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NI 43-101 Preliminary Economic Assessment - Verde Potash

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<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Cerrado <strong>Verde</strong> Project<br />

Minas Gerais, Brazil<br />

Prepared for:<br />

<strong>Verde</strong> <strong>Potash</strong> Plc<br />

47 Colborne Street, Suite 307<br />

Toronto, Ontario M5E 1P8<br />

Prepared by:<br />

7175 W. Jefferson Ave.<br />

Suite 3000<br />

Lakewood, Co 80235<br />

SRK Project Number: 3<strong>43</strong>500.020<br />

Effective Date: August 3, 2011<br />

Report Date: September 16, 2011<br />

Endorsed by Qualified Persons:<br />

Neal Rigby, CEng, MIMMM, PhD<br />

Rob Bowell, PhD, C.Chem MRSC, C. Geol FGS<br />

Volodymyr Myadzel, MAIG, PhD


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

i<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table of Contents<br />

1 INTRODUCTION (ITEM 2) ........................................................................................... 1-1<br />

1.1 Terms of Reference and Purpose of the Report ................................................... 1-1<br />

1.2 Reliance on Other Experts (Item 4) ..................................................................... 1-1<br />

1.2.1 Sources of Information ......................................................................... 1-2<br />

1.3 Qualifications of Consultants ............................................................................... 1-2<br />

1.3.1 SRK ....................................................................................................... 1-2<br />

1.3.2 BNA Consultoria e Sistemas ................................................................ 1-3<br />

1.3.3 ECM ...................................................................................................... 1-3<br />

1.3.4 AgroConsult Consultoria & Marketing ................................................ 1-3<br />

1.3.5 Site Visit................................................................................................ 1-3<br />

1.3.6 Effective Date ....................................................................................... 1-3<br />

2 PROPERTY DESCRIPTION AND LOCATION (ITEM 4) ........................................... 2-1<br />

2.1 Property Location................................................................................................. 2-1<br />

2.2 Mineral Titles ....................................................................................................... 2-1<br />

2.3 Location of Mineralization .................................................................................. 2-4<br />

2.4 Royalties, Agreements and Encumbrances .......................................................... 2-4<br />

2.5 Environmental Liabilities and Permitting ............................................................ 2-5<br />

3 ACCESSIBILITY, CLIMATE, LOCAL RESOURCES, INFRASTRUCTURE AND<br />

PHYSIOGRAPHY (ITEM 5) ...................................................................................................... 3-1<br />

3.1 Topography, Elevation and Vegetation ............................................................... 3-1<br />

3.2 Climate and Length of Operating Season ............................................................ 3-1<br />

3.3 Physiography........................................................................................................ 3-1<br />

3.4 Access to Property ............................................................................................... 3-2<br />

3.5 Surface Rights ...................................................................................................... 3-2<br />

3.6 Local Resources and Infrastructure ..................................................................... 3-2<br />

4 HISTORY (ITEM 6) ........................................................................................................ 4-1<br />

5 GEOLOGICAL SETTING AND MINERALIZATION (ITEM 7) ................................. 5-1<br />

5.1 Regional Geology ................................................................................................ 5-1<br />

5.2 Local and Project Geology ................................................................................... 5-1<br />

5.2.1 The <strong>Verde</strong>te Unit................................................................................... 5-1<br />

5.2.2 Structure ................................................................................................ 5-1<br />

5.2.3 Elevation and Erosion Level ................................................................. 5-2<br />

5.3 Mineralization ...................................................................................................... 5-2<br />

5.3.1 Mineralized Zones ................................................................................ 5-2<br />

5.3.2 Surrounding Rock Types ...................................................................... 5-3<br />

6 DEPOSIT TYPE (ITEM 8) .............................................................................................. 6-1<br />

7 EXPLORATION (ITEM 9) ............................................................................................. 7-1<br />

8 DRILLING (ITEM 10) .................................................................................................... 8-1<br />

8.1 Type and Extent of Drilling for Funchal Norte Target ........................................ 8-1<br />

8.1.1 Reverse Circulation (RC) Sampling ..................................................... 8-1<br />

8.1.2 Logging ................................................................................................. 8-1<br />

8.1.3 Bulk Density ......................................................................................... 8-1<br />

8.2 Type and Extent of Drilling for Targets 4, 6, 7, 10 and 11 .................................. 8-2<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

ii<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

8.2.1 Logging ................................................................................................. 8-3<br />

8.2.2 Recovery ............................................................................................... 8-3<br />

8.2.3 Reverse Circulation (RC) Sampling ..................................................... 8-4<br />

8.2.4 DDH Sampling...................................................................................... 8-4<br />

8.2.5 Bulk Density ......................................................................................... 8-4<br />

9 SAMPLE PREPARATION, ANALYSES AND SECURITY (ITEM 11) ...................... 9-1<br />

9.1 Sample Preparation and Assaying Methods for Funchal Norte Target ............... 9-1<br />

9.2 Sample Preparation and Assaying Methods for Targets 4, 6, 7, 10 and 11 ......... 9-1<br />

9.2.1 Quality Controls and Quality Assurance .............................................. 9-3<br />

9.2.2 Adequacy of Procedures for Targets 4, 6, 7 10 and 11 ......................... 9-3<br />

10 DATA VERIFICATION (ITEM 12) ............................................................................. 10-1<br />

10.1 Funchal Norte Target ......................................................................................... 10-1<br />

10.1.1 Bureau Veritas Pulp Duplicates .......................................................... 10-2<br />

10.1.2 Adequacy of Procedures ..................................................................... 10-2<br />

10.1.3 Limitations .......................................................................................... 10-2<br />

10.2 Targets 4, 6, 7, 10 and 11 ................................................................................... 10-2<br />

10.2.1 QA/QC Results ................................................................................... 10-2<br />

10.2.2 Data Import and Validation ................................................................ 10-4<br />

11 MINERAL PROCESSING, METALLURGICAL TESTING AND RECOVERY<br />

METHODS (ITEMS 13 AND 17) ............................................................................................. 11-1<br />

11.1 Summary of Proposed Process ........................................................................... 11-1<br />

11.1.1 Overview ............................................................................................. 11-1<br />

11.1.2 Project Scenarios and Capital Costs ................................................... 11-2<br />

11.1.3 Product Specification and Application ............................................... 11-3<br />

11.1.4 Results of Agronomic Testwork ......................................................... 11-4<br />

11.1.5 Summary, Residual Issues and Recommendations ............................. 11-6<br />

12 MINERAL RESOURCE ESTIMATE (ITEM 14) ........................................................ 12-1<br />

12.1 Funchal Norte Target ......................................................................................... 12-1<br />

12.1.1 Geological Modeling .......................................................................... 12-1<br />

12.1.2 Block Model Development ................................................................. 12-1<br />

12.1.3 Statistical Analysis .............................................................................. 12-2<br />

12.1.4 Variography ........................................................................................ 12-3<br />

12.1.5 Grade Estimation ................................................................................ 12-4<br />

12.1.6 Resource Reporting ............................................................................. 12-5<br />

12.2 Targets 4, 6, 7, 10 and 11 ................................................................................... 12-7<br />

12.2.1 Statistical Analyses of Geological Exploration .................................. 12-8<br />

12.2.2 Interpretation ..................................................................................... 12-10<br />

12.2.3 Triangulation ..................................................................................... 12-10<br />

12.2.4 Data Selection ................................................................................... 12-11<br />

12.2.5 Modeling ........................................................................................... 12-11<br />

12.2.6 Geostatistical Analysis ...................................................................... 12-12<br />

12.2.7 Grade Estimation and Resources Classification ............................... 12-12<br />

12.2.8 Assignment of Density Values to the Block Model .......................... 12-14<br />

12.2.9 Block Model Validation .................................................................... 12-14<br />

12.2.10 Resources Evaluation Results ........................................................... 12-15<br />

12.3 Mineral Resource Estimate .............................................................................. 12-16<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

iii<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

13 MI<strong>NI</strong>NG METHODS (ITEM 16) .................................................................................. 13-1<br />

13.1 Mining Operations ............................................................................................. 13-1<br />

13.1.1 Pit Optimization .................................................................................. 13-1<br />

13.1.2 Whittle Parameters .......................................................................... 13-1<br />

13.1.3 Pit Optimization Analysis ................................................................... 13-3<br />

13.1.4 Pit Design ............................................................................................ 13-4<br />

13.1.5 Production Schedule ........................................................................... 13-5<br />

13.1.6 Recovery ............................................................................................. 13-7<br />

14 PROJECT INFRASTRUCTURE (ITEM 18) ................................................................ 14-1<br />

14.1 Access Road and Transportation ....................................................................... 14-1<br />

14.2 Power Supply ..................................................................................................... 14-1<br />

14.3 Water Supply ..................................................................................................... 14-2<br />

14.3.1 Rainwater Drainage ............................................................................ 14-2<br />

14.3.2 Hydraulic Sizing ................................................................................. 14-2<br />

14.4 Buildings and Ancillary Facilities ..................................................................... 14-3<br />

14.5 Potential Processing Plant Sites ......................................................................... 14-3<br />

14.6 Potential Tailings Storage Area ......................................................................... 14-3<br />

14.7 Potential Waste Disposal Area ........................................................................... 14-3<br />

14.8 Manpower .......................................................................................................... 14-4<br />

14.9 Other Surface Rights .......................................................................................... 14-4<br />

15 MARKET STUDIES AND CONTRACTS (ITEM 19) ................................................ 15-1<br />

15.1 Market Studies ................................................................................................... 15-1<br />

15.1.1 Introduction ......................................................................................... 15-1<br />

15.1.2 Methodology ....................................................................................... 15-1<br />

15.1.3 Determining the Crop Portfolio and Formulas ................................... 15-2<br />

15.1.4 Formula Optimization Process ............................................................ 15-3<br />

15.1.5 Thermo<strong>Potash</strong> Pricing Process ........................................................... 15-4<br />

15.1.6 Process to Determine the Potential Market for Thermo<strong>Potash</strong> ........... 15-5<br />

15.2 Contracts ............................................................................................................ 15-5<br />

16 ENVIRONMENTAL STUDIES, PERMITTING AND SOCIAL OR COMMU<strong>NI</strong>TY<br />

IMPACT (ITEM 20) .................................................................................................................. 16-1<br />

17 CAPITAL AND OPERATING COSTS (ITEM 21) ..................................................... 17-1<br />

17.1 Capital Costs ...................................................................................................... 17-1<br />

17.1.1 Payback ............................................................................................... 17-2<br />

17.2 Operating Costs .................................................................................................. 17-2<br />

18 ECONOMIC ANALYSIS (ITEM 22) ........................................................................... 18-1<br />

18.1 Taxes and Royalties ........................................................................................... 18-2<br />

18.2 Sensitivity .......................................................................................................... 18-3<br />

18.3 Mine Life ........................................................................................................... 18-3<br />

19 ADJACENT PROPERTIES (ITEM 23) ........................................................................ 19-1<br />

20 OTHER RELEVANT DATA AND INFORMATION (ITEM 24) ............................... 20-1<br />

21 INTERPRETATION AND CONCLUSIONS (ITEM 25) ............................................ 21-1<br />

22 RECOMMENDATIONS (ITEMS 26) .......................................................................... 22-1<br />

22.1 Recommended Work Programs ......................................................................... 22-1<br />

22.1.1 Resources ............................................................................................ 22-1<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

iv<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

23<br />

24<br />

22.1.2 Metallurgical ....................................................................................... 22-1<br />

22.1.3 Mining ................................................................................................. 22-1<br />

22.1.4 Costs .................................................................................................... 22-2<br />

REFERENCES (ITEM 27) ............................................................................................ 23-1<br />

GLOSSARY .................................................................................................................. 24-1<br />

24.1 Mineral Resources ............................................................................................. 24-1<br />

24.2 Mineral Reserves ............................................................................................... 24-1<br />

24.3 Glossary ............................................................................................................. 24-2<br />

24.4 Abbreviations ..................................................................................................... 24-3<br />

List of Tables<br />

Table 1: Grade Tonnage Report Cerrado <strong>Verde</strong> <strong>Potash</strong> Project .................................................. IV<br />

Table 2: Indicative <strong>Economic</strong>s ....................................................................................................... V<br />

Table 3: Recommended Prefeasibility Work Program Cost Estimate (US$000’s) ....................... V<br />

Table 2.2.1: Cerrado <strong>Verde</strong> <strong>Potash</strong> Project Tenement Schedule ................................................ 2-1<br />

Table 8.1.1: Cerrado <strong>Verde</strong> <strong>Potash</strong> Project Summary Drilling Statistics ................................... 8-1<br />

Table 8.2.1: Drilling Statistics .................................................................................................... 8-3<br />

Table 8.2.2.1: Summarizes the Recovery Statistics .................................................................... 8-4<br />

Table 9.2.1: Detection Limits of XRF Analysis ......................................................................... 9-2<br />

Table 10.1.1: Standards Utilized by Bureau Veritas ................................................................. 10-2<br />

Table 11.1.2.1: Results of Carbon Speciation Analysis on Two Samples from the Scoping Level<br />

Pilot Plant ....................................................................................................................... 11-3<br />

Table 11.1.4.1: K content in soil (Mehlich 1) After 60 Days of Incubation with Different<br />

Sources of Potassium in a Clay Soil. ............................................................................. 11-4<br />

Table 11.1.4.2: K Content in Soil (Mehlich 1) After 60 Days of Incubation with Different<br />

Sources of Potassium in a Sandy Soil. ........................................................................... 11-4<br />

Table 11.1.4.3: Exchangeable Ca in the Soil After 60 Days of Incubation with Different Sources<br />

of Potassium in A Clay Soil ........................................................................................... 11-5<br />

Table 11.1.4.4: Exchangeable Ca in the Soil After 60 Days of Incubation with Different Sources<br />

of Potassium in a Sandy Soil ......................................................................................... 11-5<br />

Table 11.1.4.5: Exchangeable Mg in the Soil After 60 Days of Incubation with Different<br />

Sources of Potassium in a Clay Soil .............................................................................. 11-5<br />

Table 11.1.4.6: Exchangeable Mg in the Soil After 60 Days of Incubation with Different<br />

Sources of Potassium in a Sandy Soil ............................................................................ 11-6<br />

Table 12.1.2.1: Block Model Summary .................................................................................... 12-2<br />

Table 12.1.3.1: Summary Statistic – 2m Composites ............................................................... 12-2<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

v<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 12.1.4.1: Cerrado <strong>Verde</strong> Deposit Unweathered and Weathered Mineralized Domain<br />

Variogram Models ......................................................................................................... 12-3<br />

Table 12.1.6.1: Cerrado <strong>Verde</strong> Project Confidence Levels of Key Categorization Criteria .... 12-6<br />

Table 12.1.6.2: Cerrado <strong>Verde</strong> Deposit –February 27, 2010 Inferred Resource Grade Tonnage<br />

Report Ordinary Kriging Estimate 100mE x 100mN x 5mRL Selective Mining Unit . 12-6<br />

Table 12.2.1: Data Presentation ................................................................................................ 12-8<br />

Table 12.2.1.1: Descriptive Statistics Data for K 2 O of Target 4 .............................................. 12-9<br />

Table 12.2.1.2: Descriptive Statistics Data for K 2 O of the Target ........................................... 12-9<br />

Table 12.2.1.3: Descriptive Statistics Data for K 2 O of the Target 7 ........................................ 12-9<br />

Table 12.2.1.4: Descriptive Statistics Data for K 2 O of the Target 10 ...................................... 12-9<br />

Table 12.2.1.5: Descriptive Statistics Data for K2O of the Target 11 .................................... 12-10<br />

Table 12.2.5.1: Block Models Parameters .............................................................................. 12-12<br />

Table 12.2.6.1: Cross Validation Verification Results ........................................................... 12-12<br />

Table 12.2.7.1: Search Ellipse Parameters to Interpolate the Grades by the IDW And Kriging<br />

Methods of Target 6 ..................................................................................................... 12-13<br />

Table 12.2.7.2: Ellipse Search Parameters Used to Interpolate the Grades by the IDW Method<br />

for Target 4, 7, 10 and 11 ............................................................................................. 12-13<br />

Table 12.2.9.1: Comparison of metal tones and average K2O grade of the model, obtained by<br />

kriging and IDW2 methods to Target 6 ....................................................................... 12-14<br />

Table 12.2.9.2: Comparison of metal tonnes and average K2O grades, obtained by the Kriging<br />

method, the target to target 6 and by IDW2 for other targets, and polygonal solids<br />

evaluate by the "weighting intervals" method ............................................................. 12-15<br />

Table 12.2.10.1: Grade Tonnage Report for Target 6. Inverse Distance Weighting with power<br />

two (IDW2) estimate (Block Model - 50mE X 50mN X 10mRL) 7.5% K 2 O cut off<br />

utilized.......................................................................................................................... 12-15<br />

Table 12.2.10.2: Grade Tonnage Report for Target 7. Inverse Distance Weighting with power<br />

two (IDW2) estimate (Block Model - 50mE X 50mN X 10mRL) 7.5% K2O cut off<br />

utilized.......................................................................................................................... 12-16<br />

Table 12.2.10.3: Grade Tonnage Report for Target 4, Target 10 and Target 11. Inverse Distance<br />

Weighting with power two (IDW2) estimate (Block Model - 50mE X 50mN X 10mRL)<br />

7.5% K2O cut off utilized ............................................................................................ 12-16<br />

Table 12.3.1: Grade Tonnage Report Cerrado <strong>Verde</strong> <strong>Potash</strong> Project ..................................... 12-16<br />

Table 13.1.2.1: Whittle Block Model Dimensions ............................................................... 13-2<br />

Table 13.1.2.2: Whittle Parameters ....................................................................................... 13-3<br />

Table 13.1.3.1: Whittle Results ............................................................................................. 13-4<br />

Table 13.1.4.1: Pit Design Parameters ...................................................................................... 13-4<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

vi<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 13.1.5.1: First 10 Years of 1.1Mtpa Production Schedule .............................................. 13-5<br />

Table 13.1.5.2: First 10 Years of 2.2Mtpa Production Schedule .............................................. 13-6<br />

Table 13.1.5.3: 1.1Mtpa Product Mine Fleet and Annual Estimated Cost ............................... 13-6<br />

Table 13.1.5.4: 2.2Mtpa Product Mine Fleet and Annual Estimated Cost ............................... 13-7<br />

Table 15.1.3.1: Example of Fertilizing System Adopted for Each Crop Analyzed .................. 15-3<br />

Table 15.1.4.1: Price Composition of Raw Materials at the Uberaba Center ........................... 15-4<br />

Table 15.1.4.2: Raw Material Nutrient Levels ......................................................................... 15-4<br />

Table 15.1.4.3: Content Used and Status of Products Evaluated.............................................. 15-4<br />

Table 17.1.1: Summary Capital Cost by Facility in Reals and United States Dollars in thousands,<br />

Including Applicable Taxes for a 1.1Mtpa Operation ................................................... 17-1<br />

Table 17.1.2 Summary Capital Cost by Facility in Reals and United States Dollars in thousands,<br />

Including Applicable Taxes for a 2.2Mtpa Operation ................................................... 17-2<br />

Table 17.2.1: Summary of Operational Costs, 1.1Mtpa Using Petroleum Coke ...................... 17-3<br />

Table 17.2.2: Summary of Operational Costs, 2.2Mtpa using Petroleum Coke ....................... 17-3<br />

Table 18.1: Indicative <strong>Economic</strong>s ............................................................................................. 18-1<br />

Table 18.2.1: Sensitivity Analysis ............................................................................................ 18-3<br />

Table 22.1.4.1: Recommended Prefeasibility Work Program Cost Estimate (US$000’s) ....... 22-2<br />

Table 24.3.1: Glossary .............................................................................................................. 24-2<br />

Table 24.4.1: Abbreviations ...................................................................................................... 24-3<br />

List of Figures<br />

Figure 2-1: Location Map of Cerrado <strong>Verde</strong> <strong>Potash</strong> Project ...................................................... 2-6<br />

Figure 3-1: Cerrado <strong>Verde</strong> Project Site ...................................................................................... 3-4<br />

Figure 5-1: Cerrado <strong>Verde</strong> Regional Setting .............................................................................. 5-4<br />

Figure 5-2: Cerrado <strong>Verde</strong> Stratigraphic Chart According to LIMA, 2005 ............................... 5-5<br />

Figure 7-1: Reverse Circulation and Diamond Drilling Program for Targets 4 and 6 ............... 7-2<br />

Figure 7-2: Reverse Circulation and Diamond Drilling Program for Targets 7, 10 and 11 ....... 7-3<br />

Figure 8-1: Drillhole Location Plan ............................................................................................ 8-6<br />

Figure 8-2: RC Drilling Flowchart ............................................................................................. 8-7<br />

Figure 11-1: Conceptual Flowsheet for Cerrado <strong>Verde</strong> ThermoFertilizer Project ................... 11-7<br />

Figure 12-1: Vertical Sections Location ................................................................................. 12-17<br />

Figure 12-2: Cross Section (Section 4) ................................................................................... 12-18<br />

Figure 12-3: Cross Section (Section 5) ................................................................................... 12-19<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

vii<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Figure 12-4: Weathered (Transition Zone) Domain – 3 Dimensions ..................................... 12-20<br />

Figure 12-5: Unweathered Domain – 3 Dimensions .............................................................. 12-21<br />

Figure 12-6: Sample Length Distribution ............................................................................... 12-22<br />

Figure 12-7: Basic Statistics – 2m Composite Unweathered K 2 O ......................................... 12-23<br />

Figure 12-8: Basic Statistics – 2m Composite Weathered K 2 O ............................................. 12-24<br />

Figure 12-9: K 2 O % Estimation Steps – Plan View ............................................................... 12-25<br />

Figure 12-10: Block Model Domains High and Weathered ................................................... 12-26<br />

Figure 12-11: Grade Tonnage Curve – Domain Unweathered - Inferred Resource ............... 12-27<br />

Figure 12-12: Grade Tonnage Curve –Weathered- Inferred Resource ................................... 12-28<br />

Figure 12-13: Comparative Statistics Unweathered % K 2 O ................................................... 12-29<br />

Figure 12-14: Comparative Statistics % K 2 O Weathered ....................................................... 12-30<br />

Figure 12-15: Modeled Semi-variogram of the Top Grid ...................................................... 12-31<br />

Figure 12-16: Modeled Semi-variogram of the Base Grid ..................................................... 12-32<br />

Figure 12-17: Geologic Interpretation of Target 6 .................................................................. 12-33<br />

Figure 12-18: Geologic Interpretation of the Top and Base surfaces (Kriging method) ......... 12-34<br />

Figure 12-19: Geologic Interpretation of the Top and Base Surfaces of the Target 7 (IDW<br />

method with Power 2) .................................................................................................. 12-35<br />

Figure 12-20: Target 6 Mineralized Body Divided in Oxidized (Red) and Fresh (Green) Areas12-36<br />

Figure 12-21: Target 7 Mineralized Body Divided in Oxidized (Red) and Fresh (Green) areas12-37<br />

Figure 12-22: Search Ellipse (Radius 1) to Interpolate the Grades by the IDW and Kriging<br />

Methods to Target 6 ..................................................................................................... 12-38<br />

Figure 12-23: Search Ellipse (radius 2) to Interpolate the Grades by the IDW Method for Target<br />

4, 7, 10 and 11, and the Ore Body of the Target 7 ....................................................... 12-39<br />

Figure 12-24: Histogram and Probability Plot of the K 2 O Distribution of the Composite Samples<br />

(left) and the Block Model Interpolated by the IDW2 Method (right) of the Target 6 12-40<br />

Figure 12-25: Histogram and Probability Plot of the K 2 O Distribution of the Composite Samples<br />

(left) and the Block Model Interpolated by the IDW2 Method (right) of the Target 7 12-41<br />

Figure 12-26: Comparison of K 2 O Grades in the Samples and Blocks, Interpolated by the<br />

Kriging Method, of the Target 6 (central part .............................................................. 12-42<br />

Figure 12-27: Comparison of K 2 O Grades in the Samples and Blocks, Interpolated by the<br />

Kriging Method, of the Target 6 .................................................................................. 12-<strong>43</strong><br />

Figure 13-1: <strong>Preliminary</strong> Pit Design ......................................................................................... 13-8<br />

Figure 18-1: Annual Production and Cashflow for the 1.1Mtpa Production Case ................... 18-4<br />

Figure 18-2: Annual Production and Cashflow for the 2.2Mtpa Production Case ................... 18-5<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

List of Appendices<br />

Appendix A: Certificate of Author Forms<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

I<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Summary (Item 3)<br />

SRK Consulting (U.S.), Inc. (“SRK”) was mandated by <strong>Verde</strong> <strong>Potash</strong> Plc (“<strong>Verde</strong>”), formerly<br />

Amazon Mining Holding Plc, to prepare a National Instrument <strong>43</strong>-<strong>101</strong> (“<strong>NI</strong> <strong>43</strong>-<strong>101</strong>”)<br />

<strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> (“PEA”) on the Cerrado <strong>Verde</strong> Project (the “Project”) located<br />

in Minas Gerais, Brazil.<br />

This document provides a report on the results of mining, processing and a preliminary economic<br />

assessment of the potential project development. An update was made to the overall project<br />

resources, which now include Targets 4, 6, 7, 10 and 11. Targets 4, 6, 7, 10 and 11 resources are<br />

reported in addition to the existing Funchal Norte Target resources. The preliminary economic<br />

assessment is based only on the mineral resource estimate for the Funchal Norte Target as of<br />

March 1, 2011.<br />

Property Description and Location<br />

The Project is located in the Alto Paranaiba region of Minas Gerais State, Brazil. The<br />

boundaries of the concessions have not been surveyed as this is not a requirement of Brazil's<br />

mining code. The tenement boundaries are defined by UTM coordinates with the datum of<br />

SAD69 (Centered around coordinates 394,525 East and 7,856,531 North).<br />

Ownership<br />

Cerrado <strong>Verde</strong> mineral rights were originally requested by <strong>Verde</strong>, by means of applications for<br />

exploration licenses filed with DNPM between 2008 and 2010. Several Cerrado <strong>Verde</strong> mineral<br />

rights have been granted exploration licenses as presented in this report.<br />

<strong>Verde</strong> applied for the mineral rights directly to the DNPM. There was no prior ownership of<br />

mineral rights.<br />

Geology and Mineralization<br />

The region is mainly underlain by Neoproterozoic and Cretaceous rock units, which are partly<br />

covered by Cenozoic sandstones, lateritic sediments and soils. The oldest rocks, occurring in the<br />

southwestern portion of the region, are represented by a nucleus of calcoschists and diamictites<br />

of the Ibiá Formation (Araxá Group) surrounded by an undivided domain of the Canastra Group<br />

(quartzites, phyllites and micaschists). A model age of 1,000m.y. ( 207 Pb/ 206 Pb) has been<br />

determined for the Canastra Group, which was metamorphosed together with the Araxá Group<br />

during the Brasiliano Orogeny (600m.y.). The sequence is followed by the Bambuí Group (600-<br />

550m.y.), which comprises the marine deposits of the Paraopeba Formation, the Serra de Santa<br />

Helena Formation and the Serra da Saudade Formation, including the <strong>Verde</strong>te unit, all these units<br />

being dominated by variegated metasiltstones, and the overlying arkoses of the Três Marias<br />

Formation. After deposition of the Bambuí Group, and the Brasiliano Orogeny, the region was<br />

exposed to erosion during the Paleozoic, Triassic and Jurassic periods, giving rise to the<br />

development of a remarkable peneplane. In addition, the flat lying surface, the terrigenous<br />

sediments of the Areado Group was deposited during the Lower Cretaceous. The next<br />

stratigraphic phase is recorded by the extensive and dominantly pyroclastic kamafugitic<br />

volcanism of the Mata da Corda Group of Upper Cretaceous age.<br />

With some exceptions the <strong>Verde</strong>te unit, a potash rich rock are dominantly lying on top of the<br />

Serra da Saudade Formation and underlying the Areado sandstone. Its apparent thickness varies<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc<br />

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<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

from approximately 20m in the southernmost domain to over 50m in the northern half of the<br />

Serra da Saudade and up to 80m on the northern end where it started to be covered by younger<br />

sediments. The lower contact with the slates and metapelites of the Serra de Santa Helena<br />

Formation is transitional.<br />

Exploration<br />

<strong>Verde</strong> has completed remote sensing targeting exercise followed by regional mapping and grab<br />

samples. In addition, <strong>Verde</strong> completed a preliminary survey using an Innov-X portable XRF<br />

unit. The portable XRF unit was then correlated to pulp standards and showed good precision<br />

although returned a positive bias in the order of


<strong>Verde</strong> <strong>Potash</strong> Plc<br />

Cerrado <strong>Verde</strong> Project<br />

III<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Resource grades vary physically from an Unweathered zone on the western extent to a lower<br />

grade zone in the east. The grade distribution suggests two pits and multiple working faces can<br />

be open at all times for blending purposes feeding the process plant at a consistent 8.5% K 2 O.<br />

Two production scenarios were considered by SRK whereby 1.1Mtpa and alternately 2.2Mtpa of<br />

product would be produced annually. SRK conducted a pit optimization, pit design and<br />

production schedules to independently test the assumptions made in mine costing and reported in<br />

the economic model.<br />

Given the course nature of the resource model, the ability to sensitize or understand potential<br />

challenges to future mining operations is difficult to quantify. With a more refined and detailed<br />

block model containing lithology, grade and product distribution, the confirmation that the mine<br />

will produce the appropriate process plant feedstock can be verified and accurately estimated.<br />

This PEA is preliminary in nature. It includes inferred mineral resources that are considered too<br />

speculative geologically to have the economic considerations applied to them that would enable<br />

them to be categorized as mineral reserves. Mineral resources that are not mineral reserves do<br />

not have demonstrated economic viability. There is no certainty that the preliminary assessment<br />

will be realized.<br />

To accurately predict grade and quality of plant feedstock provided by the mine, a more<br />

complete understanding of the resource is required. In particular, the effect of K 2 O grade and<br />

mass yield calculations will effect what part of the mine is mined when and in what quantities.<br />

With a detailed infill drill program, continuation of metallurgical testing and further engineering<br />

studies SRK recommends additional work be dedicated to effect of mine dilution, possible effect<br />

of deleterious elements, construction of mining costs from first principles, RoM production<br />

targets, waste dump design and haul profiles for contractor estimation. This can be included as<br />

part prefeasibility study and will be required for any reserve generation in the future.<br />

Mineral Resource Estimate<br />

Volodymyr Myadzel, of BNA Consultoria e Sistemas Ltda (“BNA”) verified the Funchal Norte<br />

resource estimate provided by Coffey Mining as described in Section 12.1. SRK also verified<br />

this resource estimate on March 1, 2010.<br />

In addition, Dr. Myadzel constructed the geologic and resource model for Targets 4, 6, 7, 10 and<br />

11 as discussed in Section 12.2. Dr. Myadzel is responsible for the resource estimation<br />

methodology and the resource statement. Dr. Myadzel is independent of the issuer applying all<br />

of the tests in Section 1.5 of the <strong>NI</strong> <strong>43</strong>-<strong>101</strong>.<br />

The resource estimate has been undertaken in compliance with accepted Canadian Institute of<br />

Mining, Metallurgy and Petroleum (CIM) definitions for indicated and inferred resources in<br />

accordance with <strong>NI</strong> <strong>43</strong>-<strong>101</strong> Standards of Disclosure for Mineral Projects.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 1: Grade Tonnage Report Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Target Cutoff grade (%K 2 O) Tonnage (Mt) Average Grade (% K 2 O)<br />

Indicated<br />

Target 6 7.5 23.25 8.83<br />

Target 7 7.5 50.79 9.39<br />

Total Indicated 74.04 9.22<br />

Inferred<br />

Target 4 7.5 74.<strong>43</strong> 9.20<br />

Target 6 7.5 47.85 8.84<br />

Target 7 7.5 873.59 9.45<br />

Target 10 7.5 28.50 10.10<br />

Target 11 7.5 46.79 8.27<br />

Funchal Norte 10 64.39 11.17<br />

Total Inferred 1,135.55 9.47<br />

Mineral Resources are not Mineral Reserves and do not have demonstrated economic viability.<br />

Inverse Distance Weighting with power two (IDW2) estimate (Block Model - 50mE X 50mN X 10mRL).<br />

Effective date of Targets 4, 6, 7, 10 and 11 is August 3, 2011.<br />

Effective date of Funchal Norte is March 1, 2010.<br />

Indicative <strong>Economic</strong>s<br />

This document provides a report on the results of mining, processing and a preliminary economic<br />

assessment of the potential project development. An update was made to the overall project<br />

resources, which now include Targets 4, 6, 7, 10 and 11. Targets 4, 6, 7, 10 and 11 resources are<br />

reported in addition to the existing Funchal Norte Target resources. The preliminary economic<br />

assessment is based only on the mineral resource estimate for the Funchal Norte Target as of<br />

March 1, 2011.<br />

The indicative economics for the 1.1Mtpa (Base Case) and 2.2Mtpa production rates are<br />

presented in Table 2. This clearly demonstrates the very encouraging economics for the Cerrado<br />

<strong>Verde</strong> Projects based on the cost projections and price assumptions as presented in this PEA.<br />

However, readers are cautioned that this analysis is only a PEA based on indicated and inferred<br />

mineral resources, which are considered to be highly speculative geologically. Since there is no<br />

estimate of proven or probable reserves for the Project, this assessment cannot include cash flow<br />

forecasts on an annual basis.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 2: Indicative <strong>Economic</strong>s<br />

Production Rate 1.1Mtpy 2.2Mtpy<br />

Average Sales Price US$151.82/t US$133.23/t<br />

Total Production (40 year plan) 44,700kt 89,370kt<br />

Revenue US$6,786.6M US$11,906.8M<br />

Cashflow US$3,065.6M US$5,449.2M<br />

NPV (10%) US$445.5M US$844.1M<br />

NPV (12%) US$331.6M US$642.0M<br />

IRR 32.7% 40.0%<br />

Opex US$41.80/t US$36.36<br />

Initial Capex US$155.3M US$218.4M<br />

Contingency (15%) US$23.3M US$32.8M<br />

Pre-construction US$18.2M US$18.2M<br />

Total Capex US$196.8M US$269.4M<br />

Payback 2.38yrs 1.87yrs<br />

*Note: The above figures include a sustaining capital provision of 2% per annum of direct capital costs commencing in year 4.<br />

Conclusions and Recommendations<br />

Given the extensive resource base available; albeit all of which is in the indicated and inferred<br />

category, a mine life of 40 years has been assumed for both the 1.1Mtpa and 2.2Mtpa production<br />

rates.<br />

This clearly demonstrates the encouraging economics for the Cerrado <strong>Verde</strong> Projects based on<br />

the scoping study concepts, cost projections and price assumptions as presented in this PEA.<br />

SRK recommends that the Project be advanced in one phase of work to the prefeasibility level of<br />

evaluation and design. The cost estimate for the recommended work program is shown in Table<br />

3.<br />

Table 3: Recommended Prefeasibility Work Program Cost Estimate (US$000’s)<br />

Description<br />

Cost<br />

Infill Drilling 300<br />

Metallurgical Testwork 800<br />

Engineering Studies 500<br />

Environmental Baseline 150<br />

Other 250<br />

Total 2,000<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 1-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

1<br />

Introduction (Item 2)<br />

SRK Consulting (U.S.), Inc. (“SRK”) were mandated by <strong>Verde</strong> <strong>Potash</strong> Plc (“<strong>Verde</strong>”), formerly<br />

Amazon Mining Holding Plc, to prepare a National Instrument <strong>43</strong>-<strong>101</strong> (“<strong>NI</strong> <strong>43</strong>-<strong>101</strong>”)<br />

<strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> (“PEA”) on the Cerrado <strong>Verde</strong> Project (the “Project”) located<br />

in Minas Gerais, Brazil.<br />

1.1 Terms of Reference and Purpose of the Report<br />

This PEA is intended for the use of <strong>Verde</strong> to fulfill applicable securities obligations. This<br />

document provides a PEA of the Project, prepared according to <strong>NI</strong> <strong>43</strong>-<strong>101</strong> guidelines. Form <strong>NI</strong><br />

<strong>43</strong>-<strong>101</strong>F1 was used as the format for this report.<br />

This report is prepared using the industry accepted Canadian Institute of Mining, Metallurgy and<br />

Petroleum (CIM) “Best Practices and Reporting Guidelines” for disclosing mineral exploration<br />

information, the Canadian Securities Administrators revised regulations in <strong>NI</strong> <strong>43</strong>-<strong>101</strong> (Standards<br />

of Disclosure For Mineral Projects) and Companion Policy <strong>43</strong>-<strong>101</strong>CP, and CIM Definition<br />

Standards for Mineral Resources and Mineral Reserves (November 27, 2010).<br />

This document provides a report on the results of mining, processing and a preliminary economic<br />

assessment of the potential project development. An update was made to the overall project<br />

resources, which now include Targets 4, 6, 7, 10 and 11. Targets 4, 6, 7, 10 and 11 resources are<br />

reported in addition to the existing Funchal Norte Target resources. The preliminary economic<br />

assessment is based only on the mineral resource estimate for the Funchal Norte Target as of<br />

March 1, 2011.<br />

The PEA is based on inferred and indicated mineral resources only that are considered too<br />

speculative geologically to have the economic considerations applied to them that would enable<br />

them to be categorized as mineral reserves, and there is no certainty that the preliminary<br />

assessment will be realized. Mineral resources that are not mineral reserves do not have<br />

demonstrated economic viability.<br />

1.2 Reliance on Other Experts (Item 4)<br />

Section 15 of this report relies on AgroConsult Consultoria & Marketing (AgroConsult) for price<br />

and market analysis. AgroConsult prepared in depth analyses on the various agribusiness<br />

segments with a view to formulating short, medium and long term market trend reports on the<br />

main agricultural commodities as well as to developing customized studies and projects. In<br />

order to reach an average price per mixing center, the Thermo<strong>Potash</strong> benchmark price for each of<br />

the crops was weighted in accordance with the relevant demand potential. However, the average<br />

weighted price obtained reflects individual prices per crop. Consequently, the price would<br />

exceed the maximum price for some crops and the product would be too expensive. Therefore,<br />

the price was realigned to cater to 95% of the potential market. In this case, the resulting price is<br />

the potential price for Thermo<strong>Potash</strong> at the mixing center. Its complete results could be verified<br />

in the report prepared for <strong>Verde</strong> “Price and competitiveness survey for introducing<br />

Thermo<strong>Potash</strong> on the Brazilian fertilizer market” published in November of 2010.<br />

<strong>Verde</strong> provided geological data and information to BNA for Sections 5 through 9. The<br />

information provided was verified by BNA and accepted for the use in this report.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 1-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

<strong>Verde</strong> <strong>Potash</strong> retained Mr. Beau Nicholls, geologist, Dr. Gaspar Korndorfer, agronomist, Mr.<br />

Lupercio Oliveira, chemical engineer, and Mr. Ricardo Bandeira, lawyer, to provide scientific<br />

consulting services with respect to the Cerrado <strong>Verde</strong> Project.<br />

Mr. Beau Nicholls, MAIG consulting geologist to VERDE is the Qualified Person with respect<br />

to <strong>NI</strong> <strong>43</strong>-<strong>101</strong> at the Project.<br />

Mr. Lupércio Oliveira, chemical engineer, is pioneer in the studies of thermofertilizers and has<br />

been senior researcher in CETEC and past professor in Universidade Federal de Minas Gerais,<br />

Brazil. <strong>Verde</strong> <strong>Potash</strong> relies on Lupércio Oliveira on the conduction of the pilot plant where<br />

thermopotash has been produced.<br />

Dr. Gaspar Korndörfer is currently a Professor of Agriculture at the Universidade Federal de<br />

Uberlandia. He has a Post-Doctorate from University of Florida, US, and has earned his<br />

Doctorate on Soils and Plant Nutrition from ESALQ of the Universidade de São Paulo, Brazil.<br />

The company relies on Gaspar Korndörfer as agronomy consultancy and conductor of some<br />

agronomic tests.<br />

Mr. Ricardo Bandeira has worked with <strong>Verde</strong> <strong>Potash</strong> since the company was founded. He holds<br />

a Master’s degree in Civil Law from Pontifícia Universidade Católica de Minas Gerais, Brazil a<br />

Specialization degree in Strategic Management and Bachelor degree in Law from Universidade<br />

Federal de Minas Gerais, Brazil. He is a member of Brazilian Bar Associations. The company<br />

relies on Ricardo Bandeira as supervisor of legal matters including mineral rights and<br />

environmental permits.<br />

1.2.1 Sources of Information<br />

Information presented in this report has been provided by <strong>Verde</strong> and its consultants. Particularly<br />

for Sections 5 to 9. BNA has provided comment and reviewed the data and information<br />

provided and after all clarifications were made, accepted it. SRK has accepted this information<br />

and has provided comment and review of the data and information provided. Sources of<br />

information are provided in References Section 23.<br />

1.3 Qualifications of Consultants<br />

Listed below are the contributors to the PEA. Qualified Persons (“QP”) for this report are Dr.<br />

Neal Rigby and Dr. Rob Bowell of SRK, and Dr. Volodymyr Myadzel of BNA Consultoria e<br />

Sistemas Ltda (“BNA”). Descriptions of qualifications and responsibilities are presented below.<br />

1.3.1 SRK<br />

SRK is an independent, international consulting practice that provides focused advice and<br />

solutions to clients, mainly from earth and water resource industries. For mining projects, SRK<br />

offers services from exploration through feasibility, mine planning, and production to mine<br />

closure. Formed in 1974, SRK now employs more than 1,000 professionals internationally in 38<br />

permanent staffed offices on six continents.<br />

Dr. Neal Rigby<br />

Dr. Rigby is responsible for Sections 1 through 4, 10, 13 through 24 of this PEA.<br />

Dr. Rob Bowell<br />

Dr. Bowell is responsible for Sections 11 of this PEA.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 1-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

1.3.2 BNA Consultoria e Sistemas<br />

BNA Consultoria e Sistemas is a company dedicated to applying high technology to the mineral<br />

sector transforming it into sounding solutions. BNA offer effective solutions that consist of<br />

software systems and consulting services. Comprised of an experienced team of professionals<br />

with outstanding performance in the Brazilian mineral sector, having actively participated in<br />

relevant and important mine projects in Brazil.<br />

Dr. Volodymyr Myadzel<br />

Volodymyr Myadzel is responsible for Sections 5 through 9 and 12 of this PEA.<br />

1.3.3 ECM<br />

ECM, founded in 1984, is a Brazilian engineering company with extensive experience in<br />

developing multidisciplinary industrial projects of all sizes, including project design for the<br />

minerals and mining industry, from feasibility studies to plant commissioning. ECM has about<br />

550 employees and has been involved in significant mining projects over the past decade in<br />

Brazil.<br />

1.3.4 AgroConsult Consultoria & Marketing<br />

AgroConsult Consultoria & Marketing is a leading consulting company focused on agribusiness<br />

founded in 2000. Clients include: BHP Billiton, Bunge, Fosfertil, Petrobras, Heringer, Bayer,<br />

Santander, Citibank, John Deere, Banco do Brasil and Syngenta. AgroConsult’s team is<br />

comprised of a multi-disciplinary group of professionals who follow the market closely, prepare<br />

in depth analyses on the various agribusiness segments with a view to formulating short, medium<br />

and long term market trend reports on the main agricultural commodities as well as to<br />

developing customized studies and projects.<br />

1.3.5 Site Visit<br />

Mr. Volodymyr Myadzel, BNA Consultant, visited the Project site on March 15, 2011 and July<br />

20-22, 2011.<br />

1.3.6 Effective Date<br />

The effective date of this report is August 3, 2011.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 2-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

2<br />

Property Description and Location (Item 4)<br />

2.1 Property Location<br />

The Cerrado <strong>Verde</strong> <strong>Potash</strong> Project is situated in the Alto Paranaiba region of the State of Minas<br />

Gerais, Brazil (Figure 2-1). The project can be accessed from Belo Horizonte, the State capital<br />

to the town of Matutina in a distance of 320km, via a good quality paved road (BR-262). From<br />

Matutina the project area is accessed by a number of secondary gravel roads that connect the<br />

farming region.<br />

The project consists of sixty-four exploration licenses. The UTM Geographic zone is 23K and<br />

the Datum used for the area is World Geographic System 1984. The center of the project is<br />

approximately at longitude 46°00’W and latitude 19°20’S.<br />

2.2 Mineral Titles<br />

The Project comprises sixty four tenements, covering an aggregate area of 106,762ha as shown<br />

in Table 2.2.1 and Figure 2-1.<br />

Once an exploration license is granted, <strong>Verde</strong> must make annual fee payments to maintain the<br />

license, as explained in Section 17.6 of this report.<br />

Table 2.2.1: Cerrado <strong>Verde</strong> <strong>Potash</strong> Project Tenement Schedule<br />

Process Number Holder Size (Ha) Status of Mining Right Comments Mineral<br />

833329/2009 FVS 41.07 Exploration License valid until FVS informed the existence of<br />

Diamond<br />

29/10/2012<br />

potassium rocks at the area on<br />

833284/2008 FVS 1468.97 Exploration License valid until<br />

3/12/2012<br />

833264/2008 FVS 1511.58 Exploration License valid until<br />

18/11/2012<br />

833270/2008 FVS 1991.78 Exploration License valid until<br />

10/11/2012<br />

833276/2008 FVS 1334.71 Exploration License valid until<br />

18/11/2012<br />

833271/2008 FVS 1524.17 Exploration License valid until<br />

3/12/2012<br />

833252/2008 FVS 1993.71 Exploration License valid until<br />

3/12/2012<br />

833272/2008 FVS 1587.61 Exploration License valid until<br />

3/12/2012<br />

833256/2008 FVS 1994.32 Exploration License valid until<br />

3/12/2012<br />

833259/2008 FVS 1476.58 Exploration License valid until<br />

3/12/2012<br />

833266/2008 FVS 1230.03 Exploration License valid until<br />

3/12/2012<br />

833267/2008 FVS 1663.21 Exploration License valid until<br />

3/12/2012<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

833269/2008 FVS 1771.42 Exploration License valid until FVS informed the existence of Diamond<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 2-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Process Number Holder Size (Ha) Status of Mining Right Comments Mineral<br />

3/12/2012 potassium rocks at the area on<br />

28/01/2010.<br />

833290/2008 FVS 1678.42 Exploration License valid until<br />

3/12/2012<br />

833293/2008 FVS 1793.65 Exploration License valid until<br />

3/12/2012<br />

833294/2008 FVS 1492.78 Exploration License valid until<br />

3/12/2012<br />

833320/2008 FVS 1886.15 Exploration License valid until<br />

3/12/2012<br />

833331/2008 FVS 1366.49 Exploration License valid until<br />

3/12/2012<br />

833333/2008 FVS 1501.36 Exploration License valid until<br />

3/12/2012<br />

833328/2008 FVS 1790.21 Exploration License valid until<br />

3/12/2012<br />

833324/2008 FVS 1932.31 Exploration License valid until<br />

3/12/2012<br />

833335/2008 FVS 1575.41 Exploration License valid until<br />

3/12/2012<br />

833332/2008 FVS 1854.81 Exploration License valid until<br />

3/12/2012<br />

833334/2008 FVS 1914.94 Exploration License valid until<br />

3/12/2012<br />

833336/2008 FVS 1662.51 Exploration License valid until<br />

3/12/2012<br />

833647/2008 FVS 1907.6 Exploration License valid until<br />

13/11/2012<br />

833648/2008 FVS 1784.49 Exploration License valid until<br />

22/12/2012<br />

833330/2008 FVS 1464.51 Exploration License valid until<br />

3/12/2012<br />

833329/2008 FVS 41.07 Exploration License valid until<br />

24/3/2013<br />

833274/2008 FVS 1994.84 Exploration License valid until<br />

4/1/2013<br />

833253/2008 FVS 1716.04 Exploration License valid until<br />

12/3/2013<br />

833268/2008 FVS 966.82 Exploration License valid until<br />

12/3/2013<br />

833275/2008 FVS 1994.06 Exploration License valid until<br />

4/1/2013<br />

833277/2008 FVS 1992.24 Exploration License valid until<br />

4/1/2013<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

833278/2008 FVS 1993.88 Exploration License valid until FVS informed the existence of Diamond<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 2-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Process Number Holder Size (Ha) Status of Mining Right Comments Mineral<br />

4/1/2013 potassium rocks at the area on<br />

15/10/2010.<br />

833279/2008 FVS 1952.53 Exploration License valid until<br />

4/1/2013<br />

833285/2008 FVS 1993.69 Exploration License valid until<br />

4/1/2013<br />

833286/2008 FVS 19<strong>43</strong>.82 Exploration License valid until<br />

4/1/2013<br />

833297/2008 FVS 1985.37 Exploration License valid until<br />

4/1/2013<br />

833307/2008 FVS 1993.77 Exploration License valid until<br />

4/1/2013<br />

833311/2008 FVS 1993.88 Exploration License valid until<br />

4/1/2013<br />

833308/2008 FVS 1990.91 Exploration License valid until<br />

4/1/2013<br />

833316/2008 FVS 1994.21 Exploration License valid until<br />

4/1/2013<br />

833315/2008 FVS 1992.07 Exploration License valid until<br />

4/1/2013<br />

833325/2008 FVS 1916.57 Exploration License valid until<br />

4/1/2013<br />

833321/2008 FVS 1138.08 Exploration License valid until<br />

12/3/2013<br />

833319/2008 FVS 1993.72 Exploration License valid until<br />

4/1/2013<br />

833322/2008 FVS 1992.70 Exploration License valid until<br />

4/1/2013<br />

833327/2008 FVS 1916.57 Exploration License valid until<br />

4/1/2013<br />

831008/2009 FVS 244.98 Exploration License valid until<br />

1/6/2013<br />

833273/2008 FVS 1994.32 Exploration License valid until<br />

4/1/2013<br />

833292/2008 FVS 1935.96 Exploration License valid until<br />

4/1/2013<br />

833257/2008 FVS 1993.84 Exploration License valid until<br />

26/8/2012<br />

833263/2008 FVS 1844.23 Exploration License valid until<br />

29/10/2012<br />

833280/2008 FVS 1742.04 Exploration License valid until<br />

29/10/2012<br />

833295/2008 FVS 1571.46 Exploration License valid until<br />

29/10/2012<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

15/10/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

28/01/2010.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Phosphate<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

833306/2008 FVS 1712.36 Exploration License valid until FVS informed the existence of Diamond<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 2-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Process Number Holder Size (Ha) Status of Mining Right Comments Mineral<br />

29/10/2012 potassium rocks at the area on<br />

25/11/2009.<br />

833309/2008 FVS 1559.42 Exploration License valid until<br />

29/10/2012<br />

833326/2008 FVS 1920.21 Exploration License valid until<br />

29/10/2012<br />

833289/2008 FVS 1928.55 Exploration License valid until<br />

29/10/2012<br />

833305/2008 FVS 1555.92 Exploration License valid until<br />

29/10/2012<br />

833317/2008 FVS 1551,02 Exploration License valid until<br />

29/10/2012<br />

833323/2008 FVS 1536.42 Exploration License valid until<br />

29/10/2012<br />

83<strong>43</strong>89/2010 <strong>Verde</strong> 980.19 Exploration License valid until<br />

15/12/2013<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

FVS filed the “Positive Final Research<br />

Report” on 04/08/2011, which is the<br />

first document that backed the company<br />

to make an application for exploitation.<br />

On 08/08/2011 <strong>Verde</strong> also filed a<br />

request for a<br />

“Trial Mining” (in literal translation,<br />

the document that allows this trial<br />

exploitation is called by the Brazilian<br />

legislation as “Guide for utilization”).<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

FVS informed the existence of<br />

potassium rocks at the area on<br />

25/11/2009.<br />

Normal procedural progress – no<br />

comment<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Diamond<br />

Phosphate<br />

2.3 Location of Mineralization<br />

The potash mineralized zones of the Cerrado <strong>Verde</strong> Project are located within <strong>Verde</strong>te green<br />

metasiltstone of the Serra da Saudade Formation. The known mineralization is located in the<br />

concessions owned by <strong>Verde</strong>.<br />

2.4 Royalties, Agreements and Encumbrances<br />

The tenements are owned 100% by FVS Mineração Ltda. that is a subsidiary of <strong>Verde</strong>. The<br />

Cerrado <strong>Verde</strong> Project was staked in the third quarter of 2008. <strong>Verde</strong>’s subsidiary Amazon<br />

Pesquisa Mineral e Mineração Ltda (“APMM” – as of December 30, 2010, the name of this<br />

subsidiary has changed to <strong>Verde</strong> Fertilizantes Ltda) entered into a discovery contract (the<br />

“Cerrado <strong>Verde</strong> Project Discovery Contract”) dated September 29, 2008 (with retroactive term<br />

for July 26, 2008) with Ysao Munemassa (“Ysao”) pursuant to which Ysao performed, at<br />

<strong>Verde</strong>’s expense, preliminary geological surveys and research studies on the Cerrado <strong>Verde</strong><br />

Project area and the Cerrado <strong>Verde</strong> Project. The Cerrado <strong>Verde</strong> Project Discovery Contract was<br />

subsequently amended on July 27, 2010 to provide that APMM shall pay to Ysao: (a) 100,000<br />

Stock Options one year after the application for exploration permits over the Cerrado <strong>Verde</strong><br />

Project area to the National Department of Mineral Production (“DNPM”), (b) US$500,000 upon<br />

approval of a bankable feasibility study, and (c) a 3% royalty on the net result of production.<br />

APMM has the right to purchase the royalties due to Ysao at a cost of US$1,000,000 for each 1%<br />

of the protected right of royalty to Ysao.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 2-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

2.5 Environmental Liabilities and Permitting<br />

The Project has no environmental liabilities and has begun the preparation of the environmental<br />

reports required for the licensing of the Project, as it is stated in Section 16 of this technical<br />

report.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Location Map<br />

File Name: Figure_2-1.docx Date: 09/15/2011 Approved: NR Figure: 2-1


<strong>Verde</strong> <strong>Potash</strong> Plc 3-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

3<br />

Accessibility, Climate, Local Resources,<br />

Infrastructure and Physiography (Item 5)<br />

3.1 Topography, Elevation and Vegetation<br />

The peneplane developed by the <strong>Verde</strong>te unit, i.e., the ground over which the Areado Group was<br />

deposited, undulates between the altitudes of 1,000m and 850m. Higher values are found in the<br />

southern part of the Serra da Saudade range. In the middle portion of the ridge, the peneplane is<br />

placed between 880m and 920m. Therefore, all the surface exposures of the <strong>Verde</strong>te unit were<br />

the result of the Tertiary erosion cycles that stripped off the Mesozoic rocks (Mata da Corda and<br />

Areado groups).<br />

The local vegetation consists of relicts of the primitive savanna ("cerrado") still preserved<br />

between soya and coffee plantations and industrially planted forests of eucalyptus and pine trees.<br />

The farms are mainly confined to the fertile soil of the Mata da Corda Group that forms plateaux<br />

around 1,000m.<br />

3.2 Climate and Length of Operating Season<br />

The climate of the region is classified, according to IBGE (2002) as half-humid warm tropical,<br />

with annual average temperatures of 22°C Annual rainfall in the area averages between 1,300mm<br />

and 1,800mm, 84% of which falls during the rainy season between October and March, with the<br />

highest rainfall between December and January. Operations can be year round.<br />

3.3 Physiography<br />

The region is inserted in the hydrographic basin of Indaiá River, a tributary river in the left<br />

margin of São Francisco River. According to SECTES – Secretaria do Estado de Ciência e<br />

Tecnologia de Minas Gerais – (1938), Indaiá River basin is part of the geomorphological unit<br />

São Francisco Plateau where the planning surfaces, the edges of the hills and the crests point dip<br />

to NE, with high structural control (COSTA-FILHO et al, 2007).<br />

The main drainages are the rivers Indaiá, Abaeté, Borrachudo and their tributary. The<br />

morphology of those rivers is the meandering channels and the drainage style is dendritic, mainly<br />

when installed over the pelites. In the north of the area is the Três Marias dam, main mouth of<br />

the region rivers. The water depth of the dam oscillates between the altitudes of 560 and 575m<br />

(LIMA, 2005).<br />

The main topographic feature is the Serra da Saudade ridge. The landscape can be separated into<br />

three domains that may be correlated to the South American Surfaces (King, 1956):<br />

<br />

<br />

Upper Surface: Older stage of the planning that expose the Areado Group Sandstones and<br />

Mata da Corda Group;<br />

Intermediate Surface: Refer to the second stage of the planning after de dissection of the<br />

Upper Surface, triggered by the resumption of the erosive process. The average altitude<br />

is of 750 to 850m. They are irregular surfaces stretched in N-S strike, developed over the<br />

Serra da Saudade Formation represented by psamitic lithotypes. Matches to the South<br />

American Surface I, mio-pliocene; and<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 3-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Basal Surface: the youngest, bordering the São Francisco River, with elevations from 570<br />

to 630m. Exposure occurs in pelites of the Serra de Santa Helena and Serra da Saudade<br />

formations.<br />

3.4 Access to Property<br />

The project can be accessed by air from Rio de Janeiro, São Paulo, Brasilia and other cities, to<br />

Belo Horizonte, and then overland from Belo Horizonte to Matutina (approximately 320km), via<br />

a good quality paved road (BR-262). From the town of Matutina the project area is accessed by<br />

a number of secondary gravel roads that connect the farming region.<br />

The unpaved roads are in reasonable condition although some sections require improvement.<br />

3.5 Surface Rights<br />

According to Brazilian law, surface rights are separate from mining rights. Therefore, land<br />

owner has no title to the minerals contained in the soil or in the sub-soil, which are deemed a<br />

property of the Federal Government, which grant to private companies or individuals rights to<br />

exploration or exploitation.<br />

Private companies or individuals holding an Exploration Permit are supposed to enter into an<br />

agreement with the land owner allowing its access to the area in order to conduct exploration<br />

activities. In case an agreement is not reached, Brazilian Mining Code establishes a judicial<br />

procedure by means of which the mining company or individual secures access to the area by<br />

paying to the land owner compensation for damages in her/his property and loss of income due<br />

to exploration.<br />

<strong>Verde</strong> has agreements with the land owners to allow it to perform exploration in the targets<br />

selected by the company to research in the area located in the following DNPM Processes:<br />

833.263/2008, 833.270/2008, 833.274/2008, 833.280/2008, 833.287/2008, 833.289/2008,<br />

833.295/2008, 833.306/2008, 830.383/2008 and 833.323/2008. Private companies or individuals<br />

holding a Mining Concession are entitled to surface rights on the area necessary for the mine and<br />

ancillary structures. Such surface rights are obtained by agreement with the land owner,<br />

providing for compensation for the price of the land and additional losses caused by the<br />

occupation. In case such agreement is not reached, surface rights are granted by the local Court<br />

upon previous deposit by the mining company or individual of the amount judicially determined<br />

for such compensation.<br />

In addition to compensation for damages, the land owner is entitled to a royalty equal to 50% of<br />

CFEM. CFEM is federal royalty, which is established at 3.0% of the net sales of potash.<br />

However, it is common practice to negotiate a separate compensation agreement that is<br />

satisfactory to both parties.<br />

VERDE has not yet started to negotiate agreements with land owners for establishing<br />

exploitation and production activities.<br />

3.6 Local Resources and Infrastructure<br />

São Gotardo and Matutina are the closest towns with a significant population to provide<br />

manpower for a mining operation, having population around 40,000 combined. São Gotardo<br />

also has good infrastructure, with domestic power and telephone service available. Also, the<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 3-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

project is very close to Patos de Minas (129km away), the main city in the Alto Paranaiba area,<br />

which has a strong economic, cultural, educational and social environment.<br />

Belo Horizonte, located about 320km from the project site, is the capital and also the largest city<br />

in the state, with a population above 4 million. It is the major center for the Brazilian mining<br />

industry, with infrastructure for mining equipment and services available. There is a large<br />

commercial airport with domestic and international flights services. Several state and federal<br />

government agencies are based here, in addition to private businesses that provide services to the<br />

mining industry. Skilled labor is readily available in Belo Horizonte as well as at the towns of<br />

São Gotardo and Matutina near the site of the Project.<br />

Further discussion on project infrastructure is contained in Section 14.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Cerrado <strong>Verde</strong> Project Site<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_3-1 Date: 09/15/2011 Approved: NR Figure: 3-1


<strong>Verde</strong> <strong>Potash</strong> Plc 4-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

4<br />

History (Item 6)<br />

Cerrado <strong>Verde</strong> Mineral Rights were originally requested by <strong>Verde</strong>, by means of applications for<br />

exploration licenses filed with DNPM between 2008 and 2010. Several Cerrado <strong>Verde</strong> Mineral<br />

Rights have already been granted exploration licenses.<br />

<strong>Verde</strong> applied for the mineral rights directly to the DNPM. There was no prior ownership of<br />

mineral rights. The areas were available and <strong>Verde</strong> just had to make the necessary applications.<br />

<strong>Verde</strong> does not have data with respect to past owners or any prior exploration work. <strong>Verde</strong> is not<br />

aware of any historical resource estimation work on the property. There has been no historical<br />

mining on the property.<br />

There has been no prior exploration or development previous to the current owner. No historical<br />

resource estimates have been released. No historical mining of the <strong>Verde</strong>te has been undertaken.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 5-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

5<br />

Geological Setting and Mineralization (Item 7)<br />

5.1 Regional Geology<br />

The region is mainly underlain by Neoproterozoic and Cretaceous rock units, which are partly<br />

covered by Cenozoic sandstones, lateritic sediments and soils. The oldest rocks, occurring in the<br />

southwestern portion of the region, are represented by a nucleus of calcoschists and diamictites<br />

of the Ibiá Formation (Araxá Group) surrounded by an undivided domain of the Canastra Group<br />

(quartzites, phyllites and micaschists). A model age of 1,000m.y. ( 207 Pb/ 206 Pb) has been<br />

determined for the Canastra Group, which was metamorphosed together with the Araxá Group<br />

during the Brasiliano Orogeny (600m.y.). The sequence is followed by the Bambuí Group (600-<br />

550m.y.), which comprises the marine deposits of the Paraopeba Formation, the Serra de Santa<br />

Helena Formation and the Serra da Saudade Formation, including the <strong>Verde</strong>te unit, all these units<br />

being dominated by variegated slates, and the overlying arkoses of the Três Marias Formation.<br />

Following the deposition of the Bambuí Group, and the Brasiliano Orogeny, the region was<br />

exposed to erosion during the Paleozoic, Triassic and Jurassic periods, giving rise to the<br />

development of a remarkable peneplane. In addition, the flat lying surface, the terrigenous<br />

sediments of the Areado Group was deposited during the Lower Cretaceous. The next<br />

stratigraphic phase is recorded by the extensive and dominantly piroclastic kamafugitic<br />

volcanism of the Mata da Corda Group of Upper Cretaceous age.<br />

5.2 Local and Project Geology<br />

5.2.1 The <strong>Verde</strong>te Unit<br />

The <strong>Verde</strong>te unit occurs mainly at the top of the Serra da Saudade Formation and underlies the<br />

Areado Group sandstone. The Serra da Saudade Formation consists of carbonate and siliciclastic<br />

sediments that were deposited in an epicontinental platform in the late Neoproterozoic (700 –<br />

600Ma). The <strong>Verde</strong>te occurs in extensive outcrops, along both banks of Indaiá River, in a trend<br />

approximately 120km x 20km. It covers the regions of municipalities of Santa Rosa da Serra,<br />

São Gotardo and Guarda dos Ferreiros (SW), Matutina, Quartel São João and Cedro do Abaeté<br />

(centre), Paineiras and Biquinhas (NE), in the State of Minas Gerais.<br />

The thickness of the <strong>Verde</strong>te unit varies from 15 to 80m in the southernmost domain to over 50m<br />

in the northern half of the Serra da Saudade range. The lower contact with the metasiltstone of<br />

the Serra da Saudade Formation is transitional within 2-3m.<br />

The Serra da Saudade Formation was eroded during the Gondwana Cycle (King, 1956) of<br />

probably Jurassic age, and it was over this extensive peneplain that the cretaceous sandstone<br />

beds of the Areado Group were deposited.<br />

The upper contact is transitional with rhythmic intercalations of <strong>Verde</strong>te and metasiltstone with<br />

various colors (predominantly pink when weathered), defined informally as the Transition Zone.<br />

These intercalations vary from millimeters to meters in thickness.<br />

The lower contact with the metasiltstone of the Serra da Saudade Formation is transitional within<br />

2 to 3m, and contains intercalations of limestone lenses and calciferous metasiltstone.<br />

5.2.2 Structure<br />

The <strong>Verde</strong>te unit and the Transition Zone underwent two main phases of folding. The first<br />

resulted in the development of pervasive concentric and chevron folds, in which the axial planes<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 5-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

dip NNW. The strike of the foliation is NNE. The second phase formed folds with nearly<br />

vertical axial planes and sub-horizontal folding axis. In a regional scale, the folded <strong>Verde</strong>te and<br />

the transition zone display a sub-horizontal behavior.<br />

The largest extension of the <strong>Verde</strong>te unit occurs where the erosion has been less intense, and is<br />

marked by the presence of remnants of the Areado Group sandstones. This occurs mainly in the<br />

central part of the unit.<br />

5.2.3 Elevation and Erosion Level<br />

The peneplane developed by the <strong>Verde</strong>te unit, i.e., the ground over which the Areado Group was<br />

deposited, undulates between the elevation of 1,000m and 850m. Higher elevations are found in<br />

the southern part of the Serra da Saudade. In the middle portion of the ridge, the peneplane is<br />

placed between 880m and 920m. Therefore, all the surface exposures of the <strong>Verde</strong>te unit were<br />

the result of the Tertiary erosion cycles that stripped off the Mesozoic rocks (Mata da Corda and<br />

Areado groups).<br />

5.3 Mineralization<br />

<strong>Verde</strong>te is the rock-type with high content of K 2 O. It is pelitic sediment, metamorphosed in the<br />

greenschist facies. It displays a lepidoblastic texture and preserves relicts of the original fabric.<br />

Petrographically, it is classified as a metasiltstone, and has a green color due to chlorite. The<br />

chlorite was formed by the intense alteration of biotite. Biotite can still be observed locally in<br />

small plates forming massive aggregates. It also occurs in the cores of muscovite.<br />

The <strong>Verde</strong>te shows millimetric to centimetric bands rich in chlorite, interbedded with quartz-rich<br />

layers.<br />

A sample of <strong>Verde</strong>te containing 10.7% K 2 O showed the following modal composition: quartz<br />

(10%), microcline (20%), biotite-chlorite (60%) and muscovite (10%). Samples submitted for<br />

X-ray diffraction showed the following minerals: quartz, muscovite-fengite, microclineorthoclase<br />

and clinochlore (magnesium chlorite).<br />

The K 2 O content ranging from 5-6% to 13% is due to the presence of microcline-orthoclase and<br />

muscovite-fengite.<br />

This PEA is preliminary in nature. It includes inferred mineral resources that are considered too<br />

speculative geologically to have the economic considerations applied to them that would enable<br />

them to be categorized as mineral reserves. Mineral resources that are not mineral reserves do<br />

not have demonstrated economic viability. There is no certainty that the preliminary assessment<br />

will be realized.<br />

5.3.1 Mineralized Zones<br />

As stated previously, potash mineralization occurs associated with the microcline-orthoclase and<br />

muscovite-fengite minerals that are constituents of the <strong>Verde</strong>te.<br />

The <strong>Verde</strong>te held within the <strong>Verde</strong> tenements can be traced for the entire 120km strike length<br />

with a potential width up to 500m wide. Grab samples along the entire strike length range from<br />

5% to 12% K 2 O.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 5-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

5.3.2 Surrounding Rock Types<br />

The <strong>Verde</strong>te unit is partially covered by a thin layer of sandstone of Cretaceous age in its central<br />

part. To the east it is intercalated with red to yellow metapelites (argillites, rhythmites and<br />

siltstones), which forms the transition zone. The transition zone is the basal part of the <strong>Verde</strong>te<br />

unit and crops out by a combination of folding and erosion. To the west the <strong>Verde</strong>te is eroded by<br />

a N-S running creek which exposes the underlying carbonatic slate. To the north the <strong>Verde</strong>te<br />

unit is again intercalated with metapelites. To the south the <strong>Verde</strong>te is abruptly eroded,<br />

occurring only as the metapelites and slates.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Cerrado <strong>Verde</strong> Regional Setting<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_5-1.docx Date: 09/15/2011 Approved: NR Figure: 5-1


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Cerrado <strong>Verde</strong> stratigraphic<br />

chart according LIMA, 2005<br />

File Name: Figure_5-2.docx Date: 09/15/2011 Approved: NR Figure: 5-2


<strong>Verde</strong> <strong>Potash</strong> Plc 6-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

6<br />

Deposit Type (Item 8)<br />

No geological model has yet been proposed for the potash-rich <strong>Verde</strong>te metasiltstone. It is a<br />

unique type of mineralization that is known only in the Serra da Saudade Formation in the<br />

western part of the State of Minas Gerais. Presently, the <strong>Verde</strong>te is not a commercial source of<br />

potash.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 7-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

7<br />

Exploration (Item 9)<br />

The present exploration work applies to the <strong>Verde</strong>te units known as Target-4, Target-6, Target-7,<br />

Target-10 and Target-11 (Figures 7-1 and 7-2).<br />

The exploration included field and laboratory studies; geological mapping in scales 1:25,000 and<br />

1:10,000; outcrop studies and their correlation; drilling on the <strong>Verde</strong>te body; systematic<br />

sampling; chemical and physical analysis of the rock samples and drill core samples; processing<br />

and characterization testing.<br />

Initially, it was performed a bibliographic compilation of all the material about the project and<br />

surrounding areas, along with studies of economic exploitation of the potash present in silicatic<br />

rocks such as the <strong>Verde</strong>te, including technological and market aspects. The maps used as a<br />

cartographic base were the topographic map SE-23-Y-D-II 1:100.000 (Dores do Indaiá Sheet)<br />

from IBGE (government institute), the geological maps SE-23-Y-D 1:250.000 (Bom Despacho<br />

Sheet) and SE-23-YD-II 1:100.000 (Dores do Indaiá Sheet) from the Projeto São Francisco, as<br />

well as maps from theses and dissertations.<br />

Afterwards, it was performed the integration of the geological, geophysical, and geochemical<br />

information in regional scale, developing analysis and interpretation of digital satellite images<br />

for the visualization of the regional structures and occurrences of <strong>Verde</strong>te.<br />

The outcrops of the <strong>Verde</strong>te unit can be distinguished on satellite images by their characteristic<br />

green color.<br />

In the preliminary survey, the targets were defined using Google Earth images and data from<br />

SRTM (Shuttle Radar Topography Mission). These data can be found freely available on the<br />

website of EMBRAPA (government company), in form of a land numerical model grid, with<br />

90m resolution.<br />

In the first field research, held in 2008, a mapping of the main rock types present in the region<br />

was performed, on a 1:25,000 scale, as well as a survey of the access, drainage and farms of the<br />

area. For this survey were used GPS devices from Garmin ® , model GPSMAP 76 CSX.<br />

A preliminary evaluation of the potash levels on outcrop samples was made through a portable<br />

X-ray fluorescence device, followed by chemical analysis at laboratory.<br />

Later stages of field work consisted of the performance of regional geological cross sections,<br />

especially in the areas of <strong>Verde</strong>te exposure, and semi-detail mapping campaigns for recognition<br />

of the main lithofacies, stratigraphic relations and structural aspects. During the mapping, the<br />

samples collected were used to make thin sections and lithochemical and mineralogical analysis.<br />

It was collected structural data and some stratigraphic sections surveys were made.<br />

Besides surface mapping, a drilling program was made, performing 142 drill holes by a<br />

rotopercussive reverse circulation drill and 5 twin drill holes by a diamond drill.<br />

The main chemical analyses were made at ALS Minerals, Bureau Veritas, FRX Service, SGS<br />

Geosol laboratories in Vespasiano and Belo Horizonte cities, Minas Gerais State, and at the<br />

Laboratório de Caracterização Tecnológica da Escola Politécnica da USP in São Paulo State.<br />

The office works consist of the data compilation and integration, followed by the resource<br />

calculation using ARCGIS ® and MICROMINE ® software.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Reverse circulation and diamond<br />

drilling program for targets 4 and<br />

6<br />

File Name: Figure_7-1 Date: 09/15/2011 Approved: NR Figure: 7-1


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Reverse circulation and diamond<br />

drilling program for targets 7, 10 and<br />

11<br />

File Name: Figure_7-2 Date: 09/15/2011 Approved: NR Figure: 7-2


<strong>Verde</strong> <strong>Potash</strong> Plc 8-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

8<br />

Drilling (Item 10)<br />

8.1 Type and Extent of Drilling for Funchal Norte Target<br />

A drilling program was undertaken in early 2010 and has targeted only a select portion of the<br />

regional <strong>Verde</strong>te within the <strong>Verde</strong> tenements as shown in Figure 2-1. Figure 8-1 shows the<br />

location of the 15 drillholes completed by <strong>Verde</strong>. All holes were successful in intersecting the<br />

<strong>Verde</strong>te.<br />

The principal methods used for exploration drilling at Cerrado <strong>Verde</strong> have been reverse<br />

circulation drilling (RC). Table 8.1.1 summarizes pertinent drilling statistics. The main zone has<br />

been drilled at a nominal spacing of 100m to 400m.<br />

Table 8.1.1: Cerrado <strong>Verde</strong> <strong>Potash</strong> Project Summary Drilling Statistics<br />

Company/Year Drillholes Meters Contractor Drill Rig Diameter<br />

<strong>Verde</strong> / 2010 19 997 Fuad Rassi Engenharia Indústria Prominas R1-H 4.5”<br />

e Comerécio Ltda<br />

All drillholes have been drilled vertical to an average of 52m deep. No downhole surveys have<br />

been completed due to the short vertical holes and scale of mineralization. The drilling has been<br />

completed perpendicular to mineralization and as such all intercepts reflect the true thickness.<br />

Drillhole collars were surveyed by <strong>Verde</strong> surveyors using a portable GPS with accuracy of +/-<br />

5m.<br />

Accuracy of the survey measurements (downhole and surface) meets acceptable industry<br />

standards for the style of mineralization.<br />

The drilling completed has been compiled into a 3D geological model as defined in section 15,<br />

Mineral Resources, interpretation of drilling is also covered in this section.<br />

8.1.1 Reverse Circulation (RC) Sampling<br />

The samples were taken on 2m intervals and riffle split down to 3kg samples. Sample weights<br />

were not recorded but recoveries were reported as good. The RC method of sampling is not<br />

optimal and SRK would recommend that a Jones Riffle Splitter be utilized in future RC sampling<br />

programs. Although the quartering technique used by <strong>Verde</strong> is not optimal the homogenous<br />

nature of the <strong>Verde</strong>te will remove any sampling bias created.<br />

8.1.2 Logging<br />

Drill samples were sieved during drilling and a small sample of the chips was stored in chip trays<br />

for future reference.<br />

Basic weathering and lithologies were recorded by the geologists and entered into a digital<br />

database.<br />

Detailed geologic logging of the chips should be done to determine subtle changes within the<br />

formation that could be correlated with changes in grade of K 2 O<br />

8.1.3 Bulk Density<br />

<strong>Verde</strong> utilized a consulting group, ConcreSolo, to undertake Bulk Density measurements.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 8-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Coffey Mining has reviewed the methodology used by ConcreSolo, and noted that the 22<br />

samples measured the saturated Bulk Density of grab samples collected from surface.<br />

Coffey Mining considers that given the apparent leached zone in the first 10m of drilling that<br />

down hole samples should be undertaken, to determine if there is any change in density with<br />

depth.<br />

Coffey Mining also considers that saturated bulk density measurements are not appropriate for<br />

resource estimation. Dry bulk density should be determined. Saturated bulk density<br />

measurements will result in a positive bias, as it is the weight of the rock plus the water that is<br />

absorbed into the rock. The result is an over estimation of the tonnage by the moisture content.<br />

Additional dry bulk density measurements are required.<br />

The dry bulk densities should be determined at several intervals down hole (across the thickness<br />

of the section) and specifically in reference to the weathered vs. the Unweathered portions of the<br />

deposit. A number of dry bulk densities should also be taken along strike and averaged to come<br />

up with a valid density to calculate tonnage.<br />

8.2 Type and Extent of Drilling for Targets 4, 6, 7, 10 and 11<br />

Two drilling campaigns were performed. Three reverse circulation drill rigs (RC), belonging to<br />

Geosedna Perfurações Especiais S/A were used in the first campaign, which started in January<br />

2011 and finished in June 2011. These three drills (Foremost, Prominas and Explorac), drilled a<br />

total of 9,059m in 142 holes. The second campaign, which started in February 2011 and April<br />

2011 drilling amounted to 412m in five twinned RC/diamond drill holes (DDH).<br />

The 142 RC boreholes were drilled using 4¾" and 5" hammers to an average depth of 58m in a<br />

400m x 400m grid (approximately).<br />

The purpose of the twinned holes was to confirm the geology and describe, in detail, the<br />

lithological and mineralogical variations of the intercepted units, besides providing material for<br />

density measurements. All holes were vertical, and drilled to an average depth of 82m.<br />

Drillhole diameter was HQ and NQ. The drill used was a Diakor II, belonging to ISOÁgua Ltda.<br />

Downhole deviation surveys are not required in view of the shallow depth to which the holes<br />

were drilled.<br />

The drilling was carried out perpendicular to the mineralization and reflects its true thickness.<br />

Table 8.2.1 represents the number of holes for each target, and the average depth reached.<br />

The coordinates of the holes were surveyed using a Trimble ® Pathfinder Pro XR differential<br />

GPS. The data had post-correction validated by the IBGE with reference to the Santiago &<br />

Cintra station in Belo Horizonte (vertex 93,621; East 608,308.23m, North 7,799,827.00m,<br />

879.06m altitude (HAE) – recording rate: 0.5s, C/ A code + L1). All azimuth, distances, areas<br />

and perimeters were calculated following the UTM planar projection system, SAD69 datum, MC<br />

–45W and 23K zone. The accuracy of the measurements (borehole and surface) is within<br />

acceptable standards, considering the type of mineralization. The accuracy is approximately 1<br />

cm after 45 minutes of satellites tracking.<br />

The drilling data are compiled into a 3D geological model, as described later in the chapter<br />

"Mineral Resource and Mineral Reserve Estimates", detailed in the Section 15 of this Technical<br />

Report. The interpretation of the drilling results will also be made in this section.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 8-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 8.2.1: Drilling Statistics<br />

RC Drilling<br />

DC Drilling<br />

Prospect<br />

Quantity<br />

of holes<br />

Average<br />

depth (m)<br />

Meters<br />

drilled<br />

Results Received<br />

(# holes)<br />

Results<br />

Received (m)<br />

Quantity<br />

of holes<br />

Average<br />

depth (m)<br />

Target-11 9 49 542.00 9 <strong>43</strong>2.00 0 -<br />

Target-10 5 50 250.00 5 250.00 0 -<br />

Target-7 77 65 6,345.00 77 5,147.00 3 87.00<br />

Target-4 7 72 509.00 7 509.00 0 -<br />

Target-6 22 57 1,255.00 22 1,255.00 2 76.00<br />

Total 120 58 8,901.00 120 7,593.00 5 82.00<br />

8.2.1 Logging<br />

The RC chip samples are sieved at the field and small amounts are stored in chip trays. Each<br />

tray has chips from 30m drilled. The chips are described by the lithology, and also by the color<br />

and degree of weathering. The DDH core is placed in core boxes.<br />

The weathering, regolith and lithology, including the petrographic features are recorded by the<br />

geologists, as well as the recording of basic geotechnical observations (RQD – rock quality<br />

designation, weathering degree and IRS – impact resistance degree) are entered into a digital<br />

database and the information stored on a log sheet. Logging is performed in the core shed where<br />

the cores are stored.<br />

After the core is logged the boxes are photographed as a precaution against accident as well as<br />

the deterioration of the core box. The core boxes are photographed in pairs. The photographs<br />

are taken over a fixed assembly holding a camera for consistency of lighting. The photographs<br />

are edited on the computer. The borehole identification, number of the core box and the interval<br />

contained are all recorded, the database has a file with all the photographs of every core boxes.<br />

8.2.2 Recovery<br />

In the reverse circulation drilling, the recovering determinations were made considering that the<br />

bag containing that interval is weighed and the weight is compared with the reference value,<br />

using the formula below:<br />

% Rec=<br />

∗ <br />

<br />

Where, the cylinder volume (Cv) is calculated by the formula:<br />

Cv = π* R 2 *h = 3.14* 6.35 2 *100 = 3.1415 * 40.32 * 100 = 12,666.5 cm 3 * 2.3 = 29.132 kg<br />

For DDH, the recovery determinations were made by a measuring tape. The value for the core<br />

measured is compared to the value noted on the wooden information tag. Each rush has an<br />

average of 1.5m. Using the formula: recovered core x 100 / run= recovered percentage. The<br />

maximum percentage was 100%. Table 8.2.2.1 summarizes the recovery statistics.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 8-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 8.2.2.1: Summarizes the Recovery Statistics<br />

Prospect Average Recovery (%)<br />

Target-4 88.0<br />

Target-6 89.8<br />

Target-7 88.9<br />

Target-10 96.9<br />

Target-11 94.1<br />

8.2.3 Reverse Circulation (RC) Sampling<br />

RC samples are collected every 1 to 3m rush, and placed in a large plastic bag, weighed on a<br />

balance, and the weight noted by the supervisor. A small sample is also taken from the bag and<br />

placed into a chip tray for visual inspection and future logging by the geologist. The main water<br />

intersections encountered by drilling are also captured by the supervisor on site. The cyclone is<br />

cleansed by compressed air after every rod drilled.<br />

The sampling intervals were selected after a preliminary analysis by the portable XRF<br />

spectrometer. The cover rocks are not sampling. <strong>Verde</strong>te intervals containing above 6% of K 2 O<br />

were selected. A safety margin was given in these intervals. This margin ranging from 1 to 5m,<br />

taking as reference the content of 6% of K 2 O and variations up to 2% below this level. The<br />

results obtained were integrated in a spreadsheet and passed via a personal digital assistant<br />

(PDA) to the sampling responsible at the shed.<br />

At the shed, the sample is split repeatedly in a riffle splitter until a representative sample of<br />

approximately 1.3kg is obtained. This sample is destined for preparation and laboratory<br />

analyses. The riffle splitter is beaten with a rubber mallet and cleaned with compressed air after<br />

every sample, to avoid sample contamination. The wet and moist samples are split using a<br />

hollow plastic cylinder with a sharpened tip. This cylinder is projected into the sample bag, in<br />

order to perforate it in several different places. The material from the bag that is returned within<br />

the cylinder is then sampled. Approximately six punches are sufficient to obtain a representative<br />

sample of the meter interval drilled (Figure 8-2). These samples are transported to the SGS<br />

Geosol laboratories for further processing.<br />

8.2.4 DDH Sampling<br />

After logging testing the drill core selected is cut. The core is cut lengthwise by a diamond saw.<br />

One half of the core is sent for analysis and the other is retained in the core box.<br />

The samples, with a length of 2m, are packed in a plastic bag, with the identification number<br />

written with a marker on the sample together with an identification tag. The bag is placed inside<br />

another, sealed with clamps and likewise identified. All data related to sampling are recorded in<br />

a log table for subsequent correlation with the analytical results.<br />

8.2.5 Bulk Density<br />

Density measurements are made on DDH core samples. After the geological description the drill<br />

core is sawn in half. The weathered and fresh lithological units are then chosen for dry density<br />

measurements. Intervals of 10cm to 15cm are selected from the half of the drill cores.<br />

The top and the base from each section of drill core are marked and the depth recorded on the<br />

density spreadsheets for each hole. The samples are placed in labeled aluminum trays and dried<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 8-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

in electric oven with temperature of approximately 90°C for 24 hours. Using half of the drill<br />

cores assures that all internal humidity is removed from the drill core.<br />

After cooling, each sample is wrapped in Boreda ® tinfoil transparent PVC film (vinyl<br />

polychloride resin) and weighed in air by a OHAUS Adventurer ® digital balance, approved by<br />

Inmetro (the National Institute of Metrology, Normalization and Industrial Quality), with a<br />

precision of at least 2 hundredths of a gram.<br />

The sample is then completely immersed in water through a suspended steel hook attached to the<br />

central beam of the balance. The immersed weight is then recorded. Thereafter, the sample is<br />

returned to its respective place in the drill core box. The dry density calculation is made using<br />

the Archimedes Principle.<br />

Density determinations were made at the sample preparation section at VERDE in 7 samples of<br />

weathered <strong>Verde</strong>te, obtaining an average density of 1.49g/cm 3 ; and in 65 samples of fresh<br />

<strong>Verde</strong>te, with an average density of 2.11g/cm 3 .<br />

Density determinations were also made at SGS Geosol Laboratories Ltda, located at km 24.5 of<br />

Highway MG 10, Vespasiano, Minas Gerais. Measurements were made in 2 samples of<br />

weathered <strong>Verde</strong>te, obtaining an average density of 1.85g/cm 3 ; and 22 samples of fresh <strong>Verde</strong>te,<br />

with an average density of 2.09g/cm 3 . The measurements are made using the same methodology<br />

than VERDE, spending the Archimedes Principle. The weigh is determinate by a SARTORIUS<br />

TE2145 ® digital balance, with includes calibration with <strong>NI</strong>ST traceable certification and a<br />

precision of at least 4 hundredths of a gram.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Drillhole Location Plan<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_8-1.docx Date: 09/16/11 Approved: NR Figure: 8-1


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

RC Drilling Flowchart<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_8-2.docx Date: 09/15/2011 Approved: NR Figure: 8-2


<strong>Verde</strong> <strong>Potash</strong> Plc 9-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

9<br />

Sample Preparation, Analyses and Security<br />

(Item 11)<br />

9.1 Sample Preparation and Assaying Methods for Funchal Norte<br />

Target<br />

All samples following drilling were sent via a <strong>Verde</strong> vehicle to the Bureau Veritas laboratory in<br />

Belo Horizonte for analysis. All sample reject, pulps and chip trays are stored at the <strong>Verde</strong> base<br />

in Belo Horizonte.<br />

All samples have been prepared and analyzed by Bureau Veritas in Belo Horizonte.<br />

The samples were received then dried, crushed to 2mm and riffle split; and<br />

Samples were analyzed by XRF for Fe 2 O 3 , SiO 2 , Al 2 O 3 , CaO, MgO, MnO, TiO 2 , Na 2 O,<br />

K 2 O, BaO, P 2 O 5 , Cr 2 O 3 , SrO and LOI.<br />

Bureau Veritas insert duplicates, blanks and certified standards at a rate of 5% to maintain their<br />

quality control.<br />

9.2 Sample Preparation and Assaying Methods for Targets 4, 6, 7, 10<br />

and 11<br />

The aliquots for the laboratory were prepared in the office. Initially, the six firsts holes drilled<br />

were sampled meter by meter and the others were made samples every 2m. The homogenization<br />

was the first stage of the preparation. In one corner of a tarpaulin of 2 x 2m were disposed<br />

samples of 1m (from the six first holes) or of 2m (for the other holes drilled). Next, the bulk was<br />

rolled in a unique way (clockwise or counter-clockwise) raising the edges of the tarpaulin until<br />

the sample became homogeneous in terms of distribution of color and granulometry. After<br />

mixing, the sample was divided into four equal parts (splitting). In this fourth part of the sample<br />

aliquots were separated for the lab, for archive (chips). To collect the first two aliquots, a quarter<br />

of the material was distributed on the tarpaulin in a linear shape, and then small portions were<br />

collected randomly with a shovel. These aliquots were properly packaged, labeled and weighed<br />

between 2kg and 2.5kg. Something around 1kg to 2kg was separated to 5mm, and the fraction<br />

upper than 5mm was filed in core boxes, identified with name of the hole, size and number of<br />

laboratory sample. The fraction under 5mm was discarded. The other three quarters of the<br />

sample were archived.<br />

The aliquots for the laboratory were prepared in the shed at the project site, by the VERDE<br />

technicians and sent in a <strong>Verde</strong> vehicle to the SGS Geosol Laboratórios Ltda (“SGS”), laboratory<br />

with ISO 9001:2008 and ISO 14001:2004 certifications, located at km 24.5 of Highway MG 10,<br />

Vespasiano, Minas Gerais State, for analysis. All sample reject, pulps and chip trays are stored<br />

at the <strong>Verde</strong> base in Matutina.<br />

After receiving the samples at the SGS, the request for analysis and the inclusion in the CCLAS<br />

system, the samples are checked. Physical preparation quality controls are introduced by the<br />

laboratory, which include a preparation blank (quartz) and duplicate at every 20 samples. The<br />

samples are dried at 105±5°C and passed through the crusher with 95% of the sample passing at<br />

2mm. Afterwards the fractionation of the sample is made to approximately 600g (RSD or Riffles<br />

depending on the mass to fractionate). The powdering is made with 95% passing at 150#,<br />

forming the laboratory aliquot and the reserved pulp. At this stage, the laboratory quality control<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 9-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

is obtained by the inclusion of a reagent blank, certified reference materials and a laboratory<br />

duplicate within each analytical run. The blank is inserted at the beginning, standards at every<br />

20 samples and duplicate are inserted at random intervals. If necessary, additional quality<br />

control samples can be added. All data gathered for quality control samples is automatically<br />

captured by the CCLAS software, sorted and retained in the QA/QC database. The SGS quality<br />

management system complies with the requirements of International Standards ISO 9001:2008.<br />

After the loss on ignition (LOI) analysis, the analytical aliquot preparation is made by fusion<br />

with lithium tetraborate in the fusion machine with oxygen enriched flame – Phoenix ® (XRF<br />

Scientific). In this method, a calcined sample (0.5g) is added to the lithium borate fusion (50%<br />

Li 2 B 4 O 7 – 50% LiBO 2 ), mixed and fused between 1,050° and 1,100° C. The machine uses a<br />

mold which incorporates a crucible shape in which both mixing and mixing and molding is<br />

performed. When mixing is complete the molten material is cooled in the moldable and the bead<br />

is then removed using a suction cup. The analysis of the fused tablet is made by X-Ray<br />

Fluorescence Spectrometer – Axios mAX -Minerals ® (PANalytical). The samples were analyzed<br />

for Fe 2 O 3 , SiO 2 , Al 2 O 3 , CaO, MgO, MnO, TiO 2 , Na 2 O, K 2 O, P 2 O 5 , and LOI. The detection<br />

limits are described in Table 9.2.1.<br />

Sample<br />

Dry (105°C)<br />

Crush (95% @ 2mm)<br />

Fractionate<br />

Powder (95% @ 150#)<br />

LOI analysis<br />

Fusion with lithium tetraborate<br />

X‐ray flourescence analysis<br />

Quality control<br />

Table 9.2.1: Detection Limits of XRF Analysis<br />

Item Al 2 O 3 CaO Fe 2 O 3 K 2 O MgO MnO Na 2 O P 2 O 5 SiO 2 TiO 2<br />

Limit of Detection (%)


<strong>Verde</strong> <strong>Potash</strong> Plc 9-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

9.2.1 Quality Controls and Quality Assurance<br />

At the time of the drilling for Funchal Norte Target, <strong>Verde</strong> did not have appropriate internal<br />

QA/QC systems. Future drilling should include at least one twinned hole from the existing set<br />

that has good QA/QC in place that could be used to verify the values from the present reverse<br />

circulation drilling program.<br />

In May 2010, <strong>Verde</strong> introduced a QA/QC program. For the internal control reference, at every<br />

20 routine samples, a certified standard, a powder blank and a duplicate was inserted and sent to<br />

laboratory.<br />

Initially, duplicates were prepared from the splitting of previous sample pulp. After analysis at<br />

SGS laboratory, the pulp were returned and forwarded to analysis at the ALS Brasil Ltda<br />

laboratory, located at Vespasiano, Minas Gerais State. From there, the pulps were sent to ALS<br />

laboratory located in Lima, Peru for analysis. The pulps are analyzed by XRF and LOI. The<br />

ALS quality management system complies with the requirements of the International Standards<br />

ISO 9001:2008 and ISO/IEC 17025:2005. Quality control samples are inserted within each<br />

analytical run. Form XRF methods, the minimum number of QA/QC samples are 2 standards, 1<br />

duplicate and 1 blank, introduced every 39 samples. The blank is inserted at the beginning,<br />

standards are inserted at random intervals, and duplicates are analyzed at end of the batch. Every<br />

batch of samples are analyzed has a dual approval and review process. The individual analytical<br />

runs are monitored and approved by the analyst. The results are compared with the initial values<br />

of SGS in graphics for duplicate controls like Thompson and Howarth, QQ and Correlation plots.<br />

This procedure was adopted until sample CV-RCS-2151.<br />

From March 2011 on, starting at the sample CV-RCS-2171, the duplicate was obtained by<br />

quartering the routine sample, verifying, in that way, the whole laboratory sample preparation<br />

process.<br />

For the accuracy control, the Australian GeoStats Phosphate certified reference material and<br />

Brazilian Instituto de Pesquisas Tecnológicas reference material were used. There were<br />

submitted to SGS for conventional XRF analysis. The standards certificates are attached at the<br />

end of this report.<br />

The blank material was prepared from pulverized quartz obtained from a Brazilian laboratory<br />

Sulfal Química Ltda. At the time, the company did not have appropriate internal contamination<br />

control. Gravel blank composed by quartz will be provided to verify the contamination of the<br />

sample preparation.<br />

For the external control reference, after analysis at the SGS laboratory, pulps were selected from<br />

routine samples, spaced 20 by 20 and sent to analysis at ALS.<br />

9.2.2 Adequacy of Procedures for Targets 4, 6, 7 10 and 11<br />

The Geosol SGS laboratory, which were performed the preparation and the chemical analysis of<br />

the bulk samples, was inspected in July 12. The inspection of the sample preparation room<br />

confirmed that the procedure described above is satisfactory. The preparation rooms and<br />

equipment are kept clean, and upon the completion of each shift, these rooms are cleaned up. All<br />

laboratories and each equipment is provided with ventilation system and exhaust fans. All<br />

instruments are in serviceable condition. The laboratory operates according to international<br />

standards and the risk of error in chemical analysis can be assessed as low.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 10-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

10<br />

Data Verification (Item 12)<br />

10.1 Funchal Norte Target<br />

<strong>Verde</strong> did not carry out a proper QA/QC program. The current QA/QC analysis is the internal<br />

Bureau Veritas program.<br />

5% of samples sent to the Bureau Veritas were then sent to SGS in Belo Horizonte to undertake<br />

an umpire sample.<br />

In the QA/QC program implemented by <strong>Verde</strong> in May 2010, as the analytical results are<br />

received, they are immediately imported into the respective sampling spreadsheets, where any<br />

undesirable analytical deviations of standards, blanks, duplicates, or inconsistency between the<br />

sample result and its respective lithology can be easily compared. Simple inversions of sample<br />

results and typing errors of the spreadsheets after receiving the certificates, are also common and,<br />

therefore, all the results of all samples must be checked one by one and not only the control<br />

samples introduced.<br />

The accuracy, precision and contamination of the analysis should be evaluated.<br />

All reference materials require validation, to check the level of accuracy and reliability of the<br />

laboratories. The mistakes detected in the analytical procedures are identified and evaluated<br />

having as reference the precision of the method.<br />

The results for the certified reference materials (standard samples) must be between the limits of<br />

2.SD (twice the standard deviation).<br />

The validation method of the blank samples consists in verifying the presence of the analyte.<br />

Therefore it is necessary to observe the detection limit of the method.<br />

If there is any analysis deviation of the control samples or inconsistencies with the respective<br />

lithologies, the batches should be re-examined and eventually re-sampled. Depending on the<br />

situation, and certifying that there could not have been any mistake on sampling (which is<br />

common), the costs of re-examination will be on the laboratory. If the blank values are very<br />

high, the method of sample preparation should be checked. If all values for the standards are off<br />

the defined limits, the digestion method of the samples should be checked. When the results of<br />

standards and blanks are following a same trend, higher or lower than expected, the analysis for<br />

all the batch of samples sent should be repeated, including the reference ones.<br />

Besides the analysis of the results obtained, an unannounced visit to the laboratory is<br />

programmed to check the conditions of the analysis.<br />

Only after all results from each batch of samples are checked and validated, can information be<br />

fed into the database.<br />

The final validation of the results obtained is performed by an independent consultant (Qualified<br />

Person).<br />

Coffey Mining has reviewed the QA/QC results returned by Bureau Veritas as presented in Table<br />

10.1.1.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 10-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 10.1.1: Standards Utilized by Bureau Veritas<br />

Standard<br />

Expected<br />

ValueK 2 0% +/-10% (EV) Failed<br />

IPT 146 0.04 0.034 and<br />

0.042<br />

No of<br />

Analyses Minimum (%) Maximum(%) Mean (%)<br />

5 6 0 .07 0.05<br />

IPT 53 12.1 10.89 and 0 6 11.95 12.61 12.18<br />

13.31<br />

IPT53+IPT146 6.07 5.46 and 6.67 0 6 5.84 6.36 6.07<br />

Pulp Blank 0


<strong>Verde</strong> <strong>Potash</strong> Plc 10-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Information about internal quality control was presented as a single data batch, without<br />

separation of the samples by grade ranges. Two evaluation methods were used, simple linear<br />

regression and QQ (Quantile Quantile) plot.<br />

One of the parameter used in the results analyzes was the precision. Precision is a measure of<br />

how well the Y value represents the X value. It is most commonly used in assay quality control,<br />

where X is the first assay value and Y is the matching repeat assay. A perfect result has a<br />

precision of zero. Values of greater than zero represent an increasing amount of deviation; for<br />

example a precision of 10% indicates that the difference between X and Y varies by around 10%<br />

of X. The tests for K 2 O, P 2 O 5 , Al 2 O 3 , Fe 2 O 3 , SiO 2 , MgO and TiO 2 , had a high quality and<br />

accuracy in the statistical analysis, with precision accuracy lower than 5%. For MnO and Na 2 O,<br />

the tests showed a precision accuracy lower than 15%, and for CaO, the tests showed a precision<br />

accuracy higher than 15%. The numbers of tests provided are statistically representative.<br />

Precision of the Chemical Analysis<br />

The sampling precision was evaluated using the method of repeated analysis for K 2 O, P 2 O 5 ,<br />

CaO, Al 2 O 3 , Fe 2 O 3 , SiO 2 , MgO, TiO 2 , MnO, Na 2 O and LOI. In a total of 3244 samples, 108<br />

were re-examined, representing 3.3% of the total number of tests.<br />

Information on internal quality control was presented as a single data batch, without separation<br />

of the samples by grade ranges. Was used two evaluation methods, simple linear regression and<br />

QQ (Quantile Quantile) plot.<br />

In general, the tests for K 2 O, Al 2 O 3 , Fe 2 O 3 , MgO, TiO 2 and SiO 2 , had a high quality and<br />

accuracy in the statistical analysis, with accuracy higher than 5%. To P 2 O 5 , CaO, MnO and<br />

Na 2 O, tests showed a precision up to 12%.<br />

The correlation coefficient of the samples values of regular control is above 0.9, allowing it to<br />

conclude that tests for the most important elements for the mineralization in study were<br />

conducted with a satisfactory and acceptable accuracy.<br />

Inaccuracy<br />

The inaccuracy was determined as a difference in Fe 2 O 3 , SiO 2 , Al 2 O 3 , P 2 O 5 , Mn, TiO 2 , CaO,<br />

MgO, K2O, Na2O e LOI in samples, between the values determined by SGS and those<br />

determined by an independent laboratory ALS.<br />

The external control was conducted for the purpose of determination of systematic inaccuracy in<br />

the results of principal analytical laboratory. The value of the systematic inaccuracy was<br />

estimated by the same formula as used for the internal control.<br />

The number of repeated tests is 119, which is 3.6% from the total number of tests 3244.<br />

In whole, the analysis of data for each laboratory demonstrates good precision of data with high<br />

coefficient of correlation R > 0.98.<br />

The total number of control external tests is sufficient. According to the analysis of external<br />

control data, the accuracy of principal laboratories can be rated as satisfactory.<br />

Standards<br />

For quality control were used 174 standard samples, which represent 5.3% of the total number of<br />

analyzed samples.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 10-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Standard GPO-11 (<strong>43</strong> analysis results);<br />

Standard GPO-12 (<strong>43</strong> analysis results);<br />

Standard GPO-13 (54 analysis results);<br />

Standard GIOP-27 (8 analysis results);<br />

Standard IPT-53 (21 analysis results); and<br />

Standard IPT-72 (5 analysis results).<br />

Four types of standard GPO-11, GPO-12, GPO-13 and IPT-53 were analyzed, and the results<br />

were analyzed using the Shewhart Control Chart. Statistical analysis was performed for the<br />

following elements Fe 2 O 3 , SiO 2 , Al 2 O 3 , P 2 O 5 , MnO, TiO 2 , CaO, MgO, K 2 O and Na 2 O.<br />

The analyzed results, provided by SGS, present problems when compared with known results.<br />

Blank Samples<br />

For quality control were used 174 blank samples, representing 5.3% of the total number of<br />

samples analyzed.<br />

When discussing the use methodologies of the blank samples with <strong>Verde</strong> Fertilizantes Ltda.<br />

team, it was certified that powder material was sent to the laboratory.<br />

The purpose of using blank samples is attempting to quantify the contamination of samples<br />

during the preparation process. This objective was not achieved whereas the blank samples were<br />

sent to a laboratory as powder, not subject to potential contamination involved in the preparation<br />

process and reduction of other samples. This makes it unnecessary to analyze the results<br />

obtained for the blank samples to quantify the possible errors in the preparation of other samples.<br />

Conclusions<br />

It was certified that the tests relating to duplicate samples were conducted with an acceptable and<br />

satisfactory accuracy to the most important elements of the mineralization under study.<br />

There are possibilities of error in the methodology of sample analysis. Therefore, the results of<br />

sample analysis with known grades were not within the expected mean range.<br />

The methodology for the use of blank samples, as has been said, is not correct.<br />

Despite the unsatisfying results for the standards samples and the incorrect methodology used for<br />

the blank samples, the risk of errors in chemical analysis can be assessed as low.<br />

10.2.2 Data Import and Validation<br />

Data Local Validation<br />

The client did not provide information about the data local validation, so this procedure was not<br />

performed by BNA Consultoria e Sistemas.<br />

Data Validation Performed in MICROMINE Software<br />

The analytical database was exported to the format *.xls, and then imported into MICROMINE ®<br />

software. After this process, the imported database was validated using specific processes to find<br />

the following possible errors:<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 10-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

The drillhole name is present in the collar coordinate file, but is missing in the analytical<br />

database;<br />

The drillhole name is present in the analytical database, but is missing in the collar<br />

coordinate file;<br />

The drillhole name appears repeated in the analytical database and in the collar<br />

coordinate file;<br />

The drillhole name is not present in the collar coordinate file and in the analytical<br />

database;<br />

One or more coordinates notes are missing from the collar coordinate file;<br />

From or to are not present in database analysis;<br />

From > to in analytical database;<br />

Sampling intervals are not continuous in analytical database (there are breaks between the<br />

records);<br />

Sampling intervals are overlapping in the analytical database;<br />

The first sample does not correspond to 0 m in the database analysis;<br />

The azimuth is not in the range from 0 to 360 degrees;<br />

The dip angle is not in the range from 0 to 90 degrees;<br />

Azimuth or dip angle of the drillhole is missing; and<br />

The drillhole total depth is less than the depth of the last sample.<br />

The topography and cartography geological files in *.shp format were converted to the<br />

MICROMINE ® formats.<br />

Although the data do not provide a suitable structure, the validation results were satisfactory,<br />

being found only one error in the entire database.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 11-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

11<br />

Mineral Processing, Metallurgical Testing<br />

and Recovery Methods (Items 13 and 17)<br />

The Project's objective is to produce a thermo-fertilizer in the form of calcined potassium pellets,<br />

with diameters between 2 and 4mm, to be produced at <strong>Verde</strong> facilities, located at São Gotardo –<br />

MG. The primary feed material is a metasiltstone (<strong>Verde</strong>te) that typically contains 8 to 10%<br />

K 2 O The project base case is the production of 1.1Mt of thermo-fertilizer per year 8.34% K 2 O<br />

with an expected life of around 100 years at this level of production.<br />

The process approach is summarized in the conceptual flowsheet in Figure 11-1. Recovery is<br />

discussed in Section 13.1.6.<br />

11.1 Summary of Proposed Process<br />

11.1.1 Overview<br />

<strong>Verde</strong>te is mechanically extracted from the quarry is reclaimed by front loaders which load a 25-<br />

50t truck fleet. Prior blasting is regarded to be unnecessary for the majority of the quarry<br />

extension, due to the friability of the ore.<br />

Fragments up to 500mm will be discharged into a 60m 3 capacity bin, and will be screened in a<br />

75mm fixed grizzly. Oversized ore will be retained at this grizzly and then will be disaggregated<br />

through a jaw crusher. Material passing from the grizzly, finer than 75mm, along with the<br />

primary crusher product feed will be conveyed into the secondary crushing circuit.<br />

Material is fed to a 40m 3 bin which feeds a vibrating screen from which ore in the -75 to +16mm<br />

fraction will feed a secondary cone type crusher. The product from the crusher, with p 80 less<br />

than 20mm, is conveyed to a storage hall to be chevron stacked, in order to improve stockpile<br />

homogeneity.<br />

Finely crushed <strong>Verde</strong>te from the storage hall is reclaimed and fed to a dosing bin in the raw meal<br />

grinding department.<br />

Limestone, max 5% passing 1 inch, is received from an external quarry, and stacked in a conical<br />

pile with a volume of 1300m 2 . The material is transferred via truck loader to a hopper to a<br />

dosing bin in the raw meal grinding department.<br />

Both crushed <strong>Verde</strong>te and limestone are proportioned and fed to a vertical roller mill grinding<br />

circuit, nominal rate of 169t/h dry basis, comprising of a belt feeder, integrated dynamic<br />

separator, bag filter, bucket elevators for both internal circulation and final product transport.<br />

The installed power will be 1360kW.The raw meal produced in the grinding circuit is stocked in<br />

a storage silo, where the material will be homogenized pneumatically.<br />

Raw meal finely ground at 10%+170 mesh, along with recirculating off-spec fines generated in<br />

different steps of the process and agglomerator (necessary for the pelletizing step) will be fed to<br />

an 215 t/h continuous intensive vertical mixer (commercial reference adopted is RV24K Eirich).<br />

The blend will be fed via belt conveyors to pelletizing gate feeders to the pelletizing area,<br />

comprising of three 5.5m diameter disk pelletizer lines at a nominal dry basis rate of 72t/h each,<br />

where water is continuously injected (up to 18% humidity). After pelletizing, the green pellets<br />

are classified and off-spec pellets will be returned to the mixer.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 11-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Green pellets will feed a grizzly car at a rate of 210t/h wet basis. There will be approximately 7<br />

min residence time and at this time the pellets are dried in ascending and descending areas with<br />

hot air from the preheating zone. The total effective length of the grizzly car will be<br />

approximately 40m with a width of 3m.<br />

The dust generated at the grizzly car will be collected by a dust collector and will return the<br />

heated and clean air to the pellets drying areas. Fines collected return through pneumatic<br />

conveying to the fines dosing system, making part of the load that feeds the mixer. The fines<br />

generated along the bed of the grizzly car will be transported back to the bins in the mixing area.<br />

After drying the pellets feed the rotary kiln at a rate of 172t/h dry basis, 12% filling degree, 60<br />

minutes residence time, max temperature 1300C. Power supply demand for the kiln and all its<br />

auxiliary equipment will be about 3700KW. Reaction temperature will be approximately<br />

1300ºC.<br />

After roasting, thermopotash is formed and must be quickly quenched. Quenching is performed<br />

in a water reservoir. After this treatment the pellets will be extracted from the bottom of the<br />

reservoir and dried in a rotary dryer. Evaporated steam will be collected and condensed and<br />

returned to the quench circuit. Evaporation losses in the pellets drying condenser and cooling<br />

tower will be compensated with makeup water added at the cooling tower basin.<br />

From the rotary dryer thermopotash is sent to a final grinding area, where its size is reduced to<br />

100% passing 100 mesh. After classification, the product is repelletized and conveyed to a final<br />

classification step using a vibrating screen. The pellets within the specification range, -4 + 2mm,<br />

will be dried and conveyed by belt to the storage warehouse where the final product will be<br />

stored and further dispatched by trucks.<br />

The product is a potassium source only sparingly water soluble, and recovery is anticipated to be<br />

better than 90% of the 8% potassium as K 2 O.<br />

In the proposed process the purpose of calcining is to thermally release potassium from <strong>Verde</strong>te,<br />

so that potassium becomes readily exchangeable for agriculture.<br />

11.1.2 Project Scenarios and Capital Costs<br />

For this project, three potential scenarios for heating the kiln have been identified:<br />

1. Petroleum Coke heating directly in the kiln with the <strong>Verde</strong>te;<br />

2. A dead roaster for utilizing any fuel with heat exchange to the kiln (i.e., no transfer of<br />

residue); and<br />

3. Natural Gas heating.<br />

The scenarios are summarized in Table 11.1.2.1. As can be observed although capital cost is<br />

lowest for option 3 the operating cost is double options 1 and 2.<br />

Option 1 presents the middle capital cost and lowest operating cost but <strong>Verde</strong> cannot yet confirm<br />

that petroleum products do not contaminate the product during the kiln roasting and as such<br />

cautious has to be applied in advocating this process option. However, it has been stated by Dr.<br />

Gaspar Korndorfer, University of Uberlandia that even if residual organics from combustion<br />

were absorbed by the pellets, there will be a positive effect regarding agronomic efficiency.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 11-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Dead burnt carbon has beneficial properties, increasing water retention in the soil, ensuring<br />

better fertilizer retention (negative surface charge), therefore reducing deleterious elements<br />

leaching. In the case of residual hydrocarbons adsorbed by the pellets, in minor quantities, it will<br />

be hard to determine any negative effect. Indeed, in some applications of the fertilizer industries<br />

waste oil was applied to fertilizer to provide mechanical particle stability. This supports the<br />

application of option 1 or 2 for heating but requires confirmation.<br />

Option 2 would have the benefit that any fuel source could be utilized in a dead roaster up front<br />

of the kiln and transfer heat to the kiln ensuring there would be no mix of fuel and product in the<br />

kiln keeping the product pure. Although this option has the highest capital cost, the operational<br />

cost is similar to the direct petroleum coke application in the calcine and a small incremental<br />

increase in operating costs (


<strong>Verde</strong> <strong>Potash</strong> Plc 11-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

11.1.4 Results of Agronomic Testwork<br />

The available K in the soil shown in Table 11.1.4.1 and 11.1.4.2 indicated that there is no<br />

difference between the water soluble K source (KCl) and Thermo-K, 60 days after application in<br />

sandy and clay soil, using dosage applications of 200 and 400kg/ha K 2 O.<br />

This result shows that the thermal treatment applied to the <strong>Verde</strong>te (raw material used in the<br />

manufacture of Thermo-K) was very efficient from an agronomic point of view. This can be<br />

seen when comparing the results against those of the pure <strong>Verde</strong>te, without heat treatment. In<br />

this case, the K in the soil did not differ from the control standard which means that virtually no<br />

potassium from the <strong>Verde</strong>te was released to the soil, indicating a low efficiency of this material<br />

as a source of potassium for plants.<br />

Table 11.1.4.1: K content in soil (Mehlich 1) After 60 Days of Incubation with Different<br />

Sources of Potassium in a Clay Soil.<br />

Dose K 2 O<br />

K – Source<br />

kg ha -1 KCl Thermo-K <strong>Verde</strong>te<br />

Average<br />

0 -- -- -- 0,07<br />

200 0,24 * a B 0,23 * a B 0,07 ns b A 0,18<br />

400 0,36 * a A 0,32 * b A 0,07 ns c A 0,25<br />

Average 0,30 0,27 0,07<br />

CV% = 9,40<br />

DMS dose = 0,03; DMS source = 0,03; DMS Dunnet = 0,04<br />

Averages followed by distinct letters, lowercase on the line and uppercase in the column, differ by Tukey test at 0.05 significance; ns not<br />

significant by the Dunnett test at 0.05 significance, * significant by the Dunnett test at 0 05 significance;<br />

Table 11.1.4.2: K Content in Soil (Mehlich 1) After 60 Days of Incubation with Different<br />

Sources of Potassium in a Sandy Soil.<br />

Dose K 2 O<br />

Source<br />

kg ha -1 KCl Thermo-K <strong>Verde</strong>te<br />

Average<br />

0 0,04<br />

200 0,25 * a B 0,24 * a B 0,04 ns b A 0,18<br />

400 0,41 * a A 0,38 * a A 0,04 ns b A 0,28<br />

Average 0,33 0,31 0,<strong>43</strong><br />

CV% = 12,89<br />

DMS dose = 0,04; DMS source = 0,05; DMS Dunnet = 0,05<br />

Averages followed by distinct letters, lowercase on the line and uppercase in the column, differ by Tukey test at 0.05 significance; ns not<br />

significant by the Dunnett test at 0.05 significance, * significant by the Dunnett test at 0 05 significance;<br />

In addition to potassium addition the application of Thermo-K also appears to increase available<br />

Ca and Mg in the soil after 60 days of incubation. Presumably, magnesium is also released from<br />

clays in the <strong>Verde</strong>te and Ca is present as lime from calcining of limestone in the kiln (Tables<br />

11.1.4.3 through 11.1.4.6). Further with a higher application mass of Thermo-K (400kg/ha)<br />

greater availability of Ca and Mg was also observed. Potassium chloride did not affect the Ca<br />

and Mg in the soil because it simply does not have these elements in their composition.<br />

The <strong>Verde</strong>te, however, despite containing Ca and Mg in its composition, did not increase the<br />

levels of these elements in the soil, strengthening the conclusion that the <strong>Verde</strong>te has low<br />

reactivity and is not able to release nutrients to the soil in the short term.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 11-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

When comparing the doses of 200 and 400kg/ha K 2 O, only Thermo-K showed an increase in the<br />

nutrient content in the soil, which further demonstrates the high reactivity of the product even<br />

when analyzed in the short term.<br />

Table 11.1.4.3: Exchangeable Ca in the Soil After 60 Days of Incubation with Different<br />

Sources of Potassium in A Clay Soil<br />

Dose K 2 O<br />

K-Source<br />

kg ha -1 KCl Thermo-K <strong>Verde</strong>te<br />

Average<br />

0 --- --- --- 0,09<br />

200 0,08 ns b A 1,40 * a B 0,10 ns b A 0,52<br />

400 0,09 ns b A 2,20 * a A 0,10 ns b A 0,80<br />

Average 0,08 1,79 0,10<br />

CV% = 6,70<br />

DMS dose = 0,07 ; DMS source = 0,06 ; DMS Dunnet = 0,08<br />

Averages followed by distinct letters, lowercase on the line and uppercase in the column, differ by Tukey test at 0.05 significance; ns not<br />

significant by the Dunnett test at 0.05 significance, * significant by the Dunnett test at 0 05 significance<br />

Table 11.1.4.4: Exchangeable Ca in the Soil After 60 Days of Incubation with Different<br />

Sources of Potassium in a Sandy Soil<br />

Dose K 2 O<br />

K-Source<br />

kg ha -1 KCl Thermo-K <strong>Verde</strong>te<br />

Average<br />

0 --- --- --- 0,09<br />

200 0,08 ns b A 1,54 * a B 0,14 ns b A 0,58<br />

400 0,12 ns b A 2,26 * a A 0,11 ns b A 0,83<br />

Average 0,10 1,90 0,12<br />

CV% = 8,84<br />

DMS dose = 0,08 ; DMS source = 0,1 ; DMS Dunnet =0,11<br />

Averages followed by distinct letters, lowercase on the line and uppercase in the column, differ by Tukey test at 0.05 significance; ns not<br />

significant by the Dunnett test at 0.05 significance, * significant by the Dunnett test at 0 05 significance;<br />

Table 11.1.4.5: Exchangeable Mg in the Soil After 60 Days of Incubation with Different<br />

Sources of Potassium in a Clay Soil<br />

Dose K 2 O<br />

K-Source<br />

kg ha -1 KCl Thermo-K <strong>Verde</strong>te<br />

Average<br />

0 --- --- --- 0,04<br />

200 0,04 ns b A 0,<strong>43</strong> * a B 0,05 ns b A 0,17<br />

400 0,05 ns b A 0,69 * a A 0,04 ns b A 0,26<br />

Average 0,04 0,56 0,04<br />

CV% = 5,54<br />

DMS dose = 0,016 ; DMS source = 0,019 ; DMS Dunnet = 0,02<br />

Averages followed by distinct letters, lowercase on the line and uppercase in the column, differ by Tukey test at 0.05 significance; ns not<br />

significant by the Dunnett test at 0.05 significance, * significant by the Dunnett test at 0 05 significance;<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 11-6<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 11.1.4.6: Exchangeable Mg in the Soil After 60 Days of Incubation with Different<br />

Sources of Potassium in a Sandy Soil<br />

Dose K 2 O<br />

K-Source<br />

kg ha -1 KCl Thermo-K <strong>Verde</strong>te<br />

Average<br />

0 --- --- --- 0,05<br />

200 0,05 ns b A 0,48 * a B 0,05 ns b A 0,19<br />

400 0,05 ns b A 0,64 * a A 0,04 ns b A 0,24<br />

Average 0,04 0,60 0,05<br />

CV% = 12,75<br />

DMS dose = 0,04 ; DMS source = 0,04 ; DMS Dunnet = 0,05<br />

Averages followed by distinct letters, lowercase on the line and uppercase in the column, differ by Tukey test at 0.05 significance; ns not<br />

significant by the Dunnett test at 0.05 significance, * significant by the Dunnett test at 0 05 significance;<br />

This initial testwork indicates that Thermo-K provides a potentially superior source of nutrient<br />

enrichment in soils not only for potassium but also for calcium and magnesium. In addition,<br />

the source of potash is a non-chloride, non-sulfate source of potash and thus will not adversely<br />

impact soil pH or salinity. In addition, <strong>Verde</strong> conducted mass balance testwork, which<br />

demonstrated that Thermo-K is practically insoluble in water. Ergo, Thermo-K also provides a<br />

superior source of fertilizer as it would be a slow release source of nutrients which is important<br />

in climates with notably wet and dry seasons where traditional fertilizers have been weathered<br />

from soils during seasonally heavy meteoric events and unavailable during the dry season<br />

reducing the quality of agricultural soils.<br />

11.1.5 Summary, Residual Issues and Recommendations<br />

The testwork undertaken to date demonstrates that this unique process and product are<br />

potentially a valuable contribution to agriculture, particularly in regions where soils have a low<br />

natural exchangeable nutrient component. In addition although Thermo-K is relatively<br />

expensive when compared to similar potassium concentrations from salar salts it has the distinct<br />

advantages that:<br />

<br />

<br />

<br />

The source of salts is a non-chloride, non-sulfate source of salt and thus will not<br />

adversely impact soil pH or salinity components;<br />

Additional nutrients such as calcium, magnesium and silicon are present; and<br />

The nutrient source is slow release and as such more sustainable than traditional sources<br />

of fertilizer and thus will have lower usage costs for farmers as less frequent applications<br />

will be required.<br />

However residual issues remain with the product that need to be addressed in further studies.<br />

The rate of water solubilization of nutrients from the calcined product needs to be established<br />

through rinse tests simulating the quench step post calcining and long term exposure to meteoric<br />

rinsing. In addition, this testwork needs to also address potential mobilization of aluminum,<br />

manganese and iron as well as trace metals from the Thermo-K product that would adversely<br />

impact crop quality or yield. From preliminary studies <strong>Verde</strong> does not consider this to be a<br />

problem but more testwork needs to be undertaken before definitive conclusions can be made.<br />

In addition during prefeasibility assessment frequent samples to demonstrate consistency in<br />

product production and to demonstrate lack of impurities need to be undertaken.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Conceptual Flowsheet for<br />

Cerrado <strong>Verde</strong> ThermoFertlizer<br />

Project<br />

File Name: Figure_11-1 Date: 09/15/2011 Approved: RB Figure: 11-1


<strong>Verde</strong> <strong>Potash</strong> Plc 12-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

12<br />

Mineral Resource Estimate (Item 14)<br />

Volodymyr Myadzel, of BNA verified the Funchal Norte resource estimate provided by Coffey<br />

Mining as described in Section 12.1. SRK also verified this resource estimate on March 1, 2010.<br />

In addition, Dr. Myadzel constructed the geologic and resource model for Targets 4, 6, 7, 10 and<br />

11 as discussed in Section 12.2. Dr. Myadzel is responsible for the resource estimation<br />

methodology and the resource statement. Dr. Myadzel is independent of the issuer applying all<br />

of the tests in Section 1.5 of the <strong>NI</strong> <strong>43</strong>-<strong>101</strong>.<br />

The resource estimate has been undertaken in compliance with accepted Canadian Institute of<br />

Mining, Metallurgy and Petroleum (CIM) definitions for indicated and inferred resources in<br />

accordance with <strong>NI</strong> <strong>43</strong>-<strong>101</strong> Standards of Disclosure for Mineral Projects.<br />

12.1 Funchal Norte Target<br />

Coffey Mining was commissioned by <strong>Verde</strong> <strong>Potash</strong> plc to complete a resource estimate for the<br />

Project. Coffey Mining has estimated the Mineral Resource for the Project as at February 27,<br />

2010. All grade estimation was completed using Ordinary Kriging (“OK”) for <strong>Potash</strong>.<br />

This estimation approach was considered appropriate based on review of a number of factors,<br />

including the quantity and spacing of available data, the interpreted controls on mineralization,<br />

and the style of mineralization. The estimation was constrained with mineralization<br />

interpretations.<br />

12.1.1 Geological Modeling<br />

Based on grade information and geological observations from Coffey Mining and site based<br />

<strong>Verde</strong> geologists, one Unweathered domain and one Weathered domain (transition zone) have<br />

been interpreted using E-W oriented vertical sections.<br />

Interpretation and digitizing of all constraining boundaries has been undertaken on cross sections<br />

orientated at 90° (drill line orientation). The interpretation was completed using 8 vertical<br />

sections. Figure 12-1 shows the vertical sections location. The resultant digitized boundaries<br />

have been used to construct wireframe defining the three-dimensional geometry of each<br />

interpreted feature. The interpretation and wireframe models have been developed using the<br />

Gemcom Surpac mine planning software package.<br />

As the drill holes collars were surveyed using a portable GPS the RL values of each one were<br />

defined by Coffey draping those collars to the 3D topography surface.<br />

For the purpose of the resource estimation, 2 mineralized domains were interpreted and modeled<br />

to the <strong>Verde</strong>te which is characterized by the green glauconitic mineralization. Cross section<br />

examples are shown in Figures 12-2 through 12-3.<br />

Figures 12-4 and 12-5 show the two domain wireframes interpreted in 3 dimensions.<br />

12.1.2 Block Model Development<br />

A three-dimensional block model was constructed for the Cerrado <strong>Verde</strong> deposit, covering all the<br />

interpreted mineralization zones and including suitable additional waste material to allow later<br />

pit optimization studies. The block model has been developed using Gemcom Surpac Mine<br />

planning software.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 12-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

A parent block size of 100mE x 100mN x 10mRL has been used for all materials with subblocking<br />

to 50mE x 50mN x 5mRL to allow adequate volume resolution. To obtain a robust<br />

flagging of the wireframe in the block model, a percent model technique was used which<br />

calculates the percentage of the block inside the Unweathered wireframe. This provides a more<br />

accurate volume estimate. Bulk density has been coded to the block model based on the defined<br />

density values provided by <strong>Verde</strong>.<br />

The Table 12.1.2.1 shows the summary of the block model created.<br />

Table 12.1.2.1: Block Model Summary<br />

Item Y X Z<br />

Minimum Coordinates 7,868,000 407,500 600<br />

Maximum Coordinates 7,871,500 409,500 1,050<br />

User Block Size 100 100 10<br />

Min Block Size 50 50 5<br />

Rotation 0 0 0<br />

12.1.3 Statistical Analysis<br />

The drillhole database was composited to a 2m downhole composite interval, recording. The 2m<br />

composites were used for all statistical, geostatistical and grade estimation studies. The decision<br />

to use 2m composites was based the raw sample lengths of sampled intervals (Figure 12-6).<br />

Statistical analysis of the composite datasets was completed within the Weathered and<br />

Unweathered domains. Descriptive statistics are presented in Table 12.1.3.1.<br />

Table 12.1.3.1: Summary Statistic – 2m Composites<br />

Domain Item K 2 0(%)<br />

Count 244<br />

Minimum 7.09<br />

High Grade Domain Maximum Mean 13.02<br />

Std. Dev. 10.95<br />

CV 1.09<br />

Count 174<br />

Minimum 3.31<br />

Low Grade Domain Maximum 10.74<br />

Mean 6.62<br />

Std. Dev. 1.69<br />

CV 0.26<br />

"Box and whisker" plots for the mineralized intervals were compiled for Unweathered and<br />

Weathered K 2 O in Figures 12-7 and 12-8, respectively.<br />

Based on the statistical review a top cut was applied to Weathered mineralization based on the<br />

97.5 percentile which included only one Unweathered assay being reduced to 10.73% K 2 O.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

12.1.4 Variography<br />

Introduction<br />

Variography is used to describe the spatial variability or correlation of an attribute. The spatial<br />

variability is traditionally measured by means of a variogram, which is generated by determining<br />

the averaged squared difference of data points at a nominated distance (h), or lag (Srivastava and<br />

Isaacs, 1989). The averaged squared difference (variogram or v(h)) for each lag distance is<br />

plotted on a bivariate plot, where the X-axis is the lag distance and the Y-axis represents the<br />

average squared differences (v(h)) for the nominated lag distance.<br />

Several types of variogram calculations are employed to determine the directions of the<br />

continuity of the mineralization:<br />

Traditional variograms are calculated from the raw assay values;<br />

Log-transformed variography involves a logarithmic transformation of the assay data;<br />

Gausssian variograms are based on the results after declustering and a transformation to a<br />

Normal distribution;<br />

Pairwise-relative variograms attempt to 'normalize' the variogram by dividing the<br />

analyses; and<br />

Correlograms are 'standardized' by the variance calculated from the sample values that<br />

contribute to each lag.<br />

Fan variography involves the graphical representation of spatial trends by calculating a range of<br />

variograms in a selected plane and contouring the variogram values. The result is a contour map<br />

of the grade continuity within the domain.<br />

The variography was calculated and modeled in the mining planning software, Gemcom Surpac<br />

Software. The rotations are tabulated as input into Gemcom Surpac Software (geological<br />

convention), with X representing the bearing, Y representing dip and Z representing plunge. Dip<br />

and dip direction of major, semi-major and minor axes of continuity are also referred to in the<br />

text.<br />

Grade variography was generated to enable grade estimation via OK. Interpreted anisotropy<br />

directions correspond well with the modeled geology and overall geometry of the interpreted<br />

domain. The results are show in Table 12.1.4.1.<br />

Table 12.1.4.1: Cerrado <strong>Verde</strong> Deposit Unweathered and Weathered Mineralized Domain<br />

Variogram Models<br />

K2O<br />

Nugget<br />

(CO)<br />

Bearing<br />

Rotation Structure 1 Structure 2<br />

Dip Plunge<br />

Sill 1<br />

(C1)<br />

Major<br />

Range (m)<br />

Semi-<br />

Major Minor<br />

Sill 2<br />

(C2)<br />

Major<br />

Range (m)<br />

Semi<br />

Major Minor<br />

Low Grade 0.21 180 -10 0 0.34 200 100 16.53 1.20 400 200 33.06<br />

High Grade 0 21 180 -10 0 0.34 200 100 16.53 1.20 400 200 33.06<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

12.1.5 Grade Estimation<br />

Resource estimation for the Cerrado <strong>Verde</strong> mineralization was completed using Ordinary<br />

Kriging (OK) within the Weathered and Unweathered mineralized domain.<br />

OK is the most commonly used type of kriging. It assumes a constant but unknown mean.<br />

Typical ordinary kriging assumptions.<br />

The typical assumptions for the practical application of ordinary kriging are:<br />

Intrinsic stationarity or wide sense stationarity of the field; and<br />

Enough observations to estimate the variogram.<br />

The mathematical condition for applicability of ordinary kriging is:<br />

The mean E[Z(x)] = u is unknown but constant<br />

The variogram v(x,y) = E[(Z(x) - Z(y))2] of Z(x) is known. Ordinary Kriging equation<br />

Ordinary Kriging equation<br />

The kriging weights of ordinary kriging fulfill the unbiasedness condition<br />

and are given by the ordinary kriging equation system:<br />

the additional parameter µ is a Lagrange multiplier used in the minimization of the kriging error<br />

to honor the unbiasedness condition.<br />

Ordinary kriging interpolation<br />

The interpolation by ordinary kriging is given by:<br />

Ordinary kriging error<br />

The kriging error is given by:<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Properties of kriging (Cressie 1993, Chiles & Delfiner 1999, Wackernagel 1995)<br />

<br />

<br />

The kriging estimation is unbiased:<br />

The kriging estimation honors the actually observed value:<br />

The kriging estimation assumptions hold. However (e.g. Cressie 1993):<br />

As with any method: If the assumptions do not hold, kriging might be bad.<br />

There might be better nonlinear and/or biased methods.<br />

No properties are guaranteed, when the wrong variogram is used. However typically still<br />

a 'good' interpolation is achieved.<br />

Best is not necessarily good: e.g. In case of no spatial dependence the kriging<br />

interpolation is only as good as the arithmetic mean.<br />

Kriging provides correctness of the variogram.<br />

Additional to the drilling samples, channel composites samples, from complementary sampling<br />

campaign were used, after a test of adequacy of support. Figure 12-9 shows the estimation steps<br />

undertaken in the Cerrado <strong>Verde</strong> estimation.<br />

12.1.6 Resource Reporting<br />

The grade estimates for all domains have been classified as Inferred based on the confidence<br />

levels of the key criteria that were considered during the resource estimation. Key criteria are<br />

tabulated below. A summary of confidence levels of the several items involved for the resources<br />

estimation for the Cerrado <strong>Verde</strong> deposit is provided in Table 12.1.6.1 below, reflecting the<br />

updated resources for Targets 4, 6, 7, 10 and 11.<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-6<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 12.1.6.1: Cerrado <strong>Verde</strong> Project Confidence Levels of Key Categorization Criteria<br />

Items Discussion Confidence<br />

Drilling Techniques Reverse Circulation drilling is Industry standard approach. High<br />

Logging Standard nomenclature and apparent good quality. High<br />

Drill Sample Recovery Good recovery recorded. High<br />

Sub-sampling Techniques<br />

Industry standards of sampling technique and preparation Moderate<br />

and Sample Preparation<br />

Quality of Assay Data<br />

have been used for the new targets.<br />

Has filed duplicates for pulp, adequate number of samples<br />

and good results, however, methodology for the use of<br />

blank and standard samples was not satisfactory.<br />

Moderate<br />

Verification of Sampling and Assaying 119 samples were analyzed at the ALS lab and the High<br />

comparative results were very good.<br />

Location of Sampling Points Differential GPS was used for the new sample locations. High<br />

Data Density and Distribution Approximately 200m x 400m spaced drilling Moderate<br />

Audits or Reviews None N/A<br />

Database Integrity<br />

Assay hard copy sheets were randomly checked against High<br />

the digital database with no errors identified<br />

Geological Interpretation Simple geology, two domains defined. High<br />

Estimation and Modeling Techniques Ordinary Kriging has been used to obtain estimates of<br />

K2O % grade.<br />

High<br />

The Inferred resource has been classified based on blocks estimated until step 5 with a maximum<br />

range of 1,000m.<br />

The total Inferred resource estimate is shown in Table 12.1.6.2 utilizing different cut off grades.<br />

The additional figures are different views of the model as used in the validation process. Mineral<br />

resources that are not mineral reserves do not have demonstrated economic viability. Quantity<br />

and grade or quality is an estimate and should be rounded to reflect approximation.<br />

Table 12.1.6.2: Cerrado <strong>Verde</strong> Deposit –February 27, 2010 Inferred Resource Grade<br />

Tonnage Report Ordinary Kriging Estimate 100mE x 100mN x 5mRL Selective Mining<br />

Unit<br />

Domain Cutoff Grade (% K 2 0) Million Tonnes Average Grade (% K 2 0)<br />

0 67.82 6.22<br />

3 G7.82 6.22<br />

4 67.45 6.23<br />

Low Grade 5 55.85 6.41<br />

6 33.19 7 T<br />

7 14 7.78<br />

8 6.49 8.52<br />

9 1.01 9.<strong>43</strong><br />

0 92.74 10.61<br />

7 92.74 10.61<br />

8 92.20 10.63<br />

High Grade 9 86.55 10.76<br />

10 64.39 11.17<br />

11 35.71 11.61<br />

12 8.24 12.33<br />

Total Low Grade + High Grade 0 160.56 0.75<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-7<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

There are no mineral reserves at the Cerrado <strong>Verde</strong> property at this time. All mineral resources<br />

are classified as inferred. The mineral resource estimates may be influenced by a range of<br />

factors including environmental, permitting, legal, title, taxation, socio-economic, marketing,<br />

political and other issues. However, such influences cannot be determined at this time.<br />

The resource estimate has been classified as inferred mainly due to the low confidence in the<br />

Bulk Density determinations, data density of distribution and the limited QA/QC program<br />

provided by <strong>Verde</strong>. The actual model shows relative homogeneity and is a simple geological<br />

model.<br />

Figures 12-11 and 12-12 show the grade and tonnage curve for the high and low domains.<br />

Validation<br />

Validation of the grade estimate was completed with a comparative Nearest Neighbor estimation.<br />

Validation consists of a comparative statistical analysis over inferred results for Weathered and<br />

Unweathered mineralized intervals. In addition, an interactive visual validation utilizing the drill<br />

holes and the block model was completed in plan and cross section (Figures 12-13 and 12-14).<br />

The visual validation of the OK model shows a good correlation, considering the inferred level<br />

of resource classification, between the blocks estimated and the original samples.<br />

The use of OK and the simple block model method for determining resource is the accepted<br />

practice and appears to have been applied correctly in the Coffey resource estimation. The<br />

caveat is that the underlying database is weak in that the influence of the individual drill holes<br />

varies across the deposit and in the northern section do not have any east-west component to use<br />

in the model. This has the result that there is insufficient data, other than geologic inference, to<br />

construct the blocks in those areas. Given that the deposit appears to be geologically highly<br />

predictable gives the results some credence, but more drilling should be done and the assay<br />

values should be inserted into the model before assigning more than low credibility to the<br />

tonnage and grade inferred by this exercise.<br />

12.2 Targets 4, 6, 7, 10 and 11<br />

The resource estimation of the <strong>Verde</strong>te mineralization from the areas Target-4, Target-6, Target-<br />

7, Target-10 and Target-11 were performed using the K 2 O values obtained from samples<br />

collected in drill holes. Information about the initial data is presented in the Table 12.2.1.<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-8<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 12.2.1: Data Presentation<br />

Description<br />

Areas<br />

Target 4 Target 6 Target 7 Target 10 Target 11<br />

Diamond drill holes 0 2 3 0 0<br />

Reverse circulation drillholes 7 22 77 5 9<br />

Notes of drillholes sampling 197 10<strong>43</strong> 1894 98 185<br />

Notes on the drillhole geological database 509 1274 5177 250 447<br />

K 2 O chemical analyses 187 1023 1765 95 174<br />

P 2 O 5 chemical analyses 187 1023 1764 95 174<br />

CaO chemical analyses 185 <strong>101</strong>6 1737 95 163<br />

Al 2 O 3 chemical analyses 187 1023 1765 95 174<br />

Fe 2 O 3 chemical analyses 187 1023 1765 95 174<br />

SiO 2 chemical analyses 187 1023 1765 95 174<br />

MgO chemical analyses 186 1023 1765 95 174<br />

TiO 2 chemical analyses 187 1023 1765 95 174<br />

MnO chemical analyses 187 1023 1765 95 174<br />

Na 2 O chemical analyses 1<strong>43</strong> 767 1765 88 129<br />

LOI chemical analyses 187 1023 1765 95 174<br />

Density analyses SGS GEOSOL 0 10 15 0 0<br />

Density analyses VERDE 0 14 56 0 0<br />

The methodology used to evaluate the resources included several routine phases of computer<br />

manuals works. It was necessary to refine the geological interpretation of the mineralized bodies<br />

and create three-dimensional wireframe models. Then the topographic digital terrain model<br />

(DTM) was imported. After this stage, was built a block model for the interpreted mineralized<br />

body, creating blocks with size of 50 m (X) by 50 m (Y) by 10 m (Z), and refines them into subblocks<br />

with smaller size, 5 m (X) by 5 m (Y) by 1 m (Z).<br />

As the main interpolation method for the mineralized body block model of the area Target 6, was<br />

adopted the Kriging method. For the other targets was used the method Inverse Distance<br />

Weighting (IDW) with power 2. The block model with the interpolated grades was used to<br />

evaluate the resources of the <strong>Verde</strong>te deposit.<br />

Software used: MICROMINE (12.0.4).<br />

Using this software was performed the formatting and verification of all data, the construction of<br />

wireframe and block models, and the data preparation for the final report.<br />

12.2.1 Statistical Analyses of Geological Exploration<br />

This report used a classical statistical analysis to perform the following tasks:<br />

<br />

<br />

<br />

Evaluate the need of separate populations to K 2 O grades, if exist more than one<br />

population;<br />

Evaluate the effect of populations mixing;<br />

Determine the grade distribution.<br />

Initially, the statistical analysis was performed for all drilling samples, not grouped, for the K 2 O<br />

element for the entire data. Then, was performed a statistical analysis for the samples that are<br />

part of the selected mineralization area. A statistical analysis of the samples length determined<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-9<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

that the optimal composed sample size was 1m. After that a statistical analysis was performed<br />

again for the samples grouped into 1m (composite). The results of the statistical analysis are<br />

shown in Table 12.2.1.1 to 12.2.1.5.<br />

Determine a cutoff grade for interpretation was not the purpose of this statistical analysis.<br />

Table 12.2.1.1: Descriptive Statistics Data for K 2 O of Target 4<br />

Samples<br />

Quantity Minimum Maximum Mean Median Variance<br />

Standard<br />

Deviation<br />

Element<br />

All samples<br />

K 2 O 187 0.94 11.2 8.44 9.10 3.82 1.95<br />

Samples inside the mineralized bodies<br />

K 2 O 153 5.27 11.20 9.13 9.47 1.33 1.15<br />

Samples composited inside the mineralized bodies<br />

K 2 O 153 5.27 11.20 9.13 9.47 1.33 1.15<br />

Table 12.2.1.2: Descriptive Statistics Data for K 2 O of the Target<br />

Samples<br />

Quantity Minimum Maximum Mean Median Variance<br />

Standard<br />

Deviation<br />

Element<br />

All samples<br />

K 2 O 1023 2.67 11.40 7.12 7.18 4.46 2.11<br />

Samples inside the mineralized bodies<br />

K 2 O 720 4.11 11.40 8.14 8.12 2.54 1.59<br />

Samples composited inside the mineralized bodies<br />

K 2 O 808 4.11 11.40 8.22 8.15 2.53 1.59<br />

Table 12.2.1.3: Descriptive Statistics Data for K 2 O of the Target 7<br />

Samples<br />

Quantity Minimum Maximum Mean Median Variance<br />

Standard<br />

Deviation<br />

Element<br />

All samples<br />

K 2 O 1765 1.03 11.80 8.72 9.05 4.35 2.08<br />

Samples inside the mineralized bodies<br />

K 2 O 1501 1.03 11.80 9.30 9.53 2.57 1.60<br />

Samples composited inside the mineralized bodies<br />

K 2 O 1547 1.03 11.80 9.29 9.52 2.56 1.60<br />

Table 12.2.1.4: Descriptive Statistics Data for K 2 O of the Target 10<br />

Samples<br />

Quantity Minimum Maximum Mean Median Variance<br />

Standard<br />

Deviation<br />

Element<br />

All samples<br />

K 2 O 95 4.30 11.60 9.58 10.60 3.99 2.00<br />

Samples inside the mineralized bodies<br />

K 2 O 93 4.30 11.60 9.65 10.60 3.86 1.97<br />

Samples composited inside the mineralized bodies<br />

K 2 O 107 4.30 11.60 9.76 10.76 3.57 1.89<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-10<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 12.2.1.5: Descriptive Statistics Data for K2O of the Target 11<br />

Samples<br />

Quantity Minimum Maximum Mean Median Variance<br />

Standard<br />

Deviation<br />

Element<br />

All samples<br />

K 2 O 174 3.77 11.40 7.68 7.59 3.27 1.81<br />

Samples inside the mineralized bodies<br />

K 2 O 124 5.35 11.40 8.46 8.21 1.96 1.40<br />

Samples composited inside the mineralized bodies<br />

K 2 O 124 5.35 11.40 8.46 8.21 1.96 1.40<br />

12.2.2 Interpretation<br />

In the mineralized domains interpretation were used the drillhole data and the geologic mapping<br />

data. The drillhole grid in the area is characterized by irregularities. In the deposit interpretation<br />

was used the Top and Base Grid method. The Kriging method was chosen for the Grid<br />

interpolation for the Target 6; and IDW with power 2 was chosen for the others areas. The<br />

modeled semi-variograms for the body top and base are represented in the Figures 12-15 and 12-<br />

16.<br />

Then the Grids were transformed in Digital Terrain Model (DTM). This method was chosen<br />

because the body is sub-horizontal, Figure 12-19.<br />

Interpreting the geologic limits of the mineralized bodies the interpretation was performed on the<br />

half of the distance of the exploration grid of each area keeping the mineralized body thickness.<br />

In the mineralized bodies interpretation the following conditions were used:<br />

The interpretation was performed to the K 2 O;<br />

Some low grades were selectively included in the mineralization, when the grade data<br />

logically were part of the mineralization body;<br />

The interpretation was performed up to the half of the distance of the exploration grid.<br />

For the Target 6 and Target 7 the mineralized body was divided in two areas: oxidized and fresh.<br />

In the data interpreting the geological description of the holes were used for the construction of<br />

the grid. Similar interpolation parameters to those used in the construction of top and bottom of<br />

the mineralization areas were used.<br />

12.2.3 Triangulation<br />

The *.shp data files (that represent the topographic surface SRTM of the deposit area with 5m<br />

contours) were used in the construction of the topographic digital terrain model (DTM). The file<br />

was imported to the Micromine system, interconnected and then, using the obtained contours, the<br />

topographic surface was constructed.<br />

To build the mineralization body solid were used Boolean operations. At the beginning was built<br />

a solid (“box”) inside the mapped geologic limits of the mineralization zone. Then, this box was<br />

cut by base and top surfaces and by the topographic surface. As result, we get the exact solid of<br />

the mineralization body.<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-11<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

12.2.4 Data Selection<br />

The drillhole data selection is a standard procedure of certification. It is essential that, in the<br />

classic statistical analysis, geostatistics and in the grades interpolation process, are used the<br />

correct samples. To the selection of the drillhole samples were used solids of the element to be<br />

analyzed.<br />

Analyzing the collected samples to each target is noted that for the Target 6 the majority samples<br />

have a length of 1 m, and to the other targets the majority has 2 m length. To use the same<br />

methodology to all the targets was assumed a 1 m length samples for the composites. The<br />

creation process of the composed intervals began on the drillhole collar continuing on the<br />

perforation way (down).<br />

The samples with high and low K 2 O grades were divided into composed samples of 1 m. Then,<br />

files of the composed samples were encoded by the mineralization body solid. To each<br />

composed interval was assigned a value in the field ORE, being ORE=1 if the composed interval<br />

is inside the mineralized body solid, and ORE=0 if not.<br />

12.2.5 Modeling<br />

The blocks models were created in order to intersect the tridimensional solids and represent then,<br />

in defined dimensioned blocks. The blocks parameters are listed below, Table 12.2.5.1.<br />

The block model process of the solid includes the sub-blocks process. Initially, the model was<br />

filled with blocks of 50(X), 50(Y) and 10(Z) meters, that were divided into smaller subunits,<br />

with a factor for the subdivision of 10, at the contact with the three-dimension solid that limit<br />

them.<br />

As result, at the limit with the solid, the size of the blocks became 5(X), 5(Y) and 1(Z) meters.<br />

The initial size of the blocks was chosen based on the morphology of the mineralized bodies and<br />

the dimension of the exploration grid (1/4 of the grid). The Model of the Target 4 has 16.786<br />

blocks, Target 6 has 28.037 blocks, Target 7 has 193.382 blocks, Target 10 has 10.114 blocks<br />

and Target 11 has 23.889 blocks.<br />

The solid was used to create a block model inside the geologic mineralized body. This solid was<br />

used to encode this blocks. The digital model of the topographic surface was used to limit the<br />

block models by the vertical axis.<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 12-12<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 12.2.5.1: Block Models Parameters<br />

Target<br />

Target 4<br />

Target 6<br />

Target 7<br />

Target 10<br />

Target 11<br />

Extension (m)<br />

Block Models<br />

Block size Sub-block minimum Number of<br />

Minimum Maximum<br />

Directions<br />

(m)<br />

size (m) primaries blocks<br />

East 387000 390000 50 5 61<br />

North 7855000 7859000 50 5 81<br />

RL 750 1100 10 1 36<br />

East 390000 392000 50 5 41<br />

North 7856000 7859000 50 5 61<br />

RL 800 1100 10 1 31<br />

East 403000 409000 50 5 121<br />

North 7865000 7874000 50 5 181<br />

RL 750 1000 10 1 25<br />

East 408500 410500 50 5 41<br />

North 7873500 7876500 50 5 61<br />

RL 800 1000 10 1 21<br />

East 409000 415000 50 5 121<br />

North 7874000 7879000 50 5 <strong>101</strong><br />

RL 750 1100 10 1 36<br />

12.2.6 Geostatistical Analysis<br />

The target chosen to geostatistic study is target 6, because it is relative regularity of the grid<br />

exploration, amount of data (802 samples), and isometric body shape. Semi Variograms were<br />

built for this target. For the construction of semi variogram were used the composite samples<br />

file.<br />

Cross-validation process was used to check the variogram, showing a low statistical error in data<br />

interpolation. The results of verification by Cross Validation are presented in Table 12.2.6.1. A<br />

diagram of linear dependency was also built between the samples file data and the interpolated<br />

K 2 O obtained by the cross-validation process. Results were satisfactory, presenting a correlation<br />

coefficient of 0.73 and accuracy of 13.5%.<br />

Table 12.2.6.1: Cross Validation Verification Results<br />

Analysis var K 2 0<br />

Transformation<br />

None<br />

Number of points 802<br />

Mean<br />

Std Dev<br />

Raw Data 8.1965 1.5967<br />

Estimate 8.2081 1.4248<br />

Standard error 0.82398 0.24225<br />

Error statistic -0.007620 1.2884<br />

12.2.7 Grade Estimation and Resources Classification<br />

To target 6 the element K 2 O was interpolated to the empty block model by the methods Kriging<br />

and IDW (Inverse Distance Weighted).<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 12-13<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

For the mineralization in question the IDW method was used with the search ellipse defined by<br />

the axis of the geostatistical analysis. Was used the ellipse divided into four sectors. The search<br />

radius were determined by semi variogram models. The parameters of the search ellipse radius<br />

are presented in Table 12.2.7.1.<br />

Table 12.2.7.1: Search Ellipse Parameters to Interpolate the Grades by the IDW And<br />

Kriging Methods of Target 6<br />

Radius Azimuth Factor Dip Factor Thickness Factor Min. Points by Sector Min. Count Fields<br />

0.6667 324 222 30 3 2<br />

1 324 222 30 2 2<br />

2 324 222 30 2 1<br />

3 324 222 30 1 1<br />

4 324 222 30 1 1<br />

100 324 222 30 1 1<br />

After comparing the results of Kriging interpolation and IDW2 methods for target Target 6<br />

(Table 12.2.9.1), it was decided to use IDW2 as the main interpolation method for the other<br />

bodies. Search ellipse parameters used to interpolate the grades for the other targets are shown<br />

in Table 12.2.7.2.<br />

Table 12.2.7.2: Ellipse Search Parameters Used to Interpolate the Grades by the IDW<br />

Method for Target 4, 7, 10 and 11<br />

Radius Azimuth Factor Dip Factor Thickness Factor Min. Points by Sector Min. Count Fields<br />

0.6667 150 100 15 3 2<br />

1 150 100 15 2 2<br />

2 150 100 15 2 2<br />

3 150 100 15 1 1<br />

4 150 100 15 1 1<br />

100 150 100 15 1 1<br />

The blocks for each zone of the mineralization were interpolated using only composite samples<br />

belonging to the corresponding part of the body. During the interpolation process was used the<br />

discretization process for each block, using a factor 4 for the X and Y axis, and a factor 2 for Z<br />

axis. This makes it possible to evaluate each block in four positions and assign to the center of<br />

the block the average of these values. This increases the accuracy of estimating the grade of<br />

each block.<br />

The constraints presented by each ellipse search sector were: the maximum number of points in<br />

the sector - 5 and the minimum point total for the interpolation, which varied depending on the<br />

size of the ellipse (from 3 to 1). Thus, the maximum total number of samples involved in the<br />

interpolation was 20.<br />

In the resources classification was used some parameters, as: the ellipse search radius (based on<br />

geostatistical studies), the kriging variance and the minimum drillhole number used in the block<br />

interpolation. In the resources classification of Target 6, inferred and indicated resources have<br />

been allocated. For the indicated resource was allocated blocks interpolated by the first and<br />

second search ellipses, with kriging variance less than 2, drillhole grid in the area about 200 by<br />

200 m, and used in the samples interpolation at least two different drillholes.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 12-14<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

For indicated resource in Target 7 was allocated blocks interpolated by the first three search<br />

ellipses, with a drillhole grid about 300 by 300 m and with outcrops sampling approximately 100<br />

by 100 m.<br />

12.2.8 Assignment of Density Values to the Block Model<br />

The density value was allocated directly for each block of the block model. The value of<br />

1.49t/m 3 was allocated to the oxidized <strong>Verde</strong>te blocks, and the value of 2.11t/m 3 was allocated to<br />

the fresh <strong>Verde</strong>te blocks.<br />

12.2.9 Block Model Validation<br />

The block model with grades interpolated was submitted to a visual and statistics check.<br />

Histograms and probability plots were constructed to the interpolated grades. Then, the<br />

interpolated grades were compared with the same histograms and probability plots of the<br />

composite samples. Histograms and graphics of the interpolated grades and composite samples<br />

were similar, which confirmed the validity and consistency of the block model built.<br />

In addition, the grades interpolated were displayed and compared with the grades of the drillhole<br />

samples. This comparison show an approximate relation, indicating the accuracy of the block<br />

model built. Thus, several sections were built showing the grades of the block model and<br />

drillholes of Target 6.<br />

The average grade of the model was compared with the average grade of the drillhole samples.<br />

Comparing the IDW with power 2 and the kriging methods to the Target 6, was verified a<br />

relative difference of 1.09% between them, as shown in Table 12.2.9.1.<br />

A data comparison was made between a polygonal provisional estimate by the weighting<br />

"intervals" method and the data obtained by the Kriging and IPD2 interpolation method. These<br />

comparisons are presented in Table 12.2.9.2. The difference between the average K 2 O grades<br />

and of metal tones in relative percentage is approximately 1.26%, which also confirms the good<br />

convergence and high reliability of the block model data. The 0.03% difference between the<br />

volumes of solids and the block model are due to the use of different methods of limitations,<br />

since the block model was constrained by the method of contour.<br />

Table 12.2.9.1: Comparison of metal tones and average K2O grade of the model, obtained<br />

by kriging and IDW2 methods to Target 6<br />

Relative difference Relative difference<br />

Tonnes KRIG Tonnes IDW2 KRIG IDW2<br />

KRIG – IDW2 KRIG – IDW2<br />

Cut Off<br />

Mt<br />

Mt K 2 O K 2 O<br />

K<br />

% %<br />

2 O<br />

Tonnes<br />

Relative % Relative %<br />

6 95.9 94.87 8.2796 8.3695 1.09 1.07<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 12-15<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 12.2.9.2: Comparison of metal tonnes and average K2O grades, obtained by the<br />

Kriging method, the target to target 6 and by IDW2 for other targets, and polygonal solids<br />

evaluate by the "weighting intervals" method<br />

Targets Type Volume Mm 3 K 2 O %<br />

Solid 36.16 9.14<br />

Target 4<br />

Block Model (IDW2) 36.17 9.15<br />

Relative difference in % 0.03769 0.13<br />

Solid 47.27 8.22<br />

Target 6<br />

Block Model (KRIG) 47.26 8.26<br />

Relative difference in % 0.01726 0.56<br />

Solid 484.83 9.30<br />

Target 7<br />

Block Model (IDW2) 484.84 9.22<br />

Relative difference in % 0.00303 0.83<br />

Solid 14.62 9.76<br />

Target 10<br />

Block Model (IDW2) 14.63 9.82<br />

Relative difference in % 0.05190 0.55<br />

Solid 27.56 8.44<br />

Target 11<br />

Block Model (IDW2) 27.57 8.08<br />

Relative difference in % 0.04510 4.27<br />

12.2.10 Resources Evaluation Results<br />

The resources evaluation results based on the <strong>Verde</strong>te block model, with Cut Off 7.5% of K 2 O,<br />

are presented in Table 12.2.10.1 through 12.2.10.3.<br />

Table 12.2.10.1: Grade Tonnage Report for Target 6. Inverse Distance Weighting with<br />

power two (IDW2) estimate (Block Model - 50mE X 50mN X 10mRL) 7.5% K 2 O cut off<br />

utilized<br />

Cut Off K 2 O% Class Type Density (t/m3) Tonnes (Mt) K 2 O (%)<br />

Fresh 2.11 20.37 8.83<br />

Indicated Weathered 1.49 2.88 8.85<br />

Total 2.01 23.25 8.83<br />

7.5<br />

Fresh 2.11 <strong>43</strong>.98 8.84<br />

Inferred<br />

Weathered 1.49 3.87 8.89<br />

Total 2.04 47.85 8.84<br />

Total 2.03 71.10 8.84<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 12-16<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 12.2.10.2: Grade Tonnage Report for Target 7. Inverse Distance Weighting with<br />

power two (IDW2) estimate (Block Model - 50mE X 50mN X 10mRL) 7.5% K2O cut off<br />

utilized<br />

Cut Off K2O% Class Type Density (t/m3) Tonnes (Mt) K 2 O (%)<br />

Fresh 2.11 50.64 9.39<br />

Indicated Weathered 1.40 0.14 8.80<br />

Total 2.11 50.79 9.39<br />

7.5<br />

Fresh 2.11 857.42 9.45<br />

Inferred Weathered 1.49 16.16 9.29<br />

Total 2.09 873.59 9.45<br />

Total 2.09 924.37 9.44<br />

Table 12.2.10.3: Grade Tonnage Report for Target 4, Target 10 and Target 11. Inverse<br />

Distance Weighting with power two (IDW2) estimate (Block Model - 50mE X 50mN X<br />

10mRL) 7.5% K2O cut off utilized<br />

Target Cut Off K 2 O% Class Density (t/m 3) Tonnes (Mt) K 2 O (%)<br />

Target 4 7.5<br />

Inferred 2.11 74.<strong>43</strong> 9.20<br />

Total 2.11 74.<strong>43</strong> 9.20<br />

Target 10 7.5<br />

Inferred 2.11 28.50 10.10<br />

Total 2.11 28.50 10.10<br />

Target 11 7.5<br />

Inferred 2.11 46.79 8.27<br />

Total 2.11 46.79 8.27<br />

12.3 Mineral Resource Estimate<br />

The Mineral Resource statement is presented in Table 12.3.1. The resource estimate has been<br />

undertaken in compliance with accepted CIM definitions for indicated and inferred resources in<br />

accordance with <strong>NI</strong> <strong>43</strong>-<strong>101</strong> Standards of Disclosure for Mineral Projects.<br />

Table 12.3.1: Grade Tonnage Report Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Target Cutoff grade (%K 2 O) Tonnage (Mt) Average Grade (% K 2 O)<br />

Indicated<br />

Target 6 7.5 23.25 8.83<br />

Target 7 7.5 50.79 9.39<br />

Total Indicated 7.5 74.04 9.22<br />

Inferred<br />

Target 4 7.5 74.<strong>43</strong> 9.20<br />

Target 6 7.5 47.85 8.84<br />

Target 7 7.5 873.59 9.45<br />

Target 10 7.5 28.50 10.10<br />

Target 11 7.5 46.79 8.27<br />

Funchal Norte 10 64.39 11.17<br />

Total Inferred 7.64 1,135.55 9.47<br />

Mineral Resources are not Mineral Reserves and do not have demonstrated economic viability.<br />

Inverse Distance Weighting with power two (IDW2) estimate (Block Model - 50mE X 50mN X 10mRL) 7.5% K2O cut off utilized.<br />

Effective date of Targets 4, 6, 7, 10 and 11 is August 3, 2011.<br />

Effective date of Funchal Norte is March 3, 2011.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Vertical Sections Location<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_12-1 Date: 09/15/2011 Approved: BS Figure: 12-1


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Cross Section (Section 4)<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_12-2 Date: 09/15/2011 Approved: BS Figure: 12-2


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Cross Section (Section 5)<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure 12-3 Date: 09/15/2011 Approved: BS Figure: 12-3


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Weathered (Transition Zone)<br />

Domain – 3 Dimensions<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_12-4 Date: 09/15/2011 Approved: BS Figure: 12-4


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Unweathered Domain – 3<br />

Dimensions<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_12-5 Date: 09/15/2011 Approved: BS Figure: 12-5


Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Sample Length Distribution<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_12-6 Date: 09/15/2011 Approved: BS Figure: 12-6


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Basic Statistics – 2m Composite<br />

Unweathered K 2 O<br />

File Name: Figure_12-7 Date: 09/15/2011 Approved: BS Figure: 12-7


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Basic Statistics – 2m Composite<br />

Weathered K 2 O<br />

File Name: Figure_12-8 Date: 09/15/2011 Approved: BS Figure: 12-8


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

K 2 O% Estimation Steps – Plan<br />

View<br />

File Name: Figure_12-9 Date: 09/15/2011 Approved: BS Figure: 12-9


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Block Model Domains High and<br />

Weathered<br />

File Name: Figure_12-10 Date: 09/15/2011 Approved: BS Figure: 12-10


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Grade Tonnage Curve – Domain<br />

Unweathered – Inferred Resource<br />

File Name: Figure_12-11 Date: 09/15/2011 Approved: BS Figure: 12-11


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Grade Tonnage Curve -<br />

Weathered – Inferred Resource<br />

File Name: Figure_12-12 Date: 09/15/2011 Approved: BS Figure: 12-12


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Comparative Statistics<br />

Unweathered % K 2 O<br />

File Name: Figure_12-13 Date: 09/15/2011 Approved: BS Figure: 12-13


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Comparative Statistics % K 2 O<br />

Weathered<br />

File Name: Figure_12-14 Date: 09/15/2011 Approved: BS Figure: 12-14


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Modeled semi-variogram of the<br />

top grid<br />

File Name: Figure_12-15 Date: 09/15/2011 Approved: NR Figure: 12-15


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Modeled Semi-variogram<br />

of the Base Grid<br />

File Name: Figure_12-16 Date: 09/15/2011 Approved: NR Figure: 12-16


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Geologic interpretation of the<br />

Top and Base surfaces (Kriging<br />

method)<br />

File Name: Figure_12-17 Date: 09/15/2011 Approved: NR Figure: 12-17


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Geologic interpretation of the Top<br />

and Base surfaces of the Target 7<br />

(IDW method with Power 2)<br />

File Name: Figure_12-18 Date: 09/15/2011 Approved: NR Figure: 12-18


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Target 6: Mineralized body<br />

divided in oxidized (red) and<br />

fresh (green) areas<br />

File Name: Figure_12-19 Date: 09/15/2011 Approved: NR Figure: 12-19


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Target 7: Mineralized body<br />

divided in oxidized (red) and<br />

fresh (green) areas<br />

File Name: Figure_12-20 Date: 09/15/2011 Approved: NR Figure: 12-20


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Search Ellipse (radius 1) to<br />

Interpolate the Grades by the IDW<br />

and Kriging Methods to Target 6<br />

File Name: Figure_12-22.docx Date: 09/15/2011 Approved: NR Figure: 12-22


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Search Ellipse (radius 2) to<br />

Interpolate the Grades by the IDW<br />

Method for Target 4, 7, 10 and 11,<br />

and the Ore Body of the Target 7<br />

File Name: Figure_12-23.docx Date: 09/15/2011 Approved: NR Figure: 12-23


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Histogram and Probability Plot of the K 2 O<br />

Distribution of the Composite Samples<br />

(left) and the Block Model Interpolated by<br />

the IDW2 Method (right) of the Target 6.<br />

File Name: Figure_12-24.docx Date: 09/15/2011 Approved: NR Figure: 12-24


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Histogram and Probability Plot of the K 2 O<br />

Distribution of the Composite Samples<br />

(left) and the Block Model Interpolated by<br />

the IDW2 Method (right) of the Target 7<br />

File Name: Figure_12-25.docx Date: 09/15/2011 Approved: NR Figure: 12-25


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Target 7: Mineralized body<br />

divided in oxidized (red) and<br />

fresh (green) areas<br />

File Name: Figure_12-26.docx Date: 09/15/2011 Approved: NR Figure: 12-26


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Comparison of K2O Grades in the<br />

Samples and Blocks, Interpolated by<br />

the Kriging Method, of the Target 6<br />

File Name: Figure_12-27.docx Date: 09/16/11 Approved: NR Figure: 12-27


<strong>Verde</strong> <strong>Potash</strong> Plc 13-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

13<br />

Mining Methods (Item 16)<br />

This report is preliminary in nature, it includes inferred mineral resources that are considered too<br />

speculative geologically to have the economic considerations applied to them that would enable<br />

them to be categorized as mineral reserves. Mineral resources that are not mineral reserves do<br />

not have demonstrated economic viability. There is no certainty that the preliminary assessment<br />

will be realized. Additional core drilling and assaying, with adequate QA/QC, is needed to bring<br />

this property to a level where a reliable resource can be used to do the next stage of <strong>Economic</strong><br />

<strong>Assessment</strong>.<br />

13.1 Mining Operations<br />

Mining operations at Cerrado <strong>Verde</strong> will consist of small mining equipment liberating potentially<br />

minable resources hosted in gently undulating topography over a wide surface extent.<br />

It is expected that mining will be conducted by a local 3rd party mining contractors with <strong>Verde</strong><br />

staff acting as mine owners. Initial static costing for mining operations is based on a<br />

combination of excavator’s, support equipment and 20t haul trucks.<br />

Resource grades vary physically from an Unweathered zone on the western extent to a lower<br />

grade zone in the east. The grade distribution suggests two pits and multiple working faces can<br />

be open at all times for blending purposes feeding the process plant at a consistent 8.5% K 2 O.<br />

Two production scenarios were considered by SRK whereby 1.1Mtpa and alternately 2.2Mtpa of<br />

product would be produced annually. SRK conducted a pit optimization, pit design and<br />

production schedules to independently test the assumptions made in mine costing and reported in<br />

the economic model.<br />

13.1.1 Pit Optimization<br />

Pit optimization was carried out on the Cerrado <strong>Verde</strong> deposit using Whittle v4.3 pit<br />

optimization software in conjunction with Maptek’s Vulcan (v8) general-purpose mine<br />

planning package.<br />

This PEA includes the inferred mineral resources that are considered too speculative geologically<br />

to have the economic considerations applied to them that would enable them to be categorized as<br />

mineral reserves. There is no certainty that the preliminary assessment will ever be realized.<br />

Mineral resources that are not mineral reserves do not have demonstrated economic viability.<br />

13.1.2 Whittle Parameters<br />

Table13.1.2.1 illustrates the parameters and dimensions of the Vulcan block model exported to<br />

Whittle for pit optimization.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 13-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 13.1.2.1: Whittle Block Model Dimensions<br />

Whittle Parameter Type Value<br />

Base Units<br />

Inferred Unit Product Tonnes<br />

Block Model Dimensions<br />

Geological<br />

X 100<br />

Y 100<br />

Z 10<br />

No. X 20<br />

No. Y 35<br />

No. Z 45<br />

Slope<br />

Bearing<br />

Slope Angle<br />

All Walls 0 45<br />

As part of the preliminary analysis of the Cerro <strong>Verde</strong> deposit, <strong>Verde</strong> will evaluate the cost<br />

benefit analysis of building a 1.1Mpta versus 2.2mpta process plant. Due to changes in market<br />

conditions, economies of scale and operating costs based on production, SRK performed a<br />

Whittle analysis of both operating conditions. These parameters are detailed in Table 13.1.2.2.<br />

Recoveries used in the pit optimization represent the mass yield of plant feed to product<br />

produced.<br />

The Whittle parameters are estimated before the final economic model is constructed and may<br />

require further iterations in the future.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 13-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 13.1.2.2: Whittle Parameters<br />

Whittle Parameter Type Value<br />

Mining Cost<br />

Price Reference Mining Cost 2<br />

Mining Recovery Fraction 1<br />

Mining Dilution Factor 1<br />

Processing Cost 1.1 Mt<br />

Rock Type Process Name PRCS<br />

Rocktype 1<br />

HG<br />

Rocktype 2<br />

LG<br />

Process Cost ($/ore.t) Ore Selection Method Cash Flow<br />

Process Cost (1.1 Mtpa) 41.8<br />

Process Cost (2.2 Mtpa) 36.4<br />

Recoveries Mass Product Recovery (HG) 0.83<br />

Mass Product Recovery (LG) 0.83<br />

Revenue and Selling Cost<br />

Product<br />

unit<br />

Product Price (1.1 Mtpa)<br />

$151.82/prod.t<br />

Product Price (2.2 Mtpa)<br />

$133.23/prod.t<br />

Optimization<br />

Revenue factor range<br />

0.01-.99 50 factors<br />

Operational Scenario - Time Costs<br />

(Really sustaining) Initial Capital Cost (1.1 Mtpa) $ 197,000,000<br />

Initial Capital Cost (2.2 Mtpa) $ 269,000,000<br />

Discount Rate Per period 10<br />

Operational Scenario – Limits<br />

Mining Limit<br />

na<br />

Processing Method Limit (1.1 Mtpa)<br />

1,111,968 prod.t<br />

Processing Method Limit (2.2 Mtpa)<br />

2,223,158 prod.t<br />

13.1.3 Pit Optimization Analysis<br />

The results achieved through the process of pit optimization, indicated that there is minimal<br />

variability or selectivity for mining related decisions within the orebody block model at this time<br />

(2010). Given the size of block (100mx100mx10m), consistent strip ratio and profitability each<br />

block model block contains (using input parameters), the Whittle analysis is better suited as an<br />

independent check on production rate, mine life and NPV (Table 13.1.3.1).<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 13-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 13.1.3.1: Whittle Results<br />

Production Rate Units 1.1 Mtpa 2.2 Mtpa<br />

Potentially Mineable Resources t 152,411,794 152,411,794<br />

Waste t 46,206,355 46,206,355<br />

SR w:o 0.30 0.30<br />

Product Tonnes t 126,501,784 126,501,784<br />

Initial Capital US$ 197,000,000 269,000,000<br />

Sales Price US$ 152 133<br />

NPV US$ 881,992,227 1,647,723,559<br />

Life yr 137 57<br />

Payback yr 1.82 1.41<br />

IRR % 54 71<br />

*This PEA includes the inferred mineral resources that are considered too speculative geologically to have the economic considerations applied<br />

to them that would enable them to be categorized as mineral reserves. There is no certainty that the preliminary assessment will ever be realized.<br />

Mineral resources that are not mineral reserves do not have demonstrated economic viability<br />

It must be stressed that the results reported in Table 13.1.3.1 are for comparative purposes to<br />

check effect of production rate. If compared to the economic model, the NPV number will vary<br />

considerably given lack of taxes, duties, depreciation and other miscellaneous expenses. The<br />

mine life achieved for both cases re-enforce that resource inventory for feed stock is not a<br />

limiting factor for the potential operation.<br />

13.1.4 Pit Design<br />

Pit designs for the Cerrado <strong>Verde</strong> deposit were constructed using Vulcan 8 general-purpose<br />

mine planning package. The final pit design used was based on pit optimization results as a<br />

guide for toe and crest location. No Ramps were added given the preliminary nature of the block<br />

model and because the majority of the resource daylights within current valley systems on site.<br />

Pit Dimensions<br />

SRK used default pit parameters illustrated in Table 13.1.4.1.<br />

Table 13.1.4.1: Pit Design Parameters<br />

Dump Parameter<br />

Value<br />

Batter/Bench Face Angle 64º<br />

Berm Width 2.5m<br />

Bench Height<br />

5m<br />

Overall Slope 45º<br />

SRK constructed three pit designs representing three phases used in construction of a preliminary<br />

production schedule. Figure 13-1 illustrates the final pit design layout and tonnage basis for the<br />

production schedule.<br />

SRK did not construct any form of dump design. Given the low stripping ratio and abundance of<br />

land that waste can be placed, SRK does not consider creating a waste dump design material for<br />

the project at this stage.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 13-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

13.1.5 Production Schedule<br />

SRK produced a mine production schedule based on the resource block model and phased pit<br />

design. Using a target rate of either 1.1 or 2.2Mt of produced product, the RoM tonnage and<br />

variable stripping ratio of the deposit was calculated for each case. A simple pancake extraction<br />

method of benches within each phase made up the mining sequence.<br />

As the mine life was so extensive, the first 10 years of the production schedule for the 1.1 and<br />

2.2Mpta cases have been illustrated in Tables 13.1.5.1 and 13.1.5.2 respectively.<br />

Table 13.1.5.1: First 10 Years of 1.1Mtpa Production Schedule<br />

Period 1 2 3 4 5 6 7 8 9 10<br />

Target Tpd 3,940 3,940 3,940 3,940 3,940 3,940 3,940 3,940 3,940 3,940<br />

Target 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720<br />

Accumulation 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720<br />

Accumulated Grade 8.66 9.00 8.74 8.62 8.65 8.86 8.86 9.38 8.61 8.80<br />

TargetGradeK 2 0 8.50 8.50 8.50 8.50 8.50 8.50 8.50 8.50 8.50 8.50<br />

Stripping Ratio 2.<strong>43</strong> 1.20 0.63 0.66 0.75 0.65 0.65 0.46 0.32 0.35<br />

Total Tpd 13,530 8,674 6,415 6,524 6,911 6,489 6,489 5,759 5,217 5,327<br />

BK 2 O 8.66 9.00 8.74 8.62 8.65 8.86 8.86 9.38 8.61 8.80<br />

BK 2 O_MASS 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720 1,339,720<br />

TOTAL_MASS 4,600,230 2,949,073 2,181,106 2,218,264 2,349,726 2,206,411 2,206,411 1,957,952 1,773,900 1,811,074<br />

HGBK 2 O 10.32 10.76 10.69 10.61 10.61 10.89 10.89 10.89 10.89 10.85<br />

HGBK 2 O_MASS 895,600 847,423 718,<strong>43</strong>2 695,448 695,448 709,445 709,445 851,334 558,060 629,961<br />

HGTOTAL_MASS 895,600 847,423 718,<strong>43</strong>2 695,448 695,448 709,445 709,445 851,334 558,060 629,961<br />

WASTETOTAL_VOLUME 1,212,085 598,272 312,783 326,596 375,467 322,190 322,190 229,826 161,405 175,224<br />

WASTETOTAL_MASS 3,260,510 1,609,353 841,385 878,5<strong>43</strong> 1,010,005 866,690 866,690 618,231 <strong>43</strong>4,180 471,353<br />

LGBK 2 O 5.33 5.97 6.48 6.48 6.53 6.57 6.57 6.75 6.98 6.98<br />

LGBK 2 O_MASS 444,121 492,298 621,289 644,273 644,273 630,276 630,276 488,387 781,660 709,760<br />

LGTOTAL_MASS 444,121 492,298 621,289 644,273 644,273 630,276 630,276 488,387 781,660 709,760<br />

*This PEA includes the inferred mineral resources that are considered too speculative geologically to have the economic considerations applied<br />

to them that would enable them to be categorized as mineral reserves. There is no certainty that the preliminary assessment will ever be realized.<br />

Mineral resources that are not mineral reserves do not have demonstrated economic viability<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 13-6<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 13.1.5.2: First 10 Years of 2.2Mtpa Production Schedule<br />

Period 1 2 3 4 5 6 7 8 9 10<br />

Target Tpd 7,878 7,878 7,878 7,878 7,878 7,878 7,878 7,878 7,878 7,878<br />

Target 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504<br />

Accumulation 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504<br />

Accumulated Grade 9.47 9.12 8.83 8.86 9.17 9.08 9.92 9.78 9.32 9.24<br />

TargetGradeK 2 0 8.50 8.50 8.50 8.50 8.50 8.50 8.50 8.50 8.50 8.50<br />

Stripping Ratio 1.67 0.79 0.51 0.65 0.45 0.36 0.28 0.28 0.36 0.40<br />

Total Tpd 21,042 14,133 11,900 12,973 11,414 10,683 10,106 10,091 10,716 11,044<br />

BK 2 O 9.47 9.12 8.83 8.86 9.17 9.08 9.92 9.78 9.32 9.24<br />

BK 2 O_MASS 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504 2,678,504<br />

TOTAL_MASS 7,154,331 4,805,259 4,045,860 4,410,934 3,880,893 3,632,330 3,<strong>43</strong>6,012 3,<strong>43</strong>0,840 3,6<strong>43</strong>,504 3,755,079<br />

HGBK 2 O 10.57 10.61 10.89 10.89 10.85 10.85 10.91 10.91 10.92 10.92<br />

HGBK 2 O_MASS 2,113,730 1,738,619 1,418,890 1,418,890 1,551,163 1,453,635 2,003,330 1,905,802 1,587,025 1,521,407<br />

HGTOTAL_MASS 2,113,730 1,738,619 1,418,890 1,418,890 1,551,163 1,453,635 2,003,330 1,905,802 1,587,025 1,521,407<br />

WASTETOTAL_VOLUME 1,663,876 790,615 508,311 644,026 446,985 354,582 281,601 279,679 358,736 400,214<br />

WASTETOTAL_MASS 4,475,827 2,126,755 1,367,356 1,732,<strong>43</strong>0 1,202,389 953,826 757,508 752,336 964,999 1,076,575<br />

LGBK 2 O 5.33 6.36 6.50 6.57 6.85 6.98 6.98 6.98 7.00 7.02<br />

LGBK 2 O_MASS 564,774 939,885 1,259,614 1,259,614 1,127,341 1,224,869 675,174 772,702 1,091,479 1,157,097<br />

LGTOTAL_MASS 564,774 939,885 1,259,614 1,259,614 1,127,341 1,224,869 675,174 772,702 1,091,479 1,157,097<br />

*This PEA includes the inferred mineral resources that are considered too speculative geologically to have the economic considerations applied<br />

to them that would enable them to be categorized as mineral reserves. There is no certainty that the preliminary assessment will ever be realized.<br />

Mineral resources that are not mineral reserves do not have demonstrated economic viability<br />

Given the limited amount of drill hole information for such a large resource, the development of<br />

a specific mine fleet is somewhat premature. For the purposes of this report, standard operating<br />

procedures, costing and equipment sizing for a deposit of this nature has been considered.<br />

Mining will consist of clear and grubbing, waste stripping and extraction of potential resource;<br />

using front-end-loaders suitable for 20t highway trucks. The need for drill and blast operations<br />

has not been considered at this stage.<br />

<strong>Verde</strong> has indicated that a mine contractor will be employed to haul mineralized material from<br />

the mine face to the process plant facility. ECM has suggested a static mining cost per year.<br />

This static cost has been estimated over the SRK production schedule to determine a reference<br />

mining cost for comparison purposes.<br />

Along with a suggested mining fleet the total annual cost is detailed in Tables 13.1.5.3 and<br />

13.1.5.4.<br />

Table 13.1.5.3: 1.1Mtpa Product Mine Fleet and Annual Estimated Cost<br />

Equipment Model Amount Operating Costs (US$/year 000’s)<br />

Truck Scania 420 4 1,340<br />

Track Excavators R964 2 1,390<br />

Tractor D9-T 2 1,005<br />

Motor Grader 16G 1 251<br />

Truck Scania 40t 2 558<br />

Wheel Loaders 980G 2 894<br />

Mitsubishi L200 2 107<br />

Truck M.Benz 1315C/48 1 102<br />

Truck M.Benz/Lubrication 1315C/48 1 102<br />

Water Truck Scania 40t 2 371<br />

Total $6,120<br />

Source: ECM S/A Projectos Industrias, 623-01-0000-N-H25-0102, 2010<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 13-7<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

SRK is of the opinion that this cost is conservative when applied over 1.3Mtpa of RoM<br />

production at a strip ratio of 0.4 (for the 1.1Mtpa base case). Over the life of the mine this would<br />

equate to a mining cost of approximately $3.3/t moved.<br />

Table 13.1.5.4: 2.2Mtpa Product Mine Fleet and Annual Estimated Cost<br />

Equipment Model Amount Operating Costs (US$/year 000’s)<br />

Truck Scania 420 6 2,010<br />

Track Excavators R964 3 2,085<br />

Tractor D9-T 3 1,508<br />

Motor Grader 16G 1 251<br />

Truck Escânia 40t 2 558<br />

Wheel Loaders 980G 2 894<br />

Mitsubishi L200 2 107<br />

Truck M.Benz 1315C/48 1 102<br />

Truck M.Benz/Lubrication 1315C/48 1 102<br />

Water Truck Escânia 40t 2 371<br />

Total $7,988<br />

Source: ECM S/A Projectos Industrias, 623-01-0000-N-H25-0104, 2010<br />

SRK is of the opinion that this cost is conservative when applied over 2.6Mtpa of RoM<br />

production at a strip ratio of 0.4 (for the 2.2Mtpa base case). Over the life of the mine this would<br />

equate to a mining cost of approximately $2.5/t moved. While closer to expected contract rates<br />

in Brazil, but this is still quite expensive.<br />

13.1.6 Recovery<br />

<strong>Verde</strong>te deposits owned by <strong>Verde</strong> are essential outcropping, leading to a very low stripping ratio.<br />

In the scoping study, a stripping ratio of 0.1:1 was assumed, and open pit operation is being<br />

foreseen.<br />

Researches were carried out to determine an Unweathered <strong>Verde</strong>te area close to which plant site<br />

will be erected.<br />

During Thermo<strong>Potash</strong> processing, all the run-of-mine is supposed to be used for grinding the raw<br />

meal to heat treatment. Intensive quality control during processing ensures. Therefore, losses of<br />

RoM <strong>Verde</strong>te are not expected.<br />

In all pellet handling steps, dust is expected to be generated due to superficial friction. The dust<br />

is to be collected and sent to raw preparation area for recycling.<br />

As a result of this, recoverability is assumed to be in the range of 90 to 100%.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


*Map image not to scale. For illustrative purposes only.<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

<strong>Preliminary</strong> Pit Design<br />

SRK Project No.: 3<strong>43</strong>500.020<br />

File Name: Figure_13-1 Date: 09/15/2011 Approved: BS Figure: 13-1


<strong>Verde</strong> <strong>Potash</strong> Plc 14-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

14<br />

Project Infrastructure (Item 18)<br />

14.1 Access Road and Transportation<br />

The principal access to the property are; the BR-262 and BR-354, MG-235. Primary access is by<br />

gravel roads that connect the farming region. The road upgrade costs are imbedded within the<br />

mine capital and operating costs.<br />

14.2 Power Supply<br />

Sections 14.2, 14.3, 14.3.1, and 14.7 have been extracted from the ECM, 2010 report.<br />

Cerrado <strong>Verde</strong> Project at São Gotardo is scheduled to be powered by CEMIG 138kV system,<br />

connected through an exclusive transmission line 23km long, from a substation close to the town<br />

of São Gotardo.<br />

In electrical terms the development of the beneficiation shall be considered middle size, with an<br />

estimated demand of around 25MW similar to a small town such as the São Gotardo and the<br />

surrounding places.<br />

The configuration set for the factory system, has the main 138kV receiving substation, lowers to<br />

13.8kV and distributes to the substations that will serve each of the main project areas.<br />

It is observed that over 70% of the demand will be concentrated in three areas, grinding,<br />

calcination kiln, and pellets quenching systems and as a result, the location of the main<br />

substation shall be as close to the grinding and regrinding substations.<br />

For the main substation two 138-13.8kV transformers are provided with 25/40MVA estimated<br />

power, with the load distributed between both, and if one of them fails to work, the other<br />

remaining transformer shall still supply the total demand at the forced ventilation stage.<br />

According to CEMIG (governmental electrical energy agency) regulations harmonic<br />

compensation and power factor systems shall be forecasted so that the operational performance<br />

of large equipment/heavy loads do not affect the basic system network and other consumers.<br />

From the main substation power will be distributed to area substations through 13.8kV feeders,<br />

by means of radial-type simple system, and according to the need cable racks may be used for<br />

beneficiation, aerial lines for distant facilities and piping network at the operational and<br />

administrative support areas or where for safety reasons the use of aerial systems is not possible.<br />

The area substation will be constructed in its majority at masonry buildings, and there will be a<br />

few armored substations, housing all the electrical equipment to receive power at 13.8kV, lowers<br />

it and feed all the electrical charges of the area (s) and / or buildings served by it.<br />

To meet the equipment electrical supply that cannot stop operating in case of electrical failure,<br />

emergency power supply system is provided with diesel generator and an automatic generator<br />

group, mainly targeting the auxiliary grinding systems, some pumps, a compressor for pneumatic<br />

conveying, for emergency lighting and the noble parts of the supervision, control and<br />

communication systems.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 14-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

14.3 Water Supply<br />

Essentially, the water system that serves the beneficiation shall be divided into the following<br />

parts:<br />

Process Water - is part of raw water intended for industrial use, which will be stocked at<br />

the reservoir located on the site highest plateau, next to the raw water reservoir and then<br />

distributed as make up water for burnt pellets quenching system at the cooling tower<br />

tank, to process route consumption, for services and general cleaning, including the<br />

central maintenance workshop; and<br />

Raw Water - is the new water which intake will be performed from Indaiá River and<br />

stored at a tank; the intake from the river will be at dry well, with horizontal pumps, sand<br />

filter box and is located approximately 9km from the raw water reservoir. The raw water<br />

will be used for the following purposes:<br />

For pumps sealing;<br />

For pellets quenching system make up;<br />

For circulating at the heat exchangers of equipment refrigeration systems;<br />

For dust removing systems;<br />

For pelletizing;<br />

For fresh water generation by the Water Treatment Station; and<br />

For firefighting system.<br />

14.3.1 Rainwater Drainage<br />

The drainage system shall be designed to comprise all devices designed to intercept, intake and<br />

dispose of run-offs that flow to the plateaus, terraces, accesses and buildings, leading them to the<br />

point of final release.<br />

The plateaus, berms and access designed in different elevations, will be drained and its<br />

contribution will be sent to a sedimentation basin and damping.<br />

The embankment stools slopes (cut / landfill) will be cross slope to collect contributions from<br />

longitudinal discharge and sections with concrete gutters, unloading at water flowing downhill<br />

sent for intake boxes and sequentially to the drainage system.<br />

14.3.2 Hydraulic Sizing<br />

The following criteria and methods shall be considered in establishing the methodology of the<br />

hydraulic design of the devices:<br />

Physical characterization of the Area - Location, type of relief, occupation and land<br />

cover;<br />

Climate Characterization - climate is classified according to the International System of<br />

Köppen;<br />

Studies of heavy rainfall - shall be used Gumbel statistical methods and CETESB rain<br />

disaggregation;<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 14-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

<br />

Surface runoff studies - comprising the analysis of the physiographic features of the basin<br />

and its coverage;<br />

Determination of the Project Flow - shall be developed according to the Rational Method;<br />

Surface Runoff Coefficient - shall be considered depending on the type of area to be<br />

drained and surface coverage;<br />

Concentration Time - shall be calculated using the Kirpich formula;<br />

Rainfall intensity - shall be calculated for the rainfall post of the region;<br />

Rainfall Calculation - rain duration (tc) = 2.0 hours shall be adopted;<br />

Precipitation per square meter - the duration of rain (tc) = 2.0 hours shall be adopted;<br />

Precipitation per square meter that drains - the runoff coefficient = 0.90 shall be adopted;<br />

and<br />

Time Period of Return and Recurrence - (TR) = 10 years.<br />

14.4 Buildings and Ancillary Facilities<br />

There are no buildings or other facilities on the property, besides a rented small shelter for field<br />

activities support in the city of Matutina, and the main office in Brazil in Belo Horizonte. Plant,<br />

Mill, office, and mine building will be constructed as part of the mine development in the area.<br />

14.5 Potential Processing Plant Sites<br />

Among the several possibilities for site location, <strong>Verde</strong> is considering to install the plant close to<br />

Matutina, a small town close to the City of Sao Gotardo, which is a local pole. Two sites are<br />

being considered, Target 7 and Funchal Norte Target.<br />

14.6 Potential Tailings Storage Area<br />

Tailings from process are generated due to:<br />

Inadequate particle size, as the product has to be produced in a 2-4mm diameter range.<br />

Tailings are those materials which do not comply with such specification, mainly dust<br />

from pellet handling; and<br />

Unburned or not sufficiently burned material, produced mainly from flushes during kiln<br />

operation.<br />

Both are to be stored in Storage & Reclaiming stockpile, to be reprocessed. Therefore, no tailing<br />

accumulation or landfilling is foreseen for tailings. The Storage & Reclaiming stockpile area has<br />

not yet been defined.<br />

14.7 Potential Waste Disposal Area<br />

The design criteria adopted for the landfill areas (location not yet defined), shall include the<br />

implementation of the materials deposit, whether from cuts, or loan, within the limits of design<br />

sections ("offset") at the project influence areas facilities.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 14-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Confirmation of geotechnical condition will provide evaluation of classification, distribution and<br />

quantification of material to be selected from the 1st and 2nd categories, with the quality and the<br />

allocation provided, during elaboration of detailed earthworks design.<br />

Preliminarily, the following criteria were adopted for the classification, distribution and<br />

geometry of the landfill slopes, until geotechnical surveys geotechnical surveys campaigns to be<br />

programmed are carried out:<br />

Compacted landfills at a minimum 95%: 70%;<br />

Compacted landfills at a minimum 100%: 30%;<br />

degree of blistering: 30%;<br />

Landfill slopes: V=1 / H=1,5;<br />

Berms balance width: 4.0m, with cross slope of 5% and 0.5% longitudinal; and<br />

Maximum height between stools: 5.0m.<br />

The basic design shall present forms for plant restoration, as well as methods of restoration and /<br />

or protection of exposed areas (slopes, areas of loans, stools, water cuts, gutters, ditches, etc.) as<br />

per erosion resistance conditions.<br />

14.8 Manpower<br />

São Gotardo and Matutina are the closest towns with a significant population to provide<br />

manpower for a mining operation, having population around 40,000 combined.<br />

Also, the project is very close to Patos de Minas, main city in Alto Paranaiba area which has<br />

strong economic, cultural, educational and social environment.<br />

14.9 Other Surface Rights<br />

The project is at the exploration phase and surface rights for processing plant site, tailing storage<br />

and waste disposal areas have yet to be acquired.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 15-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

15<br />

Market Studies and Contracts (Item 19)<br />

15.1 Market Studies<br />

15.1.1 Introduction<br />

The goal of AgroConsult study is to analyze the economic feasibility of using Thermo<strong>Potash</strong><br />

(8% K2O) as a source of potassium for fertilizing activities in the states of Minas Gerais, Mato<br />

Grosso, Mato Grosso do Sul, São Paulo, Paraná, Goiás and Bahia.<br />

In order to determine a market potential of Thermo<strong>Potash</strong>, was conducted a comparative analysis<br />

of its pricing competitiveness in relation to traditional raw materials. The project looked at<br />

possible uses for Thermo<strong>Potash</strong> as a source of potassium in the main NPK formulas most<br />

commonly used on each crop (soybeans, cotton, sugarcane, summer corn, second crop corn, dry<br />

rice, irrigated rice, beans, potatoes, coffee, pasture, reforestation, wheat, sorghum and fruit and<br />

vegetables) in each state.<br />

Today, Brazil is the world's fourth-largest consumer of fertilizers. In 2009, 22.5Mt of fertilizer<br />

were used in Brazil and this figure is expected to rise to 23.58 million in 2010. (Source: 2009<br />

Statistical Yearbook of the Fertilizer Industry from ANDA – Associação Nacional para Difusão<br />

de Adubos – Nacional Association for Promotion of Fertilizer) Fertilizer application is vital for<br />

the performance of the farming industry and is likely to remain important for the foreseeable<br />

future. However, more than half of the fertilizer consumed in Brazil is imported, which<br />

represents a fundamental weakness for local agribusiness. There is an even greater dependence<br />

on potash, which is supplied as potassium chloride, more than 90% of which has to be imported.<br />

Since 2008, the government, the private sector and Brazilian agribusiness leaders have been<br />

playing closer attention to this issue. There is clear agreement that Brazil needs to reduce its<br />

dependence on imported fertilizers. To do so, Brazil needs to take two steps: expand raw<br />

material production and develop new sources of nutrients.<br />

In this case, introducing Thermo<strong>Potash</strong> as a new source of potassium on the Brazilian fertilizer<br />

market is a timely move, in line with government, private sector and producer concerns.<br />

Was used the forecast data for 2010 fertilizer deliveries estimated at 23.58Mt of product and 3.97<br />

million K 2 O, 82% of which is consumed as NPK formulas and 18% on its own. Using the same<br />

information, the states included in this survey represent 76% of the fertilizer market and 76.1%<br />

of Brazilian K 2 O consumption.<br />

The following sections will provide information on the Brazilian agribusiness and fertilizer<br />

markets, the methodology adopted these results by the survey as well as the price and market<br />

potential for Thermo<strong>Potash</strong> in each state.<br />

15.1.2 Methodology<br />

The goal of this study is to analyze the economic feasibility of using Thermo<strong>Potash</strong> (8% K 2 O) in<br />

the main fertilizer formulas marketed in Minas Gerais, Mato Grosso, Mato Grosso do Sul, São<br />

Paulo, Paraná, Goiás and Bahia.<br />

To do so, we evaluated the fertilizer markets in the selected regions during 2010 and estimated<br />

fertilizer delivery volumes by crop and nutrient (N, P e K 2 O). The data was taken from the<br />

AgroConsult database, which is frequently updated with market information.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 15-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

These results from the database were validated by comparing fertilizer volumes, nutrient<br />

volumes and the average formula with information from the National Association for Fertilizer<br />

Diffusion – ANDA. Furthermore, we verified that nutrient consumption by crop was compatible<br />

with estimated or actual productivity. The final results are converted into raw material<br />

consumption and consolidated figures for Brazil are compared with the supply and demand<br />

figures.<br />

Based on this data, after building an optimization model based on linear programming, we<br />

initially calculated the costs of traditional formulas (not including Thermo<strong>Potash</strong>) based on the<br />

best combination (lowest cost) of raw material mixtures best suited to expected productivity<br />

levels in each region.<br />

Subsequently, was used the same procedure including Thermo<strong>Potash</strong> with 8% K 2 O at a price of<br />

zero to determine the maximum product volume in NPK formulas. Based on the formula<br />

compositions obtained by the model, we estimated a price for Thermo<strong>Potash</strong> so that the cost of<br />

the differentiated formula was identical to the traditional formula. This allows us to calculate the<br />

average quantity of Thermo<strong>Potash</strong> per ton of fertilizer and by applying this to the planted area<br />

for each crop; we were able to estimate potential demand for Thermo<strong>Potash</strong> in the main fertilizer<br />

formulas used in each state.<br />

The raw materials were priced at market value for September/2010, based on an AgroConsult<br />

survey. In this case, the product cost at each mixing center also took into account domestic<br />

shipping as well as breakage and inventory costs. The exchange rate used was 1.8 BRL/US<br />

dollars.<br />

15.1.3 Determining the Crop Portfolio and Formulas<br />

The project took into account the fertilizer technology for the following groups of crops:<br />

<br />

Major Crops: These crops are present around 97% of the market and include pasture,<br />

soybeans, summer corn and second crop corn, rice (dry and irrigated), beans (3 types),<br />

wheat, reforestation, sugarcane, cotton, coffee and potatoes (three crops); and<br />

Other crops: These crops represent 3% of the market and include bananas, cocoa, grapes,<br />

avocados, pineapples, ramie, sisal, figs, pears, apples, melons, watermelons, strawberries,<br />

guava, guaraná, mango, passion fruit, cashew, coconuts, peanuts, other fruits, vegetables<br />

and fibers, sunflowers, sorghum and tobacco.<br />

The survey looked at the fertilizer technology adopted in each state based on the fertilizer system<br />

used. We analyzed the main formulas and dosages used to adequately fertilize in line with<br />

productivity expectations, for each crop (Table 15.1.3.1).<br />

In each region, we looked at the six main formulas used for each crop, the proportional<br />

relationship between the formulas and optimization of each formula in relation to its raw material<br />

composition.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 15-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 15.1.3.1: Example of Fertilizing System Adopted for Each Crop Analyzed<br />

Cotton Soybean Sugar Cane Corn Corn (Winter) Rice (Dry) Rice (IRR)<br />

05.20.15 00.20.20 05.25.25 03.16.16 08.16.16 04.20.20 04.20.20<br />

08.25.15 02.20.18 20.05.20 08.20.20 08.25.15 04.20.15 04.20.15<br />

05.25.15 00.18.18 14.07.28 08.25.15 12.15.15 04.22.15 05.25.15<br />

08.28.16 00.20.10 15.05.15 06.30.15 08.20.20 04.25.15 04.25.15<br />

20.00.20 02.20.10 20.00.20 20.00.20 20.00.20 20.00.20 20.00.20<br />

36.00.12 00.20.18 36.00.12 36.00.12 36.00.12 36.00.12 36.00.12<br />

Source: AgroConsult<br />

15.1.4 Formula Optimization Process<br />

The optimization model, structured by linear programming, takes into account:<br />

List of the main raw materials available at mixing centers;<br />

Raw material nutrient levels;<br />

Chemical incompatibility between raw materials;<br />

Nutrient supplies (primary, secondary and micronutrients);<br />

Lowest cost; and<br />

Market price system. For nitrogenous fertilizer and potash prices, imported raw materials<br />

were taken into account. For phosphates, imported and domestic prices for used, given<br />

the level of supply in the Minas Gerais and Catalão, GO regions.<br />

The formulas were optimized using the following criteria:<br />

Conventional formula not including Thermo<strong>Potash</strong>;<br />

The same formula using Thermo<strong>Potash</strong> at zero price, in order to determine the maximum<br />

volume of the product in the composition;<br />

A likely end price for Thermo<strong>Potash</strong> was determined so that the formula including<br />

Thermo<strong>Potash</strong> cost the same as the formula without Thermo<strong>Potash</strong>; and<br />

We then determined the average dose of Thermo<strong>Potash</strong> per ton and per crop.<br />

For raw material prices; the price composition in each mixing center was calculated based on<br />

raw material cost, transport value and breakage and inventory expenses. As an example, the<br />

prices from the Uberaba center are shown in Table 15.1.4.1. The exchange rate used was 1.8<br />

BRL/US dollars.<br />

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Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 15-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 15.1.4.1: Price Composition of Raw Materials at the Uberaba Center<br />

Raw Material Freight Cost at Break Storage<br />

Blender Raw Material Origin<br />

Cost (domestic) Factory (%) (%) Total Cost<br />

UREIA Importada 310.00 51.35 361.35 1.00 0.4 366.42<br />

SAMGR Importada 209.82 42.11 251.93 1.00 1.6 258.52<br />

Nitrato de Amonio Fosfertil 506.00 3.46 509.46 0.50 0.4<br />

Uberaba MAP GR Fosfertil 403.68 3.46 407.14 0.50 0.4 410.81<br />

TSP GR Fosfertil 247.35 3.46 250.81 0.50 0.4 253.07<br />

SSP GR BPI - 226.00 3.46 229.46 0.50 0.4 231.53<br />

Cubatao<br />

KCL GR Importada 462.80 42.11 504.91 0.50 1.6 515.55<br />

Source: Survey data<br />

The N, P and K levels in the raw materials used during optimization are listed in Table 15.1.4.2.<br />

Table 15.1.4.2: Raw Material Nutrient Levels<br />

Element SAM Urea NAM Term K SSP STP MAP DAP KCI<br />

N 20.0% 16.0% 34.5% 0.0% 10.5% 16.0%<br />

P 20.0% 46,0% 54.0% 45.0%<br />

K 8.0% 60.0%<br />

Source: Survey data<br />

The levels of K 2 O, CaO, SiO 2 , MgO and S, as well as the status of each of the three products<br />

evaluated are listed in Table 15.1.4.3.<br />

Table 15.1.4.3: Content Used and Status of Products Evaluated<br />

Elements<br />

Content (%)<br />

Product 01 Product 02 Product 03<br />

K 2 O 8.00% 8.00% 8.00%<br />

CaO 30.00% 19.50% 30.00%<br />

SiO 2 40.00% 32.70% 40.00%<br />

MgO 2.30% 8.60% 2.30%<br />

S 10.00%<br />

Status Product used in the study Product with Ca and Mg<br />

included in balancing<br />

Product undergoing<br />

technological development<br />

Source: Survey data<br />

15.1.5 Thermo<strong>Potash</strong> Pricing Process<br />

After conducting the optimization process, the model provides us with the demand for<br />

Thermo<strong>Potash</strong> and the product price, so that the differentiated formula costs the same as the<br />

traditional formula.<br />

Based on these prices, AgroConsult calculated a weighted Thermo<strong>Potash</strong> price for each of the<br />

crops based on proportion of each of the formulas in the fertilizing system. Then, in order to<br />

reach an average price per mixing center, the Thermo<strong>Potash</strong> benchmark price for each of the<br />

crops was weighted in accordance with the relevant demand potential. The assumption that<br />

formula costs would be the same was applied during this stage.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 15-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

However, the average weighted price obtained reflects individual prices per crop. Consequently,<br />

the price would exceed the maximum price for some crops and the product would be too<br />

expensive. Therefore, the price was realigned to cater to 95% of the potential market. In this<br />

case, the resulting price is the potential price for Thermo<strong>Potash</strong> at the mixing center.<br />

Then, discounting transport and ICMS costs, we obtained an adjusted Thermo<strong>Potash</strong> price at<br />

source (São Gotardo-Minas Gerais).<br />

15.1.6 Process to Determine the Potential Market for Thermo<strong>Potash</strong><br />

Was calculated the potential market for Thermo<strong>Potash</strong> for each of the crops and the results were<br />

then added together to calculate the potential in each state.<br />

In this calculation, the data was based on 2010 fertilizer demand for each crop in each state.<br />

Then, based on frequent market surveys carried out by AgroConsult, we defined the market share<br />

of each of the six formulas selected during the fertilizer process, totaling 100%. This is how we<br />

obtained the fertilizer volume used in each of the formulas.<br />

Based on the proportion of Thermo<strong>Potash</strong> in each of these formulas (1,000kg), obtained using<br />

the optimization process, we calculated the Thermo<strong>Potash</strong> potential for each formula. In this<br />

case, we multiplied the proportion of Thermo<strong>Potash</strong> by the volume of fertilizer in each of the<br />

formulas.<br />

Total Thermo<strong>Potash</strong> potential for each of the six formulas provides us with the potential market<br />

for each crop. Market potential by state is obtained by adding together the results from each<br />

crop.<br />

15.2 Contracts<br />

<strong>Verde</strong> does not yet have any contracts in place at the time of this report.<br />

The QP has reviewed data and information provided by ArgoConsult and finds that the<br />

assumptions made are reasonable.<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 16-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

16<br />

Environmental Studies, Permitting and<br />

Social or Community Impact (Item 20)<br />

Mining concessions can be applied for following a final exploration report to be submitted to,<br />

and approved by the Brazil’s Department of Mines and Energy (DNPM) by the final expiry date<br />

of the exploration license. The report must conclude and demonstrate that an economic mineral<br />

resource has been delineated and measured. Normally, a mining plan and feasibility study must<br />

be presented within a year. That is the moment for the environmental licenses. Those of<br />

installation and a license of operations are then issued by the applicable environmental agency as<br />

a prerequisite to the granting of the mining concession. A mining concession is granted for a<br />

period covering the mine life until the mineral reserves of the deposit are exhausted. A mining<br />

concession does not convey title to a mineral deposit but provides the holder with the right to<br />

extract, process, and sell minerals extracted from the deposit in accordance with a plan approved<br />

by the DNPM and environmental authorities.<br />

Environmental Regulation General environmental rules and obligations are relatively similar to<br />

those applicable in Canada. The Brazilian environmental policy is the responsibility of the<br />

Ministry of the Environment and is executed at three levels: federal, state, and municipal.<br />

SRK performed an independent review of the current regulatory context of exploration activities<br />

in Brazil. SRK also consulted with “Silva Martins, Vilas Boas, Lopes e Frattari Advogados”<br />

(SMVBLFA), a law firm with prior knowledge of the environmental permitting activities of<br />

<strong>Verde</strong>.<br />

Based on the SRK review and consultation with SMVBLFA, the requirements stipulated in the<br />

environmental legislation for the mining activities, when <strong>Verde</strong> is in this stage, is basically<br />

consolidated in the following:<br />

Study of Environmental Impacts ("EIA");<br />

Previous License ("LP");<br />

Installation License ("LI");<br />

Operational License (“LO”); and<br />

Rehabilitation Plan for Degraded Areas ("PRAD").<br />

An EIA is required as a condition for obtaining the LP for any activity which potentially causes<br />

substantial environmental impact. The LP, LI and LO are mandatory for installing, expanding,<br />

and operating any mining activity, except exploration, under the systems of mining concession or<br />

licensing. A PRAD requires suitable technical solutions to rehabilitate the soil and other aspects<br />

of the environment that might be degraded by mining operations. In recognition that the<br />

preparation of an EIA can represent a substantial financial burden for a smaller projects, a<br />

company can undertake a less detailed form of EIA called an "Environmental Diagnostic Report"<br />

in certain cases.<br />

Instituto Brasileiro do Meio Ambiente e dos Recursos Naturais Renováreis, the federal<br />

environmental agency, is in charge of the licensing of activities with environmental impacts in<br />

more than one state or in federal waters, while SUPRAM is in charge of the licensing of<br />

activities with environmental impacts within the State of Minas Gerais. The determination of<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 16-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

competence between the two environmental bodies may cause overlap which may result in some<br />

cases in problems and delays for mining companies.<br />

The proposed project, while in this phase of exploration, at first, will not require an<br />

environmental license. Parallel, the environmental reports that will be necessary to the<br />

application of the exploitation are already been prepared (EIA).<br />

The EIA is ongoing during 2011. <strong>Verde</strong> has hired the specialized company SSMA Assesoria de<br />

Consultoria LTDA (SSMA) to do all the EIA, which should be finished by the end of 2011.<br />

SSMA is in the course of preparing the study of environmental impacts (in Brazilian legislations<br />

it is named: EIA – Estudo de Impactos Ambienta) and the plan for the restoration of degraded<br />

areas (in Brazilian legislations it is named: PRAD – Plano de Recuperação de Áreas<br />

Degradadas), which is a requirement for filing the application for the Provisional License.<br />

The company filed the Description of the Activity Form (in Brazilian legislations it is named:<br />

Formulário de Caracterização do Empreendimento – FCE) on May 25, 2011, which is the first<br />

step of the environmental licensing procedure. Based on such form, the Minas Gerais<br />

Environmental Agency (which is named: Secretaria de Estado de Meio Ambiente e<br />

Desenvolvimento Sustentável – SEMAD) issued the Basic Instructions Form (in Brazilian<br />

legislations it is named: Formulário de Orientações Básicas – FOB) on September 13, 2011,<br />

which contains instructions on the issues to be addressed by the study of environmental impacts<br />

and the manners it should be prepared.<br />

Based on records available for review, <strong>Verde</strong> operates in accordance with Brazil legislation.<br />

With the completion of this Scoping Study, <strong>Verde</strong> will formalize reliable information of the<br />

project and have elements to complete the preparation of the necessary reports for obtaining the<br />

environmental permits.<br />

The selection of SSMA, a company qualified and specialized in making those reports, with<br />

experience and commitment to the observance of legal standards and best practices for<br />

implementing this will mitigate the risk of future remediation costs.<br />

It is difficult to determine the exact amounts which will be required to complete all land<br />

reclamation activities in connection with Cerrado <strong>Verde</strong> Project.<br />

The project is in an exploration phase and the reclamation bonds and other forms of financial<br />

assurance represent only a portion of the total amount of money that will be spent on reclamation<br />

activities over the life of a potential mine. Accordingly, it may be necessary to make a complete<br />

planned expenditures and operating plans in order to fund reclamation activities.<br />

As the Project seems to have a good recoverability, it appear won`t going to have the usual<br />

potential future liability for cleanup of tailings deposited on the expected future mining license<br />

areas and reprocessing. It is not possible to quantify at this time what the potential liability may<br />

be and detailed assessments need to be made to determine future land reclamation costs.<br />

The Project does not have a final Mine Plan of Operations and the conceptual level closure plan<br />

for the property, and therefore no reclamation and closure cost estimate budget due to the<br />

project’s preliminary nature.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 17-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

17<br />

Capital and Operating Costs (Item 21)<br />

17.1 Capital Costs<br />

Total capital costs are estimated at US$155.3 million for the 1.1Mtpa production rate and<br />

US$218.4 million for the 2.2Mtpa production rate. A detailed breakdown of the capital cost<br />

estimates is given in Table 17.1.1 and 17.1.2 respectively.<br />

Table 17.1.1: Summary Capital Cost by Facility in Reals and United States Dollars in<br />

thousands, Including Applicable Taxes for a 1.1Mtpa Operation<br />

Sub-area<br />

Total Price r$(000)<br />

Total Price us$(000)<br />

With Taxes<br />

With Taxes<br />

Total R$ 279,544 $155,302<br />

General area R$ 57,448 $31,915<br />

Primary crushing R$ 3,173 $1,763<br />

Secondary crushing R$ 5,253 $2,918<br />

Stockpile R$ 737 $409<br />

Limestone storage and dosing R$ 7,691 $4,273<br />

Grinding R$ 11,621 $6,456<br />

Pelletizing R$ 28,490 $15,828<br />

Furnace R$ 69,782 $38,768<br />

Quenching R$ 6,276 $3,487<br />

Pellets classification R$ 5,561 $3,089<br />

Bulk product classification,<br />

Storage, loading and shipping<br />

R$ 4,295 $2,386<br />

Raw water intake R$ 9,936 $5,520<br />

Fire fighting R$ 3,990 $2,217<br />

Compressed air R$ 6,702 $3,724<br />

Electrical substations R$ 33,254 $18,475<br />

Main substation and transmission line R$ 25,335 $14,075<br />

*Exchange Rate is R$1.80=USD1<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 17-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 17.1.2 Summary Capital Cost by Facility in Reals and United States Dollars in<br />

thousands, Including Applicable Taxes for a 2.2Mtpa Operation<br />

Sub-area<br />

Total Price R$(000)<br />

Total Price US$(000)<br />

With Taxes<br />

With Taxes<br />

Total R$ 393,131 $218,406<br />

General area R$ 57,448 $31,915<br />

Primary crushing R$ 6,204 $3,447<br />

Secondary crushing R$ 8,910 $4,950<br />

Stockpile R$ 1,965 $1,092<br />

Limestone storage and dosing R$ 9,531 $5,295<br />

Grinding R$ 20,010 $11,117<br />

Pelletizing R$ 40,138 $22,299<br />

Furnace R$ 139,563 $77,535<br />

Quenching R$ 12,552 $6,973<br />

Pellets classification R$ 8,119 $4,511<br />

Bulk product classification,<br />

storage, loading and shipping<br />

R$ 4,295 $2,386<br />

Raw water intake R$ 9,936 $5,520<br />

Fire fighting R$ 3,990 $2,217<br />

Compressed air R$ 6,702 $3,724<br />

Electrical substations R$ 38,<strong>43</strong>3 $21,352<br />

Main substation and transmission line R$ 25,335 $14,075<br />

*Exchange Rate is R$1.80=USD1<br />

17.1.1 Payback<br />

Based on the following economic evaluation for the two production rates, the 1.1Mtpa pellet<br />

production rate, project payback occurs in Year 3 of production. For the 2.2Mtpa production rate<br />

project payback occurs in Year 2 of production.<br />

17.2 Operating Costs<br />

For the production of fertilizer pellets with an estimated 8% to 10% K 2 O content, the 1.1Mtpa<br />

pellet production rate, operating costs are estimated at US$41.80/t of pellets, inclusive of General<br />

and Administrative costs. A summary breakdown of operating costs, excluding G&A, is<br />

presented in Table 17.2.1. For the 2.2Mtpa production rate operating costs are estimated at<br />

US$36.36/t of pellets produced, inclusive of G&A costs. A detailed breakdown of operating<br />

costs, excluding G&A, is presented in Table 17.2.2. Total operating costs are stated in both<br />

US$(000) and R$(000).<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 17-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Table 17.2.1: Summary of Operational Costs, 1.1Mtpa Using Petroleum Coke<br />

ITEM<br />

TOTAL/ YEAR<br />

US$(000)<br />

% US$/t pellets<br />

ELECTRIC POWER 8,317 20.3% $7.48<br />

PETCOKE 12,197 29.7% $10.97<br />

LIMESTONE 2,525 6.1% $2.27<br />

WEAR MATERIAL 88 0.2% $0.08<br />

PARTS / MAINTENANCE MATERIAL 1,996 4.9% $1.80<br />

TOTAL COSTS VARIABLES (USD) 25,123 61.2% $22.59<br />

OWN WORK FORCE (USD) 9,823 23.9% $8.83<br />

MINE (USD) 6,120 14.9% $5.50<br />

TOTAL OPERATIONAL COSTS (USD) 41,066 100% $36.93<br />

TOTAL OPERATIONAL COSTS (R$) R$ 73,919 100% R$ 66.48<br />

Table 17.2.2: Summary of Operational Costs, 2.2Mtpa using Petroleum Coke<br />

ITEM<br />

TOTAL/ YEAR<br />

US$(000)<br />

% US$/t pellets<br />

ELECTRIC POWER $16,094 22.6% $7.24<br />

PETCOKE $24,378 34.2% $10.97<br />

LIMESTONE $7,575 10.6% $3.41<br />

WEAR MATERIAL $166 0.2% $0.07<br />

PARTS / MAINTENANCE MATERIAL $3,365 4.7% $1.51<br />

TOTAL COSTS VARIABLES (USD) $51,577 72.3% $23.20<br />

OWN WORK FORCE (USD) $11,766 16.5% $5.29<br />

MINE (USD) $7,988 11.2% $3.59<br />

TOTAL OPERATIONAL COSTS (USD) $71,331 100% $32.09<br />

TOTAL OPERATIONAL COSTS (R$) R$ 128,396 100% R$ 57.75<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 18-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

18<br />

<strong>Economic</strong> Analysis (Item 22)<br />

The following economic analysis shows the results of two production rates, 1.1Mtpa and<br />

2.2Mtpa rates for the production of fertilizer pellets and is based only on the mineral resource<br />

estimated as of March 1, 2010. The base case used in this economic analysis is the 1.1Mtpa<br />

scenario. The results do not include the project resources for Targets 4, 6,7,10 and 11 that were<br />

drill defined after completion of the PEA.<br />

Readers are cautioned that this analysis is only a preliminary assessment based on conceptual<br />

mine plans and process flowsheets and inferred mineral resources, which are considered to be<br />

highly speculative geologically. There is no certainty that this PEA will be realized. Since there<br />

is no estimate of proven or probable reserves for the Project, this assessment only include cash<br />

flow forecasts on an annual basis for the mineral resource estimated as of March 1, 2010.<br />

Figures 18-1 contains the estimated annual cashflow, in thousands of USD, and production rate,<br />

in ktonnes, for the 1.1Mtpa production rate over the projected 40 year plan. The plan includes a<br />

2 year pre-production period with product recovered starting in year 3 of the project. As stated<br />

earlier, payback is estimated to occur in the 3 rd year of production.<br />

Figures 18-2 contains the estimated annual cashflow, in thousands of USD, and production rate,<br />

in ktonnes, for the 2.2Mtpa production rate over the projected 40 year plan. The plan includes a<br />

2 year pre-production period with product recovered starting in year 3 of the project. As stated<br />

earlier, payback is estimated to occur in the 2 nd year of production.<br />

The indicative economics for the 1.1Mtpa and 2.2Mtpa production rates are presented in Table<br />

18.1. This clearly demonstrates the encouraging economics for the Cerrado <strong>Verde</strong> Projects<br />

based on the scoping study concepts, cost projections and price assumptions as presented in this<br />

PEA.<br />

Table 18.1: Indicative <strong>Economic</strong>s<br />

Production Rate 1.1Mtpy 2.2Mtpy<br />

Average Sales Price US$151.82/t US$133.23/t<br />

Total Production (40 year plan) 44,700kt 89,370kt<br />

Revenue US$6,786.6M US$11,906.8M<br />

Cashflow US$3,065.6M US$5,449.2M<br />

NPV (10%) US$445.5M US$844.1M<br />

NPV (12%) US$331.6M US$642.0M<br />

IRR 32.7% 40.0%<br />

Opex US$41.80/t US$36.36<br />

Initial Capex US$155.3M US$218.4M<br />

Contingency (15%) US$23.3M US$32.8M<br />

Pre-construction US$18.2M US$18.2M<br />

Total Capex US$196.8M US$269.4M<br />

Payback 2.38yrs 1.87yrs<br />

*Note: The above figures include a sustaining capital provision of 2% per annum of direct capital costs commencing in year 4.<br />

Revenue for the 1.1Mtpa production rate is based on two product streams. 70% of the<br />

production will be sold to market area Mina Gerais at a unit price of US$160.04/t and 30% of the<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 18-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

production will be sold to market area Mato Grosso at a unit price of US$130.13/t. The average<br />

sales unit price for 1.1Mtpa case is US$151.82/t.<br />

Revenue for the 2.2Mtpa production rate is based on multiple product streams. The average<br />

sales unit price for the 2.2Mtpa production rate is US$133.23/t. The breakdown of products to<br />

be sold for both production rates are contained in Table 18.2.<br />

Table 18.2: Sales Unit Price/t for 1.1Mtpa and 2.2Mtpa Production Cases<br />

1.1Mtpa<br />

2.2Mtpa<br />

Market Area<br />

% US$/t % US$/t<br />

Minas Gerais 70% 160.04 36% 160.04<br />

Mato Grosso 30% 130.13 28% 130.13<br />

Mato Grosso do Sul 8% 122.2<br />

Goias 16% 112.98<br />

Bahia 10% 93.98<br />

Sao Paulo 2% 90.92<br />

Average Sales Price 100% 151.82 100% 133.23<br />

18.1 Taxes and Royalties<br />

In Brazil, the DNPM, Brazil’s Department of Mines and Energy, monitors exploration, mining,<br />

and mineral processing. This body also administers mineral exploration licenses and mining<br />

concessions. Mineral exploration licenses are issued by DNPM and mining concessions by the<br />

Ministry of Mining and Energy.<br />

Exploration licenses are granted for a maximum period of three years. As prerequisite, the<br />

requestor should provide all requirements and the area of interest does not overlap with an<br />

existing license. There is an annual fee of R$2.02 per hectare during the initial period. It is<br />

possible to request for an extension, situation that increase this annual tax (TAH) to R$3.06<br />

during this extension period. Those values are in force since March 2010, before that it was<br />

respectively R$1.90 and R$2.87. That mineral rights tax should to be paid to the Brazilian<br />

government. Exploration licenses can be extended for a second period no longer than three<br />

years. DNPM has the discretion of the whether requested renewal.<br />

Until the final expiry date of the exploration license, concessions can be applied for following a<br />

final exploration report. This one should be submitted to, and approved by the DNPM. The<br />

report must conclude and demonstrate that an economic mineral resource has been delineated<br />

and measured. According to the protocol of the DNPM, a mining plan and feasibility study must<br />

be presented within a year. A license of installation and a license of operations are then issued<br />

by the applicable environmental agency as a prerequisite to the granting of the mining<br />

concession. A mining concession is granted for a period covering the mine life until the mineral<br />

reserves of the deposit are exhausted. A mining concession does not convey title to a mineral<br />

deposit but provides the holder with the right to extract, process, and sell minerals extracted from<br />

the deposit in accordance with a plan approved by the DNPM and environmental authorities.<br />

A mining concession leads a royalty payment to the federal government. It is the Financial<br />

Compensation for the Exploitation of Mineral Resources ("CFEM"), which is established at 2%<br />

of the net sales of fertilizers. There is also a royalty to the landowner, if the surface rights do not<br />

belong to the mining titleholder – that is the case of the Cerrado <strong>Verde</strong> Project. This royalty<br />

amounts to 50% of CFEM. However, it is common practice to negotiate a separate<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 18-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

compensation agreement, if this amount may not be sufficient for the land owner. Surface rights<br />

in Brazil are distinct from mining rights and must be acquired separately. The land owner has no<br />

title to the subsoil or minerals contained therein. The Brazilian mining code provides for some<br />

form of expropriation of privately held surface rights subject to fair compensation. The holder of<br />

a mineral right is entitled to use the surface to conduct mining operations, including the<br />

construction of facilities required for such operations. The access to the land and reclamation of<br />

disturbed areas must be negotiated with each individual surface right holder. However, the<br />

landowners are obliged by law to provide access to the mineral license holder to conduct<br />

exploration. If an agreement cannot be reached by negotiation there are legal mechanisms in<br />

place to allow courts to lead an arrangement.<br />

18.2 Sensitivity<br />

The Cerrado <strong>Verde</strong> Project is most sensitive to the received Thermo<strong>Potash</strong> product price.<br />

Table 18.2.1: Sensitivity Analysis<br />

Simulation Rate Opex Capex Sales Price IRR range<br />

NPV range<br />

(US$M)<br />

Sim_1 12% -10% +10% -10% +30% -10% +10% 27.8% to 35.3% 281.2 to 380.4<br />

Sim_3 12% -10% +10% -10% +30% -30% +10% 23.1% to 34.5% 181.9 to 370.3<br />

Sim_4 12% -1% +50% -10% +30% -10% +10% 25.9% to 34.0% 239.9 to 359.5<br />

18.3 Mine Life<br />

Given the extensive resource base available; albeit all of which is in the inferred category, a mine<br />

life of 40 years has been assumed for both the 1.1Mtpa and 2.2Mtpa production rates.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Annual Production and Cashflow<br />

for the 1.1Mtpa production case<br />

File Name: Figure_18-1.docx Date: 09/15/2011 Approved: NR Figure: 18-1


SRK Project No.: 3<strong>43</strong>500.020<br />

Cerrado <strong>Verde</strong> <strong>Potash</strong> Project<br />

Minas Gerais, Brazil<br />

Annual Production and Cashflow<br />

for the 2.2Mtpa Production Case<br />

File Name: Figures 18-2 Date: 09/15/2011 Approved: NR Figure: 18-2


<strong>Verde</strong> <strong>Potash</strong> Plc 19-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

19<br />

Adjacent Properties (Item 23)<br />

There are no advanced potash properties in the immediate vicinity of the Cerrado <strong>Verde</strong> Project.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 20-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

20<br />

Other Relevant Data and Information (Item 24)<br />

There is no other relevant data and information that has not been presented within the<br />

appropriate sections of this report.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 21-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

21<br />

Interpretation and Conclusions (Item 25)<br />

The pertinent observations and interpretations which have been developed in producing this<br />

report are detailed in the sections above.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 22-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

22<br />

Recommendations (Items 26)<br />

22.1 Recommended Work Programs<br />

22.1.1 Resources<br />

The current resource estimate confidence can be improved by:<br />

Undertaking additional Bulk Density measurements on diamond core downhole and<br />

across the deposit focusing mainly on the weathered ore since fresh ore has already a<br />

good number of measurements;<br />

Improve the current surface topography using total station, or leaser;<br />

Improve current internal quality control procedures to enhance the methodology for<br />

utilization of sample blanks and standards;<br />

Additional drilling (core drilling) should be completed to improve confidence in grade<br />

continuity within the weathered and un-weathered zones and to enhance the control of<br />

these zone boundaries. The spacing of the drilling should conform to the size of the<br />

block model used for resource estimation, giving both down dip information as well as<br />

vertical constraints on the “ore” horizons; and<br />

Structural interpretations from the core holes will help in detailed mine planning as well<br />

as defining grade boundaries and controls within the deposit.<br />

22.1.2 Metallurgical<br />

It has to be confirmed at what level, if any, will contamination of the Thermo-K product by<br />

residual fuel components, particularly petroleum hydrocarbons, make the product unusable or<br />

limited in application across the agricultural industry. If this is the case, then a gas- or indirect<br />

dead roaster-fired solution is possible, the latter having the advantage of giving flexibility for<br />

low cost alternative fuel utilization. Due to the high temperatures (above 1100 o C) it is unlikely<br />

that any residual fuel will be present.<br />

The rate of water solubilization of nutrients from the calcined product needs to be established<br />

through rinse tests simulating the quench step post calcining and long term exposure to meteoric<br />

rinsing.<br />

22.1.3 Mining<br />

To accurately predict grade and quality of plant feedstock provided by the mine, a more<br />

complete understanding of the resource is required. In particular, the effect of K 2 O grade and<br />

mass yield calculations will effect what part of the mine is mined when and in what quantities.<br />

With a detailed infill drill program, continuation of metallurgical testing and further engineering<br />

studies SRK recommends additional work be dedicated to the effect of mine dilution, possible<br />

effect of deleterious elements, construction of mining costs from first principles, RoM<br />

production targets, waste dump design and haul profiles for contractor estimation. This can be<br />

included as part prefeasibility study and will be required for any reserve generation in the future.<br />

Given the course nature of the resource model, the ability to sensitize or understand potential<br />

challenges to future mining operations is difficult to quantify. With a more refined and detailed<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 22-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

block model containing lithology, grade and product distribution, the confirmation that the mine<br />

will produce the appropriate process plant feedstock can be verified and accurately estimate.<br />

22.1.4 Costs<br />

SRK recommends that the Project be advanced in one phase of work to the prefeasibility level of<br />

evaluation and design. The cost estimate for the recommended work program is shown in Table<br />

22.1.4.1.<br />

Table 22.1.4.1: Recommended Prefeasibility Work Program Cost Estimate (US$000’s)<br />

Description<br />

Cost<br />

Infill Drilling 300<br />

Metallurgical Testwork 800<br />

Engineering Studies 500<br />

Environmental Baseline 150<br />

Other 250<br />

Total 2,000<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 23-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

23<br />

References (Item 27)<br />

Agroconsult (2010). Price and competitiveness survey for introducing Thermo<strong>Potash</strong> on the<br />

Brazilian fertilizer market <strong>Verde</strong> Fertilizantes. Agroconsult Industry Surveys November<br />

2010. 198p.<br />

Coffey Mining, (2010). Cerrado <strong>Verde</strong> <strong>Potash</strong> Project, Brazil, Technical Report to Amazon<br />

Mining Holding Plc, March 2010.<br />

COSTA-FILHO, P. L. D. R., (2007). Estudo preliminar da vegetação da parte do médio curso<br />

do Rio Indaiá (MG) utilizando imagem ASTER. Anais XIII Simpósio Brasileiro de<br />

Sensoriamento Remoto, Florianópolis, Brasil, 21-26 abril 2007, INPE, p. 1631-1638.<br />

ECM (2010). General Project Description for Scoping Study. Report to AMAZON PESQUISA<br />

MINERAL E MINERAÇÃO LTDA. 59p.<br />

http://en.wikipedia.org/wiki/Kriging#Ordinary kriging.<br />

Jose Valarelli et al, (1992). Ardosias "<strong>Verde</strong>te" de CEdro do Abaete na Producao de<br />

Termofosfato Potassico Fundido e sua Eficiencia Agronomica.<br />

KING, L.C. 1956. A geomorfologia do Brasil oriental. Rev. Bras. Geogr.,18(2): 147-265.<br />

LIMA, O. N. B., (2005). Grupo Bambuí: Estratigrafia regional no Alto Rio São Francisco e<br />

geologia dos depósitos fosfáticos da Serra da Saudade - MG. Dissertação de Mestrado,<br />

Instituto de Geociências, Universidade Federal de Minas Gerais, 142 p.<br />

Luis A.M Da Costa et al, (2008). Potential of Potassium-Bearing Rock of the Cedro do Abaete<br />

Region, State of Minas Gerais, Brazil, Sept 2008.<br />

Persio Mandetta, (2009). Planejamento de Sondagem Exploratoria.<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

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<strong>Verde</strong> <strong>Potash</strong> Plc 24-1<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

24<br />

Glossary<br />

24.1 Mineral Resources<br />

The mineral resources and mineral reserves have been classified according to the “CIM<br />

Standards on Mineral Resources and Reserves: Definitions and Guidelines” (November 27,<br />

2010). Accordingly, the Resources have been classified as Measured, Indicated or Inferred, the<br />

Reserves have been classified as Proven, and Probable based on the Measured and Indicated<br />

Resources as defined below.<br />

A Mineral Resource is a concentration or occurrence of natural, solid, inorganic or fossilized<br />

organic material in or on the Earth’s crust in such form and quantity and of such a grade or<br />

quality that it has reasonable prospects for economic extraction. The location, quantity, grade,<br />

geological characteristics and continuity of a Mineral Resource are known, estimated or<br />

interpreted from specific geological evidence and knowledge.<br />

An ‘Inferred Mineral Resource’ is that part of a Mineral Resource for which quantity and grade<br />

or quality can be estimated on the basis of geological evidence and limited sampling and<br />

reasonably assumed, but not verified, geological and grade continuity. The estimate is based on<br />

limited information and sampling gathered through appropriate techniques from locations such<br />

as outcrops, trenches, pits, workings and drillholes.<br />

An ‘Indicated Mineral Resource’ is that part of a Mineral Resource for which quantity, grade or<br />

quality, densities, shape and physical characteristics can be estimated with a level of confidence<br />

sufficient to allow the appropriate application of technical and economic parameters, to support<br />

mine planning and evaluation of the economic viability of the deposit. The estimate is based on<br />

detailed and reliable exploration and testing information gathered through appropriate techniques<br />

from locations such as outcrops, trenches, pits, workings and drillholes that are spaced closely<br />

enough for geological and grade continuity to be reasonably assumed.<br />

A ‘Measured Mineral Resource’ is that part of a Mineral Resource for which quantity, grade or<br />

quality, densities, shape, physical characteristics are so well established that they can be<br />

estimated with confidence sufficient to allow the appropriate application of technical and<br />

economic parameters, to support production planning and evaluation of the economic viability of<br />

the deposit. The estimate is based on detailed and reliable exploration, sampling and testing<br />

information gathered through appropriate techniques from locations such as outcrops, trenches,<br />

pits, workings and drillholes that are spaced closely enough to confirm both geological and grade<br />

continuity.<br />

24.2 Mineral Reserves<br />

A Mineral Reserve is the economically mineable part of a Measured or Indicated Mineral<br />

Resource demonstrated by at least a <strong>Preliminary</strong> Feasibility Study. This Study must include<br />

adequate information on mining, processing, metallurgical, economic and other relevant factors<br />

that demonstrate, at the time of reporting, that economic extraction can be justified. A Mineral<br />

Reserve includes diluting materials and allowances for losses that may occur when the material<br />

is mined.<br />

A ‘Probable Mineral Reserve’ is the economically mineable part of an Indicated, and in some<br />

circumstances a Measured Mineral Resource demonstrated by at least a <strong>Preliminary</strong> Feasibility<br />

Study. This Study must include adequate information on mining, processing, metallurgical,<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 24-2<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

economic, and other relevant factors that demonstrate, at the time of reporting, that economic<br />

extraction can be justified.<br />

A ‘Proven Mineral Reserve’ is the economically mineable part of a Measured Mineral Resource<br />

demonstrated by at least a <strong>Preliminary</strong> Feasibility Study. This Study must include adequate<br />

information on mining, processing, metallurgical, economic, and other relevant factors that<br />

demonstrate, at the time of reporting, that economic extraction is justified.<br />

24.3 Glossary<br />

The following general mining terms may be used in this report.<br />

Table 24.3.1: Glossary<br />

Term<br />

Assay:<br />

Capital Expenditure:<br />

Composite:<br />

Concentrate:<br />

Crushing:<br />

Cutoff Grade<br />

(CoG):<br />

Dilution:<br />

Dip:<br />

Fault:<br />

Footwall:<br />

Gangue:<br />

Grade:<br />

Hangingwall:<br />

Haulage:<br />

Hydrocyclone:<br />

Igneous:<br />

Kriging:<br />

Level:<br />

Lithological:<br />

LoM Plans:<br />

LRP:<br />

Material Properties:<br />

Milling:<br />

Mineral/Mining<br />

Lease:<br />

Mining Assets:<br />

Ongoing Capital:<br />

Ore Reserve:<br />

Pillar:<br />

RoM:<br />

Sedimentary:<br />

Shaft:<br />

Definition<br />

The chemical analysis of mineral samples to determine the metal content.<br />

All other expenditures not classified as operating costs.<br />

Combining more than one sample result to give an average result over a larger distance.<br />

A metal-rich product resulting from a mineral enrichment process such as gravity<br />

concentration or flotation, in which most of the desired mineral has been separated from<br />

the waste material in the ore.<br />

Initial process of reducing ore particle size to render it more amenable for further<br />

processing.<br />

The grade of mineralized rock, which determines as to whether or not it is economic to<br />

recover its gold content by further concentration.<br />

Waste, which is unavoidably mined with ore.<br />

Angle of inclination of a geological feature/rock from the horizontal.<br />

The surface of a fracture along which movement has occurred.<br />

The underlying side of an orebody or stope.<br />

Non-valuable components of the ore.<br />

The measure of concentration of gold within mineralized rock.<br />

The overlying side of an orebody or slope.<br />

A horizontal underground excavation which is used to transport mined ore.<br />

A process whereby material is graded according to size by exploiting centrifugal forces of<br />

particulate materials.<br />

Primary crystalline rock formed by the solidification of magma.<br />

An interpolation method of assigning values from samples to blocks that minimizes the<br />

estimation error.<br />

Horizontal tunnel the primary purpose is the transportation of personnel and materials.<br />

Geological description pertaining to different rock types.<br />

Life-of-Mine plans.<br />

Long Range Plan.<br />

Mine properties.<br />

A general term used to describe the process in which the ore is crushed and ground and<br />

subjected to physical or chemical treatment to extract the valuable metals to a concentrate<br />

or finished product.<br />

A lease area for which mineral rights are held.<br />

The Material Properties and Significant Exploration Properties.<br />

Capital estimates of a routine nature, which is necessary for sustaining operations.<br />

See Mineral Reserve.<br />

Rock left behind to help support the excavations in an underground mine.<br />

Run-of-Mine.<br />

Pertaining to rocks formed by the accumulation of sediments, formed by the erosion of<br />

other rocks.<br />

An opening cut downwards from the surface for transporting personnel, equipment,<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 24-3<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Term<br />

Sill:<br />

Smelting:<br />

Stope:<br />

Stratigraphy:<br />

Strike:<br />

Sulfide:<br />

Tailings:<br />

Thickening:<br />

Total Expenditure:<br />

Unweathered<br />

Variogram<br />

Weathered<br />

Definition<br />

supplies, ore and waste.<br />

A thin, tabular, horizontal to sub-horizontal body of igneous rock formed by the injection<br />

of magma into planar zones of weakness.<br />

A high temperature pyrometallurgical operation conducted in a furnace, in which the<br />

valuable metal is collected to a molten matte or doré phase and separated from the gangue<br />

components that accumulate in a less dense molten slag phase.<br />

Underground void created by mining.<br />

The study of stratified rocks in terms of time and space.<br />

Direction of line formed by the intersection of strata surfaces with the horizontal plane,<br />

always perpendicular to the dip direction.<br />

A sulfur bearing mineral.<br />

Finely ground waste rock from which valuable minerals or metals have been extracted.<br />

The process of concentrating solid particles in suspension.<br />

All expenditures including those of an operating and capital nature.<br />

Fresh rock or protolith that has not been subject to physical or chemical changes as a<br />

result of surface processes.<br />

A statistical representation of the characteristics (usually grade).<br />

Material has been influenced by surface geochemical and physical processes that have<br />

resulted in removal of some potassium and other leachable salts.<br />

24.4 Abbreviations<br />

Metric units are used throughout this report, unless otherwise specified. The following<br />

abbreviations are typical to the mining industry and may be used in this report.<br />

Table 24.4.1: Abbreviations<br />

Abbreviation<br />

Unit or Term<br />

A<br />

ampere<br />

AA<br />

atomic absorption<br />

A/m 2<br />

amperes per square meter<br />

ANFO<br />

ammonium nitrate fuel oil<br />

Ag<br />

silver<br />

Au<br />

gold<br />

AuEq<br />

gold equivalent grade<br />

°C degrees Centigrade<br />

CCD<br />

counter-current decantation<br />

CIL<br />

carbon-in-leach<br />

CoG<br />

cutoff grade<br />

cm<br />

centimeter<br />

cm 2<br />

square centimeter<br />

cm 3<br />

cubic centimeter<br />

cfm<br />

cubic feet per minute<br />

ConfC<br />

confidence code<br />

CRec<br />

core recovery<br />

CSS<br />

closed-side setting<br />

CTW<br />

calculated true width<br />

° degree (degrees)<br />

dia.<br />

diameter<br />

EIS<br />

Environmental Impact Statement<br />

EMP<br />

Environmental Management Plan<br />

FA<br />

fire assay<br />

ft<br />

foot (feet)<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 24-4<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Abbreviation<br />

ft 2<br />

ft 3<br />

g<br />

gal<br />

g/L<br />

g-mol<br />

gpm<br />

g/t<br />

ha<br />

HDPE<br />

hp<br />

HTW<br />

ICP<br />

ID2<br />

ID3<br />

IFC<br />

ILS<br />

K<br />

kA<br />

KCl<br />

kg<br />

km<br />

km 2<br />

koz<br />

kt<br />

kt/d<br />

kt/y<br />

kV<br />

kW<br />

kWh<br />

kWh/t<br />

L<br />

L/sec<br />

L/sec/m<br />

lb<br />

LHD<br />

LLDDP<br />

LOI<br />

LoM<br />

m<br />

m 2<br />

m 3<br />

masl<br />

MARN<br />

MDA<br />

mg/L<br />

Mm<br />

mm 2<br />

mm 3<br />

MME<br />

Moz<br />

Mt<br />

Mtpa<br />

MTW<br />

MW<br />

Unit or Term<br />

square foot (feet)<br />

cubic foot (feet)<br />

gram<br />

gallon<br />

gram per liter<br />

gram-mole<br />

gallons per minute<br />

grams per tonne<br />

hectares<br />

Height Density Polyethylene<br />

horsepower<br />

horizontal true width<br />

induced couple plasma<br />

inverse-distance squared<br />

inverse-distance cubed<br />

International Finance Corporation<br />

Intermediate Leach Solution<br />

Potassium<br />

kiloamperes<br />

potassium chloride, also known as muriate of potash<br />

kilograms<br />

kilometer<br />

square kilometer<br />

thousand troy ounce<br />

thousand tonnes<br />

thousand tonnes per day<br />

thousand tonnes per year<br />

kilovolt<br />

kilowatt<br />

kilowatt-hour<br />

kilowatt-hour per metric tonne<br />

liter<br />

liters per second<br />

liters per second per meter<br />

pound<br />

Long-Haul Dump truck<br />

Linear Low Density Polyethylene Plastic<br />

Loss On Ignition<br />

Life-of-Mine<br />

meter<br />

square meter<br />

cubic meter<br />

meters above sea level<br />

Ministry of the Environment and Natural Resources<br />

Mine Development Associates<br />

milligrams/liter<br />

millimeter<br />

square millimeter<br />

cubic millimeter<br />

Mine & Mill Engineering<br />

million troy ounces<br />

million tonnes<br />

million tonnes per annum<br />

measured true width<br />

million watts<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


<strong>Verde</strong> <strong>Potash</strong> Plc 24-5<br />

Cerrado <strong>Verde</strong> Project<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong><br />

Abbreviation<br />

Unit or Term<br />

m.y.<br />

million years<br />

NGO<br />

non-governmental organization<br />

<strong>NI</strong> <strong>43</strong>-<strong>101</strong> Canadian National Instrument <strong>43</strong>-<strong>101</strong><br />

OSC<br />

Ontario Securities Commission<br />

oz<br />

troy ounce<br />

% percent<br />

PLC<br />

Programmable Logic Controller<br />

PLS<br />

Pregnant Leach Solution<br />

PMF<br />

probable maximum flood<br />

ppb<br />

parts per billion<br />

ppm<br />

parts per million<br />

QA/QC<br />

Quality Assurance/Quality Control<br />

RC<br />

rotary circulation drilling<br />

RoM<br />

Run-of-Mine<br />

RQD<br />

Rock Quality Description<br />

SEC<br />

U.S. Securities & Exchange Commission<br />

sec<br />

second<br />

SG<br />

specific gravity<br />

SOP<br />

sulphate of potash<br />

SPT<br />

standard penetration testing<br />

st<br />

short ton (2,000 pounds)<br />

t<br />

tonne (metric ton) (2,204.6 pounds)<br />

t/h<br />

tonnes per hour<br />

t/d<br />

tonnes per day<br />

t/y<br />

tonnes per year<br />

TSF<br />

tailings storage facility<br />

TSP<br />

total suspended particulates<br />

µm micron or microns<br />

V<br />

volts<br />

VFD<br />

variable frequency drive<br />

W<br />

watt<br />

wt<br />

weight<br />

XRD<br />

x-ray diffraction<br />

y<br />

year<br />

SRK Consulting (U.S.), Inc. September 16, 2011<br />

Cerrado <strong>Verde</strong>_<strong>NI</strong> <strong>43</strong>-<strong>101</strong> PEA_3<strong>43</strong>500.020_007_KG


Appendix A<br />

Certificate of Author Forms


SRK Consulting (U.S.), Inc.<br />

7175 West Jefferson Avenue, Suite 3000<br />

Lakewood, CO<br />

USA 80235<br />

denver@srk.com<br />

www.srk.com<br />

Tel: 303.985.1333<br />

Fax: 303.985.9947<br />

CERTIFICATE OF AUTHOR<br />

I, Neal Rigby, CEng, MIMMM, PhD, do hereby certify that:<br />

1. I am Corporate Mining Engineer of:<br />

SRK Consulting (U.S.), Inc.<br />

7175 W. Jefferson Ave, Suite 3000<br />

Denver, CO, USA, 80235<br />

2. I graduated with a BSc degree in Mineral Exploitation with first class honors in 1974 and a PhD in<br />

Mining Engineering in 1977 both from the University of Wales, UK.<br />

3. I am a member of the Institute of Materials, Mining and Metallurgy.<br />

4. I have worked as a Mining Engineer for a total of 36 years since my graduation from university. My<br />

relevant work experience includes underground and open pit potash, phosphate and trona projects,<br />

open pit mines and quarries, project design and evaluation and cash flow modeling.<br />

5. I have read the definition of “qualified person” set out in National Instrument <strong>43</strong>-<strong>101</strong> (<strong>NI</strong> <strong>43</strong>-<strong>101</strong>) and<br />

certify that by reason of my education, affiliation with a professional association (as defined in <strong>NI</strong> <strong>43</strong>-<br />

<strong>101</strong>) and past relevant work experience, I fulfill the requirements to be a “qualified person” for the<br />

purposes of <strong>NI</strong> <strong>43</strong>-<strong>101</strong>.<br />

6. I am responsible for the Sections 1-4, 10 and 13-24 of the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> titled <strong>NI</strong><br />

<strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong>, Cerrado <strong>Verde</strong> <strong>Potash</strong> Project, Minas Gerais, Brazil,<br />

August 3, 2011, and dated September 16, 2011 (the “<strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong>”) relating to<br />

the Cerrado <strong>Verde</strong> property. I have not visited the Cerrado <strong>Verde</strong> property.<br />

7. I have had prior involvement with the Cerrado <strong>Verde</strong> property that is the subject of the <strong>Preliminary</strong><br />

<strong>Economic</strong> <strong>Assessment</strong>. The nature of my prior involvement was as the qualified responsible for the<br />

preparation of Sections 5 through 12, 15, and 18 of the report titled, “<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong><br />

<strong>Economic</strong> <strong>Assessment</strong>, Cerrado <strong>Verde</strong> <strong>Potash</strong> Project, Minas Gerais, Brazil”, December 13, 2010.<br />

8. I am independent of the issuer applying all of the tests in section 1.5 of National Instrument <strong>43</strong>-<strong>101</strong>.<br />

9. I have read <strong>NI</strong> <strong>43</strong>-<strong>101</strong> and Form <strong>43</strong>-<strong>101</strong>F1, and the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> has been<br />

prepared in compliance with that instrument and form.<br />

Group Offices:<br />

Africa<br />

Asia<br />

Australia<br />

Europe<br />

North America<br />

South America<br />

Canadian Offices:<br />

Saskatoon 306.955.4778<br />

Sudbury 705.682.3270<br />

Toronto 416.601.1445<br />

Vancouver 604.681.4196<br />

Yellowknife 867.445.8670<br />

U.S. Offices:<br />

Anchorage 907.677.3520<br />

Denver 303.985.1333<br />

Elko 775.753.4151<br />

Fort Collins 970.407.8302<br />

Reno 775.828.6800<br />

Tucson 520.544.3688


SRK Consulting (U.S.), Inc. Page 2 of 2<br />

10. I consent to the filing of the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> with any stock exchange and other<br />

regulatory authority and any publication by them for regulatory purposes, including electronic<br />

publication in the public company files on their websites accessible by the public, of the <strong>Preliminary</strong><br />

<strong>Economic</strong> <strong>Assessment</strong>.<br />

11. As of the date of this certificate, to the best of my knowledge, information and belief, the <strong>Preliminary</strong><br />

<strong>Economic</strong> <strong>Assessment</strong> contains all scientific and technical information that is required to be disclosed<br />

to make the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> not misleading.<br />

Dated this 16 th day of September, 2011.<br />

“Signed”<br />

________________________________<br />

Dr. Neal Rigby, CEng, MIMMM, PhD<br />

Certificate_of_Author_NealRigby_Cerrado<strong>Verde</strong>PEA_20<strong>101</strong>213.docx


SRK Cardiff<br />

5th Floor<br />

Churchill House<br />

17 Churchill Way<br />

Cardiff, UK<br />

CF10 2HH<br />

Tel: +44 29 2034 8150<br />

Fax: +44 29 2034 8199<br />

CERTIFICATE OF AUTHOR<br />

I, Rob Bowell, Ph.D, C.Chem MRSC, C. Geol FGS, do hereby certify that:<br />

1. I am Corporate Consultant, (Geochemistry) of:<br />

SRK Consulting (UK) Ltd.<br />

Churchill House<br />

17 Churchill Way<br />

Cardiff, CF102HH<br />

UK<br />

2. I graduated with a degree in Geochemistry/Geology, with Class 1 Honours from the University of<br />

Manchester in 1987. In addition, I have obtained a Doctor of Philosophy from University of<br />

Southampton in 1991.<br />

3. I am a past President of the International Association of Applied Geochemists (2005-2009), VP<br />

(2003-2004). Member of the International Mine Water Association, Geological Society of London,<br />

Society of <strong>Economic</strong> Geology, Royal Society of Chemistry, Chartered Chemist, RSC (1997),<br />

Chartered Geologist, GSL (2001), Chartered Professional European Geologist (2002), Accreditation<br />

auditor, Cyanide code (2005), Visiting Research Associate, Division of materials and Minerals,<br />

Cardiff University 1998 – present, Aberystwyth University 2000-2006.<br />

4. I have worked as a Geochemist for a total of 23 years since my graduation from university. My<br />

relevant project work experience includes geochemistry of basement rocks identical to those in the<br />

project area, I have worked on potash deposits in the United Kingdom, Poland and the Congo, and<br />

other industrial mineral deposits in Brazil, United States, South Africa and Argentina.<br />

5. I have read the definition of “qualified person” set out in National Instrument <strong>43</strong>-<strong>101</strong> (<strong>NI</strong> <strong>43</strong>-<strong>101</strong>) and<br />

certify that by reason of my education, affiliation with a professional association (as defined in <strong>NI</strong> <strong>43</strong>-<br />

<strong>101</strong>) and past relevant work experience, I fulfill the requirements to be a “qualified person” for the<br />

purposes of <strong>NI</strong> <strong>43</strong>-<strong>101</strong>.<br />

6. I am responsible for the preparation of Section 11 of the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> titled “<strong>NI</strong><br />

<strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong>, Cerrado <strong>Verde</strong> Project, Minas Gerais, Brazil, <strong>Verde</strong><br />

<strong>Potash</strong> Plc”, August 03, 2011, and dated September 16, 2011 (the “<strong>Preliminary</strong> <strong>Economic</strong><br />

<strong>Assessment</strong>”) relating to the Cerrado <strong>Verde</strong> Property. I have not visited the Cerrado <strong>Verde</strong> property.<br />

7. I have had prior involvement with the Cerrado <strong>Verde</strong> property that is the subject of the <strong>Preliminary</strong><br />

<strong>Economic</strong> <strong>Assessment</strong>. The nature of my prior involvement was as qualified person for Sections 14<br />

Group Offices:<br />

Africa<br />

Asia<br />

Australia<br />

Europe<br />

North America<br />

South America<br />

Canadian Offices:<br />

Saskatoon 306.955.4778<br />

Sudbury 705.682.3270<br />

Toronto 416.601.1445<br />

Vancouver 604.681.4196<br />

Yellowknife 867.445.8670<br />

U.S. Offices:<br />

Anchorage 907.677.3520<br />

Denver 303.985.1333<br />

Elko 775.753.4151<br />

Fort Collins 970.407.8302<br />

Reno 775.828.6800<br />

Tucson 520.544.3688


SRK Consulting (U.S.), Inc. Page 2 of 2<br />

and 19 of the report titled, “<strong>NI</strong> <strong>43</strong>-<strong>101</strong> <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong>, Cerrado <strong>Verde</strong> <strong>Potash</strong><br />

Project, Minas Gerais, Brazil”, dated December 13, 2010.<br />

8. I am independent of the issuer applying all of the tests in section 1.5 of National Instrument <strong>43</strong>-<strong>101</strong>.<br />

9. I have read <strong>NI</strong> <strong>43</strong>-<strong>101</strong> and Form <strong>43</strong>-<strong>101</strong>F1, and the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> has been<br />

prepared in compliance with that instrument and form.<br />

10. I consent to the filing of the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> with any stock exchange and other<br />

regulatory authority and any publication by them for regulatory purposes, including electronic<br />

publication in the public company files on their websites accessible by the public, of the <strong>Preliminary</strong><br />

<strong>Economic</strong> <strong>Assessment</strong>.<br />

11. As of the date of this certificate, to the best of my knowledge, information and belief, the <strong>Preliminary</strong><br />

<strong>Economic</strong> <strong>Assessment</strong> contains all scientific and technical information that is required to be disclosed<br />

to make the <strong>Preliminary</strong> <strong>Economic</strong> <strong>Assessment</strong> not misleading.<br />

Dated this 16 th day of September, 2011.<br />

“Signed”<br />

________________________________<br />

Rob Bowell, PhD, C.Chem MRSC, C. Geol FGS<br />

Certificate_of_Author_RobBowell_Cerrado<strong>Verde</strong>PEA_20<strong>101</strong>213.docx

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