ANNEXURE "B"
ISSUE ENVIRONMENTAL CONCERN FOLLOW UP ACTION DECISION RESOLUTION/ACTION
I requested further advice from TGM regarding the characteristics of residual cyanide in the irrigation water (Exhibit DD-15). I concluded that the very low levels of stable cyanide in irrigation water were not a significant threat to environment. I concluded that the guiding licence commitment of no cyanide from premise was maintained.
Residual cyanide levels in irrigation water Possible toxicity in the environment I received advice (Exhibit DD-23, Pg 7, para 1) that analysis of samples taken from the raw water pond indicated no detectable free or WAD cyanide and average levels of total cyanide of 0.023 mg/l in stable cyano-complex with cobalt. I requested and received advice from EPA Science regarding toxicity of cyanide. I noted that the ANZECC guideline to protect aquatic ecosystems is 0.005 mg/l free cyanide (Exhibit DD-17). I included a condition in the Variation that prohibited irrigation that caused runoff or ponding in the forest area.
I noted advice regarding possible natural sources of cyanide in environment (Exhibit DD-17) and that analysis by TGM (Exhibit DD-23, Pg11. Para 6) of leachate from soil samples indicated levels of total and WAD cyanide. I ensured that advanced irrigation practices were included in the proposals. I ensured that the monitoring requirements of the Variation for surface and groundwater included analysis for all forms of cyanide.
I therefore concluded that this issue would not cause a significant increase in the environmental impact of the activity authorised or controlled by the Licence.
I checked "as built" details for Raw Water Dam. I was satisfied that transfer of the treated stormwater to the raw water pond was the best environmental outcome.
I confirmed that the raw water dam has single HDPE liner (Exhibit DD-5a). I concluded that the low levels of residual elements in the water presented no significant risk to the environment.
Treated wastewater in raw water dam Possible overflows from the raw water and to surface waters and leakage to groundwater I reviewed the analysis of the quality of water transferred and stored in Raw Water Dam (Exhibit DD-23, Pg 6). I ensured that the discharge conditions for the Raw Water Dam remained in force in the Licence.
I noted the direction from Dept of Mineral Resources on 22 March 2000 to Ross Mining to transfer water from the Storm Water Dam to the Raw Water Dam (Exhibit DD-14a). I concluded that no further action was required.
I noted that TGM had not breached any condition of the Licence. I concluded that this issue would not cause a significant increase in the environmental impact of the activity authorised or controlled by the Licence.
I noted the following reports and assessments:
· Greenloaning Biostudies Pty Ltd, s5A Assessment of impacts of the trial irrigation Area on Flora and Fauna, March 2000 (Exhibit DD-14);
· Dept of Mineral Resources "Environmental Impact Assessment Report" for the Pt 5, EP&A Act development application to grant the Mining Lease Applications No's 4 and 5 Inverell (ML 1386) (Exhibit DD-39a);
· Decision of Minister for Mineral Resources to grant Mining Lease Application 4 & 5 Inverell and conditions of Authority for ML 1386 especially noting the "special conditions" included in the Mining lease in regard to fauna & flora (Exhibit DD-39a, "Decision of the Minister for Mineral Resources");
· NPWS Director General's Recommendations Report for the proposed Poverty Point Timbarra Gold Mining Project to Minister for the Environment regarding the Minister for Mineral's decision to grant the Mining Lease Applications Nos' 4 and 5 Inverell (Exhibit DD-39a, Appendix No. 4); I concluded on the basis of the material I reviewed, that the variation would have no significant effect on threatened species, populations or ecological communities or their habitats.
· Threatened Species Management Plan, Timbarra Gold Project (Exhibit DD-39b, Appendix H); I ensured that extensive monitoring and reporting of soils, vegetation, surface and gorundwaters would be included in the trial.
Impacts on threatened species Risks to threatened species populations or ecological communities or habitats. · Timbarra Gold Project, Mine Lease Extension, Species Impact Statement, March 1999ERM Mitchell McCotter Pty Ltd (Exhibit DD-39). I ensured t hat benchmark groundwater and soils characteristics were analysed before the trial.
I noted that NPWS determined in their recommendations to the Minister for the Environment that the Fauna Impact Statement prepared for the Timbarra Gold Mining Project (Pt 5, EP&A Act development application to grant the Mining Lease Applications Nos' 4 and 5 Inverell) was considered a Species Impact Statement under the transitional provisions for the Threatened Species Conservation Act (1995) and the Threatened Species Conservation (Savings and transitional) regulation 1996 (Exhibit DD-39a, Appendix No.4, Pg2). I supported NPWS advice that the monitoring frequency for the Threatened Species Management Plan would continue at the mining site.
I noted the details proposed for irrigation operations (eg irrigation scheduling, monitoring of soil moisture) (Exhibit DD-10, Pg 10). I therefore concluded that this issue would not cause a significant increase in the environmental impact of the activity authorised or controlled by the Licence.
I noted irrigation would be scheduled to ensure it did not cause runoff from the proposed irrigation in the forest area (Exhibit DD-9, Pg 5).
I noted NPWS advice in their letter to Dept of Mineral Resources dated 5 April 2000 (Exhibit DD-18). NPWS raised no concerns in regard to threatened species impacts from the proposal. NPWS did indicate a preference for irrigation within cells 11-20 and that the trial be for 4ha with a possibility of extension provided Dept of Mineral resources was satisfied with monitoring results.
I was aware that threatened species monitoring program for the mine included frogs.
I was aware that the frog monitoring sites included sites downstream of the proposed irrigation areas.
I noted the details of the vegetation survey program for the forest irrigation area (Exhibit DD-32, Pg 7).
Further analysis of irrigation water was requested and carried out (Exhibit DD-15)
I requested characterisation and benchmarking of soils, surface and groundwater (Exhibit DD-15).
I requested and received advice from EPA Waters and Catchments (Exhibit DD-14).
I reviewed soils consultants reports, especially in regard to effects of elevated salts and nitrogen leaching to groundwater in the cells 11-20 area and nitrogen cycling in the forest areas (Exhibits DD-9, DD-10, DD-11, DD-11a, DD-13, DD-14, DD-19, DD-22, DD-23, DD-27. I concluded that nitrogen and total dissolved solids might leach to groundwaters.
I referred to existing ANZECC water quality guidelines for protection of aquatic ecosystems and agricultural water use (Exhibit DD-40a). I concluded that runoff containing elevated levels of total dissolved solids and nitrogen might be recorded at the discharge point to the Cell 11 Dam.
Elevated levels of total dissolved solids and nitrogen in irrigation water Possible impacts on flora & fauna. I reviewed advice contained in consultant's reports for the proposals especially the Landloch Report (Exhibit DD-10), Dobos & Ass reports (Exhibits DD-11, DD-11a), and First and Second Proposals (Exhibits DD-9, DD-23). I ensured that extensive monitoring and reporting of soils, vegetation, surface and groundwaters would be included in the trial. I ensured that benchmark groundwater and soils characteristics were analysed before the trial. In ensured that existing monitoring programs including stream condition surveys would continue. I ensured that conditions of the Variation placed limits on the quality of water to be irrigated and the quality of water that could be discharged from the Cell 11 Dam.
Possible impacts on soils and the quality of surface and ground waters. I reviewed pollution control proposals for the cell 11-20 area (Exhibit DD-35). I ensured that discharges would not be directly to waters.
I requested investigations to optimise the catchment for the cell 11-20 area and to investigate practical measures to optimise possible re-use of nitrogen in the cell11-20 area. I ensured that conditions of the licence variation did not allow irrigation in the forest area that would cause surface runoff or ponding. I ensured that construction specifications for the Cell 11 Dam included downstream works to maximise spread of any overflows to forest areas. I concluded that even though levels of total dissolved solids and nitrogen might be elevated for some periods during the trial this issue would not cause a significant increase in environmental impact of the activity controlled or authorised by the Licence.
I noted proposals for irrigation operations and monitoring of soils, vegetation, surface and groundwater to complement existing monitoring programs (Exhibit DD-27).
I requested a review of irrigation practices to maximise the opportunity for evaporation and release of nitrogen to the atmosphere.
I noted the trial was for six months involving a target of 6ML per month (Exhibit DD-9, Pgs 1 & 3).
I noted that, assuming an average application of 6ML per month over the total area of 18.1 ha, the proposals involved irrigation of approximately 2 ML per hectare.
I concluded that elevated levels of total suspended solids might be recorded at the discharge point for the Cell 11 Dam.
I was aware that prior to that time monitoring of total suspended solids and stream condition downstream of other sediment dams had indicated no significant impact in streams likely to be affected by activities on the mine site from sediment.
I requested and receive investigation reports from TGM for the unused heap leach cells 11-20 area regarding water balance studies including the irrigation trial, storm runoff calculations and investigation of sediment dam sizes at cell 11 (Exhibits DD-19, DD-22, DD-23, DD-34, DD-35). I ensured that the environment protection standard established in the Licence for sedimentation dams discharging directly to waters was maintained for discharge point number 007, the Site 3 Dam.
Elevated levels of total suspended solids Possible impacts on flora & fauna. I requested investigations to optimise the catchment for the cell11-20 area and practical measures to optimise possible treated water re-use in the cell11-20 area and minimise sediment run-off. I concluded that the standard for discharge from the Cell 11 Dam (discharge point number 006) could be different as discharge was not direct to waters and that it was not practical to construct a storage to meet the 1:20 year 72 hour storm criteria.
I requested investigation of alternative runoff arrangements for the cell 11-20 area attempting to spread the runofff from the area (Exhibit DD-24). I ensured that construction specifications for the Cell 11 Dam included downstream works to maximise spread of any overflows to forest areas to facilitate dilution, absorption and re-use.
I ensured that conditions of the Variation did not allow irrigation in the forest area that would cause surface runoff or ponding.
I ensured that strict monitoring programs would continue.
I concluded that even though levels of total suspended solids might be elevated for some periods during the trial this issue would not cause a significant increase in the environmental impact of the activity controlled or authorised by the Licence.
I concluded that slightly elevated levels of aluminium (ie above ANZECC guidelines) might be recorded at the discharge point of Cell 11 Dam and some dissolved ions may leach to groundwater.
I requested further analysis of filtered and unfiltered water samples to ensure that the total characteristics of the water were known (Exhibit DD-15). I ensured that construction specifications for the Cell 11 Dam included downstream works to maximise spread of any overflows to forest areas to facilitate dilution, absorption and re-use.
Elevated levels of metals in irrigation water Possible impacts on flora & fauna. I noted that the ANZEC water quality guidelines for metal concentrations to protect aquatic ecosystems and for agricultural use (Exhibit DD-40a). I ensured that conditions of the Variation did not allow irrigation in the forest area that would cause surface runoff or ponding.
Possible impacts on soils and the quality of surface and ground water. I reviewed the consultant's reports on the First and Second Proposal (Exhibits DD-9, DD10, DD-11, DD-11a, DD13, DD-22, DD-23, DD-27, DD-34, DD-35) in regard to the fate metals in the irrigation water. I ensured that benchmark groundwater and soils characteristics were analysed before the trial.
I ensured that strict monitoring programs would continue.
I concluded that even though levels of aluminium and dissolved ions may be elevated for some periods during the trial this issue would not cause a significant increase in the environmental impact of the activity controlled or authorised by the Licence.
I researched material in the current and draft ANZECC water quality guidelines on molybdenum for protection of aquatic ecosystems and agricultural use (Exhibit DD-40a). I concluded that slightly elevated levels (ie above ANZECC guidelines) of molybdenum might be recorded at the discharge point of the Cell 11 Dam.
I noted that the levels set in the ANZECC guidelines were set to protect grazing livestock and that a cumulative contaminant loading limit was not set in the draft guidelines due to lack of soils data and toxicity benchmarks. I ensured that construction specifications for the Cell 11 Dam included downstream works to maximise spread of any overflows to forest areas to facilitate dilution, absorption and re-use.
Elevated levels of molybdenum in irrigation water Possible fate in the environment and any environmental impacts. I note that there is no current ANZECC guideline for molybdenum to protect aquatic ecosystems but the new draft guidelines indicate a trigger value of 0.006 mg/l. I ensured that conditions of the Variation did not allow irrigation in the forest area that would cause surface runoff or ponding.
I requested characterisation of the soils in the irrigation areas for molybdenum (Exhibit DD-15). I ensured that benchmark groundwater and soils characteristics were analysed before the trial.
I noted that the agricultural use ANZECC guideline was based on levels of 10mg/kg and irrigation for at least 20 years (Exhibit DD-40a). I ensured that strict monitoring programs would continue.
I concluded that even though levels of molybdenum might be elevated for some periods during the trial this issue would not cause a significant increase in the environmental impact of the activity authorised or controlled by the Licence.