Methodology

Ozone (O3) is a colorless gas associated with smog or haze conditions.  Ozone is not a direct emission, but a secondary pollutant formed when precursor emissions, volatile organic compounds (VOCs), also known as hydrocarbons (HC), and oxides of nitrogen (NOx), react in the presence of sunlight.  Carbon monoxide (CO) is a colorless gas formed by the incomplete combustion of fuel.  Anywhere combustion takes place (i.e. industrial processes, home heating, vehicle engines, etc.) high concentrations of CO can develop.

As part of the Clean Air Act Amendments of 1990, federal officials grouped areas into air quality control regions (AQCR) based on Census Metropolitan Statistical Areas (CMSA) for the purpose of air quality planning.  In the SJTPO region, Atlantic and Cape May Counties were grouped into the Atlantic City AQCR.  Cumberland and Salem Counties, along with Burlington, Camden, Cumberland, Gloucester, and Mercer Counties, were included in New Jersey’s portion of the Philadelphia AQCR.  Both of these AQCR were designated as Non-attainment Areas for ozone.  However, in order to assist in the evaluation of air quality conformity in the SJTPO region, emission budgets for VOCs and NOx were established for the SJTPO region as a whole.  Two areas, Atlantic City and part of Penns Grove, are also now considered maintenance areas for CO.  For the purposes of evaluating CO emissions, budgets were established for all of Atlantic County and Salem County, which encompass the maintenance areas.

A combination of computer programs centered around MOBILE5a and PPAQ (Post Processor for Air Quality) were used to assess air quality in the SJTPO region.  MOBILE5a is a software package developed by the USEPA to calculate mobile source emissions.  PPAQ is a software package used to pre-format and post-format data to and from MOBILE5a.  It provides a linkage between MOBILE5a and the transportation model, the South Jersey Travel Demand Model (SJTDM). 

Emissions are calculated for three categories of pollutants: volatile organic compounds, oxides of nitrogen, and carbon monoxide. 

Test and Analysis Years

The first required analysis year, the anticipated milestone year under the upcoming Rate of Progress Plan, is 2002.  The next is the ozone attainment year, 2005, when tests for VOC and NOX are required.  The next year of concern is the CO budget year, 2007, when tests are required for CO only.  Since a full analysis is required only every 10 years, the 2007 CO tests may be done by interpolating between the results for analysis years.  This was done using the 2005 and 2015 runs.  The next analysis is for the year 2015 because it provides an interim year that is not more than 10 years from the 2005 analysis or from the Plan’s horizon year of 2025.  The Plan’s horizon is the last analysis year required.

 Applicable Tests and Budgets

The SJTPO region has emission budgets for all relevant pollutants, and as such, only budget tests are required to demonstrate conformity.  The SJTPO regional budgets anticipated under the State’s currently proposed Rate of Progress Plan State Implementation Plan (SIP) Revision were used for VOC and NOX tests.   These budgets reflect new vehicle registration data that SJTPO must now incorporate in its assessment.  Under the proposed SIP Revision, 17.49 tons per day of VOC and 33.02 tons per day of NOX are the budget levels for the year 2002.  For 2005 and later, 13.36 tons per day of VOC and 26.42 tons per day of NOX are the budget levels for the SJTPO region.  VOC and NOX budget levels corresponding to the analysis years of 2002, 2005, 2015 and 2025 are listed in Table 7-1 below.  The values correspond to emissions generated for a July weekday, the prescribed analysis day/period for the VOC and NOX emission testing in the SJTPO region.

Table 7 - 1 - Budgets for VOC and NOX (tons per day) for SJTPO

Budgets:

2002 (tons)

2005 (tons)

2015 (tons)

2025 (tons)

VOC

17.49

13.36

13.36

13.36

NOX

33.02

26.42

26.42

26.42

 *Budgets proposed December 31, 2000 – from Rate of Progress Plan SIP Revision.

CO budgets under the maintenance plan are evaluated at the county level to account for Atlantic City and part of Penns Grove maintenance areas.  For the year 1997, 80.38 tons per day of CO was the budget level established for Atlantic County.  For 2007, 59.13 tons of CO per day is the budget level.  In Salem County, the 1997 budget for CO was 41.50 tons per day.  The budgeted amount will fall to 31.33 tons per day in 2007.  CO budgets for 1997, 2007, 2015 and 2025 are listed in Table 7-2 below.  The test for CO was performed on a winter weekday.

Table 7- 2 - Budgets for CO (tons per day) for SJTPO

Maintenance Areas

Budgets:

2002 (tons)

2005 (tons)

2007 (tons)

2015 (tons)

2025 (tons)

Atlantic County

80.38

80.38

59.13

59.13

59.13

Salem County

41.50

41.50

31.11

31.11

31.11

*Budgets effective December 7, 1995 – from attainment demonstration and maintenance plan submitted June 9, 1995.

Planning Assumptions

The latest planning assumptions must be used in the conformity analysis.  Key elements utilized in the conformity assessment follow. 

·      Population & Employment

Population and employment forecasts (as endorsed by the SJTPO TAC on May 5, 2000) were used to forecast future year traffic conditions in the SJTPO area.  The assumptions for population and employment provide for three additional casinos, including the Borgata, but are lower than previously used.

·     Travel & Congestion

For all analysis years, VMT and VHT are calculated by the South Jersey Travel Demand Model.  Base year VMT was adjusted based on NJDOT’s Highway Performance Monitoring System (HPMS) estimates.  

·     Transit Operation Policy and Fare Changes

NJTRANSIT, the statewide public transportation agency, has not had a fare increase in over 10 years.  Transit ridership has continued to grow, providing a favorable effect on emissions.

·     Transportation Control Measures (TCMs)

Transportation Control Measures that were implemented in the region, as identified in previous SIPs, are included in the base network.  The current SIP does not include any Transportation Control Measures.  Therefore, neither the budgets nor the conformity analysis reflect any additional Transportation Control Measures.

Models and Inputs

There are several requirements for travel demand models for severe ozone areas.  They are:

·         General Model Requirements

·         Consistency with the Highway Performance Monitoring System (MPMS)

·         Vehicle Miles Traveled (VMT) estimates

·         Reasonable Methods to Estimate Off-Network VMT

·         Capacity and Volume Sensitive Speed and Delay Estimates

·         Consistency with SIP Emissions Modeling Assumptions

The South Jersey Travel Demand Model (SJTDM) was used along with PPAQ (Post Processor for Air Quality).  This model has been accepted and was used to establish the current 2005 budgets, as well as the proposed new budgets in the Rate of Progress Plan.  The latest emissions model for New Jersey (Mobile 5.0a_h) was used to prepare the proposed Rate of Progress budgets and was used for the conformity analysis.  The now available 1999 vehicle age and distribution data were used in the analysis process.  Since the current version of Mobile 5.0a_h does not go beyond 2020, conformity for 2025 was based on 2025 SJTDM/PPAQ outputs and Mobile 5.0a_h emission factors for 2020.

Control measures included reflect those used to prepare the proposed Rate of Progress budgets.  These include taking Tier 2/Low Sulfur credits for analysis years after 2004 when the program becomes effective.

Interagency Consultation

Requirements for interagency consultation were met primarily through an in-person meeting on conformity issues in the SJTPO region held on February 7, 2001.  An informal pre-meeting was also held on December 19, 2000.  Follow-up correspondence to the February 7th meeting completed the classification of exempt projects, which confirmed the list of projects for inclusion in the conformity analysis.  In addition, this chapter of the draft RTP will be distributed to the participating agencies and further consultation will be conducted if needed.

Public Involvement Procedure

This chapter of the draft RTP summarizes the conformity determination and is subject to a 30-day comment period, in accordance with the SJTPO Public Involvement Policy.  This will include extensive public notice, copies available for review, and a public meeting.  Any questions on technical backup will be addressed upon request to the SJTPO.

Projects Analyzed

Categories of projects analyzed for the conformity determination included all non-exempt projects that had a sufficiently defined design concept and scope and that could be modeled, including non-federal projects (usually from transportation authorities), as follows:

·     Most projects analyzed for the FY 2000 Conformity Update.  These included projects from the FY 2001-2005 Project Pool and many non-federal projects.  Differences reflected changes between this RTP and the previous one.

·     All additional non-exempt projects that could be modeled from the FY 2000-2006 Project Pool and Study and Development Program.

·     All additional expected non-exempt, non-federal projects that were identified through the Interagency Consultation process.

As agreed by the Interagency group, some projects were modeled even though they may not be regionally significant, as defined for conformity.  Regionally significant projects are the minimum that must be modeled, but including more provided a fuller perspective on emissions.  It also allowed agreement on the projects to be analyzed before the Interagency group could complete the difficult task of distinguishing which projects were regionally significant.  The list of projects included in the action scenarios by analysis year is in Attachment 1.

Table 7 - 3 - Regional Travel Summary

 

2000

2002 ACTION

2005 ACTION

2015 ACTION

2025 ACTION

Population

          552,146

          562,273

          578,550

          639,131

          702,203

Employment

          274,980

          279,606

          309,020

          331,713

          361,696

VMT Winter

     29,131,102

     29,985,731

     32,204,843

     36,824,356

     41,414,674

VHT Winter

          701,591

          722,502

          784,298

          907,497

       1,051,913

VMT Summer

     39,416,847

     40,354,430

     43,594,850

     48,695,072

     54,545,220

VHT Summer

       1,038,666

       1,082,473

       1,209,839

       1,376,725

       1,815,835