsen

ic (A

s)m

g/L

Dis

solv

ed B

ariu

m (B

a)m

g/L

Dis

solv

ed B

eryl

lium

(Be)

mg/

LD

isso

lved

Bis

mut

h (B

i)m

g/L

Dis

solv

ed B

oron

(B)

mg/

LD

isso

lved

Cad

miu

m (C

d)m

g/L

Dis

solv

ed C

alci

um (C

a)m

g/L

Dis

solv

ed C

hrom

ium

(Cr)

mg/

LD

isso

lved

Cob

alt (

Co)

mg/

LD

isso

lved

Cop

per (

Cu)

mg/

LD

isso

lved

Iron

(Fe)

mg/

LD

isso

lved

Lea

d (P

b)m

g/L

Dis

solv

ed M

agne

sium

(Mg)

mg/

LD

isso

lved

Man

gane

se (M

n)m

g/L

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solv

ed M

olyb

denu

m (M

o)m

g/L

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solv

ed N

icke

l (N

i)m

g/L

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solv

ed P

hosp

horu

s (P

)m

g/L

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solv

ed P

otas

sium

(K)

mg/

LD

isso

lved

Sel

eniu

m (S

e)m

g/L

Dis

solv

ed S

ilico

n (S

i)m

g/L

Dis

solv

ed S

ilver

(Ag)

mg/

LD

isso

lved

Sod

ium

(Na)

mg/

LD

isso

lved

Stro

ntiu

m (S

r)m

g/L

Dis

solv

ed S

ulph

ur (S

)m

g/L

Dis

solv

ed T

halli

um (T

l)m

g/L

Dis

solv

ed T

in (S

n)m

g/L

Dis

solv

ed T

itani

um (T

i)m

g/L

Dis

solv

ed T

ungs

ten

(W)

mg/

LD

isso

lved

Ura

nium

(U)

mg/

LD

isso

lved

Van

adiu

m (V

)m

g/L

Dis

solv

ed Z

inc

(Zn)

mg/

LD

isso

lved

Zirc

oniu

m (Z

r)m

g/L

Sul

phat

e (S

O4)

mg/

L

FP-1

Day

0FP

-1D

ay 7

FP-1

Day

13

FP-1

Day

21

FP-1

Day

28

FP-1

Day

35

FP-1

Day

42

FP-1

Day

49

FP-1

Day

55

FP-1

Day

63

FP-1

Day

70

FP-1

Day

77

FP-1

Day

84

FP-1

Day

91

FP-1

Day

98

FP-1

Day

105

FP-1

Day

112

FP-1

Day

119

FP-1

Day

126

FP-1

Day

133

FP-1

Day

140

07

1321

2835

4249

5563

7077

8491

9810

511

211

912

613

314

00

12

34

56

78

910

1112

1314

1516

1718

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1.00

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1.00

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1.74

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0.99

0.96

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0.95

1.12

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8.73

7.49

7.37

6.78

7.46

6.62

7.15

7.50

7.70

7.19

7.37

6.87

7.14

7.32

6.97

7.36

7.34

7.53

7.44

7.59

7.28

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0.04

0.06

0.07

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0.06

0.06

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0.11

0.06

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

2335

4642

4028

3035

2725

2930

3032

3533

3530

4033

33

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<36

6

Page 45: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 2

Com

pila

tion

of H

umid

ity C

ell T

est D

ata

Para

met

er

Da y

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kU

nits

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ume

Wat

er A

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ater

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lved

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imon

y (S

b)m

g/L

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solv

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rsen

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s)m

g/L

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solv

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ariu

m (B

a)m

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lium

(Be)

mg/

LD

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lved

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mut

h (B

i)m

g/L

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oron

(B)

mg/

LD

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lved

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miu

m (C

d)m

g/L

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solv

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alci

um (C

a)m

g/L

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solv

ed C

hrom

ium

(Cr)

mg/

LD

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lved

Cob

alt (

Co)

mg/

LD

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lved

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per (

Cu)

mg/

LD

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lved

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(Fe)

mg/

LD

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lved

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b)m

g/L

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LD

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lved

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gane

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n)m

g/L

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n (S

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LD

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lved

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ium

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LD

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lved

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ntiu

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r)m

g/L

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ulph

ur (S

)m

g/L

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halli

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l)m

g/L

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in (S

n)m

g/L

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itani

um (T

i)m

g/L

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ungs

ten

(W)

mg/

LD

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lved

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nium

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LD

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lved

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adiu

m (V

)m

g/L

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solv

ed Z

inc

(Zn)

mg/

LD

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lved

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oniu

m (Z

r)m

g/L

Sul

phat

e (S

O4)

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L

FP-2

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0FP

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98

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105

FP-2

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112

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119

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915

159

99

93

66

36

36

612

2121

3324

24

Page 46: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 2

Com

pila

tion

of H

umid

ity C

ell T

est D

ata

Para

met

er

Da y

Wee

kU

nits

Vol

ume

Wat

er A

dded

LV

olum

e W

ater

Rec

over

edL

pH--

-S

peci

fic C

ondu

ctan

cem

S

Aci

dity

as

CaC

03m

g/L

Alk

alin

ity a

s C

aC03

mg/

L

Dis

solv

ed A

lum

inum

(Al)

mg/

LD

isso

lved

Ant

imon

y (S

b)m

g/L

Dis

solv

ed A

rsen

ic (A

s)m

g/L

Dis

solv

ed B

ariu

m (B

a)m

g/L

Dis

solv

ed B

eryl

lium

(Be)

mg/

LD

isso

lved

Bis

mut

h (B

i)m

g/L

Dis

solv

ed B

oron

(B)

mg/

LD

isso

lved

Cad

miu

m (C

d)m

g/L

Dis

solv

ed C

alci

um (C

a)m

g/L

Dis

solv

ed C

hrom

ium

(Cr)

mg/

LD

isso

lved

Cob

alt (

Co)

mg/

LD

isso

lved

Cop

per (

Cu)

mg/

LD

isso

lved

Iron

(Fe)

mg/

LD

isso

lved

Lea

d (P

b)m

g/L

Dis

solv

ed M

agne

sium

(Mg)

mg/

LD

isso

lved

Man

gane

se (M

n)m

g/L

Dis

solv

ed M

olyb

denu

m (M

o)m

g/L

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solv

ed N

icke

l (N

i)m

g/L

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solv

ed P

hosp

horu

s (P

)m

g/L

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solv

ed P

otas

sium

(K)

mg/

LD

isso

lved

Sel

eniu

m (S

e)m

g/L

Dis

solv

ed S

ilico

n (S

i)m

g/L

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solv

ed S

ilver

(Ag)

mg/

LD

isso

lved

Sod

ium

(Na)

mg/

LD

isso

lved

Stro

ntiu

m (S

r)m

g/L

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solv

ed S

ulph

ur (S

)m

g/L

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solv

ed T

halli

um (T

l)m

g/L

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solv

ed T

in (S

n)m

g/L

Dis

solv

ed T

itani

um (T

i)m

g/L

Dis

solv

ed T

ungs

ten

(W)

mg/

LD

isso

lved

Ura

nium

(U)

mg/

LD

isso

lved

Van

adiu

m (V

)m

g/L

Dis

solv

ed Z

inc

(Zn)

mg/

LD

isso

lved

Zirc

oniu

m (Z

r)m

g/L

Sul

phat

e (S

O4)

mg/

L

VM-1

Day

0VM

-1D

ay 7

VM-1

Day

13

VM-1

Day

21

VM-1

Day

28

VM-1

Day

35

VM-1

Day

42

VM-1

Day

49

VM-1

Day

55

VM-1

Day

63

VM-1

Day

70

VM-1

Day

77

VM-1

Day

84

VM-1

Day

91

VM-1

Day

98

VM-1

Day

105

VM-1

Day

112

VM-1

Day

119

VM-1

Day

126

VM-1

Day

133

VM-1

Day

140

07

1321

2835

4249

5563

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9810

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211

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314

00

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34

56

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1112

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1.00

1.00

1.00

1.00

1.00

1.00

1.00

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1.00

1.76

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0.92

0.78

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0.85

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0.96

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0.97

0.98

8.05

7.61

7.19

7.47

7.94

7.34

7.94

8.09

8.10

8.01

7.75

7.57

7.01

7.68

8.07

7.56

7.04

7.65

7.51

7.51

7.27

0.07

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0.10

0.07

0.07

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0.08

0.08

0.06

0.07

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0.09

0.06

0.05

0.08

0.04

0.11

0.17

0.08

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

3463

5441

5343

3639

2747

3843

4243

4840

4833

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003

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003

<0.0

003

<0.0

003

<0.0

003

<0.0

003

<0.0

003

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003

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003

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003

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003

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003

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003

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01<0

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.001

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.001

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01<0

.001

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.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

<0.0

01<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

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02<0

.002

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02<0

.002

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02<0

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02<0

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<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

<0.0

02<0

.002

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1<0

.01

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.01

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1<0

.01

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.005

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05<0

.005

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05<0

.005

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05<0

.005

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05<0

.005

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05<0

.005

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05<0

.005

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05<0

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.005

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010.

002

0.00

20.

001

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.001

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.001

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10.

001

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.001

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03<0

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.003

0.00

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030.

006

0.00

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04<0

.004

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.004

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04<0

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04<0

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<0.0

04<0

.004

<0.0

04

912

129

99

96

69

69

66

66

63

<39

6

Page 47: Geochem Evaluation of Waste Rock in Hollinger Mine

App

endi

x 2

Com

pila

tion

of H

umid

ity C

ell T

est D

ata

Para

met

er

Da y

Wee

kU

nits

Vol

ume

Wat

er A

dded

LV

olum

e W

ater

Rec

over

edL

pH--

-S

peci

fic C

ondu

ctan

cem

S

Aci

dity

as

CaC

03m

g/L

Alk

alin

ity a

s C

aC03

mg/

L

Dis

solv

ed A

lum

inum

(Al)

mg/

LD

isso

lved

Ant

imon

y (S

b)m

g/L

Dis

solv

ed A

rsen

ic (A

s)m

g/L

Dis

solv

ed B

ariu

m (B

a)m

g/L

Dis

solv

ed B

eryl

lium

(Be)

mg/

LD

isso

lved

Bis

mut

h (B

i)m

g/L

Dis

solv

ed B

oron

(B)

mg/

LD

isso

lved

Cad

miu

m (C

d)m

g/L

Dis

solv

ed C

alci

um (C

a)m

g/L

Dis

solv

ed C

hrom

ium

(Cr)

mg/

LD

isso

lved

Cob

alt (

Co)

mg/

LD

isso

lved

Cop

per (

Cu)

mg/

LD

isso

lved

Iron

(Fe)

mg/

LD

isso

lved

Lea

d (P

b)m

g/L

Dis

solv

ed M

agne

sium

(Mg)

mg/

LD

isso

lved

Man

gane

se (M

n)m

g/L

Dis

solv

ed M

olyb

denu

m (M

o)m

g/L

Dis

solv

ed N

icke

l (N

i)m

g/L

Dis

solv

ed P

hosp

horu

s (P

)m

g/L

Dis

solv

ed P

otas

sium

(K)

mg/

LD

isso

lved

Sel

eniu

m (S

e)m

g/L

Dis

solv

ed S

ilico

n (S

i)m

g/L

Dis

solv

ed S

ilver

(Ag)

mg/

LD

isso

lved

Sod

ium

(Na)

mg/

LD

isso

lved

Stro

ntiu

m (S

r)m

g/L

Dis

solv

ed S

ulph

ur (S

)m

g/L

Dis

solv

ed T

halli

um (T

l)m

g/L

Dis

solv

ed T

in (S

n)m

g/L

Dis

solv

ed T

itani

um (T

i)m

g/L

Dis

solv

ed T

ungs

ten

(W)

mg/

LD

isso

lved

Ura

nium

(U)

mg/

LD

isso

lved

Van

adiu

m (V

)m

g/L

Dis

solv

ed Z

inc

(Zn)

mg/

LD

isso

lved

Zirc

oniu

m (Z

r)m

g/L

Sul

phat

e (S

O4)

mg/

L

VM-2

Day

0VM

-2D

ay 7

VM-2

Day

13

VM-2

Day

21

VM-2

Day

28

VM-2

Day

35

VM-2

Day

42

VM-2

Day

49

VM-2

Day

55

VM-2

Day

63

VM-2

Day

70

VM-2

Day

77

VM-2

Day

84

VM-2

Day

91

VM-2

Day

98

VM-2

Day

105

VM-2

Day

112

VM-2

Day

119

VM-2

Day

126

VM-2

Day

133

VM-2

Day

140

07

1321

2835

4249

5563

7077

8491

9810

511

211

912

613

314

00

12

34

56

78

910

1112

1314

1516

1718

1920

2.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.00

1.75

1.06

1.02

1.00

0.98

0.95

1.02

1.00

0.78

0.93

0.99

0.99

1.00

1.00

0.99

1.00

1.05

0.95

0.90

1.00

1.01

8.60

7.40

7.52

7.45

7.84

7.22

7.67

7.93

8.05

8.16

8.08

7.36

7.53

6.83

7.45

7.21

7.62

7.60

7.54

7.74

7.36

0.06

0.09

0.07

0.08

0.07

0.13

0.07

0.07

0.07

0.05

0.06

0.05

0.04

0.08

0.06

0.06

0.07

0.05

0.10

0.08

0.06

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

NM

2749

4051

4749

4044

2127

3330

3038

4042

4044

5744

39

0.15

0.19

0.24

0.27

0.33

0.38

0.26

0.31

0.17

0.19

0.21

0.19

0.17

0.17

0.19

0.22

0.24

0.29

0.18

0.21

0.23

<0.0

05<0

.005

<0.0

05<0

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05<0

.005

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05<0

.005

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05<0

.005

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05<0

.005

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05<0

.001

0.00

70.

008

0.01

0.00

90.

011

0.01

40.

015

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80.

011

0.01

40.

013

0.01

30.

013

0.01

50.

016

0.01

50.

014

0.01

10.

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0.01

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1<0

.01

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.01

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1<0

.01

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1<0

.01

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1<0

.01

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1<0

.01

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1<0

.01

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1<0

.01

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1<0

.01

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

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01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

01<0

.001

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.05

<0.0

5<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

1<0

.000

17.

37.

78.

39.

49.

410

.110

.910

.26.

38.

89.

89.

59.

510

.310

.611

.711

.29.

715

.112

.211

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.001

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.001

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01<0

.001

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.001

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01<0

.001

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01<0

.001

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01<0

.001

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.001

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01<0

.001

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01<0

.001

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01<0

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005

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005

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005

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005

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005

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005

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005

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005

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005

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005

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005

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005

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010.

002

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011.

46.

16

76.

45.

94.

85.

41.

84

44

4.3

3.7

4.1

5.2

4.3

4.3

6.5

4.3

4.4

0.00

40.

011

0.01

30.

010.

010.

011

0.01

50.

012

0.00

90.

013

0.01

60.

019

0.01

90.

020.

020.

022

0.02

0.01

40.

021

0.01

90.

017

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010.

001

0.00

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002

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.05

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53

32

22

21

1<1

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0.4

0.9

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0.9

0.9

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30.

70.

80.

70.

80.

70.

81

0.9

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17.

95.

63

21.

31.

20.

80.

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029

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23

33

33

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22

22

22

21

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.005

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.005

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<0.0

05<0

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010.

002

0.00

20.

002

0.00

10.

001

0.00

60.

001

<0.0

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0.00

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.001

<0.0

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010.

001

0.00

10.

001

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01<0

.001

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01<0

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<0.0

03<0

.003

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03<0

.003

<0.0

03<0

.003

<0.0

030.

004

<0.0

03<0

.003

<0.0

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.003

0.00

4<0

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.003

0.00

7<0

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.003

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04<0

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<0.0

04<0

.004

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.004

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.004

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.004

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.004

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<0.0

04<0

.004

<0.0

04

96

99

99

99

36

66

66

66

63

<36

6


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