Upload
all4-inc
View
778
Download
3
Tags:
Embed Size (px)
DESCRIPTION
Citation preview
What YOU Need to Know About the 1-hour NAAQS Implementation Process
Dan P. DixColin T. McCall
November 17, 2011
An All4 Inc. Webinar
Brought to you by EnviroReviewTM
2
3
Agenda Summary of NAAQS NAAQS Implementation Updates Dispersion Modeling Basics and
Inputs NAAQS Modeling Demonstration
Approach
4
About ALL4 Environmental consulting firm Founded 2002 – currently 30+ employees Offices in Kimberton, PA and Columbus, GA Specialize in air quality consulting:
• Complex air permitting and strategy development
• Air dispersion modeling• Ambient air quality monitoring
Dispersion modeling as a company-wide initiative
www.all4inc.com
National Ambient Air Quality
Standards (NAAQS)
6
NAAQS Background “Backdrop” of the Clean Air Act States design their SIPs and enforce
and implement their regulations to meet the NAAQS
Air quality construction permit programs are designed around NAAQS compliance• PSD: Maintaining NAAQS attainment• NNSR: Getting into NAAQS attainment
NAAQS reevaluated every 5 years
7
NAAQS SummaryPollutant Averaging Period
Historic NAAQS (µg/m3)
Revised NAAQS (µg/m3)
CO1-Hour 40,000 40,0008-Hour 10,000 10,000
Ozone 8-Hour 75 ppb WithdrawnPb 3-Month Rolling 1.5 0.15
PM10 24-Hour 150 150
PM2.5
24-Hour 65 35Annual 15 15
NO2
1-Hour N/A 188Annual 100 100
SO2
1-Hour N/A 1963-Hour 1,300 1,300
24-hour 365 Revoked
Annual 80 Revoked
8
Attainment/Nonattainment Designations
U.S. EPA philosophy on the SO2 NAAQS implementation process:• Proposed NAAQS – designations based
on ambient monitoring data• Final NAAQS – designations based
primarily on air quality modeling data Shift to reliance on air quality
modeling will become a critical issue for individual facilities
NAAQS Implementation
Updates
10
SO2 NAAQS Implementation NAAQS Implementation Schedule:
• June 2011: Initial state nonattainment recommendations to U.S. EPA (most counties were “unclassifiable”)
• June 2012: EPA to finalize attainment status (most states will still be “unclassifiable” or attainment)
• June 2013: Maintenance SIP submittals including individual facility modeling to achieve compliance with the NAAQS (including air quality modeling for individual facilities)
• August 2017: Full NAAQS compliance in all areas
11
SO2 NAAQS Monitoring Data
12
Implementation Update Guidance for states to evaluate
designations using AERMOD was released on September 22, 2011
Most states are currently reviewing the U.S. EPA guidance and crafting their plans
States need to decide:• Modeling now for nonattainment
designations• Model after June 2012 for the June 2013
maintenance SIP States or facilities conducting modeling?
13
SO2 Maintenance SIP Submittals
U.S. EPA: Revising PSD/NNSR programs to include new NAAQS is not sufficient. Five components are required:• “Attainment Emission Inventory”• Maintenance Demonstration• Control Strategy• Contingency Plan• Verification of Continued Attainment
Maintenance SIP will list enforceable 1-hour emission limits (August 2017)
14
SO2 NAAQS Implementation State SIPs will be based on AERMOD
dispersion modeling for the following individual facilities (by order of priority):• SO2 Actual Emissions > 100 tons per year
• SO2 PTE > 100 tons per year• Smaller facilities “with a potential to
cause or contribute” to a NAAQS violation States are considering other options based
on population
15
SO2 NAAQS Implementation Legal challenges ongoing:
• Science behind NAAQS levels• Approach of using modeling
Under the current approach, if states don’t perform modeling, U.S. EPA will
Dispersion Modeling Basics
and Inputs
17
AERMOD Process
Hourly Wind Speed
Hourly Wind Direction
Hourly Ambient Temperature
Land Use PatternsTopography
Building DimensionsStack DimensionsExhaust Velocity
Exhaust Temperature
Emission Rates
Predicted Ground Level Ambient Concentrations (µg/m3) for all
averaging times
18
Air Quality Modeling Steps
1. Emission Inventory2. Meteorological Data
(AERMET/AERSURFACE)3. Terrain Data (AERMAP)4. Building Downwash (BPIPPRM)
19
Emission Inventories Short-term (1-hour) emission rates Potential to be used as permit limits Intermittent emission units (e.g., emergency
generators, intermittent emission scenarios such as startup/shutdown operations or alternative fuels)• Latest guidance indicates following form of
standard as guideline for what to include (i.e., 99th percentile (4th highest))
Stack characteristics (height, temperature, velocity, diameter, location)
20
Meteorological Data
21
Meteorological Data 5 years of National Weather Service data Minimum of 1 year of onsite data Surface characteristics and topography
surrounding the facility should be similar to (representative of) those surrounding the meteorological station
If no representative meteorological data are available, SO2 implementation guidance suggests possibility of using AERSCREEN (with agency approval)
22
Terrain Data “Ambient Air”
Public access must be restricted in some way (e.g., fence, security guard) in order for onsite receptors to be disregarded in the modeling analysis
23
Building Downwash
24
Building Downwash
NAAQS Modeling Demonstration
Approach
26
Full NAAQS Evaluation Includes facility and other local
facilities Any modeled emission rates should
be acceptable as a 1-hour permit limit with the appropriate margin for compliance
Considerations for accounting for emissions during startup and shutdown
Emergency unit considerations
27
Modeled Emission Rate Examples
Combination Boiler SO2 modeling:• Bark: > 97% of the annual heat input to the
boiler• Boiler fires 3% sulfur residual oil as a backup
fuel• Annual NAAQS modeling: 0.025 lb/MMBtu x
Annual Heat Input• 1-hour NAAQS modeling: 3.14 lb/MMBtu at the
oil firing capacity of the boiler Do we have the appropriate
exhaust information (e.g., temperature, flowrate) to model the oil firing scenario?
28
Modeled Emission Rate Examples
Power Boiler SO2 Modeling:• Fires fuel oil and natural gas• Current emission limit: 24-hour limit;
compliance demonstrated using a CEMS• Evaluate the impact of using the 24-hour
emission limit as a modeled 1-hour emission rate
• One year of CEMS data: rare hourly exceedances of the 24-hour limit, but they do occur
• Operations need to be managed more tightly to ensure compliance with a 1-hour limit, flexibility is lost
29
Modeled Emission Rate Examples
Low-Odor Recovery Furnace:• Typical operations: < 5 ppm SO2 during black
liquor solids firing• Startup scenario: 2% sulfur fuel oil• Do we need to account for startup
emissions and exhaust characteristics of the recovery furnace?
• U.S. EPA has given states flexibility; decision will depend on the state agency
• No bright line for the annual startup/shutdown duration that is said to significantly contribute to the distribution of 1-hour daily maximum concentrations
30
Local Sources NAAQS evaluation must include
sources that result in a “significant concentration gradient” in the vicinity of the facility
Same emission rate considerations apply for local sources (although permit limit concerns wouldn’t apply)
State agency typically dictates which local sources to include in evaluation
31
NAAQS Modeling Strategy Start with an evaluation of each
individual emission source Each source will have different
factors that drive resulting ambient concentrations
The cumulative ambient concentration from all sources (plus background) will be evaluated against the NAAQS
Evaluate each source against the NAAQS as a first step
32
NAAQS Modeling Strategy Big picture factors that will drive
ambient concentrations for individual sources:• Elevated emission rates• Stack velocity (orientation of release
and flowrate)• Stack temperature (plume buoyancy)• Stack height versus surrounding terrain• Surrounding buildings and structures
(i.e., building downwash)
33
Hypothetical Modeling Example
Modeling of a hypothetical facility with the following SO2 emission sources:• Process SO2 source
• Fuel oil combustion SO2 source• Backup engine source
NAAQS modeling evaluation is based on SO2 potential-to-emit
34
Hypothetical Facility Terrain
35
“Process” SO2 Source SO2 Emission Rate: 240 lb/hr (CEMS) Stack Height: 290 feet Stack Diameter: 16.5 feet Exhaust Temp: 350 °F Exhaust Flow: 230,000 acfm Elevated emission rate, buoyant
source, tall stack (taller than the tallest buildings at the facility)
36
Process SO2 Source Impacts
37
Process SO2 Source Impacts Highest impacts in complex terrain far
from facility Wind speed doesn’t match location of
elevated concentrations Impacts occur during periods of
atmospheric stability and low mixing heights (typically early morning, low wind speed conditions)
High concentrations due partially to the limitations of the AERMOD dispersion model
38
Combustion SO2 Source SO2 Emission Rate: 20 lb/hr (AP-42) Stack Height: 60 feet Stack Diameter: 2 feet Exhaust Temp: 225 °F Exhaust Flow: 16,000 acfm Buoyant source, short stack (shorter
than the tallest buildings at the facility)
39
Combustion SO2 Source Impacts
40
Combustion SO2 Source Impacts
Elevated concentrations are closer to the facility
Building downwash effects have a noticeable impact on ambient concentrations
41
Engine SO2 Source SO2 Emission Rate: 3 lb/hr (Vendor) Stack Height: 10 feet Stack Diameter: 1.3 feet Exhaust Temp: 935 °F Exhaust Flow: Horizontal Discharge Horizontal discharge, short stack
42
Engine SO2 Source Impacts
43
Engine SO2 Source Impacts Elevated ambient concentrations at
the facility fenceline for two reasons:• Low stack height (10 feet)• No plume buoyancy due to horizontal
discharge Ambient air considerations become
very important (i.e., public access)
44
Modeling Refinements “Process” SO2 Emission Source:
• Stack height increase is technically and economically infeasible
• Raw materials are fixed due to product and consumer demand
• Upgrades to the scrubber could achieve control: ~30% more control (~170 lb/hr)
45
Process SO2 Source Impacts (Before)
46
Process SO2 Source Impacts (After)
47
Modeling Refinements Combustion SO2 Emission Source:
• Stack height increase is technically and economically infeasible
• Fuel oil firing is desirable due to cost savings considerations
• Raw materials to the source bring inherent scrubbing capacity: 50 to 65% based on previous studies
• 50% inherent scrubbing brings emission rate to 10 lb/hr (justify through testing)
48
Combustion SO2 Source Impacts (Before)
49
Combustion SO2 Source Impacts (After)
50
Modeling Refinements Engine SO2 Emission Source:
• Simplest fix is to change the stack discharge orientation from horizontal to vertical
• No changes to the vendor-guaranteed emission rate of the engine
51
Engine SO2 Source Impacts (Before)
52
Engine SO2 Source Impacts (After)
53
Cumulative Concentrations The facility must cumulatively
comply with the NAAQS Addressing each individual source
helps as a first cut This scenario still exceeds the 1-hour
NAAQS for SO2 when the sources are taken cumulatively
Haven’t even considered ambient background concentrations
54
Modeling Strategies Emissions Strategies Actual Distribution of Emissions
• Evaluate adequacy of emission limits• Evaluate emissions control options• Evaluate alternate fuels and fuel
specifications Facility Fence Line Strategies
55
Modeling Strategies Stack/Exhaust Strategies:
• Combined source exhausts• Co-located exhaust points to
increase buoyancy• Turn horizontal stacks vertical• Increase stack heights
56
Modeling Strategies Temporal pairing approach Plume transport time Surrounding surface
characteristics Wind speed monitor thresholds Mechanical mixing height
considerations Alternative models (e.g.,
CALPUFF)
57
Final Thoughts States developing their modeling plans now States will reach out to request information
and/or modeling Be involved with the SIP process:
• Provide states with good information• Conduct your own modeling (either for
the state or in parallel with the state) Avoid surprises (new limits) at the end of
the SIP process
58
We will follow up with questions submitted during the presentation that were not answered
Please feel free to e-mail or call us with additional questions and we will follow up with you
Questions?
59
Questions?
Dan [email protected](610) 933-5246 x182393 Kimberton RoadPO Box 299Kimberton, PA 19442
All4 Inc.www.all4inc.com
www.enviroreview.com
Colin McCall
[email protected](706) 221-7688 x14
5900 River RoadSuite 500
Columbus, GA 31904