S2N84SE«ilM3 63.4855 BALMER TWP · using a 4" diameter aluminum core barrel or casing and a steel...

102
S2N84SE«ilM3 6 3 . 4 8 5 5 BALMER TWP FREEGOLD FreeGold Recovery Inc. Vancouver, B.C. A Review and Verification by Wright Engineers Limited of the Sampling Technique of Campbell Red Lake Mines Limited Tailings Deposit w XV WRIGHT ENGINEERS LIMITED VANCOUVER CANADA PROJECT NO. 1^71-100 SEPT. 1986

Transcript of S2N84SE«ilM3 63.4855 BALMER TWP · using a 4" diameter aluminum core barrel or casing and a steel...

  • S2N84SE«ilM3 6 3 . 4 8 5 5 BALMER TWP

    FREEGOLD

    FreeGold Recovery Inc.

    Vancouver, B.C.

    A Review and Verification by Wright Engineers Limited of the

    Sampling Technique of Campbell Red Lake Mines Limited

    Tailings Deposit

    w XV WRIGHT ENGINEERS LIMITED VANCOUVER CANADA

    PROJECT NO. 1^71-100 SEPT. 1986

  • o/n*6-/-c-9#'

    w S3'4&3

    Phor* «604)684-B3?1 • Cable-WRK3HTENG" • Tel«i 04-S436T WRK^T ENGINEERS LIMITED •/»!

    1444 Alberni Street, Vancouver, British Columbia, Canada, V6G 2Z4

    Project No.: 1*71

    September 10, 1986

    FreeGold Recovery Inc. 1333 West 8th Ave. Vancouver, B.C. V6H 3W4

    Attention: Mr. Harry Barr, President

    Dear Harry:

    We are pleased to submit the accompanying report entit led:

    "A Review and Verification by Wright Engineers Limited of the Sample Handling Technique of Campbell Red Lake Mine Tailings".

    We wish you well in your endeavours to recover precious metals from this and other mine tailings you have sampled.

    We look forward to assisting you in any way as your testwork and project progresses.

    Yours very truly,

    WRIGHT ENGINEERS LIMITED,

    fi -AAJ-

    S.3. Andrews, P. Eng. Manager Mineral Eng. Division

    SJA/mph Encl.

    (

  • 1-1

    Project No. 1471

    August 11, 1986

    A Review and Verification by Wright Engineers Limited

    of the Sample Handling Technique of Campbell Red Lake Mine Tailings

    INTRODUCTION;

    Campbell Red Lake Mines Ltd. have been in production since 1949. During

    this period the mine has produced continuously at rates up to the present 1100 tpd.

    The resulting tailing product production is estimated at approximately 10 million tons.

    After miscellaneous losses and mine backfill are decuted the tailing deposit is

    estimated at about 8 million tons.

    Large portions of this deposit are from earlier years of production when gold

    recovery technology was not as efficient as it is today and the price of gold did not

    warrant extra costs for higher recovery. The result is a tailing deposit that may be

    retreated at a profit to the mine and the contractor.

    FreeGold Recovery Inc. have entered into a contract with Campbell Red

    Lake Mines (C.R.L.M.) to sample and measure the tailing deposit and, if economical,

    to recover a portion of the gold values in the deposit. Wright Engineers Limited were

    requested in this first stage to act as a third party to verify the sampling methods,

    techniques in handling the samples through to assay determinations and method of

    calculating the tonnage in the deposit.

  • 1-2

    SAMPLING;

    The tailings deposit under consideration was divided into two areas; the first

    being the decant or slime deposit area and the second is the 'normal' 'beach' type

    tailings disposal area. The relative areas are approximately 38 acres and 80 acres

    respectively. These areas have been divided for sampling purposes into 250 foot

    sections with sample hole spacing every 250 feet making a 250 x 250 foot sampling

    grid.

    FreeGold Recovery Inc. personnel (with assistance from C.R.L.M.) are drill

    sampling at the above grid locations. The drill being used is a Wink-Vibrahead Unit

    using a 4" diameter aluminum core barrel or casing and a steel cutter head with core

    retainer. The two piece drill units are skid mounted and can be easily moved with a

    mini 4 x 4 rubber tired, Suzuki, A.T.V. (all terrain vehicle). Spare drill barrels, core

    trays, sampling equipment, etc. are moved in a small two wheel trailer with the same

    A.T.V. See also the accompanying photographs. The vibrating power unit easily drives

    the core barrel through the tailing material. The rate of penetration of course slows

    with increasing depth but is still an acceptable rate. Some difficulties have been

    encountered when the drill hits an obstruction such as a previous submerged dyke, road

    or logs (or near vertical tree).

    When the hole is drilled completely the core barrels and core are pulled with

    the winching device (see pictures). The core flows, or is vibrated or pushed out of the

    core barrels into a plastic tray (one half of a 6" plastic pipe). The 4" x 5' core sections

    are then resampled every 4" with a 5/8" dia. tube coring tool. This yields

    approximately \5 cores out of the original 5' core length. This is a good representative

    sample of each 5' section.

    In the drilling process the core is compacted by the vibration resulting in a

    core length less than the core barrel driven length. This is accurately measured and

    compensation is made in the assay/depth and tonnage calculation.

  • 1-3

    The final secondary sample (series of 5/8" cores) was taken to the C.R.L.M.

    sample preparation room. Here the sample is dried, rolled with a bottle and screened

    to break up agglomerates. It is then thoroughly mixed on a 'rolling cloth' and 'cut' to

    obtain the sample for actual assay. The samples are then taken to the new, very

    modern, assay laboratory. The very competent C.R.L. staff of the assay department

    then assay the samples by a combination of fire assay and atomic absorption

    spectophotometer.

    As a check on the above procedure during the writer's visit separate samples

    were cut out of the 5' core sections for independent assay. One set of samples was

    taken by the writer for assay at Chemex Laboratory in Vancouver. The other check

    sample was sent to Lakefield Research for assay. This resulted in a three way assay

    check, the results of which are as follows:

    VEL/Chemex Sample No.

    5751

    5752

    5753

    5754

    5755

    Line

    4450 E

    4450 E

    4450 E

    4450 E

    4450 E

    Hole No.

    4

    5

    5

    5

    5

    Depth

    0 - 5

    0 - 5

    5 - 10

    10- 15

    15-20

    CRM

    0.060

    0.058

    0.074

    0.055

    0.043

    Chemex

    0.064

    0.054

    0.072

    0.050

    0.042

    Lakefield

    0.058

    0.053

    0.074

    -

    _

    ,&66 .6*3 .0 7^

    \

  • 1-*

    TONNAGE CALCULATION;

    Tonnage calculations are based on a planimeter survey of the map, tailing

    storage area, plus the dri l l hole depth along each of the 250 foot section lines (see

    attached example). The unit weight of tailings in place was originally calculated (as a

    first best estimate) using the value used for tailings backfill namely 19.0 f t^ / ton. This

    value has been checked by taking several core samples from the various fineness

    grades of tailings (from near discharge point to the slime pond area). The results of

    these 'in place' density tests are as follows:

    Line

    0 + 310

    *950E

    5950E

    Hole No.

    5

    5

    5

    Fines (slime area tailings)

    Medium fines tailing

    Coarse (sampled near

    discharge plant)

    ft3 per ton

    25.2*

    23.61

    22.60

    Using the above 'in place' tailings densities the tonnage of tailings in the two

    areas, Area 1 (slime tailing) and Area 2 (medium and coarse tailing) is as follows:

    Area 1 (slime tailing) @ 25.2* f t 3 /s t

    Area 2 (medium and coarse tailing) (3 23.10 f tVs t average

    Short Tons

    89*,333

    2,719,593

    Total

    Total rounded

    3,613,926

    3,600,000

  • 1-5

    CONCLUSION:

    This tailings deposit, as is commonly the case, is a relatively homogenous

    layering of finely ground tailing material. The sample grid pattern adopted will

    produce a good representative primary series of samples of each five foot depth of the

    deposit. The (»" diameter core provides a good weight and size for secondary sampling.

    The secondary sampling at Un intervals also produces a good representative secondary

    sample. The sample handling and assaying is carried out by technicians who are well

    qualified and using equipment of the latest design for accurate assays. The cross

    checking at Lakefield and Chemex indicate that there are no inherent errors in the

    sampling system.

    The tonnage, grade and contained value calculations have been checked and

    found to be based on representative samples and good engineering practice.

    S.3. Andrews, P. Eng.

    Manager Mineral Eng. Div.

  • FREEGOLD - C.R.L.M. TAILINGS RECOVERY TEST

    JULY 1986

    Sampling of #2 test area of our abandoned tailings ponds was completed the first week of July. A total of 69 holes having an average depth of 17.9 ft. were drilled on test area #2 which used to be the primary pond. Using 19 ft.'/ton for tailings density a total of 3.3 million tons of 0.053 oz./ton was outlined in this pond.

    SAMPLING PROCEDURE

    Sampling procedure remained the same as in test area #1. The sonic drill vibrated the core tube to the bottom of the tailings. This length was called the total drill length. As the core barrels were removed the sample was placed in split 6" PVC pipes and sampled every 4" using a 5/8" circular tube. Because the core liquified and compacted in the core barrel the sample was never as long as the actual length of core drilled. To adjust for this ratio of actual length drilled to length of sample was calculated (ratio C/D on sheets).

    EXAMPLE

    Area #2, line 4200 Er hole #2

    Total length drilled = 16.5 ft.

    Length of Core extracted =14.0 ft.

    Ratio = C/D = 14.0 =0.85 16.5 .

    The first core box contained 4 ft.

    4 ft. sample represents 4/0.85 = 4/̂ 71 ft.

    This corrected length was used to calculate the weighted average.

    TONNAGE CALCULATION

    A volume was calculated using a planimeter area multiplied by the average depth. On test area #1 volume • was calculted in the same way and was checked using cross-sec.tional areas and also using a pit volume program. Results were all within 10% (See tonnage calculation for test area #1) ••

  • 2 -

    (

    Total Tonnage, Grade, Contents

    Total Tons - Area #1 1.2 Million Tons Area #2 3.3 Million Tons *Total 4.5 Million Tons

    *Using 19.0 cu. ft./ton which is likely a maximum value.

    x_

    = 0.051 oz./ton

    Average grade

  • 52Ne4SE«>e43 63.4855 BALMER TWP O S O

    An Investigation of

    THE RECOVERY OF GOLD

    from Campbell Red Lake tailing samples

    submitted by

    FREEGOLD RECOVERY INCORPORATED

    Progress Report No. 1

    N

    Project No. L.R. 3181

    NOTE: This report refers to the samples as received.

    The practice of this Company in issuing reports of this nature is to require the recipient not to publish the report or any part thereof without the written consent of Lakefield Research.

    LAKEFIELD RESEARCH A DIVISION OF FALCONBRIDGE LIMITED

    September 10, 1986

  • I N T R O D U C T I O N

    In a letter dated July 21, 1986, Mr. H. Barr of FreeGold Recovery

    Incorporated authorized a test program on samples of Campbell Red Lake tailings

    and a gravity concentrate recovered from them to investigate the recovery of

    gold by flotation and cyanidation.

    LAKEFIELD RESEARCH

    R.S. Salter

    General Manager

    K.W. Sarbutt

    Chief Project Engineer

    Experimental Work by: G. Mcllmoyle

  • S U M M A R Y

    1. Head Samples

    Twenty-eight

    5700E No. 7

    5200E No. 4

    4700E No. 6

    4450E No. 6

    tailing samples were received:

    0-4' 4'-9' 9'-14' ,14'-19'*

    0-5 1/2' 5 1/2-10 10 1/2-15 15 1/2-20

    .0-5' 5-10' 10-15'

    0-7' 7-12' 12-17' 17-22'

    5450E No.

    5200E No. 1/2' 1/2 ' 1/2 »

    4450E No.

    « •

    4450E No.

    4

    6

    5

    4*

    0-5'* 5-10' 10-15' 15-20'

    0-6' 6-11* 11-16' 16-21'

    0-5'* 5-10'* 10-15' 15-20'

    Five of these samples(*) were selected for check analysis and these

    samples were dried and pulverized. The remainder of the samples were combined

    and pulped and samples removed for testwork and head analysis.

    A gravity concentrate was also received. The sample was.pulped and

    charges removed for testwork.

  • - 3 -

    Summary - Continued

    1. Head Samples - Cont'd

    Head assays and a size fraction analysis were conducted:

    Sample

    4450E No. 4 5450E No. 4 0-5 4450E No. 5 0-5 4450E No. 5 5-10 5700E No. 7 14-19

    Tailing Comp. Gravity Cone.

    Assay, g/t Au

    2.26 2.00 1.83 2.58 1.63

    1.86 3.72

    Assay %

    As J Fe 1 S

    0.18 0.29

    8.49 11.3

    0.46 . 1.07

    Size Fraction Analysis

    Tailing Comp.

    Size Fraction

    +65 Mesh -65 +100 Mesh -100 +150 Mesh -150 +200 Mesh -200 +270 Mesh -2 70 +400 Mesh -400 Mesh

    Head (Calculated)

    Weight %

    0.5 3.6 9.3 11.8 10 9.7 55.1

    100.0

    Assay g/t Au

    6.09 3.74 2.62 2.55 3.63 1.61 1.43

    2.02

    1 " •

    % Distribution Au

    1.51 6.68 12.06 14.92 18.00 7.74

    39.07

    100.00

    Gravity Concentrate

    +65 Mesh -65 +100 Mesh -100 +150 Mesh -150 +200 Mesh -200 +270 Mesh -2 70 +400 Mesh -400 Mesh

    Head (Calculated)

    4.5 13.8 24.0 19.4 13.7 10.3 14.3

    100.0

    12.4 4.67 4.13 3.92 • 3.66 2.94 3.69

    4.29

    13.02 15.04 23.13 17.74 11.70 7.07 12.31

    100.0

    1

  • Summary- Continued

    2. Testwork - Tailings Composite

    2.1. Direct Cyanidation

    Direct cyanidation tests were conducted on the tailing composite to

    investigate the effect of fineness of grind on the recovery of gold. Standard

    conditions employed in these tests were:

    1 g/L NaCN pH 10.5 33% solids 48 hours leach time

    The conditions and results of the tests are summarized in Table No. 1.

    Table No. 1

    Direct Cyanidation

    Test

    No.

    2 3 7

    8

    Grind kWh/t

    (approx . )

    0 7.25

    14.50 21.75 1

    % -400

    .'Mesh

    53.3 81.8 92.6 96.4

    Reag., Cons

    NaCN

    0.42 2.17 -1.50 1.40

    »., k g / t

    CaO

    1.34 0.98 0.71 0.83

    % Au Ex t r ac t i on *

    24 h

    38 .1 45.0

    -

    48 h

    41 .1 48 .9 51.5 53.8

    Residue

    g / t Au

    1.14 0.97 0.91 0.89

    Head

    | g / t Au

    1.94 1.90 1.88 1.93

    Recovery increased as the fineness of grind was increased. Approximately

    50 percent of the gold could be recovered after grinding to 80 percent passing

    400 mesh. Increasing the fineness to 96 percent passing 400 mesh only increased

    the recovery to 54 percent.

  • Summary - Continued

    2.2. Flotation and Cyanidation of Flotation Products

    Two tests were conducted to examine preconcentration of the tailings

    by flotation with and without a grind. A concentrate was recovered with A-350 and

    R-208 as collectors. The results of the flotation are summarized in Table No. 2.

    Table No. 2

    F l o t a t i o n Resul t s

    Test

    No.

    1 9

    Grind kHh/t

    (approx.)

    0 8.5

    % -400 Mesh

    53 83

    F l o t a t Weight

    %

    7.1 10.1

    ion Concentrate Au I %

    g / t Rec 'y

    7.36 8.61

    27.4 J 48.9

    T a i l ,

    g / t Au

    1.48 1.01

    Head

    g / t Au

    1.90 1.78

    Gold recovery increased after grinding but was still low at 49 %*

    The concentrate from each test was cyanided. Standard conditions employed

    in the cyanidation were: 1 g/L NaCN pH 10.5 33 % solids 48 hours

    The conditions and results of the cyanidation are summarized in Table No. 3,

    Table No. 3

    Cyanid

    Test No.

    1

    -9 1

    a t ion of F l o t a t i o n Concentrate

    Regrind kWh/t Cone.

    56 36

    Reag. Cons. , NaCN

    6.89 4 .71

    kg / t Cone. CaO

    2.94 2.47

    % Ex t rac t ion Au

    58.5 49.8

    Residue g / t Au

    3.05 4.32

    % Au Rec 'y C a l l

    16.0 24.4

    Even after fine regrinding only 50-60 percent of the gold in the flotation

    concentrate was recovered by cyanidation giving low overall recoveries.

  • Summary - Continued

    3. Testwork - Gravity Concentrate

    Similar testwork to that conducted on the tailing composite was also conducted

    on the gravity concentrate. The results of the direct cyanidation tests are

    summarized in Table No. 4.

    Table No. 4

    Cyanidation of Gravity Concentrate

    Test

    No.

    Grind kWh/t

    (approx.) -400 Mesh

    Reag. Cons, kg/t

    NaCN CaO

    Residue Assay Au g/t

    % Au

    Rec'y

    Head Calc. Au g/t

    4 5 10

    0 7.25

    21.75

    14 49 92

    1.40 1.30 1.45

    _.

    0.74 0.72 0.77

    2.24 1.77 1.52

    47.9 60.8 57.7

    4.30 4.51 .3.59

    After grinding recovery increased form 48 to approximately 60 percent

    from the gravity concentrate.

    One test was conducted in which the gravity concentrate was further upgraded

    by flotation and the flotation concentrate was reground and treated by cyanidation.

    The flotation concentrate amounted to 11 percent of the weight, assayed

    15.8 g/t Au and the gold recovery was 47.5 percent.

    In cyanidation 59.5 percent of the gold in the concentrate was recovered

    for an overall recovery of 28.2 percent.

  • P - 7 -

    Summary - Continued

    4. Overall Results and Recommendations

    Direct cyanidation of the tailings with no grinding gave 41 percent recovery..

    The recovery could be increased to 50-55 percent with fine regrinding.

    Flotation of ground tailings concentrated 50 percent of the Au in 10

    percent of the weight. After further regrinding and cyanidation only 50 percent

    of the Au in the concentrate was recovered by cyanidation for an overall recovery

    of only 25 percent.

    Recoveries were slightly higher from the gravity concentrate but it is not

    known how much weight or recovery the gravity concentrate represents.

    Size fraction analysis of the head sample showed that 65 percent of the Au

    was in the minus 200 mesh fraction. Therefore flotation may have more potential for

    pre-concentration than gravity. Further testwork should be directed towards improving

    the flotation response. Evaluation of grind, collector type and activators is required.

    If the flotation response can be substantially improved then further evaluation of

    cyanidation of the flotation concentrate would be warranted.

  • HMTirrUB.

    - 8 -

    DETAILS OF TESTS

    Test No. 1

    Purpose:

    Feed:

    Grind:

    Conditions:

    To investigate the recovery of gold by flotation and cyanidation.

    1 kg of tailings composite.

    As received

    Stage

    Rougher 1 Rougher 2 Rougher 3 Rougher 4

    Reagents Added, grams per tonne

    CuSO- A350 j R208

    250

    20 10

    10

    20 10

    [ DF250

    Time, minutes

    Cond.

    8 I 2 2

    8 5 4 2

    Froth

    5 3. 4 3

    PH

    -

    8.2

    Stage Flotation Cell Speed: r.p.m.

    Rougher 500 g D-l 1100

    J

  • - 9

    Test No. 1 - Continued

    Purpose:

    Procedure:

    Cyanidation of flotation concentrate.

    The sample was pulped with water in a one litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    Feed' 120 g flotation rougher concentrate

    Solution Volume: 240 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with Ca(0H)2

    Grind: 20 minutes in lab pebble mill.

    Reagent Balance:

    Time

    Hours

    Stage 1 0-5 5-24

    Stage 2 24-29 ' 29-48

    Total Stage 1 Total Stage 2

    Total

    Actus NaCN

    0.242 0.088

    0.242 0.189

    0.33

    0.431

    0.761

    Added, Grams

    Ca(0H)2

    0.10 0.050

    0.10

    0.15

    0.10

    0.25

    Equiv NaCN

    0.240 0.084

    0.240 0.180

    0.324

    0.420

    0.744

    alent CaO

    0.075 0.038

    0.075

    0.113

    0.075

    0.188

    Residual

    Grams NaCN I CaO

    0.156 0.084

    0.06 0.22

    0.084

    0.22

    0.304

    0.005

    0

    0

    "

    Consumed

    Gra NaCN

    0.084 0.156

    0.180 0.02

    0.24

    0.20

    0.44

    ms CaO

    0.075 0.038

    0.07 0.005

    0.113

    0.075

    0.188

    PH

    10.7- 9.6 10.6-10.4

    10.8-10.5 10.4

    -

    -

    gent Consumption (kg/t of cyanide feed) NaCN: 6.89 CaO: 2.94

  • - 10 -

    Test No. 1 - Continued

    Metallurgical Results

    Product

    Flotation Concentrate Flotation Tailing

    Head (Calculated)

    " • - —

    Amount

    7.05 92.95

    100.00

    Assays,mg/L,g/t

    Au

    7.36 1.48

    1.90

    % Distribution

    Au

    27.4 72.6

    100.0

    Cyanidation

    24 h Pregnant+Wash 48 h Pregnant+Wash Cyanide Residue

    Flot. Cone. (Calc.) ••

    680 mL 2000 mL 63.9 g

    63.9 g

    0.36 0.015 3.05

    7.36

    14.3 1.7

    11.4

    27.4

    52.1 6.4

    41.5

    100.0

    Screen Analyses

    Rougher Tailing

    Mesh Size (Tyler)

    + 65 100 150 200 270 400

    - 400

    Total

    % Retained Individual Cumulative

    0.6 3.6 10.6 12.0 10.6 10.4 52.2

    100.0

    0.6 4.2 14.8 26.8 37.4 47.8 100.0

    -

    . % Passing Cumulative

    99.4 95.8 85.2 73.2 62.6 52.2

    -

  • 11

    Test No. 2

    Purpose:

    Procedure:

    To investigate the recovery of gold by cyanidation of the unground tailing composite.

    The sample was pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the'test continued.

    Feed: 500 g tailings composite

    Solution Volume: 1000 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with Ca(0H)2

    Reagent Balance:

    Time

    Hours

    Stage 0-5

    5-24

    Stage 24-29 29-48

    Total Stage Total Stage

    Total

    1

    2

    1

    2

    Actua NaCN .•

    1.05 0.105

    1.05 0.105

    1.155

    1.155

    Added, Grams

    |Ca(0H)2

    0.500

    0.500

    0.50

    0 .5o

    Equiv NaCN

    1.0Q 0.10

    1.00 0.10

    1.10

    1.10

    ra lent CaO

    0.375

    0.375

    0.375

    0.375

    Residual

    Gr* NaCN

    0.900 0.95

    0.90 0.963

    0.95

    0.963

    ims CaO

    0.06 0.02

    0.025 0.023

    0.02

    0.023

    Consumed

    Gr* NaCN

    0.100 0.05

    0.100 0.037

    0.105

    0.104

    0.209

    ims CaO

    0.315 0.04

    0.35 0.002

    0.319

    0.352

    0.671

    PH

    11.2-10 10 .9- 9

    11 .3 -11 . 11.3

    -

    -

    9 8

    2

    Reagent Consumption (kg/t of cyanide feed) NaCN: 0.42 CaO: 1.34

  • - 12 -

    Test No. 2 - Continued

    Metallurgical Results

    Product

    1. 24 h Pregnant+Wash 2. 48 h Pregnant+Wash 3. Cyanide Residue

    Head (Calculated)

    Amount

    1260 mL -1925 mL 495.0 g

    495.0 g

    Assays,mg/L,g/t

    Au

    0.29 0.015 1.14

    1.94

    % Distribution

    Au

    38.10 3.03 58.87

    100.0 j

    Calculated Grades and Recoveries

    Products 1 and 2 3185 1.935 41.13

    Screen Analyses

    Cyanide Residue

    Mesh Size (Tyler)

    + 65 100 150 200 2 70 400

    - 400

    Total

    % Retained Individual - J Cumulative

    0.6 3.7 10.3 11.4 10.5 10.2 53.3

    100.0

    0.6 4.3 14.6 26.0 36.5 46.7 100.0

    -

    % Passing Cumulative

    99.4 95.7 85.4 74.0 63.5 53.3

    -

  • - 13

    Test No. 3

    Purpose:

    Procedure:

    Feed:

    To repeat test No. 2 but with a grind.

    The sample was pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    500 g tailing composite

    Solution Volume: 1000 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with Ca(0H)2

    Grind: 20 minutes inlab pebble mill.

    Reagent Balance:

    Time

    Hours

    Stage 0-5 5-24

    Stage 24-29 29-48

    Total Stage Total Stage

    Total

    1

    Added, Grams

    Actual NaCN |ca(0H)2

    1.05 0.211

    2 1.050 0.211

    1

    2

    1.261

    1.261

    0.300 0.050

    0.300

    0.350

    0.300

    Equî NaCN

    1.00 0.200

    1.00 0.200

    1.200

    1.200

    1

    /a] ent CaO

    0.225 0.038

    0.225

    0.263

    0.22!

    Residual

    Grams NaCN J CaO

    0.800 1 0.01 0.60 J -

    0.80 0.714

    0.60

    0.714

    0.03 0.03

    0.0

    0.03

    1

    Consumed

    Grams NaCN ICaO

    0.200 0.40

    0.200 0.286

    0.600

    0.486

    0.215 0.038

    0.195

    0.253

    0.195

    1.086 0.488

    10 10

    11

    PH

    .6-10.

    .6-10.

    0-11. 10.9

    -

    3 4

    0

    Reagent Consumption (kg/t of cyanide feed) NaCN: 2.17 CaO: 0.98

  • - 14 -

    Test No. 3 - Continued

    Metallurgical Results

    Product

    1. 24 h Pregnant+Wash 2. 48 h Pregnant+Wash 3. Cyanide Residue

    Head (Calculated)

    Amount

    1590 mL 1700 mL 485.3 g

    485.3 s.

    Assays,mg/L,g/t

    Au

    0.26 0.021 0.97

    1.90

    % Distribution

    Au

    45.0 3.9 51.1

    100.0

    Calculated Grades and Recoveries

    Products 1 and 2 3290 0.14 1 48.9

    Screen Analyses

    Cyanide Residue

    Mesh Size j % Reta (Tyler) j Individual

    + 150 0.2 200 1.4 270 4.9 400 11.7

    - 400 81.8

    Total j 100.0

    :.ned Cumulative

    0.2 1.6 6.5 18.2 100.0

    -

    % Passing Cumulative

    99.8 98.4 93.5 81.8

    -

  • 15

    Test No. 4

    Purpose:

    Procedure:

    Feed;

    To investigate the recovery of gold by cyanidation of the unground gravity concentrate.

    The sample was pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    500 g gravity concentrate as received.

    Solution Volume: 1000 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with Ca(0H)2

    Reagent Balance:

    Time

    Hours

    Stage 1 0-5 '; 5-24

    Stage 2 24-29 29-48

    Total Stage 1 Total State 2

    Total

    Added, Grams

    Actua NaCN."

    1.05 0.053

    1.050 0.211

    1.103

    1.261

    1 Ca(0H)z

    0.300

    0.300

    0.300

    0.300

    Equiv NaCN

    1.00 0.050

    1.00 0.20

    1.050

    1.20

    alent CaO

    0.225

    0.225

    0.225

    0.225

    Residual

    Gr* NaCN

    0.950 1.0

    0.80 0.552

    1.0

    0.552

    tms CaO

    0.07 0.02

    0.035 0.035

    0.02

    0.035

    Consumed

    Grams NaCN CaO

    0.050 0.00

    0.20 0.448

    0.050

    0.648

    0.698

    0.155 0.05

    0.165

    0.205

    0.165

    0.370

    PH

    -

    n.o-ii:o 11.0-10.8

    11.0-11.2 11.1

    -

    Reagent Consumption (kg/t of cyanide feed) NaCN: 1.396 CaO: 0.74

  • - 16 -

    Test No. 4 - Continued

    Metallurgical Results

    Product

    1. 24 h Pregnant+Wash 2. 48 h Pregnant+Wash 3. Cyanide Residue

    Head (Calculated)

    Amount

    1500 mL 1725 mL 496.9 g

    496.9

    Assays,mg/L,g/t

    Au

    0.64 0.04 2.24

    4.30

    % Distribution

    Au

    44.7 3.2 52.1

    100.0

    Calculated Grades and Recoveries

    Products 1 and 2 3225 0.80 47.9

    Screen Analyses

    Cyanide Residue

    Mesh Size (Tyler)

    + 65 100 150 200 270 400

    - 400

    Total

    % Reta Individual

    4.2 14.2 24.7 19.5 13.9 9.9 13.6

    100.0

    .ned Cumulative

    4.2 18.4 43.1 62.6 76.5 86.4 100.0

    -

    % Passing Cumulative

    95.8 81.6 56.9 37.4 23.5 13.6 -

    -

  • - 17

    Test No. 5

    Purpose:

    Procedure:

    To repeat test No. 4 but with a grind.

    The sample was -pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    Feed: 500 g gravity concentrate

    Solution Volume: 1000 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5•with Ca(0H)2

    Grind: 20 minutes in 2 kg lab pebble mill.

    Reagent Balance:

    Time

    Hours

    Stage 0-5 5-24

    Stage 24-29 29-48

    Total Stage Total Stage

    Total

    1

    2

    1

    2

    Ac tu'a NaCN

    1.05 0.53

    1.050 0.158

    1.58

    1.208

    Added, Grams

    1 Ca(0H)2

    0.25 0.100

    0.250

    0.35

    0.25

    Equi\ NaCN

    1.00 0.50

    1.00 0.15

    1.50

    1.15

    alent CaO

    0.188 0.075

    0.188

    0.263

    0.188

    Residual

    Gr* NaCN

    0.500 1.00

    0.85 1.00

    1.00

    1.00

    tms CaO

    0.02

    0.04 0.04

    0.02

    0.04

    Consumed

    Gra NaCN

    0.500 0.00

    0.15 0.00

    0.500

    0.150

    0.65

    ms CaO

    0.188 0.055

    0.148

    0.243

    0.148

    0.391

    PH

    10.8-10.3 10.9-10.6

    11.0-11.1 10.9

    -

    Reagent Consumption ( k g / t of cyanide feed) NaCN: 1.30 CaO: 0.782

  • - 18 -

    Test No. 5 - Continued

    Metallurgical Results

    Product

    1. 24 h Pregnant+Wash 2. 48 h Pregnant+Wash 3. Cyanide Residue

    Head (Calculated)

    Amount

    1490 mL 1525 mL 497.8 g

    497.8

    Assays,mg/L,g/t

    Au

    0.88 0.035 1.77

    4.51

    % Distribution

    Au

    58.40 2.36 39.24

    100.0

    Calculated Grades and Recoveries

    Products 1 and 2 3015 0.45 60.76

    Screen Analyses

    Cyanide Residue

    Mesh Size (Tyler)

    + 100 150 200 270 400

    - 400

    Total

    % Retained Individual - Cumulative

    0.2 2.3 9.2 19.1 19.9 49.3

    100.0

    0.2 2.5 11.7 30.8 50.7 100.0

    -

    % Passing Cumulative

    99.8 97.5 88.3 69.2 49.3

    -

  • - 19 -

    Test No. 6

    Purpose: To investigate the recovery of gold by flotation and cyanidation from the gravity concentrate.

    Procedure: The 1 kg sample was pulped and floated in a 1000 g. cell.. All flotation was done in the one cell.

    Feed: Gravity concentrate, as received

    Conditions:

    Stage

    Rougher 1 Rougher 2 Rougher 3 Rougher 4 Rougher 5

    Reagents Added, grams per tonne

    A350 I R208

    20 30

    10 50

    20 20

    10 50

    CuSOi,

    300

    DF250

    '8 4 4 4 8

    Time, minutes

    Cond.

    2 2 5 1 2

    Froth

    4 4 4 4 4

    PH

    7.0 7.0 7.1

    Stage Rougher 1-5 Flotation Cell 1000 g D-2 Speed: r.p.m. 1400 % Solids 33

  • • - 20 -

    Test No. 6 - Continued

    Purpose:

    Procedure: The sample was pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    Feed: 200 g rougher concentrate flotation

    Solution Volume: 400 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: ' 10.5 with Ca(0H)2

    Grind: 20 minutes in lab pebble mill.

    Reagent Balance:

    Time

    Hours

    0-17 17-24 24-29 29-48

    Added, Grams

    Actu'i NaCN

    0.43 0.380 0.42 0.042

    ]1 Ca(0H)2

    0.10 0.08 0.14

    Total 1 1.262 J 0.32

    Equiv* NaCN

    0.40-0.36 0.00 0.04

    0.800

    l e n t CaO

    0.075 0.060 0.105

    0.24

    Residual

    Gra NaCN

    0.04 0.40 0.36 0.292

    0.292

    ns CaO

    -

    0.00

    Consumed

    Gra NaCN

    0.36 0.00 0.04 0.108

    0.508

    ns CaO

    0.075

    0.24

    PH

    10 .5 - 9.0 10 .5-10.4 10.4-10.4

    9.9

    -

    Reagent Consumption (kg/t of cyanide feed) NaCN: 4.87 CaO: 2.30

  • - 21 -

    Test No. 6 - Continued

    Metallurgical Results

    Product

    Flotation Cone. Flotation Tail.

    Head (Calc.)

    Cyanidation

    24 h Pregnant+Wash 48 h Pregnant+Wash Cyanide Residue

    Head (Calc.)

    Amount

    11.1 88.9

    100.0

    1100 mL 1620 mL 104.3 g

    104.3 g |

    Assays, %

    Au

    15.8 2.18

    3.69

    0.73 0.11 6.40

    15.8

    % Distribution Au

    O'all

    47.5 52.5

    100.0 .

    23.1 5.1 19.3

    47.5

    Ind.

    48.7 10.8 40.5

    100.0

  • • - 22 -

    To repeat test No. 2 but with a finer grind.

    The sample was pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    500 g tailing composite

    Solution Volume: 1000 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with CaOOH)2

    Grind: 40 minutes in lab pebble mill

    Reagent Balance:

    Time

    Hours

    0-17 17-23 23-40 40-48

    Added, Grams

    Ac tu'a NaCN

    1.05 0.421 0.105 0.158

    Total j 1.724

    1 Ca(0H)2

    0.325 0.150

    0.475

    Equivalent NaCN CaO

    1.00-0.400 0.100 0.150

    1.650

    0.244 0.113

    0.357

    Residual

    Gr* NaCN

    0.600 0.900 0.850 0.900

    0.900

    uns CaO

    "

    -

    Consumed

    Gra NaCN

    0.400 0.100 0.150 0.100

    0.750

    is CaO

    0.244 0.113

    0.357

    PH

    10 .5-10 .0 10 .6-10 .6 10 .6-10 .4 10 .4-10 .3

    10.4

    Reagent Consumption (kg/t of cyanide feed) NaCN: 1.500 CaO: 0.714

    Test No. 7

    Purpose:

    Procedure:

    Feed:

  • - 23 -

    Test No. 7 - Continued

    Metallurgical Results

    Product

    L. Pregnant+Wash 2. Residue

    Head (Calculated)

    Amount

    1400 tnL 507.4 g

    507.4

    Assays,mg/L,g/t

    Au

    0.35 0.91

    1.88

    % Distribution

    Au

    51.5 48.5

    100.0

    Screen Analyses

    Cyanide Residue

    Mesh Size (Tyler)

    % Ret Individual

    + 400 1 7.4 - 400 92.6

    Total 100.0

    lined Cumulative

    7.4 100.0

    -

    % Passing Cumulative

    92.6

    -

  • 24 -

    Test No. 8

    Purpose:

    Procedure:

    Feed:

    To repeat test No. 2 but with a still finer grind.

    The sample was pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in one 48 hour stage. The pulp was filtered and the residue washed three times with water.

    500 g tailing composite

    Solution Volume: 1000 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with Ca(0H)2

    Grind: 60 minutes in lab pebble mill

    Reagent Balance:

    Time

    Hours

    0-17 17-23 23-40 40-48

    Added, Grams

    j Actua NaCN

    1.05 0.474 0.105 0.105

    Total 1 1.734

    Ca(0H)2

    0.325 0.150 0.050

    0.525

    Equiv NaCN

    1.00 0.450 0.100 0.100

    1.650

    ilent CaO

    0.244 0.133 0.038

    0.415

    Residual

    Grams NaCN j CaO

    0.550 0.900 0.900 0.950

    0.950 -

    Consumed

    Grams NaCN CaO

    0.450 0.100 0.100 0.050

    0.700

    0.244 0.133 0.038

    0.415

    PH

    10.5-10.0 10.6-10.4 10.6-10.4 10.4-10.4

    10.4

    Reagent Consumption (kg/t of cyanide feed) NaCN: 1.400 CaO: 0.830

  • - 25 -

    Test No. 8 - Continued

    Meta l lu rg ica l Resu l t s

    Product

    1. Pregnant+Wash 2. Residue

    Head (Calculated)

    Amount

    1460 mL 507.9 g

    507.9g 1

    Assays,mg/L,g/t

    Au

    0.36 0.89

    1.93

    % Distribution

    Au

    53.8 46.2

    100.0

    Screen Analyses

    Cyanide Residue

    Mesh Size (Tyler)

    + 400 - 400

    % Ret Individual

    3.6 96.4

    Total 100.0

    tined Cumulative

    3.6 100.0

    -

    % Passing Cumulative

    96.4

    -

  • 26

    Test No. 9

    Purpose:

    Procedure:

    Feed :

    Grind:

    Conditions:

    To determine if grinding will enhance recovery of gold by flotation from the gravity tailings sample.

    The tailings sample was ground in ball mill and floated in a series of roughers until tailings was visually barren.

    1 kg of gravity .tailings as received.

    15 minutes/kg in 2 kg lab ball mill.

    Stage

    Grind Rougher 1 Rougher 2 Rougher 3 Rougher 4

    Reagents Added, grams per tonne

    A350

    _ 100 50 50 50

    R208

    -50 30 -

    DF250

    _ 4 -1

    CuSC\

    _ -50 50

    20 1 50

    Metso

    H

    1500 --

    '

    Time, minutes

    Grind

    15 ----.

    1 Cond. Froth

    mm

    3 5 5 3

    «. 5 3 3 3

    pH

    «, 9.8 9.5 8.8 a.3

    Note:

    Stage Flot. Cell Speed:rpm % Solids

    Very heavy weight of silica in 1st rougher concentrate - stopped float and added metso to depress silica with some success.

    Rougher 1-4 1000 g D-l 1600 33

  • m.

    27

    Test No. 9 - Continued

    Purpose:

    Procedure:

    To investigate the solubility of gold.

    The sample was pulped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    Feed: 100 g rougher flotation concentrate

    Solution Volume: 300 mL Pulp Density 25 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with Ca(0H)2

    Grind: 1 kg sample ground 15 minutes in ball mill- float—rougher concentrate reground 20 minutes in pebble mill.

    Reagent Balance:

    Time

    Hours

    Added, Grams

    Actual NaCN Ca(0H)2

    Equivalent NaCN CaO

    Residual

    Grams NaCN CaO

    Consumed

    Grams NaCN CaO

    PH

    0-7 7-24 24-41 41-48

    0.316 0.221 0.142 0.091

    0.135 0.080 0.080 0.040

    0.300 0.210 0.135 0.086

    0.101 0.060 0.060 0.030

    0.09 0.165 0.214 0.251

    0.020

    0.21 0.135 0.086 0.049

    0.101 0.060 0.040 0.050

    10.5- 9.9 10.9-10.0 10.7-10.3 10.7-10.3

    Total 0.770 0.335 0.731 0.251 0.251 0.48 0.251 10.4

    Metallurgical Results

    Product

    flot. Concentrate Hot. Tailing . Head (Calculated)

    Cyanidation Pregnant+Wash Residue Head (Calc.) i

    Aimount

    10.1 89.9

    100.0

    1040 mL 101.9 g 101.9 g j

    Assays,mg/L,g/t

    Au

    8.61 1.01

    1.78

    0.42 4.32 8.61

    % Distribution Au

    O'all

    48.9 51.1

    100.0

    24.4 24.5 48.9

    Ind.

    -

    -

    49.8 50.2 100.0

  • - 28 -

    Test No. 10

    Purpose: To investigate the effect of a still finer grind on the recovery of gold from the gravity concentrate by cyanidation.

    Procedure: The sample was puLped with water in a two litre bottle. NaCN and lime were added and the cyanidation was carried out on rolls in two 24 hour stages with the solution being changed after each stage. Between each stage the pulp was filtered and the residue washed three times with water. The residue was then repulped with fresh cyanide solution and the test continued.

    Feed: 500 g gravity concentrate

    Solution Volume: 1000 mL Pulp Density 33 % solids

    Solution Composition: 1.0 g/L NaCN

    pH Range: 10.5 with Ca(OH)2

    Grind: Ground 60 minutes in lab pebble mill.

    Reagent Balance:

    Time

    Hours

    0-17 17-23 23-40 40-48

    Total

    Added, Grams

    Actua NaCN

    1.05 0.447 0.105 0.105

    1.652

    1 Ca(0H)2

    0.325 0.100 0.100

    0.525

    Equi> NaCN

    1.00 0.425 0.100 0.100

    1.625

    a l e n t CaO

    0.244 0.075 0.075

    0.394

    Residual

    Gra NaCN

    0.575 0.900 0.900 0.900

    0.900

    IIS

    CaO

    0.01

    -

    Consumed

    Gra NaCN

    0.425 0.100 0.100 0.100

    0.725

    ns CaO

    0.244 0.075 0.065

    0.384

    pH

    10.5-10 .0 10.4-10.2 10.5-10.4 10 .4-10 .4

    10.4

    Reagent Consumption (kg/t of cyanide feed) NaCN: 1.450 CaO: 0.768

  • 29

    Test No. 10 - Continued

    Metallurgical Results

    Product

    1. Pregnant+Wash 2. Residue

    Head (Calculated)

    Amount

    1380 mL 512.4 g

    512.4 g

    Assays,mg/L,g/t

    Au

    0.77 1.52

    3.59

    % Distribution

    Au

    57.7 42.3

    100.0

    Screen Analyses

    Cyanide Residue

    Mesh Size (Tyler)

    + 400 - 400

    % Ret Individual

    8.4 91.6

    Total 100.0

    ained Cumulative

    8.4 100.0

    -

    % Passing Cumulative

    91.6

    -

    LAKEFIELD RESEARCH A Division of Falconbridge Limited Lakefield, Ontario September 10, 1986 / slk

  • 52NMSEe«43 63.4855 BALMER TWP 0 3 0

    FreeGold Recovery Inc.

    Vancouver, B.C.

    Gold Recovery Plant

    Order of Magnitude Capital and Operating Cost

    Campbell Red Lake Mines Limited's

    Tailings Deposit

    w w WRIGHT ENGINEERS LIMITED VANCOUVER CANADA

    PROJECT NO. 1*71-100 OCT. 1986

  • \X-R10iT ENGINEERS LIMITED VflT Ptwnt 68«-M71 • C»W« "WRIGHTENG- • Tclei 0 4 - 5 0 6 7

    1444 Alberni Street, Vancouver, British Columbia, Canada, V6G 2Z4

    Project No.: 1471

    November 3, 1986

    FreeGold Recovery Inc. 1333 West 8th Ave. Vancouver, B.C. V6H 3W4

    Attention: Mr. Harry Barr, President

    RE: Gold Recovery from Campbell Red Lake Plant Tailing Pond

    Dear Mr. Barr:

    We are pleased to submit the accompanying report outlining a capital and operating cost estimate for a base case 2500 tons per day gold recovery plant. Other plant capacities have been considered by factoring the costs of the base case. Those costs are based on new equipment, are in order of magnitude and do not reflect any optimization.

    We hope this information will help enable you to formulate your next step on this project.

    Yours very truly,

    WRIGHT ENGINEERS LIMITED,

    1&J& Keith Remfert Senior Consultant

    KR/mph Encl.

  • 1.

    / 1

    CAPITAL AND OPERATING COST

    GOLD RECOVERY PLANT

    INTRODUCTION

    Wright Engineers Limited (WEL) were requested to formulate an order of

    magnitude capital and operating cost estimate for the recovery of gold from tailings

    using a standard sodium cyanide circuit. This study is a continuation of work relative

    to reclaiming the tailings deposited at Campbell Red Lake Mines Ltd.

    Information and reports upon which this study is based include the following:

    Wright Engineers Ltd. - Review and Verification of Sampling Technique,

    September 1986

    Lakefield Research - Progress Report //I, September 10, 1986

    FreeGoId Recovery Inc. - Report - Drilling and Sampling, Tonnage Estimate,

    ( August 20, 1986

    FreeGoId Recovery Inc. and Lakefield Research - Testwork Results,

    August 18,1986

    FreeGoId Recovery Inc. - FreeGoId Campbell Tailings Recovery Test,

    June, 1986

    A preliminary flowsheet was prepared to establish equipment sizes and

    numbers. Operating cost data was provided by Campbell Red Lake Ltd. August 19,

    1986. Consumption of reagents established during testwork at Lakefield Research was

    used.

    FLOWSHEET DEVELOPMENT

    Preliminary testwork indicates that direct cyanidation of the tailing material

    may be the preferred flowsheet. Further grinding of this material to increase the gold

    recovery is not economically favourable.

    \ * y

  • 2.

    The basic flowsheet is given in the Study Basis section of this report.

    Grinding circuits were not costed once it was obvious that the net revenue per ton

    would be less than direct cyanidation before grinding.

    STUDY BASIS

    Ton: 2500 t/d Hours (net): 23 hr/d Nominal hourly rate: 110 t/hr Density solids (calc. purpose): 2.8 t/nr»3 Estimated tons available: 3.6 x 10^

    Annual tonnage = 875000

    Basic flowsheet:

    Pond —• Traini Screen

    ' ' Leach

    i i

    • Sludge * '

    f V r \jSl4K UUIlip

    Filter

    • •

    Cla my

    —• < Dake Tailing Pond

    • Dea er« ixion 1 Filter|~» Refine

    Leach:

    pH: Time: Pulp density:

    10.5 48 hr 60% solids

    Base Cost Factors:

    Power NaCN CaO Labour

    Supervisor Ave. trade

    $.09 kWh $1.70 kg $.18 kg

    $25.50 loaded/hr $24.20 loaded/hr

    CAPITAL COST ESTIMATE

    The capital cost for the 2500 tpd plant outlined by the attached flowsheet is

    10.0 x 106 dollars Canadian. A breakdown of the equipment is found overleaf.

    file:///jSl4K

  • 3.

    MECHANICAL EQUIPMENT LIST

    BASE CASE 2500 TPD FEED

    Quantity Type

    1 6' x 16' D.D. Screen

    1 125'0 Thickener

    6 11m 0 x 11m Cyanide Leach Tank

    c/w Agitator

    1 Leach Air Blower

    2 6" x 6" Horizontal Centrifugal Pump (1 standby)

    1 Primary Filter Feed Tank

    5 12' 0 x 18' Primary Drum Filter c/w Repulper

    1 Secondary Filter Feed Tank c/w Agitator

    2 6" x 6" Horizontal Centrifugal Pump (1 standby)

    5 12' 0 x 16' Secondary Drum Filter c/w Repulper

    2 6" x 6" Horizontal Centrifugal Pump (1 standby)

    2 42" 0 x 6 ' Primary Filtrate Receiver

    1 4" x 3" Filtrate Pump

    2 42" 0 Secondary Filtrate Receiver

    4" x 3" Filtrate Pump

    42" 0x6* Moisture Trap

    Vacuum Pump (8000 cfm)

    Sump Pump (2" vertical)

    Sump Pump (2" vertical)

    Sampler

    10' 0 x 10' Pregnant Solution Tank

    4" x 4" Horizontal Centrifugal Pump

    600 ft2 Pressure Clarifier

    3'-0" 0 x 3'-6" Precoat Tank c/w Agitator

    2" Horizontal Centrifugal Pump

    1)4" Horizontal Centrifugal Pump

    Installed Order of Magnitude

    Capital Cost (Cdn. $)

    36,800

    282,000

    870,000

    65,000

    15,300

    4,700

    750,000

    7,100

    15,300

    750,000

    15,300

    4,700

    5,400

    4,700

    5,400

    4,700

    170,000

    3,200

    3,200

    45,000

    10,900

    6,100

    420,000

    2,400

    2,900

    2,500

  • 0.

    Quantity

    1

    1

    1

    1

    2

    1

    2

    1

    1

    1

    1

    1

    1

    TOTAL

    Building,

    use 2.5 rr

    Type

    81 0 x 8' Clarified Solution Tank

    0' 0 x 10" Deaeration Tower

    Zinc Feeder

    In-line Pump

    2" x 2" x 20 frame Filter Press

    (Clean bi-weekly)

    12' 0 x 12' Barren Solution Tank

    Horizontal Centrifugal Pump

    Furnace - Gas Fired 1000// c/w Blower

    Baghouse c/w Fan

    Acid Leach Tank c/w Agitator

    Exhaust Fan

    In-line Filter

    Horizontal Centrifugal Pump

    6" x 6" Thickener Pump

    piping, etc. less tailing disposal and

    multiplier

    powe r supply,

    say

    Installed Order of Magnitude

    Capital Cost (Cdn. $)

    5,300

    6,100

    12,000

    5,000

    25,000

    12,900

    12,200

    75,000

    20,000

    10,000

    11,000

    0,500

    6,100

    9,500

    3,725,200

    x2.5

    9,313,000

    $10,000,000

  • 5.

    OPERATING COST ESTIMATE

    The basis for operating cost and revenue were established by test datum

    originating from Lakefield Resource testwork, report issued August 18, 1986. The four

    tests referred to in this estimate are described below. Direct cyanidation of

    recovered tailing pond material applies in all tests.

    Test 2 No grinding of the plant feed.

    Test 3 Grind plant feed to 81.8% -400 mesh (7.25 kWh/t)

    Test 7 Grind plant feed to 92.6% -400 mesh (14.50 kWh/t)

    Test 8 Grind plant feed to 96.4% -400 mesh (21.75 kWh/t)

    Item

    Power (Grinding) Power (Agitators) Power (Est. Balance) Sub-Total

    Base Reagents NaCN CaO

    Sub-Total

    Grinding media Sub-Total

    Maintenance Supplies; Take 5% of installed mech., divided by annual tonnage

    Labour Supervisor Ave Trades

    Sub-Total

    Pond to Plant Cost (FGRI's suggested cost)

    Unit Cost $

    .09 kWh

    .09 kWh

    .09 kWh

    1.70 kg • 18 kg

    $25.50/hr $24.20/hr

    Test 2 Units

    0 3.1 3.7 6.8

    .42 1.34

    1 4 5

    Cost

    0 .28 .33 .61

    .71

    .24

    .95

    0

    .21

    .23

    .88 1.11

    1.50

    Tes Units

    7.25 3.1 3.7

    14.05

    2.17 .98

    1 5 6

    t 3 Cost

    .65

    .28

    .33 1.26

    3.69 .18

    3.87

    .35

    .35

    .21 +

    .23 1.10 1.33

    1.50

    Tes Units

    14.5 3.1 3.7

    21.3

    1.50 .71

    1 5 6

    t 7 Cost

    1.31 .28 .33

    1.92

    2.55 .13

    2.68

    .75

    .75

    .21 +

    .23 1.10 1.33

    1.50

    Test Units

    21.7 3.1 3.7

    28.5

    1.40 .83

    1 5 6

    8 Cost

    1.95 .28 .33

    2.56

    2.38 .15

    2.53

    1.10 1.10

    .21 +

    .23 1.10 1.33

    1.50

    TOTAL $/TON FEED 4.38 8.52+ 8.39+ 9.23H

  • REVENUE

    6.

    Test 2 Test 3 Test 7 Test 8

    Recovery %

    Head g/t

    Recovered g/t

    Value @ $18.Cnd/g ($400. U.S./oz.)

    Less (Oper. Cost)

    Net Sub-Total

    41.1

    1.94

    .797

    14.35

    4.38

    9.97

    48.9

    1.90

    .929

    16.72

    8.52

    8.20

    51.9

    1.88

    .976

    17.57

    8.39

    9.18

    53.8

    1.93

    1.038

    18.68

    9.23

    9.45

    Less Cap. & Cost of Cap. (@ 12.5% interest)

    Net Revenue (pre Taxes)

    Project Life =

    * Estimated Capital (2500 t/d)

    Interest Cost (12.5%)

    Total Capital

    $ 3.72* #* «* #«

    $ 6.25 /t i.e. $22.5 x 106 over life of the project

    = 4.1 years

    $10,000,000

    3.6 x 10JT 875000 T/yr

    3,380,000

    $13,380,000 divided by 3.6 x 10^ tons = $3.72

    •Grinding circuit concentrator is not considered further due to lower net revenue than established in Test 2 before cost of capital was considered.

  • CAPITAL COST FOR ALTERNATE FEED RATE

    The base case capital cost has been factored using the following formula:

    t0.6 C2 = Cj x

    where:

    ( «

    c2 Ci

    T2

    Tl

    =

    =

    =

    =

    therefore:

    Ci

    Tl

    For T2

    For T2 For T2

    z

    =

    =

    =

    cost of alternate plant

    cost of base case plant

    tonnage of alternate plant

    tonnage of base case plant

    $10,000,000

    2500 TPD

    1000 C 2 = $5.8 x 106

    5000 C 2 = $15.2 x 106

    10000 C2 = $23.0 x 106

    Project Life

    10.3 yr

    2.1 yr

    l y r

  • OPERATING COST FOR ALTERNATE FEED RATE

    8.

    TPD =

    Power $/T

    Reagents $/T

    Supplies $/T

    Labour $/T

    Supervisor

    Trades

    Feed Costs $/T

    Sub-Total Costs

    Revenue $/T

    Sub. Net $/T

    Cost of Cap. $/T

    Net $/T

    2500

    .61

    .95

    .21

    -

    .23

    (4) .88

    1.50

    4.38

    14.35

    9.97

    3.72

    6.25

    1000

    .61

    .95

    .08

    -

    .5%

    (4) 2.20

    1.50

    5.92

    14.35

    8.43

    2.88

    5.55

    5000

    .61

    .95

    .43

    -

    .12

    (4) .44

    1.50

    4.05

    14.35

    10.30

    4.85

    5.45

    10000

    .61

    .95

    .86

    -

    .06

    (6) .33

    1.50

    4.31

    14.35

    10.04

    6.82

    3.22

    CONCLUSIONS

    From the information available the following points apply:

    1. Grinding of tailings for increased recovery is not economical.

    2. The more favourable tonnage rates to be considered are 1000 tpd and

    2500 tpd. The decision here is related to length of term and original capital

    invested. The operating cost differential is principally the labour fraction

    and the cost of capital.

  • FreeGold Recovery Inc.

    Vancouver, B.C.

    Gold Recovery Plant

    Order of Magnitude Capital and Operating Cost

    Campbell Red Lake Mines Limited's

    Tailings Deposit

    w w WRIGHT ENGINEERS LIMITED VANCOUVER CANADA

    PROJECT NO. 1471-100 NOV. 1986

  • CAPITAL AND OPERATING COST

    GOLD RECOVERY PLANT

    INTRODUCTION

    Wright Engineers Limited (WEL) were requested to formulate an order of

    magnitude capital and operating cost estimate for the recovery of gold from tailings

    using a standard sodium cyanide circuit. This study is a continuation of work relative

    to reclaiming the tailings deposited at Campbell Red Lake Mines Ltd. and an

    addendum to report issued in November 1986.

    Information and reports upon which this study is based include the following:

    Wright Engineers Ltd. - Review and Verification of Sampling Technique,

    September 1986

    Lakefield Research - Progress Report //I, September 10, 1986

    FreeGold Recovery Inc. - Report - Drilling and Sampling, Tonnage Estimate,

    August 20, 1986

    FreeGold Recovery Inc. and Lakefield Research - Testwork Results,

    August 18, 1986

    FreeGold Recovery Inc. - FreeGold Campbell Tailings Recovery Test,

    June, 1986

    Preliminary test results supplied by FreeGold Recovery Inc. done at Hazen

    Research, October 1986.

    A preliminary flowsheet was prepared to establish equipment sizes and

    numbers. Operating cost data was provided by Campbell Red Lake Ltd. August 19,

    1986. Consumption of reagents established during testwork at Hazen Research was

    used. The principal difference between this report and that of November 3, 1986 is

    the reduction of leach retention time from 48 hours to 8 hours, and lower head grade.

    FLOWSHEET DEVELOPMENT

    Direct cyanidation processing of the tailing material was used as the base

    case.

    w

  • 2.

    The basic flowsheet is given in the Study Basis section of this report.

    STUDY BASIS

    Ton: 2500 t/d Hours (net): 23 hr/d Nominal hourly rate: 110 t/hr Density solids (calc. purpose): 2.8 t/m3 Estimated tons available: 3.6 x 10^

    Basic flowsheet:

    Annual tonnage = 875000

    Pondj—* Trasn Screen

    i •

    Leach l

    • Sludge 4

    O size aump

    Filter

    Clarify

    -Cake

    —1

    -—• Tailing Pond

    Deaeration Filter —* Refine

    Leach:

    pH: Time:

    10.5 8hrs

    Pulp density: 60% solids

    Base Cost Factors:

    Power NaCN CaO Labour

    Supervisor Ave. trade

    $.09 kWh $1.70 kg $.18 kg

    $25.50 loaded/hr $24.20 loaded/hr

    CAPITAL COST ESTIMATE

    The preliminary capital cost estimate for the 2500 tpd plant outlined by the

    attached flowsheet is 7.0 x 10*> dollars Canadian. A breakdown of the equipment is

    found overleaf.

  • 3.

    MECHANICAL EQUIPMENT LIST

    BASE CASE 2500 TPD FEED

    Quantity Type

    1 6'x 16' D.D. Screen

    1 125' 0 Thickener

    6 6.5m 0 x 6m Cyanide Leach Tank

    c/w Agitator

    1 Leach Air Blower

    2 6" x 6" Horizontal Centrifugal Pump (1 standby)

    1 Primary Filter Feed Tank

    3 12' 0 x 18' Primary Drum Filter c/w Repulper

    1 Secondary Filter Feed Tank c/w Agitator

    2 6" x 6" Horizontal Centrifugal Pump (1 standby)

    3 12' 0 x IZ' Secondary Drum Filter c/w Repulper

    2 6" x 6" Horizontal Centrifugal Pump (1 standby)

    2 42" 0 x 6 ' Primary Filtrate Receiver

    1 4" x 3" Filtrate Pump

    2 42" 0 Secondary Filtrate Receiver

    4" x 3" Filtrate Pump

    42" 0 x 6" Moisture Trap

    Vacuum Pump (8000 cfm)

    Sump Pump (2" vertical)

    Sump Pump (2" vertical)

    Sampler

    10' 0 x 10' Pregnant Solution Tank

    4" x 4" Horizontal Centrifugal Pump

    600 ft2 Pressure Clarifier

    3'-0" 0 x 3'-6" Precoat Tank c/w Agitator

    2" Horizontal Centrifugal Pump

    lYz" Horizontal Centrifugal Pump

    Installed Order of Magnitude

    Capital Cost (Cdn. $)

    36,800

    282,000

    372,000

    50,000

    15,300

    4,700

    450,000

    7,100

    15,300

    450,000

    15,300

    4,700

    5,400

    4,700

    5,400

    4,700

    170,000

    3,200

    3,200

    45,000

    10,900

    6,100

    420,000

    2,400

    2,900

    2,500

  • li.

    Quantity

    1

    1

    1

    1

    2

    1

    2

    1

    1

    1

    1

    1

    1

    TOTAL

    Building,

    use 2̂ 5 rr

    Type

    8' 0 x 8' Clarified Solution Tank

    4' 0 x 10' Deaeration Tower

    Zinc Feeder

    In-line Pump

    2" x 2" x 20 frame Filter Press

    (Clean bi-weekly)

    12' 0 x 12* Barren Solution Tank

    Horizontal Centrifugal Pump

    Furnace - Gas Fired 1000// c/w Blower

    Baghouse c/w Fan

    Acid Leach Tank c/w Agitator

    Exhaust Fan

    In-line Filter

    Horizontal Centrifugal Pump

    6" x 6" Thickener Pump

    piping, etc. less tailing disposal and

    multiplier

    power supply,

    say

    Installed Order of Magnitude

    Capital Cost (Cdn. $)

    5,300

    6,100

    12,000

    5,000

    25,000

    12,900

    12,200

    75,000

    24,000

    14,000

    11,000

    4,500

    6,100

    9,500

    2,612,200

    x2.5

    6,530,500

    $ 7,000,000

  • 5.

    SAMPLE DATA

    The basis for operating cost and revenue were established by test datum

    originating from Hazen testwork, preliminary report issued November, 1986.

    Bulk samples taken from the Campbell Red Lake mine tailing pond were

    combined and mixed for cyanide leach test. The samples came from three locations of

    //2 test area shown on the attached location map. FreeGold Recovery Inc. supervised

    the sampling and sample preparation and describe the samples as follows:

    above.

    Sample

    1

    2

    3

    Location

    Line 4450 Hole 8

    Line 6200 Hole 7

    Halfway between Hole 4 on Line 5200 and Hole 4 on Line 4950

    Depth

    18'

    12'

    12'

    Amount

    2 barrel volume

    2 barrel volume

    2 barrel volume

    The composite sample head assay reported was .040 oz/t (1.24 g/t).

    The following assays were provided for the individual drill holes addressed

    Location Depth Assay oz/t July 1986

    Line 4450 - Hole 8

    Line 6200 - Hole 7

    Line 5200 - Hole 4

    Line 4950 - Hole 4

    Cyanide leach tests were performed on the combined sample as described in

    the report from Hazen Research Inc. overleaf.

    26'

    30'

    22.5'

    14.5'

    .053

    .043

    .058

    .084

  • Objective: Cyanide le

    Saxtple: HRI 33738,

    Time, hr pH, Initial

    adjusted Temperature % Solids Ket Pulp Kt, s KaCN, g/l

    Reagent Additions, grams CaO HaCN

    Cumulative Consumptions: lb/ton of test feed

    CaO HaCH

    wt, g or

    vol, ml

    2 hour aliquot 50 4 hour aliquot SO R hour aliquot 60

    2< hour aliquot 60

    ech.

    , 6 rash ore feed.

    0 8.6

    11.0 amb

    30 1667

    0.27 ?.33

    Analyses, (1)

    Au

    0.1? O.IR 0.18^ 0,21

    2 10.9

    amb 30

    1666 1.93

    1.1 0.31,

    Di

    4 10,9

    amb 31

    1611 1.B7

    l . l 0.62

    ssolutton oz Au/t

    0.012 0.012 0.013 0.016

    e 10.0

    a tib 31

    \m 1.84

    #

    1.1 0.47

    »

    • 24 10.9

    amb 32

    1673 1,07

    1.1 3.60

    Test Ko. Project: Date Paget

    Dissolution, t Au

    30.0 30.0 32.5 37.6

    2 008-112 Oct '86

    1 of 1

    24 hour F/W (3) 1*00 0.15 24 hour solids 499.0 0,026

    0.014 35.0

    Calculated feed Assayed feed

    0.040

    (1) Solids analyses for gold and/or silver arc reported as troy ounces per Short ton. and other metals as percentages. Liquor analyses are reported as mg/l.

    (2) The percentage dissolutions ere based upon the calculated ffred(s). (3) Combined final pregnant and xash liquors.

    Remarks:

  • 6.

    OPERATING COST ESTIMATE

    Item

    Power (Agitators)

    Power (Est. Balance)

    Sub-total

    Base Reagents

    NaCN

    CaO

    Sub-total

    Maintenance Supplies; take 3% of

    installed mech., divided by

    tonnage

    annual

    Unit Cost $

    .09/kWh

    .09/kWh

    1.70/kg

    .18/kg

    Units

    kWh/t

    1.2

    3.7

    U.9

    kg/t

    .55*

    .50

    Cost

    .11

    .33

    Ak

    .93

    .09

    1.02

    .09

    **Labour (Total averaged/hour) $77.52/hr .70

    Pond to Plant Cost

    (FGRI's suggested cost) 1.50

    TOTAL $/TON FEED 3.75

    * The NaCN consumption data is suspect. Hazen Research indicated

    problems with the titration procedure during analysis.

    ** Reduced to a minimum crew of 13 total.

  • • 7.

    REVENUE

    Recovery %

    Head g/t

    Recovered g/t

    Value @ $18.Cnd/g ($400. U.S./oz.)

    Less (Oper. Cost)

    Net Sub-Total

    Less Cap. & Cost of Cap. {(§ 12.5% interest)

    Net Revenue (pre Taxes)

    Project Life =

    * Estimated Capital = (2500 t/d)

    Interest Cost (12.5%) +

    Total Capital

    COMMENTS

    The following points apply:

    a) Head assay results from the bulk composite range from .036 to .045 oz/t

    compared to drill core assays from the same pits of .043 to .084 oz/t.

    b) Hazen Research Laboratory recovery results for direct cyanidation for

    24 hours is 37.5% compared to Lakefield's 38.1%.

    c) Operating costs do not include costs for administration, maintenance shops,

    mobile equipment, laboratory work or the contracting out of these services.

    32.5

    1.24

    .403

    7.25

    3.75

    3.50

    $ 2.50*

    $ 1.00 /t i.e. $3.6 x 106 over life of the project

    3.6 x 10JT ., , 875000Wr = *#1 y e a r $

    $7,000,000

    2,006,000

    $9,006,000 divided by 3.6 x 10^ tons = $2.50

  • l u 4

    fc

    I •

    63.4855 BALMER TWP ,_, .. _

    0-40

    PHASE I REPORT

    ON

    FREEGOLD RECOVERY INC/CAMPBELL RED LAKE MINES

    TAILING RECLAIMING PROGRAM

    BY: Kelly Dolphin Vice-President Freegold Recovery

  • 52N«4SEee43 63.4855 BALMER TWP 040C

    CONTENTS

    •.

    Introduction

    Drilling Procedure

    Bulk Sampling Procedure

    Tonnage Calculation

    Summary

    Recommendation

    Test Area #1 Drill Logs

    Test Area #2 Drill Logs

    Screen Sizing Results >

    Test Plant Results

    References

    PAGE :•

    1

    1 - 4

    4 - 5

    5 - 6

    6

    7

    Appendix

    Appendix

    Appendix

    Appendix

    8

    t

    A

    B

    C

    D

    0

  • INTRODUCTION

    The tailings area are divided into two areas. Test

    area #1 which was the decant pond was drilled ,first due

    to the fact that C. R. L. M. already have engineering plans

    in progress to .extend the north dyke over the center of

    test area #1 (See Fig. A).

    Test area #2 which is considered to be the coarse

    tailings contained in the dyking system. This tailings

    area used to be the primary pond for the mine until

    abandoned in 1984.

    • DRILLING PROCEDURE

    A vi-cor sonic drill was used to obtain the tailings

    sample material. A grid spacing on test area #1 was used

    consisting of 250 foot lines with hole spacing on each

    line of 250 feet for a total of 28 holes drilled. The

    same grid pattern was used for test area #2 for a total

    of 69 holes in test area #2. All holes were drilled

    within 1' of surveyed location unless otherwise specified

    and were drilled completely through tailings.

    A 4" casing was driven through the tailings with a

    sonic head driven by a 7 h.p. Honda gas power motor. A

    flex cable is used in connecting the head,to the power

    pack. Drill casing was broken into 5. foot lengths, this

    made the handling of the large volume of drill cores

    easier on the drill operators.

  • - 3 -

    The sonic.head vibrated the drill casing to the bottom of

    the tailings. ; Bottom of tailings was usually noted as

    blackish lake bottom type material with dead reeds visible

    in it. A 12,000 lb. winch was then used to pull lip the

    casing. The total length of drill casing was then measured

    (D). When the holes is drilled the cased material is

    compressed. This length is also measured (C). Because the

    core liquified and compacted in the drill casing, the sample

    was never as long as the actual drill length. To adjust for

    this the following formula was used:

    Example: Line #0+310 Hole #3 -

    Total Drill Length (D)

    Compacted Core Length (C) '

    Ratio C/D = 15/12.5 =0.83

    Drill cores were removed and placed in split 6" PVC

    pipe used as core boxes. Drill cores were then sampled

    every 4" using a 5/8" circular tube.

    Drill samples were logged and assigned a number then

    sent to the Campbell Red Lake Mines Assay Office for assay.

    Remaining drill cores were then contained in 5 gal. buckets

    for future analysis.

    Freegold recovery retained Wright Engineering of

    Vancouver to oversee the sampling procedures. Mr. Stu

    Andrews was on sight for one day to visually inspect the

    sampling procedures, he sampled independently and took the

    sample with him for Assay (see Figure B). He agreed with all

    sampling procedures and was satisfied with the drilling and

    testing program. He was not satisfied with the material

  • - 4': -

    He suggested the'following procedures for Freegold and

    C.R.L.M. to use in1 determining true in place material.

    density.

    Step 1: Drill sample, measure drilled-core .length.

    . and compacted core length.

    Step 2: Pull drill core and weigh drill cores in casing.

    Step.3: Transport drill core in casing to mill lab. Pull

    drill core for a moisture content test and dry

    weight.

    He selected 3-locations within the two test areas to perform

    the density test line 0+310 hole #5, Line-4 950 E. Hole #7

    and Line 6200 E. Hole #6. Results will be forthcoming from

    this test.

    BULK SAMPLING

    A number of bulk samples were run through Freegold

    Recovery Test Plant. The plant consists of a 1' x'3* aries

    screening unit with 10 mesh decking. Minus 10 mesh feed is *

    then laundered into a salo SPV 181 slurry pump. Slurry feed

    is then pumped into a Reichert Mark 7 L.G. spiral concentrator.

    The spiral produces 3 splits, concentrates, middling and

    tailing. The qurrent flow sheet is to have the tailing being

    discarded out of the system. Middlings are being recycled

    back into the head feed. Concentrates are then fed onto a

    Gemen'i #250 finishing table. The table produces 4 splits,

    Free Au, Table Con, Table Mids and Table Tails.

  • - 5 -

    . There were a total of 8 samples splits collected per

    bulk sample processed through the test plant. Composite

    samples from each bulk sample were acquired by driving a

    3/4" soil sampler into each 5 gal. bucket, as it's fed

    to the test plant. The composite sample was then cross

    checked by obtaining a composite slurry sample from the

    screeners underfeed. Approximately every minute product

    samples from the 3 spiral splits were obtained. All

    table splits were bagged and tagged for transportation

    to the mill lab. Test results from this preliminary

    bulk sample were rather inconsistent. There was no •

    product balancing or product performance adjusting

    conducted in these test runs. This made it rather difficult

    to account for and any recovery percentages or performance

    ratios from the test plant. Part of Phase II program will

    be to conduct ratios of Freegold test plant.

    TONNAGE CALCULATION

    Volume tonnage aalculations were performed by the

    Engineering staff of Campbell Red Lake Mines. Two

    different seniraos were used in the calculation. The first

    one was calculated using a planimeter area multiplied by

    the average depth of the test holes and divided by 19.0 cu.

    ft./ton which is likely maximum volume. The second approach

    was using the pit volume program. All results were within

    10%.

  • - 6 -

    1.2 million tons

    3.3 million tons

    4.5 million tons

    Average grade = (1.2 x 10" x 0.046) (3.3 x 106 x 0.053)

    4.5 x 106

    = .051 oz./ton

    0.051 oz./ton x 4.5 x 106 Tons = 230,100 oz./Au

    SUMMARY

    The drilling of the tailing areas went very well, once a

    the drill crew modified the core catcher for the sonic drill.

    Much thanks and appreciation must go Campbell Red Lake

    Mines Surface Shops and people for their help and contributions

    in developing the new drill tooling.

    Freegold Recovery retained Lakefield Research to conduct

    bench scale lap tests. Two 20 lb. samples were sent to

    Lakefield by myself. One sample contained 28 different assay

    samples from our drilj. cores. Lakefield was to select 5

    samples for check analysis. The remainder of the samples were

    to be combined for test work. The second sample was a gravity

    con produced with one pass through the Reichert MK 7 spiral.

    Lakefield is to examine two possible flowsheets for gold

    recovery.

    Flowsheet #1: Grinding and cyanidation

    Flowsheet #2: Flotation and cyanidation of cons.

    Total Tons - Area #1

    Area #2

    TOTAL

  • - 7 -

    RECOMMENDATION '•

    1. Bring Wright Eng. into the Phase II Program as soon as

    Lakefield produces their test results. Wright can then

    product a preliminary feasibility study on cap. cost

    and overhead operating cost on a production plant.

    2. Complete a screening analysis and size fraction test

    on the tailing material. This will then determine the

    approach that might be taken with regards to classification

    and gravity recovery.

    3. Backfill ammendability testing, part of this will be

    completed in recommendation #2. An already slurryed

    product could be classified and transported relatively

    cheaply. This would help off-set some of the operating

    cost on the production plant. This part of the project

    would potentially open up new areas within the tailing

    containment dyking area.

    4. Talk with the regulatory boards and obtain an

    understanding of their position: and concerns. This

    will enable us to make the wisest decision with regards

    to plant set up and operation.

    5. Engineering and performance testing of the tailings

    with the latest technology and equipment in grinding,

    classification and recovery.

    Kelly Dolphin, Vice-President, Freegold Recovery. .

    KD*cy August 20, 1986.

  • 8 -

    R E F E R E N C E S

    CAMPBELL RED LAKE MINES LIMITED

    WRIGHT ENGINEERING

    FREEGOLD RECOVERY INC.

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