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23 AUGUST 2017 DUST IN AGRICULTURE AIR QUALITY AND DUST 2 DUST IN - - PowerPoint PPT Presentation
23 AUGUST 2017 DUST IN AGRICULTURE AIR QUALITY AND DUST 2 DUST IN - - PowerPoint PPT Presentation
FARMERS MEETING - PETERSVILLE AGRICULTURE WORKING GROUP MEETING AIR QUALITY / DUST, GROUNDWATER, SURFACE WATER AGRICULTURE AND SURROUNDING LANDOWNERS 23 AUGUST 2017 DUST IN AGRICULTURE AIR QUALITY AND DUST 2 DUST IN AGRICULTURE RISK
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RISK ASSESSMENT
- Dust Sources
- Haul Roads
- In pit activities
- TSF Construction
- Dust Modelling
- Well below license conditions
- DPC and EPA reviewed
previous modelling & set licence conditions
- Maximum level at a receptor
- ccurs when tailings dam
height increase construction
DUST IN AGRICULTURE
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LICENCE CONDITIONS
Summary of air quality compliance criteria
Substance Criteria Units Averaging Period Reference PM10 50 µg/m3 24 hoursa Hillside Mine ML Air NEPM PM2.5 25 µg/m3 24 hours Hillside Mine ML NEPM advisory reporting standard PM2.5 8c µg/m3 24 hours NEPM advisory reporting standard TSP 120 µg/m3 24 hours Hillside Mine ML TSP 90 µg/m3 12 months Hillside Mine ML TDDd 2 g/(m2 month) 30 days (for annual average) Hillside Mine ML TDD 4 g/(m2 month) 12 months Hillside Mine ML
DUST IN AGRICULTURE
TDD – Total Dust Deposited is most relevant to agriculture
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CONTROL MEASURES
- Haul road material and
construction.
- Minimise disturbed areas.
- Progressively rehabilitate land.
- Water trucks and sprays.
- Modify operations – change mining
- r dumping locations.
- Risk management – predict high
risk conditions and plan operations accordingly.
- Early warning monitoring and
- perational adjustment.
DUST IN AGRICULTURE
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MONITORING
Compliance Monitoring:
- Dust onto & off the site.
- PM10 and TSP.
- PM2.5 for one year to evaluate levels.
- Dust deposition monitoring.
Early Warning Monitoring:
- Additional operational monitoring
within the site close to sources for
- perational management.
- Informs operations of dust trends.
- Alerts triggered.
- Additional controls or changes to
- peration.
DUST IN AGRICULTURE
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MONITORING PLAN
Monitoring network:
- Focus on monitoring near
receptors (residences).
- Measure concentrations of PM10,
TSP & PM2.5 and dust deposition.
- Locations - considering prevailing
wind directions (including seasonal).
DUST IN AGRICULTURE
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DUST DEPOSITION GAUGES DUST IN AGRICULTURE
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GROUND WATER
GROUND WATER AND ADJACENT AGRICULTURE
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GROUNDWATER MANAGEMENT AND MONITORING PLAN
HYDROGEOLOGY
- Groundwater occurs in fractured basement rocks - basement rock aquifer.
- Basement rock aquifer fresh to partially weathered.
- Overlain by saprolitic (weathered) zone clays – confining layer.
- Overlain by Tertiary age sediments – unsaturated (no aquifer).
- Covered by topsoil.
- Rain falling on YP infiltrates through the soil.
- Water that has moved past the root zone then sits on top of the saprolite
zone.
- Then may infiltrate down into the formations over a long period of time,
eventually reaching the basement aquifer.
- Basement groundwater is saline to hypersaline – not used by agriculture
- Moves very slowly from west to east.
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GROUNDWATER MANAGEMENT AND MONITORING PLAN
GEOLOGICAL CROSS SECTION
Farmers get “first use” of rainfall
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GROUNDWATER MANAGEMENT AND MONITORING PLAN
HYDROGEOLOGY – BASEMENT AQUIFER WATER ELEVATIONS PRE-MINING
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GROUNDWATER MANAGEMENT AND MONTORING PLAN
OUTCOMES
Strategies:
- calibrated basement ground water model;
- ngoing calibration of the transient ground water model using data obtained
from groundwater monitoring;
- ngoing calibration of the pit lake geochemistry and hydrogeological
models using data obtained from operational monitoring;
- monitoring of process plant functions, including tank levels, flow rates,
pressures and fluid quantities;
- groundwater monitoring – depth and quality
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HYDROGEOLOGY – MODELLED BASEMENT AQUIFER WATER ELEVATIONS AFTER 5 YEARS OF OPERATION
GROUNDWATER MANAGEMENT AND MONTORING PLAN
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GROUNDWATER MANAGEMENT AND MONITORING PLAN
DEFINITIONS
Parameters to be monitored:
- Depth to water or standing water level (SWL) – in metres below
ground or a reference point.
- SWL converted to water elevations AHD (approximate sea level).
- Water quality – Salinity, pH, Calcium, Magnesium, Potassium,
Sodium, Sulphate, Chloride, Nitrate, Arsenic, Boron, Chromium, Cobalt, Copper, Iron, Manganese, Zinc, Antimony, Uranium, Total recoverable hydrocarbons (TRH) – 1 site only.
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GROUNDWATER MANAGEMENT AND MONITORING PLAN
LEADING GROUNDWATER CRITERIA
Baseline monitoring data – groundwater (to be updated prior to mining operations)
STATISTIC Chloride (mg/L) EC (µS/cm) pH
- Diss. Arsenic
- Diss. Boron
Diss. Cadmium
- Diss. Copper
- Diss. Zinc
Min 9200 30000 6.2 0.001 1.7 0.0002 0.001 0.002 Max 58000 150000 7.8 0.05 5.5 0.0045 2.8 0.44 Average 21500 63000 7.11 0.01 3.82 0.001 0.244 0.24 AV+ 2SD 47469 127589 5.43* 0.034 6.05 0.002 1.453 0.182
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PROPOSED MONITORING LOCATIONS
GROUNDWATER MANAGEMENT AND MONITORING PLAN Summary
- No water table or unconfined aquifer
- Basement aquifer confined by
saprolite – low permeability
- Cone of depression of basement
aquifer only
- Basement aquifer saline to
hypersaline – no agricultural use
- Farmers get first use of rainfall
- Dewatering of basement aquifer does
not impact available soil water
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SURFACE WATER
SUFACE WATER AND ADJACENT AGRICULTURE
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SURFACE WATER MANAGEMENT AND MONTORING PLAN
CURRENT LAND SURFACE - BASELINE CATCHMENT MODEL (1 IN A 100 YEAR FLOOD IN 6 HOURS)
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SURFACE WATER MANAGEMENT AND MONTORING PLAN
END OF MINE MODEL (1 IN A 100 YEAR FLOOD IN 6 HOURS)
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SURFACE WATER MANAGEMENT AND MONTORING PLAN
MANAGEMENT OF SURFACE WATER DURING OPERATIONS
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REPORTING
SURFACE WATER MANAGEMENT AND MONITORING PLAN
- Key stakeholders will have access to relevant groundwater monitoring
data.
- These include Rex Minerals, State and Local government agencies,
and the local community.
- The Hillside Mine will report on the performance of the Surface Water
Management Plan in the Annual Compliance Report (ACR), provide regular updates to members of the HMCV consultation group, and made available for public information on the Rex Minerals website.
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