CGE Greenhouse Gas Inventory Hands-on Training Workshop for the African Region - Energy Sector - PowerPoint PPT Presentation

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CGE Greenhouse Gas Inventory Hands-on Training Workshop for the African Region - Energy Sector

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CGE Greenhouse Gas Inventory Hands-on Training Workshop for the African Region - Energy Sector Fugitives Pretoria, South Africa 18-22 September 2006 – PowerPoint PPT presentation

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Title: CGE Greenhouse Gas Inventory Hands-on Training Workshop for the African Region - Energy Sector


1
CGE Greenhouse Gas Inventory Hands-on Training
Workshopfor the African Region- Energy Sector
FugitivesPretoria, South Africa18-22
September 2006
2
Energy Sector Fugitive Emissions
3
Introduction
  • Fugitives the sum of emissions from accidental
    discharges, equipment leaks, filling losses,
    flaring, pipeline leaks, storage losses, venting,
    flaring, and all other direct emissions except
    those from fuel use.
  • Mainly methane
  • Entrained CO2 can be significant in some cases
  • Minor N2O emissions from flaring

4
Sources of Fugitives
  • Solid fuels (primarily coal)
  • mining, handling, processing, and storage
  • Oil and natural gas systems
  • exploration, production, processing, refining,
    transmission, storage, and distribution

5
Coal Mining and Handling
  • Release of trapped methane during mining
  • In-situ methane content of coal can vary
    significantly
  • Most fugitive emissions occur at the mine
  • Some residual emissions occurring from
    post-mining handling / processing activities

6
Surface vs. Underground
  • Two types of coal mines
  • Higher emissions for underground mines
  • Emissions increase with depth of mine
  • Emissions also depend on gas content of coal
  • Some gas may remain in the coal
  • 60-75 gas released during mining activity

7
Abandoned mines
  • Emissions may continue after the mines have
    stopped producing coal
  • Typically, emissions decay rapidly once deep mine
    coal production stops
  • In some cases, emissions by the surrounding
    strata may be significant and continue for years
    afterwards.
  • Coal waste or reject piles are minor source of
    emissions
  • Flooding of mines can prevent emissions

8
Controlling Emissions
  • Degasification wells
  • Gas conservation
  • Flaring
  • Use of catalytic combustors on the outlet of
    ventilation systems for underground mines

9
Monitoring and Activity Data
  • Methane content of exhausted ventilation air
    (Tier 3)
  • Coal production (Tier 1 or 2)
  • Imports and exports by type of coal
  • post-mining emission, likely to be minor
  • Information on the depth of each mine (Tier 2)

10
Tier 1 and Tier 2
  • Tier 1 global average emission factors
  • Tier 2 country or basin-specific emission factors
    based on actual CH4 content of coal mined

11
Tier 3 Underground mines
  • Underground mines generally must have ventilation
    and degasification systems for safety reasons
  • Often also includes degasification wells around
    mining area
  • Can use data to actually estimate emissions or to
    develop more specific emission factors.
  • When methane recovery from degasification wells
    occurs before mining, emission should be
    reporting in year coal was actually extracted.

12
Coal mining issues
  • Initial focus can be on most gassy mines for
    Tier 3 approach, and apply Tier 1 or 2 for other
    mines.
  • Tier 3 not likely to be feasible for for surface
    mines or post-mining
  • Methane recovered and combusted for energy should
    be included in fuel combustion emissions
  • No method provided for coal fires
  • Significant quantities of CO2 can also be
    released during mining

13
Coal Mining Data Issues (cont.)
  • Coal statistics usually include primary (hard
    coal and lignite) and derived fuels (patent fuel,
    coke oven coke, gas coke, BKB, coke oven gas and
    blast furnace gas). Peat may also be included.
  • No information is typically provided on the
    method of mining (i.e., surface or underground)
    or the depth of the mines. A conservative
    approximation is to assume that lignite coal is
    surface mined and bituminous and anthracite coal
    is from underground mines.
  • Some useful unpublished data, including mine
    depth, are available from IEA upon special
    request.

14
Coal Mining References
  • Coal statistics are available for most countries
    from the
  • U.S. Energy Information Administration (EIA)
    (www.eia.doe.gov),
  • United Nations Statistics Department (UNSD)
    (http//unstats.un.org/unsd/)
  • International Energy Agency (IEA) (www.iea.org)

15
Oil and Natural Gas Systems
  • Equipment leaks
  • Process venting and flaring
  • Evaporation losses (i.e., from product storage
    and handling, particularly where flashing losses
    occur)
  • Accidental releases or equipment failures

16
Emission rates depend on
  • Characteristics of hydrocarbons being produced,
    processed or handled
  • conventional crude oil
  • heavy oil
  • crude bitumen
  • dry gas
  • sour gas
  • associated gas
  • Equipment numbers, type, and age
  • Industry design, operating, and maintenance
    practices
  • Local regulatory requirements and enforcement

i.e., methane content of fuel and leakiness of
equipment
17
Emissions from venting and flaring depend on
  • The amount of process activity
  • Operating practices
  • Onsite utilization opportunities for methane
  • Economic access to gas markets
  • Local regulatory requirements and enforcement

18
Accidental Releases
  • Difficult to predict
  • Can be a significant contributor
  • Can include
  • well blowouts
  • pipeline breaks
  • tanker accidents
  • tank explosions
  • gas migration to the surface around the outside
    of wells
  • surface casing vent blows
  • leakage from abandoned wells

19
Size of the facility
  • Oil and gas systems tend to include many small
    facilities
  • Exceptions
  • petroleum refineries
  • integrated oilsands mining and upgrading
    operations
  • Small facilities likely to contribute most of the
    fugitive emissions
  • Less information available for smaller facilities

20
Oil / Gas Composition
  • Raw natural gas and crude oil contains
  • a mixture of hydrocarbons
  • various impurities including H2O, N2, Ar, H2S and
    CO2
  • Impurities are removed by processing, treating or
    refining
  • H2S
  • Sour gas if more than 10 ppmv of H2S
  • Sweet gas if less than 10 ppmv of H2S
  • The concentration of H2S tends to increase with
    the depth of the well.

21
Acid Gas
  • By-product of the sweetening process to remove
    H2S
  • May contain large amounts of raw CO2
  • Regardless of how processed
  • sulphur recovery unit
  • flared or vented
  • the raw CO2 is released to the atmosphere

22
Patterns of Emissions
  • Emissions increase as you go upstream through
    system
  • Emissions decrease with concentration of hydrogen
    sulphide (H2S) in the produced oil and gas

23
Equipment Leaks
  • Tend to be continuous emitters
  • Low to moderate emission rates
  • All equipment leaks to some extent
  • Only a few percent of the potential sources at a
    site actually leak sufficiently at any time to be
    in need of repair or replacement.
  • If less than 2 percent of the total potential
    sources leak, the facility is considered
    well-maintained

24
Sources of Equipment Leaks
  • Valves
  • Flanges and other connections
  • Pumps
  • Compressors
  • Pressure relief devices
  • Process drains
  • Open-ended valves
  • Pump and compressor seal system degassing vents
  • Accumulator vessel vents
  • Agitator seals
  • Access door seals

25
Trends in Equipment Leaks
  • Leaking decreases as toxic nature increases
  • Leaking decreases as where gas has been odorized,
    thus less leaking in sour gas sections of systems
  • Leaks more when subjected to frequent thermal
    cycling, vibrations, or cryogenic service

26
Storage Losses
  • Boiling or flashing losses of methane occur from
    storage tanks
  • Occurs at production and processing facilities
    where hydrocarbon liquid flows directly from a
    pressure vessel where it has been in contact with
    natural gas

27
Methodologies
  • Tier 3 Requires detailed inventories of
    equipment, infrastructure, and bottom-up emission
    factors
  • Tier 2 Based on a mass balance estimate of the
    maximum amount of methane that could be emitted
  • Only for oil systems
  • Based on gas to oil ratios
  • Tier 1 Uses national oil and gas production
    data and aggregate emission factors

28
Fugitives Data
  • Poor quality and incomplete data about venting
    and flaring is common
  • Contact industry representatives for standard
    practices to split venting and flaring
  • Data on equipment leaks at minor facilities are
    often unavailable or incomplete
  • Well-site facilities
  • Field facilities

29
Fugitives Data (cont.)
  • Collection of activity data for fugitives sources
    is difficult and resource intensive
  • There are no real shortcuts available
  • First steps can be to interview experts in
    industry on common practices and processes
  • have then compare national practices with those
    of countries with known emissions profile (e.g.,
    an Annex I country).

30
Venting and Flaring Data
  • Flared if gas poses an odour, health, or safety
    concern
  • Otherwise vented
  • Often inconsistencies in reported vented and
    flared volumes by companies
  • Problem with some vented volumes being reported
    as flared

31
Oil and Gas System Data Issues
  • International production data are expressed on a
    net basis (i.e., after shrinkage, losses,
    reinjection, and vented and flared)
  • Crude oil normally includes hydrocarbon liquids
    from oil wells and lease condensate (separator
    liquids) recovered at natural gas facilities. May
    also include synthetic crude oil from oilsands
    and shale oil.
  • Infrastructure data is more difficult to obtain
    than production statistics

32
Oil and Gas System Data Issues (cont.)
  • Information on the numbers and types of major
    facilities, types of processes used at these
    facilities, numbers and types of active wells,
    numbers of wells drilled, and lengths of pipeline
    are typically only available from national
    agencies.
  • Information on minor facilities (e.g., wellhead
    equipment, pigging stations, field gates, and
    pump stations) may not be available, even from
    oil companies.
  • The only infrastructure data potentially required
    for Tier 1 approach are well counts and lengths
    of pipeline
  • Detailed facility information required for IPCC
    Tier 3

33
Oil and Gas System References
  • Other methodology manuals
  • American Petroleum Institute (API) (www.api.org)
  • Canadian Association of Petroleum Producers
    (CAPP) (www.capp.ca)
  • Canadian Gas Association (CGA) (www.cga.ca)
  • Gas Technology Institute (GTI) (www.gastechnology.
    org)
  • Oil and gas statistics
  • U.S. Energy Information Administration (EIA)
    (www.eia.doe.gov/neic/historic/hinternational.htm)
  • United Nations Statistics Department (UNSD)
    (http//unstats.un.org/unsd/methods/inter-natlinks
    /sd_natstat.htm and http//unstats.un.org/unsd/dat
    abases.htm)
  • International Energy Agency (IEA)
    www.iea.org/statist/index.htm

34
Oil and Gas System References (cont.)
  • Oil and Gas Journal (www.ogjresearch.com)
  • Some infrastructure data (number of wells, gas
    plant listing, major project announcements)
  • Worldwide refinery, pipeline and gas processing
    projects
  • Historical refinery, pipeline and gas processing
    projects
  • Worldwide oil field production survey
  • Worldwide refining survey
  • Worldwide gas processing survey
  • Enhanced oil recovery survey

35
- Closing -
36
Documentation Reporting
  • Transparency and documentation are the most
    important characteristic of national inventories!
  • Unless it is documented, then there is nothing to
    show that it was done or done correctly
  • Electronic reporting greatly facilitates the work
    of the UNFCCC Secretariat

37
Final remarks
  • A national inventory is not a research project
  • It is a national program that works closely with
    statistical and research institutions to create
    high quality emissions data.
  • Please feel free to email me in the future
  • Michael Gillenwater
  • gillenwater_at_alum.mit.edu

38
Extra slides
39
Quiz
  • 20 minutes

40
Quiz answers
  • Energy Quiz 1 (key).doc

41
Nitrogen Oxides (NOx)
  • Indirect greenhouse gases
  • Fuel combustion activities are the most
    significant anthropogenic source of NOx
  • energy industries
  • mobile sources
  • Two formation mechanisms
  • "fuel NOx"
  • thermal NOx"

42
Carbon monoxide (CO)
  • Indirect greenhouse gas.
  • Majority from motor vehicles, but also from small
    residential and commercial combustion
  • Intermediate product of the combustion process

43
Non-Methane Volatile Organic Compounds (NMVOCs)
  • Indirect greenhouse gases
  • Product of incomplete combustion
  • Mobile sources and residential combustion,
    especially biomass combustion
  • Low emissions for large-combustion plants

44
Sulfur dioxide (SO2)
  • Aerosol precursor
  • May have a cooling effect on climate
  • Concentration increases with burning of fossil
    fuels that contain sulfur
  • Closely related to the sulfur content of fuels

45
Quiz
  • 20 minutes

46
Quiz answers
  • Fugitives Quiz 1 (key).doc

47
(No Transcript)
48
EFDB Exercise
  • Look up available CH4 emission factors for
    biomass-agricultural wastes used for any type of
    fuel combustion

http//www.ipcc-nggip.iges.or.jp/EFDB/find_ef_s1.p
hp
49
EFDB search results
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