Title: Western States Oil and Gas Emission Inventories
1Western States Oil and Gas Emission Inventories
- Presentation to Four Corners Joint Air Quality
Task Force
January 8, 2007
2Todays Presentation
- Overview
- WRAP Phase I Emissions Inventory
- NMED Emissions Inventory
- WRAP Phase II Emissions Inventory
- Four Corners AQTF Emission Inventory and Modeling
3Overview
- Prior to WRAP Phase I, inventories were spare and
consisted mainly of larger point sources. Drill
rigs, compressors, other wellhead emissions were
largely unestimated - WRAP Phase I was the first consistent region-wide
emission inventory for OG area sources,
previously unestimated in most states - NMED inventory focused only on San Juan and Rio
Arriba counties in New Mexico with greater detail
than Phase I inventory - WRAP Phase II will improve on existing inventory
by using producer information and revised
emissions estimation methodology - WRAP Phase II results will be used in 4C modeling
4WRAP Phase I
- Adopted point source emissions from existing
state inventories - Focused on estimating area source emissions for
important NOx sources - Drill rig engines
- Natural gas compressor engines
- CBM pump engines
- Minor NOx and VOC wellhead processes were also
estimated - Reconciled point and area inventories
- Incorporated emission controls in future years
5WRAP Phase I Well locations
- Much of the estimation methodology used well
counts and locations - Databases obtained from state oil gas
commissions - Well locations not obtained for CA CARB
provided county-level emissions estimates
6WRAP Phase I Emissions Methodology
- Drill rigs
- Emissions factors from WYDEQ study of
Jonah-Pinedale area, derived from producer
information - Adjusted for other formations based on average
depth of wells and average drilling duration - Natural Gas Compressor Engines
- Emission factor 2.3x10-5 tons NOx/MCF, derived
from NMOGA inventory - Gas production obtained from oil and gas
commissions
7WRAP Phase I Emissions Methodology
- CBM Pump Engines
- Controlled emission factor from WYDEQ EPA
NONROAD uncontrolled factor elsewhere - Assumptions on pump operation and well design to
estimate engine power and hours of pumping/idling
- Minor NOx VOC Wellhead Processes
- Divided production between oil wells and gas
wells based on OGC data - Estimated emissions at oil wells by combining
production with WYDEQ oil well emission factors - Estimated emissions at gas wells by combining
production with WYDEQ gas well emission factors
8WRAP Phase IFuture Year (2018) Inventory
Procedure
- Grow 2002 emissions to 2018 based on estimated
growth in oil and gas production - Sources of data
- Local
- Resource management plans (BLM)
- Alaska Department of Natural Resources
- Regional, Energy Information Administration
- Oil production growth 1.334
- Gas production growth 1.458
- Adjust for post-2002 on-the-books controls
- Special cases
- Sierra and Otero, NM
- CBM development in Montana, North Dakota and Utah
9WRAP Phase I2002 and 2018 NOx Emissions
10WRAP Phase I2002 and 2018 VOC Emissions
11NMED Inventory Project Overview
- Estimated 2002 emissions from oil gas
activities in San Juan and Rio Arriba counties in
NW New Mexico - Obtained detailed data on equipment type, usage
activity, well schematics and gas production and
characterization directly from producers to
improve emissions inventory for these two
counties - On a well count basis, 67 - 72 response by
producers to emissions inventory survey
12NMED Inventory Comparison with WRAP Phase I
Emissions covered in WRAP Phase I and NMED
inventories for Rio Arriba and San Juan counties
indicates source category covered in NMED that
was not covered in WRAP Phase I inventory
13WRAP Phase II
Tasks in the WRAP Phase II work plan
- Update 2002 WRAP Phase I regional emissions using
detailed data to be provided by producers - Use county-level OGC data to updating baseline
emission inventory from 2002 ? 2005 - Identify and evaluate most promising control
strategies - Project emissions to 2018, then estimate
emissions with control strategies implementation - Update 2018 large point source SO2 emissions to
reflect estimated 2018 production and controls
14WRAP Phase II 2002 Emissions Inventory Update
- Major effort to update methodology for 2002
emissions inventory using detailed information
from producers - Update drilling rig emissions estimates
- Update compressor engine emissions estimates
- Examine potential for improvement of VOC
emissions from venting, flaring and dehydrators - Update CBM engine emissions estimates
- Examine potential for estimating fugitive dust
emissions from O G operations in the WRAP
region - Subtasks (a) and (b) will be completed, subtasks
- (c) (e) to be completed based on available
resources
15WRAP Phase II
- New methodology will estimate emissions on a
basin-wide average basis for all basins in the
WRAP region, focusing on those basins where major
OG activities are occurring and detailed
producer information is available
- In basins where significant activity is not
occurring, or producer information is
unavailable, will rely on Phase I estimates
16WRAP Phase II Drilling Rig Emissions
- Improve estimate of actual drilling time by
formation and basin from producer information on
drilling times (rather than spud date and well
completion date) - Improve estimate of average drilling rig engine
load by formation and basin - Determine average horsepower requirements by
formation and basin and identify most often used
or representative makes/models of drilling rig
engines - Incorporate manufacturers rated emissions
factors for makes/models identified, or
producers emissions tests where available - Estimate SO2 emissions (based on sulfur content
of fuel) and PM emissions
17WRAP Phase II Compressor Engine Emissions
- Determine for each basin either (1) the average
percentage of wells with wellhead, lateral and
central compression or (2) percentage of total HP
with wellhead, lateral or central compression - Remove all central and lateral compressors that
have been counted in a point source inventory for
each state - Determine for each basin a representative or most
often used make/model of compressor, including HP
and rated or tested emissions factors - Determine for each basin an average load factor
for wellhead/lateral compressors - Basin-wide emissions estimate on the basis of
total well count
18WRAP Phase II VOC Emissions
- Previous Work included
- Tanks flashing, working and breathing losses
(VOC) - Glycol dehydration units (VOC)
- Heaters (VOC and NOx)
- Pneumatic Devices (VOC)
- Completion-venting and flaring (VOC, NOx, CO)
- New work will look at VOC from
- Venting (from unloading fluids)
- Fugitives (using typical well diagrams)
- Dehydrators (look at point source vs. area source
distribution)
19WRAP Phase II CBM Engine and Fugitive Dust
Emissions
- CBM Engines
- Estimate drilling rig and compressor emissions in
basins with significant CBM activity - Estimate CBM pump engine emissions estimated
based on producer information - Fugitive Dust Emissions
- Explore feasibility of estimating fugitive dust
emissions on the basis of annual vehicle
activity, unpaved/paved road mileage in WRAP
region and dust emissions characteristics - Evaluate other sources of information
20WRAP Phase II Emissions Estimates Depend on
Producers Providing Information Requested
- Timeliness and quality of the revised 2002 and
2005 emissions dependent on producers data - ENVIRON questionnaire has been distributed to all
major producers, and some mid-level producers in
WRAP region. Most have agreed to provide
requested data - To date only a small fraction of required data
has been received we need data from producers!!
21WRAP Phase II Updated 2002 ? 2005 Baseline
Emissions
- 2005 represents a more current base year for
projections and can be used as a second data
point to verify projections methodology - Methodology will be to first update 2002
emissions using the Phase II tasks described
here, then to scale up 2002 emissions using 2005
county-level OGC well count or production data - In areas with no production or wells in 2002, but
with production or wells in 2005, emissions will
be scaled based on state average emissions per
well (or per production unit)
22WRAP Phase II Control Strategies
- Control technology evaluations to be conducted
- 1 Development of Control Technology will
depend on level of emissions - SOx emissions will be a function of the
sulfur content of fuels - Develop white papers on control technologies that
detail control effectiveness, costs, potential
emissions reduction, cost-effectiveness (/ton)
23WRAP Phase II Control Strategies
- Control technologies/strategies by source
category
- Drill Rigs
- Injection Timing
- SCR
- Low-Sulfur Fuel
- DPF
- DOC
- EGR
- Crankcase Emission Controls
- Other retrofit technologies
- (i.e. LNC, NOx adsorbers)
- Compressor Engines
- Rich-burn engines
- Ignition Timing
- Air-Fuel Ratio Adjustment
- NSCR
- Pre-stratified Charge
- Lean-burn engines
- Ignition Timing
- Air-Fuel Ratio Adjustment
- SCR
- High Energy Ignition System
- EGR
Other strategies Replace/repower with
low-emissions engine, electrification
24WRAP Phase II Control Strategies
Typical calculation for a single basin wellhead
compressors using EGR
Identify 3 representative makes/models of
well-head compressors based on hp
Calculate emissions reductions (ton/year) per
engine
Calculate cost-effectiveness using BACT
methodology
25WRAP Phase II Control Strategies
- Per-engine emissions reductions scaled to entire
basin using OGC well count data and percent of
wells with wellhead compressors - Total reductions will be calculated for a range
of penetration rates for each control technology - Final county- and state-level emissions
reductions calculated by determining fraction of
basin wells located in each county
26WRAP Phase II 2018 Emissions Projections
- Re-evaluate projected well count data from RMPs
and check older RMPs 2002 (or 2005) well count
accuracy - Convert EIA production-based data to well count
data by determining average production per well
by basin - Determine projected percentage of well count with
wellhead compression vs. lateral or central
compression - Obtain information from producers, future
forecasts, or state OGCs - Project to 2018 using 2005 base case and growth
factors - Calculate range of projected emissions based on
range of well counts or production report range
of estimates
27WRAP Phase II 2018 Emissions Projections
Controls Evaluation
- Recommend control strategy (-ies) in terms of
feasibility, emissions reductions and
cost-effectiveness - Incorporate control strategy (-ies) to determine
range of potential reductions in 2018 inventory
on a state-by-state basis - For basins in states outside areas of focus,
apply control factors to inventory including a
review of additional control technologies
implemented since previous inventory and any
control strategies in the works
28WRAP Phase II 2018 Point Source SO2 Emissions
- Objective is to revise existing Pechan report on
2018 SO2 emissions projections to incorporate
ENVIRON projection methodology and producers
information on growth forecasts and emissions
controls - Identify major SO2 point source emissions sources
in each state of interest - Obtain producer information on control strategy
effectiveness, implementation rate, timetable and
growth trends from 2002 2005 as well as for
2018 based on production forecasts - Conduct review of Title V Permits to determine
emissions with and without control technologies - Revise estimates of 2018 emissions
29Four Corners AQTFMitigation Assessment Modeling
Project
- Model air quality, visibility, deposition impacts
of air emissions in the Four Corners region - Evaluate impacts of alternative mitigation
strategies - Primary focus on impacts in Mesa Verde and
Weminuche Class I areas and surrounding Class II
areas
30Four Corners AQTF Modeling
- Use WRAP Phase II updated 2005 emissions as
base case inventory for oil gas area source
emissions - Use WRAP Phase II projected 2018 emissions
inventory - Model air quality effects of up to 5 mitigation
scenarios by source category
31