HAZARDOUS MATERIAL AUDIT (HMA) King George Park Amenities King George Park Rozelle NSW Prepared for: Leichhardt Municipal Council

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1 Edwards Blasche Group Pty Ltd ABN Environmental & Engineering Geoscience Occupational Hygiene Consultants HAZARDOUS MATERIAL AUDIT (HMA) King George Park Amenities King George Park Rozelle NSW 2039 Prepared for: Leichhardt Municipal Council (Report ID : EBG.HMA rpt) October 2015 This document has been prepared by EBG for the specific use at the above address. This document or any part thereof shall not be used at any other site, works or by any company or party not associated with the above works. ALL RIGHTS RESERVED BY THE AUTHOR UNAUTHORISED REPRODUCTION OR COPYING STRICTLY PROHIBITED EBG Environmental Geoscience (Edwards Blasche Group Pty Ltd) 85 Rose St, PO Box 284, Annandale 2038 Ph: Fax:

2 ebgroup.com.au CONTENTS 1.0 Hazardous Materials Audit 1.1 Asbestos Materials 1.2 Synthetic Mineral Fibre 1.3 PCB Capacitors in Fluorescent Light Fittings 1.4 Ceiling Space Dust with Elevated Lead Levels 1.5 Lead Based Paint 2.0 Photographs 3.0 Limitations of the Audit Appendix A: Asbestos Analysis Report Appendix B: Hazardous Materials Removal Specifications Appendix C: Envirolab Services Analysis Report EBG PCBs SMF NEHF Pb AS EDBs OH&S EPA (NSW) ANZECC HBSIL NOHSC HMA ABBREVIATIONS Edwards Blasche Group Poly Cyclic Biphenyls Synthetic Mineral Fibre National Environment Health Forum Lead Australian Standards Electrical Distribution Boards Occupational Health & Safety Environmental Protection Agency (NSW) Australian and New Zealand Environment Conservation Council Health Based Soil Investigation Levels National Occupational Health and Safety Hazardous Materials Audit Distribution: PDF Copies to: Julian Oon - Leichhardt Council Investigation & Reporting conducted by: Michael Edwards MAppSc, MAIG, RPGeo No Registered Professional Geoscientist Env. & Eng. Geoscientist / Occup. Hygiene Signed: Issued 29 October 2015 Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 2

3 1.0 Hazardous Materials Audit 1.1 Asbestos Materials # Location Material Sample ID / Suspect Result Type/ Visual Area m/sq* Friable or Bonded Recommendations 1 Electrical Box Rear wall facing road: Bituminous fibrous Zelminite style electrical board. (Larger board is timber, smaller black board has an asbestos content) Bituminous Elect. Dist. Board 02491/1 Chrysotile Envirolab # Bonded Remove all as Bonded Asbestos prior to demolition or refurbishment (see Appendix B: 1. Specification for the Removal of Bonded Asbestos) * NOTE TO CONTRACTORS: Area in Square Metres: The area of asbestos material is given here as an approximate quantity. Asbestos removal contractors should only rely on this figure as an indication of the scale of the amount to be removed, and should individually assess and measure the areas themselves to provide a fee proposal for the removal procedures. NON-DETECTS: NA. INSPECTION NOTES: The building is constructed of concrete blocks with a concrete roof. IMPORTANT REFURBISHMENT/DEMOLITION NOTES: If removing any concrete floor slabs, the builder/demolisher should check the sides and underneath for possible pieces of asbestos cement sheeting. These may have been used as formwork in some instances, and have been buried as waste product in other situations. Asbestos removal shall proceed as per Specifications attached. Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 3

4 1.2 Synthetic Mineral Fibre (SMF) Synthetic mineral fibre (SMF) insulation was NOT located during the inspection. Contingency Measure: Any synthetic mineral fibre (SMF) located during demolition or refurbishment shall be removed if the material is to be disturbed during the works, as per Appendix B: 2. Specification for the Removal of Synthetic Mineral Fibre (SMF) 1.3 PCBs in Fluorescent Light Fittings A number of older style light fittings were located throughout the building. The fittings were connected to mains power. The internal components could not be inspected. It is suspected that these fittings may contain internal capacitors or components with an internal PCB dielectric oil. Contingency Measure: Any light fittings located during demolition or refurbishment, with metal capacitors or older plastic capacitors, should be checked in the Identification of PCB - Containing Capacitors PCB (ANZECC, 1997) and if identified, removed as per Appendix B: 3. Specification for the Removal of Fluorescent Light Capacitors containing PCB Oil. Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 4

5 1.4 Ceiling Space Dust with Elevated Lead Levels Findings: Ceiling space dust was not located during the inspection. Health based investigation levels for lead in soil currently accepted by EPA NSW are documented in EPA NSW Guidelines for the NSW Site Auditor Scheme (June 1998). The HBSILs are: Column 1: residential (including schools) level for lead in soil of 300mg/kg. Column 2: parks and residential open space level for lead in soil of 600mg/kg. 1.5 Lead Based Paint 1. A sample of paint was taken from the external wall paint and analysed for lead content. The sample contained <0.05% of lead. (See sample 02491/2 in Envirolab report #136262). The paint IS NOT defined as lead paint according to Australian Standard: Guide to Lead Paint Management, Part 2: Residential and Commercial Buildings (AS ). In general lead paint is identified in the Australian Standard as paint having a lead content in excess of 1% by weight ( kg-1). Findings: Paint containing significant levels of lead was not detected with the sample analysis. It is suspected that lead paint shall not be an issue on the external or internal walls. NOTE: In most cases external enamel paint used from the 1800s to 1970s have levels of lead above 1%. Paint samples above this figure may become a hazard if allowed to flake, peel or deteriorate in any way that allows it to come in contact with humans. Generally external enamel paint on timber in older buildings may be regarded as containing lead (i.e. >1%). In general lead paint is identified in the Australian Standard as paint having a lead content in excess of 1% by weight ( kg-1). Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 5

6 2.0 Photographs 1. Toilet cubicle walls are brick. 2. Electrical switchbox no internal asbestos suspected. 3. Bituminous asbestos board in electrical box. 4. Old fluorescent light fittings - suspected old internal capacitors with a PCB content. 5. Electrical switchbox no internal asbestos suspected. 6. Timber verandah. Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 6

7 3.0 LIMITATIONS OF THE AUDIT This report must be read in total. No part should be extracted from the whole report to be used during the demolition or refurbishment procedures. Every effort has been made to locate and identify any hazardous materials within the buildings, however hazardous materials may be located in inaccessible areas. The survey was conducted within occupied buildings. In accordance with OH&S procedures, sampling was therefore restricted and/or difficult due to the risk of exposure to asbestos fibres when this material is broken. The scope of works for this inspection did not include demolition of suspect areas. It should be noted that without substantial demolition of the buildings it is not possible to guarantee that all (or any) hazardous materials have been located. Where sampling was possible, generally one sample of the material was analysed. One sample as a part of the whole is generally deemed adequate and common practice for the assessment of asbestos. The status of the material in regard to the asbestos content has been made from analysing this one sample. If during demolition and/or refurbishment the identified materials are found not to be homogeneous, further samples should be taken and analysed. Access to confined spaces, shallow sub floors, some ceiling spaces, and within the internal confines of any plant equipment was not possible in certain circumstances. Certain assumptions were made during the inspection taking into consideration the age of the building. This document should be used as a starting point in the identification of hazardous materials, and care should be taken if refurbishment or demolition occurs. Where suspect materials are encountered, work should cease until any unidentified material has been analysed. EBG and the author take no responsibility for the hazardous nature of any asbestos or other contamination found in the buildings, within the soil or the sub surface areas of the buildings and associated facilities. EBG and the author take no responsibility for any hazardous material that may cause risk, or is causing risk, to human health. Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 7

8 APPENDIX A: ASBESTOS ANALYSIS REPORT DATE: 21 October 2015 CLIENT: Leichhardt Council JOB No: SAMPLES FROM: King George Park Amenities NSW COLLECTED BY: Michael Edwards Sample # Location of Sample Material Analysis Result 02491/2 Electrical box distribution board Bituminous fibrous board Chrysotile asbestos was detected by stereobinocular and polarising light microscopy (PLM) including Dispersion Staining 02491/2 External paint on walls analysed for lead content (Results: <0.05% lead) Crocidolite - Blue asbestos, Chrysotile - White asbestos, Amosite - Brown asbestos, SMF - Synthetic Mineral Fibre TEST METHOD: Samples have been examined in accordance with the 1991 NATA Guidance Notes on Asbestos Identification and the EBG Identification of Asbestos in Bulk Materials IDENTIFICATION TECHNIQUE: Sample has been analysed using stereobinocular and polarising light microscopy (PLM) including Dispersion Staining, except where stated. Analysed By: Michael Edwards (BSc MAppSc) Env. Science / Occup. Hygiene Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 8

9 APPENDIX B: HAZARDOUS MATERIALS REMOVAL SPECIFICATIONS (NOTE: TO BE USED WHERE APPLICABLE) Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 9

10 1. Specification for the Removal of Bonded Asbestos Material Asbestos containing materials were located during the inspection. Bonded Asbestos Materials: Removal required if material is to be disturbed during refurbishment or demolition or it poses a health risk. In accordance with the Work Health and Safety Act 2011 (WHS Act) and Work Health and Safety Regulation 2011 (WHS Regulation) removal shall be by a Asbestos Removalist who holds a Bonded (Class B) Asbestos Removal Licence. Note: A licence is required where the surface area of bonded asbestos removed, is greater than 10m 2 (as of January ). Where practicable, plastic barriers should be constructed at the entrance to the removal area. The removalist shall wear disposable overalls of 100% synthetic material or a mixed natural/synthetic fabric capable of providing adequate protection against fibre penetration. Goggles and a head covering shall be used in the event of overhead work. A half face respirator fitted with a P1 filter shall be used. Following this removal process, the asbestos material is to be wrapped in plastic sheeting and taped. Smaller pieces of asbestos debris when removed shall be placed in heavy-duty polythene bags approximately 0.2mm thick, or other approved containers. It is recommended that a maximum bag size of 1200mm (length) x 900mm (width) be observed. Bags should be filled to no more than 50% capacity. The bags shall be marked, Caution - Asbestos: Do Not Inhale Dust, Do Not Open Bag. The top of the bag when full shall be twisted, folded down and taped. The bag shall then be placed in the plastic lined skip bin. The work shall be in accordance with WorkCover NSW, How to Safely Remove Asbestos Code of Practice. Asbestos is classified as a special waste and shall be tipped at approved sites. Copies of the tipping receipts should be provided to the project manager. All work carried out shall be in accordance with: WorkCover NSW, How to Safely Remove Asbestos Code of Practice, Work Health and Safety Act 2011 (WHS Act) Work Health and Safety Regulation 2011 (WHS Regulation) National Occupational Health and Safety (NOHSC:2002, 1998) Code of practice for the safe removal of asbestos; EPA NSW (1999) Environmental Guidelines: Assessment, Classification & Management of Liquid & Non-liquid Wastes; Protection of the Environment Operations (Waste) Regulations 1996; Protection of the Environment Operations Act 1997; Occupational Health and Safety Act, 2000; and Occupational Health and Safety Regulation, Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 10

11 2. Specification for the Removal of Synthetic Mineral Fibre (SMF) SMF containing materials were not located during the inspection. Contingency Measures (if located during development works): If any synthetic mineral fibre (SMF) is located during demolition it is recommended that it be removed prior to refurbishment or demolition where there is a possibility that the material may be disturbed. Workers shall wear long sleeved, loose fitting clothing and gloves to prevent fibre penetration. Disposable overalls may be worn if desired. Washable clothing should be laundered separately to avoid cross contamination and skin irritation of other workers. Goggles and a head covering shall be used in the event of overhead work. A half face respirator fitted with a P1 filter shall be used. All work carried out shall be in accordance with:! National Occupational Health and Safety (NOHSC:2002, 1990) Code of Practice for the Safe Use of Synthetic Mineral Fibres;! EPA NSW (1999) Environmental Guidelines: Assessment, Classification & Management of Liquid & Non-liquid Wastes;! Protection of the Environment Operations (Waste) Regulations 1996(updated 1/12/00);! Protection of the Environment Operations Act 1997; and! Occupational Health and Safety Act, 2000; and! Occupational Health and Safety Regulation, Specification for the Removal of Fluorescent Light Capacitors containing PCB Oil Older style fluorescent light fittings suspected of containing PCB components were located during the inspection. Contingency Measures: It is recommended that all fluorescent light fittings removed during demolition or refurbishment be dismantled. Lights with identified PCB capacitors as per PCB - Containing Capacitors PCB (ANZECC, 1997), or any old aluminium capacitors, shall be removed from the light fittings and placed in an appropriate sealed drum. Appropriate PPE shall be employed. The containers containing the PCBs shall be approved for the transport of dangerous goods and labelled with words to the effect: ENVIRONMENTAL CONTAMINANT - CLASS 6.1(A) CAUTION - CONTAINS POLYCHLORINATED BIPHENYL (PCB) A TOXIC ENVIRONMENTAL CONTAMINANT UN NUMBER 2315 All work carried out shall be in accordance with:! Polychlorinated Biphenyl (PCB) Wastes Chemical Control Order June 1997 (PCB CCO 1997);! National Strategy for the Management of Scheduled Waste, Polychlorinated Biphenyls Management Plan - November 1996;! NSW Waste Disposal Act;! NSW Occupational Health and Safety Act and Regulations! NSW Construction Safety Act and Regulations 84a-84j. Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 11

12 APPENDIX C: ENVIROLAB SERVICES ANALYSIS REPORT Hazardous Materials Audit : King George Park Amenities, Rozelle NSW (EBG.HMA rpt) Page 12

13 Client: Edwards Blasche Group PO Box 284 Annandale NSW 2038 CERTIFICATE OF ANALYSIS Attention: Michael Edwards Sample log in details: Your Reference: No. of samples: 1 material, 1 paint Date samples received / completed instructions received 22/10/15 / 22/10/15 Analysis Details: Please refer to the following pages for results, methodology summary and quality control data. Samples were analysed as received from the client. Results relate specifically to the samples as received. Results are reported on a dry weight basis for solids and on an as received basis for other matrices. Please refer to the last page of this report for any comments relating to the results. Report Details: Date results requested by: / Issue Date: 29/10/15 / 28/10/15 Date of Preliminary Report: Not Issued NATA accreditation number This document shall not be reproduced except in full. Accredited for compliance with ISO/IEC Tests not covered by NATA are denoted with *. Results Approved By: Envirolab Reference: Revision No: R 00 Page 1 of 7

14 Client Reference: Asbestos ID - materials Our Reference: UNITS Your Reference /1 Type of sample material Date analysed - 28/10/2015 Mass / Dimension of Sample - 10x5x1mm Sample Description - Brown fibrous bituminous material Asbestos ID in materials - Chrysotile asbestos detected Envirolab Reference: Revision No: R 00 Page 2 of 7

15 Client Reference: Lead in Paint Our Reference: UNITS Your Reference /2 Type of sample paint Date prepared - 23/10/2015 Date analysed - 23/10/2015 Lead in paint %w/w <0.05 Envirolab Reference: Revision No: R 00 Page 3 of 7

16 Client Reference: Method ID ASB-001 Metals-004 Methodology Summary Asbestos ID - Qualitative identification of asbestos in bulk samples using Polarised Light Microscopy and Dispersion Staining Techniques including Synthetic Mineral Fibre and Organic Fibre as per Australian Standard Digestion of Paint chips/scrapings/liquids for Metals determination by ICP-AES/MS and or CV/AAS. Envirolab Reference: Revision No: R 00 Page 4 of 7

17 Client Reference: QUALITY CONTROL UNITS PQL METHOD Blank Duplicate Sm# Lead in Paint Duplicate results Spike Sm# Spike % Recovery Base ll Duplicate ll %RPD Date prepared - 23/10/2 015 Date analysed - 23/10/ /10/ /10/2015 LCS-2 23/10/ /10/ /10/2015 LCS-2 23/10/2015 Lead in paint %w/w 0.05 Metals-004 < <0.05 <0.05 LCS-2 99% Envirolab Reference: Revision No: R 00 Page 5 of 7

18 Client Reference: Report Comments: Asbestos ID was analysed by Approved Identifier: Asbestos ID was authorised by Approved Signatory: Lulu Scott Lulu Scott INS: Insufficient sample for this test PQL: Practical Quantitation Limit NT: Not tested NR: Test not required RPD: Relative Percent Difference NA: Test not required <: Less than >: Greater than LCS: Laboratory Control Sample Envirolab Reference: Revision No: R 00 Page 6 of 7

19 Client Reference: Quality Control Definitions Blank: This is the component of the analytical signal which is not derived from the sample but from reagents, glassware etc, can be determined by processing solvents and reagents in exactly the same manner as for samples. Duplicate: This is the complete duplicate analysis of a sample from the process batch. If possible, the sample selected should be one where the analyte concentration is easily measurable. Matrix Spike : A portion of the sample is spiked with a known concentration of target analyte. The purpose of the matrix spike is to monitor the performance of the analytical method used and to determine whether matrix interferences exist. LCS (Laboratory Control Sample) : This comprises either a standard reference material or a control matrix (such as a blank sand or water) fortified with analytes representative of the analyte class. It is simply a check sample. Surrogate Spike: Surrogates are known additions to each sample, blank, matrix spike and LCS in a batch, of compounds which are similar to the analyte of interest, however are not expected to be found in real samples. Laboratory Acceptance Criteria Duplicate sample and matrix spike recoveries may not be reported on smaller jobs, however, were analysed at a frequency to meet or exceed NEPM requirements. All samples are tested in batches of 20. The duplicate sample RPD and matrix spike recoveries for the batch were within the laboratory acceptance criteria. Filters, swabs, wipes, tubes and badges will not have duplicate data as the whole sample is generally extracted during sample extraction. Spikes for Physical and Aggregate Tests are not applicable. For VOCs in water samples, three vials are required for duplicate or spike analysis. Duplicates: <5xPQL - any RPD is acceptable; >5xPQL % RPD is acceptable. Matrix Spikes, LCS and Surrogate recoveries: Generally % for inorganics/metals; % for organics (+/-50% surrogates) and % for labile SVOCs (including labile surrogates), ultra trace organics and speciated phenols is acceptable. In circumstances where no duplicate and/or sample spike has been reported at 1 in 10 and/or 1 in 20 samples respectively, the sample volume submitted was insufficient in order to satisfy laboratory QA/QC protocols. When samples are received where certain analytes are outside of recommended technical holding times (THTs), the analysis has proceeded. Where analytes are on the verge of breaching THTs, every effort will be made to analyse within the THT or as soon as practicable. Where sampling dates are not provided, Envirolab are not in a position to comment on the validity of the analysis where recommended technical holding times may have been breached. Envirolab Reference: Revision No: R 00 Page 7 of 7