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.
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.
|
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
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 |