Acton Campus Building #56 Hazardous Materials Report - ANU · ANU Hazardous Materials Register Site Location: Building 56, Leonard Huxley Building, Acton Campus Assessor: Anton Delac,

Acton CampusBuilding #56

Hazardous Materials Report

This document is uncontrolled once printed.You must consult the individual Building

Register prior to work commencing.

Contents Page1. Revision Table

2. ANU Hazardous Materials Register

3. ANU Hazardous Materials Maintenance Log

4. WSP Hazardous Materials Report Dated 21 February 2019

1. Revision Table – Building 56

Rev. Nature of changes Approval Date

1 Building 56 – Hazardous Materials Survey SWE 03/02/2014

2 Building 56 – Hazardous Materials Survey WSP 21/02/2019

3 Building 56 HazMat Survey – PS112993Other- Addition of ANU Hazardous Materials Register- Addition of ANU Hazardous Materials MaintenanceLog.- Addition of ANU Documentation

WSP 22/02/2019

2. ANU Hazardous Materials Register

Site Location: Building 56, Leonard Huxley Building, Acton Campus

Assessor: Anton Delac, Imam Malik, Joseph McNeill Inspection Date: 08 & 14 February 2019

Next Reinspection Date: February 2024

Sample No.

Res

ults

Phot

o ID

Description Location

Asb

esto

s Ty

pe

Con

ditio

n

Acc

essi

bilit

y

Airb

orne

Pot

entia

l

Expo

sure

Pot

entia

l

Ris

k Sc

ore

Act

ion

Prio

rity

Qua

ntity

(lm

, m2,

m3)

Actions/Comments

Asbestos Containing Materials

External Materials

WSP-110001 A, CHRefer toWSPReport

Fibre Cement Sheet Level 3 Eastern elevation (front) eave lining 1 1 2 2 2 8 L Throughout

Throughout level 1 to level 4 of rear building and level 3 tolevel 4 of front building perimeter.Maintain in good condition. Remove in accordance withWHS ACT document "How to Safely Remove Asbestos,Code of Practice 2014" prior to any majorrefurbishment/demolition.

WSP-110002 A, CHRefer toWSPReport

Fibre Cement Sheet Level 3 Eastern elevation (front) façade cladding 1 1 2 2 2 8 L Throughout

Throughout level 1 to level 4 of rear building and level 3 tolevel 4 of front building perimeter.Maintain in good condition. Remove in accordance withWHS ACT document "How to Safely Remove Asbestos,Code of Practice 2014" prior to any majorrefurbishment/demolition.

WSP-110028 CHRefer toWSPReport

Gasket Level 5, Roof, pipe flange gasket, pink colour 1 2 2 3 2 24 M <1m²

Maintain in good condition. Remove under friablecondition in accordance with WHS ACT document "How toSafely Remove Asbestos, Code of Practice 2014" prior toany major refurbishment/demolition.

Internal Materials


Joint Mastic Plant room 1.08, AHU ducting joint mastic 1 1 2 2 2 8 L Throughout

Maintain in good condition. Remove in accordance withWHS ACT document "How to Safely Remove Asbestos,Code of Practice 2014" prior to any majorrefurbishment/demolition.


Joint Mastic Plant room 1.08, AHU fresh air filter joint mastic 1 1 2 2 2 8 L Throughout

Maintain in good condition. Remove in accordance withWHS ACT document "How to Safely Remove Asbestos,Code of Practice 2014" prior to any majorrefurbishment/demolition.


Fibre Cement Sheet Level 2, Server room 206 riser wall infill panel 1 3 2 2 2 24 M 2m²

Remove loose panel on the floor.Maintain remaining asbestos wall panel in good conditionand labelled. Remove in accordance with WHS ACTdocument "How to Safely Remove Asbestos, Code ofPractice 2014" prior to any majorrefurbishment/demolition.


Brake Pad Level 6, Lift motor room, lift motor brake pad 1 2 2 3 2 24 M <1m²

Maintain in good condition. Remove under friablecondition in accordance with WHS ACT document "How toSafely Remove Asbestos, Code of Practice 2014" prior toany major refurbishment/demolition.

Lead Paint

WSP-110010 0.38%Refer toWSPReport

Brown paint system Level 1, Plant room 108, AHU compressor - - - - - - L ThroughoutMaintain in good condition.Remove prior to refurbishment/demolition.

Ozone Depleting Substances (ODS)

VisualObservation /Factory Label

Free ODSRefrigerant

Refer toWSPReport

Refrigerant Throughout - Air Conditioning Units - - - - - - - - No further action required.

Synthetic Material Fibres (SMF)

Refer toWSP-110026

SMFRefer toWSPReport

InsulationExternal - Level 2, North side adjacent store room 225E "ZonaAir" insulation

- - - - - - L 1 UnitMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

VisualAssessment


Pipe Insulation Plant room 1.08, hot water pipe insulation - - - - - - L ThroughoutMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

Refer toWSP-110012


Insulation/Filler Plant room 1.08, cable pipe penetration to wall - - - - - - L <1m²Maintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

VisualAssessment


Ceiling tiles Level 1, offices and store rooms, suspended ceiling tiles - - - - - - L ThroughoutMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

No SamplePresumed


Insulation Level 2, Gents toilet hot water unit - - - - - - L 1 UnitMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

Refer toWSP-110018


Ceiling tiles Level 2, hallway, suspended ceiling tiles - - - - - - L ThroughoutMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

VisualAssessment


Ceiling tiles Level 3, hallway, suspended ceiling tiles - - - - - - L ThroughoutMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

VisualAssessment


Ceiling tiles Level 4, hallway and office rooms, suspended ceiling tiles - - - - - - L ThroughoutMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

No asbestos detected

WSP-110006 OF, NADRefer toWSPReport

Fibre Cement Sheets External - Level 3, Rear top of facade lining - - - - - - - - No further action required.


Fibre Cement SheetsExternal - Level 1, Rear entry to room 1.18 above door wallinfill panel

- - - - - - - - No further action required.

WSP-110011 NADRefer toWSPReport

Gasket Plant room 1.08, Southeast corner pipe flange gasket - - - - - - - - No further action required.


Insulation Plant room 1.08, cable pipe penetration to wall - - - - - - - - No further action required.


Vermiculite Plant room 1.08, pipe penetration to wall - - - - - - - - No further action required.


Fibre Cement Sheet Level 2, disable toilet 2.22 wall lining - - - - - - - - No further action required.

WSP-110018 SMF, NADRefer toWSPReport

Ceiling tiles Level 2, hallway 2.01 suspended ceiling tiles - - - - - - - - No further action required.

WSP-110019 OF, SMF, NADRefer toWSPReport

Dust Level 2, Cupboard riser within room 205 - - - - - - - - No further action required.


Vermiculite Level 2, room 209 ceiling spray vermiculite - - - - - - - - No further action required.


Vinyl floor tiles Level 3, Hallway, north end cupboard floor tiles - - - - - - - - No further action required.


Bituminous Level 1 Rear concrete paving expansion joint - - - - - - - - No further action required.


Fibre Cement Sheet Level 1, Room 1.06A toilet wall lining - - - - - - - - No further action required.

WSP-110026 SMF, NADRefer toWSPReport

Insulation Level 2, adjacent store room 225E "Zona Air" insulation - - - - - - - - No further action required.


Fibre Cement Sheet Level 2, Room 225E Store wall lining - - - - - - - - No further action required.

Lead free Paints

WSP-110003 <0.005 %w/wRefer toWSPReport

Pale-blue paintsystem

Level 3, Eastern elevation (front) façade cladding - - - - - - - - No further action required.


Pale-blue paintsystem cream paintunderneath

Level 3, Front porch brick wall - - - - - - - - No further action required.


White paint system Level 3, Front porch metal beam - - - - - - - - No further action required.

WSP-110025 0.005% w/wRefer toWSPReport

Blue paint system Level 1. Door panel to room 1.11 - - - - - - - - No further action required.


Brown paint system Level 2, North of Room 225E "Zona Air" metal cover - - - - - - - - No further action required.


White paint system Roof (Level 5), Water piping and metal beams - - - - - - - - No further action required.


Blue paint systemand red paintunderneath

Roof (Level 5), Window to level 6 - - - - - - - - No further action required.

Polychlorinated Biphenyls (PCB'S)

VisualAssessment

Ducon PCBCapacitor

Refer toWSPReport

Fluorescent lightfittings

Plant room 1.08, wall & ceiling light fittings - - - - - - L Throughout

Throughout the level with old type fluorescent lightfittings.Maintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

VisualAssessment

Ducon PCBCapacitor

Refer toWSPReport


Level 3, Throughout hallways and office rooms ceiling lightfittings

- - - - - - L ThroughoutMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

VisualAssessment

Ducon PCBCapacitor

Refer toWSPReport


Level 3, Throughout hallways and office rooms ceiling lightfittings

- - - - - - L ThroughoutMaintain in good condition. Remove in accordance withstate and national guidelines prior to any majorrefurbishment/demolition.

3. ANU Hazardous Materials Maintenance Log

Hazardous Materials Maintenance Log

Site: Building 56

ANU Hazardous Materials Maintenance Log The following log should be maintained by the responsible person. It should contain information relating to the on-going maintenance or control measures associated

with ACM including removal, remedial works, repairs, inspection, monitoring and clearance details etc.

Site: Building 56

Date Scope/Location Carried out by Result/Comments Entered by

08/02/2019 Hazardous Materials Survey Anton Delac, Imam Malik &

Joseph McNeill

Undertake a survey of the site

to identify and access

hazardous materials.

Imam Malik – WSP

21/02/2019

Jaeger Swanepoel Additions Jaeger Swanepoel – WSP

22/02/2019

22/02/2019 Hazardous Materials Survey Report

completed – Building 60

Additions – ANU Cover page, Register,

Maintenance Log

4. WSP Hazardous Material Report

THE AUSTRALIAN NATIONAL UNIVERSITY

J056 - LEONARD HUXLEY BUILDING MILLS ROAD, ACTON ACT 2601

HAZARDOUS MATERIALS SURVEY

FEBRUARY 2019 CONFIDENTIAL

This document may contain confidential and legally privileged information, neither of which are intended to be waived,

and must be used only for its intended purpose. Any unauthorised copying, dissemination or use in any form or by any

means other than by the addressee, is strictly prohibited. If you have received this document in error or by any means

other than as authorised addressee, please notify us immediately and we will arrange for its return to us.

PS112993-HAZ-REP-ANU Building 56 Confidential February 2019

J056 - Leonard Huxley Building

Mills Road, Acton ACT 2601

Hazardous Materials Survey

The Australian National University

WSP

Level 1, 121 Marcus Clarke Street

Canberra ACT 2601

PO Box 1551

Canberra ACT 2600

Tel: +61 2 6201 9600

Fax: +61 2 6201 9666

wsp.com

REV DATE DETAILS

1 21/02/2019 Original

NAME DATE SIGNATURE

Prepared by: Jaeger Swanepoel 18/02/2019

Reviewed by: Imam Malik 21/02/2019

Approved by: Anton Delac 21/02/2019

1 INTRODUCTION ............................................................... A-1

1.1 LEGISLATIVE REQUIREMENTS ........................................... A-1

1.2 OBJECTIVES .......................................................................... A-2

1.3 SCOPE OF WORK .................................................................. A-2

1.3.1 TASK 1 – PRE- SITE INSPECTION PREPARATION ........................ A-2 1.3.2 TASK 2 – SITE INSPECTION AND SAMPLE COLLECTION ............. A-2 1.3.3 TASK 3 – ANALYSIS OF SUSPECT MATERIALS ............................. A-2 1.3.4 TASK 4 – REPORTING & HAZARDOUS MATERIALS

REGISTER ......................................................................................... A-3

2 METHODOLOGY .............................................................. A-4

2.1 GENERAL ............................................................................... A-4

2.2 IDENTIFICATION OF MATERIAL .......................................... A-4

2.2.1 ASBESTOS CONTAINING MATERIAL .............................................. A-4 2.2.2 LEAD-BASED PAINT SYSTEMS ....................................................... A-4 2.2.3 SYNTHETIC MINERAL FIBRES (SMF) MATERIALS ........................ A-4 2.2.4 POLYCHLORINATED BIPHENYLS (PCBS) ...................................... A-4 2.2.5 OZONE DEPLETING SUBSTANCES (ODS) ..................................... A-5

3 RESTRICTIONS / INACCESSIBLE AREA .................... A-6

4 SURVEY FINDINGS ......................................................... A-7

5 RECOMMEDATION FOR REMOVAL............................ A-9

5.1 GENERAL SITE ESTABLISHMENT ...................................... A-9

5.2 ENCLOSURE SET-UP ............................................................ A-9

5.3 NON-FRIABLE ACM FROM THE BUILDING ...................... A-10

5.4 FRIABLE ACM FROM THE INTERIOR OF THE

BUILDING ............................................................................. A-10

5.4.1 REMOVAL OF GASKET OR ROPE SEALS ..................................... A-10 5.4.2 REMOVAL OF ASBESTOS-BACKED VINYL ................................... A-11

5.5 SYNTHETIC MINERAL FIBRES (SMF) ............................... A-11

5.6 LEAD ..................................................................................... A-11

5.7 POLYCHLORINATED BIPHENYLS (PCBS) ....................... A-12

5.8 OZONE DEPLETING SUBSTANCES (ODS) ....................... A-12

6 CLOSE .............................................................................A-13

TABLE OF CONTENTS

APPENDICES

APPENDIX A – PHOTOGRAPHS

APPENDIX B – HAZARDOUS MATERIALS REGISTER

APPENDIX C – CERTIFICATES OF ANALYSIS

APPENDIX D – FLOOR PLAN

APPENDIX E – RISK ASSESSMENT

APPENDIX F – STATEMENT OF LIMITATIONS

Project No PS112993 J056 - Leonard Huxley Building Mills Road, Acton ACT 2601 Hazardous Materials Survey The Australian National University

WSP February 2019

Page A-1

1 INTRODUCTION WSP Australia was engaged by Brett Morrison the Asset Planning Officer for the Engineering & Technical Services,

Facilities and Services team of The Australian National University to undertake a hazardous materials survey of the

Building J056 – “Leonard Huxley Building” located at Mills Road, Australian National University (ANU), Acton ACT

2601.

The purpose of the survey was to identify the presence of hazardous materials and provide a management plan for the

building.

The survey was undertaken by licensed asbestos assessors, Anton Delac (License no. AA00007), Imam Malik (License

no. LAA001048) and Joseph McNeill (License no. AA464842), on behalf of WSP Australia on 8th and 14th February

2019.

For the purpose of this report, the term hazardous materials (HAZMAT) refers to the following:

— Asbestos containing materials (ACM);

— Lead based paints;

— Synthetic mineral fibre (SMF) materials,

— Light fittings and accessible electrics that may contain polychlorinated biphenyls (PCB) capacitors and;

— Ozone depleting substances (ODS)

This report provides a summary of the methodology, references, purpose and scope of works.

No one section or part of a section of this Report should be taken as giving an overall idea of this Report. Each section

must be read in conjunction with the whole of this Report, including the hazardous materials registers and sample results.

1.1 LEGISLATIVE REQUIREMENTS

The survey works and production of this report have been undertaken in accordance with the requirements of the

following documents:

— Work Health and Safety Regulation 2017

— Work Health and Safety (How to Manage and Control Asbestos in the Workplace: Code of Practice) 2014 (ACT)

— Work Health and Safety (How to Safely Remove Asbestos: Code of Practice) 2014 (ACT).

— National Code of Practice for the Control and Safe Use of Inorganic Lead at Work 1994.

— National Code of Practice for the Safe Use of Synthetic Mineral Fibres 1990.

— ANZECC (1997) Identification of PCB-containing Capacitors: An information booklet for Electricians and

Electrical Contractors.

— AS 1216, Standards Association of Australia, Classification and Class Labels for Dangerous Goods

— AS 1319, Standards Association of Australia, Rules for the Design and Use of Safety Signs for the Occupational

Environment

— AS 1715, Standards Association of Australia, Selection, Use and Maintenance of Respiratory Protective Devices

— AS 1716, Standards Association of Australia, Respiratory Protective Devices

— AS4361.2 2017 Guide to Lead Paint Management Part 2: Residential, Public & Commercial buildings


WSP February 2019

Page A-2

— AS 2601 Demolition of Structures

— AIOH positional paper: Synthetic Mineral Fibres and Occupational Health Issues 2011

— NOHSC (1989b). Guidance Note on the Membrane Filter Method for the Estimation of Airborne Synthetic Mineral

Fibres. [NOHSC:3006 (1989)] June 1989

— National Standard for Synthetic Mineral Fibres [NOSHC:1004 (1990)]

— National Code of Practice for the Safe Use of Synthetic Mineral Fibres [NOSHC:2006 (1990)]

— AS 3640 Workplace atmospheres - Methods for sampling and gravimetric determination of inhalable dust 2009

1.2 OBJECTIVES

The objectives of the hazardous material survey were to:

— identify hazardous materials;

— provide a qualitative risk assessment of the hazardous materials identified;

— provide recommendations on the control measure strategies in the event of any refurbishment or demolition works;

and

— prepare a hazardous materials register and hazardous materials management plan to ensure compliance with state

legislation, Commonwealth codes of practice and Australian Standards as outlined in Section 1.1 above.

1.3 SCOPE OF WORK

The investigation will be undertaken to identify and document all visible and accessible hazardous materials (if

identified) as far as reasonably practicable.

The scope of works covers the following:

1.3.1 TASK 1 – PRE- SITE INSPECTION PREPARATION

— Provide a Safe Work Method Statement (SWMS) for the activities on site, ensuring hazards identified within are

safely inspected for asbestos and documented within a detailed hazardous material(s) register.

1.3.2 TASK 2 – SITE INSPECTION AND SAMPLE COLLECTION

— Site investigations, includes identification of hazardous materials, location, type, condition, extent and qualitative

risk assessment;

— Sampling of representative materials suspected of containing asbestos; and

— Sampling of representative paint systems for the purpose of confirming lead content.

1.3.3 TASK 3 – ANALYSIS OF SUSPECT MATERIALS

Suspected ACM and lead containing paint collected during the survey were sent to NATA accredited laboratories for

analysis.


WSP February 2019

Page A-3

1.3.4 TASK 4 – REPORTING & HAZARDOUS MATERIALS REGISTER

All data generated from the survey was used to update the hazardous materials register/spread sheet, which identifies and

defines the condition of the materials, lists any factual findings and provides consideration to their removal priority.


WSP February 2019

Page A-4

2 METHODOLOGY

2.1 GENERAL

The identification of hazardous materials involves a combination of visual inspection of the accessible areas of the

building/structure and the collection of representative samples of the suspect materials for the purpose of analytical

confirmation. Where identical suspect materials are detected at different locations, visual confirmation only may have

been made rather than additional sample collection.

2.2 IDENTIFICATION OF MATERIAL

2.2.1 ASBESTOS CONTAINING MATERIAL

Representative samples of materials suspected of containing asbestos were collected and analysed at our in-house NATA

accredited laboratory. The identification of asbestos fibres is based on using polarised light microscopy supplemented

with dispersion staining techniques. This is detailed in Australian Standard 4964-2004 ‘Method for the qualitative

identification of asbestos in bulk samples’. Asbestos samples were only collected for analysis where the safety of

personnel would not be compromised. Sampling was conducted in accordance with the WSP’s in house survey guide and

the United Kingdom Health & Safety Executive publication, ‘Methods for the Determination of Hazardous Substances

100, surveying, sampling and assessment of asbestos-containing materials’.

2.2.2 LEAD-BASED PAINT SYSTEMS

Representative samples of paint were collected and analysed at Envirolab Services NATA Accredited Laboratory. Lead

content is reported in percentage weight by weight and compared with AS4361.2-2017, Guide to Lead Paint

Management, Part 2: Residential and Commercial Buildings lead containing paint system level of 0.1 per cent (w/w) of

the dried film.

2.2.3 SYNTHETIC MINERAL FIBRES (SMF) MATERIALS

The survey for SMF was undertaken in accordance with the guidelines documented in the Code of Practice for the Safe

Use of Synthetic Mineral Fibres [NOHSC: 2006 (1990)]. This includes documenting any materials visually assessed on

site as being consistent with SMF.

Our experienced surveyor visually identified and recorded the presence of synthetic mineral fibre products onsite.

The roof space and all levels containing ceiling voids must be visually inspected to verify the presence of SMF.

Additionally, special detail must also be paid to pipework and ducting insulations types.

2.2.4 POLYCHLORINATED BIPHENYLS (PCBS)

Where access was available and power was isolated representative examples of each major type of fluorescent light

fittings were examined to determine which lights were fitted with PCB containing ballast capacitors. The details of the

brand, model of each capacitor and capacity were recorded and checked against with the ANZECC database of known

PCB capacitors and PCB free capacitors.

The Australian and New Zealand Environment Conservation Council ‘Polychlorinated Biphenyls Management Plan,

November 1996’ outlines the National Strategy for the management of PCBs.


WSP February 2019

Page A-5

The document defines PCB materials and wastes as follows:

Table 2.1 PCB concentration classification

PCB concentration Waste classification

<2 mg/kg - PCB free.

2 mg/kg - <50 mg/kg - Non-Scheduled PCB material or waste.

>50 mg/kg - Scheduled PCB material or waste.

>100,000 mg/kg (10%) - Concentrated PCB material.

2.2.5 OZONE DEPLETING SUBSTANCES (ODS)

The main cause of ozone depletion and the ozone hole is man-made chemicals, especially man-made halocarbon

refrigerants, solvents, propellants, and foam-blowing agents which are commonly referred to as ozone-depleting

substances (ODS).

The identification of potentially ODS, such as industrial refrigerators and air conditioning units, were visually identified

during the current survey.

Where ODS have been previously identified at the site, they have been included in the updated HAZMAT register.


WSP February 2019

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3 RESTRICTIONS / INACCESSIBLE

AREA

Every effort was made to access all areas of the buildings; however, some areas were restricted due to building damage,

excessive heights and electrical hazards. This included, but is not limited to the following areas:

— The roof-line to all buildings and structures over 3.0m in height;

— Inground and underground services (pits / pipes / etc);

— Inset pipe-works to the brick/concrete walls

— Under ceramic tiles to walls and floors

— All live electricity and mechanical plant/equipment

— All electrical boards and circuit breakers.

In general, a presumption should be made that hazardous materials are present within areas not able to be accessed during

the survey. Caution should be given during demolition works and works ceased if suspected hazardous materials are

encountered and an assessment undertaken by a suitably qualified hazardous materials expert.


WSP February 2019

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4 SURVEY FINDINGS

This section of the report summarises the findings of the asbestos materials types identified and their general locations.

All findings are presented in Appendix A: Asbestos Materials Register. The register is supplemented with photos within

Appendix B: Photographs

Table 4.1 Asbestos Containing Materials

LOCATION DESCRIPTION COMMENTS

External - Level 3 & 4, Eastern elevation (front) eave linings

Asbestos containing fibre cement sheet

Maintain in good condition. Remove in accordance with WHS ACT document "How to Safely Remove Asbestos, Code of Practice 2014" prior to any major refurbishment/demolition.

External - Level 3 & 4, Eastern elevation (front) façade cladding



External - Level 1, 2, 3 & 4, Western elevation (rear) eave linings



External - Level 1, 2, 3 & 4, Western elevation (rear) façade cladding



Internal – Plant room 1.08, AHU ducting joint mastic

Asbestos containing joint mastic


Internal – Level 2, Server room 206, riser wall infill panel


Remove loose panel on the floor.

Maintain remaining asbestos wall panel in good condition and labelled. Remove in accordance with WHS ACT document "How to Safely Remove Asbestos, Code of Practice 2014" prior to any major refurbishment/demolition.

Internal – Level 6, Lift motor room, lift motor brake

Asbestos containing brake pad


Table 4.2 Synthetic Materials (SMF’s)


External – Level 2, North side

adjacent store room 225E "Zona Air"

insulation

SMF Insulation Maintain in good condition. Remove in

accordance with state and national guidelines

prior to any major refurbishment/ demolition.

Internal - Plant room 1.08, hot water

pipe insulation

SMF Pipe Insulation Maintain in good condition. Remove in




WSP February 2019

Page A-8


Plant room 1.08, cable pipe

penetration to wall

SMF Insulation/filler Maintain in good condition. Remove in



Internal - Level 1, offices and store

rooms, suspended ceiling tiles

SMF ceiling tiles Maintain in good condition. Remove in



Internal - Level 2, toilet hot water unit Presumed SMF insulation Maintain in good condition. Remove in



Internal - Level 2 & 3, hallway,

suspended ceiling tiles




Internal - Level 4, hallway and office

rooms, suspended ceiling tiles




Table 4.3 Lead Based Paint


Internal - Level 1, Plant room 108,

paint to AHU compressor

Brown Paint system Peel off in some areas. Recommendations to

either

1) Encapsulate and/or monitor the status on the

paint; or

2) Remove in accordance with state and national

guidelines.

Table 4.4 Ozone Depleting Substances (ODS’s)


External – Throughout No ODS Refrigerant No further action required.

Table 4.5 Polychlorinated Biphenyls (PCB’s)


Internal - Level 1 (Plant Room 108) throughout Level, old type fluorescent light fittings

PCB capacitors Maintain in good condition. Remove in accordance with state and national guidelines prior to any major refurbishment/ demolition.

Internal - Level 2 throughout, old type fluorescent light fittings


Internal - Level 2 throughout, old type fluorescent light fittings



WSP February 2019

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5 RECOMMEDATION FOR REMOVAL

5.1 GENERAL SITE ESTABLISHMENT

� The asbestos containing materials should be removed prior to the commencement of demolition works.

The asbestos removal works are to be conducted in accordance with the SafeWork Australia document How to

Safely Remove Asbestos – Code of Practice.

� All asbestos removal, transport and disposal must be performed in accordance with ACT legislative requirements.

� Where asbestos cannot be removed prior to mechanical demolition (e.g. where structures are unsound, inhibiting

access to asbestos removal personnel), dust suppression must be employed during demolition. All building waste

suspected of containing asbestos must be removed as asbestos waste and placed in appropriately lined bins/trucks

for disposal to an approved waste facility.

� It is recommended that the removal works to be undertaken by a licenced asbestos removal contractor. The removal

to be undertaken in accordance with the code of practice noted above and by a licenced asbestos removal contractor.

� Environmental management and WHS procedures should be put in place for the asbestos removal during demolition

works to protect the workers, surrounding residents and environment.

� It is recommended that a licenced asbestos assessor is engaged to carry out asbestos fibre air monitoring during the

removal of the asbestos materials if asbestos removal works are to take place during other demolition works. The

monitoring is to be conducted in accordance with the National Occupational Health and Safety Commission

Guidance Note on the Membrane Filter Method for the Estimating Airborne Asbestos Fibre, 2nd Edition [NOHSC

3003(2005)], April 2005, by a NATA accredited laboratory such as WSP Australia.

� At all times “H Class” asbestos vacuums and negative air units fitted with HEPA filters are to be used during

asbestos removal and remediation. These are to be regularly tested and maintained to operate at 99.995% efficiency,

in accordance with the manufacturer’s instructions.

� Filters for “H Class” vacuums should conform to the requirements for AS 4260-1997 High efficiency particulate are

(HEPA) filters – Classification, construction and performance or its equivalent.

� Disposal of asbestos containing material must be undertaken in accordance the SafeWork Australia document How

to Safely Remove Asbestos – Code of Practice 2014 and the ACT EPA Guidelines at a land fill site licenced to

accept asbestos waste.

5.2 ENCLOSURE SET-UP

� Potential entry points to the asbestos work area should be signposted and barrier taped in accordance with AS1319-

1994 Safety Signs for the Occupational Environment.

� A minimum 3 stage decontamination unit with clean change-shower-dirty shower-dirty change areas must also be

installed and used under negative air pressure. Water from the decontamination unit should be captured, filtered,

and the filters are to be disposed of as asbestos waste.

� Construction of the main negative air enclosures may require the inclusion of the outer brick walls in order to

maintain negative air conditions in the interior of the building. To obtain negative air conditions in the roof space,

the contractor will be required to place plastic sheeting (minimum of 200µm thickness) over the roof tiles or roof

sheets, eaves and back to the brick outer walls. All windows and penetrations to the dwelling such as vents will be

sealed with 200µm plastic sheeting.


WSP February 2019

Page A-10

� In order to complete the above it may be necessary to remove items such as awnings, solar panels, fences, trellises

or other fittings attached to the house, that may impact upon enclosure or scaffold set-up.

� Once the enclosure set-up is complete an asbestos assessor is conduct an enclosure integrity test to all the seals of

the enclosure and to measure the flow of the negative pressure units to ensure that it can maintain negative pressure.

Work can only commence once the asbestos assessor has deemed the enclosure to be “satisfactory” to do so. A

manometer is to be attached to the enclosure to ensure that negative air pressure within is above 12 kPa.

5.3 NON-FRIABLE ACM FROM THE BUILDING

� Remove non-friable ACM material with minimal breakage.

� Maintain work in progress air monitoring (Control and Perimeter Locations).

� Refer to Worksafe ACT How to Safely Remove Asbestos Code of Practice 2014.

� Please Note that If present, all nails, screws and fasteners associated with ACM must be removed and disposed of as

asbestos contaminated waste. All timber or metal battens must be decontaminated with the use of a HEPA vacuum

cleaner.

� Place fragments of AC Sheeting material in 200µm polythene bags which are no longer than 1200mm and no wider

than 900mm.

� Place sheets of AC Sheeting directly into a bin in close proximity to works, lined with 200 µm plastic, and kept

damp to minimise the generation of airborne asbestos. Ensure that the bin is labelled and if to remain on site for any

period of time, kept secure at all times.

� In relation to the asbestos containing joint mastic and electrical backing board, polythene sheeting drop sheets

should be placed under the material. The material removed with minimal breakage and placed within 200 µm thick

polythene bags or wrapped with 200 µm thick polythene sheeting. Any fixtures or fittings associated with the

material such as screws, nails or brackets should be removed asbestos waste or if possible decontaminated. The

area should be clear of any visible dust following the removal.

� Following the satisfactory clearance inspection and if deemed necessary by the licenced asbestos assessor, tinted

PVA solution should be sprayed on timber or metal battens and polythene drop sheets prior to its removal for the

work area and disposal.

� Following the completion of the above, an ‘emu or sparrow pick’ of the ground surface in proximity to removal

works (and along any waste/work route) is to be undertaken to remove any fragments of AC sheeting. All fragments

are to be placed in 200 µm thick polythene bags which are no longer than 1200 mm and no wider than 900 mm

wide. Bags are to be sealed and double bagged to reduce the risk of the bags splitting.

� Once the pick is complete, a clearance is to be conducted by the licenced asbestos assessor.

5.4 FRIABLE ACM FROM THE INTERIOR OF THE BUILDING

5.4.1 REMOVAL OF GASKET OR ROPE SEALS

The asbestos in gaskets and rope from plant and equipment will be friable. An enclosure with negative air extraction units

must be used for this type of asbestos removal work. When removing gaskets and rope seals: ensure the plant or

equipment is shut down and isolated

� dismantle the equipment carefully. Protect any other components with plastic sheeting;

� ensure the plant and equipment has been made safe (pipework emptied, electrical supply isolated and equipment

shutdown, etc.);

� unbolt or unscrew the flange or dismantle the equipment;


WSP February 2019

Page A-11

� once accessible, dampen the asbestos with a fine water mist or similar. Continue dampening the asbestos as more of

it is exposed/accessible;

� ease the gasket or rope seal away with the scraper and place into the waste container positioned directly

beside/beneath it. Keep the area damp and scrape away any residue; and

� consider using an industrial vacuum cleaner fitted with a HEPA filter while scraping.

5.4.2 REMOVAL OF ASBESTOS-BACKED VINYL

As asbestos millboard is typically 100 per cent asbestos and very friable. An enclosure with negative air extraction units

must be used for this type of asbestos removal work.

� The asbestos millboard should be wetted down as the vinyl is peeled from the floor, preferably with the millboard

attached.

� The vinyl can be cut into strips prior to its removal to facilitate bagging, or it can be rolled into one roll and

wrapped securely with plastic, making sure it is totally sealed.

� If the vinyl sheeting cannot be removed without leaving some of the asbestos millboard on the floor surface, the

remaining asbestos millboard should be wetted down and, when thoroughly soaked, scraped off the floor surface.

� Sufficient water should be used to dampen the asbestos millboard, but not so much that run-off or pools of

contaminated water will occur.

� Alternative removal methods should only be used if they do not result in excessive fibre release from the asbestos

millboard and do not result in any additional hazard.

5.5 SYNTHETIC MINERAL FIBRES (SMF)

Synthetic Mineral Fibres may be classified as hazardous depending on their age and manufacturing origin. It is therefore

recommended that some precautionary measures be implemented to ensure adequate protection of workers from potential

exposure.

Where SMF materials are to be handled or disturbed, the precautionary measures as outlined in the National

Occupational Health and Safety Commission's National Code of Practice for the Safe use of Synthetic Mineral Fibre Products [NOHSC:2006(1990)] should be observed. The general requirements are as follows:

� Personal protective clothing (long sleeve, loose fitting), gloves and half face (Class P1 or P2) respirators should be

used, as well as eye protection and head covering in some circumstances.

� The work area should be isolated and signposted.

� Waste material should be bagged or sealed in solid containers prior to transport and disposal.

5.6 LEAD

� It is recommended that the easily detachable items containing lead paint do not require to go through the lead paint

removal procedures (i.e. wet sanding, chemical stripping or hand scrapping). However, when these items are

removed it is recommended that 200 micron thick drop sheets are to be placed on all ground surfaces in proximity to

the works and wrapped in 200 micron thick plastic sheeting to prevent contamination to the ground surfaces

surrounding the building.

� Items that cannot be easily removed which contain lead paint will be demolished under controlled conditions to

reduce limit further ground contamination to the site and the waste will be included with demolition waste. Controls

will consist of but not limited too;


WSP February 2019

Page A-12

� Spraying the lead in paint surface with a binding agent to limit potential paint flakes or dust depositing on the ground

surface;

� Bunding around the demolition area to contain water run-off;

� Water dust suppression during the demolition and loading phase; and

� A minimum 10 metre exclusion zone around the demolition and loading out of the demolition waste.

As a precautionary and control measure, static lead in air monitoring should be undertaken during the remediation works

in accordance with Australian Standard AS 3640-2004 Workplace atmospheres - Method for sampling and gravimetric

determination of inhalable dust by an experienced environmental scientist.

� Clearance certification should be undertaken at the completion of the removal work. The clearance inspection should

to be carried out by an occupational hygienist or licensed asbestos assessor specialised in the management of

hazardous materials.

� Environmental management and OH&S procedures should be put in place for the remediation works to protect the

workers and the environment.

5.7 POLYCHLORINATED BIPHENYLS (PCBS)

If the presence of PCB’s can be confirmed with the light fittings the following should be followed for the safe removal;

� A detailed and site-specific work scope and technical specification will be developed prior to the removal of

‘hazardous materials’ from the residence;

� In accordance with the NSW WHS Regulations 2012 and NSW WHS Act 2012, removal of hazardous materials

must be completed by a contractor licensed to remove hazardous materials (i.e. asbestos, lead, PCBs) and must be

completed under a site-specific permit. This permit can only be applied for by a licensed and qualified hazardous

materials removal contractor; and

� Removal of PCB containing materials is recommended to be removed by a qualified contractor with experience in

hazardous waste and PCB removal. The removal contractor must follow legislative requirements for the PCB

containing materials removal.

5.8 OZONE DEPLETING SUBSTANCES (ODS)

� Remove in accordance with the AIRAH Refrigerant Handling Code of Practice 2007.

� Unit should be de-gassed by a licensed HVAC technician before disposal. As per the ozone protection and synthetic greenhouse gas management regulations 1996 (amended 2016).


WSP February 2019

Page A-13

6 CLOSE Thank you for the opportunity to be involved with the on-going management of hazardous materials at ANU.

If you have any queries regarding this report, please feel free to contact any of the undersigned on +61 2 6201 9600.

Yours sincerely,

Anton Delac

Senior Occupational Hygiene & Hazardous Materials Consultant

OHHS Team Leader - ACT

Licensed Asbestos Assessor - No. AA00007 ACT

On behalf of WSP Australia Pty Limited

Joseph McNeill

Occupational Hygiene Consultant

Licensed Asbestos Assessor - No. AA464842 NT


Imam Malik

Occupational Hygiene Consultant

Licensed Asbestos Assessor - No. LAA001048 NSW


PHOTOGRAPHS


WSP February 2019

Page A-15

Photograph 1. External – Level 3 Eastern elevation (front)

eave lining – WSP-110001 - Chrysotile and Amosite

Asbestos Detected.

Photograph 2. External - Level 3 Eastern elevation (front)

façade cladding – WSP-110002 - Chrysotile and Amosite

Asbestos Detected.

Photograph 3. Level 5 Roof, pipe flange gasket cladding –

WSP-110028 - Chrysotile Asbestos Detected.

Photograph 4. Internal – Plant room 1.08, AHU ducting joint

mastic – WSP-110008 - Chrysotile Asbestos Detected.

Photograph 5. Internal – Plant room 1.08, AHU fresh air

filter joint mastic – WSP-110009 - Chrysotile Asbestos

Detected.

Photograph 6. Internal – Level 2, Server room 206 riser wall

infill panel – WSP-110020 - Chrysotile Asbestos

Detected.


WSP February 2019

Page A-16

Photograph 7. Internal - Lift motor room, lift motor brake

pad – WSP-110032 - Chrysotile Asbestos Detected.

Photograph 8. External – Level 2, North side adjacent store

room 225E "Zona Air" insulation – WSP-110026 – SMF

Detected

Photograph 9. Internal - Plant room 1.08, hot water pipe

insulation – SMF Insulation

Photograph 10. External – Level 1, office and store rooms,

suspended ceiling tiles – SMF Ceiling Tiles

Photograph 11. Internal - Level 2, hallway, suspended

ceiling tiles – WSP-110018 - SMF Ceiling Tiles

Photograph 12. Internal - Level 2, Gents toilet hot water

unit – Presumed SMF Insulation


WSP February 2019

Page A-17

hotograph 13. Internal - Level 3, hallway, suspended ceiling

tiles – SMF Ceiling Tiles

Photograph 14. Level 4, hallway and office room,

suspended ceiling tiles – SMF Ceiling Tiles

Photograph 15. Internal - Plant room 1.08, wall & ceiling

light fittings – Ducon Capacitor

Photograph 16. Internal – Level 2, hallway and rooms

ceiling light fittings - Ducon Capacitor

Photograph 17. Internal – Level 3, hallway and rooms

ceiling light fittings - Ducon Capacitor

Photograph 18. Internal – Level 1, Plant room 108, AHU

compressor – WSP-1100101 - 0.38% w/w lead detected

HAZARDOUS MATERIALS REGISTER

Building J057 "Leonard Huxley" - Australian Nation University ACT IHT

ACM - Asbestos Containing Material, CH - Chrysotile, A - Amosite, C - Crocidolite, PCB's - Polychlorinated Biphenyls, ODS - Ozone Depleting Substances, NAD - No Asbestos Detected, Pr - Presumed, OF - Organic Fibres Page 1 of 3

Building NameProperty Address

J056 "Leonard Huxley Building", Mills Road - Acton ACT2601 Dates of inspection 08/02/2019 &

14/02/2019 Inaccessible areas • The roof-line to all buildings and structures over 3.0m in height• Inground and underground services (pits / pipes / etc)• Portions of Ceiling voids• Portion of wall cavities• Inset pipe-works to the walls throughout• All live electricity and mechanical plant/equipment• All electrical boards and circuit breakers

Property Description

The property consist of four storey main building and twostorey roof level. It incorporated many Offices,Laboratories, Computer Data Room, Storage Facilities andServices

Inspected byAnton DelacImam MalikJoseph McNeill

Event Location Application Material Description Sample Number Analytical Result Photo Extent Estimate Friability

Material

Condition

Risk Status

Control

Priority

Control Recommendations/ Comments

Consultant / Hygienist

name

Control action taken Date actioned Contractor details

Building 56 - External - Asbestos Containing Materials

1 Level 3 Eastern elevation (front) eave lining Eave lining Fibre Cement Sheet WSP-110001 A, CH 1 Throughout Non Friable Good Low Low

Throughout level 1 to level 4 of rear building and level3 to level 4 of front building perimeter.Maintain in good condition. Remove in accordancewith WHS ACT document "How to Safely RemoveAsbestos, Code of Practice 2014" prior to any majorrefurbishment/demolition.

2 Level 3 Eastern elevation (front) façadecladding Cladding Fibre Cement Sheet WSP-110002 A, CH 2 Throughout Non Friable Fair Low Low

Throughout level 1 to level 4 of rear building and level3 to level 4 of front building perimeter.Maintain in good condition. Remove in accordancewith WHS ACT document "How to Safely RemoveAsbestos, Code of Practice 2014" prior to any majorrefurbishment/demolition.

3 Level 5, Roof, pipe flange gasket Pink colour gasket Gasket WSP-110028 CH 3 <1m2 Non Friable Fair Low Low

Maintain in good condition. Remove in accordancewith WHS ACT document "How to Safely RemoveAsbestos, Code of Practice 2014" prior to any majorrefurbishment/demolition.

Building 56 - Internal - Asbestos Containing Materials

4 Plant room 1.08, AHU ducting joint mastic Joint mastic Mastic WSP-110008 CH 4 Throughout Non Friable Fair Low Low


5 Plant room 1.08, AHU fresh air filter jointmastic Joint Mastic Mastic WSP-110009 CH 5 Throughout Non Friable Good Low Low


6 Level 2, Server room 206 riser wall infillpanel Wall infill panell Fibre Cement Sheet WSP-110020 CH 6 2m2 Non Friable Fair Med Med

Remove loose panel on the floor.Maintain remaining asbestos wall panel in goodcondition and labelled. Remove in accordance withWHS ACT document "How to Safely RemoveAsbestos, Code of Practice 2014" prior to any majorrefurbishment/demolition.

7 Level 6, Lift motor room, lift motor brake Lift motor brake pad Brake pad WSP-110032 CH 7 <1m2 Non Friable Fair Med Med

Remove the loose panel on floor.Maintain in good condition. Remove in accordancewith WHS ACT document "How to Safely RemoveAsbestos, Code of Practice 2014" prior to any majorrefurbishment/demolition.

Building 56 - External - No Asbestos Containing Materials

8 Level 3, Rear top of facade lining Lining Fibre Cement Sheet WSP-110006 OF, NAD - Throughout - - - - No further action required.

9 Level 1, Rear entry to room 1.18 abovedoor wall infill panel Infill panell Fibre Cement Sheet WSP-110007 OF, NAD - 3m2 - - - - No further action required.

10 Level 1 Rear concrete paving expansionjoint Expansion joint Bituminous WSP-110023 NAD - Throughout - - - - No further action required.

11 Level 2, adjacent store room 225E "ZonaAir" insulation Insulation Insulation WSP-110026 SMF, NAD - 2m2 - - - - No further action required.

Building 56 - Internal - No Asbestos Containing Materials



12 Plant room 1.08, Southeast corner pipeflange gasket Flange gasket Gasket WSP-110011 OF, NAD - <1m2 - - - - No further action required.

13 Plant room 1.08, cable pipe penetration towall Insulation wall filler Insulation WSP-110012 SMF, NAD - <1m2 - - - - No further action required.

14 Plant room 1.08, pipe penetration to wall Vermiculite wall filler Vermiculite WSP-110013 OF, NAD - <1m2 - - - - No further action required.

15 Level 2, disable toilet 2.22 wall lining Wall lining Fibre Cement Sheet WSP-110017 OF, NAD - 20m2 - - - - No further action required.

16 Level 2, hallway 2.01 suspended ceilingtiles Ceiling tiles Ceiling tiles WSP-110018 SMF, NAD - 20m2 - - - - No further action required.

17 Level 2, Cupboard riser within room 205 Floor dust Dust WSP-110019 OF, SMF, NAD - 1m2 - - - - Remove incorrect label.No further action required.

18 Level 2, room 209 ceiling spray vermiculite Ceiling spray vermiculite Vermiculite WSP-110021 NAD - Throughtout - - - - No further action required.

19 Level 3, Hallway, north end cupboard floortiles Vinyl floor tiles Vinyl floor tiles WSP-110022 NAD - 2m2 - - - - No further action required.

20 Level 1, Room 1.06A toilet wall lining Wall lining Fibre Cement Sheet WSP-110024 OF, NAD - 24m2 - - - - No further action required.

21 Level 2, Room 225E Store wall lining Wall lining Fibre Cement Sheet WSP-110031 OF, NAD - 10m2 - - - - No further action required.

Building J056 - External - Synthetic Mineral Fibre (SMF)

22 Level 2, North side adjacent store room225E "Zona Air" insulation Insulation Insulation Refer to WSP-110026 SMF 8 1 unit Friabile Fair Low Low

Maintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

Building J056 - Internal - Synthetic Mineral Fibre (SMF)

23 Plant room 1.08, hot water pipe insulation Pipe insulation SMF Insulation Visual Assessment SMF 9 Throughout Friable Fair Low Low

Throuhgout all levels within the risersMaintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

24 Plant room 1.08, cable pipe penetration towall Insulation/filler Insulation Refer to WSP-110012 SMF 10 <1m2 Friable Fair Low Low

Throuhgout all levels within the risersMaintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

25 Level 1, offices and store rooms,suspended ceiling tiles Ceiling tiles Ceiling tiles Visual Assessment SMF 11 Throughtout Non-Friable Fair Low Low


26 Level 2, hallway, suspended ceiling tiles Ceiling tiles Ceiling tiles Refer to WSP-110018 SMF 12 Throughtout Non-Friable Good Low LowMaintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

27 Level 2, Gents toilet hot water unit Insulation SMF Insulation Presumed Presumed SMF 13 Throughout Friable Good Low LowMaintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

28 Level 3, hallway, suspended ceiling tiles Ceiling tiles Ceiling tiles Visual Assessment SMF - Throughtout Non-Friable Good Low LowMaintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

29 Level 4, hallway and office room,suspended ceiling tiles Ceiling tiles Ceiling tiles Visual Assessment SMF 14 Throughtout Non-Friable Good Low Low


Building J056 - External - No ODS Containing Materials


Material

Condition

Risk Status

Control

Priority



name




30 Throughout Refrigerant Free ODS refrigerant Visual Observation /Factory Labels No ODS - - - - - - No action required

Building J056 - Internal - PCB's Containing Materials

31 Plant room 1.08, wall & ceiling light fittings Fluorescent light fittings Ducon Capacitor Visual Observation /Factory Labels PCB 15 Throughout NA Good Low Low

Throuhgout the levels with old type fluorescent lightfittings.Maintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

32 Level 2, hallway and rooms ceiling lightfittings Fluorescent light fittings Ducon Capacitor Visual Observation /

Factory Labels PCB 16 Throughout NA Good Low Low


33 Level 3, hallway and rooms ceiling lightfittings Fluorescent light fittings Ducon Capacitor Visual Observation /

Factory Labels PCB 17 Throughout NA Good Low Low


Building J056 - Internal - Lead Containing Paint

34 Level 1, Plant room 108, AHU compressor Brwon paint system Paint WSP-110010 0.38% w/w 18 Throughout NA Fair Med MedMaintain in good condition. Remove in accordancewith state and national guidelines prior to any majorrefurbishment/demolition.

Building J056 - External - No Lead Containing Paint

35 Level 3, Eastern elevation (front) façadecladding Pale-blue paint system Paint WSP-110003 <0.005 %w/w - - - - - - No further action required.

36 Level 3, Front porch brick wall Pale-blue paint system creampaint underneath Paint WSP-110004 <0.005 %w/w - - - - - - No further action required.

37 Level 3, Front porch metal beam White paint system Paint WSP-110005 <0.005 %w/w - - - - - - No further action required.

38 Level 2, North of Room 225E "Zona Air"metal cover Brown paint system Paint WSP-110027 0.007% w/w - - - - - - No further action required.

39 Roof (Level 5), Water piping and metalbeams White paint system Paint WSP-110029 <0.005 %w/w - - - - - - No further action required.

40 Roof (Level 5), Window to level 6 Blue paint system and red paintunderneath Paint WSP-110030 0.075% w/w - - - - - - No further action required.

Building J056 - Internal - No Lead Containing Paint

38 Level 1. Door panel to room 1.11 Blue paint system Paint WSP-110025 0.005% w/w - - - - - - No further action required.


Material

Condition

Risk Status

Control

Priority



name


CERTIFICATES OF ANALYSIS

Lab No Sample ID Location Sample Description Sample Dimensions Identification Type

001 WSP-110001 External, level 3 eastern eave lining Fibre Cement Sheet 1.8 gm CH, OF

002 WSP-110002 External, level 3, eastern facade lining

Fibre Cement Sheet 1.9 gm CH, OF

003 WSP-110006 External level 3, top of facade lining Fibre Cement Sheet 1.8 gm OF, NAD

004 WSP-110007 External level 1, rear entry room 1.18 above door wall infill panel

Fibre Cement Sheet 1.9 gm OF, NAD

005 WSP-110008 Plant room 1.08, AHU ducting joint mastic

Mastic 2.3 gm CH

006 WSP-110009 Plant room 1.08, AHU fresh air filter joint mastic

Mastic 4.1 gm CH

007 WSP-110011 Plant room 1.08, pipe flange gasket Gasket 1.8 gm OF, NAD

008 WSP-110012 Plant room 1.08 cable pipe penetration to wall

Insulation 2.3 gm SMF, NAD

009 WSP-110013 Plant room 1.08, pipe penetration to wall

Vermiculite 6.1 gm OF, NAD

010 WSP-110014 Plant room 1.08, ceiling spray vermiculite

Vermiculite 5.5 gm NAD

011 WSP-110017 Level 2, disabled toilet 2.22 wall lining


TEST METHOD: Qualitative identification of Asbestos fibre in bulk and soil samples at WSP Corporate Laboratories, by polarised light microscopy, including dispersion staining techniques using AS4964 (2004) and supplementary in house laboratory procedure (LP3 - Identification of Asbestos Fibres). This document is issued in accordance with NATA's requirements under NATA accreditation No. 17199, accredited for compliance with ISO/IEC: 17025 - Testing. The results of the tests, calibrations and/or measurements included in this document are traceable to Australian/national standard.

DATE\S SAMPLED:

DATE RECEIVED:

DATE ANALYSED:

ORDER NUMBER:

SAMPLED BY:

11/02/2019

14/02/2019

N/A

8/02/2019

Imam MalikCONTACT:

EMAIL:

TELEPHONE: +61 2 6125 9727

[email protected]

Brett Morrison

F & S Anthony Low Building (#124), Garran Road, Acton ACT 2601

CLIENT ADDRESS:

Australian National UniversityCLIENT:

Page 1 of 2

Notes:If no asbestos is detected in vinyl tiles, mastics, sealants, epoxy resins and ore samples then confirmation by another independent analytical technique is advised due to the nature of the samples.The results contained within this report relate only to the sample(s) submitted for testing. The laboratory accepts no responsibility for location, sampling date, sample ID, sampler, and client details provided by the sampler. WSP accepts no responsibility for the initial collection, packaging or transportation of samples submitted by external persons. NATA does not accredit the sampling process, therefore sampling is not covered by the scope of accreditation. This document may not be reproduced except in full.

AUTHORISATION DATE

Approved Identifier

Name: Bec McLean

Approved Signatory

Bec McLeanName:

Thursday, 14 February 2019

NADCHACUMFSMFOF

-------

No Asbestos DetectedChrysotile Asbestos DetectedAmosite Asbestos DetectedCrocidolite Asbestos DetectedUnknown Mineral Fibres DetectedSynthetic Mineral Fibres DetectedOrganic Fibres Detected

LEGEND:

Hand picked refers to small discrete amounts of asbestos distributed unevenly in a large body of non asbestos material.

Certificate of Analysis

Level 1 121 Marcus Clarke StreetPO Box 1551 Canberra ACT 2600Telephone +61 2 6201 9600Facsimile +61 2 6201 9666Email [email protected]

WSP AustraliaPty Limited

ABN 80 078 004 798

NCSI Certified Quality System ISO 9001

CERTIFICATE NO: ACT-PS112993-110799LOCATION: ANU Building 56, Mills Road, Acton, ACT

Lab No Sample ID Location Sample Description Sample Dimensions Identification Type

012 WSP-110018 Level 2, hallway 2.01 suspended ceiling tiles

Fibre Cement Sheet 2.2 gm SMF, NAD

013 WSP-110019 Level 2, cupboard riser within room 205

Dust 9.8 gm OF, SMF,NAD

014 WSP-110020 Level 2, server room 206 wall panel Fibre Cement Sheet 1.9 gm CH

015 WSP-110021 Level 2, room 209, spray vermiculite Vermiculite 2.8 gm NAD

016 WSP-110022 Level 3, hallway north end cupboard floor tiles

Vinyl Tile 6.6 gm NAD

017 WSP-110023 External, level 1, rear concrete floor expansion joint

Bituminous Material 3.1 gm NAD

018 WSP-110024 Level 1, room 1.06A toilet wall lining Fibre Cement Sheet 1.8 gm OF, NAD

019 WSP-110026 External, level 2, adjacent store room 225E "Zona Air" insulation

Insulation 1.8 gm SMF, NAD

020 WSP-110028 Level 5, roof pipe flange gasket Gasket 1.8 gm CH

021 WSP-110031 Level 2, store room 225E, east wall lining


022 WSP-110032 Level 6, lift motor room, brake pad to lift motor

Brake Pad 1.8 gm CH

Page 2 of 2

Notes:If no asbestos is detected in vinyl tiles, mastics, sealants, epoxy resins and ore samples then confirmation by another independent analytical technique is advised due to the nature of the samples.The results contained within this report relate only to the sample(s) submitted for testing. The laboratory accepts no responsibility for location, sampling date, sample ID, sampler, and client details provided by the sampler. WSP accepts no responsibility for the initial collection, packaging or transportation of samples submitted by external persons. NATA does not accredit the sampling process, therefore sampling is not covered by the scope of accreditation. This document may not be reproduced except in full.

AUTHORISATION DATE

Approved Identifier

Name: Bec McLean

Approved Signatory

Bec McLeanName:

Thursday, 14 February 2019

NADCHACUMFSMFOF

-------

No Asbestos DetectedChrysotile Asbestos DetectedAmosite Asbestos DetectedCrocidolite Asbestos DetectedUnknown Mineral Fibres DetectedSynthetic Mineral Fibres DetectedOrganic Fibres Detected

LEGEND:

Hand picked refers to small discrete amounts of asbestos distributed unevenly in a large body of non asbestos material.

Certificate of Analysis

Level 1 121 Marcus Clarke StreetPO Box 1551 Canberra ACT 2600Telephone +61 2 6201 9600Facsimile +61 2 6201 9666Email [email protected]

WSP AustraliaPty Limited

ABN 80 078 004 798

NCSI Certified Quality System ISO 9001

CERTIFICATE NO: ACT-PS112993-110799LOCATION: ANU Building 56, Mills Road, Acton, ACT

Envirolab Services Pty Ltd

ABN 37 112 535 645

12 Ashley St Chatswood NSW 2067

ph 02 9910 6200 fax 02 9910 6201

[email protected]

www.envirolab.com.au

CERTIFICATE OF ANALYSIS 211269

Level 2, 121 Marcus Clarke St, Canberra, ACT, 2600Address

Anton DelacAttention

WSP Australia Pty LimitedClient

Client Details

12/02/2019Date completed instructions received

12/02/2019Date samples received

10 PAINTNumber of Samples

PS112993 / ANU Building 56Your Reference

Sample Details

Results are reported on a dry weight basis for solids and on an as received basis for other matrices.

Samples were analysed as received from the client. Results relate specifically to the samples as received.

Please refer to the following pages for results, methodology summary and quality control data.

Analysis Details

Tests not covered by NATA are denoted with *Accredited for compliance with ISO/IEC 17025 - Testing.

NATA Accreditation Number 2901. This document shall not be reproduced except in full.

14/02/2019Date of Issue

15/02/2019Date results requested by

Report Details

Jacinta Hurst, Laboratory Manager

Authorised By

Giovanni Agosti, Group Technical Manager

Results Approved By

Revision No: R00

211269Envirolab Reference: Page | 1 of 6

Client Reference: PS112993 / ANU Building 56

0.075<0.0050.0070.05<0.005%w/wLead in paint

14/02/201914/02/201914/02/201914/02/201914/02/2019-Date analysed

14/02/201914/02/201914/02/201914/02/201914/02/2019-Date prepared

PAINTPAINTPAINTPAINTPAINTType of sample

08/02/201908/02/201908/02/201908/02/201908/02/2019Date Sampled

WSP-110030WSP-110029WSP-110027WSP-110025WSP-110016UNITSYour Reference

211269-10211269-9211269-8211269-7211269-6Our Reference

Lead in Paint

0.0750.38<0.005<0.005<0.005%w/wLead in paint

14/02/201914/02/201914/02/201914/02/201914/02/2019-Date analysed

14/02/201914/02/201914/02/201914/02/201914/02/2019-Date prepared

PAINTPAINTPAINTPAINTPAINTType of sample

08/02/201908/02/201908/02/201908/02/201908/02/2019Date Sampled

WSP-110015WSP-110010WSP-110005WSP-110004WSP-110003UNITSYour Reference

211269-5211269-4211269-3211269-2211269-1Our Reference

Lead in Paint

Envirolab Reference: 211269

R00Revision No:

Page | 2 of 6


Digestion of Paint chips/scrapings/liquids for Metals determination by ICP-AES/MS and or CV/AAS.Metals-004

Methodology SummaryMethod ID


R00Revision No:

Page | 3 of 6


[NT]103130.0080.0078<0.005Metals-0040.005%w/wLead in paint

[NT]14/02/201914/02/201914/02/2019814/02/2019-Date analysed

[NT]14/02/201914/02/201914/02/2019814/02/2019-Date prepared

[NT]LCS-1RPDDup.Base#BlankMethodPQLUnitsTest Description

Spike Recovery %DuplicateQUALITY CONTROL: Lead in Paint


R00Revision No:

Page | 4 of 6


Not ReportedNR

National Environmental Protection MeasureNEPM

Not specifiedNS

Laboratory Control SampleLCS

Relative Percent DifferenceRPD

Greater than>

Less than<

Practical Quantitation LimitPQL

Insufficient sample for this testINS

Test not requiredNA

Not testedNT

Result Definitions

Australian Drinking Water Guidelines recommend that Thermotolerant Coliform, Faecal Enterococci, & E.Coli levels are less than1cfu/100mL. The recommended maximums are taken from "Australian Drinking Water Guidelines", published by NHMRC & ARMC2011.

Surrogates are known additions to each sample, blank, matrix spike and LCS in a batch, of compounds whichare similar to the analyte of interest, however are not expected to be found in real samples.

Surrogate Spike

This comprises either a standard reference material or a control matrix (such as a blank sand or water) fortifiedwith analytes representative of the analyte class. It is simply a check sample.

LCS (LaboratoryControl Sample)

A portion of the sample is spiked with a known concentration of target analyte. The purpose of the matrix spikeis to monitor the performance of the analytical method used and to determine whether matrix interferencesexist.

Matrix Spike

This is the complete duplicate analysis of a sample from the process batch. If possible, the sample selectedshould be one where the analyte concentration is easily measurable.

Duplicate

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 forsamples.

Blank

Quality Control Definitions


R00Revision No:

Page | 5 of 6


Measurement Uncertainty estimates are available for most tests upon request.

Where sampling dates are not provided, Envirolab are not in a position to comment on the validity of the analysis whererecommended technical holding times may have been breached.

When samples are received where certain analytes are outside of recommended technical holding times (THTs), the analysis hasproceeded. Where analytes are on the verge of breaching THTs, every effort will be made to analyse within the THT or as soon aspracticable.

In circumstances where no duplicate and/or sample spike has been reported at 1 in 10 and/or 1 in 20 samples respectively, thesample volume submitted was insufficient in order to satisfy laboratory QA/QC protocols.

Matrix Spikes, LCS and Surrogate recoveries: Generally 70-130% for inorganics/metals; 60-140% for organics (+/-50% surrogates)and 10-140% for labile SVOCs (including labile surrogates), ultra trace organics and speciated phenols is acceptable.

Duplicates: >10xPQL - RPD acceptance criteria will vary depending on the analytes and the analytical techniques but is typically inthe range 20%-50% – see ELN-P05 QA/QC tables for details; <10xPQL - RPD are higher as the results approach PQL and theestimated measurement uncertainty will statistically increase.

For VOCs in water samples, three vials are required for duplicate or spike analysis.

Spikes for Physical and Aggregate Tests are not applicable.

Filters, swabs, wipes, tubes and badges will not have duplicate data as the whole sample is generally extracted during sampleextraction.

Duplicate sample and matrix spike recoveries may not be reported on smaller jobs, however, were analysed at a frequency to meetor exceed NEPM requirements. All samples are tested in batches of 20. The duplicate sample RPD and matrix spike recoveries forthe batch were within the laboratory acceptance criteria.

Laboratory Acceptance Criteria


R00Revision No:

Page | 6 of 6

FLOOR PLAN

UNDERCROFT

DISABLED

UP

RA

MP

U

P

UNISEX

UP

1.021.02B

1.01C1.01B

1.01

1.01A

1.04

1.05

1.061.04A

LEONARD HUXLEY LECTURE THEATRE

UP

UP

PLANTROOM

RAMP UP

RE

TA

IN

IN

G W

ALL

1.07

STORE

1.08

1.06A

1.09

55.4m²

73.5m²

18.2m²

10.3m²

21.1m²

17.1m²

73.2m²

7.1m²

11.5m²

43.4m² 12m²

12.6m²

1.01

1.01A

1.01B1.01C

1.021.02B

1.04A

1.04

1.05

1.06

1.06A

1.08

1.07

1.09

1.10

1.11

1.12

1.13

1.14

1.15

1.16

1.17

1.18

1.19

1.27

1.26

1.20

1.21

1.22

1.23

1.24

1.25

1.07B

1.07C

1.07D

1.07E

1.18A

14.9m²

14.3m²

5.3m²

5.7m²

9.5m²

5.7m²

9.4m²

5.2m²

.5m²

1.7m²

2.6m²

2.2m²

.5m²

3.5m²

10m²

2.2m²

10.2m²

1.3m²

10m²

6.1m²

KITCHENETTE

OFFICE

OFFICEOFFICE

OFFICE

OFFICE

GROSS BUILDING AREA = 782.7m²

GROSS FLOOR AREA = 731.1m²

1. 13-1-99 AMENDED TITLE BLOCK & LAYERS L.FIORESE

FACILITIES AND SERVICES

LEONARD HUXLEY BUILDING

BUILDING NO. J056

FLOOR PLAN

LEVEL 1

01.03.88

CANGRAPHICS

X:\ANU CAD LIBRARY\ACTON\J056 LEONARD HUXLEY BUILDING\J056.01 ARCHITECTURAL FLOOR PLANS\A-J056-PLAN-L1

1:100

A1

A-J056-PLAN-L1 2

LEGEND (Sample Locations):

MalikI

Typewriter

WSP-110007

MalikI

Arrow

MalikI

Typewriter

WSP-110009

MalikI

Typewriter

WSP-110008

MalikI

Typewriter

WSP-110011

MalikI

Typewriter

WSP-110010

MalikI

Arrow

MalikI

Arrow

MalikI

Arrow

MalikI

Arrow

MalikI

Typewriter

WSP-110013

MalikI

Typewriter

WSP-110012

MalikI

Arrow

MalikI

Typewriter

WSP-110024

MalikI

Arrow

MalikI

Typewriter

WSP-110025

MalikI

Arrow

AUJS500530

Text Box

WSP-0154XX: No Asbestos/SMF/Lead Detected WSP-0154XX: Asbestos Detected WSP-0154XX: SMF Detected WSP-0154XX: Lead Detected

MalikI

Polygon

MalikI

Callout

Asbestos Ceiling Lining & Facada Cladding

MalikI

Callout

Asbestos Ducting Joint Mastic

MalikI

Oval

PROJECTION ROOM

LEONARD HUXLEY LECTURE THEATRE

UP

DN

UP

UP

UP

DN

UP

DN

WOMEN

MEN

UP

DN

LIFT

COMPUTER ROOM

COUNTER

COUNTER

UP

DN

RAMP DN

251253

254

209

255

256

211

217

213

214 216

OFFICE

LOBBY

OFFICE

COMP. SERVER

STORE

206

217A

217B

217C

225

225F

225E

225C

225D

227

227A

29m²

482.3m²

38m²

30m²

9.4m²

45m²22.5m² 13.4m²

21.8m²

12.2m²

11.1m²

46m²

8.7m²

218.6m²

5.6m²

30.4m²

9.1m²

9m²

9m²

14.6m²

5.3m²

137.2m²

7.9m²

14.5m²

10.6m²

Seating 240

2.06

2.09

2.11 2.13 2.14

2.16

2.17

2.17A

2.17B

2.17C

2.25F

2.25

2.25D

2.25C

2.25A

2.25E

2.56

2.552.542.53

2.51

2.27A

2.27

2.01

2.01A

2.02

2.22

2.23

2.24

2.01B

2.01C

2.03

2.04

2.08

2.05

2.08A

2.08C

2.08D

2.23A

2.23B

2.24A

2.28

2.2

9

2.30

2.31

2.32

2.33

2.34

2.27B 2.27C 2.27D 2.27E

2.35

2.36

2.37

2.38

2.39

2.40

2.41

2.42

2.08B

4.6m²

.3m²

9.8m²

.6m²

.3m²

4.9m²

9.7m²

1.3m²

48.2m²

.5m²

1.3m²

1m²

.8m²

2.1m²

26.6m²

2.4m²

5.7m²9.5m²

65m²

12m²

8.4m²

2.5m²

.9m²

2.2m²

2.2m²

4.2m²

9.7m²

217E

26.9m²

2.17E

217D

29.5m²

2.17D

OFFICE

OFFICE

SICK ROOM

SWITCH ROOM

SWITCH ROOM

OFFICE

OFFICE

OFFICE

OFFICE

OFFICEOFFICE

OFFICE

MEETING ROOM

OFFICE OFFICE OFFICE

OFFICE

GROSS BUILDING AREA = 1648m²


CORRIDOR

S.R

S.R

S.R

S.R

S.R

E.D.B

S.R

S.R

S.R



BUILDING NO. J056

FLOOR PLAN

LEVEL 2

01.03.88

CANGRAPHICS


1:100

A1

A-J056-PLAN-L2 2


MalikI

Typewriter

WSP-110020

MalikI

Typewriter

WSP-110026

MalikI

Arrow

MalikI

Arrow

MalikI

Typewriter

WSP-110017

MalikI

Typewriter

WSP-110018

MalikI

Arrow

MalikI

Arrow

MalikI

Typewriter

WSP-110019

MalikI

Arrow

MalikI

Typewriter

WSP-110021

MalikI

Typewriter

WSP-110031

MalikI

Arrow

MalikI

Typewriter

WSP-110027

AUJS500530

Text Box

WSP-0154XX: No Asbestos/SMF/Lead Detected WSP-0154XX: Asbestos Detected WSP-0154XX: SMF Detected WSP-0154XX: Lead Paint Detected

MalikI

Typewriter

WSP-110006

MalikI

Arrow

MalikI

Callout

Asbestos Ceiling lining & Facada Cladding

MalikI

Polygon

MalikI

Typewriter

Asbestos Wall Panel

MalikI

Arrow

334 335336

337

331

314313

338

330

316315

329 328 327 325326

317318

319320

321

324

312A

332

301

303

301B

301A

311

312

302

19.1m²

11.6m²11.6m²

11.6m²

26.8m²

10.5m²

11m²

11m²

11m²

11m²

29.7m²

11m²

11m²

11m²

13.8m²

13.5m²

26.3m² 18.6m²

12.9m²

12.9m²

11m²

11m²

11m²

44.4m²

11.8m²

2.8m²

7.6m²

14.4m²

11.5m²

141m²

2m²

322

1.8m²

3.01

3.01A

3.01B

3.02

3.03

3.04

3.05

3.06

3.07

3.07A

3.09

3.10

3.11

3.07B

3.08

3.12B

3.12

3.12A

3.12C

3.13 3.14 3.15 3.16 3.17 3.18 3.19 3.20 3.21

3.23

3.22

3.25 3.243.263.273.283.293.303.313.32

3.33

3.33A

3.34

3.35 3.36 3.37

3.38

3.05A 3.02A 3.02B

3.38A

3.06A

3.38B 3.39

3.40

10.4m²

9.7m²

0.3m²

2.4m²

5.8m²

0.8m²

2.3m²

0.6m²

9.7m²

3.8m²

33.1m²

0.3m²

0.3m²

41m²

1.3m²

OFFICE

OFFICEOFFICE

OFFICE

OFFICE

OFFICE

OFFICEOFFICE

OFFICE

OFFICE

OFFICEOFFICE OFFICE

OFFICEOFFICEOFFICEOFFICE

OFFICEOFFICEOFFICE

OFFICEOFFICE

MEETING

COMMON ROOM

KITCHEN

OFFICE



SICK BAY

CLNR

CLNR

Store

CLNR.

E.D.B

F.H

S.R

S.R

S.R

S.R

30.4m²

1. 13-1-99 AMENDED TITLE BLOCK & LAYERS, L.FIORESE



BUILDING NO. J056

FLOOR PLAN

LEVEL 3

01.03.88

CANGRAPHICS


1:100

A1

A-J056-PLAN-L3

1


MalikI

Typewriter

WSP-110001

MalikI

Typewriter

WSP-110002

MalikI

Typewriter

WSP-110003

MalikI

Typewriter

WSP-110004

MalikI

Typewriter

WSP-110005

MalikI

Arrow

MalikI

Arrow

MalikI

Arrow

MalikI

Arrow

MalikI

Arrow

MalikI

Typewriter

WSP-110022

MalikI

Arrow

AUJS500530

Text Box

WSP-0154XX: No Asbestos/SMF/Lead Detected WSP-0154XX: Asbestos Detected WSP-0154XX: SMF Detected WSP-0154XX: Lead Detected

MalikI

Polygon

MalikI

Polygon

MalikI

Callout


F.H.

4.32

4.31

4.23

4.24

4.26

4.22

4.27

DN

4.30A

4.29

4.28

4.23A

4.23C

4.20

4.01

4.024.03

4.044.06

DN

UP

F.H.

4.05

MEN

4.07 4.08 4.104.11

4.134.15 4.16

4.12

4.14

DN

22.5m²

19.3m²

4.34

4.094.05A

4.17

4.23B

4.30B

4.30C

4.31A

SHR.

CHANGE AREA

4.30

YELLOW RM.

4.00

19m²

54.2m²

12m²

26.8m²

21m²

22m²

7.1m²

12.2m²

16.4m²

45.5m²

13.1m²

12.9m²

18.1m²

88.7m²

2.2m²

7m²

6.1m²

26m²

12m²12m²

12m²

11.5m²11.5m² 11m²

11m²11m²

11m² 11m²

10m²

12m²

36.5m²20.5m² 25.7m²

31m²

7.9m²

7.6m²

E.D.B

4.014.02 4.03 4.04 4.06 4.07 4.08 4.10 4.11 4.13 4.15 4.16 4.17

4.05

4.09 4.12 4.14

4.05A

4.00

4.18

4.19

4.19B

4.19A

4.20

4.22

4.23

4.23A

4.23B

4.23C

4.24

4.26

4.25

4.21

4.27

4.28

4.29

4.30

4.30A

4.30B

4.30C

4.31

4.31A

4.32

4.33

4.34

4.33A

4.35

4.36

4.37

4.38

4.39

4.40

4.41

4.42

4.43

4.44

4.31B

4.32A

9.5m²

5.8m²

46.2m²

11.8m²

0.3m²

0.3m²

2.4m²

1.5m²

0.8m²

1.8m²

68.5m²

9.7m²

1.3m²

0.7m²

18.3m²

10.9m²

0.7m²

1.4m²

1.1m²

4.00A

0.5m²

TEACHING ROOM

TEACHING ROOM

TEACHING ROOM

MEETING ROOM

OFFICE

STORE

OFFICE

OFFICE

OFFICE OFFICE OFFICE OFFICE OFFICE OFFICE OFFICE OFFICE OFFICE OFFICE OFFICE OFFICE

LIFT

OFFICE

OFFICE

STORE ROOM

GROSS BUILDING AREA = 1010m²


COMMS

S.R

S.R

S.R

S.R

S.R

S.R

S.R

AMENDED21-9-991.

AMENDED T.NEW06-5-022.


AMENDED JACKSON ARCH.NOV.20104

UPDATED G.CORNISH31.7.125



BUILDING NO. J056

FLOOR PLAN

LEVEL 4

01.03.88

CANGRAPHICS


1:100

A1

A-J056-PLAN-L4 5

MalikI

Rectangle

MalikI

Rectangle

MalikI

Callout


UP

ROOF

UP

UNROOFED AREA FOR MECHANICAL PLANT

LADDER UP

DN

LIFT WELL

5.01

5.02

5.03

21.8m²

5.8m²

42.1m²



AMENDED21-9-991.





AMENDMENT.DATE.No.

PROJECT TITLE: DRAWING TITLE:

DRWG No:

Checked:

Approved:

Drawn:

Date: Scale:

Sheet Size:

APP.CKD.DWN. FACILITIES AND SERVICES

Issue

LEONARD HUXLEY

BUILDING

BUILDING N0. J056

LEVEL 5

FLOOR PLAN

01.03.88

CANGRAPHICS


1:100

A3

A-J056-PLAN-L5 5


MalikI

Typewriter

WSP-110028

MalikI

Arrow

MalikI

Arrow

MalikI

Typewriter

WSP-110030

MalikI

Arrow

MalikI

Typewriter

WSP-110029

AUJS500530

Text Box


MalikI

Typewriter

Asbestos Pipe Flange Gasket

MalikI

Oval

LIFT MOTOR

ROOM

6.01

14.8m²



AMENDED21-9-991.





AMENDMENT.DATE.No.

PROJECT TITLE: DRAWING TITLE:

DRWG No:

Checked:

Approved:

Drawn:

Date: Scale:

Sheet Size:

APP.CKD.DWN. FACILITIES AND SERVICES

Issue


BUILDING NO. J056 LEVEL 6

FLOOR PLAN

01.03.88

CANGRAPHICS


1:100

A3

A-J056-PLAN-L6 5


MalikI

Arrow

MalikI

Typewriter

WSP-110032

AUJS500530

Text Box


MalikI

Oval

MalikI

Typewriter

Asbestos Lift Motor Brake Pad

RISK ASSESSMENT

Appendix E

Risk Assessment

Asbestos and Hazardous Materials

Risk rankings were calculated by assessing the condition of, and the accessibility to the Hazardous Materials instances,

as observed during survey.

For full details of the locations, analysis results, condition, accessibility and risks associated with the identified

Hazardous Materials, please refer to the attached Hazardous Materials Register.

Asbestos

Table 1 Friable descriptors

Item Score Description

Friable Y Asbestos cement debris, or material which when dry may become crumbled, pulverised or reduced to powder by hand pressure.

N Bonded i.e. non-friable material

A Assumed (Identification Unconfirmed)

Table 2 Material Assessment Descriptors


Product type 0 No asbestos detected

1 Bonded asbestos in good condition

2 Friable asbestos in good condition or cement in poor condition

3 Friable asbestos in poor condition


Extent of Damage 0 No visible damage

1 Minor scratches or mark, broken edges

2 Significant breakage, many small areas of damage to friable material

3 High damage, visible debris


Surface Treatment 0 Bonded asbestos including encapsulated asbestos cement

1 Enclosed laggings, sprays and boards or bare cement

2 Bare board or encapsulated lagging/spray or cement debris

3 Unsealed lagging/spray



WSP February 2019

Page E-25

Table 3 Location Assessment Descriptors


Likelihood of Disturbance

0 Usually inaccessible or unlikely to be disturbed (e.g. little used store room)

1 Minimal likelihood for disturbance (e.g. office type activity)

2 Likely disturbance (e.g. industrial or vehicular activity)

3 Frequent disturbance (e.g. fire door in constant use)


Human Exposure Potential

0 Infrequent

1 Monthly

2 Weekly

3 Daily


Maintenance Activity

0 Minor disturbance (e.g. possibility of contact when gaining access)

1 Low Disturbance (e.g. changing light bulbs in asbestos insulating board ceiling).

2 Medium disturbance (e.g. lifting one or two ceiling tiles to access a valve)

3 High level of disturbance (e.g. moving a number of asbestos ceiling tiles to replace a valve or for re-cabling)


The asbestos containing material risk score is a quantitative assessment determined by the sum of the scores based on the

Materials and Location Assessments; i.e. Risk score = Material Score + Location Score (out of as possible 24).

Should no asbestos be detected then the register will indicate a risk score of 0.

Table 4 Asbestos Risk Score Descriptors


Risk 0 No asbestos risk

1 – 6 Low Risk

7 – 12 Medium Risk

13 – 24 High Risk

Other Hazardous Materials

Other hazardous materials, with the exception of asbestos.


WSP February 2019

Page E-26

Table 5 Friability Descriptors


Friable Y Unsealed SMF

N Sealed SMF

NA Applicable to PCB and Lead in paint

Table 6 Material Assessment Descriptors


Extent of Damage G Good condition

Av Average condition

P Poor condition

Surface Treatment Y Sealed

P Part sealed

N Not sealed

Table 7 Location Assessment Descriptors


Human Exposure Potential

H High traffic area

M Medium traffic area

L Low traffic area

The other hazardous materials risk score is a qualitative assessment determined by the combination of Material and

Location Assessments. Depending on the material one or all of these criteria may be used in assessing the recommended

Action.

Table 8 Other Hazardous Materials Risk Score Descriptors


Risk Score L Low exposure risk

M Medium exposure risk

H High exposure risk

Recommended Risk Controls

Following the assessment for both asbestos containing and other hazardous materials an action score is assigned. The

action score will be assigned according to the surveyor’s assessment of the situation.


WSP February 2019

Page E-27

Table 9 Recommended Risk Controls – Actions

Descriptor Item Action

P1 Priority 1 Restrict access and remove by a licensed contractors

As a guide, the material conforms to one, or more, of the following:

Friable or poorly bonded to substrate, located in accessible areas;

Severely water damaged, or unstable;

Further damage or deterioration likely;

Friable asbestos material located in air conditioning ducting;

Asbestos debris and stored asbestos in reasonably accessible areas;

Significant peeling and flaking lead paint in areas that pose immediate risk to children/resident.

P2 Priority 2 Enclose, encapsulate or seal

Reinspect Periodically


Damaged material;

In reasonably accessible area;

Friable material or poorly bonded to substrate, with bonding achievable;

Possibility of disturbance through contact;

Possibility of deterioration caused by weathering;

Large areas of peeling and flaking lead paint in an area that poses high risk.

P3 Priority 3 Remove during refurbishment or maintenance

Enclose, encapsulate or seal by general maintenance contractors

Reinspect Periodically


Asbestos debris or stored material in rarely accessed areas;

Further disturbance or damage unlikely other than during maintenance or service;

Readily visible for further assessment;

Asbestos friction materials, gaskets and brake linings;

Small/moderate areas of peeling and flaking lead paint in an area that poses low risk. Remedial works suitable by a general maintenance contractor.

P4 Priority 4 No remedial action – Reinspect Periodically


Firmly bonded to substrate and readily visible for inspection;

Inaccessible and fully contained;

Stable and damage unlikely.

STATEMENT OF LIMITATIONS


WSP February 2019

Page 1

LIMITATIONS OF A HAZARDOUS

MATERIALS INSPECTION

SCOPE OF SERVICES

This hazardous materials inspection report (‘the report’) has been prepared in accordance with the scope of services set

out in the contract, or as otherwise agreed, between the Client and WSP Australia (‘scope of services’). In some

circumstances the scope of services may have been limited by a range of factors such as time, budget, access and/or site

disturbance constraints.

RELIANCE ON DATA

In preparing the report, WSP has relied upon data, surveys, analyses, designs, plans and other information provided by

the Client and other individuals and organisations, most of which are referred to in the report (‘the data’). Except as

otherwise stated in the report, WSP has not verified the accuracy or completeness of the data. To the extent that the

statements, opinions, facts, information, conclusions and/or recommendations in the report (‘conclusions’) are based in

whole or part on the data, those conclusions are contingent upon the accuracy and completeness of the data. WSP will

not be liable in relation to incorrect conclusions should any data, information or condition be incorrect or have been

concealed, withheld, misrepresented or otherwise not fully disclosed to WSP.

NO INSPECTION CAN BE GUARANTEED TO LOCATE ALL

HAZARDOUS MATERIALS

In practice, it is generally impossible to locate all hazardous materials in the course of an inspection.

This is because of factors such as:

� The availability of building/plant construction plans. There is no instrument which can detect hazardous materials.

� Inaccessible and restricted areas during survey

The presence of hazardous materials must be determined visually, as there is no single, cost effective instrument

currently available for the purpose. Usually an inspector will take samples of suspect materials and have them analysed

in a laboratory. Thus, any restrictions on the amount of sampling will reduce confidence in the hazardous materials

inspection findings. The consequence of this is that hazardous materials which cannot be seen will not be found.


WSP February 2019

Page 2

HAZARDOUS MATERIALS ARE COMMONPLACE

From the early 1900s until the early 1970s, asbestos was widely used in industry. The use of asbestos cement sheets in

roof pipes and wall cladding was particularly widespread, as was the use of ‘limpet’ asbestos fibre insulation in steel

framed high-rise buildings. Asbestos was also used for applications such as insulation of pipes and high temperature

electricity cables, in plastics, in PVC floor tiles, for reinforcement in cements, putties and mastic and in gaskets and

friction materials.

Whilst major uses of hazardous materials were sometimes recorded on engineering drawings, there are few records of the

ad hoc use of hazardous materials and products. To give examples from the building industry, plumbers frequently used

asbestos fibre in caulking compounds and builders often used Asbestos Cement sheeting as packing under floorboards.

In short, asbestos could be almost anywhere in a building or plant constructed before the 1980s.

RELIANCE ON A HAZARDOUS MATERIALS INSPECTION

The client must not rely upon an inspection or report as indicating that a site or building is ‘hazardous materials free’.

All that the report can be relied upon to show is that no hazardous materials were found (or that only such hazardous

materials were found as was reported to have been found) in the course of the inspection. The findings of the report must

be considered together with the specific scope and limitations of the type of inspection undertaken.

REPORT FOR BENEFIT OF CLIENT

The report has been prepared for the benefit of the Client and no other party. WSP assumes no responsibility and will not

be liable to any other person or organisation for or in relation to any matter dealt with or conclusions expressed in the

report, or for any loss or damage suffered by any other person or organisation arising from matters dealt with or

conclusions expressed in the report (including without limitation matters arising from any negligent act or omission of

WSP or for any loss or damage suffered by any other party relying upon the matters dealt with or conclusions expressed

in the report). Other parties should not rely upon the report or the accuracy or completeness of any conclusions and

should make their own enquiries and obtain independent advice in relation to such matters.

For the purposes of this limitations statement, ‘conclusions’ include statements, opinions, facts, information, conclusions

and/or recommendations in the report.

Documents

Acton Campus Building #56 Hazardous Materials Report - ANU · ANU Hazardous Materials Register Site Location: Building 56, Leonard Huxley Building, Acton Campus Assessor: Anton Delac,