Title: Proposed Requirements for Calculating Emergency Planning Zones for Sour Wells, Sour Pipelines and Sour Production Facilities
1Proposed Requirements for Calculating Emergency
Planning Zones for Sour Wells, Sour Pipelines and
Sour Production Facilities
- Presented by
- Gary Neilson BSc(Hons) P.Phys
- Public Safety Implementation Team
2Presentation Outline
- Background
- Proposed new requirements
- EPZ calculation process
- Implications
- Future work
- EUBMODELS Structure
3Background
- Project initiated to address issues heard by
Provincial Advisory Committee on Public Safety
and Sour Gas - Proposed EPZ calculation requirements based on
assessing the hazard footprint of a sour gas
release using dispersion modelling
Provincial Advisory Committee on Public Safety
and Sour Gas Findings and Recommendations Final
Report December 2000
4Background
- In the past, disagreement between experts and
public about model choices and inputs that will
lead to accurate, useful and credible results - Difficult for EUB to make informed decisions in
the public interest without full understanding of
differences
5Background
- Draft requirements published mid-December 2003
- Early draft February 2002
- Technical workshop focus groups
- Peer review/EUB testing of EUBMODELS
- Requesting feedback on
- clarity of the requirements/additional
requirements - the supporting EUBMODELS documentation and
software - March 31, 2004 (extended)
- Requirements will be included in future revision
of Guide 71 - Emergency Preparedness and Response
Requirements for the Upstream Petroleum Industry
6Proposed Requirements
- Address suite of PSSG Recommendations (17,18, 19,
58 and 62) - Define the minimum standards to calculate an EPZ
to protect public SAFETY (protect against
fatalities or serious irreversible health
effects) - Replaces the simple release rate based equations
(or nomographs) - EPZ derived from new requirements remains first
step. Actual size and shape of the final EPZ must
reflect site-specific features of the area
7Proposed Requirements
- EPZ more realistically calculated
- characterization of the release (representative
gas analysis, source conditions at exit
calculated, real gas effects) - dispersion modelling,
- consequence modelling to a toxic load based
endpoint (concentration AND exposure time
important) - Credit for PRACTICAL mitigation actions (e.g.
limiting release duration through ignition) - No reduced EPZ as presently defined as single
EPZ includes mitigation actions NO EUB
PRE-APPROVAL - Applicable to new applications, ERP updates AND
interventions
8Proposed Requirements
Base Case MANDATORY
- REQUIREMENTS
- (Minimum Standards)
- Sour Gas Release Rates
- Gas composition
- Depressurization (REAL GAS EFFECTS)
- Release Duration
- Dispersion Modelling
- Meteorological Conditions
- Concentration Fluctuations
- EPZ Endpoints
EUBMODELS (Screening Level EPZ Calculation) Techni
cal Descriptions and Formulations User Guide
Tutorial Software Package
9Release Rates
- For wells maximum release rates required as
described in Guide 56 - For pipelines mass release rate profile from a
guillotine break must be calculated using the
maximum licenced pressure - account for the emergency shutdown valve (ESD)
trip set points - the distance between ESD valves
- mass of gas in adjacent pipeline segments that
escapes before the valves close
10Depressurization - why are real gas effects
important?
- Ideal gas laws under predict EPZ
- Real gases can form liquid aerosol as they expand
and cool - Well releases are sensitive to wellhead exit
conditions (pressure, temperature, hole diameter) - More detailed calculation may result in buoyant
release - Pipelines usually dense due to pressures
- EUBMODELS Base Case always dense release -
CONSERVATIVE
11Release Duration
- Duration defines exposure time
- Duration for wells must be realistic for the
scenario (drilling, servicing or producing) and
other site-specific factors - Duration for pipelines determined by transient
mass release through a guillotine break - Countermeasures such as ignition that limit the
duration of the sour gas release are permissible
(documented and PRACTICAL) - For pipelines ignition not allowed as a
countermeasure - releases not typically long enough for manual
ignition - self-ignition not guaranteed
12Dispersion Modelling
- Worst case Met conditions assumed
- Dispersion model used must account for
- real gas effects
- dense or buoyant releases
- For dense plumes parallel airflow model is
acceptable because a sour gas release from a well
or pipeline occurs at or near ground level - Plumes that rise complex terrain model may be
required - EUBMODELS Base Case must still be included in the
documentation supporting an EPZ calculation as
well as the calculation using a complex terrain
model for comparison purposes
13Complex Terrain Criterion - H2S Releases
- Requirements now address issues of terrain
- Buoyant releases may require complex terrain
modelling - Compare terrain elevations in EPZ to terrain
criteria defined in EUBMODELS - Criteria based on EUB Guide 60 (Flaring)
- kinetic energy lift sufficient to overcome
temperature gradient
complex
criterion
parallel
14Toxic Load End Points
- Endpoint described by toxic load criterion
- LKCnt
- same adverse effect for low concentration over
longer time as high concentration for short time - concentration weighted (n)
- K accounts for concentration fluctuations
(dispersion models only predict averages) - Objective of endpoint is to provide conservatism
to protect public safety (i.e. if level achieved
would not expect fatality or other serious
irreversible adverse effect)
15EPZ Calculation Process
EUBMODELS Base Case (Mandatory)
EPZ pre-approval from EUB not required
EPZ to be used for Public Involvement
EPZ tuned to reflect site specific features
Acceptable
EUBMODELS BC Parameters varied
EUB assessment
ERP
Acceptable
Alternate Methods
EUBMODELS BC must also be modelled using
alternate methods
16Implications
- Anticipate zones will change
- More effort required than previous simplistic
approach - detailed documentation (explaining mitigation
actions, variation of base case parameters,
alternate methods) - Responsibility on industry to ensure practical
mitigation measures used - Operational implications (e.g. ESD valve trip
points)
17Future Work
- Toxic load endpoints need further discussion
- workshop on H2S toxicity
- objective to assist EUB in selecting safety
endpoint - Ignition timing lower limit needs to be defined
- workshop planned
- Address stakeholder comments
- Develop implementation strategy with stakeholders
depending on impact compared to previous methods - Revise Guide 71 targeting fall 2004
- EUBRISK and EUBHVP EUBMODELS can be adapted
possibly undertake in new fiscal year
18EUBMODELS Structure
Runs 54 times for met matrix
19Summary of PROPOSED Requirements
- Requirements in draft Requirements in Guide 71
still apply - No reduced EPZ application (size of EPZ
determined by varying parameters) - single EPZ
can be taken forward to communities for
discussion and fine tuning - EUB review post public involvement as part of ERP
assessment REALISTIC MITIGATION - Requirements applicable to new applications, ERP
updates or interventions - Provide clarity to assist in EUB decisions
20Project Website
- www.eub.gov.ab.ca/BBS/new/Projects/sgr.htm
draft.protocol_at_gov.ab.ca