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16.0 Water management – Emergency discharge plans
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16.0 Water management – Emergency discharge plans
# Department Condition Description Completion date Status
Pre-Dec 2012 Post-Dec 2012
35 52d ivCompletion of upgraded emergency response plans to cover all regulated water and waste storage facilities
April 2014
36 49h, 52d i IV 53B c Develop Emergency Discharge Management Plan July 2013
Commitments completed Evergreen Commitments
Commitments work in progress Firm deliverables for that month
16.1 INTRODUCTION
QGC’s water management facilities handle substantial water volumes of varying quality. A ‘best practice’
approach requires plans and procedures for situations where equipment or facility failure could result in a spill or
emergency discharge.
A specific response guide has been developed for unforeseen emergency discharges from critical elements in
the water management system and related infrastructure. The focus is on risk scenarios using the likelihood or
potential to cause significant impacts on MNES.
This document presents the QGC Upstream Gas Field - Unforeseen Emergency Discharge Plan (UEDP) for the
QCLNG project. The plan has been prepared to fulfil Commitment 36 of the Stage 2 CSG WMMP for compliance
with the requirements of EPBC approval 53B c (formerly conditions 49h (I) and (II)) and 53B e (i) (III) (formerly
Condition 52d (I) (IV)) of federal approval EPBC 2008/4398 to develop a Stage 3 CSG WMMP.
16.1.1 PLAN FRAMEWORK AND CONTEXT
The UEDP has been designed as an overarching plan and Emergency Response Guideline (ERG) that links directly
with existing QGC incident management and emergency response plans developed under QGC’s Environmental
Management System (EMS) in accordance with the international standard AS/NZS ISO 14001.
The plan is a specific response guide developed for handling unforeseen emergency discharges from critical
elements of QGC’s water management system and related infrastructure. The plan is focused on scenarios
that are ranked in accordance with or potential to cause significant or long-term impacts or harm to a Matter
of National Environmental Significance (MNES) and events or situations that results in an abnormal state and
require an immediate response in order to contain, minimise and/or to prevent – serious environmental harm as
defined in Queensland's Environmental Protection Act 1994.
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The primary risk scenarios specifically identified in this Plan include:
• Loss of containment or discharges from CSG water storages and aggregation ponds;
• Loss of containment or discharges from brine storages and aggregation ponds;
• Uncontaminated discharge of CSG water, brine or treatment chemicals from water treatment facilities; and
• Serious rupture or damage to CSG water or brine trunklines.
This Plan complies with the relevant HSSE Management System standards and procedures as listed in the table
of references (Section 16.1.2) and has been developed to complement all existing and future management plans
and procedures for responding to environmental incidents including QGC’s site-based emergency management
procedures, dam safety emergency response plans and individual pond operating plans for individual CSG
regulated storages and water treatment plant (WTP) operations management plans.
Emergency preparedness and response at QGC is not described in one document. There are several layers of
emergency management at QGC and a range of standards, plans, procedures and guides prepared for the various
organisational and system levels. An overview of emergency management at QGC is provided in Figure 16-1.
This UEDP shall function as an Emergency Response Guide (ERG) for the purpose of QGC’s management
structure and should be read and implemented in conjunction with the QGC Environmental Emergency Incident
Response and Reporting Procedure (QCOPS-OPS-ENV-PCE-000012) and any relevant site-based emergency
response procedure in place for a particular site or asset type.
16.1.2 REFERENCE DOCUMENTS
This list of reference documents to the UEDP presented here should be read in conjunction with this
Stage 3 WMMP:
• Emergency Management Standard: QCQGC-BX00-HSS-STD-000011 (QGC, 2012);
• Incident Management Plan: QCQGC-BX00-HSS-PLN-000002 (QGC, 2012);
• Procedure for Environmental Emergency Incident Management: QCOPS-OPS-ENV-PCE-000014 (QGC, 2012);
• Environmental Emergency Incident Response and Reporting Procedure: QCOPS-OPS-ENV-PCE-000012 (QGC,
2012); and
• Site Emergency Response Procedure – Kenya: QCOPS-BX55-HSS-PCE-000001-4 (QGC, 2013).
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Figure 16-1 – QGC's environmental emergency management structure
BG Internal Control
Framework (Standards)
Safety CaseBG-ST-HSSE-AI-
001
EnvironmentBG-ST-HSSE-
ENV-001
Incident Reporting and Investigation
BG-ST-HSSE- EFF-001
Crisis Management
BGA-HSSE-GEN- ST-0900
QGC Incident and Near Miss Reporting,
Investigation and Analysis Standard
QCQGC-BX00-HSS-STD- 000011
QGC Emergency Management Standard QCQGC-BX00-HSS-STD-
000011
Safety Case – Upstream Operations
QCOPS-OPS-HSS-SAC-000001
QGC Incident Management Plan (IMP)QCQGC-BX00-HSS-PLN-
000002
Environmental Emergency Incident
Management ProcedureQCOPS-OPS-ENV-PCE-
000014
Environmental Emergency Incident
Response and Reporting Procedure
QCOPS-OPS-ENV-PCE-000012
QGC Emergency Response Procedure
(site based)
Emergency Response Guide (ERG)
This document outlines the minimum mandatory requirements for ensuring
all incidents and near misses are reported,
investigated, analysed and corrective and preventive
action implemented to prevent reoccurrence .
A Safety Case is a document that ensures
that suitable and sufficient measures are in place to
prevent a major accident or environmental event and
to reduce the effects of these events should
they occur .
Development against the requirements of ISO 14001 (as part of QGC’s EMS) and to provide linkage between
the BG Standards and QGC’s emergency response
relating specifically to an environmental incident
management .
Documents the requirements for responding to and investigating and environmental
incident . This document should be referred to in conjunction with ERG’s . It shall be used to
compliment the EMS Procedure for Environmental Emergency Incident Management .
BG Standards are documents developed by
BG Group Governance Committee . Compliance
with BG Standards is mandatory for all BG
employees and contractors .
This document outlines the fundamental concepts and
principles for emergency management activities undertaken at QGC . It also outlines the QGC
Emergency Management System structure .
This document outlines QGS’s Incident Management System .
It describes the identification, notification, escalation and activation arrangements of the QGC
Indicent Management Team (IMT) . It takes
precedence over all ERPs .
Emergency Response Procedure’s (ERPs) are a
site specific document that outlines the Emergency Response for a specific
area .
The ERG is a specific response plan developed for handling a particular type of emergency event
(i .e . gas explosion) . They are contained as
appendices to the broader Emergency Response
Procedure .
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16.1.3 EXCLUSIONS AND RELATIONSHIP WITH EXTERNAL PROJECTS
The UEDP has been developed to incorporate QGC’s QCLNG upstream gas field CSG water management
activities. In accordance with the Department variation to project conditions dated 2 November 2012 EPBC
2008/4398 QCLNG Gasfield, this plan does not incorporate elements relevant to treated CSG water provided to
SunWater under the Glebe Weir or Chinchilla Weir Pipeline Projects.
60A: The proponent must treat all coal seam gas water as required under this approval before the coal seam
gas water associated with the approved action enters the following pipelines:
• The Kenya to Chinchilla Pipeline referred to the Department (EPC 2011/6000); and
• The Woleebee Creek to Glebe Weir pipeline (EPBC 2011/6181).
Once the CSG water has been treated as required under this approval and has entered the pipelines specified
above, conditions 43-60 will no longer apply to that water. QGC is actively engaged with SunWater through
relevant water service agreements for the projects and to develop and implement resource management
and monitoring plans and operating protocols to ensure compliance with project conditions and sustainable
beneficial use.
While the Kenya to Chinchilla Weir and Woleebee Creek to Glebe Weir pipelines are not included in this plan, QGC
has amended the Kenya Site Emergency Response Procedure (ERP) (QCOPS-BX55-HSS-PCE-000001-4) and QGC
Incident Reporting Investigation Procedure (QCQGC-BX00-HSS-PCE-000017) to ensure notifications and response
actions are in place to appropriately manage risks associated with augmentation of town water supplies for the
Kenya to Chinchilla Pipeline Project, including relevant notification procedures.
16.2 ENVIRONMENTAL VALUES PROTECTION OBJECTIVES
QGC has identified the following objectives for protecting environmental values in relation to CSG water
management:
• The extraction and treatment of CSG water is not causing adverse impacts to the surrounding environment,
including site specific environmental values;
• Treated water for beneficial reuse is meeting specified water quality criteria tailored for the intended reuse
application and to avoid any adverse environmental impacts;
• Avoid the potential for accidental spills and leaks of brine ponds and saline waste;
• Avoid surface water contamination of nearby waterways;
• Protect the groundwater quality in the vicinity of the WTP and storage ponds by minimising the potential for
seepage of untreated CSG water and brine product from storage ponds to groundwater;
• Minimising the generation of concentrated brine waste from the WTPs;
• Decommissioning and rehabilitation of brine ponds/basins is to be undertaken as required throughout the
life of the project; and
• Maximise treated water recovery from the WTPs for beneficial reuse.
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16.3 WATER MANAGEMENT CRITERIA
QGC has developed a suite of management criteria intended to be utilised as a tool to assess the overall
performance of the QGC's CSG Water Management Strategy and the continual development and implementation
of the system.
The management criteria provided below incorporate specific environmental objectives against which each
component or use within the proposed water management network is to be monitored and assessed for
performance as they are progressively implemented into the network.
The criteria also constitute active tools for avoidance, management and mitigation for potential and actual
environmental harm including unforeseen emergency discharges. Control measures have been proposed to
manage the potential risks of unauthorised release or spills to an acceptable level. These measures incorporate
standard actions and procedures including monitoring.
These management criteria are not set or enforced as compliance limits but act as performance tool to assist
QGC with the continual improvement and efficiency of the water management strategy and system. The criteria
have been developed in compliance with the requirements of Section 310D (5)(e) of the EP Act and in accordance
with the associated environmental conditions contained within QGC’s relevant upstream gas field environmental
authorities.
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CSG Water
Management
System
Management
Objective
Monitoring
Frequency
Management Criteria
Performance Indicator and Actions
Production
Wells1
To monitor the
quality of CSG water
produced from
wells to ensure
environmental values
of end use beneficial
reuse are preserved
Produced water
from a sample of
production wells
is sampled and
analysed at least
annually
Performance Indicators
• Produced water quality parameters that exceed
a deviation of 20% above long-term average2 are
investigated
• Early warning detection (LOR) of restricted substances
that may cause environmental harm
• Early warning detection of elevated levels of parameters
that may cause integrity issues to well and pipeline
infrastructure4
Potential Actions Required
• Additional monitoring undertaken inform investigation
into change in chemical parameter concentrations
• Control use of water or reduce water production from
affected wells
Wellhead
Separator
Zero leaks and spills
from infrastructure.
No visible damage to
vegetation or soil on
surrounding land
Producing wells to
be visited at least
monthly to check
for signs of leaks or
vegetation damage
Performance Indicators
• Surveillance Monitoring indicates vegetation health
surrounding facilities
• Infrastructure integrity (leakage data)
Potential Actions Required
• Investigate any signs of leaks or damage to vegetation to
locate, isolate, contain and/or repair any leaks identified
Water
Gathering
Line
• Minimise leaks
or spills from
gathering line
and pumping
infrastructure
• No visible
damage to
vegetation or soil
on surrounding
land
• No observable
reduction in
groundwater
quality
Annual inspection
of ground above
a sample of the
water gathering
lines for evidence
of water leakage or
vegetation damage
Pipeline Integrity
Management
System (PIMS)
Performance Indicators
• Surveillance monitoring indicates vegetation health
surrounding facilities
• Infrastructure integrity (leakage data)
Potential Actions Required
• Investigate any signs of leaks or damage to vegetation
to locate and isolate, contain and/or repair any leaks
identified
• Inspections of additional sections of water gathering
system if warranted by findings from initial inspections
Water
Trunklines
• Minimise
leaks or spills
from pipeline
and pumping
infrastructure
• No visible
damage to
vegetation or soil
on surrounding
land
• No observable
reduction in
groundwater
quality
Data recording and
telemetry (Flow)
Annually
(surveillance)
Performance Indicators
• Surveillance monitoring indicates vegetation health
surrounding facilities
• Infrastructure integrity inspections
• Leakage rates inferred by flow metering trends and/or
variance between inflow and outflow meters
Potential Actions Required
• Determine whether inferred leakage rates are consistent
with leaking trunkline
• Locate any leaks, then isolate, contain and/or repair those
leaks
1 QGC currently samples all CSG production well. As the project expands, a selection of representative CSG production wells will be sampled in each
operating field. 2 Across the standard suite of parameters tested under the existing QGC monitoring program. 3 Limit of reporting. 4 Indicated through existing water quality sampling program of Low Point Drains (LDP).
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CSG Water
Management
System
Management
Objective
Monitoring
Frequency
Management Criteria
Performance Indicator and Actions
In-field
Storage
Tanks, Ponds
Regional
ponds
(untreated
CSG water)
• Zero leaks and
spills
• No storage
failures or
overtopping
• No untreated
CSG water
entering the
receiving
environment
• No observable
reduction in
groundwater
quality
Tanks
Data recording and
telemetry (level and
flow)
Ponds
Annual integrity
inspections
Performance Indicators Tanks
• High level alarm
Regional Ponds
• Early warning water forecasting indicates inflows
may exceed 1/5 of the regional pond storage capacity
(storages sized for five days at peak flows)
• Percentage completion of specified maintenance and
inspection routines
Potential Actions Required
• Confirm real time data reports are consistent between
flow metering systems
• Increase pond monitoring frequency
• Assess maintenance backlog and determine whether
additional resources are required to rectify backlog
• Take action to reduce levels by diverting flow, reducing
residence time in regional storage ponds and/or
increasing flows to WTP
Aggregation
Dams
(untreated
CSG water)
• No visible
damage to
vegetation or soil
on surrounding
land
• No observable
reduction in
groundwater
quality
• No mortality or
entrapment of
local fauna and
livestock
• No accumulation
of salts and other
contaminants
in the sub-soil
profile below the
collection system
• No storage
failures or
overtopping
Data recording and
telemetry (Level)
Quarterly
(quality and
surveillance)
Performance Indicators
• Early warning water level reaches Maximum Operating
Level (MOL)
• Mandatory Reporting Level (MRL)
• Full Integrity of security and fauna exclusion fencing
around HDPE lined facilities
• Pond wall, liner, and seepage collection system integrity
controls confirmed through shallow groundwater
monitoring underdrainage leakage detection
• No pond overtopping as controlled by water transfer
balancing and routine MRL monitoring
• No emergency release under normal and design storm
conditions
• EA Conditions, Notification Schedule I:
• Annual dam inspections by suitably qualified people
• Early warning detection of restricted substances that
may cause environmental harm
• Early warning detection of elevated levels of parameters
that may cause integrity issues to well and pipeline
infrastructure
Potential Actions Required
• Confirm monitoring data reports and increase
monitoring frequency as required based on analysis of
inflow forecasting;
• System modification to divert/reduce inflows and
investigate integrity/quality concerns
• Manage storage pond capacity through balancing via
transfer of water between CSG water dams
• System modification to divert/accept increase flow to
WTP and beneficial use
• Manage inflow to the pond (including diversion or
reduction of production)
• Works to rectify any leakage or seepage detected from
dams
• Works to rectify fauna exclusion structures surrounding
HDPE lined facilities
5 Infield storage tanks are designed for three hour residence time at peak flows 6 A telemetry project for ponds is currently being developed and has not yet been implemented project-wide. Where telemetry does not exist, interim transition
monitoring programs for water levels will continue to operate. Pond level monitoring according to existing systems may vary in frequency depending on
individual pond type/use and operating status.
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CSG Water
Management
System
Management
Objective
Monitoring
Frequency
Management Criteria
Performance Indicator and Actions
Reverse
Osmosis
Plants
• CSG water to
be treated to
acceptable
standards for
approved end
uses
• No visible
damage to
vegetation or soil
on surrounding
land
• Zero leaks and
spills outside
bunded areas
• No unauthorised
discharges
to receiving
environments
• No chemical
containment
failures
Data recording and
telemetry (flows
and pressure and
some water quality
parameters)
Daily, weekly and
monthly water
quality monitoring
depending on
beneficial use
Monthly
(surveillance)
Performance Indicators
• Water to be treated to specific water quality standards
relevant to the end use
• Early warning departure from water quality
requirements through daily monitoring of key permeate
characteristics (such as EC)
• Surveillance monitoring and maintenance program
indicates infrastructure integrity
Potential Actions Required
• Confirm monitoring data reports and increase
monitoring frequency
• System modification to reduce or divert inflows and
investigate integrity/quality concerns, corrective actions
taken where required
• Isolate or change source water
• System modification to recirculate outflows back to
storage ponds during remedial works and testing
• Manage production (including reduction of production)
to be instigated, remedial works required
• Implementation of Plant Operator environmental
inspection program
Treated
Water Pond
(and Pump
Stations)
• Zero leaks and
spills
• No storage
failures
• No observable
deterioration in
treated water
quality
• No mortality or
entrapment of
local fauna and
livestock
Data recording and
telemetry (Level)
Daily and weekly
(Quality)
Quarterly
(surveillance)
Performance Indicators
• Early warning water level reaches Maximum Operating
Level (MOL)
• Full Integrity of security and fauna exclusion fencing
around HDPE lined facilities
• No pond overtopping as controlled by water transfer/
balancing and routine MRL monitoring
• Early warning departure from water quality
requirements through daily monitoring of key permeate
characteristics (such as EC)
Potential Actions Required
• Confirming monitoring data reports and increase
monitoring frequency as required based on analysis of
inflow forecasting;
• System modification to reduce/divert inflows and
investigate integrity/quality concerns, corrective actions
taken where required
• Manage storage pond capacity through increasing
outflows to beneficial use where possible
• Manage WTP production (including reduction of
throughput) to be instigated, remedial works required
• Recirculate water through water treatment plant if
required or redirect water to a beneficial use for which
the quality is acceptable or alternative use such as
construction where available
• Works to rectify fauna exclusion structures surrounding
HDPE lined facilities
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CSG Water
Management
System
Management
Objective
Monitoring
Frequency
Management Criteria
Performance Indicator and Actions
Brine
Containment
Ponds
• Zero leaks and
spills
• No storage
failures
• No observable
reduction in
groundwater
quality
• No accumulation
of salts and other
contaminants
in the sub-soil
profile below the
collection system
• No mortality or
entrapment of
local fauna and
livestock
• Water quality fit
for purpose or
for contractual
agreement
Data recording and
telemetry (Level)
Quarterly
(Quality and
surveillance)
Performance Indicators
• Early warning water level reaches Maximum Operating
Level (MOL)
• Mandatory Reporting Level (MRL)
• Full Integrity of security and fauna exclusion fencing
around facilities
• Pond wall, liner, and seepage collection and
recirculation system integrity controls confirmed
through shallow groundwater monitoring/
underdrainage leakage detection and surveillance
monitoring
• No pond overtopping as controlled by water transfer/
balancing and routine MRL monitoring
• Annual dam inspections by suitably qualified people
Potential Actions Required
• Confirm monitoring data reports and increase
monitoring frequency as required based on analysis of
inflow forecasting
• System modification to reduce/divert inflows and
investigate integrity/quality concerns, corrective actions
taken where required
• Manage brine production (including reduction of WTP
throughput) to be instigated, remedial works required
• Works to rectify any leakage or seepage detected from
dams
• Works to rectify fauna exclusion structures surrounding
HDPE or synthetic geomembrane lined facilities
• Implementation of actions resulting from annual pond
inspections
Table 16-1 – QGC's water management criteria – management network
Although not specifically required for the purpose of the UEDP and for the purpose of the plan, the management
criteria outlined below for on tenement use of CSG water and preferred outlet uses has been included for
information and to illustrate how QGC will manage and monitor these activities on a routine basis and some of
the high-level control and actions in place to ensure sustainable operation.
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CSG Water Use
CSG Water
Management
System
Performance
Objective
Management
Criteria
Monitoring
Frequency
Performance Indicator and Actions
Managed
utilisation of
CSG Water for
authorised
Petroleum
Activities
Waste
irrigation
Dust suppression
Pond
construction
• No increase in
weed and pest
species
• No
accumulation
of salts
and other
contaminants
in the soil
profile
• No degradation
of soil profile
and structure
• No visible
damage to
vegetation
or soil on
surrounding
land
As required
(per event/use)
Performance Indicators
• Visual surveillance monitoring
(pre and post-event)
• Water application rates, quality
monitoring and data logging in
accordance with the QGC Land
Release Management Plan
• EA Condition – Dust Suppression
and Land Release Limits
Potential Actions Required
• Restrict/control use of water and
initiate investigations and further
monitoring
• Remediation action implemented
• Performance Improvement
process to be initiated
Direct Supply to
Water Service
Provider
Non-QGC
Infrastructure
• Provision of
100% of agreed
supply
• No reduction in
agreed supply
water quality
Real-time telemetry
(flows/pressure and
some water quality
parameters)3
Daily, weekly and
monthly water
quality monitoring
depending on
beneficial use
Monthly
(surveillance)
Performance Indicators
• Early warning departure from
water quality requirements
through daily monitoring of key
permeate characteristics
(such as EC)
Potential Actions Required
• Confirm monitoring data
reports and increase monitoring
frequency
• System modification to reduce/
divert inflows and investigate
integrity/quality concerns,
corrective actions taken where
required
• Manage production (including
reduction of production) to
be instigated, remedial works
required
• Recirculate water through water
treatment plant if required or
redirect water to a beneficial
use for which the quality is
acceptable
1 QGC’s environmental responsibility under the QGC QCLNG CWMP and Project EAs is limited to supplying the required treated associated water to the
nominated Treated Water Pond (to agreed Quality and Quantity). 2 Metering estimation is based on system performance 3 Real-time telemetry is an automated data transfer process and does not occur instantaneously.
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CSG Water Use
CSG Water
Management
System
Performance
Objective
Management
Criteria
Monitoring
Frequency
Performance Indicator and Actions
Aquifer
Repressurisation
(Managed
Aquifer
Recharge) Pilot
(Prefeasibility
Trials)
Post
treatment facility
• Zero leaks and
spills outside
bunded areas
• No storage
failures
Quarterly water
quality monitoring
of ponds
Monthly
(surveillance)
Performance Indicators
• Surveillance monitoring indicates
vegetation health surrounding
facilities, and infrastructure
integrity (no leakage)
Potential Actions Required
• System modification to restrict/
divert inflows
• Regular maintenance regime
• Shut down if required at
pump infrastructure or
isolate trunklines to instigate
maintenance
Recharge process • No degradation
of background
groundwater
quality
• No over-
pressurisation
of the aquifer
Real-time Telemetry
(flows/pressure and
some water quality
parameters)
Aquifer Monitoring
(quality)
Performance Indicators
• Water quality monitoring to
determine no deterioration of
background water quality in the
target aquifer
• Aquifer pressure monitoring to
determine no over-pressurisation
of injection well or surrounding
monitoring wells.
Potential Actions Required
• System modification to restrict/
control injection flows and
inflows
• Shut down if required at pump
infrastructure to Investigate
quality/pressure concerns
4 Refer treated water ponds objectives and criteria 5 To be determined through the feasibility stage of the aquifer pressurisation project investigations
Table 16-2 – Water management criteria – water outlets and use
16.4 ENVIRONMENTAL CONSEQUENCE RATING ASSESSMENT AND MANAGEMENT RESPONSE
QGC has considered the environmental consequence rating profile of each of the process element and over-
arching strategies for the management of CSG water, including the intended treatment proposed. The key
environmental risks for each management option have been assessed and assigned a rating based on potential
consequence with regard to environmental harm.
For the purpose of the UEDP all key infrastructure elements of the water management system have been
captured in the Environmental Rating Table (Table 16-3). The assessment and rating does not take into account
the likelihood or risk profile of such an incident occurring as the QGC Water Management Criteria (Section 16.3)
have been specifically developed to allow for continuous evaluation and optimisation of the water management
system and thus reduce the likelihood or potential for such events. Therefore the ratings assessment below is
specifically derived to determine trigger and response actions for such unforeseen emergency events if these
were to occur.
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Consequence
type
Consequences Level
Negligible I Minor II Moderate III Major IV Critical V
Natural
Environment
Negligible impact
on fauna/flora
habitat, aquatic
ecosystems or
water resources.
Incident reporting
according to
routine protocols
Impact on fauna,
flora and/or
habitat but no
negative effects
on ecosystem.
Requires
immediate
regulator
notification
Short-term
impact on
sensitive
environmental
features. Triggers
regulatory
investigation
Long-term impact
of regional
significances
on sensitive
environmental
features
(e.g. wetlands).
Regulatory
intervention
and/or action
Destruction
of sensitive
environmental
features. Severe
impact on
ecosystems.
Regulatory
and high level
government
intervention
and/or action
Potential Consequence I II III IV V
Wells – Spills and leaks
Gathering lines and trunklines – Spills and Leaks
Treated water ponds – Wall failure or discharge
Water treatment facilities-- Spills and discharge of CSG water, brine or chemicals
Regulated CSG ponds – Wall failure or discharge
Regulated brine ponds – Wall failure or discharge
Table 16-3 – UEDP Environmental Consequence Rating Table
QGC has separated the risk scenarios for unforeseen emergency discharges into two key categories: primary
and secondary risks. These categories have been selected based on the specific consequence rating relating to
unforeseen discharges from those elements of the system and the potential for of significant environmental
harm. The process of categorisation allows nomination of key areas that require specific UEDP actions above and
beyond the existing standard incident and emergency response procedures covering all unauthorised releases as
detailed in Section 16.5).
Secondary risk scenarios include accidental spills and leaks that are contained and do not result in an indirect or
direct release to groundwater or surface waters with potential for significant or long-term impacts or harm.
Secondary risk scenarios are determined as those that have been categorised with a potential consequence rating
of I, II or III and require response actions as per the standard procedures listed in Section 16.5 and include:
• Restricted spills of treated CSG water, brine or water treatment chemicals from Water Treatment Facilities;
and
• Minor leaks or spills of treated CSG water or brine from pipelines or storage ponds.
Primary risk scenarios include unforeseen emergency discharges that would result in indirect or direct release to
groundwater or surface waters with potential for significant or long-term impacts or harm.
288
Primary risk scenarios are determined as those categorised with a potential consequence rating of IV or V and
require additional UEDP monitoring, response and reporting actions as listed in Section 18.6, including:
• Loss of containment or discharges from CSG water storages and aggregation ponds;
• Loss of containment or discharges from brine storages and aggregation ponds;
• Uncontained discharge of CSG water, brine or treatment chemicals from water treatment facilities; and
• Serious rupture or damage to CSG water and brine trunklines.
Prescribed management measures including monitoring described in Section 16.6 are in additional to the
standard procures under existing Environmental Incident Plans listed in Section 16.5 are specific triggers enacted
through implementation of this UEDP.
16.5 ENVIRONMENTAL INCIDENT RESPONSE AND REPORTING PROCEDURES
The following procedures shall give guidance and direction on how to handle specific types of incidents relating
to all unauthorised releases and unforeseen discharges. These procedures are a summary of immediate response,
control and monitoring actions. The full procedures are detailed in the QGC Environmental Emergency Incident
Response and Reporting Procedure QCOPS-OPS-ENV-PCE-000012 including identification of the steps and
responses to be undertaken upon discovery of an unauthorised release.
Figure 16-2 – Environmental emergency incidents – unauthorised releases action response procedures
Emergency or Incident Environmental Impact Action Response Plan
Unauthorised release (1)
Dam collapse, breach or
overflow (2)
CSG waters
Chemicals (hydrocarbons,
TEG/other)
Brines and concentrates
Hydraulic stimulation release
Spills to land or water
Downstream flooding
Refer to Section 16.5.1 CSG Water Release
Refer to Section 16 .5 .2 Fuel, Oil and Chemical Spills
Refer to Section 16.5.3 Brines and Concentrates
Refer to Section 16.5.4 Hydraulic Stimulation Fluid Releases
Refer above
Refer to Individual Pond Operating Procedures (IPOPs)
Refer to Section 16.6.1 Dam Collapse, Breach or Overflow
289
16.5.1 CSG WATER RELEASE
Immediate response
• The person(s) after initial discovery of the incident should immediately seek to stop the flow of water if safe
and possible to do so;
• Notification of supervisor of the incident providing relevant incident category assessment according to QGC
Incident Report Matrix;
• Incident category assessment according to QGC Incident Assessment Matrix;
• Supervisor to advise Line Manager of incident in accordance with QGC Emergency Response Procedure
protocols;
• Supervisor to notify Field Environment Officer (FEO) and complete an incident report;
• Supervisor to contact Land Access Consultant if incident occurred off QGC-owned land, and provide details of
incident and actions to address the situation; and
• Land Access Consultant to contact landowner and advise of incident.
Control and minimise
• Attempt to stem the flow of the water by creating earthen bunds or using surrounding material available:
Extra caution should be taken to minimise any impacts on nearby environmentally sensitive areas (ESA) or
watercourses;
• Determine estimated quantity of water released; and
• Trace the flow of the spill to its maximum extent.
Assessment
• Perform sampling of the water at origin of the spill recording the following parameters:
• pH
• Electrical Conductivity (EC)
• Temperature (°C)
• FEO shall visit site of incident if required to do so for assessment:
• Confirm details of the spill (i.e. cause of the release, extent of spill, location, water quality parameters as
reported);
• Take photographic record of incident;
• Identify significant features (waterways, vegetation types, built structures within the receiving
environment); and
• Confirm incident category in accordance with QGC Incident Assessment Matrix.
• FEO to report details of incident to Manager Environment;
• Supervisor to issue Incident Flash, in accordance with QGC Incident and Near Miss Reporting and
Investigation Requirements; and
• Supervisor of owning business unit reports incident in Synergi in accordance with QGC Incident Reporting,
Investigation and Analysis Standard.
290
Notification
• Manager Environment provides notification to the regulatory body (DEHP) consistent with conditions of site
specific EA:
• Initial advice to be provided within 24 hours of becoming aware of incident; and
• Written Incident report required to be submitted to DEHP within 10 business days of the initial
notification in accordance with site specific EA.
• Immediate notification to SunWater and the Queensland Office of Water Supply Regulator is required where
an unplanned release of contaminant to waters occurs within the area of the Chinchilla or Dawson River
Drinking Water Supply Schemes which involves a material impact to the water quality provided under those
schemes in a way that would have an adverse effect on public health; and
• The Department notification is undertaken in accordance with Condition 106 of the gas field approval
including reporting of non-compliance and remedial action within five business days.
Remediation and monitoring
• FEO to assess need for ongoing environmental monitoring based on impact. Monitoring may include but is
not limited to:
• Soil and/or water sampling to be undertaken to assess changes from background. For soils monitoring
this may include but not be limited to three replicate samples at depth intervals of 0 to 10 cm, 20 to 30
cm and 50 to 60 cm at both an analogue and the impact site as a minimum. For monitoring of waters
this program must include upstream, downstream and impact site monitoring procedures. Advice should
be sought from a suitably qualified person in the area of land contamination matters before sampling is
undertaken; and
• Regular visual inspections of the site, including but not limited to the establishment of fixed-point
photographic monitoring points.
• FEO to assess and provide advice on the need for remedial works that addresses issues of environmental
impact. FEO shall provide such advice to the business unit who will be responsible for implementation. Such
works may include but are not limited to:
• Reinstatement of landform;
• Removal of ponded water;
• Re-vegetation of impacted areas;
• Removal of contaminated soil with cartage and disposal to be undertaken by an appropriately licensed
operator. Waste records to be forwarded to and retained by the FEO; and
• Establishment of exclusion zones to allow natural site rehabilitation.
All sampling of soils and waters shall be undertaken in accordance with the DEHP Monitoring and Sampling
Manual 2009, Environmental Protection (Water) Policy 2009 Version 2 (or any subsequent approved version).
*Sampling of soils and waters shall be undertaken in accordance with the DEHP Monitoring and Sampling Manual 2009 Environmental Protection
(Water) Policy 2009 Version 2.
291
16.5.2 FUEL, OIL, CHEMICAL OR EFFLUENT SPILLS
Immediate response
As per procedure in Section 16.5.1.
Control and minimise
• Check if the necessary product information is available. Refer to the Safety Data Sheet (SDS);
• Determine estimated quantity of contaminant; and
• Trace the flow of the spill to its maximum extent.
*All SDS, the register of hazardous substances and risk assessments are available via Chem Alert accessible by the
intranet at: http://qgcintranet/hsse/Pages/Chem%20Alert/Chem 20%Alert.aspx.*
Assessment
As per procedure in Section 16.5.1.
DEHP notification
As per procedure in Section 16.5.1.
Remediation and monitoring
As per procedure in Section 16.5.1.
16.5.3 BRINES AND CONCENTRATES
Immediate response (as per procedure in Section 16.5.1).
16.6 UEDP SPECIFIC RESPONSE ACTIONS AND REPORTING PROCEDURES
The following procedures shall give guidance and direction on how to handle significant unauthorised releases
and unforeseen discharges resulting in potential for significant or long-term environmental impact through
direct or indirect release to surface or groundwater.
These procedures are to be implemented in addition to those identified in Section 16.5.
The response plan can be triggered by four events resulting in direct or indirect release to surface or groundwater:
• Loss of containment or discharges from CSG water storages and aggregation ponds;
• Loss of containment or discharges from brine storages and aggregation ponds;
• Uncontained discharge of CSG water, brine or treatment chemicals from water treatment facilities; and
• Serious rupture or damage to CSG water and brine trunklines.
292
16.6.1 REGULATED DAM COLLAPSE, BREACH OR OVERFLOW (CSG WATER OR BRINE)
The Mandatory Reporting Level (MRL) is the level at which it is mandatory that the holder of a DEHP authorised
Environmental Authority must communicate to DEHP that there is a possibility of a spillway discharge from a
regulated dam.
Once the MRL is reached, QGC must act to reduce the pond water level to below the MRL with the aim of
reducing the risk of a pond spill occurring. Available action strategies are dependant on the individual pond type
and its connectivity to the overall water management systems and thus have to be considered on a case-by-case
basis. All regulated dams are constructed with engineered spillways to ensure that in the unlikely event of a spill
occurring that the integrity of the pond structure is maintained.
Should it become necessary to discharge CSG water from a regulated storage, such an action would be done with
notification to and engagement with the Queensland Regulator. In the event of such a release a specific receiving
environment water quality monitoring program would be implemented involving the monitoring at a number of
locations in receiving waters downstream of the release.
Figures 16-3, 16-4 and 16-5 provide regionalised surface water catchment plans for the three QCLNG Project
development areas. The plans indicate all key QCLNG project related ponds (existing and proposed at the time of
publication). The plans are to be used as a tool in the selection of potential upstream and downstream surface
water monitoring locations. In addition the plans indicate proposed surface water monitoring locations specific
to the three (3) QGC Water Treatment Plant Hubs, these locations are further described in Table 16-6 UEDP
monitoring locations for water treatment plant hubs.
Table 16-4 provides a summary of typical mechanisms to avoid, minimise and manage risks of emergency
discharge from regulated storages. This table should be read in conjunction with the water management criteria
and controls identified in Section 16-3.
Avoid Minimise Manage if Releases Occur
Operate ponds below Maximum
Operating Level (MOL)
If a pond(s) reaches MOL immediately
review system water balance and
forecast and consider if action is
required
Mitigation and monitoring procedure
implemented
Continuous monitoring of CSG water
systems (inflows, storage levels and
outflows) including increased frequency
if required
Where modelling or monitoring
indicated pond(s) may exceed MRL
initiate system management actions
(e.g. water transfer to other ponds,
increase outflows to WTP, diversion
or cease inflows to pond) to avoid or
minimise potential for controlled spill
event
• Agency and landholder notifications
• Remediation, monitoring and
reporting
Regular water balance forecasting
to provide early warning of system
peaks or triggers for management and
contingency planning
Where routine inspections indicate risk
of potential loss of hydraulic integrity
of a pond, immediately initiate system
management actions to avoid or
minimise potential for uncontrolled
spill event (e.g. actions as per above, or
where required)
Management controls during emergency
event (refer Table 16-5)
Table 16-4 – Mechanisms to avoid, minimise and manage risks – regulated storages
293
Assessment and monitoring
• Determine estimated quantity of water released;
• Trace the flow of the spill to its maximum extent;
• Implement surface water quality sampling and monitoring;
• Initial site and surface water sampling of the water at origin of the spill and downstream and at an upstream
reference point should at a minimum record the following parameters:
• pH;
• Electrical Conductivity (EC); and
• Temperature (°C);
• Where initial surface water sampling downstream at the nearest property boundary indicates elevated levels
of the above parameters in concentrations that have the potential to cause significant environmental harm
then additional UEDP monitoring should be actioned as per below;
• All of the major QCLNG project ponds (existing and proposed) are identified in Figures 16-3, 16-4 and 16-5,
current at the date of publication of the plan:
• Where these ponds fall inside regional water treatment plant hubs, potential surface water monitoring
locations should be sourced from the Table 16-7 – Unforeseen Emergency Discharge Monitoring
Locations – Water Treatment Plant Hubs. These specific monitoring locations are also identified on the
corresponding catchment area Figures 16-4 and 16-5;
• Where these ponds fall outside the identified regional water treatment plant hubs, then suitable
upstream and downstream surface water monitoring locations should be determined by the on-site
FEO or relevant environmental coordinator with guidance from the Figures 16-3, 16-4 and 16-5 indicating
surface water catchments for the respective development regions. For the Southern Gas Fields region two
(2) potential monitoring locations have been proposed for consideration as these are active QGC Receiving
Environment Monitoring Plan (REMP) sites. For the Central Gas Fields and additional four (4) sites have
been located north of the Condamine River along Columboola Creek;
• Individual Pond Operating Plans identify sensitive receptors, surface and ground water users and
downstream land users who would be impacted by these receptors in case of emergency discharge such
as a dam break. The referenced list of downstream receptors and locations may be used as a guidance and
to assist in tracing the flow of the spill to its maximum extent;
• Where downstream groundwater allocations are identified in the IPOP, advice should be sought from the
Environment Manager (based on geologist input) for these ponds; and
• Conduct monitoring of nearby water monitoring bores if required where there is likelihood of significant
or long-term groundwater impacts from infiltration.
294
Figure 16-3 – QCLNG Project UEDP Catchment – Southern Gas Fields
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C o n d a m i n e R i v e rC o n d a m i n e R i v e rC a t c h m e n tC a t c h m e n t
M a c i n t y r e & W e i r R i v e r sM a c i n t y r e & W e i r R i v e r sC a t c h m e n tC a t c h m e n t
M o o n i e R i v e rM o o n i e R i v e rC a t c h m e n tC a t c h m e n t
Kenya PondsCentralWTP
Sean 1David Pond
Jen 2(Janda)
Kenya EastStoragePond
Broadwater
Celeste
Glendower
RubyJo
HIGH ST
WINTONS RD
DALBYJANDOWAE RD
WARREGO HWY
DALBY KOGAN RD
MACALISTER BELL RDWARRAKOGAN RD
DAANDINENANDI RD
KOGANCONDAMINE RD
TARA KOGAN RD
SURATDEVELOPMENTAL RD
MOONIE HWY
CHINCHILL
AKOGAN
RD
W
ERANGA
NORTH RD
ROAD RD LAXTO
N ST
TALBOT ST
MACALISTER
WILKIE CREEK RD
BISLEY RD
ARNOLDS RD
CAMPBELLST
MIE
GU
N YA H
CT
GA
ITH
S R
D
BRYANT ST
TULL
Y RD
JONES RD
KUMARILLA
LANE
RED
LAN
D C
T
GAT
HS
RD
WILKIERD
KUM
BAR
ILLA
LAN
E
WIL
LAC
YS R
D
DAV
ISR
D
WEITZELS RD
HIGH ST
BRYAN
TSRD
DO
RA
NS
RD
KITTLES
RD
SAN
DY
CR
EEK
RD
MAR
ULA
RD
P LU
NKET
TR
D
BRIDLES RD
MI L LERSEASE M ENT RD
RYDERSRD
BO BBLACKS RD
WILKINS RD
ROSS RD
KUPUNN
DULEEN RD
FABI
ANS
RD
WINTONS RD
PERCYJURGS RD
WO
LKIS
RD
WA R
RA
WE I
RAC
CES
SR
D
LOGIE RD
WEBB RD
HILLIARS RD
DALG
LEI S
HR
D
ARN
OLD
SR
D
BID
S TR
UPS
RD
BISLE
YR
D
GRAHAMS RD
HO
SIE
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TULLY RD
WAL
LAC
ES
RD
CO
X R
D
EHLMA RD
MC
CU
TCH
EON
S R
D
WARRA
JANDOWAE RD
KARINGALAPUNYAL RD
CREEK RD
S W
OLS
KIS
RD
STEINOHRTSRD
MALES DR
OLMS R
D
W ESTS RD
WOLFFS RD
WI LSONS RD
HAY
STA
CK
NO
RTH
RD
CASEYS RD
WIL
GA
DR
WARRA
MARNHULL RD
CHAPPELLS RD
OLD
PER
TH R
D
SKER
MAN
S RD
WHYALLA RD
BARTELSR
D
MCKAYS RD
PRIC
ES
RD
BUN
GYBAH
RD
CAVES RD
VIC
KER
Y R
D
V ELL
NAS
OSRD
HEALYS
CROSS ING RD
MITCHELLS RD
LEWING
TONR
D
BAN
ANA
BRID
GERD
BOBARTS RD
KUOUNNDULEEN RD
COOPERS RD
NORMAN RD
KUPUNN DULEEN RD
ELSD
ENS
RD
WARA
MARNHULL RD
SHARPES RD
GLEN MONA RD
CAR
LIS
HS
RD
SAN
DY
CR
EEK
RD
RID
GE
RD
HEA
LYS
RD
WO LSKIS RD
GRAYS RD
TERESE RD
STRETCHWORTH RD
MARTINS RD
FLETTS RD
SMITHS RD
HAR
WO
OD
S R
D
COLS RD
BILLABONG LANE
KOOKABURRA DR
COMMUNITYLANE
EMU PDE
BULLOAK DR
TOOMBILLA RD
CHARLES DR
FLETTSRD W
FOREST RD
HOADLEYS RD
WIL
LIAM
S R
D
TUCKERANG RD
CYPRESS RD
GR
AD
EL R
D
GRAHAMS RD
MACALISTER TULLY RD
BABANA
BRIDGE RD
WE
ST V
ALLE
Y R
D
HEREWARD RD
R C
LAR
KS
RD
CROSBIES RD
WEIAMBILLA RD
NAN
DI R
D
LUCHTS R D
MUHLINGS RD
KOFOEDS RD
HAMILTONS RD
WARRA
KOGAN RD
OHALLO
RANS
RD
JONES RD
HOPELANDSCHOOL RD
HURSES RD
THE
WAL
LABY
TR
K
SOUTH RD
CH
UR
CH
RD
TIMOTHY RD
FREES RD
FAGANS RD
MYRA RD
WEGNERS R
D
DAANDINE
SOLDIERS
RD
MATTHEWS RD
SMITHS RD
KLEID
ONS RD
JOSEPH RD
WARA MARNHULL RD
KUM
BAR
ILLA
LAN
E
FORESTRY RD
GRAHA MS RD
GREENBANK
ACCESSRD
WATTLE DR
NORTH KOGAN RD
CHINCHILLASIXTEEN MILE RD
SEIGMEIERS RD
PIRRINUAN
APUNYAL RD
NA U
SC
HUTZ
RD
MCKEE DR
WO
LSK
IS R
D
WARRAMARNHULL RD
ALEX
AN
DER
S R
DNORTH KOGAN RD
WAUGH RD
ARCHER
S CROSS
ING R
D
KUMBARILLA
FOREST RD
DAANDINE WARRA RD
TAYLORS
RD
NINE MILE STOCK ROUTE RD
KUMMEROWS RD
QUIRES RD
BROWNS RD
THETEN RD
B RIDERS RD
JO
NES RD
ROCKY CR
KUPU
NN
RD
WOLFFS RD
CRYSTAL CREEK RD
LEAHYS
RD
KUM
BAR
ILLA
RD
EHL M
ABO
UN
DARY
RD
SOUTH RD
BRAEM
ARW
ARRA
RD
YOUNGS RD
JEITZS RD
OLDW
ARREGO
HWY
BRAEMAR
BOUNDARY
RD
CLYN
ES RD
BOUNDARY RD
REDGUM RD
MACALISTERWILKIE CREEK RD
MACALISTER
PIRRINUAN RD
AVE
NU
E R
D
D UC
KLO
S CH
OOL
RD
HAYSTACK RD
SCHULTZS RD
CLA
RKE
S R
D
MULLERS RD
HOPELAND SCHOOL RD
MACALISTER
BELL RD
CAR
MO
DYS
LAN
E
WA
RRA
CANAGA
CR
EEKR
D
MONTROSE RD
CECIL PLAINS
MOONIE RD
STEINOHRTS RD
CROWDERS
CREEK RD
DAANDINE RD
WEITZELSRD
CAMBRIDGE
CROSSINGRD
BRO
A DW
ATE
RR
D
SIXTEEN MILE
HALL RD
WILKIN RD
BANANA
BRIDGERD
MCLEODS
RD
CARTENS LANE
RESERVEDR D
DUCKLO GULERA RD
GO
RAN
BA
LAN
E
KUMBARILLA LANE
MCLARENS RD
KE RRS RD
GU
LER
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D
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CR OS
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DULEEN DAANDINE RD
WARREGOHWY
KENTS RD
WAR
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MILLBANK RD
CECIL PLAINS RD
DAANDINENANDI RD
JANDO
WAE
MAC
ALIS
TER
RD
BEEL BEE RD
WARREGOHWY
OLD MOONIE RD
CECIL PLAIN S MOONIE RD
KOGANCONDAMINE RD
HALLIFORD RD
TARA
KOGANRD
SURATDEVELOPMENTAL RD
DALBYKOGAN RD
MOONIE
HWY
WIL
KIE
CR
EEK
FINCH CREEK
TWEN
TY SIX MILE C
REEK
SIXTEEN MILE CREEK
WAA
R W
AAR
CR
EEK
PIEB
ALD
CR
EEK
WAMBO CREEK
CRAWLERSCREEK
MOONIE RIVER
KOGA
N CR
EEK
DOWNFALL CREEK
CATT
LE C
REEK
WEIR R
IVER
HORSE GULLY
FINCH CREEK
EASTERN BRANCH CREEK
DURABILLA CREEK
TOOMBILLA CREEK
PIEB
ALD
CR
EEK
BRAEMAR C
REEK
BRO
ADW
ATER
GU
LLY
COORANGA CREEK
JANDOWAE C
REEK
DUNMORE CREEK
FINCH CREEK
CROW
DER
CREE
K
JINGI
JINGI
CREEK
JIMBOUR CREEK
MORAMBY CREEK
BACK C
REE
K
GILBERT GULLY
CONDAMINE RIVER
KOGAN CREEK
A
B
"Based on or contains data provided by the State of Queensland (Department of Natural Resources and Mines) 2013. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws."
Note: Every effort has been made to ensure this information is spatially accurate. The location of this information should not be relied on as the exact field location.
Unforeseen Emergency Discharge Plan - South
8/07/2013 CL M_28494_03DATA SOURCE:
Map Projection: GDA94
±0 2 4 6 8
Kilometers
ADATE: CREATED BY: REV NO:MAP NO:MAP TYPE: OtherDCDB, Watercourses, Fields, Springs- DNRM; Roads - StreetPro v3LNCHECKED BY:
1:250,000SCALE: at (A3)
_̂ UEDD Monitoring Locations
Threatened Ecological Communities
Box Gum Grassy Woodland
Brigalow
Grassland
SEVT
Weeping Myall Woodlands
Trunkline - Water
Proposed Trunkline - Water
! Ponds
" Water Treatment Plant
Proposed UIC
QGC Owned Land
QCLNG EIS Area
Subcatchment Area
Major Watercourse
Minor Watercourse
Principal Road
Secondary Road
Label UEDD Monitoring Locations Easting NorthingA Condamine River at Banana Bridge crossing on the Warra-Kogan Road. 277441 7027643B Condamine River at Healy’s Crossing, south of Warra. 280411 7022132QCLNG Project UEDP Catchment – Southern Gas Fields
Kilometres
0 2 4 6 8 10
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C o n d a m i n e R i v e rC o n d a m i n e R i v e rC a t c h m e n tC a t c h m e n t
M a c i n t y r e & W e i r R i v e r sM a c i n t y r e & W e i r R i v e r sC a t c h m e n tC a t c h m e n t
M o o n i e R i v e rM o o n i e R i v e rC a t c h m e n tC a t c h m e n t
Kenya PondsCentralWTP
Sean 1David Pond
Jen 2(Janda)
Kenya EastStoragePond
Broadwater
Celeste
Glendower
RubyJo
HIGH ST
WINTONS RD
DALBYJANDOWAE RD
WARREGO HWY
DALBY KOGAN RD
MACALISTER BELL RDWARRAKOGAN RD
DAANDINENANDI RD
KOGANCONDAMINE RD
TARA KOGAN RD
SURATDEVELOPMENTAL RD
MOONIE HWY
CHINCHILL
AKOGAN
RD
W
ERANGA
NORTH RD
ROAD RD LAXTO
N ST
TALBOT ST
MACALISTER
WILKIE CREEK RD
BISLEY RD
ARNOLDS RD
CAMPBELLST
MIE
GU
N YA H
CT
GA
ITH
S R
D
BRYANT ST
TULL
Y RD
JONES RD
KUMARILLA
LANE
RED
LAN
D C
T
GAT
HS
RD
WILKIERD
KUM
BAR
ILLA
LAN
E
WIL
LAC
YS R
D
DAV
ISR
D
WEITZELS RD
HIGH ST
BRYAN
TSRD
DO
RA
NS
RD
KITTLES
RD
SAN
DY
CR
EEK
RD
MAR
ULA
RD
P LU
NKET
TR
D
BRIDLES RD
MI L LERSEASE M ENT RD
RYDERSRD
BO BBLACKS RD
WILKINS RD
ROSS RD
KUPUNN
DULEEN RD
FABI
ANS
RD
WINTONS RD
PERCYJURGS RD
WO
LKIS
RD
WA R
RA
WE I
RAC
CES
SR
D
LOGIE RD
WEBB RD
HILLIARS RD
DALG
LEI S
HR
D
ARN
OLD
SR
D
BID
S TR
UPS
RD
BISLE
YR
D
GRAHAMS RD
HO
SIE
RS
RD
TULLY RD
WAL
LAC
ES
RD
CO
X R
D
EHLMA RD
MC
CU
TCH
EON
S R
D
WARRA
JANDOWAE RD
KARINGALAPUNYAL RD
CREEK RD
S W
OLS
KIS
RD
STEINOHRTSRD
MALES DR
OLMS R
D
W ESTS RD
WOLFFS RD
WI LSONS RD
HAY
STA
CK
NO
RTH
RD
CASEYS RD
WIL
GA
DR
WARRA
MARNHULL RD
CHAPPELLS RD
OLD
PER
TH R
D
SKER
MAN
S RD
WHYALLA RD
BARTELSR
D
MCKAYS RD
PRIC
ES
RD
BUN
GYBAH
RD
CAVES RD
VIC
KER
Y R
D
V ELL
NAS
OSRD
HEALYS
CROSS ING RD
MITCHELLS RD
LEWING
TONR
D
BAN
ANA
BRID
GERD
BOBARTS RD
KUOUNNDULEEN RD
COOPERS RD
NORMAN RD
KUPUNN DULEEN RD
ELSD
ENS
RD
WARA
MARNHULL RD
SHARPES RD
GLEN MONA RD
CAR
LIS
HS
RD
SAN
DY
CR
EEK
RD
RID
GE
RD
HEA
LYS
RD
WO LSKIS RD
GRAYS RD
TERESE RD
STRETCHWORTH RD
MARTINS RD
FLETTS RD
SMITHS RD
HAR
WO
OD
S R
D
COLS RD
BILLABONG LANE
KOOKABURRA DR
COMMUNITYLANE
EMU PDE
BULLOAK DR
TOOMBILLA RD
CHARLES DR
FLETTSRD W
FOREST RD
HOADLEYS RD
WIL
LIAM
S R
D
TUCKERANG RD
CYPRESS RD
GR
AD
EL R
D
GRAHAMS RD
MACALISTER TULLY RD
BABANA
BRIDGE RD
WE
ST V
ALLE
Y R
D
HEREWARD RD
R C
LAR
KS
RD
CROSBIES RD
WEIAMBILLA RD
NAN
DI R
D
LUCHTS R D
MUHLINGS RD
KOFOEDS RD
HAMILTONS RD
WARRA
KOGAN RD
OHALLO
RANS
RD
JONES RD
HOPELANDSCHOOL RD
HURSES RD
THE
WAL
LABY
TR
K
SOUTH RD
CH
UR
CH
RD
TIMOTHY RD
FREES RD
FAGANS RD
MYRA RD
WEGNERS R
D
DAANDINE
SOLDIERS
RD
MATTHEWS RD
SMITHS RD
KLEID
ONS RD
JOSEPH RD
WARA MARNHULL RD
KUM
BAR
ILLA
LAN
E
FORESTRY RD
GRAHA MS RD
GREENBANK
ACCESSRD
WATTLE DR
NORTH KOGAN RD
CHINCHILLASIXTEEN MILE RD
SEIGMEIERS RD
PIRRINUAN
APUNYAL RD
NA U
SC
HUTZ
RD
MCKEE DR
WO
LSK
IS R
D
WARRAMARNHULL RD
ALEX
AN
DER
S R
DNORTH KOGAN RD
WAUGH RD
ARCHER
S CROSS
ING R
D
KUMBARILLA
FOREST RD
DAANDINE WARRA RD
TAYLORS
RD
NINE MILE STOCK ROUTE RD
KUMMEROWS RD
QUIRES RD
BROWNS RD
THETEN RD
B RIDERS RD
JO
NES RD
ROCKY CR
KUPU
NN
RD
WOLFFS RD
CRYSTAL CREEK RD
LEAHYS
RD
KUM
BAR
ILLA
RD
EHL M
ABO
UN
DARY
RD
SOUTH RD
BRAEM
ARW
ARRA
RD
YOUNGS RD
JEITZS RD
OLDW
ARREGO
HWY
BRAEMAR
BOUNDARY
RD
CLYN
ES RD
BOUNDARY RD
REDGUM RD
MACALISTERWILKIE CREEK RD
MACALISTER
PIRRINUAN RD
AVE
NU
E R
D
D UC
KLO
S CH
OOL
RD
HAYSTACK RD
SCHULTZS RD
CLA
RKE
S R
D
MULLERS RD
HOPELAND SCHOOL RD
MACALISTER
BELL RD
CAR
MO
DYS
LAN
E
WA
RRA
CANAGA
CR
EEKR
D
MONTROSE RD
CECIL PLAINS
MOONIE RD
STEINOHRTS RD
CROWDERS
CREEK RD
DAANDINE RD
WEITZELSRD
CAMBRIDGE
CROSSINGRD
BRO
A DW
ATE
RR
D
SIXTEEN MILE
HALL RD
WILKIN RD
BANANA
BRIDGERD
MCLEODS
RD
CARTENS LANE
RESERVEDR D
DUCKLO GULERA RD
GO
RAN
BA
LAN
E
KUMBARILLA LANE
MCLARENS RD
KE RRS RD
GU
LER
A R
D
H E AL
EYS
CR OS
SING RD
DULEEN DAANDINE RD
WARREGOHWY
KENTS RD
WAR
RAKO
GANRD
MILLBANK RD
CECIL PLAINS RD
DAANDINENANDI RD
JANDO
WAE
MAC
ALIS
TER
RD
BEEL BEE RD
WARREGOHWY
OLD MOONIE RD
CECIL PLAIN S MOONIE RD
KOGANCONDAMINE RD
HALLIFORD RD
TARA
KOGANRD
SURATDEVELOPMENTAL RD
DALBYKOGAN RD
MOONIE
HWY
WIL
KIE
CR
EEK
FINCH CREEK
TWEN
TY SIX MILE C
REEK
SIXTEEN MILE CREEK
WAA
R W
AAR
CR
EEK
PIEB
ALD
CR
EEK
WAMBO CREEK
CRAWLERSCREEK
MOONIE RIVER
KOGA
N CR
EEK
DOWNFALL CREEK
CATT
LE C
REEK
WEIR R
IVER
HORSE GULLY
FINCH CREEK
EASTERN BRANCH CREEK
DURABILLA CREEK
TOOMBILLA CREEK
PIEB
ALD
CR
EEK
BRAEMAR C
REEK
BRO
ADW
ATER
GU
LLY
COORANGA CREEK
JANDOWAE C
REEK
DUNMORE CREEK
FINCH CREEK
CROW
DER
CREE
K
JINGI
JINGI
CREEK
JIMBOUR CREEK
MORAMBY CREEK
BACK C
REE
K
GILBERT GULLY
CONDAMINE RIVER
KOGAN CREEK
A
B
"Based on or contains data provided by the State of Queensland (Department of Natural Resources and Mines) 2013. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws."
Note: Every effort has been made to ensure this information is spatially accurate. The location of this information should not be relied on as the exact field location.
Unforeseen Emergency Discharge Plan - South
8/07/2013 CL M_28494_03DATA SOURCE:
Map Projection: GDA94
±0 2 4 6 8
Kilometers
ADATE: CREATED BY: REV NO:MAP NO:MAP TYPE: OtherDCDB, Watercourses, Fields, Springs- DNRM; Roads - StreetPro v3LNCHECKED BY:
1:250,000SCALE: at (A3)
_̂ UEDD Monitoring Locations
Threatened Ecological Communities
Box Gum Grassy Woodland
Brigalow
Grassland
SEVT
Weeping Myall Woodlands
Trunkline - Water
Proposed Trunkline - Water
! Ponds
" Water Treatment Plant
Proposed UIC
QGC Owned Land
QCLNG EIS Area
Subcatchment Area
Major Watercourse
Minor Watercourse
Principal Road
Secondary Road
Label UEDD Monitoring Locations Easting NorthingA Condamine River at Banana Bridge crossing on the Warra-Kogan Road. 277441 7027643B Condamine River at Healy’s Crossing, south of Warra. 280411 7022132
295
Figure 16-4 – QCLNG Project UEDP Catchment – Central Gas Fields
X
X
XXXXXX
XXXX
"
"
!!
!
!!
!
!!!
!
!
!!
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_̂
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_̂
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_̂_̂
B a l o n n e R i v e rB a l o n n e R i v e rC a t c h m e n tC a t c h m e n t
C o n d a m i n e R i v e rC o n d a m i n e R i v e rC a t c h m e n tC a t c h m e n t
Glen Eden
Kenya EastStorage Pond
Central WTP
Lauren 1
Windibri WTP Berwyndale South 4
McNulity Pond
Large Kenya PondOrana Pond 1,2,3,4,5RhynieKenya Treated Water Pond Kenya Sedimentation
.
Celeste
CHINCH ILLA
SOUT H RD
TARA KOGAN RD
KOGAN CONDAMINE RD
CH
INCHILLATARA
RD
WARREGO HWY
DOWNES ST
LEICHHARDTHWY
INVERAI RD
CONDAMINEKOGAN RD
LEICHHARDTHWY
CHINCHILL
AKOGAN
RD
THO
RPE
ST
BAKI
NGBO
ARD
RD
BLAN
CHARD
ST
CO
LLS
CT
POLLARDST
BISLEY RD
TRAC
K
DAW
SON
S GATE
RD
QUIRKS RD
CO
LE ST
WERONA RD
RUB
BISH
DUM
P RD
JONESS RD
MIZ
PAH
DR
MCKENNA RD
CAM
PIO
NR
D
PARK
ST
BIS
LEY
RD
GA
SKE
LAN
E
CO
LOM
B
ULA STOCK RTE
WEITZELS RD
GEARYS RD
RID
GE
RD
BARKERSRD
MAC
KIE
ST
MARNILANE
RA
CEC
OU
RS E
RD
H
UNTER
RD
CECILIA RD
KRUGERS
RD
LEICH HAR
DT
RD
GOWS RD
GLE
ESO
NS
RD
GORMLEYS
RD
DAW
SON
GAT
ES
RD
PEB
BLEW
OOD ST
MCGOVERNS
RD
ELER SLEALANE E
STEVENSONS RD
WALSHS RD
DAH
LKES
RD
SPINIFIX RD
TEM
P OR
ARI L
YC
LOSE
DR
D
VERONICA RD
BURNCLUITHRD
RO
YALT
Y R
D
AIN
SWO
R TH
ST
SMIT
HS
RD
CLOSED R
D
BOOTHS RD
RYALLS RD
STANKE RD
OLD
PER
TH R
D
LON
DO
NBR
IDG
E R
D
HO
BSO
NSRD
VAN
RE
NAN
S R
D
OAK ST
CHINCHILLA
TARA RD
GLASSON ST
STE
WAR
TS R
D
RIF
LER
ANG
E R
D
CHIN
CHILLA
WOND
AI RD
HO
LM
ES RD
LEICHHARDT
HWY
BUTT
ERFL
Y R
D
C BR
AITH
WAITE
S
RD
BELL
BIR
D R
D
A GRAHAMS RD
WEI
RR
D
AKE
RS
GU
LLY
RD
MCNULTY ST
WEIR RD
TOLMAH CT
NOTHURFTS RD
B TENNYSONS RD
GORRINES RD
CH
INCH
ILLA
SOU
THR
D
OLIV
ERSRD
RYALLS RD
BUTTS RD
LITHGO
WS
RD
BARTELSRD
ALKIRA LANE
HOPELANDSCHOOL RD
CONDAMINEKOGAN RD
MARY RD
REIDS RD
ELLERSLIE
LANDRD
OLD M A
N
LAGOO N
RD
WE
IR L
AN
E
ROXBOROU GH RD
BUTLERS RD
PRIC
E S
T
PHIPPSSUBDIVISION RD
CLOSED RD
BRYA
NTS
RD
CAM
PIO
NS
RD
RENNICKS RD
CLOSED RD
DAYBREAK RD
GOSPERS RD
CHILDS RD
BRENNANS RD
CLOSED RD
THAMES RD
MC
AULL
IFFE
S R
D
WILLI
AMS RD
WIN DM
ILL
RD
SIXTEEN MILE HALL RD
TREGATHLYN R
D
ZELLER ST
CLO
SED
RD
RYANS RD
DOUGA LLS RD
TOM
ALO
U LA
NE
MARY RD
GRAYS RD
WIN
FIEL
D RD
TERESE RD
STEINOHRTS RD
R WALLS RD
MACHANESS RD
ELE RSLEALANE
AUBURN RD
CHANCES
PLA
IN RD
FLETTS RD
MULLERS RD
ELER
SLE
A LA
NE
BILLABONG LANE
KYTES RD
KOOKABURRA DR
LLOYD ST
BURNT
BRIDG
E RD
EMU PDE
HORSWOODS RD
VANR
ENAN
S RD
CHARLES DR
FLETTSRD W
CLARKS RD
RAVENS R
D
VAN RENANS RD
SOUTH RD
DOHERTYS RD
MCLENNANS RD
WE
ST V
ALLE
Y R
D
PASCOES R D
PHIP
PS R
D
GLENOLIVE RD
DAHLERS RD
R K
ER
RS
RD
CLOSED RD
HONNERYS RD
DAV
IES
RD
HUBBARDSR
D
KOFOEDS RD O
HALLOR
ANSRD
KER
WIC
KS R
D
MALES R D
GAZZARDS RD
NOTHDU RF T
SRD
TAMES RD
QUIRES RD
ROBBOS RD
TREASURES RD
AERODROME RD
SOU
THG
LEN
NO
RTH
RD
TEMPORARILY CLOSED RD
HURSES RD
THE
WAL
LABY
TR
K
CH
UR
CH
RD
PHIP
PS R
D
LEICHHARDT
HWY
KRUGERSRD
THOMPSONS
RD
RACE COURSE RD
WAI
NSRD
KUMMEROWS RD
GREENSWAMP RD
BURNCLUITH SCHOOL RD
A GRAHAMS RD
WIL
SON
RD
GRAYS RD
WARREGOHWY
SHERIFFS RD
BARAKULA RD
DAV
IES
RD
SUNNYGLEN RD
FORTUNE
DR
CRYSTAL CREEK RD
BLACKB
UR
NS R
D
HUBBARDS RD
CLOSED RD
SUTT
ON
S R
D
LEES
RD
DR
ILDO
OL R
D
S HE
RW
OO
DR
D
ORCHARD RD
RED
HILLR
D
CAM E
BYRD
GO
RAN
BA
LAN
E
BRAITHWAITES RD
NO
EL
RO
BIN
SON
SR
D
VANRENANS RD
UNDULLACREEK RD
SOUTH RD
B TENNYSONS RD
B KERRS RD
JOSEPH RD
WED
RATS
RD
GOLDEN GLOW RD
ENGINE RD
MYRA RD
C KERRS RD
CHINCHILLASIXTEEN MILE RD
CLYN
ES RD
MALES DR
RYALLS TO HOOKSW OODSTOCK RTE
BIDGOODS RD
TIMOTHY RD
AVE
NU
E R
D
STA
INE
S R
D
FREEMAN
SR
D
LUCKY RD
LEBSA
NFTS R
D
BROWNLIES RD
MC
NU
LTY
RD
BAKERS RD
HOPELAND SCHOOL RD
MONTROSE RD
MILLERS RD
SCOULLERS RD
WEITZELSRD
MILLBANK RD
ISO
NS
RD
DONOGHUE RD
CAM
EBY
RD
BLAC KSWAMP RD
OLD CAMEBY RD
HOOKSWOOD PELHAM R D
CARTENS LANE
ARCHER
S CROSS
ING R
D
MCCASKERS RD
BOORT KOI TO
RYALLS STOCK R T E
GO
OM
BI F
AIR
YME
ADO
W R
D
HU
MBUG
RD
WARRENS
RD
GREENSWAMP RD
THE PEAK RD
FAIRYMEADOW RD
UPPER HUMBUG RD
WEIAMBILLA RD
WERANGA NORTH RD
TARA
KOGANRD
BENN
ETT
SCHO
OLRD
KOGAN
CONDAMINERD
KOGAN
CONDAMINE RD
CHIN
CH
IL L A
T AR
AR
D
WARREGOHWY
CHINCHILLA
MILES
BOTTLE
TREE
CR
EEK
UNDULLACREEK
ELEV
EN M
ILE
CR
EEK
UNDULLACREEK
COLUMBOOLA CREEK
CONDAMINE RIVER
TWEN
TY SIX MILE C
REEK
SIXTEEN MILE CREEK
COBB
AREE
NA C
REEK
WAMBO CREEK
HORSE GULLY
HUMBUG CREEK
ELEV
ENM
ILE
CR
EEK
COOLOOMALA CREEK
WIEAM
BILLA CR
EEK
CHARLEYS C
REEK
CAM
EBY
CR
EEK
UNDULLA CREEK
SAN
DY
CR
EEK
UN
DU
LLA
CR
EEK
ROCKY CREEK
BRANCH
CREEK
NINE MILE CREEK
BAKING BOARD CREEK
JACK
CREEK
DO
GW
OO
D C
REE
K
BOG
RA
MBI
LLA
CR
EEK
F
CD
I
E
GJ
"Based on or contains data provided by the State of Queensland (Department of Natural Resources and Mines) 2013. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws."
Note: Every effort has been made to ensure this information is spatially accurate. The location of this information should not be relied on as the exact field location.
Unforeseen Emergency Discharge Plan - Central
9/07/2013 LN M_28494_02DATA SOURCE:
Map Projection: GDA94 Zone 56
±0 2 4 6
Kilometers
ADATE: CREATED BY: REV NO:MAP NO:MAP TYPE: OtherDCDB, Watercourses, Fields, Springs- DNRM; Roads - StreetPro v3CLCHECKED BY:
1:200,000SCALE: at (A3)
_̂ UEDD Monitoring Locations
Threatened Ecological Communities
Box Gum Grassy Woodland
Brigalow
Grassland
SEVT
Weeping Myall Woodlands
Trunkline - Water
! Ponds
" Water Treatment Plant
Proposed UIC
QGC Owned Land
QCLNG EIS Area
Subcatchment Area
Major Watercourse
Minor Watercourse
Principal Road
Secondary Road
Label UEDD Monitoring Locations Easting NorthingC Nine Mile Creek – upstream QGC Kenya site boundary (tributary of Wieambilla Creek) 251743 7015878D Wieambilla Creek – upstream QGC Kenya site boundary 245393 7015923E Wieambilla Creek – downstream QGC Kenya site boundary 243916 7018865F Wieambilla Creek –downstream QGC Kenya site at the Kogan-Condamine Road crossing. 239703 7022777G Condamine River –upstream QGC Windibri site boundary 235081 7028002H Condamine River –downstream site – outside of managed irrigation reach at Glen Olive Road crossing 220305 7026170I Sandy Creek – upstream QGC Windibri site boundary 234947 7023476J Condamine River –downstream QGC Windibri site boundary 231740 7029169
QCLNG Project UEDP Catchment – Central Gas Fields
Kilometres
0 2 4 6 8 10
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X
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XXXX
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"
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!
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!!!
!
!
!!
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_̂
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_̂
_̂
_̂_̂
B a l o n n e R i v e rB a l o n n e R i v e rC a t c h m e n tC a t c h m e n t
C o n d a m i n e R i v e rC o n d a m i n e R i v e rC a t c h m e n tC a t c h m e n t
Glen Eden
Kenya EastStorage Pond
Central WTP
Lauren 1
Windibri WTP Berwyndale South 4
McNulity Pond
Large Kenya PondOrana Pond 1,2,3,4,5RhynieKenya Treated Water Pond Kenya Sedimentation
.
Celeste
CHINCH ILLA
SOUT H RD
TARA KOGAN RD
KOGAN CONDAMINE RD
CH
INCHILLATARA
RD
WARREGO HWY
DOWNES ST
LEICHHARDTHWY
INVERAI RD
CONDAMINEKOGAN RD
LEICHHARDTHWY
CHINCHILL
AKOGAN
RD
THO
RPE
ST
BAKI
NGBO
ARD
RD
BLAN
CHARD
ST
CO
LLS
CT
POLLARDST
BISLEY RD
TRAC
K
DAW
SON
S GATE
RD
QUIRKS RD
CO
LE ST
WERONA RD
RUB
BISH
DUM
P RD
JONESS RD
MIZ
PAH
DR
MCKENNA RD
CAM
PIO
NR
D
PARK
ST
BIS
LEY
RD
GA
SKE
LAN
E
CO
LOM
B
ULA STOCK RTE
WEITZELS RD
GEARYS RD
RID
GE
RD
BARKERSRD
MAC
KIE
ST
MARNILANE
RA
CEC
OU
RS E
RD
H
UNTER
RD
CECILIA RD
KRUGERS
RD
LEICH HAR
DT
RD
GOWS RD
GLE
ESO
NS
RD
GORMLEYS
RD
DAW
SON
GAT
ES
RD
PEB
BLEW
OOD ST
MCGOVERNS
RD
ELER SLEALANE E
STEVENSONS RD
WALSHS RD
DAH
LKES
RD
SPINIFIX RD
TEM
P OR
ARI L
YC
LOSE
DR
D
VERONICA RD
BURNCLUITHRD
RO
YALT
Y R
D
AIN
SWO
R TH
ST
SMIT
HS
RD
CLOSED R
D
BOOTHS RD
RYALLS RD
STANKE RD
OLD
PER
TH R
D
LON
DO
NBR
IDG
E R
D
HO
BSO
NSRD
VAN
RE
NAN
S R
D
OAK ST
CHINCHILLA
TARA RD
GLASSON ST
STE
WAR
TS R
D
RIF
LER
ANG
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D
CHIN
CHILLA
WOND
AI RD
HO
LM
ES RD
LEICHHARDT
HWY
BUTT
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D
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WAITE
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RD
BELL
BIR
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D
A GRAHAMS RD
WEI
RR
D
AKE
RS
GU
LLY
RD
MCNULTY ST
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TOLMAH CT
NOTHURFTS RD
B TENNYSONS RD
GORRINES RD
CH
INCH
ILLA
SOU
THR
D
OLIV
ERSRD
RYALLS RD
BUTTS RD
LITHGO
WS
RD
BARTELSRD
ALKIRA LANE
HOPELANDSCHOOL RD
CONDAMINEKOGAN RD
MARY RD
REIDS RD
ELLERSLIE
LANDRD
OLD M A
N
LAGOO N
RD
WE
IR L
AN
E
ROXBOROU GH RD
BUTLERS RD
PRIC
E S
T
PHIPPSSUBDIVISION RD
CLOSED RD
BRYA
NTS
RD
CAM
PIO
NS
RD
RENNICKS RD
CLOSED RD
DAYBREAK RD
GOSPERS RD
CHILDS RD
BRENNANS RD
CLOSED RD
THAMES RD
MC
AULL
IFFE
S R
D
WILLI
AMS RD
WIN DM
ILL
RD
SIXTEEN MILE HALL RD
TREGATHLYN R
D
ZELLER ST
CLO
SED
RD
RYANS RD
DOUGA LLS RD
TOM
ALO
U LA
NE
MARY RD
GRAYS RD
WIN
FIEL
D RD
TERESE RD
STEINOHRTS RD
R WALLS RD
MACHANESS RD
ELE RSLEALANE
AUBURN RD
CHANCES
PLA
IN RD
FLETTS RD
MULLERS RD
ELER
SLE
A LA
NE
BILLABONG LANE
KYTES RD
KOOKABURRA DR
LLOYD ST
BURNT
BRIDG
E RD
EMU PDE
HORSWOODS RD
VANR
ENAN
S RD
CHARLES DR
FLETTSRD W
CLARKS RD
RAVENS R
D
VAN RENANS RD
SOUTH RD
DOHERTYS RD
MCLENNANS RD
WE
ST V
ALLE
Y R
D
PASCOES R D
PHIP
PS R
D
GLENOLIVE RD
DAHLERS RD
R K
ER
RS
RD
CLOSED RD
HONNERYS RD
DAV
IES
RD
HUBBARDSR
D
KOFOEDS RD O
HALLOR
ANSRD
KER
WIC
KS R
D
MALES R D
GAZZARDS RD
NOTHDU RF T
SRD
TAMES RD
QUIRES RD
ROBBOS RD
TREASURES RD
AERODROME RD
SOU
THG
LEN
NO
RTH
RD
TEMPORARILY CLOSED RD
HURSES RD
THE
WAL
LABY
TR
KC
HU
RC
H R
D
PHIP
PS R
D
LEICHHARDT
HWY
KRUGERSRD
THOMPSONS
RD
RACE COURSE RD
WAI
NSRD
KUMMEROWS RD
GREENSWAMP RD
BURNCLUITH SCHOOL RD
A GRAHAMS RD
WIL
SON
RD
GRAYS RD
WARREGOHWY
SHERIFFS RD
BARAKULA RD
DAV
IES
RD
SUNNYGLEN RD
FORTUNE
DR
CRYSTAL CREEK RD
BLACKB
UR
NS R
D
HUBBARDS RD
CLOSED RD
SUTT
ON
S R
D
LEES
RD
DR
ILDO
OL R
D
S HE
RW
OO
DR
D
ORCHARD RD
RED
HILLR
D
CAM E
BYRD
GO
RAN
BA
LAN
E
BRAITHWAITES RD
NO
EL
RO
BIN
SON
SR
D
VANRENANS RD
UNDULLACREEK RD
SOUTH RD
B TENNYSONS RD
B KERRS RD
JOSEPH RD
WED
RATS
RD
GOLDEN GLOW RD
ENGINE RD
MYRA RD
C KERRS RD
CHINCHILLASIXTEEN MILE RD
CLYN
ES RD
MALES DR
RYALLS TO HOOKSW OODSTOCK RTE
BIDGOODS RD
TIMOTHY RD
AVE
NU
E R
D
STA
INE
S R
D
FREEMAN
SR
D
LUCKY RD
LEBSA
NFTS R
D
BROWNLIES RD
MC
NU
LTY
RD
BAKERS RD
HOPELAND SCHOOL RD
MONTROSE RD
MILLERS RD
SCOULLERS RD
WEITZELSRD
MILLBANK RD
ISO
NS
RD
DONOGHUE RD
CAM
EBY
RD
BLAC KSWAMP RD
OLD CAMEBY RD
HOOKSWOOD PELHAM R D
CARTENS LANE
ARCHER
S CROSS
ING R
D
MCCASKERS RD
BOORT KOI TO
RYALLS STOCK R T E
GO
OM
BI F
AIR
YME
ADO
W R
D
HU
MBUG
RD
WARRENS
RD
GREENSWAMP RD
THE PEAK RD
FAIRYMEADOW RD
UPPER HUMBUG RD
WEIAMBILLA RD
WERANGA NORTH RD
TARA
KOGANRD
BENN
ETT
SCHO
OLRD
KOGAN
CONDAMINERD
KOGAN
CONDAMINE RD
CHIN
CH
IL L A
T AR
AR
D
WARREGOHWY
CHINCHILLA
MILES
BOTTLE
TREE
CR
EEK
UNDULLACREEK
ELEV
EN M
ILE
CR
EEK
UNDULLACREEK
COLUMBOOLA CREEK
CONDAMINE RIVER
TWEN
TY SIX MILE C
REEK
SIXTEEN MILE CREEK
COBB
AREE
NA C
REEK
WAMBO CREEK
HORSE GULLY
HUMBUG CREEK
ELEV
ENM
ILE
CR
EEK
COOLOOMALA CREEK
WIEAM
BILLA CR
EEK
CHARLEYS C
REEK
CAM
EBY
CR
EEK
UNDULLA CREEK
SAN
DY
CR
EEK
UN
DU
LLA
CR
EEK
ROCKY CREEK
BRANCH
CREEK
NINE MILE CREEK
BAKING BOARD CREEK
JACK
CREEK
DO
GW
OO
D C
REE
K
BOG
RA
MBI
LLA
CR
EEK
F
CD
I
E
GJ
"Based on or contains data provided by the State of Queensland (Department of Natural Resources and Mines) 2013. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws."
Note: Every effort has been made to ensure this information is spatially accurate. The location of this information should not be relied on as the exact field location.
Unforeseen Emergency Discharge Plan - Central
9/07/2013 LN M_28494_02DATA SOURCE:
Map Projection: GDA94 Zone 56
±0 2 4 6
Kilometers
ADATE: CREATED BY: REV NO:MAP NO:MAP TYPE: OtherDCDB, Watercourses, Fields, Springs- DNRM; Roads - StreetPro v3CLCHECKED BY:
1:200,000SCALE: at (A3)
_̂ UEDD Monitoring Locations
Threatened Ecological Communities
Box Gum Grassy Woodland
Brigalow
Grassland
SEVT
Weeping Myall Woodlands
Trunkline - Water
! Ponds
" Water Treatment Plant
Proposed UIC
QGC Owned Land
QCLNG EIS Area
Subcatchment Area
Major Watercourse
Minor Watercourse
Principal Road
Secondary Road
Label UEDD Monitoring Locations Easting NorthingC Nine Mile Creek – upstream QGC Kenya site boundary (tributary of Wieambilla Creek) 251743 7015878D Wieambilla Creek – upstream QGC Kenya site boundary 245393 7015923E Wieambilla Creek – downstream QGC Kenya site boundary 243916 7018865F Wieambilla Creek –downstream QGC Kenya site at the Kogan-Condamine Road crossing. 239703 7022777G Condamine River –upstream QGC Windibri site boundary 235081 7028002H Condamine River –downstream site – outside of managed irrigation reach at Glen Olive Road crossing 220305 7026170I Sandy Creek – upstream QGC Windibri site boundary 234947 7023476J Condamine River –downstream QGC Windibri site boundary 231740 7029169
296
Figure 16-5 – QCLNG Project UEDP Catchment – Northern Gas Fields
X
X
XXXX
"!
!
_̂
_̂
_̂
_̂
_̂
Woleebee Creek(Cells 1-3)NWTP Pond 1,2,3,4,5
D a w s o n R i v e rD a w s o n R i v e rC a t c h m e n tC a t c h m e n t
B a l o n n e R i v e rB a l o n n e R i v e rC a t c h m e n tC a t c h m e n t
Polaris Pond
Northern WTP
B a l o n n e R i v e rB a l o n n e R i v e rC a t c h m e n tC a t c h m e n t
Bull Gul ly
JACK
SON
WAN
DOAN
RD
LEICHH
ARDT
HW
Y
DALGOWAN
WILLIAMS RD
JOUNQUAYS RD
STIL
LER
ST
TIP
RD
ROSE RD
ROCHECREEK RD
OLD F ORRESTRD
DONNERS RD
NAR WONA
H
CROS SING
RD
IOLAN
THE R
D
DUNCANACCESS RD
CU
RR
ANS
LAN
E
STANLEYPARKRD
JAC
KS
ON SCHOOL
BU
S RTE
GALES RD
BOWLINGS RD
HO
PKIN
SRD
TIPRD
KEHLSRD
WIN
DE Y
ERRD
MAR
KW
ELL
S R
D
TRACK
BARNEYS
LANE
SOM
MERFIELD RD
EZZYSRD
NUMBER
ONE LANE
WOOLEEBEE RD
TRACK
MYRANGA RD
HUNTS RD
ELD
ERS
RD
NUMBERSIX RD
Q
RD
DALW
OG
A N
SOUTH
RD
WH
ATM
ANS
LAN
E
MILRAIN RD
BAKERS RD
BAKERS
RD
HAI
RS
RD
BRUGGEMANNS RD
SHEADYS RD
KOWGURAN RD
MAYES RD
KNIG
HTS
RD
V RD
GI LIGUL G ULRD
MCA
LLIS
TERS
RD
MARTIN
D ALE RD
M ONE RD
MYALL PARK TOHOOKSWOOD RD
JAM
ES
RD
ALDRIDGE RD
GREENS RD
MT
OR
GAN RD
WOOLEEBEE
RD
ARCHINALLS
RD
OFF
RE T
REAT RD
SAW PITLANE
C
ATTLEDOWNS RD
CROSSROADSRD
GLE
NLE
A R
D
M TW O RD
GILIGULGUL RD
ANNAMAROO RD
MYAL L
PARK RD
RETREAT RD
YAPUNYA RD
RACEC
OUR
SE
LANE
WELDONS RD
BIGVALLEY RD
UPP
ER D
OW
NFA
LLC
REE
K R
D
WILLETTS MILL RD
BOGAND
ILL A
RD
GURULMU
NDI R
D
BUNDI RD
TEMPORARILY
CLOSED RD
DIL
LON
S R
D
COMBABULA RD
JUA N
DA
HCREE
KR
D
CURR
AN
S
LANE
DRILLHAM
SCHOOLR
D
HOWARDSRD
WARRAMOO RD
CLARKE CREEK RD
CORMACKS RD
CO
RFI
ELD
S R
D
TUMBA DOWNS RD
NEL
DER
S R
D
OLD
INJUNE RD
GROSMONT RD
EWIN
GDALE R
D
DUNN
SR
D
CO
RM
ACKS
RD
BUNDI TWO RD
K RD
Q RD
LUCKY DOWNS RD
EYS RD
AQUA
PARK RD
GLE
ND O
ANRD
GLENBARWIG RD
HORNET BANK RD
WIL
LETT
SRD
DRAGONCRESTRD
DA
LGO
WAN
WI L
LIAM
SR
D
CATTLEDOWNS RD
GADSBYS RD
KABUNGAR
D
N ORTH DULACCAHALL RDFRIZZELLS RD
OFF
CR
OSS
RO
ADS
RD
HASLOPS RD
OLDCHINCHILLA RD
WHITELEYS RD
BA
ILEY SR
D
DU
LAC
CA
NO
RTH
RD
HICKS RD
L RD
GREENS RD
COCKATOO RD
CORBETTS BACK RD
HANSENS RD
NUMBERSEVEN RD
OFF LAWTON
ROBINSON
RD
HENRYS RD
SANDS RD
BOGANDILLA RD
PONTY
POOL RD
DEEARNE RD
NUMBER ONEOF
F
J ACKSON WANDOAN
RD
KTW
OR
D
DOWNFALL
CREEK RD
BUNGILDOON RD
RED RANGE RD
CHAPMANS RD
DEVONCOURT RD
TRASKS LANE
CECILS RD
BOGANDILLAWEST RD
NUMBERTWO RD
MYA
L LP A
RK
RD
DALWOGAN RD
MANTOVASRD
GLENAUBYN RD
CROSSROADS RD
BUNDI RD
HE R
MIT
A GE
RD
GULLAGIMBI RD
NUM
BER
FIVE
RD
LAWTON ROBINSON RD
WILDFLOWER RD
DULACCA
NORTH
RD
PARAD
I SE
DO
WN
SR
D
MUNDALYA RD
CROSSROADS RD
FOSTERS RD
KINFAUNS RDBR
ADSHAW
SRD
RYALS RD
MT MYRTLE RD
NUMBERFOUR RD
BUR
RA
DO
OR
D
MURRAYS RD
OLD CHINC HILLA RD
COAT
ES
RD
BURUNGA LANE
WALSHS RD
PEAK
ES R
D
WAL
LAN
CR
EEK RD
UPPERDOWNFALL RD
WELSHS RD
TARANA
CROSSI NG
RD
HOMEBUSH RD
ZILL
MANS RD
CRACOW RD
MAIDENS
RD
SUNDOWN RD
YEOVIL RD
STILLER
BROS RD
SMITHS RD
GURULMUNDI RD
GOLDENS RD
MIDDLE CREEK RD
BOORAL RD
PERRETTSRD
LTR
EE
CREEK
RD
BUN GABAN RD
TWELVEMILE RD
POTTERS
FLAT RD
INJUNE RD
ROMATAROOM RD
NATHAN RDJA
C
KSON
WA
ND
OA
N
RD
LEICHHARDT
HWY
WANDOAN
TAROOM
CO
CK
ATO
OC
REE
K
JUANDAH
CREEK
TCHANNING C
REEK
WOLE
EBEE
CREEK
WOLE
EBEE
CREEK
HORSE GULLY
BENTLEY
CR
EEK
TCH
ANN
ING
CR
EEK
BOTTLE TREE CREEK
CO
CK
ATOO
CR
EEK
TCHANNING
CREEK
WO
LEEB
EE C
REEK
WO
LEEB
EECR
EEK
KENNEDYCREEK
PIGEONCREEK
JUANDAH
CREEK
BULLOCK CREEK
JUANDAH CREEK
CONLOI CREEK
JUAN
DAH
GU
LLY
(MAI
NBR
ANC
H)
JUANDAH CREEK
DAWSON RIVER
KINNOUL CREEK
PINE
CREEK
EURO
MBA
H CR
EEK
KUNGAY MUNGAY CREEK
JUAN
DAH
CR
EEK
SAWPITCREEK
BYRNE CREEK
NINEMILECREEK
DOWNFALL CREEK
NINEMILECREEK
L TREE CREEK
MAY
NE C
REEK
NINEMILECREEK
DAWSON RIVER
HO
RS
E C
REE
K(M
AIN
BR
ANC
H)
DO
GW
OO
DC
REE
K
SAN
DY
CR
EEK
ROCHE CREEK
BRIDGE CREEKWERINGA CREEK
ROCHE CREEK
ELEVEN MILE CREEK
CAMISLA CREEK
SCOTT CREEK
SCOTCHY CREEK
SWAM
P CR
EEK
LONG GULLY
COMBABULA CREEK
JUANDAH GULLY
CANAL CREEK
BLACKBOY CREEK
BUNGABAN CREEK
BULL
OC
K G
ULL
Y
DAWSON RIVER
FOU
R M
ILE CR
EEK
STAKEYAR
D
CR
EEK
TWEN
TY MILE C
REE
K
CLARK CREEK
NO
ON
GA C
REEK
RAMYARD CREEK
PADD
YS C
REEK
CO
MBI
DIB
AN C
REE
K
WALLAN CREEK
BACK CREEK
HORSE CREEK
(EASTBRANCH)
PON
TYPOO
L CR
EEK
MUD CREEK
WANDOAN CREEK
HORSE CREEK
K
L
M
N
O
"Based on or contains data provided by the State of Queensland (Department of Natural Resources and Mines) 2013. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws."
Note: Every effort has been made to ensure this information is spatially accurate. The location of this information should not be relied on as the exact field location.
Unforeseen Emergency Discharge Plan - North
8/07/2013 LN M_28494_01DATA SOURCE:
Map Projection: GDA94
±0 2 4 6 8 10
Kilometers
ADATE: CREATED BY: REV NO:MAP NO:MAP TYPE: OtherDCDB, Watercourses, Fields, Springs- DNRM; Roads - StreetPro v3CLCHECKED BY:
1:300,000SCALE: at (A3)
_̂ UEDD Monitoring Locations
Threatened Ecological Communities
Box Gum Grassy Woodland
Brigalow
Grassland
SEVT
Weeping Myall Woodlands
Trunkline - Water
! Ponds
" Water Treatment Plant
Proposed UIC
QGC Owned Land
QCLNG EIS Area
Subcatchment Area
Major Watercourse
Minor Watercourse
Principal Road
Secondary Road
Label UEDD Monitoring Locations Easting Northing
K Wandoan Creek – un-named tributary downstream north-east of QGC Delga Park site at Bakers Road Crossing (adjacent QGC LaPilli property 773046 7093793
L Wandoan Creek – downstream north of QGC Delga Park site at Sundown Road Crossing (adjacent QGC LaPilli property) 771624 7096884
M Wandoan Creek – downstream site at Bundi Road Crossing 783916 7104970N Junda Creek – downstream of Woleebee Creek confluence at Booral Road Crossing 789104 7117403O Junda Creek – upstream of Dawson River Confluence at Leichardt Hwy Crossing 780337 7160753
X
X
XXXX
"!
!
_̂
_̂
_̂
_̂
_̂
Woleebee Creek(Cells 1-3)NWTP Pond 1,2,3,4,5
D a w s o n R i v e rD a w s o n R i v e rC a t c h m e n tC a t c h m e n t
B a l o n n e R i v e rB a l o n n e R i v e rC a t c h m e n tC a t c h m e n t
Polaris Pond
Northern WTP
B a l o n n e R i v e rB a l o n n e R i v e rC a t c h m e n tC a t c h m e n t
Bull Gul ly
JACK
SO
N
WAN
DOAN
RD
LEICHHARDT
HWY
DALGOWAN
WILLIAMS RD
JOUNQUAYS RD
STIL
LER
ST
TIP
RD
ROSE RD
ROCHECREEK RD
OLD F ORRESTRD
DONNERS RD
NAR WONA
H
CROS SING
RD
IOLAN
THE R
D
DUNCANACCESS RD
CU
RR
ANS
LAN
E
STANLEYPARKRD
JAC
KS
ON SCHOOL
BU
S RTE
GALES RD
BOWLINGS RD
HO
PKIN
SRD
TIPRD
KEHLSRD
WIN
DE Y
ERRD
MAR
KW
ELL
S R
D
TRACK
BARNEYS
LANE
SOM
MERFIELD RD
EZZYSRD
NUMBER
ONE LANE
WOOLEEBEE RD
TRACK
MYRANGA RD
HUNTS RD
ELD
ERS
RD
NUMBERSIX RD
Q
RD
DALW
OG
A N
SOUTH
RD
WH
ATM
ANS
LAN
E
MILRAIN RD
BAKERS RD
BAKERS
RD
HAI
RS
RD
BRUGGEMANNS RD
SHEADYS RD
KOWGURAN RD
MAYES RD
KNIG
HTS
RD
V RD
GI LIGUL G ULRD
MCA
LLIS
TERS
RD
MARTIND ALE RD
M ONE RD
MYALL PARK TOHOOKSWOOD RD
JAM
ES
RD
ALDRIDGE RD
GREENS RD
MT
OR
GAN RD
WOOLEEBEE
RD
ARCHINALLS
RD
OFF
RE T
REAT RD
SAW PITLANE
C
ATTLEDOWNS RD
CROSSROADSRD
GLE
NLE
A R
D
M TW O RD
GILIGULGUL RD
ANNAMAROO RD
MYAL L
PARK RD
RETREAT RD
YAPUNYA RD
RACEC
OUR
SE
LANE
WELDONS RD
BIGVALLEY RD
UPP
ER D
OW
NFA
LLC
REE
K R
D
WILLETTS MILL RD
BOGAND
ILL A
RD
GURULMU
NDI R
D
BUNDI RD
TEMPORARILY
CLOSED RD
DIL
LON
S R
D
COMBABULA RD
JUA N
DA
HCREE
KR
D
CURR
AN
S
LANE
DRILLHAM
SCHOOLR
D
HOWARDSRD
WARRAMOO RD
CLARKE CREEK RD
CORMACKS RD
CO
RFI
ELD
S R
D
TUMBA DOWNS RD
NEL
DER
S R
DOLD
INJUNE RD
GROSMONT RD
EWIN
GDALE R
D
DUNN
SR
D
CORM
ACKS
RD
BUNDI TWO RD
K RD
Q RD
LUCKY DOWNS RD
EYS RD
AQUA
PARK RD
GLE
ND O
ANRD
GLENBARWIG RD
HORNET BANK RD
WIL
LETT
SRD
DRAGONCRESTRD
DA
LGO
WAN
WI L
LIAM
SR
D
CATTLEDOWNS RD
GADSBYS RD
KABUNGAR
D
N ORTH DULACCAHALL RDFRIZZELLS RD
OFF
CR
OSS
RO
ADS
RD
HASLOPS RD
OLDCHINCHILLA RD
WHITELEYS RD
BA
ILEY SR
D
DU
LAC
CA
NO
RTH
RD
HICKS RD
L RD
GREENS RD
COCKATOO RD
CORBETTS BACK RD
HANSENS RD
NUMBERSEVEN RD
OFF LAWTON
ROBINSON
RD
HENRYS RD
SANDS RD
BOGANDILLA RD
PONTY
POOL RD
DEEARNE RD
NUMBER ONEOF
F
J ACKSON WANDOAN
RD
KTW
OR
D
DOWNFALL
CREEK RD
BUNGILDOON RD
RED RANGE RD
CHAPMANS RD
DEVONCOURT RD
TRASKS LANE
CECILS RD
BOGANDILLAWEST RD
NUMBERTWO RD
MYA
L LP A
RK
RD
DALWOGAN RD
MANTOVASRD
GLENAUBYN RD
CROSSROADS RD
BUNDI RD
HE R
MIT
A GE
RD
GULLAGIMBI RD
NUM
BER
FIVE
RD
LAWTON ROBINSON RD
WILDFLOWER RD
DULACCA
NORTH
RD
PARAD
I SE
DO
WN
SR
D
MUNDALYA RD
CROSSROADS RD
FOSTERS RD
KINFAUNS RD
BRAD
SHAWS
RD
RYALS RD
MT MYRTLE RD
NUMBERFOUR RD
BUR
RA
DO
OR
D
MURRAYS RD
OLD CHINC HILLA RD
COAT
ES
RD
BURUNGA LANE
WALSHS RD
PEAK
ES R
D
WAL
LAN
CR
EEK RD
UPPERDOWNFALL RD
WELSHS RD
TARANA
CROSSI NG
RD
HOMEBUSH RD
ZILL
MANS RD
CRACOW RD
MAIDENSRD
SUNDOWN RD
YEOVIL RD
STILLER
BROS RD
SMITHS RD
GURULMUNDI RD
GOLDENS RD
MIDDLE CREEK RD
BOORAL RD
PERRETTSRD
LTR
EE
CREEK
RD
BUN GABAN RD
TWELVEMILE RD
POTTERS
FLAT RD
INJUNE RD
ROMATAROOM RD
NATHAN RD
JAC
KSON
WA
ND
OA
N
RD
LEICHHARDT
HWY
WANDOAN
TAROOM
CO
CK
ATO
OC
REE
K
JUANDAH
CREEK
TCHANNING C
REEK
WOLEEBEE
CREEK
WOLE
EBEE
CREEK
HORSE GULLY
BENTLEY
CR
EEK
TCH
ANN
ING
CR
EEK
BOTTLE TREE CREEK
COCKATOO
CREEK
TCHANNING
CREEK
WO
LEEB
EE C
REEK
WOLE
EBEE
CREE
K
KENNEDYCREEK
PIGEONCREEK
JUANDAH
CREEK
BULLOCK CREEK
JUANDAH CREEK
CONLOI CREEK
JUAN
DAH
GU
LLY
(MAI
NBR
ANC
H)
JUANDAH CREEK
DAWSON RIVER
KINNOUL CREEK
PINE
CREEK
EURO
MBA
H CR
EEK
KUNGAY MUNGAY CREEK
JUAN
DAH
CR
EEK
SAWPITCREEK
BYRNE CREEK
NINEMILECREEK
DOWNFALL CREEK
NINEMILECREEK
L TREE CREEK
MAY
NE C
REEK
NINEMILECREEK
DAWSON RIVER
HO
RS
E C
REE
K(M
AIN
BR
ANC
H)
DOG
WO
OD
CREE
K
SAN
DY
CR
EEK
ROCHE CREEK
BRIDGE CREEK
WERINGA CREEK
ROCHE CREEK
ELEVEN MILE CREEK
CAMISLA CREEK
SCOTT CREEK
SCOTCHY CREEK
SWAM
P CR
EEK
LONG GULLY
COMBABULA CREEK
JUANDAH GULLY
CANAL CREEK
BLACKBOY CREEK
BUNGABAN CREEK
BULL
OC
K G
ULL
Y
DAWSON RIVER
FOU
R M
ILE CR
EEK
STAKEYARD
CREEK
TWEN
TY MILE C
REE
K
CLARK CREEK
NO
ON
GA C
REEK
RAMYARD CREEK
PADDYS CREEK
CO
MBI
DIB
AN C
REE
K
WALLAN CREEK
BACK CREEK
HORSE CREEK
(EASTBRANCH)
PON
TYPOO
L CR
EEK
MUD CREEK
WANDOAN CREEK
HORSE CREEK
K
L
M
N
O
"Based on or contains data provided by the State of Queensland (Department of Natural Resources and Mines) 2013. In consideration of the State permitting use of this data you acknowledge and agree that the State gives no warranty in relation to the data (including accuracy, reliability, completeness, currency or suitability) and accepts no liability (including without limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used in breach of the privacy laws."
Note: Every effort has been made to ensure this information is spatially accurate. The location of this information should not be relied on as the exact field location.
Unforeseen Emergency Discharge Plan - North
8/07/2013 LN M_28494_01DATA SOURCE:
Map Projection: GDA94
±0 2 4 6 8 10
Kilometers
ADATE: CREATED BY: REV NO:MAP NO:MAP TYPE: OtherDCDB, Watercourses, Fields, Springs- DNRM; Roads - StreetPro v3CLCHECKED BY:
1:300,000SCALE: at (A3)
_̂ UEDD Monitoring Locations
Threatened Ecological Communities
Box Gum Grassy Woodland
Brigalow
Grassland
SEVT
Weeping Myall Woodlands
Trunkline - Water
! Ponds
" Water Treatment Plant
Proposed UIC
QGC Owned Land
QCLNG EIS Area
Subcatchment Area
Major Watercourse
Minor Watercourse
Principal Road
Secondary Road
Label UEDD Monitoring Locations Easting Northing
K Wandoan Creek – un-named tributary downstream north-east of QGC Delga Park site at Bakers Road Crossing (adjacent QGC LaPilli property 773046 7093793
L Wandoan Creek – downstream north of QGC Delga Park site at Sundown Road Crossing (adjacent QGC LaPilli property) 771624 7096884
M Wandoan Creek – downstream site at Bundi Road Crossing 783916 7104970N Junda Creek – downstream of Woleebee Creek confluence at Booral Road Crossing 789104 7117403O Junda Creek – upstream of Dawson River Confluence at Leichardt Hwy Crossing 780337 7160753
QCLNG Project UEDP Catchment – Northern Gas Fields
Kilometres
0 2 4 6 8 10
297
Immediate response
• All immediate response actions as per procedure in Section 16.5.1 ;
• Review the relevant IPOP for relevant contact details for external notifications to people deemed to be
potentially impacted including;
• Sensitive Receptors – Landowners, or Persons At Risk (PAR);
• Surface Water Allocations;
• Groundwater Allocations; and
• External Emergency Contacts
Control and minimise
• Review the IPOP and implement the specific emergency management procedures. Standard emergency
action considerations are identified in Table 16-5.
Item Emergency Action Considerations
1
• Potential human injuries and environmental harm should be managed through an On-Scene Coordinator. The
On-Scene Coordinator will assist the General Manager in notifying the population at risk from the emergency
and, if required, assisting with evacuation of those people
• The potential risk of, or further, human injuries should be managed by removing any nonessential staff from
the area of the incident
2
• Risks associated with the incident should be managed by barricading off or delineating danger areas (if safe to
do so) the affected area and restricting access
• In assessing the extent of a potential uncontrolled release, no attempt should be made to traverse across or
immediately downstream of the affected area
• In the case of an imminent release, the potential release area should be barricaded (if safe to do so). Temporary
barricading options will be dependent on availability and mobilisation times (and could include temporary
earth bunds or sand bags).
3
• Water delivery pumps should be switched off
• In the event of an imminent release, excess water should be pumped or decanted from the pond if practical
and safe to do so
4
• Prevention of imminent or additional release should be managed in consultation with the Engineering Design
Officer (EDO) responsible for the certification of the Pond.
• A QGC-approved earthmoving contractor should be mobilised to site promptly and, if required, the EDO
responsible for the certification of the pond should also be mobilised to site to direct stabilisation works where
practicable to do so.
5
• In the unlikely event that the uncontrolled release has not been contained, the Queensland State Emergency
Services (SES) should be contacted. However this should not be taken as a transfer of responsibility from
the On-Scene Coordinator and support personnel. All pond specific emergency procedures should still be
implemented.
6• If there is an uncontained flow which may impact infrastructure, the relevant local council and appropriate
service providers should be contacted
7• Remediation works should be undertaken in consultation with the QGC Site Construction Manager, or Field
Operation Manager or Asset Owner, Lead Pond Engineer and RPEDA
Table 16-5 – QCLNG pond emergency actions and considerations
298
Notification
As per the procedure in Section 16.5.1.
Remediation and Monitoring
As per the procedure in Section 16.5.1 and where required as per Section 16.6.4.
16.6.2 UNCONTAINED DISCHARGE OF CSG WATER, BRINE OR CHEMICALS FROM WATER TREATMENT
FACILITIES
During operation and maintenance of QGC's Water Treatment Plans, significant or long-term environmental impact
through uncontained discharges or spills are not expected nor considered likely. This is primarily due to the plant
design, layout and operational controls in place. However, as the corresponding potential consequences of an
uncontained discharge or spoll is categorised as a primary risk scenario, specific UEDP measures have been identified
below for QGC's water treatment plant hubs.
Table 16-6 provides a summary of typical mechanisms to avoid, minimise and manage risks of uncontained
emergency discharge from water treatment plant hubs. This table should be read in conjunction with the water
management criteria and controls identified in Section 16.3 and Table 16-4 for the purposed of risk associated with
regulated storages located adjacent the Water Treatment Plants.
Where initial surface water sampling downstream at the nearest property boundary indicates elevated levels in
concentrations that have the potential to cause significant environmental harm then additional UEDP monitoring
should be actioned. Potential surface water monitoring locations should be sourced from the Table 16.7 Unforeseen
Emergency Discharge Monitoring Locations – Water Treatment Plant Hubs (also identified on the Figure 16.4 and 16.5)
and monitoring of nearby water monitoring bores should be carried out where there is likelihood of significant or
long-term groundwater impacts from infiltration.
Notification
As per the procedure in Section 16.5.1.
Remediation and Monitoring
As per the procedure in Section 18.5.1 and where required Section 13.6.4.
299
Design, monitoring and maintenance Control measures Manage if releases occur
• Treated water quality is to be
regularly monitored to determine
compliance with the adopted
criteria for authorised release and
beneficial reuse
• The WTPs are bunded where
practical to capture any CSG water
or chemical spills including sludge,
fuel, oil and chemical storage areas
• Daily and weekly inspections
indicates infrastructure integrity
• Completion of routine
environmental checklists
• Rapid close-out of incidents and
non-conformances
• All personnel to attend a site
induction which contains relevant
environmental requirements
• Additional and ongoing
environmental training as required
• Constant supervision on site
• Environmental audits of work sites,
sub-contractors and compliance
issues
• Planned and unplanned
maintenance regime indicates
infrastructure integrity
• Regular environmental alerts and
toolboxes
• Maintenance of adequate capacity
and redundancy in the water
infrastructure to provide a buffer
in case of WTP malfunction and/or
emergency incident
• Water quality controls will include
some or all of the following as
required:
• Detention storage sufficient
to manage stormwater
quantity and a combination
of an sediment separator and
stormwater rock swales to
manage stormwater quality
• Stormwater quality
improvement devices (SQID)
including gross pollutant
traps to reduces the impact of
contaminated water entering
the first flush pond
• A procedure specific to
emptying the first flush pond
• Testing of water quality in
chemical service pits prior to
removal
• Minimising disturbance and
bare areas, and where this is
unavoidable, use of sediment
control devices. During the
operation of the plant, the
scheduling of heavy vehicle
movements will (where
possible) occur during daytime
hours (7 am to 6 pm) including
chemical deliveries
• Mitigation and monitoring
procedure implemented
• Agency and landholder notifications
• Remediation, monitoring and
reporting
• Management Controls for the plant
during emergency event include:
• System modification to reduce
or divert inflows and investigate
integrity/quality concerns,
corrective actions taken where
required
• Isolate or change source water
• System modification to
recirculate outflows back to
storage ponds during remedial
works and testing
• Manage production (including
reduction of in-flows) to be
instigated during remedial
works
Table 16-6 – Mechanisms to avoid, minimise and manage the risks of emergency discharge from water treatment plants
300
Water Treatment
Plant HubsAssociated Storages Surface Water Monitoring Locations
Approximate
Coordinates
(DATUM: WGS84)
Kenya Central
Water Treatment
Plant (CWTP)
• Orana Pond 1
• Orana 2, 3 and 4 RO Reject
and Brine Ponds
• Rhynie Pond
• Kenya Pond
• WTP Sedimentation Pond
• Kenya Treated Water Pond
Nine Mile Creek – upstream QGC Kenya site
boundary (tributary of Wieambilla Creek)
0251743 easting
7015878 northing
Wieambilla Creek – upstream QGC Kenya site
boundary
0245393 easting
7015923 northing
Wieambilla Creek – downstream QGC Kenya site
boundary
0243916 easting
7018865 northing
Wieambilla Creek – downstream QGC Kenya site at
the Kogan-Condamine Road crossing.
0239703 easting
7022777 northing
Condamine River – upstream QGC Windibri site
boundary
0235081 easting
7028002 northing
Condamine River – downstream site – outside
of managed irrigation reach at Glen Olive Road
crossing
0220305 easting
7026170 northing
Windibri Water
Treatment Plant
(WWTP)
Berwyndale South Pond 4 Sandy Creek – upstream QGC Windibri site boundary 0234947 easting
7023476 northing
Condamine River – upstream QGC Windibri site
boundary
0235081 easting
7028002 northing
Condamine River – downstream QGC Windibri site
boundary
0231740 easting
7029169 northing
Condamine River – downstream site – outside
of managed irrigation reach at Glen Olive Road
crossing
0220305 easting
7026170 northing
Woleebee Creek
Northern WTP
(NWTP)
Woleebee Creek Cells 1-3
Northern NTP Pond
NWTP Pond 2 Treated Water,
NWTP Ponds 3, 4 and 5
Sedimentation, RO Reject, Brine
and Clean In Place (CIP) waste
Wandoan Creek – unnamed tributary downstream
north-east of QGC Delga Park site at Bakers Road
Crossing (adjacent QGC LaPilli property)
773046 easting
7093793 northing
Wandoan Creek – downstream north of QGC Delga
Park site at Sundown Road Crossing (adjacent QGC
LaPilli property)
771624 easting
7096884 northing
Wandoan Creek – downstream site at Bundi Road
Crossing
783916 easting
7104970 northing
Juandah Creek – downstream of Woleebee Creek
confluence at Booral Road Crossing
789104 easting
7117403 northing
Juandah Creek* – upstream of Dawson River
Confluence at Leichardt Hwy Crossing
780337 easting
7160753 northing
Notes:• The Water Treatment Plant Hub's proposed monitoring sites are to be used as a guide to UEDP sampling. These sites should only be used where safe access is
possible and where relevant to the specific UED event.• Upstream reference sites for the Northern WTP hub should be located where possible on the QGC Delga Park site using upstream drainage locations where water
is present or flowing during the event. • * Upstream Dawson River 8 Springs monitoring location for Dawson River 8 Springs. This site should only be triggered where event-related quality impacts are
detected beyond other upstream monitoring locations identified.
Table 16-7 – Unforeseen emergency discharge monitoring locations – water treatment plant hubs
301
16.6.3 SERIOUS RUPTURE OR DAMAGE TO CSG WATER AND BRINE TRUNKLINES
QGC's regionalised water treatment plants and water management system are underpinned by a network of
trunklines primary for the transport and untreated CSG water. In the future; in accordance with the development
of QGC’s brine management strategy (see Chapter 15) this network of trunklines may require to be expanded to
also include the transport of brine between treatment facilities to end use destinations. This section has been
developed based on the design information and management strategies already employed for water trunklines
and equally cover the potential for transport of brine and concentrates.
Review of any future design and development details of potential brine and CSG brine and concentrate trunklines
will be made if require to amend and update relevant portions of the avoidance, mitigation and minimisation
principles and actions procedures outlined below. Table 16.8 provides a summary of typical mechanisms to avoid,
minimise and manage risks of serious rupture or damage to CSG water and brine trunklines. The table identifies
that one of the key primary methods for avoidance of such events is though robust design and installation of
the lines. This table should be read in conjunction with the water management criteria and controls identified in
Section 16.3.
Design, Monitoring and Maintenance Control Measures Manage if Releases Occur
• Design elements of water trunklines
include:
• Concrete lined carbon steel
• Minimum 20 year design life
from first LNG production
• Nominally sized to limit the
maximum flow velocity to
between 2 to 3 m/s as an initial
estimate
• Flowmeters at each end to
detect leaks
• Pressure indication at the inlet
• Back pressure control valve may
be installed at the end of the
trunkline if elevation changes
may result in significant
negative static pressure being
experienced
• Surge protection to prevent
damage of the pipeline due to
water hammer
• Combination air/vacuum vents
installed at all high points for
removal of gas and to prevent
boiling of liquids due to vacuum
formation
• Pipelines are pressure tested to
ensure there are no leaks prior to
commissioning
• Surveillance monitoring of
vegetation health surrounding
facilities and along the ROW
• Routine Infrastructure integrity
inspections
• Online flow telemetry and control
mechanisms to allow:
• Leakage rates to be inferred by
flow metering trends and/or
variance between inflow and
outflow meters
• Control mechanisms to diver or
isolate flows
• Installation and maintenance of
marker posts along the ROW
• Obtaining accurate as built data
to support internal GIS systems
and Dial Before YOU DIG (National
Referral Service for Information on
Underground Pipes and Cables)
• Pipeline Integrity Management Unit
(PIMS).
• Mitigation and monitoring
procedure implemented
• Agency and landholder notifications
• System modification to divert
or isolate flows and investigate
integrity/quality concerns, corrective
actions taken where required
• Remediation, monitoring and
reporting
Table 16-8 – Mechanisms to avoid, minimise and manage the risks of serious rupture or damage to CSG water and brine trunklines
302
Any failure, rupture or breach of a CSG water or brine trunkline or collection header has the potential to release
contaminant that may cause environmental harm depending on the extent of the release and its location.
The potential volume of liquid released will be determined by:
• The pipe diameter;
• Volume of water contained in the pipe;
• Distance of the particular piece of pipe to isolation valves;
• Height of the failure point relative to the rest of the pipeline;
• Flow rates; and
• The time it takes to isolate the line.
Assessment and monitoring (as per the procedures in Section 16.5)
• Section 16.5.1 for CSG water, or, Section 16.5.3 for brines and concentrates;
• Where initial surface water sampling downstream at the nearest property boundary indicates elevated levels
of the listed parameters in concentrations that have the potential to cause significant environmental harm
then additional UEDP monitoring should be actioned;
• All of the major QCLNG water trunklines (existing and proposed near term) are identified in Figures 16.3, 16.4
and 16.5, current at the date of publication of the plan:
• Where any failure scenario is located in close proximity to a regional Water Treatment Plant Hub, potential
surface water monitoring locations should be sourced from the Table 16.7 Unforeseen Emergency
Discharge Monitoring Locations – Water Treatment Plant Hubs. These specific monitoring locations are
also identified on the corresponding catchment area Figures 16.4 and 16.5);
• Where any failure scenario is located outside the identified regional Water Treatment Plant Hubs, then
suitable upstream and downstream surface water monitoring locations should be determined by the
on-site FEO or relevant environmental coordinator with guidance from the Figures 16.3, 16.4 and 16.5
indicating surface water catchments for the respective development region; and
• Conduct monitoring of nearby water monitoring bores if required where there is likelihood of significant or
long term groundwater impacts from infiltration.
Notification
As per the procedure in Section 16.5.1.
Remediation and Monitoring
As per the procedure in Section 18.5.1 and where required as per Section 16.6.4.
16.7 UEDP REMEDIATION AND MONITORING
The type scale and extent of remediation works required to manage an unforeseen emergency discharge will
be developed specific to the particular situation, event location including the extent of the environmental harm
caused and with consultation and engagement with impacted stakeholders.
Where initial review of remedial works and assessment of monitoring as per Section 18.5.1 indicates ongoing risk
of an adverse or significant effect on the receiving environment or stakeholders, QGC will develop a Site Specific
Remediation Plan (SSRP).
The SSRP will be developed using input from the relevant engineering, environmental and technical disciplines
and be structured to be consistent with the principles and objectives of the QGC Remediation, Rehabilitation,
Recovery and Monitoring Plan (RRRMP) QCLNG-BX00-ENV-PLN-000026 as approved by The Department in
accordance with gas field Conditions 15 to 17.
303
The SSRP will include but not be limited to:
• An assessment of initial remedial works conducted
• Potential and actual effects on the receiving environment and the need for further investigation and
assessment;
• An assessment of potential and actual effects on environmental values and MNES and/or surface and
groundwater users; and
• Details of proposed remedial and rehabilitation actions to be taken including:
• areas to be rehabilitated;
• land uses of each area to be rehabilitated prior to disturbance;
• vegetation communities present, including a map of suitable scale displaying the distribution of
vegetation communities including impacted areas;
• proposed revegetation methods;
• timeframes for rehabilitation; and
• ongoing monitoring and reporting .
An initial SSRP (where required) will be developed within a further 10 business days post the provision of an
incident report (see Section 16.5.1) where practicable. On completion of the remediation and rehabilitation
activities identified in the SSRP a summary report will be prepared covering the following items:
• A final assessment of the actual or potential environmental harm that has occurred or may occur in the
longer term as a result of the release;
• The success or otherwise of actions taken at the time of the incident to prevent or minimise environmental
harm;
• The successes of remediation and rehabilitation activities carried out under the plan; and
• Any outstanding or ongoing issues and/or concerns.
The initial SSRPs and Summary Reports will be made available to The Department and the Queensland Regulator
as part of the engagement phase and during the ongoing remediation and monitoring process.
16.8 EMERGENCY SCENARIO SIMULATION
16.8.1 INTRODUCTION
The basis of design and operating philosophy of the water management infrastructure is to manage produced
water without the need to overflow or make an emergency discharge. To demonstrate the robustness of the
system, an extreme emergency scenario has been simulated. This simulation takes the format of an artificial
series of events affecting the Central and Northern WTP facilities. The scenario is set outside the normal
operating parameters of the system.
16.8.2 SCENARIO ASSUMPTIONS
Figure 16-6 illustrates the key infrastructure elements in the system. The simulation assumes:
• The scenario runs from the onset of major depressurisation in the Southern and Central Gas Fields in
December 2013;
• The key section begins in December 2014 when water treatment capacity is at a peak of up to 112 ML/d for
Central and Southern and 100 ML/d for Northern;
• Throughout 2013, the Central plant undergoes routine planned maintenance and upgrade shutdowns;
• All inflows from the Central and Southern regional ponds report to the raw water ponds system, Orana 1
or Orana 5;
304
Figure 16-6 – Central and Southern Gas Fields collection and storage networks
Pump
Existing ponds
Under construction or to be built
Development blocks
MCNULTY200 ML
MCNULTY
AVON DOWNS
CHINCHILLA WEIR
SUNW
ATER
KENYA WTP 112 ML/d
INDUSTRIAL REUSE
MINING SECTORREUSE
WINDIBRI WTP
6 ML/d
BELLEVUE
LAUREN104 ML
BERWYNDALE
BERWYN S / WINDIBRI
MATILDA – JOHN
LAUREN
ARGYLE
KENYA
CODIE
ORANA 15,158 ML
KENYA TREATED WATER
170 ML
KATE
ORANA 52,130 ML
KENYA EAST
JAMMAT / OWEN
MARGARET
KENYA EAST597 ML
KENYA 2,001 ML
RHYNIE3,719 ML
DAVID
SEAN
DAVID334 ML
CELESTE310 ML
JORDAN
WILL / RIDGEWOOD S
MICHELLE
WILL / RIDGEWOOD N
CELESTE
MYRTLE
TEVIOT
ABERDEEN
MARIE RAE
MYRTLE150 ML
RUBY-JO760 ML
JEN
ISABELLA
RUBY-JO
POPPY
BARNEY
CLUNIE
COUGALS
BROADWATER
HARRY
GLENDOWER
BROADWATER370 ML
GLENDOWER481 ML
POND 44,370 ML
RO R
EJEC
T
ORANA 4752 ML
ORANA 31,040 ML
ORANA 21,280 ML
RWF
BRINE CONCENTRATOR
CONC
ENTR
ATED
BRI
NE
FRO
M N
ORT
HER
N W
TP
GLEN EDEN115 ML
305
• From December 2014, additional inflows of 754 ML are added to the production profile, due to precipitation
falling directly onto pond surfaces. The ponds do not have any upstream catchments so there are no overland
flow inputs; and
• A plant breakdown has caused a stop in the treatment process or the offtake pipeline is unable to discharge
the treated water.
The objective of the analysis is to answer two key questions:
• If the treatment plant is not operating how long can CSG water abstraction continue before the raw water
ponds reach maximum operating level?
• When the raw water ponds are full, how long can the regional ponds hold water below Maximum Operating
Level (MOL) before CSG water abstraction has to be curtailed?
16.8.3 SIMULATION RESULTS
The results for Central and Southern are displayed in Figure 16-7.
Figure 16-7 – Emergency Event: Simulation results
1,000Volu
me
Stor
age
Cap
acit
y (M
L) /
Vol
um
e in
Sto
rage
(ML)
01/
11/2
013
01/
12/2
013
01/
01/
2014
01/
02/2
014
01/
03/
2014
01/
04/
2014
01/
05/
2014
01/
06
/20
14
01/
07/
2014
01/
08/
2014
01/
09
/20
14
01/
10/2
014
01/
11/2
014
01/
12/2
014
01/
01/
2015
01/
02/2
015
01/
03/
2015
01/
04/
2015
01/
05/
2015
01/
06
/20
15
01/
07/
2015
01/
08/
2015
01/
09
/20
15
01/
10/2
015
01/
11/2
015
01/
12/2
015
01/
01/
2016
01/
02/2
016
01/
03/
2016
01/
04/
2016
01/
05/
2016
01/
06
/20
16
01/
07/
2016
01/
08/
2016
01/
09
/20
16
01/
10/2
016
2,000
3,000
4,000
5,000
6,000
7,000
8,000
9,000
10,000
11,000
12,000
13,000
Updated 13 November 2013
WTPs and Pond 4 transferWithdrawal rate (ML/d)Current storage (Rynie + Orana 1 + Orana 5): 4400 ML
Rynie
Orana
Orana 5
South flows50 days of WTPs shutdown
(01/11/14-20/01/15)
Flood event December 2014
160
140
120
100
80
60
40
20
0K
WTP
Wit
hd
raw
al R
ate
(ML/
d)
306
• On the left side of the graph is the commencement of major depressurisation in January 2014;
• Inflows gradually increase over the year to a maximum of 92 ML/d;
• The yellow line displays the withdrawal rate (i.e. the volume of water treated in the plant) planned shutdowns
for maintenance during the early part of 2013 are included;
• The blue line displays the increasing combined raw water pond levels as water production ramps up;
• In December 2014, an extreme event similar to the Queensland December 2010 event is added to the
simulation – 754 ML for the Kenya WTP complex and 118 ML for the NWTP complex;
• The total valume is derived from total December 2010 rainfall of 348.8 mm (from BoM as measured at Miles
Post Office, station number 042023) and total area of the ponds (e.g. 2,191,000 m2 for the Kenya complex);
• The simulation reverts to mean rainfall from January 2015 which, at 95.4 mm, is higher than the January 2011
recorded total of 88.6 mm;
• In addition 50 days of plant shutdown are added to the simulation;
• The lack of treatment capacity results in a sharp increase in pond operating level, and
• Despite water backing up in the raw water ponds, the Maximum Operating Level (MOL) is not exceeded.
Therefore, under such a scenario the production profile can be managed without discharge of untreated water
while a plan for plant startup or wells shutdown can be implemented. Furthermore, if this analysis considered
the regional storage ponds in the Southern Gas Fields, an additional 40 days storage is available. Therefore, the
results can be considered as conservative and should represent a worst case condition over the life of the project.
Running the same scenario for the Northern Gas Fields, the duration for shut down for the Northern Gas Fields
is limited to 26 days using the same operating assumptions as for the Central and Southern case. Although
this is less time than for the Central and Southern Gas Fields, it still provides sufficient time to manage water
production such that all raw water is contained within the ponds. Again, a plan for either start-up of water
facilities or the shut-down of wells would be prepared to contain and treat all raw water. As a back-up, an
additional 46 days of storage is available in the Polaris regional pond.
In case of water quality issues, water can be recirculated for further treatment and temporarily stored in existing
ponds. If out-of-spec water is detected by the in-line monitor at the Treated Water Pond Outlet, inflow to the
Treated Water Pond ceases and the treated water is re-circulated to the Raw Water Pond.
The plants are operated under a performance incentive whereby the operator must meet the Nomination that
QGC has set for delivery of water to the respective beneficial use schemes. By managing production incentives
the potential for extended shutdowns is minimised. Therefore, an extended shutdown of up to 50 days is not
considered to be a likely scenario.
In terms of the key questions of the analysis:
• The Kenya complex can store CSG water for up to 50 days without treatment. Those 50 days are more than
adequate to address any plant failures.
• The regional pond complex adds another 40 days to the storage capacity;
• Under a similar scenario the NWTP has 26 days of storage available – also sufficient time to address plant
failures. With an additional 46 days regional storage; and
• To avoid reaching MOL the water production profile will be managed including inflows.
# Department Condition Description Completion date Status
Pre-Dec 2012 Post-Dec 2012
35 52d ivCompletion of upgraded emergency response plans to cover all regulated water and waste storage facilities
April 2014
36 49h, 52d i IV 53B c Develop Emergency Discharge Management Plan July 2013
Commitments completed Evergreen Commitments
Commitments work in progress Firm deliverables for that month