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Supplementary Information
DWER - Works & Licensing Application
&
City of Gosnells Development Application
Asphalt Manufacturing Plant
City of Gosnells
Location
6 Allott Way, Maddington, City of Gosnells
(Part of Provisional Lot 521, Previously Part of Lot 9005)
Prepared for
Perth Asphalt Supply Pty Ltd
July 2017
Holmes Environmental Pty Ltd ACN 143 154 456
In trust for The RM & KL Environmental Trust ABN 20 688 071053
18 Pindari Road, Lesmurdie WA 6076
Phone 08 9291 9284 Mob 0428 244 822
Page | ii
This document formatted for double page printing
Page | iii
1.0 APPLICATION DETAILS .................................................................................................. 1
1.1 General Company Description ............................................................................................ 1
1.2 The proposal ........................................................................................................................... 1
1.3 DWER Licence Categories Requested ............................................................................... 1
1.4 Development Application ..................................................................................................... 1
1.5 Site Development ................................................................................................................... 1
1.6 Occupier and Proponent Details ......................................................................................... 2
2.0 LOCATION ............................................................................................................................. 3
2.1 Site Ownership ....................................................................................................................... 3
2.2 Current Land Use ................................................................................................................... 3
2.3 Premises Detail ....................................................................................................................... 3
3.0 DECISION MAKING AUTHORITIES ............................................................................. 5
3.1 Department of Water & Environmental Regulation (DWER) ........................................... 5
3.2 Environmental Protection Authority (EPA) ....................................................................... 5
3.3 Department of Health (DoH) ................................................................................................. 5
3.4 Landowner Approval ............................................................................................................. 5
3.5 Local Government Authority ................................................................................................ 6
3.5.1 City of Gosnells- Town Planning Scheme No.6 (GTPS No.6) - Zoning .............................................. 6
3.5.2 Supporting Infrastructure ...................................................................................................................... 7
3.5.3 Personnel ............................................................................................................................................... 7
3.6 Department of Mines, Industry Regulation and Safety ................................................... 7
3.7 Other Regulatory Authorities ............................................................................................... 8
3.8 Relevant Standards ............................................................................................................... 8
4.0 THE EXISTING ENVIRONMENT .................................................................................. 10
Page | iv
4.1 Sensitive Receptors ............................................................................................................. 10
4.2 Contamination ...................................................................................................................... 10
4.3 Compliance - Contaminated Sites Act ............................................................................. 10
4.3.1 Previous Investigations & Approvals .................................................................................................. 10
4.3.2 Development Plan ............................................................................................................................... 10
5.0 THE ASPHALT MANUFACTURING PLANT ........................................................... 12
5.1 Summary................................................................................................................................ 12
5.2 Asphalt Plant Operation ...................................................................................................... 12
5.3 Bag House ............................................................................................................................. 13
5.4 Diesel Fuel ............................................................................................................................. 13
5.5 Bitumen .................................................................................................................................. 14
6.0 ENVIRONMENTAL MANAGEMENT ........................................................................... 16
6.1 Introduction ........................................................................................................................... 16
6.2 Fugitive Odour Emissions – Hotmix Asphalt .................................................................. 16
6.2.1 Source of Emissions ............................................................................................................................. 16
6.2.2 Odour Emission Control ...................................................................................................................... 16
6.2.3 Mitigation ............................................................................................................................................ 16
6.2.4 Summary ............................................................................................................................................. 17
6.3 Point Source Emissions ..................................................................................................... 17
6.3.1 Source of Emissions ............................................................................................................................. 17
6.3.2 Atmospheric Emission Control ............................................................................................................ 17
6.3.3 Mitigation ............................................................................................................................................ 17
6.3.4 Summary ............................................................................................................................................. 18
6.4 Gaseous Emissions ............................................................................................................. 18
6.4.1 Source of Emissions ............................................................................................................................. 18
6.4.2 Mitigation ............................................................................................................................................ 18
Page | v
6.5 Dust Emissions – Materials Handling .............................................................................. 18
6.5.1 Source of Emissions ............................................................................................................................. 18
6.5.2 Mitigation ............................................................................................................................................ 19
6.6 Noise Emissions .................................................................................................................. 19
6.6.1 Source of Emissions ............................................................................................................................. 19
6.6.2 Mitigation ............................................................................................................................................ 19
6.7 Diesel/Bitumen Storage ...................................................................................................... 19
6.7.1 Source of Emissions ............................................................................................................................. 19
6.7.2 Mitigation - Diesel ............................................................................................................................... 19
6.7.3 Mitigation - Bitumen and Lubricating Oils .......................................................................................... 20
6.8 Water Discharge ................................................................................................................... 20
6.8.1 Source of Emissions ............................................................................................................................. 20
6.8.2 Mitigation ............................................................................................................................................ 20
6.9 Solid/Liquid Wastes ............................................................................................................. 20
6.9.1 Source of Emissions ............................................................................................................................. 20
6.9.2 Mitigation ............................................................................................................................................ 20
6.10 Discharges to Land and Water .......................................................................................... 21
6.10.1 Source of Emissions ........................................................................................................................ 21
6.11 Stormwater Contamination ................................................................................................ 21
6.11.1 Source of Emissions ........................................................................................................................ 21
6.11.2 Mitigation ....................................................................................................................................... 21
6.12 Stormwater Management .................................................................................................... 21
7.0 LIMITATIONS ...................................................................................................................... 23
Page | vi
Figures
Figure 2.1 6 Allott Way, Maddington. ....................................................................................... 4
Figure 3.1 City of Gosnells TPS 6 Zoning Map .. ......................................................................... 9
Figure 4.1 Distance to nearest sensitive receptor. ................................................................... 11
Figure 5.1 Oblique view of an installed plant.. ........................................................................ 15
Figure 6.1 Wind Rose for City of Gosnells.. .............................................................................. 22
Tables
Table 1.1 Occupier and Proponent Details ............................................................................... 2
Table 2.1 Premises corner boundary geospacial locations as shown in Figure 3......................... 3
Table 5.1. Mobile Asphalt Plant data ...................................................................................... 14
DWER Attachments
Application Form Reference
Attachment
Attachment 1A Lease Agreement and Landowner Correspondence
Certificate of Title Lot 9005
Attachment 1B ASIC Company Extract
Attachment 2 Aerial Photograph + Discharge Point
Infrastructure: Allott Way Site Plan
Sensitive Receptors: Attached document Figure 3.1
Attachment 3A See Attached Document Section 1
Attachment 6A See Attached Document Section 6.3.3.
Attachment 7 Aerial photo with distances
Attachment 8 Enpoint "Site Management Plan"
Letter - DWER Contaminated Sites Branch
Attachment 9 Fee component Works Approval
Attachment 10 Works Approval and Licence Fee calculation.
1 Application Details
Page | 1
1.0 App lication Det ails
1.1 General Company Description
Perth Asphalt Supply Pty Ltd is a Western Australian company with interests in both civil and private
asphalt and concrete applications.
Asphalt surfacing and repair - civil, business and private.
Concreting - construction and maintenance - civil, business; and private.
Drainage solutions.
Plant hire.
Traffic control and management.
The proponent's clients include four major metropolitan city councils and major WA prime
contractors. A copy of the proponent's ASIC Company Extract is provided as an attachment.
1.2 The proposal
The proposal is to locate and operate a small 40 tonne per hour asphalt manufacturing plant within
leased premises at 6 Allott Way, Maddington.
The proponent currently occupies premises at 206 Maddington Road, Maddington. Due to an
increase in client demand the proponent has recently leased larger premises in Allott Way to allow for
business expansion and the opportunity to manufacture asphalt for the company's expanding
asphalting contracts.
1.3 DWER Licence Categories Requested
The mobile asphalt plant has an average capacity of about 40 tonnes per hour – depending on the
grade of aggregate employed equating to not more than 50,000 tonnes per annum - including down
time for repairs and periodic servicing and delivery limitations.
Category of works approval/licence sought
Category 35 Asphalt manufacturing: premises on which hot or cold mix asphalt is produced using
crushed or ground rock aggregates mixed with bituminous or asphaltic materials for
use at places or premises other than those premises
1.4 Development Application
See Section 3.5 below for information required by the local government authority. Drawings and
photographs required for the assessment are attached separately.
1.5 Site Development
The proposed manufacturing plant is a fixed-location plant. It will arrive on site in pre-assembled
units that are located and secured on pre-prepared concrete footings - see Table 5.1 below for details.
Support infrastructure will include 3-sided ground bins for aggregate stockpiles demountable offices
with sewer, water and electricity mains connections and hard-standing for work areas, traffic and
1 Application Details
Page | 2
parking. Ground disturbance will be limited to footings, sewer and water mains connections.
Stormwater management and drainage will be installed by the landowner.
1.6 Occupier and Proponent Details
All relevant proponent information for both Department of Environment Protection and City of
Gosnells assessment is provided in Table 1.1 below
Table 1.1 Occupier and Proponent Details
Premises Description Part of Provisional Lot 521, Previously Part of Lot 9005 on Deposited Plan 40777, Volume 2560 Folio 13
Premises Street Address 6 Allott Way, Maddington.
Premises Owner Hughes Enterprises Australia Pty Ltd (ACN
600969275)
Address 45 Bygum Lane, Martin WA 6110
Proponent and Occupier Perth Asphalt Supply Pty Ltd
Registered Company Address 5 Marion Street, Midland WA 6056
Telephone 08 9261 1800
ABN 33 618 055 477
ARBN 0126126J
ACN 618 055 477
ANZSIC Code 1709 ‘Asphalt Mixing’
Director Matthew McDowell
Mobile 0488 775 388
Telephone 9452 8040 or 9452 08643
Fax 9238 4975
Email [email protected]
Street Address 206 Maddington Road, Maddington WA 6109
Postal Address PO Box 2416, High Wycombe WA 6057
2 Location
Page | 3
2.0 Locat ion
2.1 Site Ownership
6 Allott Way is owned by Hughes Enterprises Australia Pty Ltd. A copy of the Certificates of Title is
provided as an attachment.
2.2 Current Land Use
6 Allott Way is in the process of subdivision of the existing Lot 9005 into three Provisional Lots 521,
522 and 523. The proponent intends to lease a portion of Provisional Lot 521 as shown in Figure 2.1
below. Provisional Lot 521 is a "brown-fields" development being part of the larger industrial area
that was previously used for landfill.
2.3 Premises Detail
The proposed premises boundaries are shown in Figure 2.1; corner geospatial locations are provided
in Table 2.1 below.
Table 2.1. Premises corner boundary geospacial locations as
shown in Figure 3 - rotating clockwise from northern-
most corner boundary
Corner Boundary Northing Easting
1. North 6 455 162.855 405 881.159
2. North East 6 455 132.949 405 964.026
3. 6 455 041.158 405 924.346
4. East 6 455 011.288 405 964.443
5.South 6 455 943.613 405 898.242
6.West 6 455 038.302 405 801.460
7. 6 455 078.301 405 840.595
2 Location
Page | 4
Figure 2.1 6 Allott Way Maddington. Blue lines = boundary 6 Allott Way (Lot 9005); Red lines = Leased area of proposed premises being part of Provisional Lot 521 (from Landgate)
See Site Plan, Attachment E.
3 Decision Making Authorities
Page | 5
3.0 Decision M aking Authorities
3.1 Department of Water & Environmental Regulation (DWER)
Under the Environmental Protection Regulations 1987, Asphalt Manufacturing is a prescribed
activity and as such any new operations require Works Approval and Licensing, subject to assessment
by the DER.
This document provides the information required for assessment by DWER for both works approval
and licensing. In regard to buffer distances between certain prescribed and sensitive premises (see
Section 3.2 below), the then DER stated that applications will in future be assessed on a case-by-case
basis (Letter - Agnes Tay, DER. 17jan17).
Lot 9005 (6 Allott Way) Certificate of Title includes a memorial recorded under the Contaminated
Sites Act 2003 registered 1/9/2016. Matters relating to compliance with the Contaminated Sites Act
and DWER Contaminated Sites Guidelines, as of interest to DER, DoH and City of Gosnells, are
provided in Section 4 below.
3.2 Environmental Protection Authority (EPA)
Appendix 1 of the EPA Guidance Statement No.3 Separation Distances between Industrial and
Sensitive Land Uses provides the following guidance regarding “asphalt works”.
Impacts include: noise dust and odour;
Key Government agency for advice or approval: Local Government;
Buffer Distance: 1000 metres.
In regard to the above items:
Mitigation of impacts is discussed in Section 6
The Key Government Agency for advice and approval is the City of Gosnells. Referral to
OEPA is not required.
Buffer distance will be assessed by the DWER on a case-by-case basis (see Section 3.1
above).
3.3 Department of Health (DoH)
Because 6 Allott Way has been registered under the Contaminated Sites Act 2003, proposed
development of the site may require referral to DoH by the City of Gosnells and/or DER.
3.4 Landowner Approval
Part of Provisional Lot 521 leased by the proponent is owned by Hughes Enterprises Australia Pty
Ltd. A copy of the lease agreement between the proponent and the landowner is is provided as an
attachment; also provided is a letter from the landowner stating no objection to Category 35
operations within the leased area.
3 Decision Making Authorities
Page | 6
3.5 Local Government Authority
The local government authority for this proposal is City of Gosnells. This proposal is concurrently
submitted to DWER (Works Approval and Licensing Approval) and City of Gosnells (Development
Approval).
This document provides information to assist the City of Gosnells to assess the proposal for
planning/development approval. A copy of the Development Application Form, signed by the
applicant and the owner of the property is provided as an attachment.
Definitions as provided by the City of Gosnells TPS 6 Scheme Text for the Zones indicated in Figure
3.1 below:
General Industrial - To provide for manufacturing industry, the storage and distribution of
goods and associated uses, which by the nature of their operations should be separated from
residential areas.
Business Development - To provide for the progressive and planned development of areas for
commercial and industrial uses.
Residential/Light industry - To provide for composite residential/light industrial development
to meet the needs of businesses which require a residential component and provide a suitable
interface between industrial zoned land and residential zoned land.
Residential - To provide for residential development at a range of densities with a variety of
housing to meet the needs of different household types.
Residential Development - To provide for the progressive and planned development of future
urban areas for residential purposes and for commercial and other uses normally associated
with residential development.
General Rural - To provide for a range of rural pursuits which are compatible with the
capability of the land and retain the rural character and amenity of the locality.
3.5.1 City of Gosnells- Town Planning Scheme No.6 (GTPS No.6) - Zoning
6 Allott Way is located within the General Industry Zone (see Figure 3.1 below) that has the
following objective:
"To provide for manufacturing industry, the storage and distribution of goods and associated uses,
which by the nature of their operations should be separated from residential areas."
The proposal before City of Gosnells is for the operation of an Asphalt Manufacturing Plant that will
require works approval and licensing under the Environmental Protection Regulations (1987) - and as
such is defined under the GTPS No.6 as "industry - noxious", as defined under GTPS 6 Scheme Text:
"means an industry which is subject to licensing as “Prescribed Premises” under the Environmental
Protection Act 1986 (as amended)"
3 Decision Making Authorities
Page | 7
Under The GTPS No.6 Zoning Table "Industry - noxious" is catagorised "A" which has the following
definition:
"means that the use is not permitted unless the local government has exercised its discretion by
granting planning approval after giving special notice in accordance with clause 64 of the Planning
and Development (Local Planning Scheme) Regulations 2015 Schedule 2"
Therefore the proponent requests that the Gosnells City Council consider development approval for
this application taking into account that the application is submitted concurrently to DWER and will
be subject to assessment under both Part V of the Environmental Protection Act 1986 and
Contaminated Sites Act 2003 taking into consideration technical and environmental information
provided elsewhere in this document.
3.5.2 Supporting Infrastructure
The asphalt plant will require diesel-electric motive power, diesel fuel for aggregate heating and
drying, and maintaining the temperature of stored liquid bitumen. Five grades of crushed granite
aggregate will be stockpiled in three-sided bins. The proposed layout is provided in Figure 4.1 below
showing the location of all infrastructure, hardstands and traffic circulation.
Administrative and staff support facilities will be required including offices, mess room, kitchen and
toilets within a demountable building as shown in Figure 4.2 below.. All services including
electricity, water and sewage will be connected to offsite reticulated facilities.
Earthworks and drainage for stormwater management and runoff will be provided by the landowner
(see attached drawings).
3.5.3 Personnel
Fourteen people will be employed on site including four for asphalt production, five subcontractors
for raw material and product transport with the remainder being support staff.
3.6 Department of Mines, Industry Regulation and Safety
The proponent intends to maintain diesel fuel storage on site no more than 5,000 litres. Diesel fuel
will be stored within a bunded compound as required by DWER guidelines - sufficient to contain
110% of the volume of the largest container or tank within the compound.
Dangerous Goods Safety Guidance Note S01/09. Manifest quantity for diesel fuel is 100,000 litres.
The requirement is that a site must be licensed under Dangerous Goods requirements if DG are stored
in exceedance of the manifest quantity. The anticipated diesel fuel storage will not exceed 5,000
litres.
3 Decision Making Authorities
Page | 8
3.7 Other Regulatory Authorities
The on-site operations will also be regulated by the following:
Environmental Protection (Unauthorised Discharges) Regulations 1987
Environmental Protection (Noise) Regulation 1997
Dangerous Goods Safety (Storage and Handling) Regulations 2007
Occupational Safety and Health Act 1984
Occupational Safety and Health Regulations 1996
Environmental Protection (NEPM-NPI) Regulations 1998;
National Greenhouse and Energy Reporting Act 2007;
Local Government Act 1995;
Contaminated Sites Act 2003; and
Contaminated Sites Regulations 2006.
3.8 Relevant Standards
AS 1940-2004 The Storage and Handling of Flammable and Combustible Liquids.
3 Decision Making Authorities
Page | 9
Figure 3.1. City of Gosnells TPS 6 Zoning Map. An approximate 1,000 metre radius about the proposed premises is indicated. See Section 3.5 for zoning definitions.
4 The Existing Environment
Page | 10
4.0 The Existing Environment
4.1 Sensitive Receptors
The nearest sensitive receptors are indicated in Figure 3.1 above and Figure 4.1 below. Bickley
Creek, indicated in both figures is located to the south of the proposed premises..
4.2 Contamination
The Certificate of Title includes a memorial recorded under the Contaminated Sites Act 2003
registered 1/9/2016.
4.3 Compliance - Contaminated Sites Act
4.3.1 Previous Investigations & Approvals
Enpoint Environmental Asset Management was engaged by the landowner of Lot 9005, Allott Way
Maddington to prepare a Site Management Plan for Lot 9005 (attached).
As per the SMP document
Enpoint has been engaged by the Hughes Family Trust (HFT) to prepare a Site Management Plan
(SMP) to facilitate the clearance of Environmental Condition number 9 contained within the
Western Australian Planning Commission (WAPC) conditional approval to subdivide Lot 9005
Allott Way, Maddington. This SMP applies to provisional Lots 521, 522 and 523, which
collectively comprise an area of approximately 3.1 hectares.
Subsequently, DWER received a Mandatory Auditor's Report in respect of the submitted SMP. In
response, a letter was forwarded by Contaminated Sites Branch (attached) confirming as follows:
Based on the information provided, DER and DoH concur with the Auditor's conclusions that
investigations for soil, soil gas, and groundwater contamination at the site were carried out in
general accordance with the DER's Contaminated Sites Guidelines.
and
Proposed building designs should be endorsed by an accredited DER Auditor and subsequently
approved by the DER and DoH, prior to development and construction on the site. Subsequently,
DER considers that Condition 9 of WAPC Subdivision Approval No. 152284 has been
satisfactorily met for Lot 9005 Allot Way, Maddington.
4.3.2 Development Plan
As per Section 1.5 above, the proponent has prepared drawings for the Site Development Plan
(attached) that comply with the recommendations of the Enpoint Site Management Plan. Ground
disturbance will be limited to footings required for the asphalt manufacturing plant and sewer and
water mains connections. Footings for the asphalt plant will be to a maximum depth of 700 mm (Page
3c - Development Plans). Trenching and footing works will not be left open for more than two days
as per Enpoint recommendations. The landowner has committed to ground water issued as per
Enpoint's recommendations outlined in the Site Management Plan.
4 The Existing Environment
Page | 11
Table 4.1 Distance to nearest sensitive receptor. Distance to Bickly Creek is approximately 330 metres (from Google Maps).
5 The Asphalt Manufacturing Plant
Page | 12
5.0 The Asphalt M anufacturing Plant
5.1 Summary
Manufacturing infrastructure includes:
cold aggregate feeder bins that are topped up by loader from the ground bins
rotating heater/dryer drum
pug-mill for mixing heated aggregate and liquid bitumen
gob-hopper for loading trucks.
Integrated infrastructure includes:
bag house
diesel-heated 30,000 litre mobile bitumen tanker
Support infrastructure includes
front-end loader
aggregate stock piles in 3-sided aggregate ground bins
5,000 litre on-site bunded fuel tank.
diesel generator
An oblique view of the layout of a similar plant is provided in Figure 5.1 and tabulated information is
provided in Table 5.1 below.
Raw materials and fuels required for energy will include
Five grades of aggregate
Bitumen
Diesel fuel.
No fillers other than recovered bag house dust (see Section 5.3 below), will be included in the
manufacturing process.
5.2 Asphalt Plant Operation
Table 5.1 below provides a tabulated summary of data provided by the manufacturer.
Aggregates are transferred by loader from the stock-pile ground bins to the cold-aggregate feeder
bins, each bin for a given aggregate size. Under computer control, aggregate is loaded from the cold
aggregate bins onto a slinger conveyor in precise quantities for loading into the dryer/heating barrel.
While the drum rotates to ensure even heating, a diesel-fired burner within the barrel heats the
aggregate to a set temperature. Dust generated during aggregate rotation within the drum is drawn
into the baghouse by a powerful induction fan with cleansed air discharged via the vertical stack. The
baghouse includes a return auger which returns filtered dust back to the drum for recycling into
product.
The asphalt production operation is controlled by a computer-control panel that is housed in a sound-
proof, air-conditioned control cabin. Proportioning of the output from the feeder bins is controlled by
5 The Asphalt Manufacturing Plant
Page | 13
this computer with outputs of between 25 and 50 tonnes per hour being selected, depending on the
grade of aggregate used.
When aggregate rotating within the dryer/heater drum reaches the required temperature, the hot
aggregate is dumped to a pug-mill which is then closed before the exact volume of liquid bitumen is
injected. The pug-mill is rotated for approximately one minute to deliver hotmix asphalt. The fresh
hotmix asphalt is then dumped via the discharge chute to the enclosed, inclined hotmix conveyor to
the gob-hopper where it may wait or be immediately delivered into a waiting truck.
5.3 Bag House
The baghouse consists of a two levels system where course particles in the air stream are removed via
a gravity collector and fine particles collected in air-filtration bags. Accumulated dust in the filtration
bags are removed via and air pulsing system. Filtered air is then discharged via a vertical stack on the
bag house.
Filter bags are of American heat-resistant Nomex material with a maximum instantaneous temperature
of 235℃. Elastic clamps secure bags to the bag frame to facilitate fast and secure installation and
replacement. Access to the bag house for periodic inspection and bag replacement is via the bag
house top cover. The upper level of the baghouse normally operates below atmospheric pressure
where bag cleaning is achieved via a pulsing system that is a reverse flow of normal atmospheric
pressure into the upper chamber.
Dust collection bags are periodically pulsed to shake loose collected dust. A screw auger returns both
gravity and pulsed dust to the filler elevator where dust is re-incorporated into the manufacturing
process.
Aggregate heating and baghouse filtration is an integrated system designed to operate between 80 and
180°C. The integrity of the bag house is insured via air temperature monitoring at the induction fan.
A short-term limit of 220°C is allowed with an over-temperature cut-out at 230°C. Also, an alarm is
set to alert the operator in the event that temperature drops to 80°C. The over-temperature stop device
consisting of a cold-fan valve on the inlet of the baghouse ensuring that temperatures within the
baghouse do not exceed the short-term temperature limit - in the event that temperature exceeds the
cut-out value, the control system will cut off fuel to the burner in the dryer/heater drum.
The temperature control system not only protects the integrity of the baghouse, but also ensures that
product quality is maintained by ensuring the drum temperature remains within defined limits - this
also prevents blue-smoke emissions arising from over-temperature exceedances. In an older
generation of plants, blue-smoke emissions arising from over heating were a major cause of odour
emissions.
5.4 Diesel Fuel
Diesel fuel will be stored on site in a 5,000 litre tank bunded to accommodate 110% of the volume of
the storage tank (5,500 litres).
5 The Asphalt Manufacturing Plant
Page | 14
5.5 Bitumen
Bitumen will be stored on-site in a mobile 40,000 litre heated/stirred container. The temperature of
the stored bitumen will be maintained using an on-site generator.
Table 5.1. Mobile Asphalt Plant data
Integrated Asphalt Manufacturing Plant Tietuo Machinery QLB-40
Average Capacity of Machinery 40 tonnes per hour.
Stack height 4.2 m
Plant Motive Power Diesel Generator
Heater/Dryer Drum Burner Diesel Fuel
Bitumen Tank Temperature Electric, via Diesel Genset.
Cold Aggregate Bins 5
Bitumen Storage and Heating Tank 30,000 litres
Installed Diesel Storage 5,000 litres
Water for dust control & safety 2,000 L
Installed Genset 265 KVa
Asphalt maximum daily production 300 tonnes
Estimated Annual Production if fully utilised < 50,000 tonnes
Baghouse
Dust Collection Area 160 m2
Operating Temperature 80°C to 180°C
Maximum Temperature 230°C
Dust Collection 266 Nomex Bags
Dust Collection Efficiency Better than 99%
5 The Asphalt Manufacturing Plant
Page | 15
Figure 5.1. Oblique view of an installed plant (from Fujian Tietuo Machinery - but not in the configuration as per the proposal)
6 Environmental Management
Page | 16
6.0 Environment al M anagement
6.1 Introduction
The proposed operation presents very low, if not negligible environmental risk or amenity issues for
nearest sensitive premises. Furthermore, the operation does not result in the discharge of liquid or
solid wastes that could be of adverse impact to either groundwater or to Bickley Creek located to the
south of the proposed premises.
Potential impacts identified in the EPA Guidance Statement No.3 are noise, dust and odour. These
emissions can be further identified:
Emissions from the aggregate heater/dryer drum.
Potential odour emissions from hot-mix asphalt
Dust from aggregate handling and movement.
Noise from generators, front-end-loader aggregate movement.
Potential spillages include hot bitumen, diesel fuel and lubricating oil.
6.2 Fugitive Odour Emissions – Hotmix Asphalt
6.2.1 Source of Emissions
Hotmix asphalt has a characteristic odour that is present when hotmix asphalt during manufacture, or
is either being loaded or transported or applied to roadway or other surfaces.
6.2.2 Odour Emission Control
Aggregate/bitumen mixing takes place within an enclosed pug-mill. Digital monitoring of the drum
temperature ensures aggregate heating does not exceed a defined temperature limit - thus maximising
fuel efficiency and ensuring controlled temperature for aggregate/bitumen mixing - also eliminating
the generation of fugitive blue-smoke emission. When mixing is completed hotmix asphalt is briefly
exposed to the atmosphere when dumped to the gob-hopper via an enclosed conveyor and later when
dumped to a waiting truck. The load is covered as soon as truck loading is completed so as to
minimise temperature loss which also minimises fugitive odour emission.
6.2.3 Mitigation
Aggregate heating and liquid bitumen temperature is maintained in the optimum temperature
bandwidth for the hotmix product that avoids fuel wastage, quality degradation and odour
emission. The manufacturing process is digitally controlled and is monitored in the operators
cabin by the operator. Odours arising from a previous generation of older asphalt plants were
related principally to blue-smoke emissions caused by overheating the bitumen/aggregate mix
within the heating/drying drum. The proposed operation employs pug mill mixing rather than
bitumen injection to the heating/drying drum.
Departing vehicles carrying hotmix asphalt are required to cover their loads to ensure
optimum temperature is maintained. This requirement also minimises fugitive odour
emissions from moving vehicles.
6 Environmental Management
Page | 17
Potential residential areas and current residentially occupied areas are of sufficient distance
for potential fugitive odour emissions to be of no concern. The location of the
"Residential/Light Industry" zoning to the south of the proposed premises is located at a
distance of about 400 metres (Figure 3.1 above) - however, the status of permanent residence
in the nearest houses is uncertain as the zoning allows mixed industry/residential that does not
at present appear include residential premises. The distance to the nearest currently occupied
residence is 660 metres as shown in Figure 4.1. Furthermore, average seasonal winds (Figure
6.1) are predominantly from the southwest and south - placing nearest sensitive premises
mostly upwind of the proposed operation.
The nearest Bureau of Meteorology weather station to the proposed premises is located at the
City of Gosnells. The average five-year wind rose for Gosnells is shown in Figure 6.1 below.
Comparing Figure 6.1 and Figure 3.1 (Zoning Map) indicates average seasonal winds are
predominantly from the southwest and south - placing nearest potentially sensitive premises
at most upwind of the proposed operation.
6.2.4 Summary
Odour emissions are highly unlikely to impact the amenity of the nearest residential zoned areas due
to:
Employment of modern computer controlled manufacturing process that strictly controls
drum heating temperatures.
Fugitive odour emissions may arise briefly from hot mix asphalt production via gob hopper
and truck loading operation.
Departing vehicles are required to cover hotmix loads that will minimise odour emission.
Sufficient distance to the nearest "Residential" zoned area.
Nearest residential-zoned areas are on average, infrequently downwind of predominant wind
directions.
6.3 Point Source Emissions
6.3.1 Source of Emissions
The drying/heating of aggregate within a rotating drum may result in atmospheric particulate
emissions. Heating energy is supplied by diesel fuel to the drum burner - resulting in potential
gaseous emission.
6.3.2 Atmospheric Emission Control
Air from the aggregate drying and heating process is forced through the baghouse by a high velocity
inductions fan before being discharged via the vertical stack on the baghouse.
6.3.3 Mitigation
Stack testing on the same model plant indicates that point-source particulate emissions to be
substantially below DWER guideline emission value.
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Stack tests previously conducted on the same model plant in Western Australia -dated
29/3/2016 gave the following emissions data (g/min, STP dry):
o Particulates: 25.0
o NO2: 9.0
o SO2: 11.0
o CO: 12.0
Predominant wind directions in relation to the various zoned areas is presented in Section
6.2.3 above.
Operators carry out first-echelon maintenance of the plant including the baghouse on a
scheduled basis. The baghouse also receives an annual service where all bags are checked
and replaced as required. Spare bags are kept in stock for replacement when required.
Operators will be required to immediately report to management an increase in the visible tail
discharge from the stack. In the event of a suspected bag leak - coloured die may be added
the baghouse induction port. Any leakages will be evident once the baghouse has been
opened for inspection.
6.3.4 Summary
Particulate emissions are unlikely to impact the local environment because:
Efficient filtering of particulates arising from drying/heating process
Regular maintenance and bag replacement will be conducted to ensure compliance with
DWER emission requirements.
Any visible increase stack tail emissions will be followed up by an inspection and
replacement of bags as required.
Periodic stack testing will be conducted to verify compliance with DWER licence conditions.
6.4 Gaseous Emissions
6.4.1 Source of Emissions
During the heating and mixing process, various gases are released to the atmosphere as per Section
6.3.3 above. These arise from the combustion of fuel and the balance of fuel oxygen mix at the
burner.
6.4.2 Mitigation
Annual stack-testing will be conducted to verify compliance with DWER gaseous and
particulate emission limitations.
6.5 Dust Emissions – Materials Handling
6.5.1 Source of Emissions
A front-end loader will be used to top up cold aggregate bins from stock piles. Dust may be generated
during loading operations under windy conditions.
Dust may be generated by the movement of the loader and trucks.
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6.5.2 Mitigation
Mitigation factors include:
Stockpiles will be maintained within 3-sided bins that are not loaded beyond the height of bin
walls.
All materials movement will be conducted on a hardstand to facilitate good housekeeping
practices.
Any aggregate and dust spills to the hardstand will be removed on a daily basis.
During dry and windy conditions, stock piles and operating/trafficed areas will be kept damp
using misting sprays.
6.6 Noise Emissions
6.6.1 Source of Emissions
Noise will be generated by several sources including
Aggregate movement and loading operations
Generator operations
Vehicle movement.
6.6.2 Mitigation
Asphalt plants are not inherently noisy operations. The dominant noise source from the
asphalt plant itself is due to rotation of aggregate in the heating drum – together with other
noise emissions from vehicles and generator operation, noise emissions would be
substantially below the statutory noise limitation at the premises boundary.
The proposed premises is bounded by tall tilt-up panel concrete buildings on the south and
west of the site. These buildings will severely attenuate any noise emissions to the south and
west.
The distance to the nearest sensitive premises is at a sufficient distance to mitigate any
potential noise emissions.
Perth Asphalt Supply is aware of the requirements of the Environmental Protection Noise
Regulations, 1997 and will ensure that the Regulations are observed.
6.7 Diesel/Bitumen Storage
6.7.1 Source of Emissions
Potential hydrocarbon spills may occur during refilling and refuelling operations - these are most
likely to be either drip or at most small volumes less than a few litres.
6.7.2 Mitigation - Diesel
All operations will be conducted on a hard stand that will prevent loss of hydrocarbons to the
underlying soil and facilitate any potential spill cleanups.
A spill-kit bin will be kept on site for cleanup in the event of a minor spill.
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Diesel fuel will be stored according to DWER bunding requirements. Diesel fuel will be
stored within a bunded compound that is capable of containing 110% of the largest container
within the bund.
The fuel supply to the diesel burner is controlled by pump at the burner. Consequently, fuel is
drawn under negative pressure. Any potential leakage in the supply line would result in air
entering the fuel line and fuel running back to the tanker.
Any minor spills and drips during refuelling will be recovered by containing the spill with
sand and returning this to the manufacturing process.
6.7.3 Mitigation - Bitumen and Lubricating Oils
Any bitumen that might be spilled during topping up of the bitumen tank will set rapidly to a solid
state as it cools. This will be retrieved and recycled into the operation. Bitumen does not present an
environmental risk. Roads in WA are surfaced with the same product that will be produced by the
proposed operation.
It is likely that the diesel generator and other plant will require servicing while located within the
proposed premises. Such plant will operate and be surfaced on a hardstand. Any potential spills are
likely be very minor and easily recovered. All waste lubricating oil will be stored for recycling as per
City of Gosnells recommendations and requirements.
6.8 Water Discharge
6.8.1 Source of Emissions
Misting water sprays will be used for controlling:
dust emissions
aggregate stockpiles
operational/trafficked hardstands
It is possible that excessive use of water will result in a discharge from the premises.
6.8.2 Mitigation
Mitigation factors include:
Saturation of stockpiles is to be avoided as drying will require additional heating.
Water sprays on stockpiles and hardstand will not be to the point of run-off.
6.9 Solid/Liquid Wastes
6.9.1 Source of Emissions
Wastes will not be generated by asphalt operations apart from waste lubrication oils from servicing
plant and equipment.
6.9.2 Mitigation
In the event, waste lubrication oils are collected for recycling.
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6.10 Discharges to Land and Water
6.10.1 Source of Emissions
The asphalt operation will not discharge any wastes or substances to land or water.
6.11 Stormwater Contamination
6.11.1 Source of Emissions
The only possible contamination of stormwater would be due to diesel drips and spills during
refuelling.
6.11.2 Mitigation
See measures required to mitigate diesel-refuelling risks above.
6.12 Stormwater Management
Stormwater will be managed according to earthworks and drainage above prepared and implemented
by the landowner.
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Figure 6.1. Wind Rose for City of Gosnells.
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7.0 Limit ations
This report has been prepared in accordance with the usual care and thoroughness of the consulting
profession for use by Perth Asphalt Supply Pty Ltd in application to the Department of Environment
Regulation on behalf of Perth Asphalt Supply Pty Ltd. The report is based on generally accepted
practices and standards at the time that it was prepared. No other warranty, expressed or implied, is
made as to the professional advice included in this report. It is prepared in accordance with
information provided by the client Perth Asphalt Supply Pty Ltd and various government agency
websites that are assume to be correct at the time of interrogation.
In regard to the methodology adopted and sources of information outlined in this report, no
independent verification of this information beyond the agreed scope of works has been undertaken
and the author assumes no responsibility for any inaccuracies or omissions. No indications were
found during the investigations that information contained in this report was false. Advice has been
sought from relevant public servants, however although this advice was provided in good faith, there
is no guarantee that the advice is accurate.
This report was prepared during May and July 2017 and is based on the conditions encountered and
information reviewed at the time of preparation. The author disclaims responsibility for any changes
that may have occurred after this time.
This report should be read in full. No responsibility is accepted for use of any part of this report in
any other context or for any other purpose or by third parties. This report does not purport to give
legal advice. Legal advice can only be given by qualified legal practitioners