Title: Roseville Rail Yard Mitigation and Monitoring
1Roseville Rail Yard Mitigation
and Monitoring
Meredith Kurpius EPA Region 9 January 24, 2008
2Outline
- Background
- Risk Assessment
- Monitoring
- Mitigation Measures
3Background on Rail Yard
- J.R. Davis Rail Yard
- In operation since 1905
- Located in Roseville, CA (15 miles east of
Sacramento) - Operated by Union Pacific (UP) Railroad
- The largest classification yard operated by Union
Pacific west of the Mississippi
4Recent Concerns
- Rail yard expansion in 1996
- Citizen complaints regarding odors and air toxics
- Placer County APCD concerns about diesel PM and
its impact on public health
5Setting of Roseville Rail Yard
- About 4 miles long
- Oriented in northeast-southwest direction
- Approx. 31,000 locomotives stop at facility each
year (additional 15,000 trains passed through on
northside tracks) - 98 of UPRRs Northern CA traffic moves through
the facility - Maintenance, service and classification yard
(24/7 operation)
6Layout of Roseville Rail Yard
7Risk Assessment Contribution of Diesel PM by
Area and Activity
8CARB Modeling Results
9Layout of Roseville Rail Yard
Areas of highest risk
service yard
hump-trip
10Roseville RY Service Yard
11Agreement Between UP and Placer County APCD (2004)
- Mitigation Plan
- -reduce additional 10 of DPM emissions from
rail yard 2005-2007 - -UPRR indicated they had reduced emissions by
15 since the - initiation of the Risk Assessment in 2000
(25 total reduction) - Grant Program
- -provide grants at least 150,000 between
2005-2007 to achieve one - ton DPM emissions reduction from other
sources of background - emissions in Roseville area
- Monitoring Plan
- -provide at least 100,000 to monitor DPM
emissions from the rail - yard
12Air Monitoring Project Objectives
- Determine, through monitoring, localized air
pollutant impacts from the UPRR facility - Verify effectiveness of mitigation measures over
time - Improve accuracy of future modeling analyses
- Provide feedback to the public
13Air Monitoring Sites
- Denio-Pool
- Next to service yard
- Denio Downwind (dirty)
- Pool Upwind (clean)
- Church-Vernon
- Next to hump/trim
- Church Downwind
- Vernon Upwind
14Air Monitoring Measurements
- Nighttime sampling from 10pm to 5am to optimize
upwind/downwind pairing - PM2.5
- Manual FRM (both 7 hour and 24 hour samples)
- Continuous BAM
- NO
- NOx
- Black carbon
15Air Monitoring ResultsBlack Carbon
16Air Monitoring ResultsPM2.5
17Air Monitoring ResultsNO
18Air Monitoring ResultsNOx
19Additional Placer County-EPA Analysis of Size
resolved Aerosols, summer, 2005
- Diesel exhaust was characteristic of idling
engines - Confirms the prior ARB estimates 2004
- Supports the UPRR installation of anti idling
protocols and hardware - Diesel concentrations were in good agreement with
prior ARB estimates - Confirms the ARB/OEHHA modeled risk factors in
the 2004 report - Nighttime enhancements of sulfur similar to RRAMP
nighttime NO data
20Additional Placer County-EPA Analysis of Size
resolved Aerosols, summer, 2005
- Most of the fine organic matter seen at the Denio
site was regional and natural, not from rail yard
operations - The PAH concentrations, on the other hand, were
rail yard associated - PAHs occurred primarily in the ultrafine (lt 0.1
?m) size mode, leading to both high lung
deposition and new options for mitigation - Heavy PAHs were higher in molecular weight, and
thus more toxic, than diesel truck data
21Molecular weight of rail yard diesel PAHs versus
truck PAHs
Mass of benzoapyrene
22Main Mitigation Strategies
- Idling reductions
- -hardware (Smart Start Technology)
- -operations/policy
- Low-sulfur diesel fuel for intrastate switchers
and locomotives - Switcher fleet replacement/upgrade
- Emission control from service test repair area
(e.g., HOOD project)
23HOOD Project
- ALECS Advanced Locomotive Emission Control
Systems - Demonstration that a single set of emissions
control equipment in an exhaust stack could
simultaneously treat up to 10 stationary
locomotives (idling or undergoing testing) - PM, NOx, SOx and VOC reductions
24Concept of ALECS at Service Test and Repair Area
25Bonnet Pre-Docking
26Locomotive Test Setup
27Demonstration Test Construction
Emissions Control Subsystem deployed in Roseville
28HOOD Test Observations
- Accomplished significant cleanup of NOx and PM
- NOx control exceeded expectations (gt95)
- PM control looks to be a little less than
expected (lt99) - Sound reduction about 7 dB
- Emissions control equipment performed reliably
- Bonnet and ducting worked, but design improvement
needed to be more robust - Some control aspects need improvement
-
29Stay Tuned
- Mitigation measures still being implemented
- Discussions underway about permanent installation
of HOOD system at UPRR - Trend analysis with 3 years of monitoring data
- Additional year of monitoring this summer
- HOOD system went to Long Beach for maritime
application - Need more info?
- Contact Meredith Kurpius, 415-947-4534,
kurpius.meredith_at_epa.gov
30(No Transcript)
31 32RRAMP Monitoring Strategy
- Utilize two pairs of upwind/downwind site
locations - Minimize non-UPRR emissions sources between each
pair - Optimize pair orientation to the prevailing wind
direction - Optimize time of year with predominance of
prevailing wind summer months - Utilize continuous monitors, including
aethalometers, to select those periods of time
when wind blows from upwind to downwind
33RRAMP Project Duration
- 3 Years (2005-2007)
- Coincides with implementation of mitigation
measures from UP/PCAPCD agreement - Could extend beyond 2007
- Main sampling program during 2-3 month period
each year - Some monitors may remain year-round
- Main field program began August 2005
34Diurnal Considerations
- Emissions from Rail Yard fairly constant
throughout the day/night.
35 Diurnal Considerations Nighttime Wind Rose for
Roseville June-July
Persistent winds at night
36HOOD Testing Completed
- Testing conducted Sept. 7, 2006 through Sept 20,
2006 - Testing performed by Engine, Fuel, and Emissions
Engineering, Inc. - CARB and South Coast AQMD also conducted testing.