ATTACHMENT C.1 EXXONMOBIL INTERIM TRUCKING FOR SYU PHASED RESTART AIR QUALITY ANALYSIS

Similar documents
SYU LFC INTERIM TRUCKING DESCRIPTION

ExxonMobil SYU LFC Interim Trucking Industrial Risk Analysis

ExxonMobil SYU LFC Interim Trucking Industrial Risk Analysis

ATTACHMENT B.1 VICINITY MAP

LOADING OF ORGANIC LIQUID CARGO VESSELS. (Adopted 10/13/1992, revised 1/18/2001)

This rule shall apply to any stationary source which is a major source of regulated air pollutants or of hazardous air pollutants.

RULE LIQUEFIED PETROLEUM GAS TRANSFER OR DISPENSING (Adopted 1/13/2015)

WORKSHOP REPORT. No, the RICE NESHAP applies only to stationary engines as defined in 40 CFR

Metro and you, building together.

General Plan Approval and General Operating Permit BAQ-GPA/GP-5 and Proposed Exemption 38. Citizens Advisory Council Meeting March 19, 2013

SAN JOAQUIN VALLEY UNIFIED AIR POLLUTION CONTROL DISTRICT. Guideline for Expedited Application Review (GEAR) Oil Field Sump Replacement Tanks

3.1 Air Pollution Control Officer (APCO): as defined in Rule 1020 (Definitions).

ICAPCD RULE APPENDIX C

EPA Tier 4 and the Electric Power Industry

EPA TIER 4 AND THE ELECTRIC POWER INDUSTRY. Tim Cresswell Tier 4 Product Definition Manager Electric Power Division

The purpose of this rule is to limit VOC emissions from the transfer of organic liquids.

ON-ROAD HEAVY-DUTY TRUCK APPLICATION

Regulatory and Permitting Requirements of Stationary Generators In Delaware

RULE 4352 SOLID FUEL FIRED BOILERS, STEAM GENERATORS AND PROCESS HEATERS (Adopted September 14, 1994; Amended October 19, 1995; Amended May 18, 2006)

Review of the SMAQMD s Construction Mitigation Program Enhanced Exhaust Control Practices February 28, 2018, DRAFT for Outreach

ALLEGHENY COUNTY HEALTH DEPARTMENT AIR QUALITY PROGRAM

ALLEGHENY COUNTY HEALTH DEPARTMENT AIR QUALITY PROGRAM

ELECTRICAL GENERATING STEAM BOILERS, REPLACEMENT UNITS AND NEW UNITS (Adopted 1/18/94; Rev. Adopted & Effective 12/12/95)

(lb/day) Excavation and Installation. NO NO NO NO NO Emission calculations assume that all construction phases overlap.

Reducing Emissions from Marine Shipping Update on Local Initiatives. Santa Barbara Channel Shipping Lanes

Effective [one year after date of adoption] the provisions of this rule shall apply to:

Clean Air Construction Standard Draft for Public Comment November 5, 2018


Truck and Bus Regulation National Pavement Expo West

MARINE VESSEL REPOWER APPLICATION

H.1 Construction Emissions

Table Existing Traffic Conditions for Arterial Segments along Construction Access Route. Daily

MARAMA 2015 SCIENCE MEETING JULY 29-30, 2015 RICHMOND, VIRGINIA

DIESEL PARTICULATE MATTER MITIGATION PLAN FOR THE BNSF RAILROAD SAN DIEGO RAIL YARD

AUTHORITY TO CONSTRUCT

Prepared for: BP-Husky Refining LLC 4001 Cedar Point Road Oregon, Ohio Prepared by:

Facility Name: Chevron Products Company Doraville Terminal City: Doraville County: DeKalb AIRS #: Application #: 40411

1.1 Purpose of This Environmental Impact Report EIR Process Use of This Report Report Organization...

RULE BOILERS, STEAM GENERATORS, AND PROCESS HEATERS (Adopted 5/11/93, Revised 6/13/95, 6/13/00, 9/11/12)

Alternative 3 Air Quality and Climate Change Calculations

Evolution Of Tier 4 Regulations & Project Specific Diesel Engine Emissions Requirements

COST EFFECTIVENESS EVALUATION. A. Selective Catalytic Reduction System

Methods to Find the Cost-Effectiveness of Funding Air Quality Projects

The Need to Reduce Marine Shipping Emissions

The Village at Playa Vista. Appendix E-6. Alternative Analysis

Appendix E3 Emissions Worksheets UPDATED

Crude by Rail. Public Document. Air Permit Application. Valero Benicia Refinery Benicia, California. February

Texas Oil and Gas Emissions Inventory Improvement Projects

Impact of Transportation Emissions on New Jersey s Air Quality

STATE OF NEW JERSEY. ASSEMBLY, No th LEGISLATURE

DATE: MAY 3, 2007 ENVIRONMENTAL MANAGEMENT DIVISION

RULE 210 AND RULE 213 FEES FOR FISCAL YEAR July 1, 2017

RULE 326. STORAGE OF REACTIVE ORGANIC COMPOUND LIQUIDS. (Adopted 12/14/1993, revised 1/18/2001)

STATE IMPLEMENTATION PLAN CREDIT FOR EMISSION REDUCTIONS GENERATED THROUGH INCENTIVE PROGRAMS (Adopted June 20, 2013)

NARRATIVE. Dika Kuoh Steve Allison DATE: August 5, 2015

DRAFT AUTHORITY TO CONSTRUCT

RULE STATIONARY GAS TURBINES Adopted (Amended , ) INDEX

3. GENERAL CONDITIONS

RULE 412 STATIONARY INTERNAL COMBUSTION ENGINES LOCATED AT MAJOR STATIONARY SOURCES OF NO X Adopted INDEX

SAN JOAQUIN VALLEY UNIFIED AIR POLLUTION CONTROL DISTRICT DRAFT STAFF REPORT

BACT Determination Information

Construction Emissions Estimates ICTF Modernization Project Long Beach, California

San Joaquin Valley s. AIR POLLUTION CONTROL DISTRICT

Areas of the State not meeting Federal Air Quality Standards. Fleet Rule for Transit Agencies

4. No person shall install a coaxial Phase I vapor recovery system unless the system was certified by CARB after January 1, 1994.

California Environmental Protection Agency. Air Resources Board. Low Carbon Fuel Standard (LCFS) Update 2015 CRC LCA of Transportation Fuels Workshop

IAPH Tool Box for Port Clean Air Programs

Questions/Comments During Workshop

La Canada Flintridge Parents for Healthy Air November 1, 2018 Presented by Elizabeth Krider, Ph.D., Esther Kornfeld and Tamar Tujian

Attachment C: Benefit-Cost Analysis Spreadsheet

Pima Association of Governments Energy Programs Clean Cities

Appendix K. Final DOC Conditions

Emergency Episode Plan for Traffic Abatement

California s Success in Controlling Large Industrial Sources

Emission from gasoline powered vehicles are classified as 1. Exhaust emission 2. Crank case emission 3. Evaporative emission. Table 1.

LNG: Legal and regulatory framework. Canepa Monica World Maritime University

DIESEL TO DIESEL ENGINE REPOWER OPTION

Alternative Fuel Vehicle Program and Garbage Trucks

AND LIVESTOCK OPERATIONS

Industrial, Commercial and Institutional Boilers at Area Source Facilities (Boiler GACT) Final Reconsidered Rule Requirements Summary

Fleet Average NOx Emission Performance of 2004 Model Year Light-Duty Vehicles, Light-Duty Trucks and Medium-Duty Passenger Vehicles

AUTHORITY TO CONSTRUCT

Public Service Company of Colorado THE SOURCE TO WHICH THIS PERMIT APPLIES IS DESCRIBED AND LOCATED AS FOLLOWS:

Appendix C SIP Creditable Incentive-Based Emission Reductions Moderate Area Plan for the 2012 PM2.5 Standard

DRAFT April 9, STATE IMPLEMENTATION PLAN CREDIT FOR EMISSION REDUCTIONS GENERATED THROUGH INCENTIVE PROGRAMS (Adopted [adoption date])

AIR EMISSION PERMIT NO IS ISSUED TO. Northern Natural Gas Company

Middle Harbor Project: Draft EIS/EIR LA Chamber of Commerce June 26, 2008, APM Maersk HQ Pier 400

Bureau of Air Quality Technical Support Document General Permit GP-5 January 31, 2013

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C

NATURAL GAS TRANSMISSION

Air Quality Mandates Affecting the Caltrans Fleet Caltrans Division of Equipment Sacramento, CA June, 2009

MITIGATION LIST USS IOWA PROJECT ENVIRONMENTAL IMPACT REPORT (EIR)

U.S. EPA Finalizes Tier 2 Standards and Limits on Gasoline Sulfur

Air Quality Impacts of Advance Transit s Fixed Route Bus Service

Regulation No. 3 Changes For Internal Combustion Engines. Christine Hoefler November 14, 2012

DRAFT PERMIT TO OPERATE 5651-R6 EXXONMOBIL SYU PROJECT LAS FLORES CANYON OIL & GAS PLANT CALLE REAL, GOLETA SANTA BARBARA COUNTY, CA

TRANSFER OF ORGANIC COMPOUNDS INTO MOBILE TRANSPORT TANKS (Effect: 5/6/77: Rev. Effect. 7/26/00)

Emission Reduction Credit Availability/Cost/Efforts Taken in South Coast

PM2.5 (lb/day) PM2.5 (ton/yr) PM2.5 (lb/day)

Proposed Rule Amendment

Transcription:

ATTACHMENT C.1 EXXONMOBIL INTERIM TRUCKING FOR SYU PHASED RESTART AIR QUALITY ANALYSIS Revision 2 Page 1 of 7 January 2018

ExxonMobil Production Company, a division of Exxon Mobil Corporation (ExxonMobil or Applicant ) is requesting approval from the Santa Barbara County Planning and Development Department and the Santa Barbara County Air Pollution Control District (APCD) for the onsite construction and operation of the ExxonMobil Interim Trucking for Phased Restart (Interim Trucking) activities. These activities include installation of a crude truck loading facility at Las Flores Canyon, including associated piping and components, to allow transfer of product from LFC to crude transport trucks for delivery to local markets. The emissions from the LFC interim trucking include both stationary source emissions from the operation of the truck loading facilities at LFC and the mobile source emissions from operation of the crude transport trucks delivering the product to markets. Stationary Source At LFC, the LFC interim trucking operation will result in additional air emissions of Reactive Organic Compounds (ROCs) and respective greenhouse emissions expressed in carbon dioxide equivalents (CO2e). Emission sources include piping components necessary to transfer product, emissions occurring during the truck loading operations, and emissions from the transfer of truck vapors to the facility s vapor recovery system. In addition, since the Bureau of Safety and Environmental Enforcement (BSEE) requires Lease Automatic Custody Transfer (LACT) units be installed for royalty measurement determination, the fugitive component category includes the emissions from these components based on preliminary engineering information. The Interim Trucking facilities at LFC will include the following: 1. Installation of a truck rack at an existing previously disturbed pad at LFC just north of the Transportation Terminal (TT) [area designated as Truck Loading Area ]; 2. Installation of product transfer piping from a connection point in the TT to the Truck Loading Area to allow for the loading of trucks; 3. Installation of off-specification product transfer piping from the Truck Loading Area to a connection point in the TT to recycle product back to a crude storage tank; 4. Installation of vapor recovery piping from the Truck Loading Area to a connection point at the existing TT Vapor Recovery Compressor system to collect truck loading vapors. From the TT, the vapors will be routed to the Oil Treating Plant (OTP) and then to the Stripping Gas Treating Plant (SGTP) for compression, processing and use as fuel gas within the facility; 5. Installation of fuel gas piping from a connection point in the TT to the Truck Loading Area to automatically inject fuel gas into the vapor recovery system, as necessary, to reduce oxygen content to safe levels; Revision 2 Page 2 of 7 January 2018

6. Installation of associated piping and components as well as electrical and communication connections to support the Interim trucking activities; 7. Installation of four (4) LACT units at the Truck Loading Area for royalty measurement as required by BSEE; 8. Installation of an operator shelter at the Truck Loading Area; 9. Excavation for pipe supports, and containment and drainage grading, as required; 10. Paving of selected area, as required The emissions from the proposed loading operation are required to be controlled in accordance with the Best Available Control Technology (BACT) requirements defined in the APCD s rules pertaining to New Source Review. ExxonMobil will comply with this requirement by including a number of features during the truck loading operation to reduce or eliminate the release of hydrocarbons to the environment to the maximum extent practical as summarized below: - Conduct Crude Oil Motor Carrier Safety Survey of selected trucking companies prior to use; - Utilize low-leak transfer hose connections; - Automatically inject plant fuel gas into loading vapor recovery system to reduce oxygen content to safe levels; - Construct interconnecting piping (product, off-specification product, vapor, and fuel gas) with welded connections, wherever possible, and utilize low leak valves, wherever practical; - Control truck vapors generated during loading by connecting to loading vapor recovery line that enters existing Transportation Terminal (TT) vapor recovery compressor system (operates at -5 psig); - Transfer loading vapors with crude storage tank vapors to existing Oil Treating Plant (OTP) vapor recovery compressors for transfer to Stripping Gas Treating Plant (SGTP); - Control truck loading vapors by routing to the Stripping Gad Treating Plant (SGTP) for conversion to fuel gas for plant operations (reduces fuel gas purchased to operate facility equipment); - Include Interim Trucking piping, valves, and components in facility Leak Detection and Repair (LDAR) program; - Inspect truck transport trailers and connections prior to and after each loading to verify proper operation and no leaks; The Truck Loading Area will be designed to allow simultaneous loading of up to four (4) trucks at a time and up to eight (8) trucks in any hour. The Interim Trucking operations will be limited to a maximum of no more than seventy (70) trucks per day leaving LFC. Additionally, as the SYU stationary source has previously triggered the requirement to provide emission offsets under the APCD s New Source Review regulation, all future projects must provide emission offsets. ExxonMobil will provide offsets in the form of emission reduction Revision 2 Page 3 of 7 January 2018

credits (ERCs) for the stationary source emissions associated with the LFC interim trucking. The stationary source greenhouse gas emissions are not required to be offset. The estimated stationary source emissions from the LFC interim trucking are summarized below. The analysis utilizes a minimum overall 95% vapor recovery efficiency (APCD default) during truck loading and vapor transfer operations as directed by the APCD. Table C.1-1: Estimated Stationary Source Emissions ROC (TPY) ROC (lb/day) CO2e (MT/yr) Fugitive Hydrocarbon Components 10.65 58.38 44.8 ExxonMobil will work with the agencies with jurisdiction to appropriately mitigate the emissions associated with the LFC interim trucking to satisfy the compliance obligations as required by CEQA and the APCD. At this time, ExxonMobil proposes to purchase applicable SBC ERCs to provide to the APCD for the ROC emission increases. Revision 2 Page 4 of 7 January 2018

Mobile Source The LFC interim trucking will result in mobile emission from the exhaust gases generated during operation of the crude transport truck engines. These mobile sources include air emissions of criteria pollutants (Nitrogen Oxides (NOx), Reactive Organic Compounds (ROC), Carbon Monoxide (CO), Sulfur Oxides (SO2), and Particulate Matter (PM)) and greenhouse gas (GHG) emissions expressed in CO2e. Mobile source emissions are determined using the following factors: number of trucks per day transporting product to the unloading facility, distance each truck travels to and from unloading facility, number of trucks in fleet, and truck engine emissions based on T7 Tractor vehicle category utilizing emission rate data approach. The calculations assume that each truck returns to LFC after unloading at the designated facility to re-load. In order to reduce emissions, ExxonMobil will require the trucking contractor to restrict trucks to only those that have a 2017 or newer model-year engine. The engine emissions are based on EMFAC2014 criteria pollutant and CO2 emission factors for on-road vehicles per the California Air Resources Board s EMFAC2014 Web Database. Emissions were estimated for 2018 in Santa Barbara County for vehicle model years- 2017, 2018, 2019, with vehicle speeds aggregated. The Vehicle Category is based on EMFAC2011 vehicle definitions, applying the T7 Tractor vehicle type for both running exhaust and idle exhaust, as directed by the SBC APCD. The EMFAC2014 particulate matter emission factors are supplemented with US EPA factors for on-road vehicle paved road dust entrainment. Two truck transport scenarios are provided to cover the most likely operating situations. In Scenario 1, all of the trucks (70 per day) will load product at LFC and travel to the P66 Santa Maria Terminal for unloading. All of the trucks are assumed to return to LFC for re-loading. In Scenario 2, 68 trucks per day will load product at LFC and travel to the Plains Pentland Terminal for unloading. All of the trucks are assumed to return to LFC for re-loading. On any particular day some portion of the total truck trips may go to P66 Santa Maria Terminal with the remainder going to Plains Pentland Terminal. Note the estimated mobile source emissions associated with travel to the Plains Pentland Terminal incorporate the requirement to include both in-county and out-of-county truck travel emissions to account for the full impact of the project under CEQA. Since the P66 Santa Maria Terminal is located within Santa Barbara County, no out of county mobile source emission evaluation is necessary. The estimated mobile source emissions for the project are summarized in the table below. The table provides both the total truck travel emissions in all counties (SBC/SLO/Kern) as well as the emissions in only Santa Barbara County. Under CEQA, the total mobile source emissions including both in-county and out-of-county truck travel emissions will be evaluated and compared to the SBC mobile emissions significance thresholds. Revision 2 Page 5 of 7 January 2018

Based on the estimated emissions, both the NOx daily significance threshold of 25 lb/day (mobile emissions) and the GHG annual significance threshold of 1,000 MT/yr of CO2e will be exceeded. ExxonMobil will work with the agencies with jurisdiction to appropriately mitigate the emissions associated with the LFC interim trucking to satisfy the compliance obligations as required by CEQA and the APCD. Table: C.1-2: Estimated Mobile Source Emissions Criteria Pollutants ROC NOx PM 10 CO SO2 CO2e Scenario 1 Total Trips Emissions 0.91 13.33 10.05 5.33 0.23 SBC Only Trip Emissions 0.91 13.33 10.05 5.33 0.23 MT/Yr Total Trip Emissions (Tons/Yr) 0.16 2.33 1.83 0.96 0.04 4.38k Scenario 2 Total Trips Emissions 2.25 32.51 25.13 13.23 0.57 SBC Trip Emissions 0.93 13.65 10.30 5.47 0.23 Total Trip Emissions (Tons/Yr) 0.41 5.83 4.59 2.40 0.10 10.95k Note: Emissions based on 70 trucks per day for Scenario 1 and 68 trucks per day for Scenario 2 Stationary and Mobile Sources Combined Combined stationary and mobile emissions are summarized in the table below. The ROC combined emissions exceed the CEQA significance threshold of 55 lbs/day. However, these emissions would be mitigated below the significance threshold after emission reduction credit offsets provided to the APCD for the stationary source are applied. Likewise, the GHG combined emissions exceed the CEQA significance threshold of 1,000 MT CO2e/yr. These emissions will likely be mitigated through Cap and Trade credits and potentially an appropriate project. ExxonMobil will work with the agencies with jurisdiction to appropriately mitigate the emissions (e.g., NOx, GHG) associated with the LFC interim trucking to satisfy the compliance obligations as required by CEQA and the APCD. Revision 2 Page 6 of 7 January 2018

Table C.1-3: Combined Stationary and Mobile Source Emissions Criteria Pollutants ROC NOx PM 10 CO SO2 CO2e Scenario 1 Daily Stationary Source Emissions Daily Mobile Source Emissions Daily Stationary + Mobile Source Emissions MT/Yr 58.38 0 0 0 0 44.8 0.91 13.33 10.05 5.33 0.23 4.38k 59.29 13.33 10.05 5.33 0.23 4.42k Scenario 2 Daily Stationary Source Emissions Daily Mobile Source Emissions Daily Stationary + Mobile Source Emissions 58.38 0 0 0 0 44.8 2.25 32.51 25.13 13.23 0.57 10.95k 60.63 32.51 25.13 13.23 0.57 10.99k Note: Stationary source emissions based on 70 trucks per day for Scenario 1 and 2. Mobile source emissions based on 70 trucks/day for Scenario 1 and 68 trucks per day for Scenario 2. Revision 2 Page 7 of 7 January 2018