The Importance of Measurement in Determining Gas Emissions from Flares and Vents Technical Consultant Dr. Jeff Gibson Presented by Dr. Norman Glen 12 June 2013
The Importance of Measurement in
Determining Gas Emissions from
Flares and Vents
Technical Consultant
Dr. Jeff Gibson
Presented by
Dr. Norman Glen
12 June 2013
Contents
Introductory slides:
Why is measurement important?
The UK National Measurement Office (NMO) and the National
Measurement System (NMS)
Main presentation:
Emissions from flares / Worldwide legislation
Methods used to determine quantity flared
Issues affecting flare measurement
Case study – The use of CFD simulation to determine the
installation error in flare gas meters
Any questions?
Measurement plays a fundamental part in the innovation
process. To develop new products and processes, companies
need to measure quantity, quality and performance.
To trade successfully, companies utilise a regulatory
framework, based upon measurement confidence, ensuring
access to global markets that are fair and open and without
unnecessary barriers to trade.
National Measurement Office (NMO)
Why is measurement important?
National Measurement System (NMS)
The NMS is a Network of laboratories and processes that
provide measurement standards and calibration testing
facilities.
It maintains the national measurement infrastructure
It represents the position of UK measurement
Internationally and influences the development of
standards.
Energy,
Oil & Gas
Low Carbon
TechnologiesEnvironment
UK National Standard for Fluid Flow Measurement:
A Global centre of excellence for flow measurement and
fluid flow systems serving both industry and Government
World class research, development, modelling, calibration,
consultancy, measurement and testing services to clients
across many sectors including: Energy, Oil & Gas, Low
Carbon Technology and the Environment
NEL (Scotland, UK)
Measurement system requirements
Design of system will depend on the “type” or
purpose of metering required:
Custody transfer
Allocation
Management and Control
Process operation
Environmental reporting (e.g. EU ETS)
The cost of errors
Oil field producing
20,000 BBL/Day
Cost per barrel: $100
Revenue: $2.0M per day
Suppose the meter under-reads (error) by
1%
3%
= Loss of revenue $20,000 per day
= Loss of revenue $60,000 per day
Main Presentation:
The Importance of Measurement in
Determining Gas Emissions from
Flares and Vents
Main Purpose of Flare System
Emergency relief system (fire risk, prevent over-
pressurisation, leaks and spills)
To allow for depressurisation for routine shutdowns and
maintenance periods
To vent-down vessels and pipework during equipment
trips and “black-outs”
Purging of O2 prevents pre-ignition
Steam/air injection reduces smoke and improves
efficiency
Yes, require an economic route for the gas, e.g.
Sell as gas, burn as fuel, LNG export, distil as
chemical product (methanol, dimethylether...)
Pipeline or LNG plant = large investment
Low gas price = less incentive to capture gas
Flare Gas Recovery (FGR) system is needed to allow
capture with safe operation
Can’t the gas be reused instead
of flaring it?
Flare normally
extinguished
FOV lifts when
pressure exceeds
safe limit
Global Gas Flaring/Venting Impact
Over 150 billion m3 gas flared/vented per year
= 30% of entire EU gas usage per year
= 30.6 billion USD in revenue wasted
= 360 million tonne CO2 equivalent (tCO2e)
Source: World Bank Global Gas Flaring Reduction (GGFR)
Partnership
Country
Quantity
Flared
(bcm/year)
% of Global
Flaring
(by volume)
1 Russia 37.4 26.72 Nigeria 14.6 10.43 Iran 11.4 8.14 Iraq 9.4 6.75 USA 7.1 5.16 Algeria 5 3.67 Kazakhstan 4.7 3.48 Angola 4.1 2.99 Saudi Arabia 3.7 2.6
10 Venezuela 3.5 2.5
Total 100.9 70
(Sources: Worldbank, 2011 data)
Top 10 Gas Flaring Nations
76% of
associated gas
40% of
associated gas
NOAA Satellite Imaging Datahttp://www.ngdc.noaa.gov/dmsp/interest/gas_flares.html
Gulf of MexicoNorth Sea
Nigeria
Flare Header lines
Liquid knockout / seal drums
Flare gas recovery (FGR) system
Pilot gas ignition system
Steam or air injection system
Elevated stacks or ground-based
flare-battery (onshore only)
Incinerators may be used
Key Elements of a Flare System
Ground FlaresElevated Flare Stacks
Emissions from Flaring & Venting
Greenhouse gases (GHGs): H2O, CO2, CH4, N2O, O3,
SF6 (electrical industry), Fluorocarbons and
Hydrofluorocarbons (refrigerants)
Main GHGs emitted: CO2 & CH4
Other unwanted gases (and effects):
SO2 & NOx - acid rain, ozone depletion
Non-methane VOCs – alkanes, alkenes, aromatics...
CO, particulates, smoke (incomplete combustion)
H2S, mercaptans (highly toxic, acidic, odours)
Noise & light pollution, radiation hazards…etc.
Legislation
Just about all nations have some form of legislation
for flaring and venting
Some more rigorously enforced than others (e.g.
Nigeria vs European Union)
Most prominent schemes: EU (ETS), Norway (ETS,
Taxation), Canada (e.g. ERCB Directive 060) and
USA (e.g. Rule 30 CFR 250, Subpart K)
Backed-up with Measurement & Reporting
Regulations (e.g. EU ETS MRR from Jan 2013)
EU Emissions Trading Scheme (1)
EU Kyoto target is combined 20% reduction by 2020
EU ETS is seen as key policy instrument for
Controlling and Reducing GHG emissions (others:
renewable, energy efficiency & CCS)
EU ETS is predominantly a CO2 Cap-and-trade
Scheme
Targets largest emitters (> 20 MWth aggregate)
Scheme commenced 2005, now in Phase III
Measurement uncertainty
Requirements set by tier level depending on total CO2
Should take into account stated uncertainty in equipment
(and/or calibration) and in use
Data, and associated measurement uncertainty, must be
verified by an accredited body
Traceability of equipment
Regular calibration, adjustment and checks (ISO 17025
lab or equivalent)
Measurement equipment traceable to International
Standards
Where no traceable standards available - identify other
alternative control and verification measures
EU ETS Phase III Monitoring &
Reporting Regs (MRR)
Volume
flow, Q
Steam/Air
Acid gas
(CO2/H2S)
Q = Metered or Calculated
EF = From gas composition
OF = Typically a constant value
Open flame
Air dilution
(unknown)
Mass CO2 =
f(Q, EF, OF)
EU ETS “Calculation Method”
Emission
“Cloud”
where:
Q = Standard volume (m3)
EF = Emission Factor (tCO2/m3)
OF =Oxidation Factor (-)
CO2 Emissions = Activity Data x Emission Factor x Oxidation Factor
tCO2 = Q x EF x OF
• Voume, Q (m3):
(Amount of Gas Flared)
• Emission Factor, EF(tCO2/m3):
(Process modelling software)
• Oxidation Factor, OF (-):
(Assume = 1.0, all C CO2
UK Benchmark = 0.98)
Measurement Uncertainty:
Cat A Cat B Cat C
< 50 ktCO2e 50-500 ktCO2e > 500 ktCO2e
± 17.5% ± 12.5% ± 7.5%
Uncertainty given in EU ETS MRR
EU ETS Minimum Tier Requirements
Very wide velocity range (> 1000:1)
Minimal pressure drop required
Large line sizes
Meters often welded (“hot-tapped”) to existing pipe
Low flow (< 0.1 m/s):
• Resolution problems
• Re < 10,000 = Transition, Stratification,
High instability
Blow-downs (50 - 100 m/s+):
• Compressible, unstable and noisy
• Rapid temperature drops
• Liquid carry-over/drop-out, suspended solids
Issues for Flare Measurement
Calibration & Traceability Issues
Difficult to remove meters for lab calibration (full flow range
unlikely to be achievable in any case)
Calibration unlikely to be done except prior to commissioning
spool-pieced meters
In situ verification flow tests:
Gas tracer techniques (e.g. Kr85, SF6, He…)
All in situ methods “at mercy” of prevailing flow conditions
/ unknown leaks / inadequate tracer mixing….
Insertion probes - H&S issues?
Comparison against other meters (e.g. Deliberately divert
gas to flare through a “reference” meter = costly)
Basic in situ checks (Note: not flow tests)
• Post-installation verification – dimensional checks
• Zero-checks of electronics/cabling
• Online „self-check‟: e.g. Check speed of sound is
“sensible” (ultrasonic meters)
• Extraction/checking of transducers “in a box”
containing reference gas (e.g. nitrogen) against a
baseline reading
Checks transducers/cabling/electronics, but not
response under flowing conditions
Verification Checks
Many technologies available as insertion-type (or
separate transducers) that can be installed through
bosses. Here are some of these:
Insertion turbine
Insertion vortex
Averaging pitot
Thermal mass
Ultrasonic meters
Optical correlation meters
Limited range
Wider range
Dedicated Flare Meters
These are “Point” (or at best “Line”) measurement
devices
Only “see” only a portion of the flow and measure local
velocity (need corrections to get to average velocity
and volume flow)
Multiple paths / points can improve measurement, but
low flow region remains a challenge
Cannot be calibrated unless pre-installed in a spool-
piece that can be removed for periodic flow calibration
Insertion-type meters
Use transit-time method to get velocity (volume via
correction and geometry):
Many applications worldwide both on and offshore
Very wide flow range with low overall DP
Density (possibly EF) from MW = f(SOS, T, p….)
Single-path measurement (affected by flow profile)
Large errors/scatter at low flow
“Beam Drift” at high flow
Liquids cause over-reading and SNR problems
Ultrasonic Flare Gas Meters
When can indirect (estimation) methods be used to
determine flare quantities?
de-minimus quantities (< 2% of total emissions)
When installing meters is unfeasible
For periods where meters malfunction (back-up)
“Un-measurable” conditions (very high flow)
Cross-referencing (redundancy)
As part of a distributed metering system
Estimation Methods
Gas produced
Difference = Gas Flared
Exported gas
Fuel gas
Re-injected gas
More accurate during high flaring (meter back-up)
Unsuitable for low, background flaring…
Here’s a simple example to prove this....
By-difference Method
Assume, for simplicity, Uncertainty = 5% on both
gas in and gas out figures
Gas in = 100 t/hr 5% ( 5 t/hr)
Gas out = 60 t/hr 5% ( 3 t/hr)
Gas flared = 100 – 60 = 40 t/hr
% Unc = (52 + 32)0.5/40 x 100
= 14.6%
Example 1: High Flare
5%
5%
Gas in = 100 t/hr 5% ( 5 t/hr)
Gas out = 99 t/hr 5% ( 4.95 t/hr)
Gas flared = 100 – 99 = 1.0 t/hr
% Unc = (52 + 4.952)0.5/1.0 x 100
= 704%
or -6 to +8 t/hr
Example 2: Low Flare
Incorrect methods & equipment used
Poor maintenance & lack of traceability
Loss of signal at low/high flow (resolution/noise)
Bad installation and resulting errors/noise
Liquids, sand, scale… (especially at high flow)
Inadequate measurement uncertainty calculations
Poor spreadsheet analysis (incorrect filtering)
Inadequate measurement and use of p, T & Mw etc..
Inadequate data acquisition
General Measurement Issues
Some real-life Examples
Typical Meter Output
1) Background flaring
2) Routine Flaring
3) Upset condition
Area under graph = Total gas flared
Same data plotted cumulatively
Flo
w (
kg/h
r)
250
200
150
100
50
0
1 2 3 4 5 6
(days)
High Flow (meter over-ranged)
Wide variation with sudden spikes in data
Mass flow tops-out at 250 kg/hr (20 mA)
Low Flow Issues (refinery flare)
Negative velocity!!
Positive velocity
Courtesy: GE Sensing
Velocity on
various meter
paths
Temp & dew
Point plot
BY CALCULATION
PROCESS MODELLING
SOFTWARE
• „‟Advocated‟‟ in EU ETS MRR
• Requires knowledge of:
All inputs
Relative percentages
Process conditions
• Depends on reliable and
accurate process modelling
software!
• Models need to be “trained”
BY MEASUREMENT
GAS SAMPLING
• Manual sample (Flare-line):
H&S issues x
low pressure x
contributing streams
• Automated sampling Cost??
* baseline
* normal
* blow-down ?
contributing streams
ULTRASONIC
FLARE GAS METER
• Estimate gas composition
from speed of sound:
(average molecular weight)
* Use to estimate nitrogen
content (purge)
Flare Gas Composition
Mole-weight output (FG US meters) used in Norway to
enable corrections (reduction in tCO2) by nitrogen injection
Not widely used in North Sea, or worldwide
Could provide a method of determining Mw (and CO2
emission factor) during process upsets
Case Study – Using CFD Simulation to
Determine Installation Error in a Flare Gas
Flow Meter
Offshore operator was unhappy with the current
metering systems on two of their North Sea platforms
Company invested in a new ultrasonic metering system
on one of the platform to replace dual metering system
Meter welded to the flare boom pipework – there were
two main issues with this:
1. There was not enough straight length upstream to
ensure developed flow [carried out by NEL]
2. Meter required a heat shield to protect against
radiant heat from flare tip [addressed by the meter
manufacturer]
Case Study
Most flare meters are retrofitted to existing lines
Space/access is often a problem offshore
Shutdown to upgrade costs lots of ……
Installation Error
Result: meters installed in short pipe-runs
Bends, reducers, tees etc. cause:
flatness, asymmetry, swirl, and increased
turbulenceInstallation
error
Uncertainty
Installation Error
Flow
Meter
Good
Direction of flow
Error /
Increased
Uncertainty
Bad Flow
Meter
0
0.2
0.4
0.6
0.8
1
1.2
-1 -0.5 0 0.5 1r/R
vel
oci
ty
0
0.2
0.4
0.6
0.8
1
1.2
-1 -0.5 0 0.5 1
r/R
vel
ocit
y
0
0.2
0.4
0.6
0.8
1
1.2
-1 -0.5 0 0.5 1
r/R
vel
oci
ty
0
0.2
0.4
0.6
0.8
1
1.2
-1 -0.5 0 0.5 1
r/R
vel
ocit
y
Fully Developed Peaked Flattened Skewed
Asymmetric velocity profiles
Flow Profile and Swirl Patterns
Swirl patterns
Cannot install a flow conditioner owing to pressure drop
Change metering system? (Costly, need shutdown)
Determine a correction factor(s) to remove error:
• Bespoke lab tests? (Costly, representative?)
• In situ gas tracer tests? (Costly, flow stability)
• CFD simulation is cost-effective, and generally
more informative and enlightening than testing,
but a good knowledge of CFD modelling, flow
measurement is needed
• Validation is important
Remedial Actions
Proposed
Meter
Position
CFD Analysis – offshore flare (1)
3d mesh used to represent the
flow to through meter
Proposed
Meter
Position
Flow split
varied
Disturbed flow
profile + high
swirl = Error
CFD Analysis – offshore flare (2)
CFD (Flare Ultrasonic meter)
Single bend
Ideal, fully
developed flow
Disturbed flow
Dual-path research meter tested and
simulated at NEL (NMO funded project)
CFD Validation work
(Research Supported by NMO)
Flare is a uniquely difficult measurement application:
Very wide turn-down, erratic behaviour, low
temperatures, unstable flow
Hot-tapped meters cannot be removed for calibration
Installation errors, liquids, very low flow etc.
What uncertainty can we realistically expect to
achieve? (facility-specific: onshore vs offshore)
Practical, but comprehensive guidance is needed
Summary (1)
Summary (2)
Sampling from flare lines is difficult
Samples of fuel gas ok if mol weight during process
upsets can be characterised/estimated (taking into
account inorganic gases: N2, He etc.
Must take ratio of low/high flare into account (i.e.
contribution to total gas flared)
Direct measurement techniques (optical etc.) to
characterise emissions (costly)
Multiple meter technologies / methods may provide a
solution to complex installations
Examine flow and composition data properly – must
involve measurement experts to advise environmental
managers and consultants
Legislation, with cost implications (e.g. EU ETS), will
hopefully help drive innovation
Gas price dictates the value in capturing gas (e.g.
fracking in US has driven down the gas price
Summary (3)
Thank you for listening
Any questions?
The National Measurement System is the UK‟s national infrastructure of measurement
laboratories, which deliver world-class measurement science and technology through four
National Measurement Institutes (NMIs): LGC, NPL, the National Physical laboratory, NEL the
former National Engineering Laboratory, and the National Measurement Office (NMO).