Queensland Mining Approvals IndexMining Capital Funds

Data as at 14 September 2026 · from the Queensland EP Act public register

Coal environmental authority

EPML00963013 · STANMORE SMC PTY LTD

Coal environmental authority EPML00963013 (STANMORE SMC PTY LTD), Granted. 149 conditions indexed. Holds PRC plan P-PRCP-100680336.

Status
Granted
Holders
STANMORE SMC PTY LTD
Tenures
ML4749; ML70116
PRC plan
P-PRCP-100680336 · effective 2025-07-24
How it was read
Numbered conditions
Register
Register record · Instrument PDF

Conditions

149 numbered conditions read from the current instrument. Page numbers link into the register PDF.

  1. A1

    This environmental authority authorises environmental harm referred to in the conditions. Where there is no condition or this environmental authority is silent on a matter, the lack of a condition or silence does not authorise environmental harm.

  2. A2

    Prevent and /or minimise likelihood of environmental harm In carrying out the environmentally relevant activities, the environmental authority holder must take all reasonable and practicable measures to prevent and/or to minimise the likelihood of environmental harm being caused. Any environmentally relevant activity, that, if carried out incompetently, or negligently, may cause environmental harm, in a manner that could have been prevented, shall be carried out in a proper manner in accordance with the conditions of this environmental authority.

  3. A3

    Maintenance of measures, plant and equipment The environmental authority holder must ensure: a) that all measures, plant and equipment necessary to ensure compliance with the conditions of this environmental authority are installed; b) that such measures, plant and equipment are maintained in a proper condition; c) that such measures, plant and equipment are operated in a proper manner; and d) that all instruments and devices used for the measurement or monitoring of any parameter under any condition of this environmental authority are properly calibrated.

    page 5Monitoring and reporting
  4. A4

    Monitoring and records Except where specified otherwise in another condition of this environmental authority, all monitoring records and reports required by this environmental authority must be kept for a period of not less than five (5) years.

    page 5Monitoring and reporting
  5. A5

    Monitoring and determinations required under any condition of this environmental authority must be conducted by an appropriately qualified person.

    page 5Monitoring and reporting
  6. A6

    Upon request from the administering authority, copies of monitoring results, records, registers, management plans and reports required by the conditions of this environmental authority must be made available and provided to the administering authority within ten (10) business days or an alternative timeframe agreed between the administering authority and the environmental authority holder.

    page 5Monitoring and reporting
  7. A7

    Notification of emergencies, incidents and exceptions The environmental authority holder must notify the administering authority by written notification within twenty-four (24) hours after becoming aware of any emergency or incident that results in the release of contaminants not in accordance, or reasonably expected to be not in accordance, with the conditions of this environmental authority. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 5Monitoring and reporting
  8. A8

    Within ten (10) business days following the initial notification under condition A7, or the receipt of monitoring results associated with the notification made under condition A7, whichever is the latter, the environmental authority holder must provide further written advice to the administering authority, including the following: a) results and interpretation of any samples taken and analysed; b) outcomes of actions taken at the time to prevent or minimise unlawful environmental harm; and c) proposed actions to prevent a recurrence of the emergency or incident.

    page 6Monitoring and reporting
  9. A9

    Complaints The environmental authority holder must record all environmental complaints received about the mining activities, including: a) name, address and contact number of the complainant; b) time and date of complaint; c) reasons for the complaint; d) investigations undertaken; e) conclusions formed; f) actions taken to resolve the complaint, including the use of appropriate dispute resolution if required; g) any abatement measures implemented; and h) person responsible for resolving the complaint.

    page 6Monitoring and reporting
  10. A10

    A register of alternative arrangements must be established and maintained by the environmental authority holder. The register must include: a) the location to which the alternative arrangement applies; b) the period of the alternative arrangement; c) details about the particular environmental nuisance impact or impacts the arrangement is for; and d) details about the mitigation measures, where relevant.

  11. A11

    Monitoring on request When requested by the administering authority, the environmental authority holder must investigate any nuisance, or contaminant release, or environmental harm, or complaint that is neither frivolous nor vexatious in the opinion of the authorised person, by: a) undertaking the monitoring specified by the administering authority; b) undertaking the monitoring in the timeframe nominated or agreed to by the administering authority; c) completing an analysis and interpretation of the monitoring results; and d) implementing abatement measures, where required.

    page 6Monitoring and reporting
  12. A12

    The results of the investigation undertaken in accordance with condition A11 must be provided to the administering authority within twenty (20) business days of completion of the monitoring timeframe in accordance with condition A11(b), or a longer timeframe agreed to by the administering authority. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 6Monitoring and reporting
  13. A13

    Coal extraction rate The environmental authority holder is approved for a coal extraction rate of up to seven and a half (7.5) million tonnes per annum (mtpa) of run-of-mine (ROM) ore in accordance with this environmental authority.

  14. A14

    Authorised disturbance Surface disturbance by mining activities is authorised within areas marked "Approved surface disturbance" in Figure 1 (Authorised Surface and Sub-Surface Disturbance Areas).

  15. A15

    Sub-surface disturbance by mining activities is authorised within areas marked as "Approved sub- surface disturbance" in Figure 1 (Authorised Surface and Sub-Surface Disturbance Areas).

  16. A16

    Highwall Mining disturbance is not authorised within the area marked as "Restricted Highwall Mining Zone" in Figure 1 (Authorised Surface and Sub-Surface Disturbance Area).

  17. A17

    Any disturbance outside of the areas marked "Authorised surface disturbance" in Figure 1 (Authorised Surface and Sub-Surface Disturbance Areas): a) is only authorised to the extent reasonably necessary for roads, fences, underground services, low-impact telecommunications facilities, electrical sub-stations, transmission grid works and supply network works, storage depots, similar minor infrastructure and ancillary facilities for any of the above listed minor infrastructure; and b) must not result in significant residual impact to prescribed environmental matters. Permit Environmental Authority EPML00963013 - Poitrel Mine Schedule B: Air Condition Condition number

  18. B1

    Odour nuisance The release of noxious or offensive odour or any other noxious or offensive airborne contaminant resulting from the mining activities must not cause an environmental nuisance, at any sensitive place or commercial place.

  19. B2

    If the administering authority determines odour released from the mining activities to constitute an environmental nuisance, the environmental authority holder must immediately implement abatement measures so that emissions from the mining activities do not result in further environmental nuisance.

  20. B3

    Dust nuisance The release of dust or particulate matter or both resulting from the mining activities must not cause an environmental nuisance, at any sensitive place or commercial place.

  21. B4

    Monitoring of dust and particulate matter resulting from the mining activities, undertaken in accordance with condition A11, must be carried out at a place relevant to the potentially affected sensitive place or commercial place and must not exceed the following levels when measured at any sensitive place or commercial place: a) dust deposition, measured as total insoluble matter, of 120 milligrams per square metre per day, averaged over one month, when monitored in accordance with the most recent version of Australian Standard AS3580.10.1 Methods for sampling and analysis of ambient air - Determination of particulate matter - Deposited matter - Gravimetric method. b) a concentration of particulate matter with an aerodynamic diameter of less than 10 micrometres (PM10) suspended in the atmosphere of 50 micrograms per cubic metre over a 24-hour averaging time, when monitored in accordance with the most recent version of either: i. Australian Standard AS3580.9.6 Methods for sampling and analysis of ambient air - Determination of suspended particulate matter - PM10 high volume sampler with size selective inlet - Gravimetric method; or ii. Australian Standard AS3580.9.8 Methods for sampling and analysis of ambient air - Determination of suspended particulate matter - PM10 continuous direct mass method using a tapered element oscillating microbalance analyser; or iii. Australian Standard AS3580.9.9 Methods for sampling and analysis of ambient air - Determination of suspended particulate matter - PM10 low volume sampler - Gravimetric method; or iv. Australian Standard AS3580.9.11 Methods for sampling and analysis of ambient air - Determination of suspended particulate matter - PM10 beta attenuation monitors. NOTE: Exceedances due to events that cannot be managed by the environmental authority holder, such as bushfires, fuel reduction burning for fire management purposes or dust storms, would not be considered to be in breach of condition B4 if the environmental authority holder can demonstrate that the exceedance was caused by such events.

    page 8Air, Monitoring and reporting
  22. B5

    If monitoring, undertaken in accordance with condition A11, indicates exceedance of the relevant limits in condition B4, the environmental authority holder must immediately implement abatement measures so that emissions from the mining activities do not result in further environmental nuisance. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 8Monitoring and reporting
  23. B6

    Monitoring of ambient weather conditions A weather station for continuous representative monitoring and recording of wind direction and wind speed must be installed and operated on the mining leases.

    page 9Monitoring and reporting
  24. B7

    Dust deposition monitoring Dust deposition monitoring must be carried out in accordance with Table B1 (Dust Deposition Monitoring), to confirm the modelling prediction that operations will not result in a significant increase in dust levels. NOTE: Monitoring must be carried out in accordance with Australian Standard AS3580.10.1 Methods for sampling and analysis of ambient air - Determination of particulate matter - Deposited matter - Gravimetric method.

    page 9Air, Monitoring and reporting
  25. B8

    Air Quality Management Plan An Air Quality Management Plan must be developed and implemented by an appropriately qualified person by 31 March 2021.

  26. B9

    The Air Quality Management Plan required by condition B8 must include: a) an air quality monitoring program for PM10 and dust deposition; b) a Trigger Action Response Plan; and c) a requirement for 2-yearly review and update. Table B1 (Dust Deposition Monitoring) Air Quality Determination Monitoring Points Frequency Olive Downs Residence Monthly Particulate matter deposition rate in Winchester Downs Residence milligrams per square metre per day (averaged over one month) Permit Environmental Authority EPML00963013 - Poitrel Mine Schedule C: Noise and Vibration Condition Condition number

    page 9Air, Noise and vibration, Monitoring and reporting
  27. C1

    Noise nuisance Noise from the mining activities must not cause an environmental nuisance, at any sensitive place or commercial place.

    page 10Noise and vibration
  28. C2

    Noise is not considered an environmental nuisance under condition C1 if monitoring shows that noise does not exceed the limits in Table C1 (Noise Limits) at any sensitive place or commercial place.

    page 10Noise and vibration, Monitoring and reporting
  29. C3

    Noise monitoring Noise monitoring, undertaken in accordance with condition A11, must comply with the most recent version of the administering authority's Noise Measurement Manual, and must include the following descriptors, characteristics and conditions: a) LA eq, adj, 1 hour; b) LA 1, adj, 10 mins; c) the level and frequency of occurrence of impulsive or tonal noise; d) atmospheric conditions including wind speed and direction; e) effects due to extraneous factors such as traffic noise; and f) location, date and time of recording.

    page 10Noise and vibration, Monitoring and reporting
  30. C4

    If monitoring, undertaken in accordance with condition A11, indicates exceedance of the relevant limits in Table C1 (Noise Limits), the environmental authority holder must immediately implement abatement measures so that emissions from the mining activities do not result in further environmental nuisance. Table C1 (Noise Limits) Monday to Sunday (including public holidays) Noise Level Day Evening Night dB(A) (7am to 6pm) (6pm to 10pm) (10pm to 7am) LA eq, adj, 1 hour Sensitive Place LA1, adj, 10 mins 40 40 35 LA eq, adj, 1 hour 50 50 45 Commercial Place 50 50 50 Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 10Noise and vibration, Monitoring and reporting
  31. C5

    Vibration nuisance Vibration from the mining activities must not cause an environmental nuisance, at any sensitive place or commercial place.

    page 11Noise and vibration
  32. C6

    Vibration is not considered an environmental nuisance under condition C5 if monitoring shows that vibration does not exceed the limits specified in Table C2 (Vibration Limits).

    page 11Noise and vibration, Monitoring and reporting
  33. C7

    Airblast overpressure nuisance The airblast overpressure level from blasting operations on the mining leases must not cause an environmental nuisance, at any sensitive place or commercial place.

    page 11Noise and vibration
  34. C8

    Airblast overpressure is not considered an environmental nuisance under condition C7 if monitoring shows that airblast overpressure does not exceed the levels specified in Table C3 (Airblast Overpressure Level).

    page 11Noise and vibration, Monitoring and reporting
  35. C9

    Vibration and/or airblast overpressure monitoring Vibration and/or airblast overpressure monitoring, undertaken in accordance with condition A11, must comply with the most recent version of the administering authority's Noise Measurement Manual, and must include the following descriptors, characteristics and conditions: a) location of the blast within the mining area (including which bench level); b) atmospheric conditions including temperature, relative humidity and wind speed and direction; and c) location, date and time of recording.

    page 11Noise and vibration, Monitoring and reporting
  36. C10

    If monitoring, undertaken in accordance with condition A11, indicates exceedance of the relevant limits in Table C2 (Vibration Limits) or Table C3 (Airblast Overpressure Level), the environmental authority holder must immediately implement abatement measures so that emissions from the mining activities do not result in further environmental nuisance. Location Table C2 (Vibration Limits) Sensitive place or commercial place Vibration Measured 5 mm/s peak particle velocity for nine (9) out of ten (10) consecutive blasts and not greater than 10 mm/s peak particle velocity at any time. Table C3 (Airblast Overpressure Level) Location Airblast Overpressure Measured Sensitive place or commercial place 115 dB (Linear peak) for nine (9) out of ten (10) consecutive blasts and not greater than 120 dB (Linear peak) at any time. Permit Environmental Authority EPML00963013 - Poitrel Mine Schedule D: Waste Condition Condition number

    page 11Noise and vibration, Waste, Monitoring and reporting
  37. D1

    Waste management The holder of this Environmental Authority must develop, document and implement a waste management program for all mining activities at the licensed place. The program must include: a) a description of the mining activity that may generate waste; and b) waste management control strategies including: i. recording of the types and amounts of wastes generated by the mining activity; ii. segregation of the wastes; iii. storage of the wastes; iv. transport of the wastes; v. disposal of waste including leachate management; and vi. monitoring and reporting matters concerning the waste; and c) the hazard characteristics of the wastes generated including disposal procedures for regulated wastes; and d) a program for reusing, recycling or disposing of all wastes; and e) how the waste will be dealt with in accordance with the waste and resource management hierarchy, including a description of the types and amounts of waste that will be dealt with under each of the waste management practices in the waste management hierarchy (i.e. avoidance, reuse, recycling, energy recovery, disposal); and f) how the waste will be stored, handled and transferred in a proper and effective manner; and g) procedures for identifying and implementing opportunities to minimise the amount of waste generated, promote efficiency in the use of resources and improve the waste management practices employed; and h) procedures for dealing with accidents, spills, and other incidents that may impact on waste management; and i) how often the performance of the waste management practices will be assessed; and j) indicators or other criteria on which the performance of the waste management practices will be assessed; and k) staff training and induction to the waste management program; and l) a system for regular review; and m) be updated at intervals of no greater than 5 years.

    page 12Waste, Monitoring and reporting
  38. D2

    The environmental authority holder must submit the Waste Management Program required by condition D1 to the administering authority: a) upon request; and/or b) prior to commencing a new process, or varying an existing process, for reprocessing any waste. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 12Waste
  39. D3

    Waste receipt The only waste permitted to be received is: a) the types of waste specified in Table D1 (Mining Waste) and b) sewage and sludge for treatment in accordance with Schedule H: Sewage Treatment; and c) from Red Mountain Infrastructure CHPP (EPML00819113), South Walker Creek Coal Mine (EPML00712313), Isaac Downs Coal Mine (EA0002817), Isaac Plains Coal Mine (EPML00932713), Millennium Coal Mine (EPML00819213) and Vulcan Coal Mine (EA0002912).

    page 13Waste
  40. D4

    Waste reprocessing The only waste permitted to be reprocessed is: a) spoil or overburden; b) vegetation; c) water or sediment containing hydrocarbons; d) fuels, oils, lubricants and coolants; e) bulk rubber; f) inert waste; g) poly-pipe and other plastic; h) fibreglass; i) treated and untreated timber; and j) asphalt.

    page 13Waste, Land and soil, Biodiversity
  41. D5

    Waste disposal Unless otherwise specified in Table D1 (Mining Waste), waste, other than spoil or overburden or vegetation removed as part of the mining activity, must not be disposed of within the mining leases listed on this environmental authority and must be taken to a facility that is lawfully allowed to accept such waste under the provisions of the Environmental Protection Act 1994. Waste type Permit Environmental Authority EPML00963013 - Poitrel Mine Table D1 (Mining Waste) Authorised Disposal Location Rejects and sediment containing Spoil emplacements hydrocarbons Regulated structures in accordance with Schedule G: Tailings and water or sediment containing Structures of this environmental authority hydrocarbons Pits and voids Dedicated rejects emplacements Temporarily stored in structures in the overburden for the purpose of dewatering/ evaporation prior to being disposed as rejects in accordance with this Table. Bulk rubber, inert waste, polypipe and other In pits or voids plastics, fibreglass, treated and untreated In spoil emplacements; and timber, asphalt, and asbestos. Left in situ below ground level; Permit Environmental Authority EPML00963013 - Poitrel Mine Schedule E: Land Condition Condition number

    page 13Regulated structures, Waste, Land and soil, Biodiversity
  42. E1

    Topsoil Topsoil must be strategically stripped ahead of mining in accordance with a Topsoil Management Plan.

    page 15Land and soil
  43. E2

    A topsoil inventory, which identifies the topsoil requirements for rehabilitation and availability of suitable topsoil on site, must be provided with any Estimated Rehabilitation Cost application.

    page 15Rehabilitation, Land and soil
  44. E3

    PRCP schedule Progressive rehabilitation of the disturbed land must be carried out in accordance with the approved Progressive Rehabilitation and Closure Plan (PRCP) schedule P-PRCP-100680336 for this environmental authority.

    page 15Rehabilitation
  45. E4

    Surrender The holder must meet the conditions and the rehabilitation milestones under the PRCP schedule P- PRCP-100680336 prior to the surrender of the environmental authority.

    page 15Rehabilitation
  46. E5

    Preventing contaminant release to land Contaminants must not be released to land in manner that constitutes a nuisance, material harm or serious environmental harm.

  47. E6

    Storage and handling of chemicals and flammable or combustible liquids All chemicals and flammable or combustible liquids must be stored and handled in accordance with the most recent version of an Australian Standard where such is applicable. Where no relevant Australian Standard exists, store such materials within an effective on-site containment system.

  48. E7

    Impacts to Prescribed Environmental Matters Significant residual impacts to prescribed environmental matters, other than if the impacts were authorised by an existing authority issued before the commencement of the Environmental Offsets Act 2014, are not authorised under this environmental authority or the Environmental Offsets Act 2014 unless the impact is specified in Table E2 (Significant Residual Impacts to Prescribed Environmental Matters) and Figure 2 (Ground-truthed Regulated Vegetation and Regional Ecosystems).

    page 15Biodiversity
  49. E8

    Records demonstrating that each impact to a prescribed environmental matter not listed in Table E2 (Significant Residual Impacts to Prescribed Environmental Matters) did not, or is not likely to, result in a significant residual impact to that matter must be: a) completed by an appropriately qualified person; and b) kept for the life of the environmental authority. Permit Environmental Authority EPML00963013 - Poitrel Mine Table E2 (Significant Residual Impacts to Prescribed Environmental Matters) Prescribed Environmental Matter Maximum Extent of Impact Environmental Offset Required Regulated Vegetation Endangered regional ecosystem - 11.4.9 Endangered regional ecosystem - 11.4.8 142ha2 No1 Endangered regional ecosystem - 11.3.1 Protected Wildlife Habitat Habitat for an animal that is vulnerable wildlife - Geophaps scripta scripta -- Squatter 310.2ha No1 Pigeon (southern) NOTE: 1 Offsets for these values are to be offset under the EPBC Poitrel Mine Approval 2004/1770 2 156ha of regulated vegetation has been offset under EPBC Poitrel Mine Approval 2004/1770. Permit Environmental Authority EPML00963013 - Poitrel Mine Schedule F: Water Condition Condition number

    page 15Biodiversity, Monitoring and reporting
  50. F1

    Contaminant Release Contaminants that will or have the potential to cause environmental harm must not be released directly or indirectly to any waters as a result of the mining activities, except as permitted under the conditions of this environmental authority.

  51. F2

    Unless otherwise permitted under the conditions of this environmental authority, the release of mine affected water to waters must only occur from the release points specified in Table F1 (Mine Affected Water Release Points).

    page 17Surface water
  52. F3

    The release of mine affected water to internal water management infrastructure that is installed and operated in accordance with a Water Management Plan that complies with conditions F33 to F37 inclusive is permitted. Table F1 (Mine Affected Water Release Points) Release Easting Northing Mine Affected Water Monitoring Point Receiving Waters Point (GDA94) (GDA94) Source and Location Description (RP) 630315 7557024

    page 17Surface water, Monitoring and reporting
  53. F4

    Notwithstanding condition F2 of this environmental authority, the release of mine affected water to waters from RP3 is not permitted until the environmental authority holder amends this environmental authority to include: a) the location details for RP3 in Table F1 (Mine Affected Water Release Points, Sources and Receiving Waters); b) the location details for RP3 in Table F2 (Mine Affected Water Release Limits); c) the location details of Sediment Dam 4 in Table F5 (Onsite Water Storage Monitoring); and d) the location details of MP6 in Table F8 (Receiving Water Upstream Background Sites and Downstream Monitoring Points).

    page 17Surface water, Regulated structures, Land and soil, Monitoring and reporting
  54. F5

    The release of mine affected water to waters in accordance with condition F2 must not exceed the release limits stated in Table F2 (Mine Affected Water Release Limits) when measured at the monitoring points specified in Table F1 (Mine Affected Water Release Points) for each quality characteristic. Permit Environmental Authority EPML00963013 - Poitrel Mine Table F2 (Mine Affected Water Release Limits) Quality Characteristic Release Limit Monitoring Frequency 1 Comment Electrical Conductivity Release limit specified in Daily during release (the first (-S/cm) Table F4 for variable flow sample must be taken within criteria. 2 hours or as soon as practicable of commencement of release) pH 6.5 (minimum) Daily during release (the first (pH units) 9.0 (maximum) sample must be taken within 2 hours or as soon as practicable of commencement of release) Daily during release (the first Turbidity 2 sample must be taken within Turbidity is required to assess (NTU) 500 2 hours or as soon as ecosystem impacts and can practicable of provide instantaneous results. commencement of release) At commencement and prior Suspended solids are Suspended Solids * N/A to cessation of release (at a required to measure the (mg/L) minimum) and weekly during performance of erosion and release. sediment control measures. Sulphate (SO42-) Release limit specified in At commencement and prior Drinking water environmental (mg/L) Table F4 for variable flow to cessation of release (at a values from NHMRC 2006 minimum) and weekly during guidelines or ANZECC. criteria. release. NOTES: * Limit for suspended solids can be omitted if turbidity limit is included. Limit for turbidity not required if suspended solids limit included. Both indicators should be measured in all cases. 1 While all endeavours are taken to collect the necessary data, manual sampling work will not be conducted in the event of unsafe access to locations or infrastructure. Should such access limitations arise, the administering authority will be notified as soon as practicable. 2 Insufficient historical analysis of suspended solid concentration prevents the establishment of a site specific trigger. Future monitoring of

    page 17Surface water, Land and soil, Monitoring and reporting
  55. F6

    The release of mine affected water to waters from the release points must be monitored at the locations specified in Table F1 (Mine Affected Water Release Points) for each quality characteristic and at the frequency specified in Table F2 (Mine Affected Water Release Limits) and Table F3 (Release Contaminant Trigger Investigation Levels). NOTE: the administering authority will take into consideration any extenuating circumstances prior to determining an appropriate enforcement response in the event condition F6 is contravened due to a temporary lack of safe or practical access. The administering authority expects the environmental authority holder to take all reasonable and practicable measures to maintain safe and practical access to designated monitoring locations. Permit Environmental Authority EPML00963013 - Poitrel Mine Table F3 (Release Contaminant Trigger Investigation Levels) Quality Characteristic Trigger Comment of Trigger Level Monitoring Level Frequency (-g/L) Aluminium 55 For aquatic ecosystem protection, based on SMD guideline Arsenic 13 For aquatic ecosystem protection, based on SMD guideline Cadmium 0.2 For aquatic ecosystem protection, based on SMD guideline Chromium 1 For aquatic ecosystem protection, based on SMD guideline Copper 2 For aquatic ecosystem protection, based on LOR for ICPMS Iron 300 For aquatic ecosystem protection, based on low reliability guideline Lead 4 For aquatic ecosystem protection, based on SMD guideline Mercury Nickel 0.2 For aquatic ecosystem protection, based on LOR for CV FIMS 11 For aquatic ecosystem protection, based on SMD guideline Zinc 8 For aquatic ecosystem protection, based on SMD guideline Commencement Boron 370 For aquatic ecosystem protection, based on SMD guideline of release and Cobalt 90 For aquatic ecosystem protection, based on low reliability guideline thereafter weekly Manganese 1900 For aquatic ecosystem protection, based on SMD guideline during release Molybdenum 34 For aquatic ecosystem protection, based on low reliability guideline Selenium 10 For aquatic ecosystem protection, based on LOR for ICPMS Silver 1 For aquatic ecosystem protection, based on LOR for ICPMS Uranium 1 For aquatic ecosystem protection, based on LOR for ICPMS Vanadium 10 For aquatic ecosystem protection, based on LOR for ICPMS Ammonia 900 For aquatic ecosystem protection, based on SMD guideline Nitrate 1100 For aquatic ecosystem protection, based on ambient Qld WQ Petroleum hydrocarbons (C6-C9) 20 Guidelines (2006) for TN

    page 18Surface water, Monitoring and reporting
  56. F7

    If quality characteristics of the release exceed any of the trigger levels specified in Table F3 (Release Contaminant Trigger Investigation Levels) during a release event, the environmental authority holder must compare the downstream results in the receiving waters to the trigger values specified in Table F3 (Release Contaminant Trigger Investigation Levels) and: (1) where the trigger values are not exceeded then no action is to be taken; or (2) where the downstream results exceed the trigger values specified in Table F3 (Release Contaminant Trigger Investigation Levels) for any quality characteristic, compare the results of the downstream site to the data from background monitoring sites and; (a) if the result is less than the background monitoring site data, then no action is to be taken; or (b) if the result is greater than the background monitoring site data, complete an investigation into the potential for environmental harm and provide a written report to the administering authority in the next annual return, outlining: i. details of the investigations carried out; and ii. actions taken to prevent environmental harm. NOTE: Where an exceedance of a trigger level has occurred and is being investigated, in accordance with condition F7(2)(b), no further reporting is required for subsequent trigger events for that quality characteristic.

    page 20Surface water, Monitoring and reporting
  57. F8

    If an exceedance in accordance with condition F7(2)(b) is identified, the environmental authority holder must notify the administering authority within twenty-four (24) hours of receiving the result.

    page 20Monitoring and reporting
  58. F9

    Mine Affected Water Release Events The environmental authority holder must ensure a stream flow gauging station is installed, operated and maintained to determine and record stream flows at the locations and flow recording frequency specified in Table F4 (Mine Affected Water Release During Flow Events).

    page 20Surface water, Monitoring and reporting
  59. F10

    Notwithstanding any other condition of this environmental authority, the release of mine affected water to waters in accordance with condition F2 must only take place during periods of natural flow events in accordance with the receiving water flow criteria for discharge specified in Table F4 (Mine Affected Water Release During Flow Events) for the release point specified in Table F1 (Mine Affected Water Release Points).

    page 20Surface water
  60. F11

    The release of mine affected water to waters in accordance with condition F2 must not exceed the Electrical Conductivity and Sulphate release limits or the Maximum Release Rate (for all combined release point flows) for each receiving water flow criteria for discharge specified in Table F4 (Mine Affected Water Release During Flow Events) when measured at the monitoring points specified in Table F1 (Mine Affected Water Release Points).

    page 20Surface water, Monitoring and reporting
  61. F12

    The daily quantity of mine affected water released from each release point must be measured and recorded at the monitoring points in Table F1 (Mine Affected Water Release Points).

    page 20Surface water, Monitoring and reporting
  62. F13

    Releases to waters must be undertaken so as not to cause erosion of the bed and banks of the receiving waters, or cause a material build-up of sediment in such waters. Permit Environmental Authority EPML00963013 - Poitrel Mine Table F4 (Mine Affected Water Release During Flow Events) Receiving Release Gauging Gauging Gauging Receiving Receiving Maximum Electrical Conductivity and Sulphate waters Point Station Station Station Water Flow Water Flow Release Release Limits Northing Recording Criteria for Rate (RP) Easting (GDA94) Frequency Discharge (GDA94) (for all 7556405 (m3/s) combined RP flows) Isaac River RP1, Isaac River 627831 Continuous Low Flow Maximum Electrical conductivity 720 -S/cm

    page 20Surface water, Land and soil
  63. F14

    Notification of release event The environmental authority holder must notify the administering authority via WaTERS as soon as practicable and no later than twenty-four (24) hours after commencing to release mine affected water to the receiving environment. The release commencement notification must include the submission of written advice to the administering authority of the following information: a) release commencement date and time; b) expected release cessation date and time; c) release point; d) release rate; e) receiving water including the natural flow rate; and f) any details (including available data) regarding likely impacts on the receiving water.

    page 22Surface water, Monitoring and reporting
  64. F15

    The environmental authority holder must notify the administering authority via WaTERS as soon as practicable and no later than twenty-four (24) hours after cessation of a release event notified under condition F14. The release cessation notification must include the submission of written advice to the administering authority of the following information: a) release cessation date and time; b) receiving water including the natural flow rate; and c) volume of water released. NOTE: Successive or intermittent releases occurring within twenty-four (24) hours of the cessation of any individual release can be considered part of a single release event and do not require individual notification for the purpose of compliance with conditions

    page 22Surface water, Monitoring and reporting
  65. F14

    and F15 and F16, provided the relevant details of the release are included within the notification provided in accordance with conditions F14 and F15 and F16.

    page 22Monitoring and reporting
  66. F16

    Within twenty-eight (28) days of notification under condition F15, the environmental authority holder must provide the administrating authority via WaTERS the following information in writing: a) confirmation of: i. the release commencement date and time; ii. the release cessation date and time; iii. receiving water including the natural flow rate; iv. volume of water released; b) all in-situ and laboratory water quality monitoring results; c) details regarding the compliance of the release with the conditions of Schedule F: Water of this environmental authority (i.e. contamination limits, natural flow, discharge volume); d) whether the release of water resulted in any impacts to the receiving environment; and e) any other matter pertinent to the water release event.

    page 22Surface water, Monitoring and reporting
  67. F17

    Notification of release event exceedance If the release limits defined in Table F2 (Mine Affected Water Release Limits) are exceeded, the environmental authority holder must notify the administering authority within twenty-four (24) hours of receiving the results. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 22Surface water, Monitoring and reporting
  68. F18

    The environmental authority holder must, within twenty-eight (28) days of the notification provided in accordance with condition F17, provide a report to the administering authority via WaTERS detailing: a) the reason for the release; b) the location of the release; c) the total volume of the release and which (if any) part of this volume was non-compliant; d) the total duration of the release and which (if any) part of this period was non-compliant; e) all water quality monitoring results; f) any general observations; g) all calculations; and h) any other matters pertinent to the water release event.

    page 23Monitoring and reporting
  69. F19

    Monitoring of Water Storage Quality Water storages stated in Table F5 (Onsite Water Storage Monitoring) which are associated with the release points must be monitored for the water quality characteristics specified in Table F6 (Onsite Water Storage Contaminant Limits) at the monitoring locations and at the monitoring frequency specified in Table F5 (Onsite Water Storage Monitoring).

    page 23Surface water, Monitoring and reporting
  70. F20

    In the event that water storages defined in Table F5 (Onsite Water Storage Monitoring) exceed the contaminant limits defined in Table F6 (Onsite Water Storage Contaminant Limits), the environmental authority holder must implement measures, where practicable, to prevent access to waters by all livestock. Table F5 (Onsite Water Storage Monitoring) Water Storage Easting Northing Monitoring Location Monitoring Description (GDA94) (GDA94) Frequency At pump inlet - mixed sample over depth profile Sediment Dam 1 630088 7561371 At pump inlet - western embankment of dam Quarterly Sediment Dam 2 629918 7560183 Sediment Dam 3 630303 7557057 At release gates - mixed sample over depth profile Sediment Dam 4 TBA TBA TBA Permit Environmental Authority EPML00963013 - Poitrel Mine Table F6 (Onsite Water Storage Contaminant Limits) Quality Characteristic Units Test Value Contaminant Limit pH pH units Range Greater than 4, less than 92 Electrical Conductivity -S/cm Maximum 59701 Sulphate mg/L Maximum 10001 Fluoride mg/L Maximum 21 Aluminium mg/L Maximum 51 Arsenic mg/L Maximum 0.51 Cadmium mg/L Maximum 0.011 Cobalt mg/L Maximum 11 Copper mg/L Maximum 11 Lead mg/L Maximum 0.11 Nickel mg/L Maximum 11 Zinc mg/L Maximum 201 NOTES: Total measurements (unfiltered) must be taken and analysed 1 Contaminant limit based on ANZECC & ARMCANZ (2000) stock water quality guidelines. 2 Page 4.2-15 of ANZECC & ARMCANZ (2000) "Soil and animal health will not generally be affected by water with pH in the range of 4-9".

    page 23Regulated structures, Land and soil, Monitoring and reporting
  71. F21

    Receiving Environment Monitoring and Contaminant Trigger Levels The quality of the receiving waters must be monitored at the locations specified in Table F8 (Receiving Water Upstream Background and Downstream Monitoring Points) for each quality characteristic and at the monitoring frequency stated in Table F7 (Receiving Waters Contaminant Trigger Levels) and Table F3 (Release Contaminant Trigger Investigation Levels).

    page 24Surface water, Monitoring and reporting
  72. F22

    If quality characteristic of the receiving water at the downstream monitoring point MP3 exceed any of the trigger levels specified in Table F7 (Receiving Waters Contaminant Trigger Levels) during a release event the environmental authority holder must compare the downstream results to the upstream results in the receiving waters and: (1) where the downstream result is the same or a lower value than the upstream value for the quality characteristic then no action is to be taken; or (2) where the downstream results exceed the upstream results, complete an investigation into the potential for environmental harm and provide a written report to the administering authority in the next annual return, outlining: (a) details of the investigations carried out; and (b) actions taken to prevent environmental harm. NOTE: Where an exceedance of a trigger level has occurred and is being investigated in accordance with F22(2) of this condition, no further reporting is required for subsequent trigger events for that quality characteristic. Permit Environmental Authority EPML00963013 - Poitrel Mine Table F7 (Receiving Waters Contaminant Trigger Levels) Quality Characteristic Trigger Level Monitoring Frequency3 pH 6.5 to 8.5 (pH units) Electrical Conductivity 1000 (-S/cm) Turbidity 750 Daily during the release (the first sample (NTU) TBA1 must be taken within 2 hours or as soon Suspended Solids as practicable of commencement of (mg/L) release) Sulphate (SO42-) 250 (mg/L) Sodium TBA2 (mg/L) NOTES: 1 Insufficient historical analysis of suspended solid concentration prevents the establishment of a site specific trigger. Future monitoring of suspended solid concentrations will enable a trigger level to be determined. Turbidity is proposed to be used as a surrogate in the interim. 2 Insufficient analysis of sodium concentration prevents the establishment of a site specific trigger. Future monitoring of sodium concentrations will enable a trigger level to be determined. 3 While all endeavours are taken to collect the necessary data, manual sampling work will not be conducted in the event of unsafe access to locations or infrastructure. Should such access limitations arise, the administering authority will be notified as soon as practicable.

    page 24Surface water, Monitoring and reporting
  73. MP5

    Isaac River - 4760m upstream of the confluence of New Chum 627831 7556405 Creek and Isaac River Downstream Monitoring Points

    page 25Monitoring and reporting
  74. MP3

    Isaac River - 3000m downstream of the confluence of New Chum 633694 7552809 Creek and Isaac River NOTES: (a) Requires only in situ samples taken using electronic sampling equipment. (b) Data obtained from MP4 and MP2 are for information purposes only and is not subject to condition F22. (c) The upstream monitoring point should be within 5km of the release point (New Chum Creek confluence with Isaac River). (d) The downstream point should not be greater than 4km from the release point (New Chum Creek confluence with Isaac River). (e) The data from background monitoring points must not be used where they are affected by releases from other mines. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 25Surface water, Monitoring and reporting
  75. F23

    Receiving Environment Monitoring Program (REMP) The environmental authority holder must develop and implement a Receiving Environment Monitoring Program (REMP) to monitor, identify and describe any adverse impacts to surface water environmental values, quality and flows due to the authorised mining activity. This must include monitoring the effects of the mine on the receiving environment periodically (under natural flow conditions) and while mine affected water is being discharged from the site. For the purposes of the REMP, the receiving environment is the waters of the Isaac River and connected or surrounding waterways within fifteen (15) kilometres downstream of the release. The REMP should encompass any sensitive receiving waters or environmental values downstream of the authorised mining activity that will potentially be directly affected by an authorised release of mine affected water.

    page 26Surface water, Monitoring and reporting
  76. F24

    The REMP must: a) assess the condition or state of receiving waters, including upstream conditions, spatially within the REMP area, considering background water quality characteristics based on accurate and reliable monitoring data that takes into consideration temporal variation (e.g. seasonality); b) be designed to facilitate assessment against water quality objectives for the relevant environmental values that need to be protected; c) include monitoring from background reference sites (e.g. upstream or background) and downstream sites from the release (as a minimum, the locations specified in Table F8 (Receiving Water Upstream Background and Downstream Monitoring Points)); d) specify the frequency and timing of sampling required in order to reliably assess ambient conditions and to provide sufficient data to derive site specific background reference values in accordance with the Queensland Water Quality Guidelines 2009. This should include monitoring during periods of natural flow irrespective of mine or other discharges; e) include monitoring and assessment of dissolved oxygen saturation, temperature and all water quality parameters listed in Table F2 (Mine Affected Water Release Limits) and Table F3 (Release Contaminant Trigger Investigation Levels)); f) include, where appropriate, monitoring of metals/metalloids in sediments (in accordance with ANZECC & ARMCANZ 2000, BATLEY and/or the most recent version of AS5667.1 Guidance on Sampling of Bottom Sediments); g) include, where appropriate, monitoring of macroinvertebrates in accordance with the AusRivas methodology, h) apply procedures and/or guidelines from ANZECC & ARMCANZ 2000 and other relevant guideline documents; i) describe sampling and analysis methods and quality assurance and control; and j) incorporate stream flow and hydrological information in the interpretations of water quality and biological data.

    page 26Surface water, Land and soil, Monitoring and reporting
  77. F25

    A REMP Design Document that addresses each criterion presented in conditions F23 and F24 must be maintained. Due consideration must be given to any comments made by the administering authority on the REMP Design Document and subsequent implementation of the REMP. Permit Environmental Authority EPML00963013 - Poitrel Mine

  78. F26

    A report outlining the findings of the REMP, including all monitoring results and interpretations in accordance with conditions F23 and F24 must be prepared annually. This report must include the following: a) an assessment of background reference water quality; b) the condition of downstream water quality compared against water quality objectives; and c) the suitability of current discharge limits to protect downstream environmental values.

    page 27Monitoring and reporting
  79. F27

    Water reuse Mine affected water may be piped or trucked or transferred by some other means that does not contravene the conditions of this environmental authority and deposited into artificial water storage structures, such as farm dams or tanks, or used directly at properties owned by the environmental authority holder or a third party for the purpose of: a) supplying stock water subject to compliance with the quality release limits specified in Table F9 (Stock Water Release Limits); or b) supplying irrigation water subject to compliance with quality release limits in Table F10 (Irrigation Water Release Limits); or c) supplying water for construction and/or road maintenance in accordance with the conditions of this environmental authority. Table F9 (Stock Water Release Limits) Quality Characteristic Units Minimum Maximum pH pH units 6.5 8.5 -S/cm N/A 5000 Electrical Conductivity Table F10 (Irrigation Water Release Limits) Maximum Quality Characteristic 8.5 pH Units Minimum pH units 6.5 Site specific value determined Electrical Conductivity in accordance with ANZECC -S/cm N/A & ARMCANZ (2000) Irrigation Guidelines

    page 27Surface water, Regulated structures
  80. F28

    Mine affected water may be piped or trucked or transferred by some other means that does not contravene the conditions of this environmental authority and deposited into artificial water storage structures, such as dams or tanks, for the purpose of supplying water to any operation licensed for either

    page 27Surface water, Regulated structures
  81. F29

    If the responsibility for mine affected water is given or transferred to another person in accordance with conditions F27 or F28: a) the responsibility for the mine affected water must only be given or transferred in accordance with a written agreement (the third party agreement); and b) the third party agreement must include a commitment from the person utilising the mine affected water to use it in such a way as to prevent environmental harm or public health incidents and specifically make the persons aware of the General Environmental Duty (GED) under section 319 of the Environmental Protection Act 1994, environmental sustainability of the water disposal and protection of environmental values of waters; and c) the third party agreement must be signed by both parties to the agreement.

    page 28Surface water
  82. F30

    Water general All determinations of water quality and biological monitoring must be: a) performed by a person or body possessing appropriate experience and qualifications to perform the required measurements; b) made in accordance with methods prescribed in the latest edition of the administering authority's Monitoring and Sampling Manual; c) collected from the monitoring locations identified within this environmental authority, within ten hours of each other where possible; d) carried out on representative samples; and e) analysed at a laboratory accredited (e.g. NATA) for the method of analysis being used. Note: Condition F30 requires the Monitoring and Sampling Manual to be followed and where it is not followed because of exceptional circumstances this should be explained and reported with the results.

    page 28Monitoring and reporting
  83. F31

    The release of any contaminants as permitted by this environmental authority, directly or indirectly to waters, other than internal water management infrastructure that is installed and operated in accordance with a Water Management Plan that complies with conditions F33 to F37 inclusive: a) must not produce any visible discolouration of receiving waters; and b) must not produce any slick or other visible or odorous evidence of oil, grease or petrochemicals nor contain visible floating oil, grease, scum, litter or other objectionable matter.

    page 28Surface water
  84. F32

    Annual water monitoring reporting The following information must be recorded in relation to all water monitoring required under the conditions of this environmental authority and submitted to the administering authority in the specified format with each annual return: a) the date on which the sample was taken; b) the time at which the sample was taken; c) the monitoring point at which the sample was taken; d) the measured or estimated daily quantity of mine affected water released from all release points; e) the release flow rate at the time of sampling for each release point; f) the results of all monitoring and details of any exceedances of the conditions of this environmental authority; and g) water quality monitoring data must be provided to the administering authority in the specified electronic format upon request. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 28Surface water, Monitoring and reporting
  85. F33

    Water Management Plan A Water Management Plan must be developed by an appropriately qualified person and implemented for all mining activities.

  86. F34

    The Water Management Plan required by condition F33 must: a) provide for effective management of actual and potential environmental impacts resulting from water management associated with the mining activity carried out under this environmental authority; and b) be developed in accordance with administering authority's guideline Preparation of water management plans for mining activities and include: i. a study of the source of contaminants; ii. a water balance model for the site; iii. a water management system for the site; iv. measures to manage and prevent saline drainage; v. measures to manage and prevent acid rock drainage; vi. contingency procedures for emergencies; and vii. a program for monitoring and review of the effectiveness of the Water Management Plan.

    page 29Monitoring and reporting
  87. F35

    The Water Management Plan required by condition F33 must be reviewed each calendar year and a report prepared by an appropriately qualified person. The report must: a) assess the plan against the requirements under condition F34; b) include recommended actions to ensure actual and potential environmental impacts are effectively managed for the coming year; and c) identify any amendments made to the Water Management Plan following the review.

    page 29Monitoring and reporting
  88. F36

    The environmental authority holder must attach to the review report required by condition F35 a written response to the report and recommended actions, detailing the actions taken or to be taken by the environmental authority holder on stated dates: a) to ensure compliance with this environmental authority; and b) to prevent a recurrence of any non-compliance issues identified.

    page 29Monitoring and reporting
  89. F37

    The review report required by condition F35 and the written response to the review report required by condition F36 must be submitted to the administering authority with the subsequent annual return under the signature of the appointed signatory for the annual return.

    page 29Monitoring and reporting
  90. F38

    Saline drainage The environmental authority holder must ensure proper and effective measures are taken to avoid or otherwise minimise the generation and/or release of saline drainage.

  91. F39

    Acid rock drainage The environmental authority holder must ensure proper and effective measures are taken to avoid or otherwise minimise the generation and/or release of acid rock drainage.

  92. F40

    Permit F41 Environmental Authority EPML00963013 - Poitrel Mine F42

  93. F43

    Stormwater and water sediment controls

    page 30Surface water, Land and soil
  94. G1

    Assessment of consequence category The consequence category of any structure must be assessed by a suitably qualified and experienced person, in accordance with the most recent version of the Manual for Assessing Consequence Categories and Hydraulic Performance of Structures, at the following times: a) prior to the design and construction of the structure, if it is not an existing structure; or b) prior to any change in its purpose or the nature of its stored contents.

    page 31Regulated structures
  95. G2

    A consequence assessment report and certification must be prepared for each structure assessed and the report may include a consequence assessment for more than one structure.

    page 31Monitoring and reporting
  96. G3

    Certification must be provided by the suitably qualified and experienced person who undertook the assessment, in the form set out in the most recent version of the Manual for Assessing Consequence Categories and Hydraulic Performance of Structures.

    page 31Regulated structures
  97. G4

    Design and construction of a regulated structure Conditions G5 to G9 inclusive do not apply to existing structures. NOTE: Construction of a dam includes modification of an existing dam - see definitions.

    page 31Regulated structures
  98. G5

    All regulated structures must be designed by, and constructed under the supervision of, a suitably qualified and experienced person in accordance with the requirements of the most recent version of the Manual for Assessing Consequence Categories and Hydraulic Performance of Structures. NOTE: Certification of design and construction may be undertaken by different persons.

    page 31Regulated structures
  99. G6

    Construction of a regulated structure is prohibited unless the environmental authority holder has submitted a consequence category assessment report and certification to the administering authority has been certified by a suitably qualified and experienced person for the design and design plan and the associated operating procedures in compliance with the relevant condition of this environmental authority.

    page 31Regulated structures, Monitoring and reporting
  100. G7

    Certification must be provided by the suitably qualified and experienced person who oversees the preparation of the design plan in the form set out in the most recent version of the Manual for Assessing Consequence Categories and Hydraulic Performance of Structures, and must be recorded in the Register of Regulated Structures. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 31Regulated structures
  101. G8

    Regulated structures must: a) be designed and constructed in accordance with and conform to the requirements of the most recent version of the Manual for Assessing Consequence Categories and Hydraulic Performance of Structures; b) be designed and constructed with due consideration given to ensuring that the design integrity would not be compromised on account of: i. floodwaters from entering the regulated dam from any watercourse or drainage line; and ii. wall failure due to erosion by floodwaters arising from any watercourse or drainage line. c) for regulated dams associated with a failure to contain - seepage, have the floor and sides of the dam designed and constructed to prevent or minimise the passage of the wetting front and any entrained contaminants through either the floor or sides of the dam during the operational life of the dam and for any period of decommissioning and rehabilitation of the dam.

    page 32Rehabilitation, Surface water, Regulated structures, Land and soil
  102. G9

    Certification by the suitably qualified and experienced person who supervises the construction must be submitted to the administering authority on the completion of construction of the regulated structure, and state that: a) the 'as constructed' drawings and specifications meet the original intent of the design plan for that regulated structure; and b) construction of the regulated structure is in accordance with the design plan.

    page 32Regulated structures
  103. G10

    Operation of a regulated structure Operation of a regulated structure, except for an existing structure, is prohibited unless the environmental authority holder has submitted to the administering authority: a) one paper copy and one electronic copy of the design plan and certification of the `design plan' in accordance with condition G6; b) a set of `as constructed' drawings and specifications; c) certification of those `as constructed drawings and specifications' in accordance with condition G9; d) where the regulated structure is to be managed as part of an integrated containment system for the purpose of sharing the DSA volume across the system, a copy of the certified system design plan; e) the requirements of this environmental authority relating to the construction of the regulated structure have been met; f) the environmental authority holder has entered the details, required under this environmental authority, into the Register of Regulated Structures; and g) there is a current operational plan for the regulated structures.

    page 32Regulated structures
  104. G11

    For existing structures that are regulated structures: a) where the existing structure that is a regulated structure is to be managed as part of an integrated containment system for the purpose of sharing the DSA volume across the system, the environmental authority holder must submit to the administering authority within twelve (12) months of the commencement of this condition a copy of the certified system design plan including that structure; and b) there must be a current operational plan for the existing structures. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 32Regulated structures
  105. G12

    Each regulated structure must be maintained and operated, for the duration of its operational life until decommissioned and rehabilitated, in a manner that is consistent with the current operational plan and, if applicable, the current design plan and associated certified `as constructed' drawings.

    page 33Rehabilitation, Regulated structures
  106. G13

    Mandatory Reporting Level Conditions G14 to G17 inclusive only apply to regulated structures which have not been certified as low consequence category for `failure to contain - overtopping'.

    page 33Regulated structures, Monitoring and reporting
  107. G14

    The Mandatory Reporting Level (the MRL) must be marked on a regulated dam in such a way that, during routine inspections of that dam, it is clearly observable.

    page 33Regulated structures, Monitoring and reporting
  108. G15

    The environmental authority holder must, as soon as practical and within forty-eight (48) hours of becoming aware, notify the administering authority when the level of the contents of a regulated dam reaches the MRL.

    page 33Regulated structures, Monitoring and reporting
  109. G16

    The environmental authority holder must immediately on becoming aware that the MRL has been reached, act to prevent the occurrence of any unauthorised discharge from the regulated dam.

    page 33Regulated structures
  110. G17

    The environmental authority holder must record any changes to the MRL in the Register of Regulated Structures.

    page 33Regulated structures, Monitoring and reporting
  111. G18

    Design Storage Allowance The environmental authority holder must assess the performance of each regulated dam or linked containment system over the preceding November to May period based on actual observations of the available storage in each regulated dam or linked containment system taken prior to 1 July of each year.

    page 33Regulated structures
  112. G19

    By 1 November of each year, storage capacity must be available in each regulated dam (or network of linked containment systems with a shared DSA volume), to meet the Design Storage Allowance (DSA) volume for the dam (or network of linked containment systems).

    page 33Regulated structures
  113. G20

    The environmental authority holder must notify the administering authority as soon as possible and within forty-eight (48) hours of becoming aware that the regulated dam (or network of linked containment systems) will not have the available storage to meet the DSA volume on 1 November of any year.

    page 33Regulated structures, Monitoring and reporting
  114. G21

    The environmental authority holder must, immediately on becoming aware that a regulated dam (or network of linked containment systems) will not have the available storage to meet the DSA volume on 1 November of any year, act to prevent the occurrence of any unauthorised discharge from the regulated dam or linked containment systems.

    page 33Regulated structures
  115. G22

    Annual inspection report Each regulated structure must be inspected each calendar year by a suitably qualified and experienced person. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 33Regulated structures, Monitoring and reporting
  116. G23

    At each annual inspection, the condition and adequacy of all components of the regulated structure must be assessed and a suitably qualified and experienced person must prepare an annual inspection report containing details of the assessment and include recommended actions to ensure the integrity of the regulated structure.

    page 34Regulated structures, Monitoring and reporting
  117. G24

    The suitably qualified and experienced person who prepared the annual inspection report must certify the report in accordance with the most recent version of the Manual for Assessing Consequence Categories and Hydraulic Performance of Structures.

    page 34Regulated structures, Monitoring and reporting
  118. G25

    The environmental authority holder must: a) within twenty (20) business days of receipt of the annual inspection report, provide to the administering authority: i. the recommendations section of the annual inspection report; and ii. if applicable, any actions being taken in response to those recommendations; and b) if, following receipt of the recommendations and (if applicable) actions, the administering authority requests a full copy of the annual inspection report from the environmental authority holder, provide this to the administering authority within ten (10) business days of receipt of the request.

    page 34Monitoring and reporting
  119. G26

    Transfer arrangements The environmental authority holder must provide a copy of any reports, documentation and certifications prepared under this environmental authority, including but not limited to any Register of Regulated Structures, consequence assessment, design plan and other supporting documentation, to a new holder on transfer of this authority.

    page 34Regulated structures, Monitoring and reporting
  120. G27

    Register of Regulated Structures A Register of Regulated Structures must be established and maintained by the environmental authority holder for each regulated structure.

    page 34Regulated structures
  121. G28

    The environmental authority holder must provisionally enter the required information in the Register of Regulated Structures when a design plan for a regulated structure is submitted to the administering authority.

    page 34Regulated structures
  122. G29

    The environmental authority holder must make a final entry of the required information in the Register of Regulated Structures once compliance with condition G10 and G11 has been achieved.

    page 34Regulated structures
  123. G30

    The environmental authority holder must ensure that the information contained in the Register of Regulated Structures is current and complete on any given day.

    page 34Regulated structures
  124. G31

    All entries in the Register of Regulated Structures must be approved by the chief executive officer for the environmental authority holder, or their delegate, as being accurate and correct.

    page 34Regulated structures
  125. G32

    The environmental authority holder must, at the same time as providing the annual return, supply to the administering authority a copy of the records contained in the Register of Regulated Structures, in the electronic format required by the administering authority. Permit Environmental Authority EPML00963013 - Poitrel Mine

    page 34Regulated structures, Monitoring and reporting
  126. G33

    Transitional arrangements All existing structures that have not been assessed in accordance with either, the Manual or the former Manual for Assessing Hazard Categories and Hydraulic Performance of Dams, must be assessed and certified in accordance with the Manual within six (6) months of amendment of the environmental authority adopting this schedule.

    page 35Regulated structures
  127. G34

    All existing structures must subsequently comply with the timetable for any further assessments in accordance with the Manual specified in Table G1 (Transitional Requirements for Existing Structures), depending on the consequence category for each existing structure assessed in the most recent previous certification for that structure.

    page 35Regulated structures
  128. G35

    Table G1 (Transitional Requirements for Existing Structures) ceases to apply for a structure once any of the following events has occurred: a) it has been brought into compliance with the hydraulic performance criteria applicable to the structure under the Manual; or b) it has been decommissioned; or c) it has been certified as no longer being assessed as a regulated structure.

    page 35Regulated structures
  129. G36

    Certification of the transitional assessment required by G35 and G36 (as applicable) must be provided to the administering authority within six (6) months of amendment of the environmental authority adopting this schedule. Table G1 (Transitional Requirements for Existing Structures) Transition period required for existing structures to achieve the requirements of the most recent version of the Manual for Assessing Consequence Categories and Hydraulic Performance of Structures Compliance with Criteria High Significant Low >90% and a history of good No transition required No transition required No transitional conditions compliance performance in apply. Review consequence assessment every 7 years. last 5 years >70% to 90% Within 7 years, unless Within 10 years, unless No transitional conditions otherwise agreed with the otherwise agreed with the apply. Review consequence assessment every 7 years. administering authority, administering authority, based on no history of based on no history of unauthorised releases. unauthorised releases. 50 to 70% Within 5 years unless Within 7 years unless Review consequence otherwise agreed with the otherwise agreed with the assessment every 7 years. administering authority, administering authority, based on no history of based on no history of unauthorised releases. unauthorised releases. 50% Within 5 years or as per Within 5 years or as per Review consequence compliance requirements compliance requirements assessment every 5 years. (e.g. TEP timing) (e.g. TEP timing) Permit Environmental Authority EPML00963013 - Poitrel Mine Schedule H: Sewage Treatment Condition Condition number

    page 35Regulated structures
  130. H1

    Treated sewage effluent The cumulative total daily peak design capacity of the sewage treatment plant/s must not exceed 1500 equivalent persons (EP). Small package plants and/or septic systems, each with a daily peak design capacity less than 21EP, are not included in the cumulative total daily peak design capacity.

  131. H2

    Treated sewage effluent must not be directly released from the sewage treatment plant/s to any waters. Note: `waters' does not include structures associated with the mine affected water management system.

    page 36Surface water
  132. H3

    Treated sewage effluent may be: a) released to the mine affected water management system for mixing with other mine affected water; b) released to land via a sub-surface infiltration trench; c) irrigated or sprayed for dust suppression or firefighting or evaporation; or d) removed as waste.

    page 36Surface water, Air, Waste
  133. H4

    Treated sewage effluent that is released in accordance with condition H3(a) and has mixed with other mine affected water must be managed as mine affected water in accordance with the conditions of this environmental authority.

    page 36Surface water
  134. H5

    Treated sewage effluent that is released in accordance with condition H3(b) or H3(c) must be carried out in a manner such that: a) vegetation is not damaged; b) there is no surface ponding of effluent; and c) there is no run-off of treated sewage effluent to waters.

    page 36Biodiversity
  135. H6

    Treated sewage effluent released in accordance with condition H3(a) or H3(b) or H3(c) from any sewage treatment plant that has a daily peak design capacity of greater than 21EP must be monitored: a) at the point where the treated sewage effluent is released from the sewage treatment plant/s; b) for the quality characteristics specified in Table H1 (Treated Sewage Effluent Monitoring Requirements); and c) at the frequency specified in Table H1 (Treated Sewage Effluent Monitoring Requirements). Permit Environmental Authority EPML00963013 - Poitrel Mine Table H1 (Treated Sewage Effluent Monitoring Requirements) Quality Characteristic Units Monitoring Frequency 5-day Biochemical Oxygen Demand (uninhibited) mg/L pH pH units Monthly Colonies per 100mL Monthly Thermotolerant coliforms Monthly Total nitrogen mg/L Monthly mg/L Monthly Total phosphorus

    page 36Monitoring and reporting
  136. H7

    If treated sewage effluent is being released in accordance with condition H3(c): a) the results of monitoring in accordance with condition H6 must not exceed the release limits specified in Table H2 (Treated Sewage Effluent Contaminant Release Limits); and b) the release must not cause spray drift or over spray to any sensitive place or commercial place.

    page 37Monitoring and reporting
  137. H8

    If the release limits specified in Table H2 (Treated Sewage Effluent Contaminant Release Limits) are exceeded in accordance with condition H7(a), the environmental authority holder must notify the administering authority in accordance with conditions A7 and A8. Table H2 (Treated Sewage Effluent Contaminant Release Limits) Quality Characteristic Release Limit Units Limit Type 50 mg/L Maximum 5-day Biochemical Oxygen Demand (uninhibited) pH units pH 6.0 to 9.0 Colonies per 100mL Range 1000 Maximum Thermotolerant coliforms, based on the average of a minimum of five samples collected Permit Environmental Authority EPML00963013 - Poitrel Mine Schedule I: Groundwater Condition Condition number

    page 37Groundwater, Monitoring and reporting
  138. I1

    The holder of this environmental authority must not release contaminants to groundwater.

    page 38Groundwater
  139. I2

    Groundwater Monitoring and Management Program A Groundwater Monitoring and Management Program must be: a) developed by an appropriately qualified person; and b) implemented by the environmental authority holder for all stages of mining activities.

    page 38Groundwater, Monitoring and reporting
  140. I3

    The Groundwater Monitoring and Management Program required by condition I2 must: a) identify potential groundwater impacts due to the mining activities; b) include a site conceptual groundwater model; c) describe the sampling and monitoring methodology; d) detail an appropriate quality assurance and quality control program; and e) provide the process for notifying the administering authority and investigating exceedances in accordance with conditions I4-I5.

    page 38Groundwater, Monitoring and reporting
  141. I4

    Groundwater Monitoring Groundwater quality and standing water levels must be monitored: a) at the locations and at the frequencies specified in Table I1 - Groundwater Monitoring Program; and b) for the quality characteristics specified in Table I2 - Groundwater Trigger Levels.

    page 38Groundwater, Monitoring and reporting
  142. I5

    If the groundwater level or contaminant triggers defined in Table I2 - Groundwater Trigger Levels are exceeded on three (3) consecutive monitoring occasions, then the environmental authority holder must notify the administering authority via WaTERS within twenty-four hours of receiving the results.

    page 38Groundwater, Monitoring and reporting
  143. I6

    Trigger investigation If monitoring results from the compliance bores specified in Table I1 - Groundwater Monitoring Program, exceed any of the groundwater level or contaminant triggers defined in Table I2 - Groundwater Trigger Levels on three (3) consecutive sampling occasions the environmental authority holder must complete an investigation within fourteen (14) days of receiving the results to determine if the exceedance is a result of: a) activities authorised under this environmental authority; or b) natural variation; or c) neighbouring land use resulting in groundwater impacts.

    page 38Groundwater, Monitoring and reporting
  144. I7

    The holder of this environmental authority must provide a report of the investigation to the administering authority via WaTERS within fourteen (14) days of completion of the investigation under condition I6. Permit Environmental Authority EPML00963013 - Poitrel Mine

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  145. I8

    If the investigation under condition I6 determines that the three (3) consecutive exceedances were the result of activities authorised under this environmental authority, then a further investigation must be completed within twenty-eight (28) days of provision of the report under I7. The investigation must determine the source, cause and extent of contamination (environmental harm) and implement appropriate mitigation and management measures to address any groundwater contamination and prevent recurrence of groundwater contamination. The further investigation report must be provided to the administering authority via WaTERS within twenty-eight (28) days of completion.

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  146. I9

    An appropriately qualified person must review the Groundwater Monitoring and Management Program and prepare a review report every two (2) calendar years. The review report must: a) analyse the results of groundwater monitoring to: i. describe any impacts to groundwater levels and groundwater quality due to the mining activity; ii. determine trends in groundwater levels and groundwater quality; b) assess any differences between the groundwater level impact predicted and actual impacts for corresponding periods in the most current numerical groundwater model; and c) provide recommendations to the environmental authority holder to address the findings of parts (a) and (b) of the review.

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  147. I10

    Within twenty (20) business days of receiving the review report required by condition I9, the environmental authority holder must provide to the administering authority: a) the review report; b) if applicable, any actions being taken by the environmental authority holder to address the recommendations of the review report; and c) if action is not being taken to address a recommendation, the environmental authority holder must provide justification for not taking action.

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  148. I11

    Annual groundwater monitoring data must be submitted to the administering authority via WaTERS by 30 September each calendar year.

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  149. I12

    Bore construction The construction, management, maintenance and decommissioning of groundwater monitoring bores must be undertaken in a manner that: a) prevents contaminants entering the groundwater; b) ensures the integrity of the bores to obtain representative groundwater samples from the target aquifer; and c) maintains the hydrogeological environment within the aquifer. Permit Environmental Authority EPML00963013 - Poitrel Mine Table I1 - Groundwater Monitoring Program Monitoring Hydrogeological Surface RL Screened Location (GDA94) Monitoring Bore unit (mAHD) interval RL (mbg) Frequency Easting Northing

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