Monthly Environmental Monitoring Report. Yancoal Hunter Valley Operations April 2018

Transcription

1 Monthly Environmental Monitoring Report Yancoal Hunter Valley Operations April 218 1

2 CONTENTS 1. INTRODUCTION AIR QUALITY Meteorological Monitoring Rainfall Wind Speed and Direction Depositional Dust Suspended Particulates HVAS PM1 Results TSP Results Real Time PM1 Results Real Time Alarms for Air Quality WATER QUALITY Surface Water Site Water Use HRSTS Discharge Groundwater Monitoring Results BLASTING Blast Monitoring Results NOISE Attended Noise Monitoring Results OPERATIONAL DOWNTIME REHABILITATION COMPLAINTS ENVIRONMENTAL INCIDENTS Appendix A: Meteorological Data

3 Figures Figure 1: Rainfall Summary Figure 2: HVO Corporate Wind Rose April Figure 3: HVO Cheshunt Wind Rose April Figure 4: Air Quality Monitoring Location Plan 5 Figure 5: Depositional Dust Results April Figure 6: Individual PM1 Results April Figure 7: Year to Date Average PM1 April Figure 8: Year to Date Average Total Suspended Particulates April Figure 9: Real Time PM1 24hr average and YTD average April Figure 1: Moses Crossing Blast Monitoring Results April Figure 11: Jerrys Plains Blast Monitoring Results April Figure 12: Maison Dieu Blast Monitoring Results April Figure 13: Warkworth Blast Monitoring Results April Figure 14: Knodlers Lane Blast Monitoring Results April Figure 15: Blast Monitoring Location Plan 12 Figure 16: Noise Monitoring Location Plan 17 Figure 17: Operational Downtime by Equipment Type April Figure 18: Rehabilitation YTD April Tables Table 1: Monthly Rainfall HVO 4 Table 2: Real-time PM1 Investigation Results 8 Table 3: Blasting Criteria 1 Table 4: L Aeq, 15 minute HVO South - Impact Assessment Criteria April Table 5: LAeq, 15 minute HVO South - Land Acquisition Criteria April Table 6: L A1, 1minute HVO South - Impact Assessment Criteria April Table 7: L Aeq, 15minute HVO North Impact Assessment Criteria April Table 8: L Aeq,15minute HVO North - Land Acquisition Criteria April Table 9: L A1, 1Minute HVO North - Impact Assessment Criteria April Table 1: Low Frequency Noise Assessment - April Table 11: Complaints Summary YTD 19 Table 12: Meteorological Data - HVO Corporate Meteorological Station April Revision History Version No. Person Responsible Document Status Date 1. Environmental Advisor Draft 29/5/ Environmental Specialist Final 17/7/218 3

4 JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Monthly Rainfall (mm) Cumulative Rainfall (mm) 1. INTRODUCTION Wind Speed and Direction This report has been compiled to provide a monthly summary of environmental monitoring results for Hunter Valley Operations (HVO). This report includes all m o nitoring data collected for the period 1 st April to 3 th April 218. North-westerly and South-easterly w i nds w ere d ominan t during April as shown in Figure 2 (HVO Corporate) and Figure 3 (HVO Cheshunt). 2. AIR QUALITY 2.1 Meteorological Monitoring HVO maintains two meteorological stations; Corporate and Cheshunt (Refer to Figure 4: Air Quality Monitoring Location Plan) Rainfall Rainfall for the period is summarised in Table 1, the 218 trend and historical tren d are s how n in Figure 1. Table 1: Monthly Rainfall HVO 218 Monthly Rainfall (mm) Cumulative Rainfall (mm) Figure 2: HVO Corporate Wind Rose April 218 April Monthly Rainfall 216 Monthly Rainfall 217 Monthly Rainfall 218 Cumulative Rainfall 216 Cumulative Rainfall 217 Cumulative Rainfall 218 Figure 3: HVO Cheshunt Wind Rose April 218 Figure 1: Rainfall Summary 218 4

5 Figure 4: Air Quality Monitoring Location Plan 5

6 Insoluble Solids (g/m2/month) Particulate Matter <1µm (µg/m³) 2.2 Depositional Dust To monitor regional air quality, HVO operates and maintains a network of nine depositional dust gauges, situated on private and mine owned land surrounding HVO. Figure 5 displays insoluble solids results fro m d epositional dust gauges during the reporting period compared against the year-to-date average and th e an nual impact assessm ent criteria. During the reporting period the D118, DL3 and Warkw orth monitors recorded a monthly re sult ab ove th e lo ng te rm impact assessment criteria of 4. g/m 2 per month. The field notes associated with the D118, DL3 and Warkworth monitor s results indicate no evidence to suggest that the result was contaminated. An assessmen t o f H VO s contribution against the long term impact assessment criteria will be provided in the 218 Annual Review HVAS PM1 Results Figure 6 shows individual PM1 results at each m onitoring station against the short term impact assessment cri teria o f 5 µg/m 3. On 13/4/218 four HVAS PM1 units recorded and elevated 24 hour averages ; Glider Club (76µg/m 3 ), Long Point (15µg/m 3 ), Knodlers Lane (71µg/m 3 ) and Maison Dieu (61µg/m 3 ). Investigation determined that H VO s maxim um contribution at each monitor is as follows: Glider Club 49 µg/m 3 ; or 64.5% of the measured result. Long Point <49 µg/m 3 or <46.7% of the measured result Knodlers Lane - 44 µg/m 3 or 62% of the measured result Maison Dieu - 34 µg/m 3 or 55.7% of the measured result Accordingly, no further action is required (as per approved Air Quality Monitoring Programme) April YTD Long Term Impact Assessment Criteria Figure 5: Depositional Dust Results April Suspended Particulates Kilburnie South Long Point Warkworth 29 24hr Criteria Knodlers Lane Maison Dieu Glider Club Suspended particulates are measured by a network o f H igh Volume Air Samplers (HVAS) m easuring To tal S uspended Particulates (TSP) and Particulate Matter <1µm (PM1). Th e location of these monitors can be found in F igure 4. Ea ch HVAS was run for 24 hours on a six-day cycle. Figure 6: Individual PM1 Results April 218 Figure 7 shows the year to date annual average PM1 results. An assessment of HVO s contribution against th e l ong term impact assessment criteria w ill b e p rovided in th e 218 Annual Review. 6

7 Particulate Matter <1µm (µg/m³) Total Suspended Particulates (µg/m³) YTD Figure 7: Year to Date Average PM 1 April TSP Results Long Term Impact Assessment Criteria Figure 8 shows the annual average TSP results compared against the long term impact assessment criteria of 9µg/m³. An assessment of HVO s contribution against th e l ong term impact assessment criteria w ill b e p rovided in th e 218 Annual Review. YTD Figure 8: Year to Date Average Total Suspended Particulates April Real Time PM1 Results Long Term Impact Assessment Criteria Hunter Valley Operations maintains a network o f re al ti me PM 1 monitors. The real time air quality monitoring statio ns continuously log information and transmit data to a ce ntral database, generating alarms when particulate matter l evels exceed internal trigger limits. Results fro m real tim e PM 1 monitoring are used as a reactive measure to guid e minin g operations to ensure compliance with the relevant conditions of the project approval. Results for real time dust sam pling is sh own in Fi gure 9, including the daily 24 hour average PM 1 result and the year to date 24 hour PM1 annual average. Results from investigations of elevated results are presented in Table Real Time Alarms for Air Quality During April the real time monitoring system ge nerated 59 automated air quality related alarm s. 23 w ere related to adverse weather conditions and 36 alarms relating to PM1. 7

8 1/4/218 2/4/218 3/4/218 4/4/218 5/4/218 6/4/218 7/4/218 8/4/218 9/4/218 1/4/218 11/4/218 12/4/218 13/4/218 14/4/218 15/4/218 16/4/218 17/4/218 18/4/218 19/4/218 2/4/218 21/4/218 22/4/218 23/4/218 24/4/218 25/4/218 26/4/218 27/4/218 28/4/218 29/4/218 3/4/218 Knodlers Lane Maison Dieu Warkworth Particulate Matter <1µm (µg/m³) YTD Knodlers Lane Maison Dieu Warkworth Impact Assessment Criteria Figure 9: Real Time PM 1 24hr average and YTD average April 218 Table 2: Real-time PM1 Investigation Results Date Site 24hr PM 1 result (µg/m 3 ) Estimated contribution from HVO (µg/m 3 ) Discussion 13/4/218 Maison Dieu TEOM An internal investigation determined HVO maximum potential contribution to be in the order of 33.6ug/m3 or 59% of the total measured based on prevailing wind conditions and upwind monitoring results. 15/4/218 Knodlers Lane TEOM An internal investigation determined HVO maximum potential contribution to be in the order of 6.8g/m3 or 11.5% of the total measured based on prevailing wind conditions and upwind monitoring results. 8

9 15/4/218 Maison Dieu TEOM An internal investigation determined HVO maximum potential contribution to be in the order of 18.1g/m3 or 25.7% of the total measured based on prevailing wind conditions and upwind monitoring results. 15/4/218 Warkworth TEOM An internal investigation determined HVO maximum potential contribution to be in the order of 5.g/m3 or 1.6% of the total measured based on prevailing wind conditions and upwind monitoring results. 3. WATER QUALITY During the reporting period no water was discharged under the HRSTS HVO maintains a network of surface water and groundwater monitoring sites Surface Water Groundwater Monitoring Results Surface water courses are sampled on a quarterly sam plin g regime. Water quality is evaluated through the parameters of ph, Electrical Conductivity (EC) and Total Suspen ded S olids (TSS). Results of monitoring on Site Dams and the Hunter R ive r as well as other natural tributaries are provided on a q uarterly basis, results will a ppear in the June 218 report. Groundwater monitoring is undertaken on a quarterly basis in accordance with the HVO Water Management Plan and Ground Water Monitoring Programme. Results of groundwater monitoring are reported quarterly and as su ch will be reported in the June 218 monthly report Site Water Use Under water allocation licences issued by the NSW DPI Water, HVO is permitted to extract water from th e H unter R iver. During the reporting period, HVO extracted 35.3ML of w a ter from the Hunter River HRSTS Discharge HVO participates in the Hunter River Salinity Trading Scheme (HRSTS), allowing discharge from licensed discharge p oints Dam 11N (to Farrell s Creek), Lake James (to the Hunter River) and Parnell s Dam (to Parnell s Creek). Discharges ca n o nly take place subject to HRSTS regulations. 9

10 3/4/218 5/4/218 7/4/218 9/4/218 11/4/218 13/4/218 15/4/218 17/4/218 19/4/218 21/4/218 23/4/218 25/4/218 27/4/218 29/4/218 Airblast Overpressure (db(l)) Ground Vibration (mm/s) 3/4/218 5/4/218 7/4/218 9/4/218 11/4/218 13/4/218 15/4/218 17/4/218 19/4/218 21/4/218 23/4/218 25/4/218 27/4/218 29/4/218 Airblast Overpressure (db(l)) Ground Vibration (mm/s) 4. BLASTING HVO have a network of five blast monitoring units. These a re located at nearby privately owned residences and function as regulatory compliance monitors. The location of these monitors can be found in Figure 15. Blasting criteria are summarised in Table 3. Table 3: Blasting Criteria Airblast Overpressure (db(l)) Comments % of the total number of blasts in a 12 month period 4 12 % Ground Vibration (mm/s) Comments 5% of the total number of blasts 5 in a 12 month period 1 % Airblast Overpressure Airblast Overpressure Limit for Max 5% Airblast Overpressure Limit Ground Vibration Ground Vibration Limit for Max 5% Ground Vibration Limit Figure 1: Moses Crossing Blast Monitoring Results April Blast Monitoring Results During April, 29 blasts were initiated at HVO Figure 1 through to Figure 14 show the blast monitoring results for the reporting period against the impact assessment criteria. Th e criteria are summarised in Table Airblast Overpressure Airblast Overpressure Limit for Max 5% Airblast Overpressure Limit Ground Vibration Ground Vibration Limit for Max 5% Ground Vibration Limit Figure 11: Jerrys Plains Blast Monitoring Results April 218 1

11 3/4/218 5/4/218 7/4/218 9/4/218 11/4/218 13/4/218 15/4/218 17/4/218 19/4/218 21/4/218 23/4/218 25/4/218 27/4/218 29/4/218 Airblast Overpressure (db(l)) Ground Vibration (mm/s) 3/4/218 5/4/218 7/4/218 9/4/218 11/4/218 13/4/218 15/4/218 17/4/218 19/4/218 21/4/218 23/4/218 25/4/218 27/4/218 29/4/218 3/4/218 5/4/218 7/4/218 9/4/218 11/4/218 13/4/218 15/4/218 17/4/218 19/4/218 21/4/218 23/4/218 25/4/218 27/4/218 29/4/218 Airblast Overpressure (db(l)) Ground Vibration (mm/s) Airblast Overpressure (db(l)) Ground Vibration (mm/s) Airblast Overpressure Airblast Overpressure Limit for Max 5% Airblast Overpressure Limit Ground Vibration Ground Vibration Limit for Max 5% Ground Vibration Limit Airblast Overpressure Airblast Overpressure Limit for Max 5% Airblast Overpressure Limit Ground Vibration Ground Vibration Limit for Max 5% Ground Vibration Limit Figure 12: Maison Dieu Blast Monitoring Results April 218 Figure 14: Knodlers Lane Blast Monitoring Results April Airblast Overpressure Airblast Overpressure Limit for Max 5% Airblast Overpressure Limit Ground Vibration Ground Vibration Limit for Max 5% Ground Vibration Limit Figure 13: Warkworth Blast Monitoring Results April

12 Figure 15: Blast Monitoring Location Plan 12

13 5. NOISE Routine attended noise monitoring is carried out at defined locations around HVO as described in the HVO No ise Mo nito ring Programme. The purpose of the noise surveys is to quantify and describe the acoustic enviro nm ent arou nd th e site an d compare results with specified limits. Unattended monitoring (real time noise monitoring) also occurs at five sites surro undin g HVO. The attended noise monitoring locations are displayed in Figure Attended Noise Monitoring Results Attended monitoring was conducted at receiver locations surrounding HVO on the nights of 5 th April 218. Monito ring re sults are detailed in Table 4 to Table 9. Table 4: LAeq, 15 minute HVO South - Impact Assessment Criteria April 218 Location Date and Time Wind Speed (m/s) 5 VTG 5 db (A) Applies? 1,6 HVO South L Aeq db 2,4 Exceedance 3 Knodlers Lane 5/4/218 23: No 27 NA Maison Dieu 6/4/218 : Yes 31 Nil Shearers Lane 6/4/218 : No 3 NA Kilburnie South 5/4/218 23: No 36 NA Jerrys Plains Village 5/4/218 21: No IA NA Jerrys Plains East 5/4/218 21: Yes NM Nil Long Point 5/4/218 21: Yes IA Nil HVGC 6/4/218 : No 33 NA Table 5: L Aeq, 15 minute HVO South - Land Acquisition Criteria April 218 Location Date and Time Wind Speed (m/s) 5 VTG 5 db (A) Applies? 1,6 HVO South L Aeq db 2,4 Exceedance 3 Knodlers Lane 5/4/218 23: No 27 NA Maison Dieu 6/4/218 : Yes 31 Nil Shearers Lane 6/4/218 : No 3 NA Kilburnie South 5/4/218 23: No 36 NA Jerrys Plains Village 5/4/218 21: No IA NA Jerrys Plains East 5/4/218 21: Yes NM Nil Long Point 5/4/218 21: Yes IA Nil HVGC 6/4/218 : NA No 33 NA 13

14 Table 6: L A1, 1minute HVO South - Impact Assessment Criteria April 218 Location Date and Time Wind Speed (m/s) 5 VTG 5 db (A) HVO South L A1, Applies? 1,6 1min db 2,4 Exceedance 3 Knodlers Lane 5/4/218 23: No 32 NA Maison Dieu 6/4/218 : Yes 43 Nil Shearers Lane 6/4/218 : No 37 NA Kilburnie South 5/4/218 23: No 53 NA Jerrys Plains Village 5/4/218 21: No IA NA Jerrys Plains East 5/4/218 21: Yes NM Nil Long Point 5/4/218 21: Yes IA Nil HVGC 6/4/218 : NA NA IA NA Notes 1. Noise emission limits apply for wind speeds up to 3 metres per second (at a height of 1m), or temperature inversion conditions of up to 3 degrees/1m (at a height of 1m); 2. Estimated or measured LAeq,15minute db attributed to HVO South Pit Area; 3. NA in exceedance column means atmospheric conditions outside specified in approval and so criterion is not applicable; 4. Bolded results in red indicate exceedance of criteria; 5. Atmospheric data is sourced from the HVO Corporate or Cheshunt weather station using logged met data; 6. may or may not apply due to rounding of meteorological data values Table 7: L Aeq, 15minute HVO North Impact Assessment Criteria April 218 Location Date and Time Wind Speed (m/s) 5 VTG 5 db (A) Applies? 1,6 HVO North L Aeq db 2,4 Exceedance 3 Knodlers Lane 5/4/218 23: No IA NA Maison Dieu 6/4/218 : No IA NA Shearers Lane 6/4/218 : No IA NA Kilburnie South 5/4/218 23: No IA NA Jerrys Plains Village 5/4/218 21: No IA NA Jerrys Plains East 5/4/218 21: No IA NA Long Point 5/4/218 21: No IA NA HVGC 6/4/218 : NA NA IA NA Table 8: L Aeq,15minute HVO North - Land Acquisition Criteria April 218 Location Date and Time Wind Speed (m/s) 5 VTG 5 db (A) Applies? 1,6 HVO North L Aeq db 2,4 Exceedance 3 Knodlers Lane 5/4/218 23: Yes IA Nil Maison Dieu 6/4/218 : Yes IA Nil Shearers Lane 6/4/218 : Yes IA Nil Kilburnie South 5/4/218 23: Yes IA Nil Jerrys Plains Village 5/4/218 21: Yes 3 Nil Jerrys Plains East 5/4/218 21: Yes 33 Nil Long Point 5/4/218 21: Yes IA Nil 14

15 HVGC 6/4/218 : NA NA IA NA Table 9: L A1, 1Minute HVO North - Impact Assessment Criteria April 218 Location Date and Time Wind Speed (m/s) 5 VTG 5 db (A) Applies? 1,6 HVO North L A1, 1min db 2,4 Exceedance 3 Knodlers Lane 5/4/218 23: Yes IA Nil Maison Dieu 6/4/218 : Yes IA Nil Shearers Lane 6/4/218 : Yes IA Nil Kilburnie South 5/4/218 23: Yes IA Nil Jerrys Plains Village 5/4/218 21: Yes 3 Nil Jerrys Plains East 5/4/218 21: Yes 33 Nil Long Point 5/4/218 21: Yes IA Nil HVGC 6/4/218 : NA NA IA NA Notes 1. Noise emission limits apply under all meteorological conditions, except during periods of rain or hail, when average winds speed at microphone heights exceeds 5 metres per second, when wind speeds greater than 3 metres per second are measured at 1m above ground level, or during temperature inversion conditions greater than 3 degrees C/1m;2. Estimated or measured LAeq,15minute db attributed to HVO North Area; 3. NA in exceedance column means atmospheric conditions outside specified in approval and so criterion is not applicable; 4. Bolded results in red indicate exceedance of criteria; 5. Atmospheric data is sourced from the HVO Corporate or Cheshunt weather station using logged met data; 6. may or may not apply due to rounding of meteorological data values 15

16 5.2 NPfI Low Frequency Assessment In accordance with the requirements of the EPA s Noise Policy for Industry (NPfI ), th e ap plicability o f th e lo w fre quency modification penalty has been assessed. During April 218 no m easuremen ts re quired th e p enalty to b e ap plied. Th e assessment for low frequency noise is shown i n Table 1. Table 1: Low Frequency Noise Assessment - April 218 Location Date and Time Measured Site Only LA eq db (Sth/Nth) Site Only LC eq db 4 (Sth/Nth) Site Only LC eq-la eq db 1,4 (Sth/Nth) Result Max exceedance of ref spectrum db 2,3,4 (Sth/Nth) Penalty db(a) Exceedance Knodlers Lane 5/4/218 23:55 27/IA NA/NA NA/NA NA/NA Nil Maison Dieu 6/4/218 :49 31/IA 54/NA 23/NA /NA Nil Shearers Lane 6/4/218 :27 3/IA NA/NA NA/NA NA/NA Nil Kilburnie South 5/4/218 23:59 36/IA NA/NA NA/NA NA/NA Nil Jerrys Plains Village 5/4/218 21:34 IA/3 NA/NA NA/NA NA/NA Nil Jerrys Plains East 5/4/218 21:2 NM/33 NA/NA NA/NA NA/NA Nil Long Point 5/4/218 21:28 IA/IA NA/NA NA/NA NA/NA Nil HVGC 6/4/218 :33 33/IA NA/NA NA/NA NA/NA Nil Notes: 1. As per NPfI, if LCeq LAeq >= 15 db further assessment of low frequency noise required. 2. As per NPfI, compare measured spectrum against reference spectrum to determine if the low frequency modifying factor is tr iggered and application of penalty is required; 3. Bold results and penalties in red are where the relevant modifying factor trigger was exceeded; and 4. Where it is not possible to determine the site only result due to the presence of other low frequency noise sources occurr ing during the measurement, or where criteria were not applicable due to meteorological conditions, this is noted as NA (not available) and no further assessment has been undertaken. 16

17 Figure 16: Noise Monitoring Location Plan 17

18 218 Target 218 YTD 218 Target 218 YTD 218 Target 218 YTD 218 Target 218 YTD Land Area (Ha) Real Time Noise Monitoring 7. REHABILITATION HVO utilises a network of real-time directional noise monitors to manage noise impacts on a continuous basis. Noise alarms are in place at five monitoring locations ( Kn odlers La ne, Maison Dieu, Jerrys Plains, Moses Crossing, and Long Po int), which alert HVO staff to elevated noise levels likely to b e attributable to HVO. Noise alarms are i nvestigated a nd responded to with the app ropriate level o f o p erational modification. Changes i n resp onse to a n oise alarm can include replacing equipment with quieter (noise attenuated) units, changing or relocating tasks, and shutting down equipment. It should be noted that this assessment does not compliment or conflict with attended noise monitoring detailed in Section 5.1, and that real time monitoring data in clu des n on-m ine noise sources such as dogs, cows, or more co m monly, ro ad traffic. During April.1 Ha of land was released,.1 Ha o f land w as bulk shaped 6.1 Ha of land was topsoiled,.8 Ha of land w as composted and 7.6 Ha of land was rehabilitated. Year to date progress can be viewed in Figure OPERATIONAL DOWNTIME During April, a total of 89 hours of equipment downtime w as logged in response to real time monitoring and visual inspections for environmental reasons such as dust, noise and meteorological conditions. Operational downtime by equipment type is shown in Figure 17. Released HVO North Bulk Shaped Figure 18: Rehabilitation YTD April 218 Topsoiled HVO South Rehab Truck Shovel Dragline Dozer Duration (hours) Figure 17: Operational Downtime by Equipment Type April

19 8. COMPLAINTS One complaint was received durin g th e re porting p eriod. Details of complaints received YTD are sh own in Table 11 below. Table 11: Complaints Summary YTD Noise Dust Blast Lighting Other Total January February March April May June July August September October November December Total ENVIRONMENTAL INCIDENTS During the reporting period there were no reportable environmental incidents. 19

20 Appendix A: Meteorological Data 2

21 Table 12: Meteorological Data - HVO Corporate Meteorological Station April 218 Date Air Temperature Maximum ( C) Air Temperature Minimum ( C) Relative Humidity Maximum (%) Relative Humidity Minimum (%) Solar Radiation Maximum (W/Sq. M) Wind Direction Average ( ) Wind Speed Average (m/sec) Rainfall(mm) 1/4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ /4/ Indicates that data was not available due to technical issues. 21