Marimaca Copper Corp. (“Marimaca Copper” or the “Company”) (TSX:
MARI) is pleased to announce results of the Phase 6 Metallurgical
testing program (the “Phase 6 Program” or the “Program”) for the
Company’s flagship Marimaca Oxide Copper Project (“the MOD” or “the
Project”), located in northern Chile.
The Phase 6 program was designed to evaluate
leaching conditions to optimize acid consumption, recoveries and
leaching efficiency to be incorporated into the ongoing Definitive
Feasibility Study (“DFS”).
Highlights
-
Comprehensive 5 column-test program evaluating the impact
of curing, leaching rates and acid concentration in solution on
acid consumption, recoveries and impurities
generation
-
Significantly improved acid consumption based on
optimization of leaching conditions
- Net acid
consumption of 30.6kg/t from experimental samples – an approximate
25% reduction from the 40.6kg/t derived from previous metallurgical
campaigns
- Provides
further confidence in expected acid consumption with clear
potential to enhance operating cost profile for the
DFS
- Confirms
average copper recovery of 74.9% - in-line with previous results
from metallurgical campaigns (Phases 1-5)
-
Flexibility for further reductions in acid consumption with
relatively low recovery losses
- Program
completed with recycled sea-water sourced from Marimaca’s intended
water supplier under its water option agreement to accurately
reflect process water to be utilized at the Project
- Further
de-risking of the Marimaca metallurgy – allows for improved
predictability of metallurgical performance during
operations
- Results
will be incorporated into the final geo-metallurgical model to be
utilized in the DFS which will define, at high resolution, the
metallurgical performance of each ore-feed type in the
DFS
- Results
demonstrate the self-regulation of impurities in the leaching cycle
which allows for simple SX-EW process design and capital efficiency
for the planned DFS
Hayden Locke, President and CEO of
Marimaca Copper, commented:
“We are pleased with the Phase 6 metallurgical
results and particularly the implications for acid consumption
optimization in the DFS and in future operations.
Acid consumption is a key component of our
operating costs, and fluctuations in acid price were identified as
a core external factor in our projected operating margins as we
move towards first copper. The results from this program show,
firstly, that our base case assumptions, with respect to acid
consumption, can be materially reduced via simple changes to our
operational approach with no significant impact to our expected
recoveries.
Secondly, the testing highlights that we have
further flexibility to reduce acid consumption, with relatively
small recovery losses. From my perspective, this is the most
important outcome from the testing, because it allows us to make
operational changes to preserve margin and cashflow during periods
of high acid prices, which increases the resilience of the Project
to external shocks.
“The Marimaca Project continues to demonstrate
unique positioning in the copper development space. We are excited
to move through the final development milestones as we rapidly
advance toward first copper.”
Program Overview
Phase 6 Metallurgy comprised of a set of
leaching tests in five 1m high, 6-inch diameter columns. The sample
set consisted of green oxides comprised 50% brochantite/atacamite
and 50% chrysocholla with a total sample size of 240kg which was
crushed at P90 ½”, consistent with previous metallurgical test-work
phases. The sample was subjected to separation by sieving, in the
½”, ¼”, 10 and -10 Tyler meshes, and then, from each granulometric
fraction, a sample size was taken as required to form the program
design cut under the standardized “cut by mono size” technique.
Process seawater used in the column tests was
sourced from the counterparty to Marimaca’s water option agreement
to accurately represent the industrial process water that will be
used at the Marimaca operation (see Water Option press release
dated November 7, 2022). The leaching conditions were focused on
variables to optimize acid consumption. The two variables
controlled were acid dosing in curing step, and the Leaching Ratio
(m3 irrigate solution/tonne ore). The head grade of the ore, the
grade of ripios resulting from leaching, the initially acidified
seawater, the pregnant leaching solution (“PLS”) and the raffinate
solutions were each characterized by the elements for which the
evolution of impurities was monitored. The evolution of impurities
was quantified by determining the concentration in the PLS
solutions of the following elements: FeT, Al, Mg, Mn, Na, Cl- and
SO4= and Cu. Cu was removed from the PLS solutions by solvent
extraction (SX), at the end of each leaching cycle.
Column Tests
Results were evaluated from two leaching cycles
over five columns. In both irrigation cycles, the tests operate in
a closed circuit with a volume of irrigation solution equivalent to
10 days of operation, which, at an irrigation rate of 10 L/h/m2 is
equivalent to a leaching rate of 0.93m3/to (approximately) for each
cycle and 1.86 m3/t in total.
Column 1 (C-1) and Column 2 (C-2) were leached
with seawater and acid in the first cycle, then the PLS obtained
was treated by solvent extraction and the raffinate produced was
used for the second leaching cycle. The PLS from the second cycle
of each column (C-1 and C-2) was then treated by solvent extraction
(SX) and both raffinate solutions produced were mixed and used as
the leaching solution for Column 3 (C-3). The post-SX raffinate of
the C-3 PLS was used to leach Column 4 (C-4) and similarly for C-4
to Column 5 (C-5).
Each column was agglomerated and cured under
identical conditions, summarized in Table 3.
Table 1. Sample Set Mass
Allocation
Usage |
Unit |
Value |
Columns |
kg |
150 (5x30kg) |
Head Grade |
kg |
10 |
Back Up |
kg |
80 (4x20kg) |
|
Table 2. Particle Size Distribution of
Sample Set
Granulometric Fraction |
Mass (kg) |
C-1 |
C-2 |
C-3 |
C-4 |
C-5 |
Backup |
1/2" |
3.25 |
3.25 |
3.25 |
3.25 |
3.25 |
8.66 |
1/4" |
9.51 |
9.51 |
9.51 |
9.51 |
9.51 |
25.37 |
+10 # |
8.62 |
8.62 |
8.62 |
8.62 |
8.62 |
22.97 |
-10 # |
8.62 |
8.62 |
8.62 |
8.62 |
8.62 |
22.99 |
TOTAL |
30.0 |
30.0 |
30.0 |
30.0 |
30.0 |
80.0 |
|
Table 3. Agglomeration and Curing
Conditions
Parameter |
Unit |
Value |
Moisture (Seawater) |
% |
6 |
Acid Dose Curing |
kg/ton |
20 |
Curing Time |
days |
3 |
|
Following the irrigation cycle in each column,
the solution contained inside the column was allowed to drain, and
the ripios were washed by passing a seawater solution at pH 3 at an
irrigation rate of 10 L/h/m2 for 24 hours. The drained volume was
measured and analyzed for the same elements considered in the
analysis of the PLS solutions.
Following drainage of the washing stage, the
ripios were unloaded from the respective columns and the wet and
dry weights were recorded. A subsample equal to a quarter of the
total ripios sample was sent for chemical assays following
separation.
Results
Acid Consumption
Acid consumption was measured by both total acid
consumption (CAB) and net acid consumption (CAN). CAN reflects acid
consumed only by the gangue minerals (carbonate, aluminium, total
iron, magnesium) given raffinate is recirculated with the acid
consumed by copper post the SX stage. Geomet 6 was designed to
evaluate the optimization of acid consumption by evaluating three
variables: acid curing rate (20kg/t), acid concentration (10gpl)
and leaching ratio (1.86m3/t).
Results of the column test acid consumption is
presented in Figure 1. Average CAB was 36.91kg/t while average CAN
was 30.63kg/t.
Figure 1. Acid Consumption – Columns
1-5
By controlling the noted variables, acid
consumption can be optimized given the sequential nature of
consumption by each of the gangue minerals – for example, the
majority of acid consumption in the curing stage is driven by
carbonate, followed by copper, aluminum, total iron and magnesium
predominantly during the leaching cycle.
Copper Recovery
Table 4 and Figure 2 show the calculated head
and head/ripio base copper recovery by columns. The average copper
recovery of the 5 columns per head calculated was 74.9%, while the
recovery per head/ripios was 73.0%. Results are in-line with
expected results based on previous test-work and demonstrate that
copper recovery can be maintained while optimizing the variables
that reduce acid consumption and impurities generation.
Table 4. Column Recoveries
Column |
Analyzed Cu Head Grade |
Calculated Cu Head Grade |
Fine Cu Analyzed Head Grade |
Copper Leached |
Copper in Ripios |
Copper Calculated Head |
Recovery Calculated from Head(R CC) |
Recovery Calculated from Ripios(R C/R) |
(N°) |
(%) |
(%) |
(g) |
(g) |
(g) |
(g) |
(%) |
(%) |
C-1 |
0.620 |
0.568 |
186.00 |
122.64 |
47.74 |
170.4 |
72.0 |
74.3 |
C-2 |
0.620 |
0.628 |
186.00 |
139.47 |
49.03 |
188.4 |
74.0 |
73.6 |
C-3 |
0.620 |
0.638 |
186.00 |
143.68 |
47.74 |
191.4 |
75.1 |
74.3 |
C-4 |
0.620 |
0.718 |
186.00 |
166.72 |
48.83 |
215.4 |
77.4 |
73.7 |
C-5 |
0.620 |
0.815 |
186.00 |
186.3 |
58.05 |
244.5 |
76.2 |
68.8 |
|
Figure 2. Column Recoveries
Impurities Generation
The column tests were evaluated to determine the
experimental evolution of impurities generation vs. the theoretical
evolution of impurities generation to determine the equilibrium
point of the system. This was studied to determine the expected
performance of the SX-EW plant and its ability to handle the
solution generation from leaching of Marimaca ores.
Results shows that as the recirculation of
leaching solution occurs, as is the case in industrial operations,
the capacity of the system to dissolve impurities decreases, which
indicates that the system self-regulates before any impurities
mitigation is required in the SX-EW process design. In industrial
terms, by feeding the heap with fresh ore, the curing acid and the
leaching solutions will dissolve new impurities, but simultaneously
others will precipitate in the heap, and the system will reach
equilibrium.
This concept is demonstrated in Figure 3.
Whereby results from Geomet 6 show the experimental sulfate
concentration in each cycle deviates and plateaus relative to the
theoretical sulfate concentration with the correlation coefficient
of the experimental results of 0.9992. When projecting the
experimental curve 3 additional cycles, it can be observed that the
sulfate saturation level is approximately 147 gpl.
Table 5. Evolution of Impurities
Concentration in PLS solution
Column |
FeT |
Al+3 |
Mg+2 |
Mn+2 |
Na+ |
Cl- |
SO4= |
(Nº) |
(g/L) |
(g/L) |
(g/L) |
(g/L) |
(g/L) |
(g/L) |
(g/L) |
C-1 |
6,54 |
3,14 |
3,49 |
0,25 |
13,15 |
27,55 |
46,21 |
C-2 |
6,18 |
3,03 |
3,21 |
0,20 |
12,55 |
26,67 |
44,76 |
C-3 |
9,61 |
5,40 |
4,03 |
0,37 |
13,42 |
28,81 |
74,98 |
C-4 |
13,50 |
6,99 |
5,61 |
0,57 |
16,05 |
31,43 |
103,37 |
C-5 |
17,52 |
10,34 |
6,80 |
0,80 |
18,53 |
38,16 |
120,32 |
|
Figure 3. Evolution of Sulfate
Concentration in PLS solution
Appendix: Chemical Characterization of
Experimental Inputs
Below the chemical characterization of the head
sample, the seawater input, and the leaching solution are
presented.
Table 6. Chemical Characterization of
Head Sample
Elements |
CuT(%) |
FeT(%) |
|
Al(%) |
Mg(%) |
|
Mn(%) |
Na(%) |
CO3(%) |
Cl-(%) |
SO4=(%) |
Head Grade |
0.641 |
7.66 |
|
6.72 |
1.05 |
|
0.07 |
3.09 |
0.63 |
0.25 |
0.15 |
|
Table 7. Chemical Characterization of
Seawater Used
Element |
Cu+2(mg/L) |
|
FeT(mg/L) |
Al+3(mg/L) |
Mg+2(g/L) |
Mn+2(mg/L) |
Na+(g/L) |
Cl- (g/L) |
SO4=(g/L) |
pH |
Seawater |
0,00 |
|
0,90 |
1,70 |
1,44 |
ND |
11,33 |
23,21 |
2,10 |
7,60 |
|
Table 8. Chemical Characterization of the
Initial Leaching Solution (for Columns C-1 and C-2)
|
Cu+2 |
FeT |
Fe+2 |
Al+3 |
Mg+2 |
Mn+2 |
Na+ |
Cl- |
H+ |
pH |
SO4= |
(mg/L) |
(mg/L) |
(mg/L) |
(mg/L) |
(g/L) |
(mg/L) |
(g/L) |
(g/L) |
(g/L) |
|
(g/L) |
Leach Solution |
0,00 |
0,90 |
ND |
1,70 |
1,44 |
ND |
11,33 |
22,10 |
9,38 |
0,75 |
9,94 |
|
Qualified Person
The Qualified Person for technical information
in this news release is Gabriel Vera, an extractive metallurgical
engineer with over 35 years of experience. Mr. Vera is a registered
member of the Comision Minera (Chilean Mining Commission) and a
Qualified Person for the purposes of NI 43-101.
The QP confirms they have reviewed and approved
the scientific and technical information related to metallurgy in
this news release.
Contact InformationFor further
information please visit www.marimaca.com or contact:
Tavistock +44 (0) 207 920
3150Gareth Tredway / Adam
Baynesmarimaca@tavistock.co.uk
Forward Looking Statements
This news release includes certain
“forward-looking statements” under applicable Canadian securities
legislation. There can be no assurance that such statements will
prove to be accurate, and actual results and future events could
differ materially from those anticipated in such statements.
Forward-looking statements reflect the beliefs, opinions and
projections on the date the statements are made and are based upon
a number of assumptions and estimates that, while considered
reasonable by Marimaca Copper, are inherently subject to
significant business, economic, competitive, political and social
uncertainties and contingencies. Many factors, both known and
unknown, could cause actual results, performance or achievements to
be materially different from the results, performance or
achievements that are or may be expressed or implied by such
forward-looking statements and the parties have made assumptions
and estimates based on or related to many of these factors. Such
factors include, without limitation: risks related to share price
and market conditions, the inherent risks involved in the mining,
exploration and development of mineral properties, the
uncertainties involved in interpreting drilling results and other
geological data, fluctuating metal prices, the possibility of
project delays or cost overruns or unanticipated excessive
operating costs and expenses, uncertainties related to the
necessity of financing, uncertainties relating to regulatory
procedure and timing for permitting reviews, the availability of
and costs of financing needed in the future as well as those
factors disclosed in the annual information form of the Company
dated March 27, 2023 and other filings made by the Company with the
Canadian securities regulatory authorities (which may be viewed
at www.sedar.com). Statements regarding the Company’s planned
DFS on the Project are forward-looking information and may not be
realized. Readers should not place undue reliance on
forward-looking statements. Marimaca Copper undertakes no
obligation to update publicly or otherwise revise any
forward-looking statements contained herein whether as a result of
new information or future events or otherwise, except as may be
required by law.
Neither the Toronto Stock Exchange nor the
Canadian Investment Regulatory Organization accepts
responsibility for the adequacy or accuracy of this
release.
Photos accompanying this announcement are available
at:https://www.globenewswire.com/NewsRoom/AttachmentNg/ac8d7b9a-d2b9-4fec-84aa-d78fa8fc60cc
https://www.globenewswire.com/NewsRoom/AttachmentNg/122b22f6-613a-405e-a803-d1cbe5767c3f
https://www.globenewswire.com/NewsRoom/AttachmentNg/e4807430-c676-4e69-b4eb-a23f33ce194a
Marimaca Copper (TSX:MARI)
Historical Stock Chart
From Jan 2025 to Feb 2025
Marimaca Copper (TSX:MARI)
Historical Stock Chart
From Feb 2024 to Feb 2025