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CITIGOLD CORPORATION LTD.
Charters Towers Gold Integrated Exploration Project
EPM 13932
PARTIAL RELINQUISHMENT REPORT
SUB-BLOCKS RELINQUISHED JUNE 2006
Distribution: Citigold BrisbaneCTG Charters Towers DNR&M
Authors: Morrison R J & McGregor-Dawson J Date: November 2006
Report No.: CT2006-16
Charters Towers Gold Pty LtdACN 070 643 631, ABN 34 070 643 631
Treatment Plant Site, Clermont Highway Via Charters Towers QLD 4820PO Box 414 Charters Towers QLD 4820
Telephone: 07 4787 8300, Facsimile: 07 4787 8600, Email: [email protected]
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CONTENTS
Page Number
Summary 3
1.0 Introduction 3
2.0 Tenure 3
3.0 Geology
3.1 Regional Geology 4
3.2 Tenement Geology 6
4.0 Exploration
4.1 Mineral Occurrence Evaluation 8
4.2 Aeromagnetic Interpretation 9
4.3 Soil and Rock Chip Sampling 10
5.0 Conclusions 10
6.0 Rehabilitation 10
7.0 References 11
LIST OF FIGURES
Figure 1 Location Map, EPM 13932 Relinquished Sub-blocks
Figure 2 GSQ regional geology (Hutton et. al. 1996), showing relinquished sub-
blocks. Figure 3 GSQ geology of western sub-block
Figure 4 GSQ geology of eastern sub-block
Figure 5 Aeromagnetic data over part of eastern sub-block group
Figure 6 Soil sample locations and sample numbers, eastern sub-
blocks. Figure 7 Soil sample locations and sample numbers, western
sub-blocks.
LIST OF APPENDICES
Appendix 1 Soil & Rock Chip Descriptions and Assays
Appendix 2 Assaying Methods, Sampling Procedures and Standard
Geological Abbreviations
Appendix 3 Environmental Code of Practice Report
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SUMMARY
Nine sub-blocks relinquished from EPM 13932 in June 2006 were explored for gold.
Methods used included geophysical interpretation and mineral occurrence evaluation. The
areas are predominantly underlain by Palaeozoic granitoids which are locally covered by
Tertiary laterites and recent alluvium. Only one un-named prospect is reported by GSQ to
occur in the area of the relinquished sub-blocks (GSQ 292702).
1.0 Introduction
The nine relinquished sub-blocks are in two groups and are centred 15 km SW (4 sub-
blocks) and 10 km SSE (5 sub-blocks) from the centre of Charters Towers, Queensland,
(Figure 1). Charters Towers is located about 105 km SSW of Townsville. Landforms
comprise low hills and plains within the Burdekin River catchment.
The tenement lies on the Charters Towers 1:100,000 Sheet Number 8157. Access is
generally good via a network of formed roads. The area is held as grazing properties.
The Charters Towers goldfield is world class, having produced 6.6 million ounces of gold at
a grade of over 1 ounce to the tonne.
The objective of Citigold’s exploration on the EPM was to delineate mineable gold resources
for processing at the Black Jack treatment plant. Citigold’s existing infrastructure would
facilitate the early development of any viable gold deposit located in the tenement area.
2.0 Tenure
EPM 13932 was granted on 23rd of June 2003 to Charters Towers Gold Mines Ltd
(CTGM). In November 2003 CTGM changed its name to Citigold Corporation Ltd.
Nine sub-blocks were relinquished on 22nd of June 2006. The relinquished sub-blocks are
shown on figures 1 & 2, and are listed as follows:
BIM Block Sub-Blocks
CLER 98 R, S, W, X
CLER 100 U, W, X, Y, Z
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Figure 1: Location of the nine sub-blocks relinquished.
3.0 Geology
3.1 Regional Geology
The Charters Towers Goldfield lies along a regional scale geological structure, the
Mosgardies Shear Zone. Hutton (1994) has shown that this shear zone is a major crustal
block boundary separating two separate types of deep crustal rocks. Work by the
Australian Geological Survey Organisation (Shaw et al, 1996) has established that the
Mosgardies is part of a coincident E-W gravity and magnetic boundary over 300km long.
The deep crustal structures are believed to have acted as channelways for the ore fluids
from which the Devonian gold orebodies were deposited. This major regional structural
control explains the extent, continuity, and relatively uniform structural control of most ore
bearing fissures in the district.
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GSQ regional geology (Hutton et. al. 1996), showing relinquished sub-blocks.
District geology was described by Hutton and Rienks (1997). The Ravenswood Batholith
dominates the current land surface; an Ordovician to mid-Devonian igneous complex
intruded into a Pre-Ordovician package of metamorphosed sediments and igneous rocks.
The Batholith is in turn cut by Permo-Carboniferous intrusives.
The first phase of development of the Ravenswood Batholith was intrusion of granites
commencing at 490Ma (Hutton and Rienks, 1997). A major phase of intrusive activity
continued until the mid Ordovician. A second phase, dominated by extensional granodiorites
and tonalitic intrusives occurred from the mid-Silurian to the mid-Devonian. Deformation,
which occurred from the mid-Ordovician to mid-Silurian, is typically represented in the older
granitoids by steeply dipping, east striking narrow mylonite zones.
Mafic intrusives within the Batholith range from Ordovician to Silurian. Typical examples are
the Stannett Ck Gabbro and the mafic complexes north of Black Jack. Aplite and minor
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pegmatite dykes are widespread, and NE trending basaltic dyke swarms occur near
Charters Towers. The Silurian Millchester Creek Tonalite, an irregular NW trending
intrusion that occupies the central Charters Towers area, cuts the older units.
The Early Devonian Broughton River and Deane Granodiorites were intruded at around 406
- 410Ma. These intrusives are more radioactive than most in the region and are distinctly
zoned as observed on radiometric and aeromagnetic images. The zoning may possibly be
evidence of convection? &/or differentiating magma chambers.
Shortly after, at ca. 400Ma, the Charters Towers mineralisation occurred at the same time
as the Lolworth Igneous Complex was intruded to the west. The mineralisation is
predominantly quartz reef hosted pyrite - sphalerite - galena - gold. The gold mineralised
fissures and associated sericitic alteration post dates the granitic intrusives and cuts across
all the earlier units in the area.
The Charters Towers style gold bearing ore shoots were typically precipitated as fissure
hosted quartz veins in structurally controlled trap sites at considerable depth. Many of these
are along kilometre scale lode zones, predominantly within granitic host rocks. On a regional
scale, Charters Towers style mineralisation is known for over 60 km. along the east-west
trend from Mt Hope in the west, to east of the Hadleigh Castle mine (Hartley & Dash, 1993).
Later NNW trending faults of possibly Permo-Triassic age cut the whole sequence.
Remnants of lateritised early Tertiary fluvial sediments occur locally associated with
duricrust capped palaeo-land surfaces.
3.2 Tenement Geology
The western group of four relinquished sub-blocks (Figure 3) is underlain by Siluro-
Devonian granitoids consisting of the Powlathanga Tonalite (SDgp) and the Centauri
Granodiorite (SDgc) (Hutton et al, 1996). Both these units are locally mottled and leached
indicating deep weathering. Tertiary and Quaternary sediments cover much of the
granitoids, especially over the western two sub-blocks. The main units of the cover
sequence are as follows:
Qa & Qr: Quaternary sands, clays, gravels, soils & alluvium.
TQr: Tertiary sand, mud, gravel, ferricrete & residual
soils.
Ts: Quartzose Sandstone, Clayey sandstone, mudstone, conglomerate,
undifferentiated sediments (including the Southern Cross
Formation).
Td: Tertiary duricrust – indurated weathering profile.
Figure 3: GSQ Geology of the western group of 4 sub-blocks (Hutton et al, 1996)
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The five sub-blocks of the eastern group (Figure 4) are underlain by Ordovician granitoids
(Ogh & Oso), and one local occurrence of Pre-Cambrian metamorphics (P€ct) (Hutton et
al, 1996). The various units are described as follows:
Oso: Ordovician La Villa Igneous Complex (gabbros, quartz diorites &
diorites). Ogh:Ordovician Hogsflesh Creek Granodiorite (locally granites occur).
P€ct: Pre-Cambrian Charters Towers Metamorphics.
One significant shear zone is traceable for 11 km in an ENE – WSW direction. This shear
cuts the two southeastern sub-blocks of the eastern group of 5 sub-blocks relinquished.
This shear zone is based on geophysical interpretation.
Figure 4: GSQ Geology of the eastern group of 5 sub-blocks (Hutton et al, 1996)
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4.0 Exploration
Work on the nine relinquished sub-blocks included obtaining and reviewing past
exploration and mineral occurrence data, the evaluation of exploration potential, soil
geochemical sampling, and aeromagnetic and radiometric interpretation. Fieldwork was
only undertaken on road reserves.
4.1 Mineral Occurrence Evaluation
Hartley (1993) evaluated the mineral occurrences on the Charters Towers 1:100,000 sheet
for the Geological Survey of Qld in the late 1980s. This work was evaluated and highlighted
one mineral occurrence on the relinquished sub-blocks (Figure 4). This is an un-named
Au/Ag prospect (GSQ 292702) that is located on the southeast sub-block in the eastern
group of five sub-blocks (near the junction of Hogsflesh and Roberts Creeks).
Figure 5: Aeromagnetic data (RTP – 1999) covering part of the eastern 5 sub-blocks.
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4.2 Aeromagnetic Interpretation
The Company undertook detailed low level aeromagnetic and radiometric survey of adjacent
tenements in 1999-2000 (UTS Geophysics, 2000). The survey extended into the northern
and western sections of the eastern group of five sub-blocks (Figure 5). The full results
were previously reported to the Department (Morrison et al., 2001).
The aeromagnetic image in figure 5 has been converted to “Reduced to Pole” format to
assist interpretation. The northern and western parts of the eastern group of five sub-blocks
are just inside the survey area. It is clear that a prominent NE-SW lineament would extend
through the western most sub-block, and a strong NW-SE lineament would cut the middle
sub-block. No mineralisation or alteration is recorded along these lineaments. The NE-SW
lineament appears to represent the hidden contact of the Charters Towers Metamorphics in
this location. The NW-SE lineament does not appear to represent a rock type contact, but
the stream drainages may indicate a significant fault structure. Over several kilometres to
the
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NW, along the NW-SE lineament, there appears to be an alignment of several prospects
including: Bonnie Doon, Marquis of Lorne, Telegraph and the Union Lode.
4.3 Soil and Rock Chip Sampling
Several reconnaissance soil lines were put in along roads, and totalled 83 samples
(Appendix 1). The eastern group of five sub-blocks contains three soil lines for a total of 65
samples (Figure 6), while the western group of four sub-blocks has one soil line of 18
samples (Figure 7). The soil samples were unsieved apart from coarse fragments and
designed to include any quartz or gossanous lag material. They were taken from a depth of
about 20cm, and were analysed for gold, silver, copper, lead, zinc, arsenic, bismuth,
molybdenum, iron, and sulphur. None of the 83 samples contain significant gold, and only
occasional weak lead values (<100ppm) showed some anomalism in the soils. Details of
assaying methods, sampling procedures, and standard geological codes used are located in
Appendix 2.
One rock chip sample (203833) was collected from the relinquished sub-blocks. This
came from the eastern group of five sub-blocks, and was taken somewhere along
Woodchopper Road, north of Hogsflesh Creek, in sub-block “U” of Clermont block 100
(AMG co-ords: E429457 & N7772383). It is described as a sub-outcrop quartz vein
sample that appears to be hosted in the Ordovician La Villa Igneous Complex (Oso). The
assay returned the following results (in ppm): 1.42 Au; 1.0 Ag; 33 Cu; 311 Pb; 115 Zn; 19
As; 3 Mo; 40,500 Fe, & 265 S. Despite the anomalous gold value, there has been no
follow-up of this sample.
5.0 Conclusions
No economically significant mineral occurrences were identified on the
relinquished sub-blocks.
Interpretation of aeromagnetic and radiometric data assisted the structural
and geological understanding of the tenements.
6.0 Rehabilitation
Fieldwork on the relinquished sub-blocks did not involve any significant ground disturbance.
Therefore no rehabilitation is required. A report on compliance with the Environmental Code
of Practice is included as Appendix 3.
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7.0 References
Hartley J S & Dash P H, 1993. Mineral Occurrences on the Charters Towers 1:100,000
Sheet, Qld. Queensland Geological Record 1993/6.
Hutton L J, (1994). Mineralisation styles, controls, and a possible tectonic model in the
Charters Towers Area, North Queensland. Queensland Exploration Potential
Symposium, Qld. Dept of Mines & Energy.
Hutton, L.J., Beams, S.D & Rapkins, R.J., 1996. Australia 1:100, 000 Geological Series,
Charters Towers, Qld. Sheet 8157.
Hutton L J & Rienks I P, 1997. Geology of the Ravenswood Batholith. Queensland Geology
8. Qld. Dept of Mines & Energy, Brisbane.
Morrison R J, 2002. EPMs 10593, 11067 & 13106. Combined Annual Report for the period
1 January 2001 to 31 December 2001. CTGM Report No CT2002-05 (Unpubl.).
Shaw R D, Wellman P, Gunn P, Whitacker A J, Tarlowski C, & Morse M, 1996. A guide to
using the Australian Crustal Elements Map. AGSO Record 1996/30, AGSO, Canberra.
UTS Geophysics, 2000. Logistics Report for a Detailed Airborne Magnetic, Radiometric and
Digital Elevation Survey for the Charters Towers Project carried out on behalf of
Charters Towers Gold Mines N L by UTS Geophysics (UTS Job #A346). CTGM Report
CT2000-09 (Unpubl.)
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Appendix 1
Soil & Rock Chip Descriptions and Assays
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Appendix 2
Assaying Methods, Sampling Procedures and Standard Geological Abbreviations
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Appendix 3
Environmental Code of Practice Report
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SGS / Analabs Assay Methods
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PROCEDURE – BEFORE FIELD SAMPLING
Before attempting to do any soil sampling, rock chipping, lag sampling or stream sediment work, ensure that all the correct access to land procedures have been followed and that the land you are going to sample on has been cleared and authorized by management. Refer to SOP 051 – Access to Land. Also refer to the Sampling Survey Protocols.
Make sure your location has been clearly marked on the Field Location Map and that you have sufficient communication with your Department head or representative.
PROCEDURE - ASSAY METHODS
Assay methods used obviously depend on what the results are to be used for. Refer to Assay and Standard Protocols. For routine work the assays should be performed by the current NATA certified assay contractor. Normally different assay contractors are used for drilling / resource estimation assays from those used for rock chip / soil / stream sediment work. Sample submission is undertaken as described in SOP 511 - Geological Data Entry.
Specialised analytical methods are used where appropriate. In particular screen fire assays are used where coarse gold is potentially present such as in pyritic and/or gossanous quartz samples. Where more precise multi-element assays are required, typically a four acid “near total” digestion is used, HF-HNO3-HClO4 acid digestion and HCl leach.
Routine multi-element ICP analyses using aqua regia digest are undertaken to assist definition of mineral zonation, to investigate any high sulphide areas, and to check sulphide content for future environmental waste characterisation. Lead, and to a lesser extent zinc assays are useful indicators of gold mineralisation.
For routine work the following procedures are followed and elements are assayed for:
Rock Chip & non-quartz-sulphide diamond core samples Sample preparation (jaw crush to -6mm, ring mill pulverise entire sample to 85% -75um), Assay for Au (50g fire assay, AAS finish; detection 0.01ppm), Assay for Ag, As, Cu, Pb, Zn, Bi, Mo, Fe, S (ICP-AES after high temperature perchloric-hydrochloric-nitric acid digest).
75um),Soil samples Sample preparation (dry, ring mill pulverise up to 1.5kg to 85% -
Assay for Au (50g aqua regia leach at <800, graphite furnace finish; detection 0.001 ppm),Assay for Ag, As, Cu, Pb, Zn, Bi, Mo, Fe, S (ICP-AES using an aliquot from the gold aqua regia digest; semi-quantitative results).
Exploration stream sediment samples Bulk leach extractable gold (2kg active 24 hr pH controlled caustic cyanide solution extraction; detection 1ppb).
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PROCEDURE - QUALITY ASSURANCE, STANDARDS, DUPLICATES AND BLANK ASSAY SAMPLES
Quality Assurance and Control (QA/QC
QA/QC assay blanks, standards and evaluation is routinely undertaken by the NATA certified assay contractors used by the Company. These include regular checking of assay data for precision and accuracy using re-splits, repeats, blanks and standards. Such check assays should usually be in the ratio of 2 standards, 5 replicates and 1 reagent blank per 50 to 84 sample.
In addition to these, internal quality assurance and control methods are being developed based on the Assay and Standard Protocols. The results of the standard assays are to be reviewed on a batch-by-batch basis and, if sample numbers permit, on a monthly basis with charts of the results prepared. All samples returning an initial assay greater than 1 g/t Au with potential to be included in resource estimation should be re-assayed. Inter-laboratory comparisons are to be run periodically which indicate an assay precision of better than +/-15% of the mean. Duplicate samples should have a precision of +/-10%.
Standards
Standards are to be inserted into assay batches to maintain a record of the laboratories quality control and assay accuracy. Standards come in a range of assay values and appropriately valued standards should be used with accompanying samples. Where Au values of samples taken are expected to be low, an appropriate standard of a low Au value should be used and vice versa. For current assay standards refer to the Assay & Standard Protocols. Normally, standards are added after every 50th sample, or 1 standard per batch where a lesser number of samples is submitted.
Different sampling applications will dictate various methods of use of standards, however, as a guideline, use the recommendations below. For rock chips, underground face, stockpile and diamond drill sampling, use discretion when choosing the value of the standard to be included. Assess the sampled material and decide whether the assay results should be high or low in Au, then, attach the appropriate sample.
Soil sampling: 1 standard per batch Low Au valueRock Chip sampling: 1 standard per batch Low to high Au
valueStream Sediment sampling 1 standard per batch Low Au value(If BLEG standard available)
SOIL SAMPLING:
PROCEDURE:
Before sampling:
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Organise sampling equipment (First Aid Kit, drinking water, pick and shovel, sample books and bags or Kraft envelopes, data entry sheets, sieves, polyweave sacks, maps and GPS etc.)
Upon arrival at a sample site, take note of the best location to take a sample, trying to avoid any soil that may have been disturbed by earthworks, transported by creek systems or affected by old workings or constructions. These are the most common causes of soil contamination.Note: Samples taken from such areas are not a true representation of the local geochemical environment and should be avoided (if possible) at all times.
Sampling:First establish the correct material to sample and any size fraction and weight requirements. When a suitable site is found, dig out roughly a half metre by half metre area down to approx ten centimetres deep. Discard this top layer taking care to get rid of any large rocks and vegetation from the hole. You should start to see a change in the soil colour at this depth. If not, scratch further down until you do and discard this soil also. Sometimes, the soil colour will not change, in black soil areas for example. Make note of circumstances such as this and use your own discretion e.g. don’t dig forever looking for a colour change.
Once the surface layer (A Horizon) has been scraped clear of the hole, continue digging down (into the B Horizon) until you have enough to fill the bag or kraft envelope to the required weight. Discard any large rocks and excess vegetation and then sieve off the correct size fraction if this is required. Fill the sample bag and tie it off. Refill the hole and tamp down. Place the sample into a polyweave sack pre written with the lab address and sample numbers. Approximately 25 kg of samples in each sack is sufficient weight.
On the sample description sheet note the sample number, it’s location from the GPS, soil colour and any other comments you feel need to be made. Once all details have been recorded, proceed to the next sample site and repeat the same process. If soiling along a road, look for any approaching traffic before pulling out.
HAZARDS: Irate landholders Equipment damage Hand injury Eye injury Back injury Weather exposure Vehicle breakdown without support Vehicle accident Falls (creek banks, hidden timber etc.) Heat stress / Dehydration Getting lost Snake or insect bites Incorrect sample
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HAZARD CONTROL: Adhere to SOP 051 Access to Land Use appropriate PPE Sufficient Training Sufficient communication Sufficient location information at base Due diligence and care Maintenance of vehicle and equipment First Aid Kit / Snake bite kit
PPE REQUIRED: Safety glasses Steel capped boots Protective clothing i.e. long sleeved shirt and trousers Sun protection, sunscreen (recommended) Gloves (recommended)
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ROCK CHIP SAMPLING:(Includes niche sampling specific rock types or mineralisation)
PROCEDURE:
Before sampling:Upon arrival at site, write down sample number, coordinates of sample and a description of the rock chip taken using the rock chip sampling sheets. Be sure to wear safety glasses and a long sleeve shirt and trousers when hitting any rocks.
Sampling:
When you have decided on the rock to be sampled, break off a specimen piece to take back to the office and write the corresponding sample number on it. This piece can be handy as a quick reference in case of any anomalous assays.
Break up enough pieces of rock to about 2 kg, or if there is not enough for this, gather what you can and put in sample bag. Never break rocks by hand. Never break rocks in your hand with the G-pick. Preferably hold the rock firmly to the ground with your foot when hitting it, as long as it is big enough to do so safely. Tie off sample bag and place into pre numbered and lab addressed polyweave sack. Only mark the sample site if requested by the geologist. Spray paint a small mark at the site with fluorescent paint if permitted.
HAZARDS: Irate landholders Equipment damage Hand injury Eye injury Back injury Weather exposure Vehicle breakdown without support Vehicle accident Falls (creek banks, hidden timber etc.) Heat stress / Dehydration Getting lost Snake or insect bites
HAZARD CONTROL: Adhere to SOP 051 Access to Land Use appropriate PPE Sufficient Training
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Protective clothing i.e. long sleeved shirt and trousers Sun protection, sunscreen (recommended) Gloves (recommended) Steel capped boots
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STREAM SEDIMENT SAMPLING:
PROCEDURE:
Before sampling:
Stream sediment sampling is undertaken to gather indicative geochemical information from a wide area without using extensive and costly exploration techniques. Active streams will carry minerals washed down from surrounding higher ground and this give you a very broad and diluted idea of mineral occurrences in the area. Samples are generally only taken from smaller creek systems. Stream sediment sampling is usually a first pass exploration tool.
The most common causes of contamination of a stream are disturbance by earthworks, old workings, constructions (Buildings, Stock yards etc) and bridges or vehicle crossings. Where possible these sites should be avoided.
Upon arrival at site, take note of the best location in which to take your sample according to the geologist’s requests. Write down the sample number, coordinates of the sample and other data required as well as any other relevant information necessary e.g. width of creek, outcrop nearby etc.
Sampling:
Collect your sample by taking a small channel of active stream sediment across the creek bed, generally avoiding any trap sites and sieving into a gold pan or dish, making sure to extract any vegetation from the sample. Sieve sizes, sample weights and collection methods may vary. Tie off sample bag / packet and place into pre numbered polyweave sack or carton.
HAZARDS: Irate landholders Weather exposure Vehicle breakdown without support Vehicle accident Falls (creek banks, hidden timber etc.) Heat stress / Dehydration Getting lost Snake or insect bites
HAZARD CONTROL: Adhere to SOP 051 Access to Land Use appropriate PPE
Sun protection, sunscreen Protective clothing i.e. long sleeved shirt and trousers Gloves (recommended) Steel capped boots
STANDARD GEOLOGICAL CODES AND ABBREVIATIONS TO BE USED FOR LOGGING AND MAPPING
LITHOLOGYCode DescriptionALUV AlluviumAND AndesiteAP Aplite
BAN Basaltic AndesiteBAS BasaltBD Basaltic DykeBX Breccia
CALIC CalicheCBV Carbonate VeinCHT Chert
CLAY ClayCOLV Colluvium
CS CalcsilicateCTM Metamorphics (Undifferentiated)
DI DioriteDO DoleriteFEL FelsiteGAB GabbroGD Granitic Dyke
GDR GranodioriteGFM Gold "Formation" (sericitic alt)GOS GossanGRA GraniteHNF HornfelsHPD Hornblende Porphyry DykeHPP Diorite Porphyry Dyke
LODE LodeMD Mafic Dyke
META MetasedimentMGR MicrograniteMSH Meta-Shale / SlateMSL Meta-SiltstoneMSS Meta-SandstoneMY Mylonite
PEG PegmatitePHY Phyllite
PORP PorphyryQCBV Quartz Carbonate Veining
QV Quartz VeinQZT QuartziteRHY Rhyolite
SAND SandSCH Schist
SHEAR ShearSOIL SoilTAN Trachytic AndesiteTON TonaliteTQC Continental Seds (consolidated.)TS Continental Seds (lateritised)
XENO Xenolith
Collection MethodCode DescriptionCHN Channel / Chip lineCOM CompositeMP Multiple pointSP Single Point
MINERALCode Descriptionalb Albite
amph Amphiboleasp ArsenopyriteAu Goldazu Azuritebio Biotitebn Bornitecal Calcitecb Carbonatecer Cerussitechl Chloritecp Chalcopyritect Chalcociteep Epidotefs Feldspargl Galena
glsp Galena & Sphaleritegoe Goethitegrp Graphitegyp Gypsumhb Hornblende
hem Haematitejar Jarosite
laum Laumontitelim Limonite
mag Magnesitemal Malachitemic Micaceousmn Mn oxide (pyrolusite etc)mol Molybdenitemon Montmorillonitemt Magnetite
musc Muscoviteplag Plagioclasepo Pyrrhotitepx Pyroxenepy Pyrite
pycp Pyrite & Chalcopyritepyct Pyrite & Chalcocitepygl Pyrite & Galenapysp Pyrite & Sphaleriteqtz Quartzsco Scorolitese Sericitesp Sphalerite
sulph Undifferentiated Sulphidetal Talc
tour Tourmaline
COLOURCode Description
Bf BuffBk Black
BkGy Black GreyBl BlueBr Brown
BrGy Brown GreyCr CreamGn GreenGy Grey
GyGn Grey GreenGyOr Grey OrangeGyPk Grey PinkGyRd Grey RedGyWh Grey WhiteGyYl Grey YellowOr Orange
OrBr Orange BrownOrGy Orange GreyOrPk Orange PinkPk Pink
PkBr Pink BrownPkGy Pink Grey
Rd RedRdYl Red YellowWh White
WhGy White GreyYl Yellow
TEXTURE (continued)Code Descriptionfss Fissilegos Gossanousgrnl Granularrad Radiatinglam Laminated
mass Massivemgr Medium Grainedmy Myloniticpeg Pegmatiticporp Porphyryticsh Shearedsht Shatteredshy Shaleytab Tabularvfg Very Fine Grainedvug Vughy
SAMPLE CLASSCode DescriptionEX Not in situFL FloatML MullockOC OutcropSC SubcropSF Stope fill
REGOLITHCode DescriptionCLZ Clay ZoneFR Fresh (unweathered) rockLAT LateriteMOZ Mottled ZoneMW Moderately WeatheredSAP SaproliteSOIL Soil, inc. unconsolidatedSRK Saprock
GENERAL ABBREVIATIONSCode Description
// Parallelalt Alteration
ang Angularapprox Approximately
av Averagebot Bottomca Core Axiscol Colour
contm Contaminateddeg Degreedia Diameterdiss Disseminateddist Distributedepi Epithermalgr Graingrc Graphitichd Hard
homg Homogeneoushvy Heavyjsp Jasperiodalmat Materialmax Maximummeso Mesothermalmin Minimumminl Mineralmtx Matrixreg Regularsec Secondaryseds Sedimentsselv Selvagestrk Streak
v veryvar variablevd Vein-Dykevol Volumextl Crystal
wd Weathered cl Clevageclf Colloformcox Cockscomb Dogtoothdisc Disc Fracturingfgr Fine Grainedfol Foliated
frac Fracturedfri Friable
18 August 2004
StandardAbbreviationCodes.xls 12/05/2005
wd Weathered cl Clevageclf Colloformcox Cockscomb Dogtoothdisc Disc Fracturingfgr Fine Grainedfol Foliated
frac Fracturedfri Friable
EXTENTCode DescriptionMOD ModerateSTR StrongTR TraceWK Weak
HUE (colour prefix)Code Description
d darkl light
1PRESCRIBED ACTIVITY NOT
APPLICABLEAPPLICABLE
REQUIRED COMPLETED AUDITED1. LAND MANAGEMENT1.1 Disturbed areas minimized and kept <500sq.m in any one location √ √1.2 Erosion Prevention
1.2.1 Existing tracks and roads used where possible
1.2.2 New tracks cleared to above level of topsoil. Minimised clearing of vegetation and avoidance of mature trees.
1.2.3 Diversion banks constructed across inclined tracks.
1.2.4 Blade spillage windrows constructed on the contour when reshaping areas of disturbance.
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1.3 Landform Management1.3.1 Subject to 1.7.1, upon completion of sampling, mapping etc excavations, backfilled with
stockpiled overburden returned to the excavation. All backfilled excavations should be overfilled to allow for settlement.
1.3.2 Disturbed land rehabilitated after completion of use including replacement of topsoil.
1.3.3 Disturbed land and excavations recontoured similar to adjacent undisturbed land.
1.3.4 Drill holes plugged and backfilled.
1.3.5 Shafts, adits and costean pits make safe at all times.
1.3.6 Compacted areas contour ripped to 0.5m depth where practicable using rippers with a minimum spacing of 1m.
1.3.7 Stable and non eroding land surfaces restored.
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1.4 Waste Management1.4.1 Maintenance activities carried out such that spillage of hazardous material (oils, fuels, drilling
chemicals, radioactive materials and industrial refuse, including sample bags) will be collected for disposal off-site.
1.4.2 All domestic refuse removed from the project area or buried at a depth of at least 1.5m and covered with rock material and at least 100m from a water course.
1.4.3 All sample bags and litter removed from drill sites.
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PRESCRIBED ACTIVITY NOT APPLICABLE
APPLICABLEREQUIRED COMPLETED AUDITED
1.4.4 Sulphide material in any pit backfilled and covered with 1m of benign, lowpermeability material.
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1.5 Topsoil Utilisation1.5.1 All areas of significant disturbance stripped of topsoil and/or surface material
useful for regeneration or revegetation be immediately reused, or stockpiled in a way which maintains the biological and nutrient quality.
1.5.2 Stripped material spread over all disturbed areas as a rooting medium for the revegetation process.
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1.6 Revegetation1.6.1 All disturbed areas allowed to regenerate or be revegetated on completion of
use.
1.6.2 Vegetation similar to adjacent vegetation established on all revegetation areas.
1.6.3 Suitable nutrient conditions provided for all plantings using fertiliser if necessary.
1.6.4 All revegetation processes continued until the potential for vegetation development to a similar extent as in undisturbed land established.
1.6.5 Stock proof fencing erected where necessary.
1.6.7 Appropriate vegetation cover restored.
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1.7 Water Storage Structures1.7.1 Pits and excavations containing water for beneficial use as agreed by the
landowner not backfilled.
1.7.2 All excavations to remain after termination of tenure left with safe and stable access for livestock/native fauna and complying with any landowner agreement.
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1.8 Contaminated Land1.8.1 Contamination of land avoided.
1.8.2 Any contaminated land occurring as a result of activities remediated so that there is no risk of hazard to public health and the environment.
1.8.3 Weed importation and weed succession avoided.
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2. WATER MANAGEMENT1.9 Natural Waters √
1.9.1 Clean storm water diverted away from disturbed areas.
1.9.2 Removal of riparian material limited to 500kg/km of water course.
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PRESCRIBED ACTIVITY NOT APPLICABLE
APPLICABLEREQUIRED COMPLETED AUDITED
2.1.3 Clearing of riparian vegetation limited to 500km2 at any one location and placed not to foul water courses.
2.1.4 Surface, ground or coastal water impacts managed in conformity with the Environmental Protection Policy for Water.
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2.2 Waste and Waste Water Containment2.2.3 All waste oil and grease removed off-site for recycling or disposal.
2.2.4 All domestic waste and effluents managed in accordance with local health requirements.
2.2.5 All liquid/slurry waste containments (including fuel tank spillage bunds and process water ponts) have a volume at least equal to the design volume (volume of fuel tank, process water volume, tailings volume, etc.) PLUS an additional 10% of that volume.
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2.3 Storm Water Treatment2.3.3 Storm water treatment using silt traps or silt fences installed where necessary.
2.3.4 Storm water treatment silt traps maintained at least annually.
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3. SOCIAL3.1 Informed all personnel and contractors of environmental requirements. √ √
3.2 Noise nuisance to the public and sensitive wildlife managed in conformity with theEnvironmental Protection Policy for Noise.
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3.3 Dust nuisance to the public managed in conformity with the Environmental Protection Policy
for Air.
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3.4 Vibration and light nuisance to the public minimised. √3.5 Disruption to any native title rights and interests minimised. √4. ENVIRONMENTALLY SENSITIVE AREAS
Site specific conditions for impacts to nature conservation and community cultural, historicand landscape values and sites, etc., developed through consultation with Department of Minerals and Energy and the relevant administering authority.
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5. LANDHOLDERS (Voluntary)5.1 Consulted with landholders prior to commencing activities, including site visit where possible.
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5.2 Notified landholder of significant water in drill holes and/or excavations and requested advise
on whether to backfill or leave open.
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5.3 Inspected sites with landholder prior to rehabilitation to establish specific requirements. √5.4 Inspected rehabilitated sites with landholder 3 to 6 months after wet season. √
PRESCRIBED ACTIVITY NOT APPLICABLE
APPLICABLEREQUIRED COMPLETED AUDITED
6. PHOTOGRAPHIC RECORD (Voluntary)6.1 Prior to activity. √6.2 Immediately after activity. √6.3 Rehabilitated site 3 to 6 months after wet season. √