# VISTAS’ Common Modeling Protocol 

# 42 

# CALPUFF input file. The advantage of selecting a smaller CALPUFF computational domain in

the regional CALPUFF simulations is that CALPUFF run time is proportional to the numb er and

residence time of the puffs on the domain (and other factors such as the number of receptors and

the internal time step computed by the model). A CALPUFF domain covering an area 300 km

from a source in all directions would involve only 50 x 50 12

- k m grid cells, which will require

modest computational resources.

CALMET output files for the VISTAS regional domain shown in Figure 4

- 2 will be provided to

VISTAS by Earth Tech. These files will be in CALPUFF

- ready format, and as such, no

CALMET user inpu ts will be required. An option in CALMET allows finer grid CALMET input

files to be calculated from the 12

- km CALMET files.

The basic characteristics of the CALMET, CALPUFF and CALPOST configurations for the

initial analyses are listed below.

CALMET Model ing Configuration (12

- km initial exemption modeling)

The CALMET model configuration for the regional CALMET simulations will be defined by

Earth Tech in collaboration with the VISTAS States. The basic model configuration will follow

the recommended IWAQM guidance (EPA, 1998; Pages A

- 1 through A

- 6), except as noted

below.

The basic features of the modeling simulation are the following:

- Modeling period: 3 years (2001

- 2003)

- Meteorological inputs: MM5 data provide initial guess fields in CALMET

- CALMET grid resolution: 12

- km (same Lambert Conformal coordinate system and grid

cells as the 12

- km 2001/2002 MM5 simulations)

- CALMET vertical layers: 10 layers. Cell face heights (meters): 0, 20, 40, 80, 160, 320,

640, 1200, 2000, 3000, 4000.

- CALM ET mode: No

- Observations mode including option to read overwater data directly

from MM5.

- Diagnostic options: IWAQM default values, except as follows: diagnostic terrain

blocking and slope flow algorithms used for 2003 simulations (using 36

- km MM5 dat a), but

no diagnostic terrain adjustments in 2001 and 2002 simulation (using 12

- km MM5 data)

- CALMET options dealing with radius of influence parameters (R1, R2, RMAX1, RMAX2,

RMAX3), BIAS, ICALM parameters are not used in No

- Observations mode.

# VISTAS’ Common Modeling Protocol 

# 43 

# - TERR AD (terrain scale) is required for runs with diagnostic terrain adjustments (i.e., the

2003 simulations). Values of ~10

- 20 km will be tested, and an appropriate value

determined.

- Land use defining water: JWAT1 = 55, JWAT2 = 55 (large bodies of water). This feature

allows the temperature field over large bodies of water such as the Atlantic Ocean and the

Great lakes to be properly characterized by buoy observations.

- Mixing height averaging parameter (MNMDAV) will be determined by Earth Tech for the

r egional simulations based on sensitivity tests. The purpose of the testing is to optimize the

variable to allow spatial variability in the mixing height field, but without excessive noise.

- Geophysical data for regional runs: SRTM

- GTOPO30 30

- arcsec terr ain data, Composite

Theme Grid (CTG) USGS 200m land use dataset. References for these and other CALMET

datasets can be found on the CALPUFF data page of the official CALPUFF site

( www.src.com ).

CALPUFF Modeling Configu ration (Initial exemption modeling)

The CALPUFF model configuration for the regional CALPUFF initial simulations will follow the

recommended IWAQM guidance (EPA, 1998; Pages B

- 1 through B

- 8), except as noted below:

- CALPUFF domain configured to include the source and all Class I areas within 300km of

the source plus 50km buffer zone in each direction. CALPUFF is recommended for all

source

- receptor distances to be considered in the BART analyses.

- Chemical mechanism : MESOPUFF II module

- Species modele d : SO 2 

# , SO 4 

# , NO

x 

# , HNO 3 

# , NO 3 

# and particulate matter in size categories of

<0.625 μ m, 0.625

- 1.0 μ m, 1.0

- 1.25 μ m, 1.25

- 2.5 μ m, 2.5

- 6.0 μ m and 6

- 10 μ m aerodynamic

diameters. As noted below, the particulate matter emissions by size category will be

combined in to the appropriate species for the visibility analysis (i.e., elemental carbon (EC),

fine PM or “soil” (< 2.5 μ m in diameter), coarse PM (between 2.5

- 10 μ m in diameter) and

organics (called secondary organic aerosols (SOA) in the CALPOST postprocessor).

- Emission rates for modeling based on EPA BART guidance, i.e., maximum 24

- hour actual

emission rate with normal operations from the highest emitting day of the meteorological

period modeled (excluding days where start

- up, shutdown or malfunctions occurred

s ometime during the day.) Note that potential emissions are used to determine if a source is

BART

- eligible, but 24

- hour average maximum emissions are used for modeling purposes

(70 FR 39162). Pollutants considered include SO 2 

# , H 2 

# SO 4 

# , NO

x 

# and PM 10



# .

Conde nsable emissions are considered as primary fine particulate matter and allocated

equally to the two submicrometer

- particle size classes. If actual source emissions data are

not available, the modeling should be based on permit limits. If source

- specific size

# VISTAS’ Common Modeling Protocol 

# 44 

# categories are not available, then AP

- 42 factors may be used for sources where AP

- 42

factors are available. For sources where AP

- 42 factors are not available, alternative

approaches to speciation are given below.

Excluded from the modeling are pollu tants with plant

- wide emissions less than de minimis

levels (40 tons per year for SO 2 

# and NO

x 

# and 15 tons per year for PM 10 

# ). De minimis levels

are plant wide for each visibility

- impairing pollutant, so individual units may be modeled

even if they have emi ssions below de minimis if the plant total is greater than de minimis

.

- Particulate emissions speciation : Break down, as appropriate, filterable and condensable

particulate matter into the following species categories: elemental carbon (soot), “soil” (fi ne

PM < 2.5 μ m diameter), coarse particulate matter (2.5

- 10 μ m diameter) and organics. The

process is illustrated in Figure 4

- 3. If source

- specific speciated emissions factors are not

available, AP

- 42 factors or speciation information developed by the Nati onal Park Service

( http://www2.nature.nps.gov/air/permits/ect/index.cfm ) can be used to estimate the PM

speciation for many source sectors.

Figure 4

- 3. Speciation of PM

- 10 Emissio ns. (PMC is coarse particulate matter

-- 2.5 to 10 μ m

diameter.) PM

- 10

Filterable Condensabl e

EC PM

- 2.5 PMC PM

(including

H 2 

# SO 4 

# )

As Prim. 

# SO4) 

# Organic PM

(SOA)

EC Soil PMC SO 4



# f(RH) Non

- SO 4 

# Inorganic OC

# VISTAS’ Common Modeling Protocol 

# 45 

# Otherwise, assumptions will need to be proposed by the source, and reviewed and approved

by the State. Possible acceptable alternative approaches to estimating speciation include the

follow ing:

 Speciation profiles developed by the SMOKE emissions model for use in

VISTAS’ CMAQ regional air quality modeling (available at http://www.vistas

sesarm.org/BART/calpuff.asp ).

 The approach described in a memo available at http://www.vistas

sesarm.org/BART/calpuff.asp , which provides reasonably conservative estimates

in situations where data are incomplete.

- Class I receptors : Us e FLM Class I receptor list with receptor elevations provided

(available from the NPS).

- CALPUFF model options : Use IWAQM (EPA, 1998) default guidance, including

Pasquill

- Gifford dispersion coefficients.

- Ozone dataset

– use observed ozone data for 200 1

- 2003 from CASTNet and AIRS stations.

Only non

- urban ozone stations should be used in the OZONE.DAT file. Monthly average

ozone (backup) background values are to be computed based on daytime average ozone

concentrations from the OZONE.DAT file (6am

- 6pm average ozone concentrations

computed by month).

- Background ammonia concentration: In CALPUFF, use constant (0.5 ppb) value for

ammonia.

- Puff representation: integrated puff sampling methodology.

- Building downwash: Ignore building downwash unle ss source is within 50

- km of a Class I

area and the State instructs the source to specifically consider building downwash.

CALPOST and POSTUTIL Configuration (Initial exemption modeling)

- Use Visibility Method 6 in CALPOST

- Species considered in visibil ity analysis: SO 4 

# , NO 3 

# , EC, SOA (i.e., condensable organic

emissions), soil, coarse PM

- Natural background light extinction: Several options are acceptable at the discretion of the

State: (1) A single annual average natural background extinction for each Class I area, as

presented in Appendix B of EPA’s natural conditions guidance (EPA, 2003b); (2) A single

value that represents the average haze index on the 20% best natural conditions days, again

as presented in the same Appendix B; or (3) A monthly aver age natural background as

calculated by CALPOST under Method 6, based on annual average default natural

# VISTAS’ Common Modeling Protocol 

# 46 

# conditions component concentrations and monthly average f(RH) values for the centroid of

the Class I area, from Table A

- 3 in the natural conditions guid ance document,.

A special procedure is needed for options 1 and 2, since CALPOST requires input of natural

background concentrations of PM components while the backgrounds for options 1 and 2

are expressed in EPA’s guidance document as extinction coeffici ents or haze indices (in

deciviews). In order to produce the appropriate natural background in CALPOST for these

options, use Equation 3

- 2 to calculate the extinction coefficient that corresponds to EPA’s

haze index value for the Class I area (if necessar y), subtract the Rayleigh scattering value of

10 Mm - 1 

# , and enter a soil concentration (in μ g/m 3 

# ) into CALPOST that is numerically equal

to this result. (Since the extinction efficiency of soil is 1 m 2 

# /g, Equation 3

- 1 shows that this

process produces a back ground extinction that equals the EPA’s value.) Leave the

concentrations of all other species blank, since the number that is entered represents

extinction by all components.

- Light extinction efficiencies: Use EPA (2003a) values. If a source chooses, th e new

IMPROVE algorithm for calculating light extinction (see Section 3.2.3) may be used in

addition to the default IMPROVE algorithm. (Calculations would need to be performed

outside CALPOST or CALPOST would need to be modified to accommodate the new

alg orithm.)

- Nitrate repartitioning in POSTUTIL: Do not use for the initial modeling.

The initial run results will be based on the highest change in light extinction (deciviews) from

natural conditions over the three

- year modeling period for each Class I a rea considered.

Predicted changes exceeding the “contribution” threshold (0.5 deciviews) will trigger a finer grid

CALPUFF modeling analysis.



# 4.4 Finer Grid Modeling Procedures

4.4.1 Rationale for and Overview of Finer Grid Modeling Approach

There are t wo potential applications for finer grid CALPUFF modeling:

BART Exclusion Modeling. First, finer grid CALPUFF modeling can be used to demonstrate

that a source does not cause or contribute to visibility impairment in any Class I areas, and thus

can be ex cluded from BART controls. As shown in Figure 4

- 1, if the initial regional modeling

results are not below the threshold for visibility impacts, the next step is to conduct modeling

using a finer grid resolution for the meteorological fields and the treatm ent of terrain effects and

land use variability. In the finer grid modeling the predicted visibility impairment that is

compared to the threshold is based on the BART guidance of the 98 th 

# percentile change in

deciviews value rather than the more conservat ive highest value used in the initial analysis.

The BART guidance indicates that the emissions rate to be used for such modeling is the highest

24

- hr rate during the modeling period. Depending on the availability of source data, the following

# VISTAS’ Common Modeling Protocol 

# 47 

# emissions inf ormation (listed in order of priority) should be used with CALPUFF for BART

exclusion modeling:

- 24 hr maximum value emissions for the period 2001

- 2003 (Continuous Emission Monitor,

CEM data)

- 24 hr maximum value from continuous emissions monitoring d ata

- facility stack test emissions

- potential to emit

- permit allowable emissions, if available

- emissions factors from AP

- 42 source profiles

Quantify Benefits of BART

. The second application of refined modeling is to quantify the

visibility benefits from the BART control options. This is accomplished by running CALPUFF

with the baseline emissions rates and again with emissions after BART controls. It is important

that emission reductions be evaluated in the postprocessing step rather than b y using “negative”

emission rates in the CALPUFF model. The chemical scheme requires that emission rates always

be positive.

For any of these applications, a source

- specific modeling protocol that defines source properties

and the specific model configur ation is required. As discussed in Section 5, the source specific

protocol should include source

- specific emissions data and can refer to this document for all

methods and assumptions that follow this common protocol.

4.4.2 Model Configuration and Setti ngs for Finer Grid Modeling

Grid resolution substantially better than 12

- km is needed for a finer grid CALPUFF assessment of

visibility impacts in most cases involving Class I areas in complex terrain or coastal areas. Thus,

the CALMET fine grid resolutio n in the subregional modeling domains used for finer grid

modeling will depend on the terrain, land use (especially coastal boundaries), location of the

source, distance of the source from Class I areas, and total size of the subregional modeling

domain.

VISTAS States have 2001

- 2003 CALMET files for five 4

- km sub

- regional domains as illustrated

in Figure 4

- 4. The subdomains are designed to address all BART eligible sources within each

VISTAS states and all Class I areas within 300 km of the BART

- eligible sources. For application

for a single source, a smaller domain of roughly 200

- 300 km by 200

- 300 km is recommended.

Requests to obtain the 4

- km CALMET files should be made to the State BART representatives.

# VISTAS’ Common Modeling Protocol 

# 48 

# Figure 4

- 4. The five subregional domains for 4

- km CALMET modeling.

In some instances, as part of the source

- specific protocol, a source may propose to the State to use

an even finer grid simulation to properly characterize the flow fields and land use changes that

affect dispersion. An application f or source

- receptor distances within about 50 km may require a

grid resolution less than 1 km if complex terrain effects are likely to be important. This

determination should be made on a case

- by

- case basis. There is not a single distance at which a

parti cular grid size is appropriate. It depends on factors such as the complexity of the terrain, the

source

- receptor distances involved, the location of the source relative to the terrain features, the

physical stack parameters (e.g., a tall stack in complex t errain may be unaffected by the terrain

forced flow), proximity of the source and Class I area to a coastline, and other factors including

availability of representative observational data.

The finer grid CALMET simulations were run in hybrid mode, using b oth MM5 data to define

the initial guess fields and meteorological observational data in the Step 2 calculations.

Overwater (buoy) data will be provided in addition to the hourly surface meteorological

observations, precipitation observations and twice

- da ily upper air sounding data.

# VISTAS’ Common Modeling Protocol 

# 49 

# A domain

- specific set of modeling parameters will be defined for each subregional domain. The

proper selection of the CALMET diagnostic wind field parameters that are used to blend

observations with the Step 1 wind field dep ends on factors such as the locations of the

meteorological stations relative to terrain and coastal features (which affects the

representativeness of the observational data), the terrain length scale, and the quality (resolution)

of the MM5 data used to d efine the initial guess field and its ability to properly resolve wind

flows on the fine

- scale CALMET domain. The definition of the proper CALMET parameters is

done as part of sensitivity testing where model performance is evaluated against available

obse rvations and expected terrain effects, such as channeling of flows within a valley.

In addition to the better grid resolution and the introduction of observational data in the finer grid

simulations, several other modeling refinements can enhance the acc uracy of the finer grid

modeling. These include use of the higher resolution terrain DEM data (~3 arc sec USGS data)

in defining the gridded terrain fields and application of the ammonia limiting method in the

POSTUTIL post

- processor. Otherwise, the sour ce configuration, emissions, pollutant speciation,

Class I receptors, ozone datasets and CALPUFF model options will be the same as in the initial

runs. Similarly, CALPOST will be used in the same manner as for the initial analyses. However,

POSTUTIL can b e used to repartition nitrate in the finer grid modeling, using background

ammonia concentrations according to the IWAQM Phase 2 report (IWAQM, 1998).

For the finer grid BART exclusion analysis, the test for evaluating whether a source is

contributing to v isibility impairment is based on the 98 th 

# percentile modeled value (rather than the

highest predicted value used for the initial evaluation), which is consistent with EPA’s BART

guidance.



# 4.5 Presentation of Modeling Results

The CALPOST processing compute s the daily maximum change in deciviews. A sample of the

summary table produced by CALPOST is shown in Table 4

- 1. For evaluating compliance with

the VISTAS screening threshold, the highest change in extinction value, located at the bottom of

the CALPOST list file is compared to the threshold value (e.g., 0.5 dv). For example, in the

sample shown in Table 4

- 1, the summary at the bottom shows that the highest visibility impact is

1.219 dv, with 9 days over the year showing values greater than 0.5 dv. Ther efore this source

would not pass the initial analysis, and finer grid modeling would be required.

In addition to the highest change in deciview value on each day over all the receptors in a

particular Class I area, the CALPOST summary table in Table 4

- 1 c ontains the coordinates of the

receptor, receptor type (D indicates discrete receptors), the total haze level (background + source,

in dv), the background haze in deciviews, the change in haziness (delta dv), the humidity term

applied to hygroscopic aeroso ls (f(RH)), and the contribution of each species to light extinction

(in percent of the total source contribution) for SO 4 

# , NO 3 

# , organics, elemental carbon, coarse and

fine particulate matter.

# VISTAS’ Common Modeling Protocol 

# 50 

# Table 4

- 1. Example of CALPOST Output, Showing Maximum Daily Impacts of Source and Locations of Those Impacts.

YEAR DAY HR RECEPTOR COORDINATES (km) TYPE DV(Total) DV(BKG) DELTA DV F(RH) %_SO4 %_NO3 %_OC %_EC %_PMC %_PMF

2001 2 0 3 20.540 79.782 D 5.397 5 .358 0.039 4.314 44.33 47.22 3.07 1.07 0.00 4.30

2001 3 0 9 31.680 79.822 D 4.566 4.421 0.145 1.767 40.75 33.89 9.19 3.24 0.00 12.94

2001 4 0 1 24.723 77 .951 D 4.540 4.540 0.000 2.076 0.00 0.00 0.00 0.00 0.00 0.00

2001 5 0 77 30.228 94.571 D 4.950 4.939 0.011 3.144 43.13 44.74 4.64 1.45 0.00 6.05

2001 6 0 1 24.723 77.951 D 5.181 5.166 0.015 3.772 38.58 56.05 1.90 0.70 0.00 2.76

2001 7 0 3 20.540 79.782 D 6.366 5.745 0.620 5.439 44.98 44.99 3.69 1.26 0.00 5.0 8

.

.

.

2001 363 0 113 27.414 103.782 D 5.725 5.652 0.073 5.164 53.49 35.51 4.03 1.39 0.00 5.58

2001 364 0 113 27.414 103.782 D 6.554 6.521 0.033 7.826 48.1 2 47.09 1.67 0.64 0.00 2.48

2001 365 0 1 24.723 77.951 D 6.499 6.499 0.000 7.757 0.00 0.00 0.00 0.00 0.00 0.00

--- Number of days with Delta

- Deciview => 0.50: 9

-- - Number of days with Delta

- Deciview => 1.00: 2

--- Largest Delta

- Deciview = 1.219

# VISTAS’ Common Modeling Protocol 

# 51 

# For the finer grid analysis, the data in the table can be imported into a spreadsheet and sorted on

the delta dv column. Table 4

- 2 shows an example of the ranked visibility impacts (change in dv)

for each of three years at six different Class I areas. The 98 th 

# percentile (8 th 

# highest value) in the

sorted table would be compared to the contribution threshold (e.g., 0.5 dv). In the e xample

shown in this table, the source passes the finer grid analysis because the highest 98 th 

# percentile

visibility impact is below the contribution threshold of 0.5 dv.

The Results section of the CALPUFF modeling report should contain the following info rmation:

1. Map of source location and Class I areas within 300 km of the source

2. For the VISTAS 12

- km CALPUFF initial exemption modeling domain, a table listing all

Class I areas in the VISTAS domain and those in neighboring states and impacts at those

Class I areas within 300 km of the source, as illustrated in Table 4

- 3

.

3. A discussion of the number of Class I areas with visibility impairment from the source on

98 th 

# percentile days in each year greater than 0.5 dv (total visibility impairment minus

impairme nt on 20% best days for natural background visibility equals delta

- dv, the

visibility impact attributed to the source).

4. For the Class I area with the maximum impact, discussion of the number of days below

the 98 th 

# percentile that the impact of the source exceeds 0.5 dv, the number of receptors in

the Class I area where the impact exceeds 0.5 dv, and the maximum impact.

5. For finer grid CALPUFF exemption modeling, results for those Class I areas for which

impacts of the source exceeded 0.5 dv in the 12

- km in itial exemption modeling. Report

same results as provided for 12

- km initial exemption modeling.

6. For control option modeling, each control option tested should be listed in tabular format.

For each control option and for each Class I area where the impact of the source exceeded

0.5 dv, report the change in pollutant emissions and the change in visibility impact from

the source as a result of the control option. The effectiveness of candidate control options

are to be compared to each other, not to a speci fic target improvement.

States will provide further guidance on graphic presentation of results to simplify

evaluation of effectiveness of control measures. For example, a temporal plot of the

change in deciviews between the controlled and uncontrolled cases could be developed for

the receptor with the maximum modeled impact in each Class I area.

7. Copies of all input files and input data in electronic format for the CALMET, CALPUFF,

CALPOST and POSTUTIL runs should be archived and provided to the State.

# VISTAS’ Common Modeling Protocol 

# 52 

# Table 4

- 2. Example of Visibility Impact Rankings at Six Class I Areas

Class I Area 2001 2002 2003

Delta

Deciview

Ranks 1

- 8 Delta

Deciview

Ranks 1

- 8 Delta

Deciview

Ranks 1

- 8

Great Smoky NP 0.99

0.88

0.62

0.59

0.55

0.52

0.48

0.47 0.95

0.63

0.51

0.50

0 .46

0.42

0.37

0.36 1.20

0.90

0.73

0.72

0.59

0.47

0.45

0.42

Linville Gorge 0.67

0.45

0.43

0.33

0.29

0.27

0.25

0.23 0.81

0.69

0.65

0.50

0.45

0.33

0.31

0.29 0.76

0.47

0.37

0.35

0.31

0.30

0.28

0.28

Shining Rock 0.66

0.43

0.41

0.35

0.26

0.24

0.23

0.22 0.73

0. 69

0.63

0.52

0.46

0.34

0.29

0.26 0.75

0.45

0.36

0.34

0.28

0.27

0.26

0.25

Cohutta 0.26

0.23

0.22

0.21

0.20

0.19

0.18

0.16 0.54

0.47

0.43

0.37

0.37

0.31

0.31

0.30 0.61

0.42

0.30

0.29

0.28

0.28

0.25

0.25

Joyce Kilmer

- Slickrock 0.34

0.33

0.31

0.26

0.24

0.20

0.18

0.17 0.52

0.43

0.32

0.31

0.30

0.28

0.24

0.24 0.27

0.24

0.23

0.20

0.14

0.13

0.11

0.10

Mammoth Cave NP 0.56

0.44

0.38

0.29

0.25

0.24

0.22

0.21 0.57

0.56

0.53

0.35

0.33

0.33

0.30

0.29 0.50

0.37

0.36

0.35

0.31

0.24

0.21

0.19

# VISTAS’ Common Modeling Protocol 

# 53 

# Table 4

- 3. Format of Summa ry of Results for CALPUFF Modeling in VISTAS’ 12

- km Modeling

Domain to Determine if a BART Eligible Source is Subject to BART.

Class I area Distance

(km)

from

source to

Class I

area

boundary # of days 1



# and # of

receptors

with impact

> 0.5 dv in

Class I area:

2001 # of days 1



# and # of

receptors

with impact

> 0.5 dv in

Class I area:

2002 # of days 1



# and # of

receptors

with impact

> 0.5 dv in

Class I area:

2003 # of days 1 

# and

# of receptors

with impact

> 1.0 dv in

Class I area

for 3

- yr

period Ma x. 24

- hr

impact over

3

- yr period

Dolly Sods, WV

Shenandoah, VA

James River

Face, VA

Mammoth Cave,

KY

Sipsey, AL

Great Smoky

Mtns, TN

Cohutta, GA

Shining Rock,

NC

Linvi lle Gorge,

NC

Swanquarter, NC

Cape Romain,

SC

Okefenokee, GA

Saint Marks, FL

Chassahowitzka,

FL

Everglades, FL

Brigantine, NJ

Breton Island,

LA

Caney Creek,

AR

Upper Buffalo,

AR

Mingo, MO

Hercules Glade,

MO

1 

# Days below the 98 th 

# percentile of days in each year or the three

- year modeling period, as appropriate

# VISTAS’ Common Modeling Protocol 

# 54 

# 4.6 VISTAS Contribution to CALPUFF Modeling of BART Eligib le Sources

VISTAS will provide updates and supporting information concerning the Common Modeling

Protocol (this document) on the VISTAS website. In addition, VISTAS will make publicly

available the following data bases developed by Earth Tech:

• VISTAS versi on of the CALPUFF modeling system, maintained on the CALPUFF website.

Version 5.754 includes CALMET, CALPUFF, CALPOST, and POSTUTIL files, updated in

December 2005. The last update in this VISTAS version is a CALMET update that addresses

over water disper sion, which was developed for the Minerals Management Service (MMS) in

fall 2005. This VISTAS version of CALPUFF will not be updated further unless errors are

found in the code, except that a new one

- step POSTUTIL procedure will be incorporated.

BART

- el igible sources in the VISTAS states will be able to use this VISTAS version

throughout the BART modeling exercise.

• 12

- km CALMET output files for 2001, 2002, and 2003 produced as described in previous

sections. Further detail on model configuration and s ettings will be provided with the output

files and will be made available on the CALPUFF website.

• CALMET will include a software modification to allow the meteorological data inputs into

CALMET to be used to generate finer grid CALMET files without having to go back to the

original MM5 output files

• Five 4

- km CALMET subdomains for 2001, 2002, and 2003, produced as described in

previous sections. Further detail on model configuration and settings will be provided with

the output files and will be made availa ble on the website.

• File with CALPUFF model configuration and settings sufficient to replicate CALPUFF

modeling done for VISTAS using 12 km CALMET, including

o Ozone data used to run CALPUFF

o Ammonia concentrations used to run CALPUFF.

o All other set up files used in VISTAS 12

- km CALPUFF run

Samples of these data files and examples of their application with CALPUFF for BART

screening analyses can be found on the CALPUFF web site at

( http://www.s rc.com/verio/download/sample_files.htm ).

# Source

- Specific Modeling Protocol 

# 55 

# 5

. SOURCE

- SPECIFIC MODELING PR OTOCOL

Sources are required to submit a source

- specific protocol to the State for review and approval

prior to source

- specific modeling. States will provide t he documentation to EPA and FLM for

their review. An outline of the typical contents of the site

- specific protocol is provided in Table

5

- 1.

If a source

- specific modeling approach is proposed that differs from the common approach in

Chapter 4, a more

- deta iled modeling protocol than that required under the common procedures is

required. This protocol must explain the data sources, model configuration, and rationale for

changes in the model approach from the common protocol and must be approved by the State.

Unit

- specific source data include the following parameters:

- Location (e.g., UTM coordinates, UTM zone and datum)

- Stack height above the ground

- Stack diameter

- Exit velocity

- Exit temperature

- Emission rates (SO 2 

# , H 2 

# SO 4 

# , NO

x 

# and PM 10 

# ).

Addit ional building dimension information (building width, length, height and corner locations)

is needed for short stacks that are less than Good Engineering Practice (GEP) height. This

information is used in providing effective structure dimensions for build ing downwash

calculations. (The requirement to conduct building downwash modeling may be waived by

individual States or if the transport distance is greater than 50 km.)

The source coordinates must be expressed in the coordinate system used to define the CALMET

and CALPUFF modeling domains. For the regional screening simulations, a Lambert Conformal

Conic (LCC) coordinate system will be used. The required parameters to define an LCC

coordinate include two matching parallels, latitude/longitude of the pro jection origin, coordinate

datum, and false Easting and Northing (if used) of the projection origin. Subregional and source

specific domains may be using either an LCC or UTM projection.

The CALPUFF Graphical User Interface (GUI) system provides softwar e (called COORDS) to

compute to/from latitude/longitude, LCC and UTM coordinates for a large number of datums. In

addition, the CALVIEW graphics feature allows the use of georeferenced satellite or aerial

photographs to be used as base maps to confirm sou rce locations. Links to sources of suitable

base maps can be found on the CALPUFF data site ( www.src.com ) in the section on “Aerial

Photos”.

# Source

- Specific Modeling Protocol 

# 56 

# Table 5

- 1

. Sample Table of Contents of a Sourc e

- Specific Fine

- Scale Modeling Protocol.

1. INTRODUCTION

1.1 Objectives

1.2 Location of Source vs. Relevant Class I Areas

1.3 Source Impact Evaluation Criteria

2. SOURCE DESCRIPTION

2.1 Unit

- specific Source Data

2.2 Boundary Conditions

3. GEOPHYSICAL AND METEOROLOGICAL DATA

3.1 Modeling Domain and Terrain

3.2 Land Use

3.3 Meteorological Data Base

3.3.1 MM5 Simulations

3.3.2 Measurements and Observations

3.4 Air Quality Data Base

3.4.1 Ozone Concentrations

– Measured or Modeled

3.4.2 Ammonia Co ncentrations

– Measured or Modeled

3.4.3 Concentrations of Other Pollutants

– Measured or Modeled

3.5 Natural Conditions at Class I Areas

4. AIR QUALITY MODELING METHODOLOGY

4.1 Plume Model Selection

4.1.1 Major Relevant Features of CALMET

4.2.2 Ma jor Relevant Features of CALPUFF

4.2 Modeling Domain Configuration

4.3 CALMET Meteorological Modeling

4.4 CALPUFF Computational Domain and Receptors

4.5 CALPUFF Modeling Option Selections

4.6 Light Extinction and Haze Impact Calculations

4.7 Modelin g Products

5. REVIEW PROCESS

6.1 CALMET Fields

6.2 CALPUFF, CALPOST, and POSTUTIL Results

6. REFERENCES

APPENDICES

A.1 VISTAS BART MODELING PROTOCOL

A.2 ... other appendices as needed

# Source

- Specific Modeling Protocol 

# 57 

# An example of the data that need to be reported is provided in Table 5

- 2. More detail on the

stack data, emissions species, and particulate size fractions to be reported will be made available

on the CALPUFF website, www.src.com , Check with your State for the more detailed for mat of

Table 5

- 2 that is to be used.

Discussions with the regulatory authorities should be conducted prior to development of a

protocol to ensure all of the relevant issues are included in the protocol.

Table 5

- 2. Example of Source Documentation fo r BART Eligible Source.

Unit name

and/or

description Start

- up dates SO 2 

# potential

emissions (tpy) NO

x 

# potential

emissions (tpy) Total PM

potential

emissions (tpy)

Emissions source

name

...

Total emissions

Potential BART

eligible

emissions

# Quality Assurance 

# 58 

# 6. QUALITY ASSURANCE

6.1 Scope and Purpose of the QA program

Air quality modeling covered under this protocol is an important tool for use in determining

whether a BART

- eligible source can be reasonable expected to cause or c ontribute to visibility

impairment in a Class I area, and therefore whether this source should be subject to BART

controls, and if so, to determine the relative benefits of various BART controls. The purpose of

the quality assurance (QA) program is to esta blish procedures for ensuring that products produced

by the application of the modeling techniques for BART studies satisfy the regulatory objectives

of the BART program.

The scope of the QA program affects different users differently. Common features of m ost

applications will be the setup and execution of the CALPUFF air quality model and processing of

modeling results to determine if a source contributes to visibility impairment at a Class I area. In

many cases, users will be provided meteorological datas ets that have been developed with

VISTAS funding under a suitable QA program for use in the BART modeling. Other users will

be involved in site

- specific or source

- specific analyses that will use additional datasets and

potentially different modeling option s and/or tools. More extensive quality assurance will be

required in these latter types of applications. It is the responsibility of the modeler to ensure that

an adequate QA protocol is in place for a particular application.

The CALPUFF modeling system c ontains built

- in features to facilitate quality assurance of the

modeling results. These include the automatic production of “QA” files for various datasets,

including geophysical fields, sources and receptors, and imbedded tracking of model options and

s witches within the output files from the major modeling units of the modeling system. The

Graphical User Interface system (GUI) provided as part of the latest CALPUFF modeling system

allows these QA files to be displayed graphically.

In addition, a detail ed software management system is in place to track version and level numbers

associated each program and utility within the CALPUFF modeling system. This information is

carried forward in all of the output files to create an audit trail of software versio ns and major

model options used that can be retrieved and displayed from the model output files.

Because the required QA procedures will depend heavily on the exact application, there will be

differences among different users and different applications.

In addition, the BART modeling process involves multiple organizations. The States have overall

responsibility for the process and may also execute some or all of the modeling. VISTAS is

contributing general guidance via this protocol and is preparing meteor ological fields and

performing modeling under the guidance of the States. The sources that are BART

- eligible need

to provide process information and emissions data for use in the analyses. In addition, those

sources that are involved in BART assessments wi ll need to be actively involved in control

# Quality Assurance 

# 59 

# technology decisions and assessments. Finally, some of the modeling steps may be carried out by

contractors on behalf of VISTAS, a State, or a source.

Each of these organizations has a responsibility to ensure tha t it is providing correct information

to others and to evaluate the quality of any analyses it is performing, whether with data of its own

or from others. This chapter provides general guidance and information on those aspects of

quality assurance that are specific to the CALPUFF modeling effort, irrespective of which

organization is carrying out the effort. The focus is on the common protocol efforts described in

Chapter 4. As described in Section 6.3, more comprehensive QA may be needed for the unique

asp ects of the source

- specific modeling described in Chapter 5.



# 6.2 QA Procedures for Common Protocol Modeling

The VISTAS common protocol (Section 4) describes the methods and procedures for use in

conducting regional scale screening modeling to determine th e whether a particular source or

group of sources is subject to BART controls. In the initial application, the regional CALPUFF

ready meteorological data files will be provided by VISTAS. The amount of effort for end

- users

performing QA of these pre

- defi ned meteorological fields will be reduced from what is required

in developing source

- specific meteorological fields, as described below. Also, VISTAS is

planning to provide five subregional CALMET meteorological datasets in a CALPUFF

- ready

format. The de velopment of these CALMET datasets will be subject to a QA program as part of

their development, so the necessary quality assurance activity of end

- users is again reduced from

what would be required in the development of the dataset. It is not expected th at the quality

assurance steps in the development will be repeated in each application. The VISTAS

- provided

regional and subregional meteorological fields will include a test case simulation for

demonstrating that expected modeling results are obtained on the user’s computer platform. This

test should be repeated by every user.

Although the CALPUFF modeling system is recommended by the U.S. Environmental Protection

Agency for application to BART analyses, a considerable amount of expertise and modeling

ju dgment is needed at certain stages of the analysis. The modeling is not a “cookbook” exercise,

a fact that was recognized by the U.S. EPA in describing the expertise needed for CALMET

modeling (EPA, 1998; pp. 9

- 10,). Current methods for performing refine d chemistry calculation

also require an understanding of the chemical and meteorological processing affecting

ammonium nitrate formation. VISTAS has committed to provide appropriate CALPUFF training

to assist States in obtaining the necessary expertise wi th the latest CALPUFF modeling tools and

techniques. An appropriate level of knowledge of the model formulation, technical approach and

assumptions is essential for successful BART modeling.

6.2.1 Quality Control of Input Data

The input data required by the model depends on the application. At a minimum, source data is

required by CALPUFF (see Section 6.2.3) along with a list of choices made about model options

and switches. Most of the modeling option choices are specified or recommended by regulatory

# Quality Assurance 

# 60 

# guidance and default values (see references in Section 4.3.3). However, remodeling of the

boundary conditions is not required for VISTAS

- provided finer grid domains so the expertise

level is not as high as it would be for development of the boundary condi tions files from scratch.

To the extent that modeling applications are using pre

- defined CALMET files and CALPUFF

templates, the quality assurance will be straightforward. More detailed steps are needed for the

setup of modeling files for source

- specific applications of subregional domains finer than 4 km.

The basic procedures that will apply to all CALPUFF model applications will include a

confirmation of the source data, including units, verification of the correct source and receptor

locations, includi ng datum and projection, confirmation of the switch selections relative to

modeling guidance, checks of the program switches and file names for the various processing

steps, and confirmation of the use of the proper version and level of each model program. It is a

common and recommended procedure for an independent modeler not involved in the setup of

the modeling files to independently confirm the model switches and data entry in the actual

model input files and to conduct an independent run of the worst case event as a confirmation

check.

In addition, common practice requires that a model project CD (or DVD or set of DVDs) be

created that contains all of the data and program files needed to reproduce the model results

presented in a report. The model lis t files from each step are included on the project CD. This

information allows independent checking and confirmation of the modeling process.

6.2.2 Quality Control of Application of CALMET

For users of the VISTAS CALPUFF

- ready CALMET meteorological files , a number of large

datafiles will be provided by VISTAS on external USB2 or Firewire hard drives in a format ready

for use with the CALPUFF model. The QA steps associated with the development of the

VISTAS common datasets will be provided separately as p art of the modeling documentation. It

is not expected that the QA steps conducted in the development of the meteorological datasets

will be repeated in each application, although tests to confirm that the dataset is suitable for the

application for which it is being used should be performed as part of the QA. This is discussed in

more detail below.

The regional screening CALMET grid is defined in Chapter 4 on a 12

- km Lambert Conformal

Conic (LCC) grid system. The subregional and source

- specific domains ma y be defined in either

LCC or Universal Transverse Mercator (UTM) coordinates. In the case of the LCC projection,

two matching parallels, latitude/longitude of the projection origin, coordinate datum, and false

Easting and Northing (if used) of the projec tion origin must also be defined. For any domains in

UTM coordinates, the UTM zone (see Appendix D of the CALMET User’s Guide) and datum

must be defined. The appropriate projection and map factors are provided as part of the

definition of the VISTAS regi onal grid system. For a source

- specific domain, the grid parameters

will be provided as part of the source

- specific protocol.

# Quality Assurance 

# 61 

# Appendix A of the IWAQM report (EPA, 1998) contains a list of recommended CALMET switch

settings. Except as modified in Chapter 4 of this protocol or in a source

- specific protocol, the

IWAQM guidance should be used in setting up the CALMET simulations. The CALMET model

obtains the switch settings from an ASCII “control file” with a default name of CALMET.INP.

Whether the model is run using a GUI or from the control line in a DOS, Linux, or Unix window,

it is essential that the control file be reviewed as part of the CALMET QA analysis. The

CALMET GUI retains all of the input descriptive information that is part of the standard

CA LPUFF.INP file structure. This includes the default value for each variable, a text description

of the variable, the meaning of each variable option, the units of the variable and inter

relationships among variables indicating if/when the variable is used . Some third

- party

commercial GUIs strip out this descriptive information, which makes the QA step more difficult,

although it is essential for perform nonetheless using the variable names as references for the

variables in the file.

Part of the CALPUFF mo deling system’s built

- in QA capabilities is a variable tracking system

that retains the control file inputs for CALMET and CALPUFF in the output files create by the

models. This information includes the Version and Level numbers of the processor codes and

main model codes used in the simulations as well as the control files from the main models

(CALMET and CALPUFF). The information from the preprocessing steps and the CALMET

and CALPUFF model simulations is all carried forward and saved in the

CALPUFF/pos tprocessor output files so that the final concentration/flux files contain a history of

the model options and switch settings. This allows a user or reviewing agency to confirm the

switch settings provided in a control file with that actually used in the m odel simulations. An

optional switch in the CALPOST processor creates a complete listing of the QA data. This step

requires access to the output CALPUFF concentration and/or flux files, which are normally

practical to store on CDs or DVDs and to provide a part of the Project CD/DVD set.

6.2.3 Quality Control of Application of CALPUFF

The quality assurance of the source and emissions data is a major component of the CALPUFF

modeling. Also, many errors are found in source coordinates and related projection /datum

parameters, so confirmation of the source location is an important part of the modeling QA.

The locations of the Class I area receptors are another important CALPUFF input. The use of

pre

- defined receptors as provided by the National Park Service ( NPS) receptor dataset is

recommended in the VISTAS common protocol. However, although the latitude and longitude of

each receptor point is provided, it is necessary to ensure that the proper UTM or LCC coordinates

have been computed for computational doma in selected. In particular, the datum of the NPS

conversion software is not specified, so it is recommended that coordinates be checked using the

CALPUFF GUI’s COORDS software or another comparable coordinate translation software

package that recognizes v arious datums.

Most of the CALPUFF input variables contain default values. Appendix B of the IWAQM report

contains a list of recommended CALPUFF switch settings. Except as modified in Chapter 4 of

# Quality Assurance 

# 62 

# this protocol or in a source

- specific protocol, the IWAQM guidance should be used in setting up

the CALPUFF simulations. The CALPUFF model obtains the switch settings from an ASCII

“control file” with a default name called the CALPUFF.INP file. As is the case with the

comparable CALMET file, it is essential tha t the control file be reviewed manually as part of the

CALPUFF QA analysis. To facilitate this process, as was the case with the CALMET GUI, the

CALPUFF GUI retains all of the input descriptive information that is part of the standard

CALPUFF.INP file str ucture. Some third

- party commercial GUIs strip out this descriptive

information, which makes the QA step more difficult, although it is essential for perform

nonetheless using the variable names as references for the variables in the file.

6.2.4 Quality C ontrol of Application of CALPOST and POSTUTIL

CALPOST is run separately for each Class I area in order to obtain the necessary visibility

statistics for evaluating compliance with the BART screening and finer grid modeling thresholds.

The inputs to CALPOS T involve selection of the visibility method (Method 6 in the standard

EPA BART guidance), entry of Class I area

- specific data for computing background extinction

(either average or best 20% natural conditions, as prescribed by the State) and monthly rela tive

humidity factors for hygroscopic aerosols. CALPOST contains a receptor screening that allow

subsets of a receptor network modeling in CALPUFF to be selected for processing in a given

CALPOST run. This is how receptors within a single Class I area ar e selected for processing

from a CALPUFF output file that may contain receptors from several Class I areas. CALPOST

contains options for creating plot files that will help in the confirmation that the proper receptor

subset is extracted.

The CALPOST outpu t file contains a listing of the highest visibility impact each day of the model

simulation over all receptors included in CALPOST analysis. Receptors will normally be

selected in each CALPOST run so that each CALPOST run represents the impacts at a singl e

Class I area. The table includes the data shown in the example in Table 4

- 1. For a screening

assessment, the peak value of the change in extinction is shown at the bottom of the visibility

table (see Table 4

- 1). For a finer grid simulation, the 98 th 

# p ercentile value (8 th 

# highest day) is

used for comparison against the BART threshold of 0.5 deciviews. It is necessary to import the

results of the CALPOST table into a sorting program such as a spreadsheet to rank the daily

change in extinction values suc h as is presented in Table 4

- 2.

The CALPOST inputs that need to be carefully checked as part of the CALPOST quality

assurance are:

- Visibility technique (Method 6 in the common VISTAS protocol)

- Monthly Class I

- specific relative humidity factors for Me thod 6

- Background light extinction values

# Quality Assurance 

# 63 

# - Inclusion of all appropriate species from modeled sources (e.g., sulfate, nitrate,

organics, (as SOA), coarse and fine particulate matter and elemental carbon.

- Appropriate species names for coarse PM used

- Extinction efficiencies for each species

- Appropriate Rayleigh scattering term (10 Mm

- 1 

# for screening modeling but Class I area

specific value for finer grid modeling)

- Screen to select appropriate Class I receptors for each CALPOST simulation.

The CALPOST program produces plot files compatible with CALVIEW that allow confirmation

of receptor locations that is useful in evaluating the receptor screening step.

POSTUTIL allows the user to sum the contributions of sources from different CALPUFF

simulati ons into a total concentration file. In addition, it contains options to scale the

concentrations from different modeled species (e.g., different particle sizes) into species

dependent size distributions for the particulate matter. For example, PM is of ten simulated with

unit emission rates for each particle size category and, in the POSTUTIL stage, the contributions

of each size category based on the species being considered (e.g., elemental carbon, coarse

particulate matter, etc.) are combined to form the species concentrations for input into

CALPOST. This process, although simple, requires a careful review of the weighting factors for

each source. POSTUTIL also allows a repartitioning of nitric acid and nitrate to account for the

effects of ammonia li miting conditions.

If source

- specific modeling is performed using different sources of data or different techniques,

the source

- specific modeling protocol should provide justification for deviations from the

VISTAS common protocol, and a QA plan specific for the application provided to address the

quality assurance of the data used.



# 6.3 Additional QA Issues for Alternative Source

- Specific Modeling

The level of QA required for application of source

- specific protocols will be substantially higher

than for t he use of datasets that have already been subject to a QA procedure. For example,

source

- specific protocols may include the use of on

- site meteorological datasets, the use of higher

resolution prognostic meteorological (e.g., MM5) datasets, alternative vi sibility calculations,

different extinction coefficients, or other changes to the common protocol. In addition to

providing a source

- specific modeling protocol describing and justifying the changes to the

modeling approach from the VISTAS common protocol, the site

- specific applications should

include the development of a QA plan to properly evaluate the data used in the site

- specific

modeling.

The critical CALMET input parameters depend on the mode in which the model is run

(observations mode, hybrid mode or no

- observations mode), and the location and spatial

# Quality Assurance 

# 64 

# representativeness of any observational data. In a site specific protocol involving the

development of a meteorological dataset, the elements of the QA process include preparation of

wind rose (using observed, MM5 and CALMET

- derived data), including examination of the data

as a function of season and time of day (e.g., 4am, 10am, 4pm wind roses), time series analyses,

and presentation of 2

- D vector plots illustrating terrain effects/sea breeze circulat ion or other

features of the flow expected to occur within the domain. For example, 2

- D vector plots

produced during light wind speed stable conditions (e.g., early morning such as 4 am) are good

for assessing the performance of the CALMET model configura tion and switches in reproducing

terrain effects because these conditions are likely to maximize the terrain impacts in the model.

Season wind roses at 4 am, 10 am and 4 pm would be expected to show the development of sea

breeze circulations that may be i mportant for certain applications. Customization of the QA

process for the individual site

- specific domain based on the availability of data and the physical

processes expected to be important at that location should be conducted as part of the site

- speci fic

QA plan development.

If site

- specific CALPUFF simulations involving the Ammonia Limiting Method are conducted,

performance of the model in reproducing observed CASTNet or IMPROVE sulfate and nitrate

concentrations at measurement sites within the site

- s pecific modeling domain should be

evaluated. The use of alternative ammonia concentration data (e.g., CMAQ output rather than

derived ammonia based on aerosol measurements) will require an evaluation of the model

performance relative to the techniques in the VISTAS common protocol.

In any site

- specific protocol a site

- specific QA plan should be prepared.



# 6.4 Assessment of Uncertainty in Modeling Results

Chapter 3 discussed the uncertainties and known limitations in CALPUFF. The source specific

modeling report does not need to repeat the uncertainties listed in Chapter 3, but the reviewer

should interpret results in light of these limitations. It is expected that the performance of the

model will be better in predicting changes in visibility impacts due to BART controls than in

predicting absolute visibility values. This is because uncertainties in meteorological conditions

transport and dispersion are expected to be less important in evaluating a change in impact, since

a comparable effect will be inclu ded in both the base and sensitivity simulations.

# References 

# 65 

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Perry, S.G., D.J. Burns, L.H. Adams, R.J. Paine, M.G. Dennis, M.T. Mills, D.G. Strimaitis, R.J.

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for Unstable Situations (CTDMPLUS) Volume 1: Model Description and User Instructions. EPA/600/8

-

89/041, U.S. EPA, Research Triangle Park, North Carolina.

Schulman, L.L., D.G. Strimatitis, and J.S. Scire, 2000: Devel opment and Evaluation of the PRIME Plume

Rise and Building Downwash Model, J. Air & Waste Manage. Assoc., 50 , 378

- 390.

Scire, J.S., F.W. Lurmann, A. Bass and S.R. Hanna, 1984: Development of the MESOPUFF II

Dispersion Model. EPA

- 600/3

- 84

- 057, U.S. Envir onmental Protection Agency, Research Triangle Park,

NC.

Scire, J.S. and F.R. Robe, 1997: Fine

- Scale Application of the CALMET Meteorological Model to a

Complex Terrain Site. Paper 97

- A1313. Air & Waste Management Association 90th Annual Meeting &

Exhibiti on, Toronto, Ontario, Canada. 8

- 13 June 1997.

Scire, J.S., D.G. Strimaitis, and R.J. Yamartino, 2000a: A User’s Guide for the CALPUFF Dispersion

Model (Version 5). Earth Tech, Inc., Concord, Massachusetts

Scire, J.S., F.R. Robe, M.E. Fernau, and R.J. Yamar tino, 2000b: A User’s Guide for the CALMET

Meteorological Model (Version 5). Earth Tech, Inc., Concord, Massachusetts.

Scire, J.S., Z

- X Wu, D.G. Strimaitis and G.E. Moore, 2001: The Southwest Wyoming Regional

CALPUFF Air Quality Modeling Study

– Volume I. Prepared for the Wyoming Dept of Environmental

Quality. Available from Earth Tech, Inc., 196 Baker Avenue, Concord, MA.

Scire, J.S., Z.

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on Air Quality Models: The Path Forward. Mystic, CT, 22

- 24 October 2003.

Scire, J.S., D.G. Strimaitis and F.R. Robe, 2005: Evaluation of enhancements to the CALPUFF model for

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October 2005.

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- Rural Differences. Paper presented at the

AAAR International Specialty Conference, PM: Supersite Program and Related Studies, Atlan ta, 7

- 11

February 2005.

# INVISTA Camden Plant B - 1 Trinity Consultants

BART Applicability Modeling Analysis 

# A PPENDIX 

# B

S AMPLE 

# CALPUFF, POSTUTIL, AND 

# CALPOST I NPUT 

# F ILES

# INVISTA Camden Plant B - 2 Trinity Consultants

BART Applicability Modeling Analysis 

# CALPUFF BATCH PROCESSING FILE

12-KM SCREENING ANALYSES

# runcpuff.bat 10/23/2006

REM INVISTA CAMDEN

REM BART APPLICABILITY ANALYSIS

REM MZ/AH 10.23.06

REM RUN 2003

CALL CALPUFFl.EXE invcam03.INP

REM RUN 2002

CALL CALPUFFl.EXE invcam02.INP

REM RUN 2001

CALL CALPUFFl.EXE invcam01.INP

CALL runcPOST.BAT

PAUSE

1

# runcPOST.bat 10/23/2006

REM INVISTA CAMDEN

REM SCREENING RUNS 12 KM DATA

REM POSTUTIL AND CALPOST

POSTUTILL.EXE UTINVCAM01.INP

POSTUTILL.EXE UTINVCAM02.INP

POSTUTILL.EXE UTINVCAM03.INP

CALPOSTL.EXE VANINVCAM01CR.INP

CALPOSTL.EXE VANINVCAM02CR.INP

CALPOSTL.EXE VANINVCAM03CR.INP

CALPOSTL.EXE VANINVCAM01GS.INP

CALPOSTL.EXE VANINVCAM02GS.INP

CALPOSTL.EXE VANINVCAM03GS.INP

CALPOSTL.EXE VANINVCAM01LG.INP

CALPOSTL.EXE VANINVCAM02LG.INP

CALPOSTL.EXE VANINVCAM03LG.INP

CALPOSTL.EXE VANINVCAM01SR.INP

CALPOSTL.EXE VANINVCAM02SR.INP

CALPOSTL.EXE VANINVCAM03SR.INP

CALPOSTL.EXE V20INVCAM01CR.INP

CALPOSTL.EXE V20INVCAM02CR.INP

CALPOSTL.EXE V20INVCAM03CR.INP

CALPOSTL.EXE V20INVCAM01GS.INP

CALPOSTL.EXE V20INVCAM02GS.INP

CALPOSTL.EXE V20INVCAM03GS.INP

CALPOSTL.EXE V20INVCAM01LG.INP

CALPOSTL.EXE V20INVCAM02LG.INP

CALPOSTL.EXE V20INVCAM03LG.INP

CALPOSTL.EXE V20INVCAM01SR.INP

CALPOSTL.EXE V20INVCAM02SR.INP

CALPOSTL.EXE V20INVCAM03SR.INP

PAUSE

1

# INVISTA Camden Plant B - 3 Trinity Consultants

BART Applicability Modeling Analysis 

# SAMPLE CALPUFF INPUT FILE

INVCAM02.INP

12-KM SCREENING A NALYSIS YEAR 2002INVCAM02.inp10/23/2006INVISTACAMDENBARTSCREENINGANALYSIS12KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006UPDATED07.21.2006w/revised12KMMET----------------Runtitle(3lines)------------------------------------------CALPUFFMODELCONTROLFILE---------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames--------------DefaultNameTypeFileName-------------------------CALMET.DATinput*METDAT=*orISCMET.DATinput*ISCDAT=*orPLMMET.DATinput*PLMDAT=*orPROFILE.DATinput*PRFDAT=*SURFACE.DATinput*SFCDAT=*RESTARTB.DATinput*RSTARTB=*--------------------------------------------------------------------------------CALPUFF.LSToutput!PUFLST=INVCAM02.lst!CONC.DAToutput!CONDAT=INVCAM02.con!DFLX.DAToutput*DFDAT=puff2002-sm.dry*WFLX.DAToutput*WFDAT=puff2002-sm.wet*VISB.DAToutput*VISDAT=puff2002-sm.vis*RESTARTE.DAToutput*RSTARTE=puff2002-sm.res*--------------------------------------------------------------------------------EmissionFiles--------------PTEMARB.DATinput*PTDAT=*VOLEMARB.DATinput*VOLDAT=*BAEMARB.DATinput*ARDAT=*LNEMARB.DATinput*LNDAT=*--------------------------------------------------------------------------------OtherFiles-----------OZONE.DATinput!OZDAT=OZCAM02.dat!VD.DATinput*VDDAT=*CHEM.DATinput*CHEMDAT=*H2O2.DATinput*H2O2DAT=*HILL.DATinput*HILDAT=*HILLRCT.DATinput*RCTDAT=*COASTLN.DATinput*CSTDAT=*1INVCAM02.inp10/23/2006FLUXBDY.DATinput*BDYDAT=*BCON.DATinput*BCNDAT=*DEBUG.DAToutput*DEBUG=*MASSFLX.DAToutput*FLXDAT=*MASSBAL.DAToutput*BALDAT=*FOG.DAToutput*FOGDAT=*--------------------------------------------------------------------------------AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASET=lowercase!LCFILES=T!F=UPPERCASENOTE:(1)file/pathnamescanbeupto70charactersinlengthProvisionformultipleinputfiles----------------------------------NumberofCALMET.DATfilesforrun(NMETDAT)Default:1!NMETDAT=12!NumberofPTEMARB.DATfilesforrun(NPTDAT)Default:0!NPTDAT=0!NumberofBAEMARB.DATfilesforrun(NARDAT)Default:0!NARDAT=0!NumberofVOLEMARB.DATfilesforrun(NVOLDAT)Default:0!NVOLDAT=0!!END!-------------Subgroup(0a)-------------ThefollowingCALMET.DATfilenamesareprocessedinsequenceifNMETDAT>1DefaultNameTypeFileName-------------------------noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-01r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-02r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-03r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-04r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-05r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-06r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-07r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-08r.dat!!END!2INVCAM02.inp10/23/2006noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-09r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-10r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-11r.dat!!END!noneinput!METDAT=T:\VISTAS\Domain0-2002\met2002-12r.dat!!END!INPUTGROUP:1--Generalruncontrolparameters--------------Optiontorunallperiodsfoundinthemet.file(METRUN)Default:0!METRUN=0!METRUN=0-RunperiodexplicitlydefinedbelowMETRUN=1-Runallperiodsinmet.fileStartingdate:Year(IBYR)--Nodefault!IBYR=2002!(usedonlyifMonth(IBMO)--Nodefault!IBMO=1!METRUN=0)Day(IBDY)--Nodefault!IBDY=1!Hour(IBHR)--Nodefault!IBHR=1!Basetimezone(XBTZ)--Nodefault!XBTZ=5.0!PST=8.,MST=7.CST=6.,EST=5.Lengthofrun(hours)(IRLG)--Nodefault!IRLG=8760!Numberofchemicalspecies(NSPEC)Default:5!NSPEC=19!Numberofchemicalspeciestobeemitted(NSE)Default:3!NSE=17!FlagtostoprunafterSETUPphase(ITEST)Default:2!ITEST=2!(Usedtoallowcheckingofthemodelinputs,files,etc.)ITEST=1-STOPSprogramafterSETUPphaseITEST=2-ContinueswithexecutionofprogramafterSETUPRestartConfiguration:Controlflag(MRESTART)Default:0!MRESTART=0!0=Donotreadorwritearestartfile1=Readarestartfileatthebeginningoftherun2=Writearestartfileduringrun3INVCAM02.inp10/23/20063=ReadarestartfileatbeginningofrunandwritearestartfileduringrunNumberofperiodsinRestartoutputcycle(NRESPD)Default:0!NRESPD=0!0=Filewrittenonlyatlastperiod>0=FileupdatedeveryNRESPDperiodsMeteorologicalDataFormat(METFM)Default:1!METFM=1!METFM=1-CALMETbinaryfile(CALMET.MET)METFM=2-ISCASCIIfile(ISCMET.MET)METFM=3-AUSPLUMEASCIIfile(PLMMET.MET)METFM=4-CTDMplustowerfile(PROFILE.DAT)andsurfaceparametersfile(SURFACE.DAT)METFM=5-AERMETtowerfile(PROFILE.DAT)andsurfaceparametersfile(SURFACE.DAT)MeteorologicalProfileDataFormat(MPRFFM)(usedonlyforMETFM=1,2,3)Default:1!MPRFFM=1!MPRFFM=1-CTDMplustowerfile(PROFILE.DAT)MPRFFM=2-AERMETtowerfile(PROFILE.DAT)PGsigma-yisadjustedbythefactor(AVET/PGTIME)**0.2AveragingTime(minutes)(AVET)Default:60.0!AVET=60.!PGAveragingTime(minutes)(PGTIME)Default:60.0!PGTIME=60.!!END!-------------------------------------------------------------------------------INPUTGROUP:2--Technicaloptions--------------Verticaldistributionusedinthenearfield(MGAUSS)Default:1!MGAUSS=1!0=uniform1=GaussianTerrainadjustmentmethod4INVCAM02.inp10/23/2006(MCTADJ)Default:3!MCTADJ=3!0=noadjustment1=ISC-typeofterrainadjustment2=simple,CALPUFF-typeofterrainadjustment3=partialplumepathadjustmentSubgrid-scalecomplexterrainflag(MCTSG)Default:0!MCTSG=0!0=notmodeled1=modeledNear-fieldpuffsmodeledaselongatedslugs?(MSLUG)Default:0!MSLUG=0!0=no1=yes(slugmodelused)Transitionalplumerisemodeled?(MTRANS)Default:1!MTRANS=1!0=no(i.e.,finalriseonly)1=yes(i.e.,transitionalrisecomputed)Stacktipdownwash?(MTIP)Default:1!MTIP=1!0=no(i.e.,nostacktipdownwash)1=yes(i.e.,usestacktipdownwash)Methodusedtosimulatebuildingdownwash?(MBDW)Default:1!MBDW=1!1=ISCmethod2=PRIMEmethodVerticalwindshearmodeledabovestacktop?(MSHEAR)Default:0!MSHEAR=0!0=no(i.e.,verticalwindshearnotmodeled)1=yes(i.e.,verticalwindshearmodeled)Puffsplittingallowed?(MSPLIT)Default:0!MSPLIT=0!0=no(i.e.,puffsnotsplit)1=yes(i.e.,puffsaresplit)Chemicalmechanismflag(MCHEM)Default:1!MCHEM=1!0=chemicaltransformationnotmodeled1=transformationratescomputedinternally(MESOPUFFIIscheme)2=user-specifiedtransformationratesused3=transformationratescomputedinternally(RIVAD/ARM3scheme)5INVCAM02.inp10/23/20064=secondaryorganicaerosolformationcomputed(MESOPUFFIIschemeforOH)Aqueousphasetransformationflag(MAQCHEM)(UsedonlyifMCHEM=1,or3)Default:0!MAQCHEM=0!0=aqueousphasetransformationnotmodeled1=transformationratesadjustedforaqueousphasereactionsWetremovalmodeled?(MWET)Default:1!MWET=1!0=no1=yesDrydepositionmodeled?(MDRY)Default:1!MDRY=1!0=no1=yes(drydepositionmethodspecifiedforeachspeciesinInputGroup3)Gravitationalsettling(plumetilt)modeled?(MTILT)Default:0!MTILT=0!0=no1=yes(puffcenterfallsatthegravitationalsettlingvelocityfor1particlespecies)Restrictions:-MDRY=1-NSPEC=1(mustbeparticlespeciesaswell)-sg=0GEOMETRICSTANDARDDEVIATIONinGroup8issettozeroforasingleparticlediameterMethodusedtocomputedispersioncoefficients(MDISP)Default:3!MDISP=3!1=dispersioncoefficientscomputedfrommeasuredvaluesofturbulence,sigmav,sigmaw2=dispersioncoefficientsfrominternallycalculatedsigmav,sigmawusingmicrometeorologicalvariables(u*,w*,L,etc.)3=PGdispersioncoefficientsforRURALareas(computedusingtheISCSTmulti-segmentapproximation)andMPcoefficientsinurbanareas4=sameas3exceptPGcoefficientscomputedusingtheMESOPUFFIIeqns.5=CTDMsigmasusedforstableandneutralconditions.Forunstableconditions,sigmasarecomputedasin6INVCAM02.inp10/23/2006MDISP=3,describedabove.MDISP=5assumesthatmeasuredvaluesarereadSigma-v/sigma-theta,sigma-wmeasurementsused?(MTURBVW)(UsedonlyifMDISP=1or5)Default:3!MTURBVW=0!1=usesigma-vorsigma-thetameasurementsfromPROFILE.DATtocomputesigma-y(validforMETFM=1,2,3,4,5)2=usesigma-wmeasurementsfromPROFILE.DATtocomputesigma-z(validforMETFM=1,2,3,4,5)3=usebothsigma-(v/theta)andsigma-wfromPROFILE.DATtocomputesigma-yandsigma-z(validforMETFM=1,2,3,4,5)4=usesigma-thetameasurementsfromPLMMET.DATtocomputesigma-y(validonlyifMETFM=3)Back-upmethodusedtocomputedispersionwhenmeasuredturbulencedataaremissing(MDISP2)Default:3!MDISP2=3!(usedonlyifMDISP=1or5)2=dispersioncoefficientsfrominternallycalculatedsigmav,sigmawusingmicrometeorologicalvariables(u*,w*,L,etc.)3=PGdispersioncoefficientsforRURALareas(computedusingtheISCSTmulti-segmentapproximation)andMPcoefficientsinurbanareas4=sameas3exceptPGcoefficientscomputedusingtheMESOPUFFIIeqns.[DIAGNOSTICFEATURE]MethodusedforLagrangiantimescaleforSigma-y(usedonlyifMDISP=1,2orMDISP2=1,2)(MTAULY)Default:0!MTAULY=0!0=Draxlerdefault617.284(s)1=ComputedasLag.Length/(.75q)--afterSCIPUFF10<Directuserinput(s)--e.g.,306.9[DIAGNOSTICFEATURE]MethodusedforAdvective-DecaytimescaleforTurbulence(usedonlyifMDISP=2orMDISP2=2)(MTAUADV)Default:0!MTAUADV=0!0=Noturbulenceadvection1=Computed(OPTIONNOTIMPLEMENTED)10<Directuserinput(s)--e.g.,3007INVCAM02.inp10/23/2006Methodusedtocomputeturbulencesigma-v&sigma-wusingmicrometeorologicalvariables(UsedonlyifMDISP=2orMDISP2=2)(MCTURB)Default:1!MCTURB=1!1=StandardCALPUFFsubroutines2=AERMODsubroutinesPGsigma-y,zadj.forroughness?Default:0!MROUGH=0!(MROUGH)0=no1=yesPartialplumepenetrationofDefault:1!MPARTL=1!elevatedinversion?(MPARTL)0=no1=yesStrengthoftemperatureinversionDefault:0!MTINV=0!providedinPROFILE.DATextendedrecords?(MTINV)0=no(computedfrommeasured/defaultgradients)1=yesPDFusedfordispersionunderconvectiveconditions?Default:0!MPDF=0!(MPDF)0=no1=yesSub-GridTIBLmoduleusedforshoreline?Default:0!MSGTIBL=0!(MSGTIBL)0=no1=yesBoundaryconditions(concentration)modeled?Default:0!MBCON=0!(MBCON)0=no1=yes,usingformattedBCON.DATfile2=yes,usingunformattedCONC.DATfileAnalysesoffoggingandicingimpactsduetoemissionsfromarraysofmechanically-forcedcoolingtowerscanbeperformedusingCALPUFFinconjunctionwithacoolingtoweremissionsprocessor(CTEMISS)anditsassociatedpostprocessors.Hourlyemissionsofwatervaporandtemperaturefromeachcoolingtower8INVCAM02.inp10/23/2006cellarecomputedforthecurrentcellconfigurationandambientconditionsbyCTEMISS.CALPUFFmodelsthedispersionoftheseemissionsandprovidescloudinformationinaspecializedformatforfurtheranalysis.OutputtoFOG.DATisprovidedineither'plumemode'or'receptormode'format.ConfigureforFOGModeloutput?Default:0!MFOG=0!(MFOG)0=no1=yes-reportresultsinPLUMEModeformat2=yes-reportresultsinRECEPTORModeformatTestoptionsspecifiedtoseeiftheyconformtoregulatoryvalues?(MREG)Default:1!MREG=0!0=NOchecksaremade1=TechnicaloptionsmustconformtoUSEPALongRangeTransport(LRT)guidanceMETFM1or2AVET60.(min)PGTIME60.(min)MGAUSS1MCTADJ3MTRANS1MTIP1MCHEM1or3(ifmodelingSOx,NOx)MWET1MDRY1MDISP2or3MPDF0ifMDISP=31ifMDISP=2MROUGH0MPARTL1SYTDEP550.(m)MHFTSZ0!END!-------------------------------------------------------------------------------INPUTGROUP:3a,3b--Specieslist-------------------------------9INVCAM02.inp10/23/2006Subgroup(3a)------------Thefollowingspeciesaremodeled:!CSPEC=SO2!!END!!CSPEC=SO4!!END!!CSPEC=NOX!!END!!CSPEC=HNO3!!END!!CSPEC=NO3!!END!!CSPEC=POC081!!END!!CSPEC=POC056!!END!!CSPEC=PIC081!!END!!CSPEC=PIC056!!END!!CSPEC=PMC800!!END!!CSPEC=PMC425!!END!!CSPEC=PMF187!!END!!CSPEC=PMF112!!END!!CSPEC=PMF081!!END!!CSPEC=PMF056!!END!!CSPEC=EC187!!END!!CSPEC=EC112!!END!!CSPEC=EC081!!END!!CSPEC=EC056!!END!DryOUTPUTGROUPSPECIESMODELEDEMITTEDDEPOSITEDNUMBERNAME(0=NO,1=YES)(0=NO,1=YES)(0=NO,(0=NONE,(Limit:121=COMPUTED-GAS1=1stCGRUP,Characters2=COMPUTED-PARTICLE2=2ndCGRUP,inlength)3=USER-SPECIFIED)3=etc.)!SO2=1,1,1,0!!SO4=1,1,2,0!!NOX=1,1,1,0!!HNO3=1,0,1,0!!NO3=1,0,2,0!!POC081=1,1,2,0!!POC056=1,1,2,0!!PIC081=1,1,2,0!!PIC056=1,1,2,0!!PMC800=1,1,2,0!!PMC425=1,1,2,0!!PMF187=1,1,2,0!!PMF112=1,1,2,0!!PMF081=1,1,2,0!!PMF056=1,1,2,0!!EC187=1,1,2,0!!EC112=1,1,2,0!10INVCAM02.inp10/23/2006!EC081=1,1,2,0!!EC056=1,1,2,0!!END!-------------Subgroup(3b)-------------ThefollowingnamesareusedforSpecies-Groupsinwhichresultsforcertainspeciesarecombined(added)priortooutput.TheCGRUPnamewillbeusedasthespeciesnameinoutputfiles.Usethisfeaturetomodelspecificparticle-sizedistributionsbytreatingeachsize-rangeasaseparatespecies.Ordermustbeconsistentwith3(a)above.-------------------------------------------------------------------------------INPUTGROUP:4--MapProjectionandGridcontrolparameters--------------Projectionforall(X,Y):-------------------------Mapprojection(PMAP)Default:UTM!PMAP=LCC!UTM:UniversalTransverseMercatorTTM:TangentialTransverseMercatorLCC:LambertConformalConicPS:PolarStereographicEM:EquatorialMercatorLAZA:LambertAzimuthalEqualAreaFalseEastingandNorthing(km)attheprojectionorigin(UsedonlyifPMAP=TTM,LCC,orLAZA)(FEAST)Default=0.0!FEAST=0.000!(FNORTH)Default=0.0!FNORTH=0.000!UTMzone(1to60)(UsedonlyifPMAP=UTM)(IUTMZN)NoDefault!IUTMZN=0!HemisphereforUTMprojection?(UsedonlyifPMAP=UTM)(UTMHEM)Default:N!UTMHEM=N!N:Northernhemisphereprojection11INVCAM02.inp10/23/2006S:SouthernhemisphereprojectionLatitudeandLongitude(decimaldegrees)ofprojectionorigin(UsedonlyifPMAP=TTM,LCC,PS,EM,orLAZA)(RLAT0)NoDefault!RLAT0=40N!(RLON0)NoDefault!RLON0=97W!TTM:RLON0identifiescentral(trueN/S)meridianofprojectionRLAT0selectedforconvenienceLCC:RLON0identifiescentral(trueN/S)meridianofprojectionRLAT0selectedforconveniencePS:RLON0identifiescentral(gridN/S)meridianofprojectionRLAT0selectedforconvenienceEM:RLON0identifiescentralmeridianofprojectionRLAT0isREPLACEDby0.0N(Equator)LAZA:RLON0identifieslongitudeoftangent-pointofmappingplaneRLAT0identifieslatitudeoftangent-pointofmappingplaneMatchingparallel(s)oflatitude(decimaldegrees)forprojection(UsedonlyifPMAP=LCCorPS)(XLAT1)NoDefault!XLAT1=33N!(XLAT2)NoDefault!XLAT2=45N!LCC:ProjectionconeslicesthroughEarth'ssurfaceatXLAT1andXLAT2PS:ProjectionplaneslicesthroughEarthatXLAT1(XLAT2isnotused)----------Note:Latitudesandlongitudesshouldbepositive,andincludealetterN,S,E,orWindicatingnorthorsouthlatitude,andeastorwestlongitude.Forexample,35.9NLatitude=35.9N118.7ELongitude=118.7EDatum-region------------TheDatum-Regionforthecoordinatesisidentifiedbyacharacterstring.ManymappingproductscurrentlyavailableusethemodeloftheEarthknownastheWorldGeodeticSystem1984(WGS-84).Otherlocalmodelsmaybeinuse,andtheirselectioninCALMETwillmakeitsoutputconsistentwithlocalmappingproducts.ThelistofDatum-RegionswithofficialtransformationparametersisprovidedbytheNationalImageryandMappingAgency(NIMA).NIMADatum-Regions(Examples)------------------------------------------------------------------------------WGS-84WGS-84ReferenceEllipsoidandGeoid,Globalcoverage(WGS84)12INVCAM02.inp10/23/2006NAS-CNORTHAMERICAN1927Clarke1866Spheroid,MEANFORCONUS(NAD27)NAR-CNORTHAMERICAN1983GRS80Spheroid,MEANFORCONUS(NAD83)NWS-84NWS6370KMRadius,SphereESR-SESRIREFERENCE6371KMRadius,SphereDatum-regionforoutputcoordinates(DATUM)Default:WGS-84!DATUM=NWS-84!METEOROLOGICALGrid:RectangulargriddefinedforprojectionPMAP,withXtheEastingandYtheNorthingcoordinateNo.Xgridcells(NX)Nodefault!NX=160!No.Ygridcells(NY)Nodefault!NY=172!No.verticallayers(NZ)Nodefault!NZ=10!Gridspacing(DGRIDKM)Nodefault!DGRIDKM=12.!Units:kmCellfaceheights(ZFACE(nz+1))NodefaultsUnits:m!ZFACE=0.,20.,40.,80.,160.,320.,640.,1200.,2000.,3000.,4000.!ReferenceCoordinatesofSOUTHWESTcornerofgridcell(1,1):Xcoordinate(XORIGKM)Nodefault!XORIGKM=137.973!Ycoordinate(YORIGKM)Nodefault!YORIGKM=-1625.974!Units:kmCOMPUTATIONALGrid:ThecomputationalgridisidenticaltoorasubsetoftheMET.grid.Thelowerleft(LL)cornerofthecomputationalgridisatgridpoint(IBCOMP,JBCOMP)oftheMET.grid.Theupperright(UR)cornerofthecomputationalgridisatgridpoint(IECOMP,JECOMP)oftheMET.grid.ThegridspacingofthecomputationalgridisthesameastheMET.grid.XindexofLLcorner(IBCOMP)Nodefault!IBCOMP=81!(1<=IBCOMP<=NX)13INVCAM02.inp10/23/2006YindexofLLcorner(JBCOMP)Nodefault!JBCOMP=78!(1<=JBCOMP<=NY)XindexofURcorner(IECOMP)Nodefault!IECOMP=129!(1<=IECOMP<=NX)YindexofURcorner(JECOMP)Nodefault!JECOMP=112!(1<=JECOMP<=NY)SAMPLINGGrid(GRIDDEDRECEPTORS):Thelowerleft(LL)cornerofthesamplinggridisatgridpoint(IBSAMP,JBSAMP)oftheMET.grid.Theupperright(UR)cornerofthesamplinggridisatgridpoint(IESAMP,JESAMP)oftheMET.grid.Thesamplinggridmustbeidenticaltoorasubsetofthecomputationalgrid.Itmaybeanestedgridinsidethecomputationalgrid.ThegridspacingofthesamplinggridisDGRIDKM/MESHDN.Logicalflagindicatingifgriddedreceptorsareused(LSAMP)Default:T!LSAMP=F!(T=yes,F=no)XindexofLLcorner(IBSAMP)Nodefault!IBSAMP=1!(IBCOMP<=IBSAMP<=IECOMP)YindexofLLcorner(JBSAMP)Nodefault!JBSAMP=1!(JBCOMP<=JBSAMP<=JECOMP)XindexofURcorner(IESAMP)Nodefault!IESAMP=1!(IBCOMP<=IESAMP<=IECOMP)YindexofURcorner(JESAMP)Nodefault!JESAMP=1!(JBCOMP<=JESAMP<=JECOMP)Nestingfactorofthesamplinggrid(MESHDN)Default:1!MESHDN=1!(MESHDNisaninteger>=1)!END!-------------------------------------------------------------------------------14INVCAM02.inp10/23/2006INPUTGROUP:5--OutputOptions--------------**FILEDEFAULTVALUEVALUETHISRUN-------------------------------Concentrations(ICON)1!ICON=1!DryFluxes(IDRY)1!IDRY=0!WetFluxes(IWET)1!IWET=0!RelativeHumidity(IVIS)1!IVIS=0!(RHfileisrequiredforVISIBILITYanalyses)Usedatacompressionoptioninoutputfile?(LCOMPRS)Default:T!LCOMPRS=T!*0=Donotcreatefile,1=createfileQAPLOTFILEOUTPUTOPTION:Createastandardseriesofoutputfiles(e.g.locationsofsources,receptors,grids...)suitableforplotting?(IQAPLOT)Default:1!IQAPLOT=1!0=no1=yesDIAGNOSTICMASSFLUXOUTPUTOPTIONS:Massfluxacrossspecifiedboundariesforselectedspeciesreportedhourly?(IMFLX)Default:0!IMFLX=0!0=no1=yes(FLUXBDY.DATandMASSFLX.DATfilenamesarespecifiedinInputGroup0)Massbalanceforeachspeciesreportedhourly?(IMBAL)Default:0!IMBAL=0!0=no1=yes(MASSBAL.DATfilenameisspecifiedinInputGroup0)LINEPRINTEROUTPUTOPTIONS:15INVCAM02.inp10/23/2006Printconcentrations(ICPRT)Default:0!ICPRT=0!Printdryfluxes(IDPRT)Default:0!IDPRT=0!Printwetfluxes(IWPRT)Default:0!IWPRT=0!(0=Donotprint,1=Print)Concentrationprintinterval(ICFRQ)inhoursDefault:1!ICFRQ=1!Dryfluxprintinterval(IDFRQ)inhoursDefault:1!IDFRQ=1!Wetfluxprintinterval(IWFRQ)inhoursDefault:1!IWFRQ=1!UnitsforLinePrinterOutput(IPRTU)Default:1!IPRTU=3!forforConcentrationDeposition1=g/m**3g/m**2/s2=mg/m**3mg/m**2/s3=ug/m**3ug/m**2/s4=ng/m**3ng/m**2/s5=OdourUnitsMessagestrackingprogressofrunwrittentothescreen?(IMESG)Default:2!IMESG=2!0=no1=yes(advectionstep,puffID)2=yes(YYYYJJJHH,#oldpuffs,#emittedpuffs)SPECIES(orGROUPforcombinedspecies)LISTFOROUTPUTOPTIONS----CONCENTRATIONS----------DRYFLUXES------------WETFLUXES--------MASSFLUX--SPECIES/GROUPPRINTED?SAVEDONDISK?PRINTED?SAVEDONDISK?PRINTED?SAVEDONDISK?SAVEDONDISK?----------------------------------------------------------------------------------------------!SO2=0,1,0,0,0,0,0!!SO4=0,1,0,0,0,0,0!!NOX=0,1,0,0,0,0,0!!HNO3=0,1,0,0,0,0,0!!NO3=0,1,0,0,0,0,0!!POC081=0,1,0,0,0,0,0!!POC056=0,1,0,0,0,0,0!!PIC081=0,1,0,0,0,0,0!!PIC056=0,1,0,0,0,0,0!16INVCAM02.inp10/23/2006!PMC800=0,1,0,0,0,0,0!!PMC425=0,1,0,0,0,0,0!!PMF187=0,1,0,0,0,0,0!!PMF112=0,1,0,0,0,0,0!!PMF081=0,1,0,0,0,0,0!!PMF056=0,1,0,0,0,0,0!!EC187=0,1,0,0,0,0,0!!EC112=0,1,0,0,0,0,0!!EC081=0,1,0,0,0,0,0!!EC056=0,1,0,0,0,0,0!OPTIONSFORPRINTING"DEBUG"QUANTITIES(muchoutput)Logicalfordebugoutput(LDEBUG)Default:F!LDEBUG=F!Firstpufftotrack(IPFDEB)Default:1!IPFDEB=1!Numberofpuffstotrack(NPFDEB)Default:1!NPFDEB=10!Met.periodtostartoutput(NN1)Default:1!NN1=10!Met.periodtoendoutput(NN2)Default:10!NN2=10!!END!-------------------------------------------------------------------------------INPUTGROUP:6a,6b,&6c--Subgridscalecomplexterraininputs----------------------------------------Subgroup(6a)---------------Numberofterrainfeatures(NHILL)Default:0!NHILL=0!Numberofspecialcomplexterrainreceptors(NCTREC)Default:0!NCTREC=0!TerrainandCTSGReceptordataforCTSGhillsinputinCTDMformat?(MHILL)NoDefault!MHILL=0!1=HillandReceptordatacreated17INVCAM02.inp10/23/2006byCTDMprocessors&readfromHILL.DATandHILLRCT.DATfiles2=HilldatacreatedbyOPTHILL&inputbelowinSubgroup(6b);ReceptordatainSubgroup(6c)FactortoconverthorizontaldimensionsDefault:1.0!XHILL2M=0.!tometers(MHILL=1)FactortoconvertverticaldimensionsDefault:1.0!ZHILL2M=0.!tometers(MHILL=1)X-originofCTDMsystemrelativetoNoDefault!XCTDMKM=0.0E00!CALPUFFcoordinatesystem,inKilometers(MHILL=1)Y-originofCTDMsystemrelativetoNoDefault!YCTDMKM=0.0E00!CALPUFFcoordinatesystem,inKilometers(MHILL=1)!END!---------------Subgroup(6b)---------------1**HILLinformationHILLXCYCTHETAHZGRIDRELIEFEXPO1EXPO2SCALE1SCALE2AMAX1AMAX2NO.(km)(km)(deg.)(m)(m)(m)(m)(m)(m)(m)(m)--------------------------------------------------------------------------------Subgroup(6c)---------------COMPLEXTERRAINRECEPTORINFORMATIONXRCTYRCTZRCTXHH(km)(km)(m)----------------------------------------1DescriptionofComplexTerrainVariables:18INVCAM02.inp10/23/2006XC,YC=CoordinatesofcenterofhillTHETAH=Orientationofmajoraxisofhill(clockwisefromNorth)ZGRID=Heightofthe0ofthegridabovemeansealevelRELIEF=HeightofthecrestofthehillabovethegridelevationEXPO1=Hill-shapeexponentforthemajoraxisEXPO2=Hill-shapeexponentforthemajoraxisSCALE1=HorizontallengthscalealongthemajoraxisSCALE2=HorizontallengthscalealongtheminoraxisAMAX=MaximumallowedaxislengthforthemajoraxisBMAX=MaximumallowedaxislengthforthemajoraxisXRCT,YRCT=CoordinatesofthecomplexterrainreceptorsZRCT=Heightoftheground(MSL)atthecomplexterrainReceptorXHH=Hillnumberassociatedwitheachcomplexterrainreceptor(NOTE:MUSTBEENTEREDASAREALNUMBER)**NOTE:DATAforeachhillandCTSGreceptoraretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUP:7--Chemicalparametersfordrydepositionofgases--------------SPECIESDIFFUSIVITYALPHASTARREACTIVITYMESOPHYLLRESISTANCEHENRY'SLAWCOEFFICIENTNAME(cm**2/s)(s/cm)(dimensionless)---------------------------------------------------------------------------------!SO2=0.1509,1000.,8.,0.,0.04!!NOX=0.1656,1.,8.,5.,3.5!!HNO3=0.1628,1.,18.,0.,0.00000008!!END!-------------------------------------------------------------------------------INPUTGROUP:8--Sizeparametersfordrydepositionofparticles--------------19INVCAM02.inp10/23/2006ForSINGLESPECIES,themeanandstandarddeviationareusedtocomputeadepositionvelocityforNINT(seegroup9)size-ranges,andthesearethenaveragedtoobtainameandepositionvelocity.ForGROUPEDSPECIES,thesizedistributionshouldbeexplicitlyspecified(bythe'species'inthegroup),andthestandarddeviationforeachshouldbeenteredas0.Themodelwillthenusethedepositionvelocityforthestatedmeandiameter.SPECIESGEOMETRICMASSMEANGEOMETRICSTANDARDNAMEDIAMETERDEVIATION(microns)(microns)--------------------------------------------!SO4=0.48,2.!!NO3=0.48,2.!!POC081=0.8125,0.!!POC056=0.5625,0.!!PIC081=0.8125,0.!!PIC056=0.5625,0.!!PMC800=8.,0.!!PMC425=4.25,0.!!PMF187=1.875,0.!!PMF112=1.125,0.!!PMF081=0.8125,0.!!PMF056=0.5625,0.!!EC187=1.875,0.!!EC112=1.125,0.!!EC081=0.8125,0.!!EC056=0.5625,0.!!END!-------------------------------------------------------------------------------INPUTGROUP:9--Miscellaneousdrydepositionparameters--------------Referencecuticleresistance(s/cm)(RCUTR)Default:30!RCUTR=30.0!Referencegroundresistance(s/cm)(RGR)Default:10!RGR=10.0!Referencepollutantreactivity(REACTR)Default:8!REACTR=8.0!Numberofparticle-sizeintervalsusedtoevaluateeffectiveparticledepositionvelocity(NINT)Default:9!NINT=9!20INVCAM02.inp10/23/2006Vegetationstateinunirrigatedareas(IVEG)Default:1!IVEG=1!IVEG=1foractiveandunstressedvegetationIVEG=2foractiveandstressedvegetationIVEG=3forinactivevegetation!END!-------------------------------------------------------------------------------INPUTGROUP:10--WetDepositionParameters---------------ScavengingCoefficient--Units:(sec)**(-1)PollutantLiquidPrecip.FrozenPrecip.-------------------------------------!SO2=3.0E-05,0.0E00!!SO4=1.0E-04,3.0E-05!!NOX=0.0E00,0.0E00!!HNO3=6.0E-05,0.0E00!!NO3=1.0E-04,3.0E-05!!POC081=1.0E-04,3.0E-05!!POC056=1.0E-04,3.0E-05!!PIC081=1.0E-04,3.0E-05!!PIC056=1.0E-04,3.0E-05!!PMC800=1.0E-04,3.0E-05!!PMC425=1.0E-04,3.0E-05!!PMF187=1.0E-04,3.0E-05!!PMF112=1.0E-04,3.0E-05!!PMF081=1.0E-04,3.0E-05!!PMF056=1.0E-04,3.0E-05!!EC187=1.0E-04,3.0E-05!!EC112=1.0E-04,3.0E-05!!EC081=1.0E-04,3.0E-05!!EC056=1.0E-04,3.0E-05!!END!-------------------------------------------------------------------------------INPUTGROUP:11--ChemistryParameters---------------Ozonedatainputoption(MOZ)Default:1!MOZ=1!21INVCAM02.inp10/23/2006(UsedonlyifMCHEM=1,3,or4)0=useamonthlybackgroundozonevalue1=readhourlyozoneconcentrationsfromtheOZONE.DATdatafileMonthlyozoneconcentrations(UsedonlyifMCHEM=1,3,or4andMOZ=0orMOZ=1andallhourlyO3datamissing)(BCKO3)inppbDefault:12*80.!BCKO3=29.71,35.12,36.10,43.28,44.47,47.19,47.52,46.81,37.20,27.20,27.66,27.83!Monthlyammoniaconcentrations(UsedonlyifMCHEM=1,or3)(BCKNH3)inppbDefault:12*10.!BCKNH3=0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50!NighttimeSO2lossrate(RNITE1)inpercent/hourDefault:0.2!RNITE1=.2!NighttimeNOxlossrate(RNITE2)inpercent/hourDefault:2.0!RNITE2=2.0!NighttimeHNO3formationrate(RNITE3)inpercent/hourDefault:2.0!RNITE3=2.0!H2O2datainputoption(MH2O2)Default:1!MH2O2=1!(UsedonlyifMAQCHEM=1)0=useamonthlybackgroundH2O2value1=readhourlyH2O2concentrationsfromtheH2O2.DATdatafileMonthlyH2O2concentrations(UsedonlyifMQACHEM=1andMH2O2=0orMH2O2=1andallhourlyH2O2datamissing)(BCKH2O2)inppbDefault:12*1.!BCKH2O2=1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00!---DataforSECONDARYORGANICAEROSOL(SOA)Option(usedonlyifMCHEM=4)TheSOAmoduleusesmonthlyvaluesof:Fineparticulateconcentrationinug/m^3(BCKPMF)Organicfractionoffineparticulate(OFRAC)VOC/NOXratio(afterreaction)(VCNX)tocharacterizetheairmasswhencomputingtheformationofSOAfromVOCemissions.Typicalvaluesforseveraldistinctairmasstypesare:22INVCAM02.inp10/23/2006Month123456789101112JanFebMarAprMayJunJulAugSepOctNovDecCleanContinentalBCKPMF1.1.1.1.1.1.1.1.1.1.1.1.OFRAC.15.15.20.20.20.20.20.20.20.20.20.15VCNX50.50.50.50.50.50.50.50.50.50.50.50.CleanMarine(surface)BCKPMF.5.5.5.5.5.5.5.5.5.5.5.5OFRAC.25.25.30.30.30.30.30.30.30.30.30.25VCNX50.50.50.50.50.50.50.50.50.50.50.50.Urban-lowbiogenic(controlspresent)BCKPMF30.30.30.30.30.30.30.30.30.30.30.30.OFRAC.20.20.25.25.25.25.25.25.20.20.20.20VCNX4.4.4.4.4.4.4.4.4.4.4.4.Urban-highbiogenic(controlspresent)BCKPMF60.60.60.60.60.60.60.60.60.60.60.60.OFRAC.25.25.30.30.30.55.55.55.35.35.35.25VCNX15.15.15.15.15.15.15.15.15.15.15.15.RegionalPlumeBCKPMF20.20.20.20.20.20.20.20.20.20.20.20.OFRAC.20.20.25.35.25.40.40.40.30.30.30.20VCNX15.15.15.15.15.15.15.15.15.15.15.15.Urban-nocontrolspresentBCKPMF100.100.100.100.100.100.100.100.100.100.100.100.OFRAC.30.30.35.35.35.55.55.55.35.35.35.30VCNX2.2.2.2.2.2.2.2.2.2.2.2.Default:CleanContinental!BCKPMF=1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00!!OFRAC=0.15,0.15,0.20,0.20,0.20,0.20,0.20,0.20,0.20,0.20,0.20,0.15!!VCNX=50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00!!END!-------------------------------------------------------------------------------INPUTGROUP:12--Misc.DispersionandComputationalParameters---------------23INVCAM02.inp10/23/2006Horizontalsizeofpuff(m)beyondwhichtime-dependentdispersionequations(Heffter)areusedtodeterminesigma-yandsigma-z(SYTDEP)Default:550.!SYTDEP=5.5E02!SwitchforusingHeffterequationforsigmazasabove(0=NotuseHeffter;1=useHeffter(MHFTSZ)Default:0!MHFTSZ=0!Stabilityclassusedtodetermineplumegrowthratesforpuffsabovetheboundarylayer(JSUP)Default:5!JSUP=5!Verticaldispersionconstantforstableconditions(k1inEqn.2.7-3)(CONK1)Default:0.01!CONK1=.01!Verticaldispersionconstantforneutral/unstableconditions(k2inEqn.2.7-4)(CONK2)Default:0.1!CONK2=.1!FactorfordeterminingTransition-pointfromSchulman-SciretoHuber-SnyderBuildingDownwashscheme(SSusedforHs<Hb+TBD*HL)(TBD)Default:0.5!TBD=.5!TBD<0==>alwaysuseHuber-SnyderTBD=1.5==>alwaysuseSchulman-ScireTBD=0.5==>ISCTransition-pointRangeoflandusecategoriesforwhichurbandispersionisassumed(IURB1,IURB2)Default:10!IURB1=10!19!IURB2=19!Sitecharacterizationparametersforsingle-pointMetdatafiles---------(neededforMETFM=2,3,4,5)Landusecategoryformodelingdomain(ILANDUIN)Default:20!ILANDUIN=20!Roughnesslength(m)formodelingdomain(Z0IN)Default:0.25!Z0IN=.25!Leafareaindexformodelingdomain(XLAIIN)Default:3.0!XLAIIN=3.0!Elevationabovesealevel(m)(ELEVIN)Default:0.0!ELEVIN=.0!Latitude(degrees)formetlocation24INVCAM02.inp10/23/2006(XLATIN)Default:-999.!XLATIN=-999.0!Longitude(degrees)formetlocation(XLONIN)Default:-999.!XLONIN=-999.0!Specializedinformationforinterpretingsingle-pointMetdatafiles-----Anemometerheight(m)(UsedonlyifMETFM=2,3)(ANEMHT)Default:10.!ANEMHT=10.0!FormoflateralturbulancedatainPROFILE.DATfile(UsedonlyifMETFM=4,5orMTURBVW=1or3)(ISIGMAV)Default:1!ISIGMAV=1!0=readsigma-theta1=readsigma-vChoiceofmixingheights(UsedonlyifMETFM=4)(IMIXCTDM)Default:0!IMIXCTDM=0!0=readPREDICTEDmixingheights1=readOBSERVEDmixingheightsMaximumlengthofaslug(met.gridunits)(XMXLEN)Default:1.0!XMXLEN=1.0!Maximumtraveldistanceofapuff/slug(ingridunits)duringonesamplingstep(XSAMLEN)Default:1.0!XSAMLEN=1.0!MaximumNumberofslugs/puffsreleasefromonesourceduringonetimestep(MXNEW)Default:99!MXNEW=99!MaximumNumberofsamplingstepsforonepuff/slugduringonetimestep(MXSAM)Default:99!MXSAM=99!Numberofiterationsusedwhencomputingthetransportwindforasamplingstepthatincludesgradualrise(forCALMETandPROFILEwinds)(NCOUNT)Default:2!NCOUNT=2!Minimumsigmayforanewpuff/slug(m)(SYMIN)Default:1.0!SYMIN=1.0!Minimumsigmazforanewpuff/slug(m)(SZMIN)Default:1.0!SZMIN=1.0!Defaultminimumturbulencevelocitiessigma-vandsigma-w25INVCAM02.inp10/23/2006foreachstabilityclassoverlandandoverwater(m/s)(SVMIN(12)andSWMIN(12))----------LAND-------------------WATER----------StabClass:ABCDEFABCDEF------------------------------------DefaultSVMIN:.50,.50,.50,.50,.50,.50,.37,.37,.37,.37,.37,.37DefaultSWMIN:.20,.12,.08,.06,.03,.016,.20,.12,.08,.06,.03,.016!SVMIN=0.500,0.500,0.500,0.500,0.500,0.500,0.370,0.370,0.370,0.370,0.370,0.370!!SWMIN=0.200,0.120,0.080,0.060,0.030,0.016,0.200,0.120,0.080,0.060,0.030,0.016!Divergencecriterionfordw/dzacrosspuffusedtoinitiateadjustmentforhorizontalconvergence(1/s)PartialadjustmentstartsatCDIV(1),andfulladjustmentisreachedatCDIV(2)(CDIV(2))Default:0.0,0.0!CDIV=.0,.0!Minimumwindspeed(m/s)allowedfornon-calmconditions.Alsousedasminimumspeedreturnedwhenusingpower-lawextrapolationtowardsurface(WSCALM)Default:0.5!WSCALM=.5!Maximummixingheight(m)(XMAXZI)Default:3000.!XMAXZI=3000.0!Minimummixingheight(m)(XMINZI)Default:50.!XMINZI=50.0!Defaultwindspeedclasses--5upperbounds(m/s)areentered;the6thclasshasnoupperlimit(WSCAT(5))Default:ISCRURAL:1.54,3.09,5.14,8.23,10.8(10.8+)WindSpeedClass:12345---------------!WSCAT=1.54,3.09,5.14,8.23,10.80!Defaultwindspeedprofilepower-lawexponentsforstabilities1-6(PLX0(6))Default:ISCRURALvaluesISCRURAL:.07,.07,.10,.15,.35,.55ISCURBAN:.15,.15,.20,.25,.30,.30StabilityClass:ABCDEF------------------26INVCAM02.inp10/23/2006!PLX0=0.07,0.07,0.10,0.15,0.35,0.55!DefaultpotentialtemperaturegradientforstableclassesE,F(degK/m)(PTG0(2))Default:0.020,0.035!PTG0=0.020,0.035!Defaultplumepathcoefficientsforeachstabilityclass(usedwhenoptionforpartialplumeheightterrainadjustmentisselected--MCTADJ=3)(PPC(6))StabilityClass:ABCDEFDefaultPPC:.50,.50,.50,.50,.35,.35------------------!PPC=0.50,0.50,0.50,0.50,0.35,0.35!Slug-to-pufftransitioncriterionfactorequaltosigma-y/lengthofslug(SL2PF)Default:10.!SL2PF=5.0!Puff-splittingcontrolvariables------------------------VERTICALSPLIT--------------Numberofpuffsthatresulteverytimeapuffissplit-nsplit=2meansthat1puffsplitsinto2(NSPLIT)Default:3!NSPLIT=3!Time(s)ofadaywhensplitpuffsareeligibletobesplitonceagain;thisistypicallysetonceperday,aroundsunsetbeforenocturnalsheardevelops.24values:0ismidnight(00:00)and23is11PM(23:00)0=donotre-split1=eligibleforre-split(IRESPLIT(24))Default:Hour17=1!IRESPLIT=0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,1,0,0,0,0,0,0!Splitisallowedonlyiflasthour'smixingheight(m)exceedsaminimumvalue(ZISPLIT)Default:100.!ZISPLIT=100.0!Splitisallowedonlyifratiooflasthour'smixinghttothemaximummixinghtexperiencedbythepuffislessthanamaximumvalue(thispostponesasplituntilanocturnallayerdevelops)(ROLDMAX)Default:0.25!ROLDMAX=0.25!27INVCAM02.inp10/23/2006HORIZONTALSPLIT----------------Numberofpuffsthatresulteverytimeapuffissplit-nsplith=5meansthat1puffsplitsinto5(NSPLITH)Default:5!NSPLITH=5!Minimumsigma-y(GridCellsUnits)ofpuffbeforeitmaybesplit(SYSPLITH)Default:1.0!SYSPLITH=1.0!Minimumpuffelongationrate(SYSPLITH/hr)duetowindshear,beforeitmaybesplit(SHSPLITH)Default:2.!SHSPLITH=2.0!Minimumconcentration(g/m^3)ofeachspeciesinpuffbeforeitmaybesplitEnterarrayofNSPECvalues;ifasinglevalueisentered,itwillbeusedforALLspecies(CNSPLITH)Default:1.0E-07!CNSPLITH=1.0E-07!Integrationcontrolvariables------------------------FractionalconvergencecriterionfornumericalSLUGsamplingintegration(EPSSLUG)Default:1.0e-04!EPSSLUG=1.0E-04!FractionalconvergencecriterionfornumericalAREAsourceintegration(EPSAREA)Default:1.0e-06!EPSAREA=1.0E-06!Trajectorystep-length(m)usedfornumericalriseintegration(DSRISE)Default:1.0!DSRISE=1.0!BoundaryCondition(BC)Puffcontrolvariables------------------------Minimumheight(m)towhichBCpuffsaremixedastheyareemitted(MBCON=2ONLY).Actualheightisresettothecurrentmixingheightatthereleasepointifgreaterthanthisminimum.(HTMINBC)Default:500.!HTMINBC=500.0!Searchradius(km)aboutareceptorforsamplingnearestBCpuff.BCpuffsaretypicallyemittedwithaspacingofonegridcelllength,sothesearchradiusshouldbegreaterthanDGRIDKM.(RSAMPBC)Default:10.!RSAMPBC=15.0!Near-Surfacedepletionadjustmenttoconcentrationprofileusedwhen28INVCAM02.inp10/23/2006samplingBCpuffs?(MDEPBC)Default:1!MDEPBC=0!0=ConcentrationisNOTadjustedfordepletion1=AdjustConcentrationfordepletion!END!-------------------------------------------------------------------------------INPUTGROUPS:13a,13b,13c,13d--Pointsourceparameters-----------------------------------------------Subgroup(13a)---------------Numberofpointsourceswithparametersprovidedbelow(NPT1)Nodefault!NPT1=3!Unitsusedforpointsourceemissionsbelow(IPTU)Default:1!IPTU=1!1=g/s2=kg/hr3=lb/hr4=tons/yr5=OdourUnit*m**3/s(vol.fluxofodourcompound)6=OdourUnit*m**3/min7=metrictons/yrNumberofsource-speciescombinationswithvariableemissionsscalingfactorsprovidedbelowin(13d)(NSPT1)Default:0!NSPT1=0!Numberofpointsourceswithvariableemissionparametersprovidedinexternalfile(NPT2)Nodefault!NPT2=0!(IfNPT2>0,thesepointsourceemissionsarereadfromthefile:PTEMARB.DAT)!END!---------------Subgroup(13b)---------------29INVCAM02.inp10/23/2006aPOINTSOURCE:CONSTANTDATA-----------------------------bcSourceXYStackBaseStackExitExitBldg.EmissionNo.CoordinateCoordinateHeightElevationDiameterVel.Temp.DwashRates(km)(km)(m)(m)(m)(m/s)(deg.K)------------------------------------------------------------------------1!SRCNAM=P13a!1!X=1491.195,-503.713,60.96,64.0,3.35,9.66,444.3,.0,6.61E+01,1.27E+00,1.68E+01,0.00E+00,0.00E+00,1.59E-01,1.59E-01,0.00E+00,0.00E+00,3.52E-01,5.03E-01,2.01E-01,7.54E-02,2.01E-01,1.51E-01,0.00E+00,0.00E+00,0.00E+00,2.48E-02!1!ZPLTFM=.0!1!FMFAC=1.0!!END!2!SRCNAM=P13b!2!X=1491.195,-503.713,60.96,64.0,3.35,9.66,444.3,.0,6.61E+01,1.27E+00,1.68E+01,0.00E+00,0.00E+00,1.59E-01,1.59E-01,0.00E+00,0.00E+00,3.52E-01,5.03E-01,2.01E-01,7.54E-02,2.01E-01,1.51E-01,0.00E+00,0.00E+00,0.00E+00,2.48E-02!2!ZPLTFM=.0!2!FMFAC=1.0!!END!3!SRCNAM=NB27-32!3!X=1490.761,-503.846,31.70,64.0,1.37,4.27,298.2,.0,0.00E+00,0.00E+00,0.00E+00,0.00E+00,0.00E+00,1.70E-01,1.70E-01,0.00E+00,0.00E+00,0.00E+00,0.00E+00,1.71E-01,1.71E-01,1.71E-01,1.71E-01,0.00E+00,0.00E+00,0.00E+00,0.00E+00!3!ZPLTFM=.0!3!FMFAC=1.0!!END!--------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.SRCNAMisa12-characternameforasource(Nodefault)Xisanarrayholdingthesourcedatalistedbythecolumnheadings(Nodefault)SIGYZIisanarrayholdingtheinitialsigma-yandsigma-z(m)(Default:0.,0.)ZPLTFMistheplatformheight(m)forsourcesinfluencedbyanisolated30INVCAM02.inp10/23/2006structurethathasasignificantopenareabetweenthesurfaceandthebulkofthestructure,suchasanoffshoreoilplatform.TheBaseElevationisthatofthesurface(groundorocean),andtheStackHeightisthereleaseheightabovetheBase(notabovetheplatform).BuildingheightsenteredinSubgroup13cmustbethoseofthebuildingsontheplatform,measuredfromtheplatformdeck.ZPLTFMisusedonlywithMBDW=1(ISCdownwashmethod)forsourceswithbuildingdownwash.(Default:0.0)FMFACisaverticalmomentumfluxfactor(0.or1.0)usedtorepresenttheeffectofrain-capsorotherphysicalconfigurationsthatreducemomentumriseassociatedwiththeactualexitvelocity.(Default:1.0--fullmomentumused)b0.=Nobuildingdownwashmodeled,1.=downwashmodeledNOTE:mustbeenteredasaREALnumber(i.e.,withdecimalpoint)cAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyIPTU(e.g.1forg/s).---------------Subgroup(13c)---------------BUILDINGDIMENSIONDATAFORSOURCESSUBJECTTODOWNWASH-------------------------------------------------------SourceaNo.Effectivebuildingheight,width,lengthandX/Yoffset(inmeters)every10degrees.LENGTH,XBADJ,andYBADJareonlyneededforMBDW=2(PRIMEdownwashoption)----------------------------------------------------------------------------------aBuildingheight,width,length,andX/Yoffsetfromthesourcearetreatedasaseparateinputsubgroupforeachsourceandthereforemustendwithaninputgroupterminator.TheX/Yoffsetistheposition,relativetothestack,ofthecenteroftheupwindfaceoftheprojectedbuilding,withthex-axispointingalongtheflowdirection.---------------Subgroup(13d)---------------31INVCAM02.inp10/23/2006aPOINTSOURCE:VARIABLEEMISSIONSDATA---------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin13b.Factorsenteredmultiplytheratesin13b.Skipsourcesherethathaveconstantemissions.Formoreelaboratevariationinsourceparameters,usePTEMARB.DATandNPT2>0.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant1=Diurnalcycle(24scalingfactors:hours1-24)2=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupperbounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUPS:14a,14b,14c,14d--Areasourceparameters-----------------------------------------------Subgroup(14a)---------------Numberofpolygonareasourceswithparametersspecifiedbelow(NAR1)Nodefault!NAR1=0!Unitsusedforareasourceemissionsbelow(IARU)Default:1!IARU=1!1=g/m**2/s32INVCAM02.inp10/23/20062=kg/m**2/hr3=lb/m**2/hr4=tons/m**2/yr5=OdourUnit*m/s(vol.flux/m**2ofodourcompound)6=OdourUnit*m/min7=metrictons/m**2/yrNumberofsource-speciescombinationswithvariableemissionsscalingfactorsprovidedbelowin(14d)(NSAR1)Default:0!NSAR1=0!Numberofbuoyantpolygonareasourceswithvariablelocationandemissionparameters(NAR2)Nodefault!NAR2=0!(IfNAR2>0,ALLparameterdataforthesesourcesarereadfromthefile:BAEMARB.DAT)!END!---------------Subgroup(14b)---------------aAREASOURCE:CONSTANTDATA----------------------------bSourceEffect.BaseInitialEmissionNo.HeightElevationSigmazRates(m)(m)(m)--------------------------------------------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.bAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyIARU(e.g.1forg/m**2/s).---------------Subgroup(14c)---------------COORDINATES(km)FOREACHVERTEX(4)OFEACHPOLYGON--------------------------------------------------------33INVCAM02.inp10/23/2006SourceaNo.OrderedlistofXfollowedbylistofY,groupedbysource--------------------------------------------------------------------------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.---------------Subgroup(14d)---------------aAREASOURCE:VARIABLEEMISSIONSDATA--------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin14b.Factorsenteredmultiplytheratesin14b.Skipsourcesherethathaveconstantemissions.Formoreelaboratevariationinsourceparameters,useBAEMARB.DATandNAR2>0.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant1=Diurnalcycle(24scalingfactors:hours1-24)2=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupperbounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------34INVCAM02.inp10/23/2006INPUTGROUPS:15a,15b,15c--Linesourceparameters------------------------------------------Subgroup(15a)---------------Numberofbuoyantlinesourceswithvariablelocationandemissionparameters(NLN2)Nodefault!NLN2=0!(IfNLN2>0,ALLparameterdataforthesesourcesarereadfromthefile:LNEMARB.DAT)Numberofbuoyantlinesources(NLINES)Nodefault!NLINES=0!Unitsusedforlinesourceemissionsbelow(ILNU)Default:1!ILNU=1!1=g/s2=kg/hr3=lb/hr4=tons/yr5=OdourUnit*m**3/s(vol.fluxofodourcompound)6=OdourUnit*m**3/min7=metrictons/yrNumberofsource-speciescombinationswithvariableemissionsscalingfactorsprovidedbelowin(15c)(NSLN1)Default:0!NSLN1=0!Maximumnumberofsegmentsusedtomodeleachline(MXNSEG)Default:7!MXNSEG=7!ThefollowingvariablesarerequiredonlyifNLINES>0.Theyareusedinthebuoyantlinesourceplumerisecalculations.NumberofdistancesatwhichDefault:6!NLRISE=6!transitionalriseiscomputedAveragebuildinglength(XL)Nodefault!XL=.0!(inmeters)Averagebuildingheight(HBL)Nodefault!HBL=.0!(inmeters)Averagebuildingwidth(WBL)Nodefault!WBL=.0!(inmeters)35INVCAM02.inp10/23/2006Averagelinesourcewidth(WML)Nodefault!WML=.0!(inmeters)Averageseparationbetweenbuildings(DXL)Nodefault!DXL=.0!(inmeters)Averagebuoyancyparameter(FPRIMEL)Nodefault!FPRIMEL=.0!(inm**4/s**3)!END!---------------Subgroup(15b)---------------BUOYANTLINESOURCE:CONSTANTDATA----------------------------------aSourceBeg.XBeg.YEnd.XEnd.YReleaseBaseEmissionNo.CoordinateCoordinateCoordinateCoordinateHeightElevationRates(km)(km)(km)(km)(m)(m)------------------------------------------------------------------------------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.bAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyILNTU(e.g.1forg/s).---------------Subgroup(15c)---------------aBUOYANTLINESOURCE:VARIABLEEMISSIONSDATA----------------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin15b.Factorsenteredmultiplytheratesin15b.Skipsourcesherethathaveconstantemissions.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant36INVCAM02.inp10/23/20061=Diurnalcycle(24scalingfactors:hours1-24)2=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupperbounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUPS:16a,16b,16c--Volumesourceparameters------------------------------------------Subgroup(16a)---------------Numberofvolumesourceswithparametersprovidedin16b,c(NVL1)Nodefault!NVL1=0!Unitsusedforvolumesourceemissionsbelowin16b(IVLU)Default:1!IVLU=1!1=g/s2=kg/hr3=lb/hr4=tons/yr5=OdourUnit*m**3/s(vol.fluxofodourcompound)6=OdourUnit*m**3/min7=metrictons/yrNumberofsource-speciescombinationswithvariableemissionsscalingfactorsprovidedbelowin(16c)(NSVL1)Default:0!NSVL1=0!37INVCAM02.inp10/23/2006Numberofvolumesourceswithvariablelocationandemissionparameters(NVL2)Nodefault!NVL2=0!(IfNVL2>0,ALLparameterdataforthesesourcesarereadfromtheVOLEMARB.DATfile(s))!END!---------------Subgroup(16b)---------------aVOLUMESOURCE:CONSTANTDATA------------------------------bXYEffect.BaseInitialInitialEmissionCoordinateCoordinateHeightElevationSigmaySigmazRates(km)(km)(m)(m)(m)(m)----------------------------------------------------------------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.bAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyIVLU(e.g.1forg/s).---------------Subgroup(16c)---------------aVOLUMESOURCE:VARIABLEEMISSIONSDATA----------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin16b.Factorsenteredmultiplytheratesin16b.Skipsourcesherethathaveconstantemissions.Formoreelaboratevariationinsourceparameters,useVOLEMARB.DATandNVL2>0.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant1=Diurnalcycle(24scalingfactors:hours1-24)38INVCAM02.inp10/23/20062=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupperbounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUPS:17a&17b--Non-gridded(discrete)receptorinformation--------------------------------------Subgroup(17a)---------------Numberofnon-griddedreceptors(NREC)Nodefault!NREC=1076!!END!---------------Subgroup(17b)---------------aNON-GRIDDED(DISCRETE)RECEPTORDATA------------------------------------XYGroundHeightbReceptorCoordinateCoordinateElevationAboveGroundNo.(km)(km)(m)(m)-------------------------------------------------1!X=1609.918,-633.619,0,0.00!!END!2!X=1610.682,-633.471,1,0.00!!END!3!X=1610.506,-632.561,1,0.00!!END!4!X=1611.27,-632.414,1,0.00!!END!5!X=1611.094,-631.504,1,0.00!!END!39INVCAM02.inp10/23/20066!X=1611.858,-631.356,1,0.00!!END!7!X=1610.154,-630.742,1,0.00!!END!8!X=1610.918,-630.594,1,0.00!!END!9!X=1611.682,-630.446,1,0.00!!END!10!X=1612.446,-630.298,1,0.00!!END!11!X=1610.742,-629.684,1,0.00!!END!12!X=1611.506,-629.536,1,0.00!!END!13!X=1612.269,-629.389,1,0.00!!END!14!X=1610.566,-628.774,0,0.00!!END!15!X=1611.33,-628.627,1,0.00!!END!16!X=1612.093,-628.479,1,0.00!!END!17!X=1612.857,-628.331,1,0.00!!END!18!X=1610.39,-627.865,1,0.00!!END!19!X=1611.154,-627.717,1,0.00!!END!20!X=1610.214,-626.955,1,0.00!!END!21!X=1610.978,-626.807,1,0.00!!END!22!X=1611.741,-626.66,1,0.00!!END!23!X=1610.802,-625.898,1,0.00!!END!24!X=1611.565,-625.75,1,0.00!!END!25!X=1610.626,-624.988,1,0.00!!END!26!X=1611.389,-624.84,2,0.00!!END!27!X=1612.152,-624.692,1,0.00!!END!28!X=1615.968,-623.952,0,0.00!!END!29!X=1611.213,-623.931,1,0.00!!END!30!X=1611.976,-623.783,1,0.00!!END!31!X=1616.554,-622.895,0,0.00!!END!32!X=1611.037,-623.021,1,0.00!!END!33!X=1611.8,-622.873,1,0.00!!END!34!X=1612.386,-621.816,1,0.00!!END!35!X=1613.149,-621.668,1,0.00!!END!36!X=1617.727,-620.779,0,0.00!!END!37!X=1612.973,-620.758,1,0.00!!END!38!X=1613.736,-620.61,1,0.00!!END!39!X=1621.949,-618.069,0,0.00!!END!40!X=1622.711,-617.92,1,0.00!!END!41!X=1623.474,-617.771,1,0.00!!END!42!X=1614.146,-618.643,1,0.00!!END!43!X=1623.297,-616.862,1,0.00!!END!44!X=1624.059,-616.713,1,0.00!!END!45!X=1624.821,-616.564,1,0.00!!END!46!X=1625.584,-616.415,1,0.00!!END!47!X=1633.208,-614.921,1,0.00!!END!48!X=1633.97,-614.771,0,0.00!!END!49!X=1614.732,-617.586,1,0.00!!END!50!X=1621.594,-616.25,0,0.00!!END!51!X=1622.357,-616.102,1,0.00!!END!52!X=1623.119,-615.953,1,0.00!!END!53!X=1623.881,-615.804,1,0.00!!END!54!X=1624.644,-615.655,1,0.00!!END!40INVCAM02.inp10/23/200655!X=1625.406,-615.506,1,0.00!!END!56!X=1626.169,-615.357,1,0.00!!END!57!X=1626.931,-615.208,1,0.00!!END!58!X=1627.693,-615.059,1,0.00!!END!59!X=1628.456,-614.909,2,0.00!!END!60!X=1629.218,-614.76,2,0.00!!END!61!X=1629.98,-614.611,1,0.00!!END!62!X=1630.742,-614.461,2,0.00!!END!63!X=1631.505,-614.311,1,0.00!!END!64!X=1633.791,-613.862,0,0.00!!END!65!X=1615.318,-616.528,1,0.00!!END!66!X=1616.08,-616.38,1,0.00!!END!67!X=1616.843,-616.232,1,0.00!!END!68!X=1620.654,-615.49,0,0.00!!END!69!X=1621.417,-615.341,1,0.00!!END!70!X=1622.179,-615.192,1,0.00!!END!71!X=1622.942,-615.044,1,0.00!!END!72!X=1623.704,-614.895,1,0.00!!END!73!X=1624.466,-614.746,1,0.00!!END!74!X=1625.228,-614.597,1,0.00!!END!75!X=1628.277,-614,1,0.00!!END!76!X=1629.04,-613.851,1,0.00!!END!77!X=1632.088,-613.253,1,0.00!!END!78!X=1634.375,-612.803,0,0.00!!END!79!X=1619.715,-614.729,0,0.00!!END!80!X=1620.477,-614.58,1,0.00!!END!81!X=1621.24,-614.432,1,0.00!!END!82!X=1622.002,-614.283,1,0.00!!END!83!X=1622.764,-614.134,1,0.00!!END!84!X=1623.526,-613.986,1,0.00!!END!85!X=1624.288,-613.837,1,0.00!!END!86!X=1625.051,-613.688,1,0.00!!END!87!X=1625.813,-613.539,1,0.00!!END!88!X=1626.575,-613.389,1,0.00!!END!89!X=1627.337,-613.24,1,0.00!!END!90!X=1629.624,-612.792,1,0.00!!END!91!X=1630.386,-612.643,1,0.00!!END!92!X=1631.148,-612.493,1,0.00!!END!93!X=1631.91,-612.344,1,0.00!!END!94!X=1634.196,-611.894,0,0.00!!END!95!X=1618.776,-613.968,1,0.00!!END!96!X=1619.538,-613.82,1,0.00!!END!97!X=1620.3,-613.671,1,0.00!!END!98!X=1621.062,-613.523,1,0.00!!END!99!X=1621.824,-613.374,1,0.00!!END!100!X=1622.587,-613.225,1,0.00!!END!101!X=1623.349,-613.076,1,0.00!!END!102!X=1624.111,-612.927,1,0.00!!END!103!X=1624.873,-612.778,1,0.00!!END!41INVCAM02.inp10/23/2006104!X=1625.635,-612.629,1,0.00!!END!105!X=1626.397,-612.48,1,0.00!!END!106!X=1627.159,-612.331,1,0.00!!END!107!X=1627.921,-612.182,1,0.00!!END!108!X=1628.683,-612.033,1,0.00!!END!109!X=1629.445,-611.883,1,0.00!!END!110!X=1630.207,-611.734,1,0.00!!END!111!X=1630.969,-611.584,1,0.00!!END!112!X=1634.017,-610.985,0,0.00!!END!113!X=1620.123,-612.762,1,0.00!!END!114!X=1620.885,-612.613,1,0.00!!END!115!X=1621.647,-612.465,1,0.00!!END!116!X=1622.409,-612.316,1,0.00!!END!117!X=1623.171,-612.167,1,0.00!!END!118!X=1623.933,-612.018,1,0.00!!END!119!X=1624.695,-611.869,1,0.00!!END!120!X=1625.457,-611.72,1,0.00!!END!121!X=1626.219,-611.571,1,0.00!!END!122!X=1626.981,-611.422,1,0.00!!END!123!X=1627.743,-611.273,1,0.00!!END!124!X=1628.505,-611.123,1,0.00!!END!125!X=1633.077,-610.226,0,0.00!!END!126!X=1633.839,-610.076,1,0.00!!END!127!X=1634.6,-609.927,1,0.00!!END!128!X=1621.47,-611.555,1,0.00!!END!129!X=1622.232,-611.407,1,0.00!!END!130!X=1622.993,-611.258,1,0.00!!END!131!X=1623.755,-611.109,1,0.00!!END!132!X=1624.517,-610.96,1,0.00!!END!133!X=1625.279,-610.811,1,0.00!!END!134!X=1626.041,-610.662,1,0.00!!END!135!X=1626.803,-610.513,1,0.00!!END!136!X=1627.565,-610.364,1,0.00!!END!137!X=1628.327,-610.214,1,0.00!!END!138!X=1629.089,-610.065,1,0.00!!END!139!X=1629.851,-609.916,1,0.00!!END!140!X=1630.613,-609.766,1,0.00!!END!141!X=1634.422,-609.018,0,0.00!!END!142!X=1624.34,-610.051,1,0.00!!END!143!X=1625.102,-609.902,1,0.00!!END!144!X=1625.863,-609.753,1,0.00!!END!145!X=1626.625,-609.604,1,0.00!!END!146!X=1627.387,-609.455,1,0.00!!END!147!X=1628.149,-609.305,1,0.00!!END!148!X=1628.911,-609.156,1,0.00!!END!149!X=1629.672,-609.007,1,0.00!!END!150!X=1630.434,-608.857,1,0.00!!END!151!X=1634.243,-608.109,0,0.00!!END!152!X=1628.732,-608.247,1,0.00!!END!42INVCAM02.inp10/23/2006153!X=1629.494,-608.098,1,0.00!!END!154!X=1630.256,-607.948,1,0.00!!END!155!X=1631.017,-607.799,1,0.00!!END!156!X=1629.316,-607.189,1,0.00!!END!157!X=1630.077,-607.039,1,0.00!!END!158!X=1630.839,-606.89,1,0.00!!END!159!X=1631.6,-606.74,1,0.00!!END!160!X=1629.899,-606.13,1,0.00!!END!161!X=1630.66,-605.981,1,0.00!!END!162!X=1631.422,-605.831,1,0.00!!END!163!X=1629.721,-605.221,1,0.00!!END!164!X=1630.482,-605.072,1,0.00!!END!165!X=1201.214,-417.246,521,0.00!!END!166!X=1204.191,-416.805,521,0.00!!END!167!X=1189.038,-417.173,521,0.00!!END!168!X=1190.527,-416.954,522,0.00!!END!169!X=1192.015,-416.736,523,0.00!!END!170!X=1193.503,-416.517,521,0.00!!END!171!X=1194.991,-416.298,538,0.00!!END!172!X=1196.48,-416.079,550,0.00!!END!173!X=1197.968,-415.859,640,0.00!!END!174!X=1199.456,-415.639,607,0.00!!END!175!X=1200.944,-415.419,523,0.00!!END!176!X=1202.432,-415.199,548,0.00!!END!177!X=1203.92,-414.978,524,0.00!!END!178!X=1205.408,-414.757,608,0.00!!END!179!X=1208.384,-414.315,546,0.00!!END!180!X=1209.871,-414.093,566,0.00!!END!181!X=1211.359,-413.871,541,0.00!!END!182!X=1212.847,-413.649,530,0.00!!END!183!X=1181.33,-416.432,683,0.00!!END!184!X=1182.818,-416.216,711,0.00!!END!185!X=1184.306,-415.998,583,0.00!!END!186!X=1185.795,-415.781,599,0.00!!END!187!X=1187.283,-415.564,561,0.00!!END!188!X=1188.771,-415.346,582,0.00!!END!189!X=1190.259,-415.128,703,0.00!!END!190!X=1191.747,-414.909,707,0.00!!END!191!X=1193.235,-414.69,522,0.00!!END!192!X=1194.722,-414.471,760,0.00!!END!193!X=1196.21,-414.252,846,0.00!!END!194!X=1197.698,-414.033,952,0.00!!END!195!X=1199.186,-413.813,765,0.00!!END!196!X=1200.674,-413.593,1067,0.00!!END!197!X=1202.161,-413.372,915,0.00!!END!198!X=1203.649,-413.152,730,0.00!!END!199!X=1205.136,-412.931,822,0.00!!END!200!X=1206.624,-412.71,748,0.00!!END!201!X=1208.112,-412.488,544,0.00!!END!43INVCAM02.inp10/23/2006202!X=1209.599,-412.267,706,0.00!!END!203!X=1211.086,-412.045,627,0.00!!END!204!X=1212.574,-411.822,845,0.00!!END!205!X=1214.061,-411.6,772,0.00!!END!206!X=1215.549,-411.377,836,0.00!!END!207!X=1220.01,-410.707,665,0.00!!END!208!X=1175.112,-415.469,554,0.00!!END!209!X=1176.6,-415.254,760,0.00!!END!210!X=1178.088,-415.038,805,0.00!!END!211!X=1179.576,-414.822,703,0.00!!END!212!X=1181.064,-414.605,729,0.00!!END!213!X=1182.552,-414.388,699,0.00!!END!214!X=1184.04,-414.171,1109,0.00!!END!215!X=1185.528,-413.954,1001,0.00!!END!216!X=1187.015,-413.737,811,0.00!!END!217!X=1188.503,-413.519,522,0.00!!END!218!X=1189.991,-413.301,581,0.00!!END!219!X=1191.478,-413.082,629,0.00!!END!220!X=1192.966,-412.864,634,0.00!!END!221!X=1194.453,-412.645,582,0.00!!END!222!X=1195.941,-412.425,612,0.00!!END!223!X=1197.428,-412.206,944,0.00!!END!224!X=1198.916,-411.986,1281,0.00!!END!225!X=1200.403,-411.766,1427,0.00!!END!226!X=1201.891,-411.546,1221,0.00!!END!227!X=1203.378,-411.325,1030,0.00!!END!228!X=1204.865,-411.105,983,0.00!!END!229!X=1206.352,-410.883,894,0.00!!END!230!X=1207.84,-410.662,675,0.00!!END!231!X=1209.327,-410.44,950,0.00!!END!232!X=1210.814,-410.219,915,0.00!!END!233!X=1212.301,-409.996,732,0.00!!END!234!X=1213.788,-409.774,980,0.00!!END!235!X=1216.762,-409.328,1020,0.00!!END!236!X=1218.249,-409.105,886,0.00!!END!237!X=1219.736,-408.881,615,0.00!!END!238!X=1221.222,-408.657,680,0.00!!END!239!X=1176.335,-413.427,767,0.00!!END!240!X=1177.823,-413.211,919,0.00!!END!241!X=1179.311,-412.994,905,0.00!!END!242!X=1180.798,-412.778,911,0.00!!END!243!X=1182.286,-412.561,965,0.00!!END!244!X=1183.773,-412.344,837,0.00!!END!245!X=1185.261,-412.127,1055,0.00!!END!246!X=1186.748,-411.91,716,0.00!!END!247!X=1188.235,-411.692,825,0.00!!END!248!X=1189.723,-411.474,609,0.00!!END!249!X=1191.21,-411.255,814,0.00!!END!250!X=1192.697,-411.037,1006,0.00!!END!44INVCAM02.inp10/23/2006251!X=1194.184,-410.818,1036,0.00!!END!252!X=1195.672,-410.599,732,0.00!!END!253!X=1197.159,-410.379,746,0.00!!END!254!X=1198.646,-410.16,929,0.00!!END!255!X=1200.133,-409.94,1008,0.00!!END!256!X=1201.62,-409.72,1288,0.00!!END!257!X=1203.107,-409.499,1266,0.00!!END!258!X=1204.594,-409.278,1218,0.00!!END!259!X=1206.081,-409.057,959,0.00!!END!260!X=1207.568,-408.836,681,0.00!!END!261!X=1209.054,-408.614,920,0.00!!END!262!X=1210.541,-408.392,1170,0.00!!END!263!X=1212.028,-408.17,956,0.00!!END!264!X=1213.514,-407.948,818,0.00!!END!265!X=1215.001,-407.725,1223,0.00!!END!266!X=1216.488,-407.502,1270,0.00!!END!267!X=1217.974,-407.279,872,0.00!!END!268!X=1219.461,-407.055,694,0.00!!END!269!X=1220.947,-406.832,963,0.00!!END!270!X=1222.434,-406.608,859,0.00!!END!271!X=1223.92,-406.383,1000,0.00!!END!272!X=1170.121,-412.46,365,0.00!!END!273!X=1171.608,-412.245,406,0.00!!END!274!X=1173.096,-412.03,600,0.00!!END!275!X=1174.583,-411.815,591,0.00!!END!276!X=1176.07,-411.599,644,0.00!!END!277!X=1177.558,-411.383,1036,0.00!!END!278!X=1179.045,-411.167,1309,0.00!!END!279!X=1180.532,-410.951,1262,0.00!!END!280!X=1182.019,-410.734,1261,0.00!!END!281!X=1183.506,-410.517,1072,0.00!!END!282!X=1184.994,-410.3,1199,0.00!!END!283!X=1186.481,-410.083,1097,0.00!!END!284!X=1187.968,-409.865,720,0.00!!END!285!X=1189.455,-409.647,640,0.00!!END!286!X=1190.942,-409.429,873,0.00!!END!287!X=1192.429,-409.21,852,0.00!!END!288!X=1193.915,-408.991,978,0.00!!END!289!X=1195.402,-408.772,809,0.00!!END!290!X=1196.889,-408.553,761,0.00!!END!291!X=1198.376,-408.333,987,0.00!!END!292!X=1199.863,-408.113,874,0.00!!END!293!X=1201.349,-407.893,1147,0.00!!END!294!X=1202.836,-407.673,1323,0.00!!END!295!X=1204.322,-407.452,1221,0.00!!END!296!X=1205.809,-407.231,1097,0.00!!END!297!X=1207.295,-407.01,800,0.00!!END!298!X=1208.782,-406.788,942,0.00!!END!299!X=1210.268,-406.566,1167,0.00!!END!45INVCAM02.inp10/23/2006300!X=1211.755,-406.344,1052,0.00!!END!301!X=1213.241,-406.122,1012,0.00!!END!302!X=1214.727,-405.899,1002,0.00!!END!303!X=1216.214,-405.676,1143,0.00!!END!304!X=1217.7,-405.453,998,0.00!!END!305!X=1219.186,-405.23,710,0.00!!END!306!X=1220.672,-405.006,998,0.00!!END!307!X=1222.158,-404.782,907,0.00!!END!308!X=1223.644,-404.558,1200,0.00!!END!309!X=1225.13,-404.333,1173,0.00!!END!310!X=1226.616,-404.108,1067,0.00!!END!311!X=1228.102,-403.883,896,0.00!!END!312!X=1229.588,-403.658,799,0.00!!END!313!X=1231.074,-403.432,683,0.00!!END!314!X=1169.857,-410.632,330,0.00!!END!315!X=1171.344,-410.418,523,0.00!!END!316!X=1172.831,-410.203,599,0.00!!END!317!X=1174.318,-409.988,769,0.00!!END!318!X=1175.805,-409.772,831,0.00!!END!319!X=1177.292,-409.556,941,0.00!!END!320!X=1178.779,-409.34,1150,0.00!!END!321!X=1180.266,-409.124,1194,0.00!!END!322!X=1181.753,-408.907,1084,0.00!!END!323!X=1183.24,-408.69,1206,0.00!!END!324!X=1184.727,-408.473,1225,0.00!!END!325!X=1186.213,-408.256,987,0.00!!END!326!X=1187.7,-408.038,1063,0.00!!END!327!X=1189.187,-407.82,873,0.00!!END!328!X=1190.673,-407.602,921,0.00!!END!329!X=1192.16,-407.384,1233,0.00!!END!330!X=1193.646,-407.165,1006,0.00!!END!331!X=1195.133,-406.946,1024,0.00!!END!332!X=1196.619,-406.726,792,0.00!!END!333!X=1198.106,-406.507,1015,0.00!!END!334!X=1199.592,-406.287,1094,0.00!!END!335!X=1201.079,-406.067,996,0.00!!END!336!X=1202.565,-405.846,1148,0.00!!END!337!X=1204.051,-405.626,1368,0.00!!END!338!X=1205.537,-405.405,1052,0.00!!END!339!X=1207.023,-405.184,958,0.00!!END!340!X=1208.51,-404.962,988,0.00!!END!341!X=1209.996,-404.74,1019,0.00!!END!342!X=1211.482,-404.518,1344,0.00!!END!343!X=1212.968,-404.296,1246,0.00!!END!344!X=1214.454,-404.073,1377,0.00!!END!345!X=1215.94,-403.85,1135,0.00!!END!346!X=1217.426,-403.627,1196,0.00!!END!347!X=1218.911,-403.404,851,0.00!!END!348!X=1220.397,-403.18,883,0.00!!END!46INVCAM02.inp10/23/2006349!X=1221.883,-402.956,1060,0.00!!END!350!X=1223.369,-402.732,1207,0.00!!END!351!X=1224.854,-402.507,1245,0.00!!END!352!X=1226.34,-402.283,1045,0.00!!END!353!X=1227.826,-402.058,1068,0.00!!END!354!X=1229.311,-401.832,870,0.00!!END!355!X=1230.797,-401.607,782,0.00!!END!356!X=1241.194,-400.02,1326,0.00!!END!357!X=1169.593,-408.805,453,0.00!!END!358!X=1171.08,-408.59,439,0.00!!END!359!X=1172.567,-408.376,582,0.00!!END!360!X=1174.054,-408.16,664,0.00!!END!361!X=1175.54,-407.945,770,0.00!!END!362!X=1177.027,-407.729,853,0.00!!END!363!X=1178.514,-407.513,810,0.00!!END!364!X=1180,-407.297,979,0.00!!END!365!X=1181.487,-407.08,809,0.00!!END!366!X=1182.973,-406.864,818,0.00!!END!367!X=1184.46,-406.646,1027,0.00!!END!368!X=1185.946,-406.429,1372,0.00!!END!369!X=1187.432,-406.211,1203,0.00!!END!370!X=1188.919,-405.994,975,0.00!!END!371!X=1190.405,-405.775,1077,0.00!!END!372!X=1191.891,-405.557,1343,0.00!!END!373!X=1193.377,-405.338,1463,0.00!!END!374!X=1194.864,-405.119,1193,0.00!!END!375!X=1196.35,-404.9,932,0.00!!END!376!X=1197.836,-404.68,1059,0.00!!END!377!X=1199.322,-404.461,1144,0.00!!END!378!X=1200.808,-404.24,1231,0.00!!END!379!X=1202.294,-404.02,1197,0.00!!END!380!X=1203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9.405,-386.527,765,0.00!!END!767!X=1220.888,-386.303,961,0.00!!END!768!X=1222.37,-386.079,963,0.00!!END!769!X=1223.853,-385.855,1391,0.00!!END!770!X=1225.336,-385.63,1485,0.00!!END!771!X=1226.818,-385.405,1332,0.00!!END!772!X=1228.301,-385.18,1520,0.00!!END!773!X=1229.783,-384.955,1705,0.00!!END!774!X=1231.266,-384.729,1572,0.00!!END!775!X=1232.748,-384.503,1802,0.00!!END!776!X=1234.23,-384.277,1371,0.00!!END!777!X=1235.713,-384.05,1674,0.00!!END!778!X=1237.195,-383.823,1676,0.00!!END!779!X=1238.677,-383.596,1586,0.00!!END!780!X=1240.159,-383.369,1727,0.00!!END!781!X=1241.641,-383.142,1516,0.00!!END!782!X=1243.123,-382.914,1359,0.00!!END!783!X=1244.606,-382.686,1097,0.00!!END!784!X=1246.088,-382.457,1022,0.00!!END!785!X=1247.569,-382.228,1016,0.00!!END!786!X=1249.051,-382,732,0.00!!END!787!X=1198.372,-387.805,652,0.00!!END!788!X=1199.855,-387.585,1164,0.00!!END!789!X=1201.338,-387.365,1129,0.00!!END!55INVCAM02.inp10/23/2006790!X=1202.821,-387.144,1070,0.00!!END!791!X=1204.304,-386.924,942,0.00!!END!792!X=1205.786,-386.703,668,0.00!!END!793!X=1207.269,-386.481,425,0.00!!END!794!X=1208.752,-386.26,532,0.00!!END!795!X=1210.235,-386.038,696,0.00!!END!796!X=1211.717,-385.816,673,0.00!!END!797!X=1213.2,-385.593,775,0.00!!END!798!X=1214.682,-385.371,1061,0.00!!END!799!X=1216.165,-385.148,939,0.00!!END!800!X=1217.647,-384.925,817,0.00!!END!801!X=1219.13,-384.701,763,0.00!!END!802!X=1220.612,-384.478,616,0.00!!END!803!X=1222.094,-384.254,877,0.00!!END!804!X=1223.577,-384.029,892,0.00!!END!805!X=1225.059,-383.805,910,0.00!!END!806!X=1226.541,-383.58,1134,0.00!!END!807!X=1228.023,-383.355,1358,0.00!!END!808!X=1229.505,-383.13,1512,0.00!!END!809!X=1230.988,-382.904,1674,0.00!!END!810!X=1232.47,-382.678,1806,0.00!!END!811!X=1233.952,-382.452,1678,0.00!!END!812!X=1235.434,-382.225,1725,0.00!!END!813!X=1236.916,-381.999,1256,0.00!!END!814!X=1238.397,-381.772,1160,0.00!!END!815!X=1239.879,-381.544,1382,0.00!!END!816!X=1241.361,-381.317,1289,0.00!!END!817!X=1242.843,-381.089,1584,0.00!!END!818!X=1244.325,-380.861,1317,0.00!!END!819!X=1245.806,-380.633,1170,0.00!!END!820!X=1211.444,-383.99,548,0.00!!END!821!X=1212.926,-383.768,730,0.00!!END!822!X=1214.408,-383.545,699,0.00!!END!823!X=1215.89,-383.323,749,0.00!!END!824!X=1217.372,-383.099,624,0.00!!END!825!X=1218.854,-382.876,608,0.00!!END!826!X=1220.336,-382.652,530,0.00!!END!827!X=1221.818,-382.428,797,0.00!!END!828!X=1223.3,-382.204,1103,0.00!!END!829!X=1224.782,-381.98,1110,0.00!!END!830!X=1226.264,-381.755,1130,0.00!!END!831!X=1227.746,-381.53,1499,0.00!!END!832!X=1229.228,-381.305,1742,0.00!!END!833!X=1230.71,-381.079,1769,0.00!!END!834!X=1232.191,-380.853,1639,0.00!!END!835!X=1233.673,-380.627,1342,0.00!!END!836!X=1235.155,-380.401,1247,0.00!!END!837!X=1236.636,-380.174,1168,0.00!!END!838!X=1238.118,-379.947,1012,0.00!!END!56INVCAM02.inp10/23/2006839!X=1239.599,-379.72,959,0.00!!END!840!X=1241.081,-379.492,1366,0.00!!END!841!X=1242.562,-379.265,1348,0.00!!END!842!X=1244.044,-379.037,1526,0.00!!END!843!X=1245.525,-378.808,1042,0.00!!END!844!X=1214.134,-381.72,488,0.00!!END!845!X=1215.616,-381.497,515,0.00!!END!846!X=1217.097,-381.274,491,0.00!!END!847!X=1218.579,-381.051,550,0.00!!END!848!X=1220.061,-380.827,579,0.00!!END!849!X=1221.542,-380.603,781,0.00!!END!850!X=1223.024,-380.379,900,0.00!!END!851!X=1224.506,-380.155,1059,0.00!!END!852!X=1225.987,-379.93,1123,0.00!!END!853!X=1227.469,-379.705,1307,0.00!!END!854!X=1228.95,-379.48,1166,0.00!!END!855!X=1230.432,-379.254,1302,0.00!!END!856!X=1231.913,-379.028,1672,0.00!!END!857!X=1233.394,-378.802,1533,0.00!!END!858!X=1234.876,-378.576,1429,0.00!!END!859!X=1236.357,-378.349,1457,0.00!!END!860!X=1237.838,-378.122,1391,0.00!!END!861!X=1239.319,-377.895,937,0.00!!END!862!X=1240.8,-377.668,1015,0.00!!END!863!X=1242.281,-377.44,1056,0.00!!END!864!X=1243.763,-377.212,1071,0.00!!END!865!X=1245.244,-376.984,1060,0.00!!END!866!X=1218.304,-379.225,427,0.00!!END!867!X=1219.785,-379.002,480,0.00!!END!868!X=1221.266,-378.778,488,0.00!!END!869!X=1222.748,-378.554,624,0.00!!END!870!X=1224.229,-378.33,761,0.00!!END!871!X=1225.71,-378.105,732,0.00!!END!872!X=1227.191,-377.88,881,0.00!!END!873!X=1228.673,-377.655,821,0.00!!END!874!X=1230.154,-377.429,1000,0.00!!END!875!X=1231.635,-377.204,1094,0.00!!END!876!X=1233.116,-376.978,1208,0.00!!END!877!X=1234.597,-376.751,860,0.00!!END!878!X=1236.078,-376.525,857,0.00!!END!879!X=1237.558,-376.298,1391,0.00!!END!880!X=1239.039,-376.071,1265,0.00!!END!881!X=1240.52,-375.843,1067,0.00!!END!882!X=1242.001,-375.616,921,0.00!!END!883!X=1243.482,-375.388,611,0.00!!END!884!X=1226.914,-376.055,608,0.00!!END!885!X=1229.876,-375.604,699,0.00!!END!886!X=1231.356,-375.379,785,0.00!!END!887!X=1232.837,-375.153,892,0.00!!END!57INVCAM02.inp10/23/2006888!X=1234.318,-374.927,622,0.00!!END!889!X=1235.798,-374.7,762,0.00!!END!890!X=1237.279,-374.473,1130,0.00!!END!891!X=1238.759,-374.246,1458,0.00!!END!892!X=1240.24,-374.019,1097,0.00!!END!893!X=1241.72,-373.791,823,0.00!!END!894!X=1243.201,-373.563,603,0.00!!END!895!X=1232.558,-373.328,534,0.00!!END!896!X=1234.039,-373.102,545,0.00!!END!897!X=1235.519,-372.875,582,0.00!!END!898!X=1236.999,-372.649,735,0.00!!END!899!X=1238.479,-372.422,885,0.00!!END!900!X=1239.959,-372.194,873,0.00!!END!901!X=1349.498,-350.859,468,0.00!!END!902!X=1350.236,-350.735,457,0.00!!END!903!X=1349.345,-349.949,478,0.00!!END!904!X=1350.083,-349.825,576,0.00!!END!905!X=1347.717,-349.286,550,0.00!!END!906!X=1348.455,-349.162,472,0.00!!END!907!X=1349.193,-349.039,721,0.00!!END!908!X=1349.931,-348.915,759,0.00!!END!909!X=1350.668,-348.791,600,0.00!!END!910!X=1351.406,-348.667,517,0.00!!END!911!X=1347.564,-348.376,641,0.00!!END!912!X=1348.302,-348.252,439,0.00!!END!913!X=1349.04,-348.129,607,0.00!!END!914!X=1349.778,-348.005,881,0.00!!END!915!X=1350.516,-347.881,758,0.00!!END!916!X=1347.412,-347.466,920,0.00!!END!917!X=1348.15,-347.342,665,0.00!!END!918!X=1348.887,-347.218,458,0.00!!END!919!X=1349.625,-347.095,585,0.00!!END!920!X=1350.363,-346.971,870,0.00!!END!921!X=1347.997,-346.432,826,0.00!!END!922!X=1348.735,-346.308,518,0.00!!END!923!X=1349.472,-346.185,525,0.00!!END!924!X=1350.21,-346.061,695,0.00!!END!925!X=1350.948,-345.937,892,0.00!!END!926!X=1347.845,-345.522,874,0.00!!END!927!X=1348.582,-345.398,581,0.00!!END!928!X=1349.32,-345.274,573,0.00!!END!929!X=1350.057,-345.151,664,0.00!!END!930!X=1348.43,-344.488,728,0.00!!END!931!X=1349.167,-344.364,694,0.00!!END!932!X=1349.905,-344.241,914,0.00!!END!933!X=1348.277,-343.578,756,0.00!!END!934!X=1349.014,-343.454,631,0.00!!END!935!X=1349.752,-343.331,944,0.00!!END!936!X=1348.124,-342.668,826,0.00!!END!58INVCAM02.inp10/23/2006937!X=1348.862,-342.544,624,0.00!!END!938!X=1349.599,-342.42,965,0.00!!END!939!X=1347.972,-341.758,732,0.00!!END!940!X=1348.709,-341.634,685,0.00!!END!941!X=1349.446,-341.51,889,0.00!!END!942!X=1347.819,-340.848,890,0.00!!END!943!X=1348.556,-340.724,697,0.00!!END!944!X=1349.294,-340.6,827,0.00!!END!945!X=1346.93,-340.061,1096,0.00!!END!946!X=1347.667,-339.938,749,0.00!!END!947!X=1348.404,-339.814,816,0.00!!END!948!X=1349.141,-339.69,1106,0.00!!END!949!X=1346.777,-339.151,1055,0.00!!END!950!X=1347.514,-339.027,762,0.00!!END!951!X=1348.251,-338.904,909,0.00!!END!952!X=1348.988,-338.78,1092,0.00!!END!953!X=1345.888,-338.364,941,0.00!!END!954!X=1346.625,-338.241,813,0.00!!END!955!X=1347.362,-338.117,953,0.00!!END!956!X=1348.098,-337.994,1097,0.00!!END!957!X=1348.835,-337.87,1083,0.00!!END!958!X=1345.735,-337.454,923,0.00!!END!959!X=1346.472,-337.331,924,0.00!!END!960!X=1347.209,-337.207,901,0.00!!END!961!X=1347.946,-337.084,1114,0.00!!END!962!X=1348.683,-336.96,1219,0.00!!END!963!X=1345.583,-336.544,946,0.00!!END!964!X=1346.32,-336.421,983,0.00!!END!965!X=1347.056,-336.297,1142,0.00!!END!966!X=1346.167,-335.511,1063,0.00!!END!967!X=1273.44,-416.507,1629,0.00!!END!968!X=1274.184,-416.39,1586,0.00!!END!969!X=1274.928,-416.274,1370,0.00!!END!970!X=1275.672,-416.157,1274,0.00!!END!971!X=1276.416,-416.04,1181,0.00!!END!972!X=1268.832,-416.294,1183,0.00!!END!973!X=1269.576,-416.178,1416,0.00!!END!974!X=1270.321,-416.062,1541,0.00!!END!975!X=1271.065,-415.945,1677,0.00!!END!976!X=1271.809,-415.828,1640,0.00!!END!977!X=1272.553,-415.712,1770,0.00!!END!978!X=1273.297,-415.595,1679,0.00!!END!979!X=1274.041,-415.478,1585,0.00!!END!980!X=1274.785,-415.361,1529,0.00!!END!981!X=1275.529,-415.244,1309,0.00!!END!982!X=1276.273,-415.127,1128,0.00!!END!983!X=1267.946,-415.498,1097,0.00!!END!984!X=1268.69,-415.382,1217,0.00!!END!985!X=1269.434,-415.266,1536,0.00!!END!59INVCAM02.inp10/23/2006986!X=1270.178,-415.149,1463,0.00!!END!987!X=1270.922,-415.033,1436,0.00!!END!988!X=1271.666,-414.916,1629,0.00!!END!989!X=1272.41,-414.8,1771,0.00!!END!990!X=1273.154,-414.683,1622,0.00!!END!991!X=1273.898,-414.566,1425,0.00!!END!992!X=1274.641,-414.449,1312,0.00!!END!993!X=1275.385,-414.332,1362,0.00!!END!994!X=1276.129,-414.215,1067,0.00!!END!995!X=1276.873,-414.098,1162,0.00!!END!996!X=1277.617,-413.981,1399,0.00!!END!997!X=1267.059,-414.702,1029,0.00!!END!998!X=1267.803,-414.586,1227,0.00!!END!999!X=1268.547,-414.47,1505,0.00!!END!1000!X=1269.291,-414.354,1347,0.00!!END!1001!X=1270.035,-414.237,1317,0.00!!END!1002!X=1270.779,-414.121,1536,0.00!!END!1003!X=1271.523,-414.004,1675,0.00!!END!1004!X=1272.267,-413.887,1729,0.00!!END!1005!X=1273.01,-413.771,1523,0.00!!END!1006!X=1273.754,-413.654,1544,0.00!!END!1007!X=1274.498,-413.537,1429,0.00!!END!1008!X=1275.242,-413.42,1315,0.00!!END!1009!X=1275.986,-413.303,1068,0.00!!END!1010!X=1276.73,-413.186,1066,0.00!!END!1011!X=1277.473,-413.069,1352,0.00!!END!1012!X=1266.173,-413.906,1024,0.00!!END!1013!X=1266.917,-413.79,1296,0.00!!END!1014!X=1267.661,-413.674,1404,0.00!!END!1015!X=1268.404,-413.558,1373,0.00!!END!1016!X=1269.148,-413.441,1198,0.00!!END!1017!X=1269.892,-413.325,1198,0.00!!END!1018!X=1270.636,-413.208,1419,0.00!!END!1019!X=1271.38,-413.092,1571,0.00!!END!1020!X=1272.124,-412.975,1741,0.00!!END!1021!X=1272.867,-412.859,1717,0.00!!END!1022!X=1273.611,-412.742,1616,0.00!!END!1023!X=1274.355,-412.625,1569,0.00!!END!1024!X=1275.099,-412.508,1422,0.00!!END!1025!X=1275.842,-412.391,1161,0.00!!END!1026!X=1265.287,-413.11,968,0.00!!END!1027!X=1266.03,-412.994,1198,0.00!!END!1028!X=1266.774,-412.878,1362,0.00!!END!1029!X=1267.518,-412.762,1470,0.00!!END!1030!X=1268.262,-412.645,1248,0.00!!END!1031!X=1269.006,-412.529,1058,0.00!!END!1032!X=1269.749,-412.413,1170,0.00!!END!1033!X=1270.493,-412.296,1415,0.00!!END!1034!X=1271.237,-412.18,1689,0.00!!END!60INVCAM02.inp10/23/20061035!X=1271.98,-412.063,1547,0.00!!END!1036!X=1272.724,-411.946,1550,0.00!!END!1037!X=1273.468,-411.83,1437,0.00!!END!1038!X=1274.212,-411.713,1508,0.00!!END!1039!X=1274.955,-411.596,1300,0.00!!END!1040!X=1275.699,-411.479,1176,0.00!!END!1041!X=1268.863,-411.617,1012,0.00!!END!1042!X=1269.606,-411.501,1285,0.00!!END!1043!X=1270.35,-411.384,1366,0.00!!END!1044!X=1271.094,-411.268,1566,0.00!!END!1045!X=1271.837,-411.151,1451,0.00!!END!1046!X=1272.581,-411.034,1359,0.00!!END!1047!X=1273.325,-410.918,1273,0.00!!END!1048!X=1274.068,-410.801,1274,0.00!!END!1049!X=1274.812,-410.684,1280,0.00!!END!1050!X=1275.555,-410.567,1155,0.00!!END!1051!X=1270.207,-410.472,1179,0.00!!END!1052!X=1270.951,-410.355,1348,0.00!!END!1053!X=1271.694,-410.239,1488,0.00!!END!1054!X=1270.808,-409.443,1442,0.00!!END!1055!X=1271.551,-409.327,1565,0.00!!END!1056!X=1272.295,-409.21,1505,0.00!!END!1057!X=1273.038,-409.093,1409,0.00!!END!1058!X=1273.782,-408.977,1380,0.00!!END!1059!X=1274.525,-408.86,1303,0.00!!END!1060!X=1275.268,-408.743,1104,0.00!!END!1061!X=1269.921,-408.648,1500,0.00!!END!1062!X=1271.408,-408.415,1678,0.00!!END!1063!X=1272.152,-408.298,1707,0.00!!END!1064!X=1272.895,-408.181,1515,0.00!!END!1065!X=1273.638,-408.065,1321,0.00!!END!1066!X=1274.382,-407.948,1219,0.00!!END!1067!X=1271.265,-407.502,1394,0.00!!END!1068!X=1272.008,-407.386,1522,0.00!!END!1069!X=1272.752,-407.269,1411,0.00!!END!1070!X=1273.495,-407.152,1234,0.00!!END!1071!X=1271.122,-406.59,1189,0.00!!END!1072!X=1271.865,-406.474,1343,0.00!!END!1073!X=1272.609,-406.357,1265,0.00!!END!1074!X=1270.979,-405.678,1045,0.00!!END!1075!X=1271.722,-405.562,1235,0.00!!END!1076!X=1272.465,-405.445,1066,0.00!!END!-------------aDataforeachreceptoraretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.61INVCAM02.inp10/23/2006bReceptorheightabovegroundisoptional.Ifnovalueisentered,thereceptorisplacedontheground.62

# INVISTA Camden Plant B - 4 Trinity Consultants

BART Applicability Modeling Analysis 

# SAMPLE POSTUTIL INPUT FILE

UTINVCAM02.INP

12-KM SCREENING A NALYSIS YEAR 2002UTINVCAM02.inp5/31/2006INVISTACAMDEN-CombinePMSpeciesBARTANALYSIS12KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006UPDATED05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------POSTUTILMODELCONTROLFILE----------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames---------------------------Subgroup(0a)-------------OutputFiles------------FileDefaultFileName---------------------ListFilePOSTUTIL.LST!UTLLST=UTINVCAM02.lst!DataFileMODEL.DAT!UTLDAT=UTINVCAM02.con!InputFiles-----------MeteorologicaldatafilesareneededfortheHNO3/NO3partitionoption.Themetdatafileisthe'CALMET.DAT'formatfileusedintheCALPUFFsimulation.IfmultipleCALMETfileshadbeenusedinsequence,youmaylistallofthesefilesinsubgroup0b.SpecifythetotalnumberofCALMETfilesrunsyouneedtouse,andprovidethefilenameforeachinsubgroup0b.NumberofCALMETdatafiles(NFILES)Default:0!NMET=0!AnumberofCALPUFFdatafilesmaybeprocessedinthisapplication.ThefilesmayrepresentindividualCALPUFFsimulationsthatweremadeforaspecificsetofspeciesand/orsources.SpecifythetotalnumberofCALPUFFrunsyouwishtocombine,andprovidethefilenameforeachinsubgroup0b.NumberofCALPUFFdatafiles(NFILES)Default:1!NFILES=1!1UTINVCAM02.inp5/31/2006AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASEConvertfilenamestolowercase?Default:T!LCFILES=T!T=lowercaseF=UPPERCASE!END!-----------------------------------------------------------NOTE:file/pathnamescanbeupto70charactersinlength------------------------------------------------------------------------Subgroup(0b)-------------NMETCALMETDataFiles:InputFileDefaultFileName---------------------------1MET.DAT*UTLMET=CALMET.DAT*InputFileDefaultFileName---------------------------1CALPUFF.DAT!MODDAT=INVCAM02.con!!END!-------------Note:provideNMETlinesoftheform*UTLMET=name**END*andNFILESlinesoftheform*MODDAT=name**END*wherethe*shouldbereplacedwithanexclamationpoint,thespecialdelimitercharacter.--------------------------------------------------------------------------------INPUTGROUP:1--Generalruncontrolparameters--------------Startingdate:Year(ISYR)--Nodefault!ISYR=2002!Month(ISMO)--Nodefault!ISMO=1!Day(ISDY)--Nodefault!ISDY=1!Hour(ISHR)--Nodefault!ISHR=1!Numberofperiodstoprocess(NPER)--Nodefault!NPER=8760!2UTINVCAM02.inp5/31/2006NumberofspeciestoprocessfromCALPUFFruns(NSPECINP)--Nodefault!NSPECINP=19!Numberofspeciestowritetooutputfile(NSPECOUT)--Nodefault!NSPECOUT=9!Numberofspeciestocomputefromthosemodeled(mustbenogreaterthanNSPECOUT)(NSPECCMP)--Nodefault!NSPECCMP=4!Whenmultiplefilesareused,aspeciesnamemayappearinmorethanonefile.Dataforthisspecieswillbesummed(appropriateiftheCALPUFFrunsusedifferentsourcegroups).Ifthissummingisnotappropriate,removeduplicatespeciesfromthefile(s).Stoprunifduplicatespeciesnamesarefound?(MDUPLCT)Default:0!MDUPLCT=0!0=no(i.e.,duplicatespeciesaresummed)1=yes(i.e.,runishalted)DataforeachspeciesinaCALPUFFdatafilemayalsobescaledastheyareread.ThiscanbedonetoaltertheemissionrateofallsourcesthatweremodeledinaparticularCALPUFFapplication.ThescalingfactorforeachspeciesisenteredinSubgroup(2d),foreachfileforwhichscalingisrequested.NumberofCALPUFFdatafilesthatwillbescaled(mustbenogreaterthanNFILES)(NSCALED)Default:0!NSCALED=0!OptiontorecomputetheHNO3/NO3concentrationpartitionpriortoperformingotheractions.ThisoptionwillNOTalteranydepositionfluxescontainedintheCALPUFFfile(s).Twopartitionselectionsareprovided.Thefirst(MNITRATE=1)computesthepartitionfortheTOTAL(allsources)concentrationfields(SO4,NO3,HNO3;NH3),andthesecond(MNITRATE=2)usesthispartition(fromapreviousapplicationofPOSTUTIL)tocomputethepartitionforindividualsourcegroups.RequiredinformationforMNITRATE=1includes:speciesNO3,HNO3,andSO4NH3concentration(s)met.datafileforRHandTRequiredinformationforMNITRATE=2includes:speciesNO3andHNO3forasourcegroupspeciesNO3ALLandHNO3ALLforallsourcegroups,properly3UTINVCAM02.inp5/31/2006partitionedRecomputetheHNO3/NO3partitionforconcentrations?(MNITRATE)Default:0!MNITRATE=0!0=no1=yes,forallsourcescombined2=yes,forasourcegroupAmmoniaconcentrationsmaybeavailableasamodeledspeciesintheCALPUFFfiles.WhenNH3islistedasaprocessedspeciesinSubgroup(2a)(asoneoftheNSPECINPASPECIentries),themodeledvalueswillbeusedinthechemicalequilibriumcalculation.IfNH3isnotonthislist,thedefaultmonthlybackgroundvalueslistedbelowwillbeused.Ifasinglevalueisentered,thisisusedforall12months.Month1isJANUARY,Month12isDECEMBER.Defaultammoniaconcentration(ppb)usedforHNO3/NO3partition:(BCKNH3)inppbDefault:12*10.!BCKNH3=12*0.5!!END!-------------------------------------------------------------------------------INPUTGROUP:2--SpeciesProcessingInformation---------------------------Subgroup(2a)-------------!ASPECI=SO2!!END!!ASPECI=SO4!!END!!ASPECI=NOX!!END!!ASPECI=HNO3!!END!!ASPECI=NO3!!END!!ASPECI=POC081!!END!!ASPECI=POC056!!END!!ASPECI=PIC081!!END!!ASPECI=PIC056!!END!!ASPECI=PMC800!!END!!ASPECI=PMC425!!END!!ASPECI=PMF187!!END!!ASPECI=PMF112!!END!!ASPECI=PMF081!!END!!ASPECI=PMF056!!END!!ASPECI=EC187!!END!!ASPECI=EC112!!END!!ASPECI=EC081!!END!!ASPECI=EC056!!END!4UTINVCAM02.inp5/31/2006-------------Subgroup(2b)-------------ThefollowingNSPECOUTspecieswillbewritten:!ASPECO=SO2!!END!!ASPECO=SO4!!END!!ASPECO=NOX!!END!!ASPECO=HNO3!!END!!ASPECO=NO3!!END!!ASPECO=EC!!END!!ASPECO=SOIL!!END!!ASPECO=SOA!!END!!ASPECO=PMC!!END!-------------Subgroup(2c)-------------ThefollowingNSPECCMPspecieswillbecomputedbyscalingandsummingoneormoreoftheprocessedinputspecies.Identifythename(s)ofthecomputedspeciesandprovidethescalingfactorsforeachoftheNSPECINPinputspecies(NSPECCMPgroupsofNSPECINP+1lineseach):!CSPECCMP=EC!!EC187=1.0000!!EC112=1.0000!!EC081=1.0000!!EC056=1.0000!!END!!CSPECCMP=SOIL!!PMF187=1.0000!!PMF112=1.0000!!PMF081=1.0000!!PMF056=1.0000!!PIC081=1.0000!!PIC056=1.0000!!END!!CSPECCMP=SOA!!POC081=1.0000!!POC056=1.0000!!END!!CSPECCMP=PMC!!PMC800=1.0000!!PMC425=1.0000!5UTINVCAM02.inp5/31/2006!END!-------------Subgroup(2d)-------------EachspeciesinNSCALEDCALPUFFdatafilesmaybescaledbeforebeingprocessed(e.g.,tochangetheemissionrateforallsourcesmodeledintherunthatproducedadatafile).Foreachfile,identifythefilenameandthenprovidethename(s)ofthescaledspeciesandthecorrespondingscalingfactors(A,Bwherex'=Ax+B).A(Default=1.0)B(Default=0.0)----------------------------6

# INVISTA Camden Plant B - 5 Trinity Consultants

BART Applicability Modeling Analysis 

# SAMPLE CALPOST INPUT FILE

VANINVCAM02CR.INP

12-KM SCREENING A NALYSIS YEAR 2002

CAPE ROMAIN ANNUAL AVE RAGE NATURAL BACKGROUNDVANINVCAM02CR.inp5/31/2006INVISTACAMDEN-VisibilitywithAnnualBackgroundCAPEROMAINBARTSCREENINGANALYSIS12KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006UPDATED05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------CALPOSTMODELCONTROLFILE---------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames--------------InputFiles-----------FileDefaultFileName---------------------Conc/DepFluxFileMODEL.DAT!MODDAT=UTINVCAM02.con!RelativeHumidityFileVISB.DAT*VISDAT=*BackgroundDataFileBACK.DAT*BACKDAT=*TransmissometerorVSRN.DAT*VSRDAT=*NephelometerDataFileorDATSAVWeatherDataFileorPrognosticWeatherFileOutputFiles------------FileDefaultFileName---------------------ListFileCALPOST.LST!PSTLST=VANINVCAM02CR.lst!PathnameforTimeseriesFiles(blank)*TSPATH=*(activatewithexclamationpointsonlyifprovidingNON-BLANKcharacterstring)PathnameforPlotFiles(blank)*PLPATH=*(activatewithexclamationpointsonlyifprovidingNON-BLANKcharacterstring)UserCharacterString(U)toaugmentdefaultfilenames(activatewithexclamationpointsonlyifprovidingNON-BLANKcharacterstring)TimeseriesTSERIES_ASPEC_ttHR_CONC_TSUNAM.DATPeakValuePEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DAT*TSUNAM=*1VANINVCAM02CR.inp5/31/2006TopNthRankPlotRANK(ALL)_ASPEC_ttHR_CONC_TUNAM.DATorRANK(ii)_ASPEC_ttHR_CONC_TUNAM.GRD*TUNAM=*ExceedancePlotEXCEED_ASPEC_ttHR_CONC_XUNAM.DATorEXCEED_ASPEC_ttHR_CONC_XUNAM.GRD*XUNAM=*EchoPlot(SpecificDays)yyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.DAToryyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.GRDVisibilityPlotDAILY_VISIB_VUNAM.DAT*VUNAM=*(DailyPeakSummary)AuxiliaryOutputFiles----------------------FileDefaultFileName---------------------VisibilityChangeDELVIS.DAT*DVISDAT=*--------------------------------------------------------------------------------AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASET=lowercase!LCFILES=T!F=UPPERCASENOTE:(1)file/pathnamescanbeupto132charactersinlengthNOTE:(2)FilenamesforALLPLOTandTIMESERIESFILESareconstructedusingatemplatethatincludesapathname,user-suppliedcharacter(s),andcontext-specificstrings,whereASPEC=SpeciesNameCONC=CONCOrWFLXOrDFLXOrTFLXtt=AveragingPeriod(e.g.03)ii=Rank(e.g.02)hh=Hour(ending)inLSTszzzz=BasetimezoneshiftfromUTC(ESTis-0500)yyyy=Year(LST)mm=Month(LST)dd=dayofmonth(LST)aredeterminedinternallybasedonselectionsmadebelow.Ifapathoruser-suppliedcharacter(s)aresupplied,each2VANINVCAM02CR.inp5/31/2006mustcontainatleast1non-blankcharacter.!END!--------------------------------------------------------------------------------INPUTGROUP:1--Generalruncontrolparameters--------------Optiontorunallperiodsfoundinthemet.file(s)(METRUN)Default:0!METRUN=0!METRUN=0-RunperiodexplicitlydefinedbelowMETRUN=1-RunallperiodsinCALPUFFdatafile(s)Startingdate:Year(ISYR)--Nodefault!ISYR=2002!(usedonlyifMonth(ISMO)--Nodefault!ISMO=1!METRUN=0)Day(ISDY)--Nodefault!ISDY=1!Hour(ISHR)--Nodefault!ISHR=1!Numberofhourstoprocess(NHRS)--Nodefault!NHRS=8760!Processeveryhourofdata?(NREP)--Default:1!NREP=1!(1=everyhourprocessed,2=every2ndhourprocessed,5=every5thhourprocessed,etc.)Species&Concentration/DepositionInformation----------------------------------------------Speciestoprocess(ASPEC)--Nodefault!ASPEC=VISIB!(ASPEC=VISIBforvisibilityprocessing)Layer/depositioncode(ILAYER)--Default:1!ILAYER=1!'1'forCALPUFFconcentrations,'-1'fordrydepositionfluxes,'-2'forwetdepositionfluxes,'-3'forwet+drydepositionfluxes.Scalingfactorsoftheform:--Defaults:!A=0.0!X(new)=X(old)*A+BA=0.0!B=0.0!(NOTappliedifA=B=0.0)B=0.0AddHourlyBackgroundConcentrations/Fluxes?(LBACK)--Default:F!LBACK=F!Sourceinformation------------------Optiontoprocesssourcecontributions:3VANINVCAM02CR.inp5/31/20060=Processonlytotalreportedcontributions1=Sumallindividualsourcecontributionsandprocess2=RuninTRACEBACKmodetoidentifysourcecontributionsataSINGLEreceptor(MSOURCE)--Default:0!MSOURCE=0!Receptorinformation--------------------Griddedreceptorsprocessed?(LG)--Default:F!LG=F!Discretereceptorsprocessed?(LD)--Default:F!LD=T!CTSGComplexterrainreceptorsprocessed?(LCT)--Default:F!LCT=F!--ReportresultsbyDISCRETEreceptorRING?(onlyusedwhenLD=T)(LDRING)--Default:F!LDRING=F!--SelectrangeofDISCRETEreceptors(onlyusedwhenLD=T):SelectALLDISCRETEreceptorsbysettingNDRECPflagto-1;ORSelectSPECIFICDISCRETEreceptorsbyenteringaflag(0,1)foreach0=discretereceptornotprocessed1=discretereceptorprocessedusingrepeatedvaluenotationtoselectblocksofreceptors:Flagforallreceptorsafterthelastoneassignedissetto0(NDRECP)--Default:-1!NDRECP=164*1,736*0,66*0,110*0!--SelectrangeofGRIDDEDreceptors(onlyusedwhenLG=T):XindexofLLcorner(IBGRID)--Default:-1!IBGRID=-1!(-1OR1<=IBGRID<=NX)YindexofLLcorner(JBGRID)--Default:-1!JBGRID=-1!(-1OR1<=JBGRID<=NY)XindexofURcorner(IEGRID)--Default:-1!IEGRID=-1!(-1OR1<=IEGRID<=NX)YindexofURcorner(JEGRID)--Default:-1!JEGRID=-1!(-1OR1<=JEGRID<=NY)Note:EntiregridisprocessedifIBGRID=JBGRID=IEGRID=JEGRID=-1--SpecificgriddedreceptorscanalsobeexcludedfromCALPOST4VANINVCAM02CR.inp5/31/2006processingbyfillingaprocessinggridarraywith0sand1s.Iftheprocessingflagforreceptorindex(i,j)is1(ON),thatreceptorwillbeprocessedifitlieswithintherangedelineatedbyIBGRID,JBGRID,IEGRID,JEGRIDandifLG=T.Ifitis0(OFF),itwillnotbeprocessedintherun.Bydefault,allarrayvaluesaresetto1(ON).NumberofgriddedreceptorrowsprovidedinSubgroup(1a)toidentifyspecificgriddedreceptorstoprocess(NGONOFF)--Default:0!NGONOFF=0!!END!--------------Subgroup(1a)--Specificgriddedreceptorsincluded/excluded--------------SpecificgriddedreceptorsareexcludedfromCALPOSTprocessingbyfillingaprocessinggridarraywith0sand1s.AtotalofNGONOFFlinesarereadhere.Eachlinecorrespondstoone'row'inthesamplinggrid,startingwiththeNORTHERNMOSTrowthatcontainsreceptorsthatyouwishtoexclude,andfinishingwithrow1totheSOUTH(nointerveningrowsmaybeskipped).Withinarow,eachreceptorpositionisassignedeithera0or1,startingwiththewesternmostreceptor.0=griddedreceptornotprocessed1=griddedreceptorprocessedRepeatedvaluenotationmaybeusedtoselectblocksofreceptors:23*1,15*0,12*1Becauseallvaluesareinitiallysetto1,anyreceptorsnorthofthefirstrowentered,oreastofthelastvalueprovidedinarow,remainON.(NGXRECP)--Default:1-------------------------------------------------------------------------------INPUTGROUP:2--VisibilityParameters(ASPEC=VISIB)--------------IdentifytheBaseTimeZonefortheCALPUFFsimulation(BTZONE)--Nodefault!BTZONE=5.0!Particlegrowthcurvef(RH)forhygroscopicspecies(MFRH)--Default:2!MFRH=2!5VANINVCAM02CR.inp5/31/20061=IWAQM(1998)f(RH)curve(originallyusedwithMVISBK=1)2=FLAG(2000)f(RH)tabulation3=EPA(2003)f(RH)tabulationMaximumrelativehumidity(%)usedinparticlegrowthcurve(RHMAX)--Default:98!RHMAX=95.0!ModeledspeciestobeincludedincomputingthelightextinctionIncludeSULFATE?(LVSO4)--Default:T!LVSO4=T!IncludeNITRATE?(LVNO3)--Default:T!LVNO3=T!IncludeORGANICCARBON?(LVOC)--Default:T!LVOC=T!IncludeCOARSEPARTICLES?(LVPMC)--Default:T!LVPMC=T!IncludeFINEPARTICLES?(LVPMF)--Default:T!LVPMF=T!IncludeELEMENTALCARBON?(LVEC)--Default:T!LVEC=T!And,whenrankingforTOP-N,TOP-50,andExceedancetables,IncludeBACKGROUND?(LVBK)--Default:T!LVBK=T!SpeciesnameusedforparticulatesinMODEL.DATfileCOARSE(SPECPMC)--Default:PMC!SPECPMC=PMC!FINE(SPECPMF)--Default:PMF!SPECPMF=SOIL!ExtinctionEfficiency(1/Mmperug/m**3)----------------------------------------MODELEDparticulatespecies:PMCOARSE(EEPMC)--Default:0.6!EEPMC=0.6!PMFINE(EEPMF)--Default:1.0!EEPMF=1.0!BACKGROUNDparticulatespecies:PMCOARSE(EEPMCBK)--Default:0.6!EEPMCBK=0.6!Otherspecies:AMMONIUMSULFATE(EESO4)--Default:3.0!EESO4=3.0!AMMONIUMNITRATE(EENO3)--Default:3.0!EENO3=3.0!ORGANICCARBON(EEOC)--Default:4.0!EEOC=4.0!SOIL(EESOIL)--Default:1.0!EESOIL=1.0!ELEMENTALCARBON(EEEC)--Default:10.!EEEC=10.0!BackgroundExtinctionComputation---------------------------------Methodusedforthe24h-averageofpercentchangeoflightextinction:Hourlyratioofsourcelightextinction/backgroundlightextinctionisaveraged?(LAVER)--Default:F!LAVER=F!Methodusedforbackgroundlightextinction(MVISBK)--Default:2!MVISBK=6!1=Supplysinglelightextinctionandhygroscopicfraction-HourlyF(RH)adjustmentappliedtohygroscopicbackground6VANINVCAM02CR.inp5/31/2006andmodeledsulfateandnitrate2=ComputeextinctionfromspeciatedPMmeasurements(A)-HourlyF(RH)adjustmentappliedtoobservedandmodeledsulfateandnitrate-F(RH)factoriscappedatF(RHMAX)3=ComputeextinctionfromspeciatedPMmeasurements(B)-HourlyF(RH)adjustmentappliedtoobservedandmodeledsulfateandnitrate-Receptor-hourexcludedifRH>RHMAX-Receptor-dayexcludediffewerthan6validreceptor-hours4=Readhourlytransmissometerbackgroundextinctionmeasurements-HourlyF(RH)adjustmentappliedtomodeledsulfateandnitrate-Hourexcludedifmeasurementinvalid(missing,interference,orlargeRH)-Receptor-hourexcludedifRH>RHMAX-Receptor-dayexcludediffewerthan6validreceptor-hours5=Readhourlynephelometerbackgroundextinctionmeasurements-Rayleighextinctionvalue(BEXTRAY)addedtomeasurement-HourlyF(RH)adjustmentappliedtomodeledsulfateandnitrate-Hourexcludedifmeasurementinvalid(missing,interference,orlargeRH)-Receptor-hourexcludedifRH>RHMAX-Receptor-dayexcludediffewerthan6validreceptor-hours6=ComputeextinctionfromspeciatedPMmeasurements-FLAGmonthlyRHadjustmentfactorappliedtoobservedandmodeledsulfateandnitrate7=Useobservedweatherorprognosticweatherinformationforbackgroundextinctionduringweatherevents;otherwise,useMethod2-HourlyF(RH)adjustmentappliedtomodeledsulfateandnitrate-F(RH)factoriscappedatF(RHMAX)-Duringobservedweatherevents,computeBextfromvisualrangeifusinganobservedweatherdatafile,or-Duringprognosticweatherevents,useBextfromtheprognosticweatherfile-UseMethod2forhourswithoutaweathereventAdditionalinputsusedforMVISBK=1:--------------------------------------Backgroundlightextinction(1/Mm)(BEXTBK)--Nodefault!BEXTBK=0.0!Percentageofparticlesaffectedbyrelativehumidity(RHFRAC)--Nodefault!RHFRAC=0.0!AdditionalinputsusedforMVISBK=6:--------------------------------------Extinctioncoefficientsforhygroscopicspecies(modeledandbackground)arecomputedusingamonthlyRHadjustmentfactorinplaceofanhourlyRHfactor(VISB.DATfileisNOTneeded).Enterthe12monthlyfactorshere(RHFAC).Month1isJanuary.7VANINVCAM02CR.inp5/31/2006(RHFAC)--Nodefault!RHFAC=3.3,3.0,2.9,2.8,3.2,3.7,3.6,4.1,4.0,3.7,3.4,3.2!AdditionalinputsusedforMVISBK=7:--------------------------------------Theweatherdatafile(DATSAVabbreviatedspace-delimited)thatisidentifiedasVSRN.DATmaycontaindataformorethanonestation.Identifythestationsthatareneededintheorderinwhichtheywillbeusedtoobtainvalidweatherandvisualrange.Thefirststationthatcontainsvaliddataforanhourwillbeused.EnteruptoMXWSTA(setinPARAMSfile)integerstationIDsofupto6digitseachasvariableIDWSTA,andenterthecorrespondingtimezoneforeach,asvariableTZONE(=UTC-LST).AprognosticweatherdatafilewithBextforweathereventsmaybeusedinplaceoftheobservedweatherfile.IdentifythisastheVSRN.DATfileanduseastationIDofIDWSTA=999999,andTZONE=0.NOTE:TZONEidentifiesthetimezoneusedinthedataset.TheDATSAVabbreviatedspace-delimiteddatausuallyarepreparedwithUTCtimeratherthanlocaltime,soTZONEistypicallysettozero.(IDWSTA)--Nodefault!IDWSTA=999999!(TZONE)--Nodefault!TZONE=0.0!AdditionalinputsusedforMVISBK=2,3,6,7:--------------------------------------------BackgroundextinctioncoefficientsarecomputedfrommonthlyCONCENTRATIONSofammoniumsulfate(BKSO4),ammoniumnitrate(BKNO3),coarseparticulates(BKPMC),organiccarbon(BKOC),soil(BKSOIL),andelementalcarbon(BKEC).Month1isJanuary.(ug/m**3)(BKSO4)--Nodefault!BKSO4=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!(BKNO3)--Nodefault!BKNO3=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!(BKPMC)--Nodefault!BKPMC=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!(BKOC)--Nodefault!BKOC=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,8VANINVCAM02CR.inp5/31/20060.00,0.00,0.00,0.00!(BKSOIL)--Nodefault!BKSOIL=11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21!(BKEC)--Nodefault!BKEC=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!AdditionalinputsusedforMVISBK=2,3,5,6,7:----------------------------------------------ExtinctionduetoRayleighscatteringisadded(1/Mm)(BEXTRAY)--Default:10.0!BEXTRAY=10.0!!END!-------------------------------------------------------------------------------INPUTGROUP:3--Outputoptions--------------Documentation-------------DocumentationrecordscontainedintheheaderoftheCALPUFFoutputfilemaybewrittentothelistfile.Printdocumentationimage?(LDOC)--Default:F!LDOC=F!OutputUnits------------UnitsforAllOutput(IPRTU)--Default:1!IPRTU=3!forforConcentrationDeposition1=g/m**3g/m**2/s2=mg/m**3mg/m**2/s3=ug/m**3ug/m**2/s4=ng/m**3ng/m**2/s5=OdourUnitsVisibility:extinctionexpressedin1/Mega-meters(IPRTUisignored)Averagingtime(s)reported--------------------------1-hraverages(L1HR)--Default:T!L1HR=F!3-hraverages(L3HR)--Default:T!L3HR=F!24-hraverages(L24HR)--Default:T!L24HR=T!9VANINVCAM02CR.inp5/31/2006Run-lengthaverages(LRUNL)--Default:T!LRUNL=F!User-specifiedaveragingtimeinhours-resultsforanaveragingtimeofNAVGhoursarereportedforNAVGgreaterthan0:(NAVG)--Default:0!NAVG=0!Typesoftabulationsreported------------------------------1)Visibility:dailyvisibilitytabulationsarealwaysreportedfortheselectedreceptorswhenASPEC=VISIB.Inaddition,anyoftheothertabulationslistedbelowmaybechosentocharacterizethelightextinctioncoefficients.[ListfileorPlot/AnalysisFile]2)Top50tableforeachaveragingtimeselected[Listfileonly](LT50)--Default:T!LT50=F!3)Top'N'tableforeachaveragingtimeselected[ListfileorPlotfile](LTOPN)--Default:F!LTOPN=T!--Numberof'Top-N'valuesateachreceptorselected(NTOPmustbe<=4)(NTOP)--Default:4!NTOP=1!--Specificranksof'Top-N'valuesreported(NTOPvaluesmustbeentered)(ITOP(4)array)--Default:!ITOP=1!1,2,3,44)Thresholdexceedancecountsforeachreceptorandeachaveragingtimeselected[ListfileorPlotfile](LEXCD)--Default:F!LEXCD=F!--Identifythethresholdforeachaveragingtimebyassigninganon-negativevalue(outputunits).--Default:-1.0Thresholdfor1-hraverages(THRESH1)!THRESH1=-1.0!Thresholdfor3-hraverages(THRESH3)!THRESH3=-1.0!10VANINVCAM02CR.inp5/31/2006Thresholdfor24-hraverages(THRESH24)!THRESH24=-1.0!ThresholdforNAVG-hraverages(THRESHN)!THRESHN=-1.0!--Countsfortheshortestaveragingperiodselectedcanbetallieddaily,andreceptorsthatexperiencemorethanNCOUNTcountsoveranyNDAYperiodwillbereported.ThistypeofexceedanceviolationoutputistriggeredonlyifNDAY>0.Accumulationperiod(Days)(NDAY)--Default:0!NDAY=0!Numberofexceedancesallowed(NCOUNT)--Default:1!NCOUNT=1!5)Selecteddaytable(s)EchoOption--Manyrecordsarewritteneachaveragingperiodselectedandoutputisgroupedbyday[ListfileorPlotfile](LECHO)--Default:F!LECHO=F!TimeseriesOption--Averagesatallselectedreceptorsforeachselectedaveragingperiodarewrittentotimeseriesfiles.Eachfilecontainsoneaveragingperiod,andallreceptorsarewrittentoasinglerecordeachaveragingtime.[TSERIES_ASPEC_ttHR_CONC_TSUNAM.DATfiles](LTIME)--Default:F!LTIME=F!PeakValueOption--Averagesatallselectedreceptorsforeachselectedaveragingperiodarescreenedandthepeakvalueeachperiodiswrittentotimeseriesfiles.Eachfilecontainsoneaveragingperiod.[PEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DATfiles](LPEAK)--Default:F!LPEAK=F!--Daysselectedforoutput(IECHO(366))--Default:366*0!IECHO=366*0!(366valuesmustbeentered)Plotoutputoptions-------------------PlotfilescanbecreatedfortheTop-N,Exceedance,andEchotablesselectedabove.Twoformatsforthesefilesareavailable,DATAandGRID.IntheDATAformat,resultsatallreceptorsarelistedalongwiththereceptorlocation[x,y,val1,val2,...].IntheGRIDformat,resultsatonlygriddedreceptorsarewritten,11VANINVCAM02CR.inp5/31/2006usingacompactrepresentation.Thegriddedvaluesarewritteninrows(xvaries),startingwiththemostsouthernrowofthegrid.TheGRIDformatisgiventhe.GRDextension,andincludesheaderscompatiblewiththeSURFER(R)plottingsoftware.Aplottingandanalysisfilecanalsobecreatedforthedailypeakvisibilitysummaryoutput,inDATAformatonly.GeneratePlotfileoutputinadditiontowritingtablestoListfile?(LPLT)--Default:F!LPLT=F!UseGRIDformatratherthanDATAformat,whenavailable?(LGRD)--Default:F!LGRD=F!AuxiliaryOutputFiles(forsubsequentanalyses)------------------------------------------------VisibilityAseparateoutputfilemayberequestedthatcontainsthechangeinvisibilityateachselectedreceptorwhenASPEC=VISIB.ThisfilecanbeprocessedtoconstructvisibilitymeasuresthatarenotavailableinCALPOST.Outputfilewiththevisibilitychangeateachreceptor?(MDVIS)--Default:0!MDVIS=1!0=DoNotcreatefile1=CreatefileofDAILY(24hour)Delta-Deciview2=CreatefileofDAILY(24hour)ExtinctionChange(%)3=CreatefileofHOURLYDelta-Deciview4=CreatefileofHOURLYExtinctionChange(%)AdditionalDebugOutput-----------------------OutputselectedinformationtoListfilefordebugging?(LDEBUG)--Default:F!LDEBUG=F!OutputhourlyextinctioninformationtoREPORT.HRV?(VisibilityMethod7)(LVEXTHR)--Default:F!LVEXTHR=F!!END!12VANINVCAM02CR.inp5/31/200613

# INVISTA Camden Plant B - 6 Trinity Consultants

BART Applicability Modeling Analysis 

# CALPUFF BATCH PROCESSING FILE

4-KM REFINED ANALYSES

# runcpuff.bat 10/23/2006

REM INVISTA CAMDEN

REM BART APPLICABILITY REFINED ANALYSIS

REM MZ/AH 10.23.06

REM RUN 2001

CALL CALPUFFL.EXE INVCAM01.INP

CALL POSTUTILL.EXE UTINVCAM01A1.INP

CALL POSTUTILL.EXE UTINVCAM01B1.INP

CALL POSTUTILL.EXE UTINVCAM01C1.INP

COPY APPEND01.INP APPEND.INP

CALL APPEND.EXE APPEND.INP

COPY APPEND.LST APPEND01.LST

DEL APPEND.INP

DEL APPEND.LST

CALL POSTUTILL.EXE UTINVCAM01.INP

CALL CALPOSTL.EXE V20INVCAM01CR.INP

CALL CALPOSTL.EXE V20INVCAM01GS.INP

CALL CALPOSTL.EXE V20INVCAM01LG.INP

CALL CALPOSTL.EXE V20INVCAM01SR.INP

CALL CALPOSTL.EXE VANINVCAM01CR.INP

CALL CALPOSTL.EXE VANINVCAM01GS.INP

CALL CALPOSTL.EXE VANINVCAM01LG.INP

CALL CALPOSTL.EXE VANINVCAM01SR.INP

REM RUN 2002

CALL CALPUFFL.EXE INVCAM02.INP

CALL POSTUTILL.EXE UTINVCAM02A1.INP

CALL POSTUTILL.EXE UTINVCAM02B1.INP

CALL POSTUTILL.EXE UTINVCAM02C1.INP

COPY APPEND02.INP APPEND.INP

CALL APPEND.EXE APPEND.INP

COPY APPEND.LST APPEND02.LST

DEL APPEND.INP

DEL APPEND.LST

CALL POSTUTILL.EXE UTINVCAM02.INP

CALL CALPOSTL.EXE V20INVCAM02CR.INP

CALL CALPOSTL.EXE V20INVCAM02GS.INP

CALL CALPOSTL.EXE V20INVCAM02LG.INP

CALL CALPOSTL.EXE V20INVCAM02SR.INP

CALL CALPOSTL.EXE VANINVCAM02CR.INP

CALL CALPOSTL.EXE VANINVCAM02GS.INP

CALL CALPOSTL.EXE VANINVCAM02LG.INP

CALL CALPOSTL.EXE VANINVCAM02SR.INP

REM RUN 2003

CALL CALPUFFL.EXE INVCAM03.INP

CALL POSTUTILL.EXE UTINVCAM03A1.INP

CALL POSTUTILL.EXE UTINVCAM03B1.INP

CALL POSTUTILL.EXE UTINVCAM03C1.INP

COPY APPEND03.INP APPEND.INP

CALL APPEND.EXE APPEND.INP

COPY APPEND.LST APPEND03.LST

DEL APPEND.INP

DEL APPEND.LST

CALL POSTUTILL.EXE UTINVCAM03.INP

CALL CALPOSTL.EXE V20INVCAM03CR.INP

CALL CALPOSTL.EXE V20INVCAM03GS.INP

CALL CALPOSTL.EXE V20INVCAM03LG.INP

CALL CALPOSTL.EXE V20INVCAM03SR.INP

CALL CALPOSTL.EXE VANINVCAM03CR.INP

CALL CALPOSTL.EXE VANINVCAM03GS.INP

CALL CALPOSTL.EXE VANINVCAM03LG.INP

CALL CALPOSTL.EXE VANINVCAM03SR.INP

PAUSE

1

# INVISTA Camden Plant B - 7 Trinity Consultants

BART Applicability Modeling Analysis 

# SAMPLE CALPUFF INPUT FILE

INVCAM02.INP

4-KM REFINED ANALYSIS YEAR 2002INVCAM02.inp10/23/2006INVISTACAMDENBARTREFINEDANALYSIS4KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006Update05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------CALPUFFMODELCONTROLFILE---------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames--------------DefaultNameTypeFileName-------------------------CALMET.DATinput*METDAT=*orISCMET.DATinput*ISCDAT=*orPLMMET.DATinput*PLMDAT=*orPROFILE.DATinput*PRFDAT=*SURFACE.DATinput*SFCDAT=*RESTARTB.DATinput*RSTARTB=*--------------------------------------------------------------------------------CALPUFF.LSToutput!PUFLST=INVCAM02.lst!CONC.DAToutput!CONDAT=INVCAM02.con!DFLX.DAToutput*DFDAT=puff2002-sm.dry*WFLX.DAToutput*WFDAT=puff2002-sm.wet*VISB.DAToutput*VISDAT=puff2002-sm.vis*RESTARTE.DAToutput*RSTARTE=puff2002-sm.res*--------------------------------------------------------------------------------EmissionFiles--------------PTEMARB.DATinput*PTDAT=*VOLEMARB.DATinput*VOLDAT=*BAEMARB.DATinput*ARDAT=*LNEMARB.DATinput*LNDAT=*--------------------------------------------------------------------------------OtherFiles-----------OZONE.DATinput!OZDAT=OZCAM02.dat!VD.DATinput*VDDAT=*CHEM.DATinput*CHEMDAT=*H2O2.DATinput*H2O2DAT=*HILL.DATinput*HILDAT=*HILLRCT.DATinput*RCTDAT=*COASTLN.DATinput*CSTDAT=*1INVCAM02.inp10/23/2006FLUXBDY.DATinput*BDYDAT=*BCON.DATinput*BCNDAT=*DEBUG.DAToutput*DEBUG=*MASSFLX.DAToutput*FLXDAT=*MASSBAL.DAToutput*BALDAT=*FOG.DAToutput*FOGDAT=*--------------------------------------------------------------------------------AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASET=lowercase!LCFILES=T!F=UPPERCASENOTE:(1)file/pathnamescanbeupto70charactersinlengthProvisionformultipleinputfiles----------------------------------NumberofCALMET.DATfilesforrun(NMETDAT)Default:1!NMETDAT=36!NumberofPTEMARB.DATfilesforrun(NPTDAT)Default:0!NPTDAT=0!NumberofBAEMARB.DATfilesforrun(NARDAT)Default:0!NARDAT=0!NumberofVOLEMARB.DATfilesforrun(NVOLDAT)Default:0!NVOLDAT=0!!END!-------------Subgroup(0a)-------------ThefollowingCALMET.DATfilenamesareprocessedinsequenceifNMETDAT>1DefaultNameTypeFileName-------------------------noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-01a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-01b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-01c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-02a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-02b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-02c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-03a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-03b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-03c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-04a.DAT!!END!2INVCAM02.inp10/23/2006noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-04b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-04c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-05a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-05b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-05c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-06a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-06b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-06c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-07a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-07b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-07c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-08a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-08b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-08c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-09a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-09b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-09c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-10a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-10b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-10c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-11a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-11b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-11c.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-12a.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-12b.DAT!!END!noneinput!METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-12c.DAT!!END!INPUTGROUP:1--Generalruncontrolparameters--------------Optiontorunallperiodsfoundinthemet.file(METRUN)Default:0!METRUN=0!METRUN=0-RunperiodexplicitlydefinedbelowMETRUN=1-Runallperiodsinmet.fileStartingdate:Year(IBYR)--Nodefault!IBYR=2002!(usedonlyifMonth(IBMO)--Nodefault!IBMO=1!METRUN=0)Day(IBDY)--Nodefault!IBDY=1!Hour(IBHR)--Nodefault!IBHR=1!Basetimezone(XBTZ)--Nodefault!XBTZ=5.0!PST=8.,MST=7.CST=6.,EST=5.Lengthofrun(hours)(IRLG)--Nodefault!IRLG=8760!Numberofchemicalspecies(NSPEC)Default:5!NSPEC=19!3INVCAM02.inp10/23/2006Numberofchemicalspeciestobeemitted(NSE)Default:3!NSE=17!FlagtostoprunafterSETUPphase(ITEST)Default:2!ITEST=2!(Usedtoallowcheckingofthemodelinputs,files,etc.)ITEST=1-STOPSprogramafterSETUPphaseITEST=2-ContinueswithexecutionofprogramafterSETUPRestartConfiguration:Controlflag(MRESTART)Default:0!MRESTART=0!0=Donotreadorwritearestartfile1=Readarestartfileatthebeginningoftherun2=Writearestartfileduringrun3=ReadarestartfileatbeginningofrunandwritearestartfileduringrunNumberofperiodsinRestartoutputcycle(NRESPD)Default:0!NRESPD=0!0=Filewrittenonlyatlastperiod>0=FileupdatedeveryNRESPDperiodsMeteorologicalDataFormat(METFM)Default:1!METFM=1!METFM=1-CALMETbinaryfile(CALMET.MET)METFM=2-ISCASCIIfile(ISCMET.MET)METFM=3-AUSPLUMEASCIIfile(PLMMET.MET)METFM=4-CTDMplustowerfile(PROFILE.DAT)andsurfaceparametersfile(SURFACE.DAT)METFM=5-AERMETtowerfile(PROFILE.DAT)andsurfaceparametersfile(SURFACE.DAT)MeteorologicalProfileDataFormat(MPRFFM)(usedonlyforMETFM=1,2,3)Default:1!MPRFFM=1!MPRFFM=1-CTDMplustowerfile(PROFILE.DAT)MPRFFM=2-AERMETtowerfile(PROFILE.DAT)PGsigma-yisadjustedbythefactor(AVET/PGTIME)**0.2AveragingTime(minutes)(AVET)4INVCAM02.inp10/23/2006Default:60.0!AVET=60.!PGAveragingTime(minutes)(PGTIME)Default:60.0!PGTIME=60.!!END!-------------------------------------------------------------------------------INPUTGROUP:2--Technicaloptions--------------Verticaldistributionusedinthenearfield(MGAUSS)Default:1!MGAUSS=1!0=uniform1=GaussianTerrainadjustmentmethod(MCTADJ)Default:3!MCTADJ=3!0=noadjustment1=ISC-typeofterrainadjustment2=simple,CALPUFF-typeofterrainadjustment3=partialplumepathadjustmentSubgrid-scalecomplexterrainflag(MCTSG)Default:0!MCTSG=0!0=notmodeled1=modeledNear-fieldpuffsmodeledaselongatedslugs?(MSLUG)Default:0!MSLUG=0!0=no1=yes(slugmodelused)Transitionalplumerisemodeled?(MTRANS)Default:1!MTRANS=1!0=no(i.e.,finalriseonly)1=yes(i.e.,transitionalrisecomputed)Stacktipdownwash?(MTIP)Default:1!MTIP=1!0=no(i.e.,nostacktipdownwash)1=yes(i.e.,usestacktipdownwash)Methodusedtosimulatebuildingdownwash?(MBDW)Default:1!MBDW=1!1=ISCmethod5INVCAM02.inp10/23/20062=PRIMEmethodVerticalwindshearmodeledabovestacktop?(MSHEAR)Default:0!MSHEAR=0!0=no(i.e.,verticalwindshearnotmodeled)1=yes(i.e.,verticalwindshearmodeled)Puffsplittingallowed?(MSPLIT)Default:0!MSPLIT=0!0=no(i.e.,puffsnotsplit)1=yes(i.e.,puffsaresplit)Chemicalmechanismflag(MCHEM)Default:1!MCHEM=1!0=chemicaltransformationnotmodeled1=transformationratescomputedinternally(MESOPUFFIIscheme)2=user-specifiedtransformationratesused3=transformationratescomputedinternally(RIVAD/ARM3scheme)4=secondaryorganicaerosolformationcomputed(MESOPUFFIIschemeforOH)Aqueousphasetransformationflag(MAQCHEM)(UsedonlyifMCHEM=1,or3)Default:0!MAQCHEM=0!0=aqueousphasetransformationnotmodeled1=transformationratesadjustedforaqueousphasereactionsWetremovalmodeled?(MWET)Default:1!MWET=1!0=no1=yesDrydepositionmodeled?(MDRY)Default:1!MDRY=1!0=no1=yes(drydepositionmethodspecifiedforeachspeciesinInputGroup3)Gravitationalsettling(plumetilt)modeled?(MTILT)Default:0!MTILT=0!0=no1=yes(puffcenterfallsatthegravitationalsettlingvelocityfor1particlespecies)Restrictions:6INVCAM02.inp10/23/2006-MDRY=1-NSPEC=1(mustbeparticlespeciesaswell)-sg=0GEOMETRICSTANDARDDEVIATIONinGroup8issettozeroforasingleparticlediameterMethodusedtocomputedispersioncoefficients(MDISP)Default:3!MDISP=3!1=dispersioncoefficientscomputedfrommeasuredvaluesofturbulence,sigmav,sigmaw2=dispersioncoefficientsfrominternallycalculatedsigmav,sigmawusingmicrometeorologicalvariables(u*,w*,L,etc.)3=PGdispersioncoefficientsforRURALareas(computedusingtheISCSTmulti-segmentapproximation)andMPcoefficientsinurbanareas4=sameas3exceptPGcoefficientscomputedusingtheMESOPUFFIIeqns.5=CTDMsigmasusedforstableandneutralconditions.Forunstableconditions,sigmasarecomputedasinMDISP=3,describedabove.MDISP=5assumesthatmeasuredvaluesarereadSigma-v/sigma-theta,sigma-wmeasurementsused?(MTURBVW)(UsedonlyifMDISP=1or5)Default:3!MTURBVW=0!1=usesigma-vorsigma-thetameasurementsfromPROFILE.DATtocomputesigma-y(validforMETFM=1,2,3,4,5)2=usesigma-wmeasurementsfromPROFILE.DATtocomputesigma-z(validforMETFM=1,2,3,4,5)3=usebothsigma-(v/theta)andsigma-wfromPROFILE.DATtocomputesigma-yandsigma-z(validforMETFM=1,2,3,4,5)4=usesigma-thetameasurementsfromPLMMET.DATtocomputesigma-y(validonlyifMETFM=3)Back-upmethodusedtocomputedispersionwhenmeasuredturbulencedataaremissing(MDISP2)Default:3!MDISP2=3!(usedonlyifMDISP=1or5)2=dispersioncoefficientsfrominternallycalculatedsigmav,sigmawusingmicrometeorologicalvariables(u*,w*,L,etc.)3=PGdispersioncoefficientsforRURALareas(computedusingtheISCSTmulti-segmentapproximation)andMPcoefficientsinurbanareas4=sameas3exceptPGcoefficientscomputedusing7INVCAM02.inp10/23/2006theMESOPUFFIIeqns.[DIAGNOSTICFEATURE]MethodusedforLagrangiantimescaleforSigma-y(usedonlyifMDISP=1,2orMDISP2=1,2)(MTAULY)Default:0!MTAULY=0!0=Draxlerdefault617.284(s)1=ComputedasLag.Length/(.75q)--afterSCIPUFF10<Directuserinput(s)--e.g.,306.9[DIAGNOSTICFEATURE]MethodusedforAdvective-DecaytimescaleforTurbulence(usedonlyifMDISP=2orMDISP2=2)(MTAUADV)Default:0!MTAUADV=0!0=Noturbulenceadvection1=Computed(OPTIONNOTIMPLEMENTED)10<Directuserinput(s)--e.g.,300Methodusedtocomputeturbulencesigma-v&sigma-wusingmicrometeorologicalvariables(UsedonlyifMDISP=2orMDISP2=2)(MCTURB)Default:1!MCTURB=1!1=StandardCALPUFFsubroutines2=AERMODsubroutinesPGsigma-y,zadj.forroughness?Default:0!MROUGH=0!(MROUGH)0=no1=yesPartialplumepenetrationofDefault:1!MPARTL=1!elevatedinversion?(MPARTL)0=no1=yesStrengthoftemperatureinversionDefault:0!MTINV=0!providedinPROFILE.DATextendedrecords?(MTINV)0=no(computedfrommeasured/defaultgradients)1=yesPDFusedfordispersionunderconvectiveconditions?Default:0!MPDF=0!(MPDF)0=no1=yes8INVCAM02.inp10/23/2006Sub-GridTIBLmoduleusedforshoreline?Default:0!MSGTIBL=0!(MSGTIBL)0=no1=yesBoundaryconditions(concentration)modeled?Default:0!MBCON=0!(MBCON)0=no1=yes,usingformattedBCON.DATfile2=yes,usingunformattedCONC.DATfileAnalysesoffoggingandicingimpactsduetoemissionsfromarraysofmechanically-forcedcoolingtowerscanbeperformedusingCALPUFFinconjunctionwithacoolingtoweremissionsprocessor(CTEMISS)anditsassociatedpostprocessors.HourlyemissionsofwatervaporandtemperaturefromeachcoolingtowercellarecomputedforthecurrentcellconfigurationandambientconditionsbyCTEMISS.CALPUFFmodelsthedispersionoftheseemissionsandprovidescloudinformationinaspecializedformatforfurtheranalysis.OutputtoFOG.DATisprovidedineither'plumemode'or'receptormode'format.ConfigureforFOGModeloutput?Default:0!MFOG=0!(MFOG)0=no1=yes-reportresultsinPLUMEModeformat2=yes-reportresultsinRECEPTORModeformatTestoptionsspecifiedtoseeiftheyconformtoregulatoryvalues?(MREG)Default:1!MREG=0!0=NOchecksaremade1=TechnicaloptionsmustconformtoUSEPALongRangeTransport(LRT)guidanceMETFM1or2AVET60.(min)PGTIME60.(min)MGAUSS1MCTADJ3MTRANS1MTIP1MCHEM1or3(ifmodelingSOx,NOx)9INVCAM02.inp10/23/2006MWET1MDRY1MDISP2or3MPDF0ifMDISP=31ifMDISP=2MROUGH0MPARTL1SYTDEP550.(m)MHFTSZ0!END!-------------------------------------------------------------------------------INPUTGROUP:3a,3b--Specieslist-------------------------------Subgroup(3a)------------Thefollowingspeciesaremodeled:!CSPEC=SO2!!END!!CSPEC=SO4!!END!!CSPEC=NOX!!END!!CSPEC=HNO3!!END!!CSPEC=NO3!!END!!CSPEC=POC081!!END!!CSPEC=POC056!!END!!CSPEC=PIC081!!END!!CSPEC=PIC056!!END!!CSPEC=PMC800!!END!!CSPEC=PMC425!!END!!CSPEC=PMF187!!END!!CSPEC=PMF112!!END!!CSPEC=PMF081!!END!!CSPEC=PMF056!!END!!CSPEC=EC187!!END!!CSPEC=EC112!!END!!CSPEC=EC081!!END!!CSPEC=EC056!!END!DryOUTPUTGROUPSPECIESMODELEDEMITTEDDEPOSITEDNUMBERNAME(0=NO,1=YES)(0=NO,1=YES)(0=NO,(0=NONE,(Limit:121=COMPUTED-GAS1=1stCGRUP,10INVCAM02.inp10/23/2006Characters2=COMPUTED-PARTICLE2=2ndCGRUP,inlength)3=USER-SPECIFIED)3=etc.)!SO2=1,1,1,0!!SO4=1,1,2,0!!NOX=1,1,1,0!!HNO3=1,0,1,0!!NO3=1,0,2,0!!POC081=1,1,2,0!!POC056=1,1,2,0!!PIC081=1,1,2,0!!PIC056=1,1,2,0!!PMC800=1,1,2,0!!PMC425=1,1,2,0!!PMF187=1,1,2,0!!PMF112=1,1,2,0!!PMF081=1,1,2,0!!PMF056=1,1,2,0!!EC187=1,1,2,0!!EC112=1,1,2,0!!EC081=1,1,2,0!!EC056=1,1,2,0!!END!-------------Subgroup(3b)-------------ThefollowingnamesareusedforSpecies-Groupsinwhichresultsforcertainspeciesarecombined(added)priortooutput.TheCGRUPnamewillbeusedasthespeciesnameinoutputfiles.Usethisfeaturetomodelspecificparticle-sizedistributionsbytreatingeachsize-rangeasaseparatespecies.Ordermustbeconsistentwith3(a)above.-------------------------------------------------------------------------------INPUTGROUP:4--MapProjectionandGridcontrolparameters--------------Projectionforall(X,Y):-------------------------Mapprojection(PMAP)Default:UTM!PMAP=LCC!11INVCAM02.inp10/23/2006UTM:UniversalTransverseMercatorTTM:TangentialTransverseMercatorLCC:LambertConformalConicPS:PolarStereographicEM:EquatorialMercatorLAZA:LambertAzimuthalEqualAreaFalseEastingandNorthing(km)attheprojectionorigin(UsedonlyifPMAP=TTM,LCC,orLAZA)(FEAST)Default=0.0!FEAST=0.000!(FNORTH)Default=0.0!FNORTH=0.000!UTMzone(1to60)(UsedonlyifPMAP=UTM)(IUTMZN)NoDefault!IUTMZN=0!HemisphereforUTMprojection?(UsedonlyifPMAP=UTM)(UTMHEM)Default:N!UTMHEM=N!N:NorthernhemisphereprojectionS:SouthernhemisphereprojectionLatitudeandLongitude(decimaldegrees)ofprojectionorigin(UsedonlyifPMAP=TTM,LCC,PS,EM,orLAZA)(RLAT0)NoDefault!RLAT0=40N!(RLON0)NoDefault!RLON0=97W!TTM:RLON0identifiescentral(trueN/S)meridianofprojectionRLAT0selectedforconvenienceLCC:RLON0identifiescentral(trueN/S)meridianofprojectionRLAT0selectedforconveniencePS:RLON0identifiescentral(gridN/S)meridianofprojectionRLAT0selectedforconvenienceEM:RLON0identifiescentralmeridianofprojectionRLAT0isREPLACEDby0.0N(Equator)LAZA:RLON0identifieslongitudeoftangent-pointofmappingplaneRLAT0identifieslatitudeoftangent-pointofmappingplaneMatchingparallel(s)oflatitude(decimaldegrees)forprojection(UsedonlyifPMAP=LCCorPS)(XLAT1)NoDefault!XLAT1=33N!(XLAT2)NoDefault!XLAT2=45N!LCC:ProjectionconeslicesthroughEarth'ssurfaceatXLAT1andXLAT2PS:ProjectionplaneslicesthroughEarthatXLAT1(XLAT2isnotused)----------Note:Latitudesandlongitudesshouldbepositive,andincludea12INVCAM02.inp10/23/2006letterN,S,E,orWindicatingnorthorsouthlatitude,andeastorwestlongitude.Forexample,35.9NLatitude=35.9N118.7ELongitude=118.7EDatum-region------------TheDatum-Regionforthecoordinatesisidentifiedbyacharacterstring.ManymappingproductscurrentlyavailableusethemodeloftheEarthknownastheWorldGeodeticSystem1984(WGS-84).Otherlocalmodelsmaybeinuse,andtheirselectioninCALMETwillmakeitsoutputconsistentwithlocalmappingproducts.ThelistofDatum-RegionswithofficialtransformationparametersisprovidedbytheNationalImageryandMappingAgency(NIMA).NIMADatum-Regions(Examples)------------------------------------------------------------------------------WGS-84WGS-84ReferenceEllipsoidandGeoid,Globalcoverage(WGS84)NAS-CNORTHAMERICAN1927Clarke1866Spheroid,MEANFORCONUS(NAD27)NAR-CNORTHAMERICAN1983GRS80Spheroid,MEANFORCONUS(NAD83)NWS-84NWS6370KMRadius,SphereESR-SESRIREFERENCE6371KMRadius,SphereDatum-regionforoutputcoordinates(DATUM)Default:WGS-84!DATUM=NWS-84!METEOROLOGICALGrid:RectangulargriddefinedforprojectionPMAP,withXtheEastingandYtheNorthingcoordinateNo.Xgridcells(NX)Nodefault!NX=248!No.Ygridcells(NY)Nodefault!NY=257!No.verticallayers(NZ)Nodefault!NZ=10!Gridspacing(DGRIDKM)Nodefault!DGRIDKM=4.!Units:kmCellfaceheights(ZFACE(nz+1))NodefaultsUnits:m!ZFACE=0.,20.,40.,80.,160.,320.,640.,1200.,2000.,3000.,4000.!ReferenceCoordinatesofSOUTHWESTcornerofgridcell(1,1):13INVCAM02.inp10/23/2006Xcoordinate(XORIGKM)Nodefault!XORIGKM=718.005!Ycoordinate(YORIGKM)Nodefault!YORIGKM=-1214.003!Units:kmCOMPUTATIONALGrid:ThecomputationalgridisidenticaltoorasubsetoftheMET.grid.Thelowerleft(LL)cornerofthecomputationalgridisatgridpoint(IBCOMP,JBCOMP)oftheMET.grid.Theupperright(UR)cornerofthecomputationalgridisatgridpoint(IECOMP,JECOMP)oftheMET.grid.ThegridspacingofthecomputationalgridisthesameastheMET.grid.XindexofLLcorner(IBCOMP)Nodefault!IBCOMP=100!(1<=IBCOMP<=NX)YindexofLLcorner(JBCOMP)Nodefault!JBCOMP=132!(1<=JBCOMP<=NY)XindexofURcorner(IECOMP)Nodefault!IECOMP=242!(1<=IECOMP<=NX)YindexofURcorner(JECOMP)Nodefault!JECOMP=233!(1<=JECOMP<=NY)SAMPLINGGrid(GRIDDEDRECEPTORS):Thelowerleft(LL)cornerofthesamplinggridisatgridpoint(IBSAMP,JBSAMP)oftheMET.grid.Theupperright(UR)cornerofthesamplinggridisatgridpoint(IESAMP,JESAMP)oftheMET.grid.Thesamplinggridmustbeidenticaltoorasubsetofthecomputationalgrid.Itmaybeanestedgridinsidethecomputationalgrid.ThegridspacingofthesamplinggridisDGRIDKM/MESHDN.Logicalflagindicatingifgriddedreceptorsareused(LSAMP)Default:T!LSAMP=F!(T=yes,F=no)XindexofLLcorner(IBSAMP)Nodefault!IBSAMP=1!(IBCOMP<=IBSAMP<=IECOMP)YindexofLLcorner(JBSAMP)Nodefault!JBSAMP=1!(JBCOMP<=JBSAMP<=JECOMP)14INVCAM02.inp10/23/2006XindexofURcorner(IESAMP)Nodefault!IESAMP=1!(IBCOMP<=IESAMP<=IECOMP)YindexofURcorner(JESAMP)Nodefault!JESAMP=1!(JBCOMP<=JESAMP<=JECOMP)Nestingfactorofthesamplinggrid(MESHDN)Default:1!MESHDN=1!(MESHDNisaninteger>=1)!END!-------------------------------------------------------------------------------INPUTGROUP:5--OutputOptions--------------**FILEDEFAULTVALUEVALUETHISRUN-------------------------------Concentrations(ICON)1!ICON=1!DryFluxes(IDRY)1!IDRY=0!WetFluxes(IWET)1!IWET=0!RelativeHumidity(IVIS)1!IVIS=0!(RHfileisrequiredforVISIBILITYanalyses)Usedatacompressionoptioninoutputfile?(LCOMPRS)Default:T!LCOMPRS=T!*0=Donotcreatefile,1=createfileQAPLOTFILEOUTPUTOPTION:Createastandardseriesofoutputfiles(e.g.locationsofsources,receptors,grids...)suitableforplotting?(IQAPLOT)Default:1!IQAPLOT=1!0=no1=yesDIAGNOSTICMASSFLUXOUTPUTOPTIONS:15INVCAM02.inp10/23/2006Massfluxacrossspecifiedboundariesforselectedspeciesreportedhourly?(IMFLX)Default:0!IMFLX=0!0=no1=yes(FLUXBDY.DATandMASSFLX.DATfilenamesarespecifiedinInputGroup0)Massbalanceforeachspeciesreportedhourly?(IMBAL)Default:0!IMBAL=0!0=no1=yes(MASSBAL.DATfilenameisspecifiedinInputGroup0)LINEPRINTEROUTPUTOPTIONS:Printconcentrations(ICPRT)Default:0!ICPRT=0!Printdryfluxes(IDPRT)Default:0!IDPRT=0!Printwetfluxes(IWPRT)Default:0!IWPRT=0!(0=Donotprint,1=Print)Concentrationprintinterval(ICFRQ)inhoursDefault:1!ICFRQ=1!Dryfluxprintinterval(IDFRQ)inhoursDefault:1!IDFRQ=1!Wetfluxprintinterval(IWFRQ)inhoursDefault:1!IWFRQ=1!UnitsforLinePrinterOutput(IPRTU)Default:1!IPRTU=3!forforConcentrationDeposition1=g/m**3g/m**2/s2=mg/m**3mg/m**2/s3=ug/m**3ug/m**2/s4=ng/m**3ng/m**2/s5=OdourUnitsMessagestrackingprogressofrunwrittentothescreen?(IMESG)Default:2!IMESG=2!0=no1=yes(advectionstep,puffID)2=yes(YYYYJJJHH,#oldpuffs,#emittedpuffs)SPECIES(orGROUPforcombinedspecies)LISTFOROUTPUTOPTIONS16INVCAM02.inp10/23/2006----CONCENTRATIONS----------DRYFLUXES------------WETFLUXES--------MASSFLUX--SPECIES/GROUPPRINTED?SAVEDONDISK?PRINTED?SAVEDONDISK?PRINTED?SAVEDONDISK?SAVEDONDISK?----------------------------------------------------------------------------------------------!SO2=0,1,0,0,0,0,0!!SO4=0,1,0,0,0,0,0!!NOX=0,1,0,0,0,0,0!!HNO3=0,1,0,0,0,0,0!!NO3=0,1,0,0,0,0,0!!POC081=0,1,0,0,0,0,0!!POC056=0,1,0,0,0,0,0!!PIC081=0,1,0,0,0,0,0!!PIC056=0,1,0,0,0,0,0!!PMC800=0,1,0,0,0,0,0!!PMC425=0,1,0,0,0,0,0!!PMF187=0,1,0,0,0,0,0!!PMF112=0,1,0,0,0,0,0!!PMF081=0,1,0,0,0,0,0!!PMF056=0,1,0,0,0,0,0!!EC187=0,1,0,0,0,0,0!!EC112=0,1,0,0,0,0,0!!EC081=0,1,0,0,0,0,0!!EC056=0,1,0,0,0,0,0!OPTIONSFORPRINTING"DEBUG"QUANTITIES(muchoutput)Logicalfordebugoutput(LDEBUG)Default:F!LDEBUG=F!Firstpufftotrack(IPFDEB)Default:1!IPFDEB=1!Numberofpuffstotrack(NPFDEB)Default:1!NPFDEB=10!Met.periodtostartoutput(NN1)Default:1!NN1=10!Met.periodtoendoutput(NN2)Default:10!NN2=10!!END!-------------------------------------------------------------------------------17INVCAM02.inp10/23/2006INPUTGROUP:6a,6b,&6c--Subgridscalecomplexterraininputs----------------------------------------Subgroup(6a)---------------Numberofterrainfeatures(NHILL)Default:0!NHILL=0!Numberofspecialcomplexterrainreceptors(NCTREC)Default:0!NCTREC=0!TerrainandCTSGReceptordataforCTSGhillsinputinCTDMformat?(MHILL)NoDefault!MHILL=0!1=HillandReceptordatacreatedbyCTDMprocessors&readfromHILL.DATandHILLRCT.DATfiles2=HilldatacreatedbyOPTHILL&inputbelowinSubgroup(6b);ReceptordatainSubgroup(6c)FactortoconverthorizontaldimensionsDefault:1.0!XHILL2M=0.!tometers(MHILL=1)FactortoconvertverticaldimensionsDefault:1.0!ZHILL2M=0.!tometers(MHILL=1)X-originofCTDMsystemrelativetoNoDefault!XCTDMKM=0.0E00!CALPUFFcoordinatesystem,inKilometers(MHILL=1)Y-originofCTDMsystemrelativetoNoDefault!YCTDMKM=0.0E00!CALPUFFcoordinatesystem,inKilometers(MHILL=1)!END!---------------Subgroup(6b)---------------1**HILLinformationHILLXCYCTHETAHZGRIDRELIEFEXPO1EXPO2SCALE1SCALE2AMAX1AMAX2NO.(km)(km)(deg.)(m)(m)(m)(m)(m)(m)(m)(m)------------------------------------------------------------18INVCAM02.inp10/23/2006--------------------Subgroup(6c)---------------COMPLEXTERRAINRECEPTORINFORMATIONXRCTYRCTZRCTXHH(km)(km)(m)----------------------------------------1DescriptionofComplexTerrainVariables:XC,YC=CoordinatesofcenterofhillTHETAH=Orientationofmajoraxisofhill(clockwisefromNorth)ZGRID=Heightofthe0ofthegridabovemeansealevelRELIEF=HeightofthecrestofthehillabovethegridelevationEXPO1=Hill-shapeexponentforthemajoraxisEXPO2=Hill-shapeexponentforthemajoraxisSCALE1=HorizontallengthscalealongthemajoraxisSCALE2=HorizontallengthscalealongtheminoraxisAMAX=MaximumallowedaxislengthforthemajoraxisBMAX=MaximumallowedaxislengthforthemajoraxisXRCT,YRCT=CoordinatesofthecomplexterrainreceptorsZRCT=Heightoftheground(MSL)atthecomplexterrainReceptorXHH=Hillnumberassociatedwitheachcomplexterrainreceptor(NOTE:MUSTBEENTEREDASAREALNUMBER)**NOTE:DATAforeachhillandCTSGreceptoraretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUP:7--Chemicalparametersfordrydepositionofgases--------------SPECIESDIFFUSIVITYALPHASTARREACTIVITYMESOPHYLLRESISTANCEHENRY'SLAWCOEFFICIENTNAME(cm**2/s)(s/cm)(dimensionless)19INVCAM02.inp10/23/2006---------------------------------------------------------------------------------!SO2=0.1509,1000.,8.,0.,0.04!!NOX=0.1656,1.,8.,5.,3.5!!HNO3=0.1628,1.,18.,0.,0.00000008!!END!-------------------------------------------------------------------------------INPUTGROUP:8--Sizeparametersfordrydepositionofparticles--------------ForSINGLESPECIES,themeanandstandarddeviationareusedtocomputeadepositionvelocityforNINT(seegroup9)size-ranges,andthesearethenaveragedtoobtainameandepositionvelocity.ForGROUPEDSPECIES,thesizedistributionshouldbeexplicitlyspecified(bythe'species'inthegroup),andthestandarddeviationforeachshouldbeenteredas0.Themodelwillthenusethedepositionvelocityforthestatedmeandiameter.SPECIESGEOMETRICMASSMEANGEOMETRICSTANDARDNAMEDIAMETERDEVIATION(microns)(microns)--------------------------------------------!SO4=0.48,2.!!NO3=0.48,2.!!POC081=0.8125,0.!!POC056=0.5625,0.!!PIC081=0.8125,0.!!PIC056=0.5625,0.!!PMC800=8.,0.!!PMC425=4.25,0.!!PMF187=1.875,0.!!PMF112=1.125,0.!!PMF081=0.8125,0.!!PMF056=0.5625,0.!!EC187=1.875,0.!!EC112=1.125,0.!!EC081=0.8125,0.!!EC056=0.5625,0.!!END!-------------------------------------------------------------------------------20INVCAM02.inp10/23/2006INPUTGROUP:9--Miscellaneousdrydepositionparameters--------------Referencecuticleresistance(s/cm)(RCUTR)Default:30!RCUTR=30.0!Referencegroundresistance(s/cm)(RGR)Default:10!RGR=10.0!Referencepollutantreactivity(REACTR)Default:8!REACTR=8.0!Numberofparticle-sizeintervalsusedtoevaluateeffectiveparticledepositionvelocity(NINT)Default:9!NINT=9!Vegetationstateinunirrigatedareas(IVEG)Default:1!IVEG=1!IVEG=1foractiveandunstressedvegetationIVEG=2foractiveandstressedvegetationIVEG=3forinactivevegetation!END!-------------------------------------------------------------------------------INPUTGROUP:10--WetDepositionParameters---------------ScavengingCoefficient--Units:(sec)**(-1)PollutantLiquidPrecip.FrozenPrecip.-------------------------------------!SO2=3.0E-05,0.0E00!!SO4=1.0E-04,3.0E-05!!NOX=0.0E00,0.0E00!!HNO3=6.0E-05,0.0E00!!NO3=1.0E-04,3.0E-05!!POC081=1.0E-04,3.0E-05!!POC056=1.0E-04,3.0E-05!!PIC081=1.0E-04,3.0E-05!!PIC056=1.0E-04,3.0E-05!!PMC800=1.0E-04,3.0E-05!!PMC425=1.0E-04,3.0E-05!!PMF187=1.0E-04,3.0E-05!!PMF112=1.0E-04,3.0E-05!21INVCAM02.inp10/23/2006!PMF081=1.0E-04,3.0E-05!!PMF056=1.0E-04,3.0E-05!!EC187=1.0E-04,3.0E-05!!EC112=1.0E-04,3.0E-05!!EC081=1.0E-04,3.0E-05!!EC056=1.0E-04,3.0E-05!!END!-------------------------------------------------------------------------------INPUTGROUP:11--ChemistryParameters---------------Ozonedatainputoption(MOZ)Default:1!MOZ=1!(UsedonlyifMCHEM=1,3,or4)0=useamonthlybackgroundozonevalue1=readhourlyozoneconcentrationsfromtheOZONE.DATdatafileMonthlyozoneconcentrations(UsedonlyifMCHEM=1,3,or4andMOZ=0orMOZ=1andallhourlyO3datamissing)(BCKO3)inppbDefault:12*80.!BCKO3=29.71,35.12,36.10,43.28,44.47,47.19,47.52,46.81,37.20,27.20,27.66,27.83!Monthlyammoniaconcentrations(UsedonlyifMCHEM=1,or3)(BCKNH3)inppbDefault:12*10.!BCKNH3=0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50,0.50!NighttimeSO2lossrate(RNITE1)inpercent/hourDefault:0.2!RNITE1=.2!NighttimeNOxlossrate(RNITE2)inpercent/hourDefault:2.0!RNITE2=2.0!NighttimeHNO3formationrate(RNITE3)inpercent/hourDefault:2.0!RNITE3=2.0!H2O2datainputoption(MH2O2)Default:1!MH2O2=1!(UsedonlyifMAQCHEM=1)0=useamonthlybackgroundH2O2value1=readhourlyH2O2concentrationsfromtheH2O2.DATdatafileMonthlyH2O2concentrations22INVCAM02.inp10/23/2006(UsedonlyifMQACHEM=1andMH2O2=0orMH2O2=1andallhourlyH2O2datamissing)(BCKH2O2)inppbDefault:12*1.!BCKH2O2=1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00!---DataforSECONDARYORGANICAEROSOL(SOA)Option(usedonlyifMCHEM=4)TheSOAmoduleusesmonthlyvaluesof:Fineparticulateconcentrationinug/m^3(BCKPMF)Organicfractionoffineparticulate(OFRAC)VOC/NOXratio(afterreaction)(VCNX)tocharacterizetheairmasswhencomputingtheformationofSOAfromVOCemissions.Typicalvaluesforseveraldistinctairmasstypesare:Month123456789101112JanFebMarAprMayJunJulAugSepOctNovDecCleanContinentalBCKPMF1.1.1.1.1.1.1.1.1.1.1.1.OFRAC.15.15.20.20.20.20.20.20.20.20.20.15VCNX50.50.50.50.50.50.50.50.50.50.50.50.CleanMarine(surface)BCKPMF.5.5.5.5.5.5.5.5.5.5.5.5OFRAC.25.25.30.30.30.30.30.30.30.30.30.25VCNX50.50.50.50.50.50.50.50.50.50.50.50.Urban-lowbiogenic(controlspresent)BCKPMF30.30.30.30.30.30.30.30.30.30.30.30.OFRAC.20.20.25.25.25.25.25.25.20.20.20.20VCNX4.4.4.4.4.4.4.4.4.4.4.4.Urban-highbiogenic(controlspresent)BCKPMF60.60.60.60.60.60.60.60.60.60.60.60.OFRAC.25.25.30.30.30.55.55.55.35.35.35.25VCNX15.15.15.15.15.15.15.15.15.15.15.15.RegionalPlumeBCKPMF20.20.20.20.20.20.20.20.20.20.20.20.OFRAC.20.20.25.35.25.40.40.40.30.30.30.20VCNX15.15.15.15.15.15.15.15.15.15.15.15.Urban-nocontrolspresentBCKPMF100.100.100.100.100.100.100.100.100.100.100.100.OFRAC.30.30.35.35.35.55.55.55.35.35.35.30VCNX2.2.2.2.2.2.2.2.2.2.2.2.23INVCAM02.inp10/23/2006Default:CleanContinental!BCKPMF=1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00,1.00!!OFRAC=0.15,0.15,0.20,0.20,0.20,0.20,0.20,0.20,0.20,0.20,0.20,0.15!!VCNX=50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00,50.00!!END!-------------------------------------------------------------------------------INPUTGROUP:12--Misc.DispersionandComputationalParameters---------------Horizontalsizeofpuff(m)beyondwhichtime-dependentdispersionequations(Heffter)areusedtodeterminesigma-yandsigma-z(SYTDEP)Default:550.!SYTDEP=5.5E02!SwitchforusingHeffterequationforsigmazasabove(0=NotuseHeffter;1=useHeffter(MHFTSZ)Default:0!MHFTSZ=0!Stabilityclassusedtodetermineplumegrowthratesforpuffsabovetheboundarylayer(JSUP)Default:5!JSUP=5!Verticaldispersionconstantforstableconditions(k1inEqn.2.7-3)(CONK1)Default:0.01!CONK1=.01!Verticaldispersionconstantforneutral/unstableconditions(k2inEqn.2.7-4)(CONK2)Default:0.1!CONK2=.1!FactorfordeterminingTransition-pointfromSchulman-SciretoHuber-SnyderBuildingDownwashscheme(SSusedforHs<Hb+TBD*HL)(TBD)Default:0.5!TBD=.5!TBD<0==>alwaysuseHuber-SnyderTBD=1.5==>alwaysuseSchulman-ScireTBD=0.5==>ISCTransition-pointRangeoflandusecategoriesforwhichurbandispersionisassumed(IURB1,IURB2)Default:10!IURB1=10!19!IURB2=19!24INVCAM02.inp10/23/2006Sitecharacterizationparametersforsingle-pointMetdatafiles---------(neededforMETFM=2,3,4,5)Landusecategoryformodelingdomain(ILANDUIN)Default:20!ILANDUIN=20!Roughnesslength(m)formodelingdomain(Z0IN)Default:0.25!Z0IN=.25!Leafareaindexformodelingdomain(XLAIIN)Default:3.0!XLAIIN=3.0!Elevationabovesealevel(m)(ELEVIN)Default:0.0!ELEVIN=.0!Latitude(degrees)formetlocation(XLATIN)Default:-999.!XLATIN=-999.0!Longitude(degrees)formetlocation(XLONIN)Default:-999.!XLONIN=-999.0!Specializedinformationforinterpretingsingle-pointMetdatafiles-----Anemometerheight(m)(UsedonlyifMETFM=2,3)(ANEMHT)Default:10.!ANEMHT=10.0!FormoflateralturbulancedatainPROFILE.DATfile(UsedonlyifMETFM=4,5orMTURBVW=1or3)(ISIGMAV)Default:1!ISIGMAV=1!0=readsigma-theta1=readsigma-vChoiceofmixingheights(UsedonlyifMETFM=4)(IMIXCTDM)Default:0!IMIXCTDM=0!0=readPREDICTEDmixingheights1=readOBSERVEDmixingheightsMaximumlengthofaslug(met.gridunits)(XMXLEN)Default:1.0!XMXLEN=1.0!Maximumtraveldistanceofapuff/slug(ingridunits)duringonesamplingstep(XSAMLEN)Default:1.0!XSAMLEN=1.0!MaximumNumberofslugs/puffsreleasefromonesourceduringonetimestep(MXNEW)Default:99!MXNEW=99!MaximumNumberofsamplingstepsfor25INVCAM02.inp10/23/2006onepuff/slugduringonetimestep(MXSAM)Default:99!MXSAM=99!Numberofiterationsusedwhencomputingthetransportwindforasamplingstepthatincludesgradualrise(forCALMETandPROFILEwinds)(NCOUNT)Default:2!NCOUNT=2!Minimumsigmayforanewpuff/slug(m)(SYMIN)Default:1.0!SYMIN=1.0!Minimumsigmazforanewpuff/slug(m)(SZMIN)Default:1.0!SZMIN=1.0!Defaultminimumturbulencevelocitiessigma-vandsigma-wforeachstabilityclassoverlandandoverwater(m/s)(SVMIN(12)andSWMIN(12))----------LAND-------------------WATER----------StabClass:ABCDEFABCDEF------------------------------------DefaultSVMIN:.50,.50,.50,.50,.50,.50,.37,.37,.37,.37,.37,.37DefaultSWMIN:.20,.12,.08,.06,.03,.016,.20,.12,.08,.06,.03,.016!SVMIN=0.500,0.500,0.500,0.500,0.500,0.500,0.370,0.370,0.370,0.370,0.370,0.370!!SWMIN=0.200,0.120,0.080,0.060,0.030,0.016,0.200,0.120,0.080,0.060,0.030,0.016!Divergencecriterionfordw/dzacrosspuffusedtoinitiateadjustmentforhorizontalconvergence(1/s)PartialadjustmentstartsatCDIV(1),andfulladjustmentisreachedatCDIV(2)(CDIV(2))Default:0.0,0.0!CDIV=.0,.0!Minimumwindspeed(m/s)allowedfornon-calmconditions.Alsousedasminimumspeedreturnedwhenusingpower-lawextrapolationtowardsurface(WSCALM)Default:0.5!WSCALM=.5!Maximummixingheight(m)(XMAXZI)Default:3000.!XMAXZI=3000.0!Minimummixingheight(m)(XMINZI)Default:50.!XMINZI=50.0!Defaultwindspeedclasses--5upperbounds(m/s)areentered;26INVCAM02.inp10/23/2006the6thclasshasnoupperlimit(WSCAT(5))Default:ISCRURAL:1.54,3.09,5.14,8.23,10.8(10.8+)WindSpeedClass:12345---------------!WSCAT=1.54,3.09,5.14,8.23,10.80!Defaultwindspeedprofilepower-lawexponentsforstabilities1-6(PLX0(6))Default:ISCRURALvaluesISCRURAL:.07,.07,.10,.15,.35,.55ISCURBAN:.15,.15,.20,.25,.30,.30StabilityClass:ABCDEF------------------!PLX0=0.07,0.07,0.10,0.15,0.35,0.55!DefaultpotentialtemperaturegradientforstableclassesE,F(degK/m)(PTG0(2))Default:0.020,0.035!PTG0=0.020,0.035!Defaultplumepathcoefficientsforeachstabilityclass(usedwhenoptionforpartialplumeheightterrainadjustmentisselected--MCTADJ=3)(PPC(6))StabilityClass:ABCDEFDefaultPPC:.50,.50,.50,.50,.35,.35------------------!PPC=0.50,0.50,0.50,0.50,0.35,0.35!Slug-to-pufftransitioncriterionfactorequaltosigma-y/lengthofslug(SL2PF)Default:10.!SL2PF=5.0!Puff-splittingcontrolvariables------------------------VERTICALSPLIT--------------Numberofpuffsthatresulteverytimeapuffissplit-nsplit=2meansthat1puffsplitsinto2(NSPLIT)Default:3!NSPLIT=3!Time(s)ofadaywhensplitpuffsareeligibletobesplitonceagain;thisistypicallysetonceperday,aroundsunsetbeforenocturnalsheardevelops.27INVCAM02.inp10/23/200624values:0ismidnight(00:00)and23is11PM(23:00)0=donotre-split1=eligibleforre-split(IRESPLIT(24))Default:Hour17=1!IRESPLIT=0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,0,1,0,0,0,0,0,0!Splitisallowedonlyiflasthour'smixingheight(m)exceedsaminimumvalue(ZISPLIT)Default:100.!ZISPLIT=100.0!Splitisallowedonlyifratiooflasthour'smixinghttothemaximummixinghtexperiencedbythepuffislessthanamaximumvalue(thispostponesasplituntilanocturnallayerdevelops)(ROLDMAX)Default:0.25!ROLDMAX=0.25!HORIZONTALSPLIT----------------Numberofpuffsthatresulteverytimeapuffissplit-nsplith=5meansthat1puffsplitsinto5(NSPLITH)Default:5!NSPLITH=5!Minimumsigma-y(GridCellsUnits)ofpuffbeforeitmaybesplit(SYSPLITH)Default:1.0!SYSPLITH=1.0!Minimumpuffelongationrate(SYSPLITH/hr)duetowindshear,beforeitmaybesplit(SHSPLITH)Default:2.!SHSPLITH=2.0!Minimumconcentration(g/m^3)ofeachspeciesinpuffbeforeitmaybesplitEnterarrayofNSPECvalues;ifasinglevalueisentered,itwillbeusedforALLspecies(CNSPLITH)Default:1.0E-07!CNSPLITH=1.0E-07!Integrationcontrolvariables------------------------FractionalconvergencecriterionfornumericalSLUGsamplingintegration(EPSSLUG)Default:1.0e-04!EPSSLUG=1.0E-04!FractionalconvergencecriterionfornumericalAREAsourceintegration(EPSAREA)Default:1.0e-06!EPSAREA=1.0E-06!Trajectorystep-length(m)usedfornumericalrise28INVCAM02.inp10/23/2006integration(DSRISE)Default:1.0!DSRISE=1.0!BoundaryCondition(BC)Puffcontrolvariables------------------------Minimumheight(m)towhichBCpuffsaremixedastheyareemitted(MBCON=2ONLY).Actualheightisresettothecurrentmixingheightatthereleasepointifgreaterthanthisminimum.(HTMINBC)Default:500.!HTMINBC=500.0!Searchradius(km)aboutareceptorforsamplingnearestBCpuff.BCpuffsaretypicallyemittedwithaspacingofonegridcelllength,sothesearchradiusshouldbegreaterthanDGRIDKM.(RSAMPBC)Default:10.!RSAMPBC=15.0!Near-SurfacedepletionadjustmenttoconcentrationprofileusedwhensamplingBCpuffs?(MDEPBC)Default:1!MDEPBC=0!0=ConcentrationisNOTadjustedfordepletion1=AdjustConcentrationfordepletion!END!-------------------------------------------------------------------------------INPUTGROUPS:13a,13b,13c,13d--Pointsourceparameters-----------------------------------------------Subgroup(13a)---------------Numberofpointsourceswithparametersprovidedbelow(NPT1)Nodefault!NPT1=3!Unitsusedforpointsourceemissionsbelow(IPTU)Default:1!IPTU=1!1=g/s2=kg/hr3=lb/hr4=tons/yr5=OdourUnit*m**3/s(vol.fluxofodourcompound)6=OdourUnit*m**3/min7=metrictons/yrNumberofsource-speciescombinationswithvariable29INVCAM02.inp10/23/2006emissionsscalingfactorsprovidedbelowin(13d)(NSPT1)Default:0!NSPT1=0!Numberofpointsourceswithvariableemissionparametersprovidedinexternalfile(NPT2)Nodefault!NPT2=0!(IfNPT2>0,thesepointsourceemissionsarereadfromthefile:PTEMARB.DAT)!END!---------------Subgroup(13b)---------------aPOINTSOURCE:CONSTANTDATA-----------------------------bcSourceXYStackBaseStackExitExitBldg.EmissionNo.CoordinateCoordinateHeightElevationDiameterVel.Temp.DwashRates(km)(km)(m)(m)(m)(m/s)(deg.K)------------------------------------------------------------------------1!SRCNAM=P13a!1!X=1491.195,-503.713,60.96,64.0,3.35,9.66,444.3,.0,6.61E+01,1.27E+00,1.68E+01,0.00E+00,0.00E+00,1.59E-01,1.59E-01,0.00E+00,0.00E+00,3.52E-01,5.03E-01,2.01E-01,7.54E-02,2.01E-01,1.51E-01,0.00E+00,0.00E+00,0.00E+00,2.48E-02!1!ZPLTFM=.0!1!FMFAC=1.0!!END!2!SRCNAM=P13b!2!X=1491.195,-503.713,60.96,64.0,3.35,9.66,444.3,.0,6.61E+01,1.27E+00,1.68E+01,0.00E+00,0.00E+00,1.59E-01,1.59E-01,0.00E+00,0.00E+00,3.52E-01,5.03E-01,2.01E-01,7.54E-02,2.01E-01,1.51E-01,0.00E+00,0.00E+00,0.00E+00,2.48E-02!2!ZPLTFM=.0!2!FMFAC=1.0!!END!3!SRCNAM=NB27-32!3!X=1490.761,-503.846,31.70,64.0,1.37,4.27,298.2,.0,0.00E+00,0.00E+00,0.00E+00,0.00E+00,0.00E+00,1.70E-01,1.70E-01,0.00E+00,0.00E+00,0.00E+00,0.00E+00,1.71E-01,1.71E-01,1.71E-01,1.71E-01,0.00E+00,0.00E+00,0.00E+00,0.00E+00!3!ZPLTFM=.0!30INVCAM02.inp10/23/20063!FMFAC=1.0!!END!--------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.SRCNAMisa12-characternameforasource(Nodefault)Xisanarrayholdingthesourcedatalistedbythecolumnheadings(Nodefault)SIGYZIisanarrayholdingtheinitialsigma-yandsigma-z(m)(Default:0.,0.)ZPLTFMistheplatformheight(m)forsourcesinfluencedbyanisolatedstructurethathasasignificantopenareabetweenthesurfaceandthebulkofthestructure,suchasanoffshoreoilplatform.TheBaseElevationisthatofthesurface(groundorocean),andtheStackHeightisthereleaseheightabovetheBase(notabovetheplatform).BuildingheightsenteredinSubgroup13cmustbethoseofthebuildingsontheplatform,measuredfromtheplatformdeck.ZPLTFMisusedonlywithMBDW=1(ISCdownwashmethod)forsourceswithbuildingdownwash.(Default:0.0)FMFACisaverticalmomentumfluxfactor(0.or1.0)usedtorepresenttheeffectofrain-capsorotherphysicalconfigurationsthatreducemomentumriseassociatedwiththeactualexitvelocity.(Default:1.0--fullmomentumused)b0.=Nobuildingdownwashmodeled,1.=downwashmodeledNOTE:mustbeenteredasaREALnumber(i.e.,withdecimalpoint)cAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyIPTU(e.g.1forg/s).---------------Subgroup(13c)---------------BUILDINGDIMENSIONDATAFORSOURCESSUBJECTTODOWNWASH-------------------------------------------------------SourceaNo.Effectivebuildingheight,width,lengthandX/Yoffset(inmeters)every10degrees.LENGTH,XBADJ,andYBADJareonlyneededfor31INVCAM02.inp10/23/2006MBDW=2(PRIMEdownwashoption)----------------------------------------------------------------------------------aBuildingheight,width,length,andX/Yoffsetfromthesourcearetreatedasaseparateinputsubgroupforeachsourceandthereforemustendwithaninputgroupterminator.TheX/Yoffsetistheposition,relativetothestack,ofthecenteroftheupwindfaceoftheprojectedbuilding,withthex-axispointingalongtheflowdirection.---------------Subgroup(13d)---------------aPOINTSOURCE:VARIABLEEMISSIONSDATA---------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin13b.Factorsenteredmultiplytheratesin13b.Skipsourcesherethathaveconstantemissions.Formoreelaboratevariationinsourceparameters,usePTEMARB.DATandNPT2>0.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant1=Diurnalcycle(24scalingfactors:hours1-24)2=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupperbounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.32INVCAM02.inp10/23/2006-------------------------------------------------------------------------------INPUTGROUPS:14a,14b,14c,14d--Areasourceparameters-----------------------------------------------Subgroup(14a)---------------Numberofpolygonareasourceswithparametersspecifiedbelow(NAR1)Nodefault!NAR1=0!Unitsusedforareasourceemissionsbelow(IARU)Default:1!IARU=1!1=g/m**2/s2=kg/m**2/hr3=lb/m**2/hr4=tons/m**2/yr5=OdourUnit*m/s(vol.flux/m**2ofodourcompound)6=OdourUnit*m/min7=metrictons/m**2/yrNumberofsource-speciescombinationswithvariableemissionsscalingfactorsprovidedbelowin(14d)(NSAR1)Default:0!NSAR1=0!Numberofbuoyantpolygonareasourceswithvariablelocationandemissionparameters(NAR2)Nodefault!NAR2=0!(IfNAR2>0,ALLparameterdataforthesesourcesarereadfromthefile:BAEMARB.DAT)!END!---------------Subgroup(14b)---------------aAREASOURCE:CONSTANTDATA----------------------------bSourceEffect.BaseInitialEmissionNo.HeightElevationSigmazRates(m)(m)(m)------------------------------------33INVCAM02.inp10/23/2006--------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.bAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyIARU(e.g.1forg/m**2/s).---------------Subgroup(14c)---------------COORDINATES(km)FOREACHVERTEX(4)OFEACHPOLYGON--------------------------------------------------------SourceaNo.OrderedlistofXfollowedbylistofY,groupedbysource--------------------------------------------------------------------------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.---------------Subgroup(14d)---------------aAREASOURCE:VARIABLEEMISSIONSDATA--------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin14b.Factorsenteredmultiplytheratesin14b.Skipsourcesherethathaveconstantemissions.Formoreelaboratevariationinsourceparameters,useBAEMARB.DATandNAR2>0.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant1=Diurnalcycle(24scalingfactors:hours1-24)2=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupper34INVCAM02.inp10/23/2006bounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUPS:15a,15b,15c--Linesourceparameters------------------------------------------Subgroup(15a)---------------Numberofbuoyantlinesourceswithvariablelocationandemissionparameters(NLN2)Nodefault!NLN2=0!(IfNLN2>0,ALLparameterdataforthesesourcesarereadfromthefile:LNEMARB.DAT)Numberofbuoyantlinesources(NLINES)Nodefault!NLINES=0!Unitsusedforlinesourceemissionsbelow(ILNU)Default:1!ILNU=1!1=g/s2=kg/hr3=lb/hr4=tons/yr5=OdourUnit*m**3/s(vol.fluxofodourcompound)6=OdourUnit*m**3/min7=metrictons/yrNumberofsource-speciescombinationswithvariableemissionsscalingfactorsprovidedbelowin(15c)(NSLN1)Default:0!NSLN1=0!Maximumnumberofsegmentsusedtomodeleachline(MXNSEG)Default:7!MXNSEG=7!35INVCAM02.inp10/23/2006ThefollowingvariablesarerequiredonlyifNLINES>0.Theyareusedinthebuoyantlinesourceplumerisecalculations.NumberofdistancesatwhichDefault:6!NLRISE=6!transitionalriseiscomputedAveragebuildinglength(XL)Nodefault!XL=.0!(inmeters)Averagebuildingheight(HBL)Nodefault!HBL=.0!(inmeters)Averagebuildingwidth(WBL)Nodefault!WBL=.0!(inmeters)Averagelinesourcewidth(WML)Nodefault!WML=.0!(inmeters)Averageseparationbetweenbuildings(DXL)Nodefault!DXL=.0!(inmeters)Averagebuoyancyparameter(FPRIMEL)Nodefault!FPRIMEL=.0!(inm**4/s**3)!END!---------------Subgroup(15b)---------------BUOYANTLINESOURCE:CONSTANTDATA----------------------------------aSourceBeg.XBeg.YEnd.XEnd.YReleaseBaseEmissionNo.CoordinateCoordinateCoordinateCoordinateHeightElevationRates(km)(km)(km)(km)(m)(m)------------------------------------------------------------------------------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.bAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyILNTU36INVCAM02.inp10/23/2006(e.g.1forg/s).---------------Subgroup(15c)---------------aBUOYANTLINESOURCE:VARIABLEEMISSIONSDATA----------------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin15b.Factorsenteredmultiplytheratesin15b.Skipsourcesherethathaveconstantemissions.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant1=Diurnalcycle(24scalingfactors:hours1-24)2=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupperbounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUPS:16a,16b,16c--Volumesourceparameters------------------------------------------Subgroup(16a)---------------Numberofvolumesourceswithparametersprovidedin16b,c(NVL1)Nodefault!NVL1=0!37INVCAM02.inp10/23/2006Unitsusedforvolumesourceemissionsbelowin16b(IVLU)Default:1!IVLU=1!1=g/s2=kg/hr3=lb/hr4=tons/yr5=OdourUnit*m**3/s(vol.fluxofodourcompound)6=OdourUnit*m**3/min7=metrictons/yrNumberofsource-speciescombinationswithvariableemissionsscalingfactorsprovidedbelowin(16c)(NSVL1)Default:0!NSVL1=0!Numberofvolumesourceswithvariablelocationandemissionparameters(NVL2)Nodefault!NVL2=0!(IfNVL2>0,ALLparameterdataforthesesourcesarereadfromtheVOLEMARB.DATfile(s))!END!---------------Subgroup(16b)---------------aVOLUMESOURCE:CONSTANTDATA------------------------------bXYEffect.BaseInitialInitialEmissionCoordinateCoordinateHeightElevationSigmaySigmazRates(km)(km)(m)(m)(m)(m)----------------------------------------------------------------aDataforeachsourcearetreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.bAnemissionratemustbeenteredforeverypollutantmodeled.Enteremissionrateofzeroforsecondarypollutantsthataremodeled,butnotemitted.UnitsarespecifiedbyIVLU(e.g.1forg/s).38INVCAM02.inp10/23/2006---------------Subgroup(16c)---------------aVOLUMESOURCE:VARIABLEEMISSIONSDATA----------------------------------------Usethissubgrouptodescribetemporalvariationsintheemissionratesgivenin16b.Factorsenteredmultiplytheratesin16b.Skipsourcesherethathaveconstantemissions.Formoreelaboratevariationinsourceparameters,useVOLEMARB.DATandNVL2>0.IVARYdeterminesthetypeofvariation,andissource-specific:(IVARY)Default:00=Constant1=Diurnalcycle(24scalingfactors:hours1-24)2=Monthlycycle(12scalingfactors:months1-12)3=Hour&Season(4groupsof24hourlyscalingfactors,wherefirstgroupisDEC-JAN-FEB)4=Speed&Stab.(6groupsof6scalingfactors,wherefirstgroupisStabilityClassA,andthespeedclasseshaveupperbounds(m/s)definedinGroup125=Temperature(12scalingfactors,wheretemperatureclasseshaveupperbounds(C)of:0,5,10,15,20,25,30,35,40,45,50,50+)--------aDataforeachspeciesaretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.-------------------------------------------------------------------------------INPUTGROUPS:17a&17b--Non-gridded(discrete)receptorinformation--------------------------------------Subgroup(17a)---------------Numberofnon-griddedreceptors(NREC)Nodefault!NREC=1076!!END!39INVCAM02.inp10/23/2006---------------Subgroup(17b)---------------aNON-GRIDDED(DISCRETE)RECEPTORDATA------------------------------------XYGroundHeightbReceptorCoordinateCoordinateElevationAboveGroundNo.(km)(km)(m)(m)-------------------------------------------------1!X=1609.918,-633.619,0,0.00!!END!2!X=1610.682,-633.471,1,0.00!!END!3!X=1610.506,-632.561,1,0.00!!END!4!X=1611.27,-632.414,1,0.00!!END!5!X=1611.094,-631.504,1,0.00!!END!6!X=1611.858,-631.356,1,0.00!!END!7!X=1610.154,-630.742,1,0.00!!END!8!X=1610.918,-630.594,1,0.00!!END!9!X=1611.682,-630.446,1,0.00!!END!10!X=1612.446,-630.298,1,0.00!!END!11!X=1610.742,-629.684,1,0.00!!END!12!X=1611.506,-629.536,1,0.00!!END!13!X=1612.269,-629.389,1,0.00!!END!14!X=1610.566,-628.774,0,0.00!!END!15!X=1611.33,-628.627,1,0.00!!END!16!X=1612.093,-628.479,1,0.00!!END!17!X=1612.857,-628.331,1,0.00!!END!18!X=1610.39,-627.865,1,0.00!!END!19!X=1611.154,-627.717,1,0.00!!END!20!X=1610.214,-626.955,1,0.00!!END!21!X=1610.978,-626.807,1,0.00!!END!22!X=1611.741,-626.66,1,0.00!!END!23!X=1610.802,-625.898,1,0.00!!END!24!X=1611.565,-625.75,1,0.00!!END!25!X=1610.626,-624.988,1,0.00!!END!26!X=1611.389,-624.84,2,0.00!!END!27!X=1612.152,-624.692,1,0.00!!END!28!X=1615.968,-623.952,0,0.00!!END!29!X=1611.213,-623.931,1,0.00!!END!30!X=1611.976,-623.783,1,0.00!!END!31!X=1616.554,-622.895,0,0.00!!END!32!X=1611.037,-623.021,1,0.00!!END!33!X=1611.8,-622.873,1,0.00!!END!34!X=1612.386,-621.816,1,0.00!!END!35!X=1613.149,-621.668,1,0.00!!END!36!X=1617.727,-620.779,0,0.00!!END!37!X=1612.973,-620.758,1,0.00!!END!38!X=1613.736,-620.61,1,0.00!!END!40INVCAM02.inp10/23/200639!X=1621.949,-618.069,0,0.00!!END!40!X=1622.711,-617.92,1,0.00!!END!41!X=1623.474,-617.771,1,0.00!!END!42!X=1614.146,-618.643,1,0.00!!END!43!X=1623.297,-616.862,1,0.00!!END!44!X=1624.059,-616.713,1,0.00!!END!45!X=1624.821,-616.564,1,0.00!!END!46!X=1625.584,-616.415,1,0.00!!END!47!X=1633.208,-614.921,1,0.00!!END!48!X=1633.97,-614.771,0,0.00!!END!49!X=1614.732,-617.586,1,0.00!!END!50!X=1621.594,-616.25,0,0.00!!END!51!X=1622.357,-616.102,1,0.00!!END!52!X=1623.119,-615.953,1,0.00!!END!53!X=1623.881,-615.804,1,0.00!!END!54!X=1624.644,-615.655,1,0.00!!END!55!X=1625.406,-615.506,1,0.00!!END!56!X=1626.169,-615.357,1,0.00!!END!57!X=1626.931,-615.208,1,0.00!!END!58!X=1627.693,-615.059,1,0.00!!END!59!X=1628.456,-614.909,2,0.00!!END!60!X=1629.218,-614.76,2,0.00!!END!61!X=1629.98,-614.611,1,0.00!!END!62!X=1630.742,-614.461,2,0.00!!END!63!X=1631.505,-614.311,1,0.00!!END!64!X=1633.791,-613.862,0,0.00!!END!65!X=1615.318,-616.528,1,0.00!!END!66!X=1616.08,-616.38,1,0.00!!END!67!X=1616.843,-616.232,1,0.00!!END!68!X=1620.654,-615.49,0,0.00!!END!69!X=1621.417,-615.341,1,0.00!!END!70!X=1622.179,-615.192,1,0.00!!END!71!X=1622.942,-615.044,1,0.00!!END!72!X=1623.704,-614.895,1,0.00!!END!73!X=1624.466,-614.746,1,0.00!!END!74!X=1625.228,-614.597,1,0.00!!END!75!X=1628.277,-614,1,0.00!!END!76!X=1629.04,-613.851,1,0.00!!END!77!X=1632.088,-613.253,1,0.00!!END!78!X=1634.375,-612.803,0,0.00!!END!79!X=1619.715,-614.729,0,0.00!!END!80!X=1620.477,-614.58,1,0.00!!END!81!X=1621.24,-614.432,1,0.00!!END!82!X=1622.002,-614.283,1,0.00!!END!83!X=1622.764,-614.134,1,0.00!!END!84!X=1623.526,-613.986,1,0.00!!END!85!X=1624.288,-613.837,1,0.00!!END!86!X=1625.051,-613.688,1,0.00!!END!87!X=1625.813,-613.539,1,0.00!!END!41INVCAM02.inp10/23/200688!X=1626.575,-613.389,1,0.00!!END!89!X=1627.337,-613.24,1,0.00!!END!90!X=1629.624,-612.792,1,0.00!!END!91!X=1630.386,-612.643,1,0.00!!END!92!X=1631.148,-612.493,1,0.00!!END!93!X=1631.91,-612.344,1,0.00!!END!94!X=1634.196,-611.894,0,0.00!!END!95!X=1618.776,-613.968,1,0.00!!END!96!X=1619.538,-613.82,1,0.00!!END!97!X=1620.3,-613.671,1,0.00!!END!98!X=1621.062,-613.523,1,0.00!!END!99!X=1621.824,-613.374,1,0.00!!END!100!X=1622.587,-613.225,1,0.00!!END!101!X=1623.349,-613.076,1,0.00!!END!102!X=1624.111,-612.927,1,0.00!!END!103!X=1624.873,-612.778,1,0.00!!END!104!X=1625.635,-612.629,1,0.00!!END!105!X=1626.397,-612.48,1,0.00!!END!106!X=1627.159,-612.331,1,0.00!!END!107!X=1627.921,-612.182,1,0.00!!END!108!X=1628.683,-612.033,1,0.00!!END!109!X=1629.445,-611.883,1,0.00!!END!110!X=1630.207,-611.734,1,0.00!!END!111!X=1630.969,-611.584,1,0.00!!END!112!X=1634.017,-610.985,0,0.00!!END!113!X=1620.123,-612.762,1,0.00!!END!114!X=1620.885,-612.613,1,0.00!!END!115!X=1621.647,-612.465,1,0.00!!END!116!X=1622.409,-612.316,1,0.00!!END!117!X=1623.171,-612.167,1,0.00!!END!118!X=1623.933,-612.018,1,0.00!!END!119!X=1624.695,-611.869,1,0.00!!END!120!X=1625.457,-611.72,1,0.00!!END!121!X=1626.219,-611.571,1,0.00!!END!122!X=1626.981,-611.422,1,0.00!!END!123!X=1627.743,-611.273,1,0.00!!END!124!X=1628.505,-611.123,1,0.00!!END!125!X=1633.077,-610.226,0,0.00!!END!126!X=1633.839,-610.076,1,0.00!!END!127!X=1634.6,-609.927,1,0.00!!END!128!X=1621.47,-611.555,1,0.00!!END!129!X=1622.232,-611.407,1,0.00!!END!130!X=1622.993,-611.258,1,0.00!!END!131!X=1623.755,-611.109,1,0.00!!END!132!X=1624.517,-610.96,1,0.00!!END!133!X=1625.279,-610.811,1,0.00!!END!134!X=1626.041,-610.662,1,0.00!!END!135!X=1626.803,-610.513,1,0.00!!END!136!X=1627.565,-610.364,1,0.00!!END!42INVCAM02.inp10/23/2006137!X=1628.327,-610.214,1,0.00!!END!138!X=1629.089,-610.065,1,0.00!!END!139!X=1629.851,-609.916,1,0.00!!END!140!X=1630.613,-609.766,1,0.00!!END!141!X=1634.422,-609.018,0,0.00!!END!142!X=1624.34,-610.051,1,0.00!!END!143!X=1625.102,-609.902,1,0.00!!END!144!X=1625.863,-609.753,1,0.00!!END!145!X=1626.625,-609.604,1,0.00!!END!146!X=1627.387,-609.455,1,0.00!!END!147!X=1628.149,-609.305,1,0.00!!END!148!X=1628.911,-609.156,1,0.00!!END!149!X=1629.672,-609.007,1,0.00!!END!150!X=1630.434,-608.857,1,0.00!!END!151!X=1634.243,-608.109,0,0.00!!END!152!X=1628.732,-608.247,1,0.00!!END!153!X=1629.494,-608.098,1,0.00!!END!154!X=1630.256,-607.948,1,0.00!!END!155!X=1631.017,-607.799,1,0.00!!END!156!X=1629.316,-607.189,1,0.00!!END!157!X=1630.077,-607.039,1,0.00!!END!158!X=1630.839,-606.89,1,0.00!!END!159!X=1631.6,-606.74,1,0.00!!END!160!X=1629.899,-606.13,1,0.00!!END!161!X=1630.66,-605.981,1,0.00!!END!162!X=1631.422,-605.831,1,0.00!!END!163!X=1629.721,-605.221,1,0.00!!END!164!X=1630.482,-605.072,1,0.00!!END!165!X=1201.214,-417.246,521,0.00!!END!166!X=1204.191,-416.805,521,0.00!!END!167!X=1189.038,-417.173,521,0.00!!END!168!X=1190.527,-416.954,522,0.00!!END!169!X=1192.015,-416.736,523,0.00!!END!170!X=1193.503,-416.517,521,0.00!!END!171!X=1194.991,-416.298,538,0.00!!END!172!X=1196.48,-416.079,550,0.00!!END!173!X=1197.968,-415.859,640,0.00!!END!174!X=1199.456,-415.639,607,0.00!!END!175!X=1200.944,-415.419,523,0.00!!END!176!X=1202.432,-415.199,548,0.00!!END!177!X=1203.92,-414.978,524,0.00!!END!178!X=1205.408,-414.757,608,0.00!!END!179!X=1208.384,-414.315,546,0.00!!END!180!X=1209.871,-414.093,566,0.00!!END!181!X=1211.359,-413.871,541,0.00!!END!182!X=1212.847,-413.649,530,0.00!!END!183!X=1181.33,-416.432,683,0.00!!END!184!X=1182.818,-416.216,711,0.00!!END!185!X=1184.306,-415.998,583,0.00!!END!43INVCAM02.inp10/23/2006186!X=1185.795,-415.781,599,0.00!!END!187!X=1187.283,-415.564,561,0.00!!END!188!X=1188.771,-415.346,582,0.00!!END!189!X=1190.259,-415.128,703,0.00!!END!190!X=1191.747,-414.909,707,0.00!!END!191!X=1193.235,-414.69,522,0.00!!END!192!X=1194.722,-414.471,760,0.00!!END!193!X=1196.21,-414.252,846,0.00!!END!194!X=1197.698,-414.033,952,0.00!!END!195!X=1199.186,-413.813,765,0.00!!END!196!X=1200.674,-413.593,1067,0.00!!END!197!X=1202.161,-413.372,915,0.00!!END!198!X=1203.649,-413.152,730,0.00!!END!199!X=1205.136,-412.931,822,0.00!!END!200!X=1206.624,-412.71,748,0.00!!END!201!X=1208.112,-412.488,544,0.00!!END!202!X=1209.599,-412.267,706,0.00!!END!203!X=1211.086,-412.045,627,0.00!!END!204!X=1212.574,-411.822,845,0.00!!END!205!X=1214.061,-411.6,772,0.00!!END!206!X=1215.549,-411.377,836,0.00!!END!207!X=1220.01,-410.707,665,0.00!!END!208!X=1175.112,-415.469,554,0.00!!END!209!X=1176.6,-415.254,760,0.00!!END!210!X=1178.088,-415.038,805,0.00!!END!211!X=1179.576,-414.822,703,0.00!!END!212!X=1181.064,-414.605,729,0.00!!END!213!X=1182.552,-414.388,699,0.00!!END!214!X=1184.04,-414.171,1109,0.00!!END!215!X=1185.528,-413.954,1001,0.00!!END!216!X=1187.015,-413.737,811,0.00!!END!217!X=1188.503,-413.519,522,0.00!!END!218!X=1189.991,-413.301,581,0.00!!END!219!X=1191.478,-413.082,629,0.00!!END!220!X=1192.966,-412.864,634,0.00!!END!221!X=1194.453,-412.645,582,0.00!!END!222!X=1195.941,-412.425,612,0.00!!END!223!X=1197.428,-412.206,944,0.00!!END!224!X=1198.916,-411.986,1281,0.00!!END!225!X=1200.403,-411.766,1427,0.00!!END!226!X=1201.891,-411.546,1221,0.00!!END!227!X=1203.378,-411.325,1030,0.00!!END!228!X=1204.865,-411.105,983,0.00!!END!229!X=1206.352,-410.883,894,0.00!!END!230!X=1207.84,-410.662,675,0.00!!END!231!X=1209.327,-410.44,950,0.00!!END!232!X=1210.814,-410.219,915,0.00!!END!233!X=1212.301,-409.996,732,0.00!!END!234!X=1213.788,-409.774,980,0.00!!END!44INVCAM02.inp10/23/2006235!X=1216.762,-409.328,1020,0.00!!END!236!X=1218.249,-409.105,886,0.00!!END!237!X=1219.736,-408.881,615,0.00!!END!238!X=1221.222,-408.657,680,0.00!!END!239!X=1176.335,-413.427,767,0.00!!END!240!X=1177.823,-413.211,919,0.00!!END!241!X=1179.311,-412.994,905,0.00!!END!242!X=1180.798,-412.778,911,0.00!!END!243!X=1182.286,-412.561,965,0.00!!END!244!X=1183.773,-412.344,837,0.00!!END!245!X=1185.261,-412.127,1055,0.00!!END!246!X=1186.748,-411.91,716,0.00!!END!247!X=1188.235,-411.692,825,0.00!!END!248!X=1189.723,-411.474,609,0.00!!END!249!X=1191.21,-411.255,814,0.00!!END!250!X=1192.697,-411.037,1006,0.00!!END!251!X=1194.184,-410.818,1036,0.00!!END!252!X=1195.672,-410.599,732,0.00!!END!253!X=1197.159,-410.379,746,0.00!!END!254!X=1198.646,-410.16,929,0.00!!END!255!X=1200.133,-409.94,1008,0.00!!END!256!X=1201.62,-409.72,1288,0.00!!END!257!X=1203.107,-409.499,1266,0.00!!END!258!X=1204.594,-409.278,1218,0.00!!END!259!X=1206.081,-409.057,959,0.00!!END!260!X=1207.568,-408.836,681,0.00!!END!261!X=1209.054,-408.614,920,0.00!!END!262!X=1210.541,-408.392,1170,0.00!!END!263!X=1212.028,-408.17,956,0.00!!END!264!X=1213.514,-407.948,818,0.00!!END!265!X=1215.001,-407.725,1223,0.00!!END!266!X=1216.488,-407.502,1270,0.00!!END!267!X=1217.974,-407.279,872,0.00!!END!268!X=1219.461,-407.055,694,0.00!!END!269!X=1220.947,-406.832,963,0.00!!END!270!X=1222.434,-406.608,859,0.00!!END!271!X=1223.92,-406.383,1000,0.00!!END!272!X=1170.121,-412.46,365,0.00!!END!273!X=1171.608,-412.245,406,0.00!!END!274!X=1173.096,-412.03,600,0.00!!END!275!X=1174.583,-411.815,591,0.00!!END!276!X=1176.07,-411.599,644,0.00!!END!277!X=1177.558,-411.383,1036,0.00!!END!278!X=1179.045,-411.167,1309,0.00!!END!279!X=1180.532,-410.951,1262,0.00!!END!280!X=1182.019,-410.734,1261,0.00!!END!281!X=1183.506,-410.517,1072,0.00!!END!282!X=1184.994,-410.3,1199,0.00!!END!283!X=1186.481,-410.083,1097,0.00!!END!45INVCAM02.inp10/23/2006284!X=1187.968,-409.865,720,0.00!!END!285!X=1189.455,-409.647,640,0.00!!END!286!X=1190.942,-409.429,873,0.00!!END!287!X=1192.429,-409.21,852,0.00!!END!288!X=1193.915,-408.991,978,0.00!!END!289!X=1195.402,-408.772,809,0.00!!END!290!X=1196.889,-408.553,761,0.00!!END!291!X=1198.376,-408.333,987,0.00!!END!292!X=1199.863,-408.113,874,0.00!!END!293!X=1201.349,-407.893,1147,0.00!!END!294!X=1202.836,-407.673,1323,0.00!!END!295!X=1204.322,-407.452,1221,0.00!!END!296!X=1205.809,-407.231,1097,0.00!!END!297!X=1207.295,-407.01,800,0.00!!END!298!X=1208.782,-406.788,942,0.00!!END!299!X=1210.268,-406.566,1167,0.00!!END!300!X=1211.755,-406.344,1052,0.00!!END!301!X=1213.241,-406.122,1012,0.00!!END!302!X=1214.727,-405.899,1002,0.00!!END!303!X=1216.214,-405.676,1143,0.00!!END!304!X=1217.7,-405.453,998,0.00!!END!305!X=1219.186,-405.23,710,0.00!!END!306!X=1220.672,-405.006,998,0.00!!END!307!X=1222.158,-404.782,907,0.00!!END!308!X=1223.644,-404.558,1200,0.00!!END!309!X=1225.13,-404.333,1173,0.00!!END!310!X=1226.616,-404.108,1067,0.00!!END!311!X=1228.102,-403.883,896,0.00!!END!312!X=1229.588,-403.658,799,0.00!!END!313!X=1231.074,-403.432,683,0.00!!END!314!X=1169.857,-410.632,330,0.00!!END!315!X=1171.344,-410.418,523,0.00!!END!316!X=1172.831,-410.203,599,0.00!!END!317!X=1174.318,-409.988,769,0.00!!END!318!X=1175.805,-409.772,831,0.00!!END!319!X=1177.292,-409.556,941,0.00!!END!320!X=1178.779,-409.34,1150,0.00!!END!321!X=1180.266,-409.124,1194,0.00!!END!322!X=1181.753,-408.907,1084,0.00!!END!323!X=1183.24,-408.69,1206,0.00!!END!324!X=1184.727,-408.473,1225,0.00!!END!325!X=1186.213,-408.256,987,0.00!!END!326!X=1187.7,-408.038,1063,0.00!!END!327!X=1189.187,-407.82,873,0.00!!END!328!X=1190.673,-407.602,921,0.00!!END!329!X=1192.16,-407.384,1233,0.00!!END!330!X=1193.646,-407.165,1006,0.00!!END!331!X=1195.133,-406.946,1024,0.00!!END!332!X=1196.619,-406.726,792,0.00!!END!46INVCAM02.inp10/23/2006333!X=1198.106,-406.507,1015,0.00!!END!334!X=1199.592,-406.287,1094,0.00!!END!335!X=1201.079,-406.067,996,0.00!!END!336!X=1202.565,-405.846,1148,0.00!!END!337!X=1204.051,-405.626,1368,0.00!!END!338!X=1205.537,-405.405,1052,0.00!!END!339!X=1207.023,-405.184,958,0.00!!END!340!X=1208.51,-404.962,988,0.00!!END!341!X=1209.996,-404.74,1019,0.00!!END!342!X=1211.482,-404.518,1344,0.00!!END!343!X=1212.968,-404.296,1246,0.00!!END!344!X=1214.454,-404.073,1377,0.00!!END!345!X=1215.94,-403.85,1135,0.00!!END!346!X=1217.426,-403.627,1196,0.00!!END!347!X=1218.911,-403.404,851,0.00!!END!348!X=1220.397,-403.18,883,0.00!!END!349!X=1221.883,-402.956,1060,0.00!!END!350!X=1223.369,-402.732,1207,0.00!!END!351!X=1224.854,-402.507,1245,0.00!!END!352!X=1226.34,-402.283,1045,0.00!!END!353!X=1227.826,-402.058,1068,0.00!!END!354!X=1229.311,-401.832,870,0.00!!END!355!X=1230.797,-401.607,782,0.00!!END!356!X=1241.194,-400.02,1326,0.00!!END!357!X=1169.593,-408.805,453,0.00!!END!358!X=1171.08,-408.59,439,0.00!!END!359!X=1172.567,-408.376,582,0.00!!END!360!X=1174.054,-408.16,664,0.00!!END!361!X=1175.54,-407.945,770,0.00!!END!362!X=1177.027,-407.729,853,0.00!!END!363!X=1178.514,-407.513,810,0.00!!END!364!X=1180,-407.297,979,0.00!!END!365!X=1181.487,-407.08,809,0.00!!END!366!X=1182.973,-406.864,818,0.00!!END!367!X=1184.46,-406.646,1027,0.00!!END!368!X=1185.946,-406.429,1372,0.00!!END!369!X=1187.432,-406.211,1203,0.00!!END!370!X=1188.919,-405.994,975,0.00!!END!371!X=1190.405,-405.775,1077,0.00!!END!372!X=1191.891,-405.557,1343,0.00!!END!373!X=1193.377,-405.338,1463,0.00!!END!374!X=1194.864,-405.119,1193,0.00!!END!375!X=1196.35,-404.9,932,0.00!!END!376!X=1197.836,-404.68,1059,0.00!!END!377!X=1199.322,-404.461,1144,0.00!!END!378!X=1200.808,-404.24,1231,0.00!!END!379!X=1202.294,-404.02,1197,0.00!!END!380!X=1203.78,-403.799,1220,0.00!!END!381!X=1205.266,-403.579,1342,0.00!!END!47INVCAM02.inp10/23/2006382!X=1206.751,-403.357,1350,0.00!!END!383!X=1208.237,-403.136,1251,0.00!!END!384!X=1209.723,-402.914,1467,0.00!!END!385!X=1211.209,-402.692,1407,0.00!!END!386!X=1212.694,-402.47,1671,0.00!!END!387!X=1214.18,-402.247,1369,0.00!!END!388!X=1215.666,-402.025,1412,0.00!!END!389!X=1217.151,-401.801,1279,0.00!!END!390!X=1218.637,-401.578,863,0.00!!END!391!X=1220.122,-401.354,823,0.00!!END!392!X=1221.608,-401.131,1103,0.00!!END!393!X=1223.093,-400.906,1432,0.00!!END!394!X=1224.578,-400.682,1448,0.00!!END!395!X=1226.064,-400.457,1352,0.00!!END!396!X=1227.549,-400.232,1094,0.00!!END!397!X=1229.034,-400.007,802,0.00!!END!398!X=1230.519,-399.781,756,0.00!!END!399!X=1239.43,-398.422,1213,0.00!!END!400!X=1240.915,-398.195,1312,0.00!!END!401!X=1169.33,-406.978,365,0.00!!END!402!X=1170.816,-406.763,393,0.00!!END!403!X=1172.303,-406.548,455,0.00!!END!404!X=1173.789,-406.333,590,0.00!!END!405!X=1175.275,-406.118,775,0.00!!END!406!X=1176.762,-405.902,690,0.00!!END!407!X=1178.248,-405.686,697,0.00!!END!408!X=1179.734,-405.47,678,0.00!!END!409!X=1181.22,-405.253,607,0.00!!END!410!X=1182.707,-405.037,824,0.00!!END!411!X=1184.193,-404.82,802,0.00!!END!412!X=1185.679,-404.602,1033,0.00!!END!413!X=1187.165,-404.385,1241,0.00!!END!414!X=1188.651,-404.167,1297,0.00!!END!415!X=1190.137,-403.949,1503,0.00!!END!416!X=1191.623,-403.73,1477,0.00!!END!417!X=1193.108,-403.512,1533,0.00!!END!418!X=1194.594,-403.293,1242,0.00!!END!419!X=1196.08,-403.073,1270,0.00!!END!420!X=1197.566,-402.854,1198,0.00!!END!421!X=1199.052,-402.634,1372,0.00!!END!422!X=1200.537,-402.414,1394,0.00!!END!423!X=1202.023,-402.194,1187,0.00!!END!424!X=1203.508,-401.973,1517,0.00!!END!425!X=1204.994,-401.752,1490,0.00!!END!426!X=1206.479,-401.531,1518,0.00!!END!427!X=1207.965,-401.31,1632,0.00!!END!428!X=1209.45,-401.088,1692,0.00!!END!429!X=1210.936,-400.866,1888,0.00!!END!430!X=1212.421,-400.644,1951,0.00!!END!48INVCAM02.inp10/23/2006431!X=1213.906,-400.422,1603,0.00!!END!432!X=1215.392,-400.199,1543,0.00!!END!433!X=1216.877,-399.976,1292,0.00!!END!434!X=1218.362,-399.752,1067,0.00!!END!435!X=1219.847,-399.529,928,0.00!!END!436!X=1221.332,-399.305,1190,0.00!!END!437!X=1222.817,-399.081,1415,0.00!!END!438!X=1224.302,-398.856,1066,0.00!!END!439!X=1225.787,-398.632,899,0.00!!END!440!X=1227.272,-398.407,714,0.00!!END!441!X=1228.757,-398.182,703,0.00!!END!442!X=1237.666,-396.825,1097,0.00!!END!443!X=1239.15,-396.597,1224,0.00!!END!444!X=1240.635,-396.37,1526,0.00!!END!445!X=1242.119,-396.142,1566,0.00!!END!446!X=1243.604,-395.914,1311,0.00!!END!447!X=1245.088,-395.686,1283,0.00!!END!448!X=1246.573,-395.458,1482,0.00!!END!449!X=1169.066,-405.15,290,0.00!!END!450!X=1170.552,-404.936,389,0.00!!END!451!X=1172.038,-404.721,506,0.00!!END!452!X=1173.524,-404.506,644,0.00!!END!453!X=1175.01,-404.291,578,0.00!!END!454!X=1176.496,-404.075,539,0.00!!END!455!X=1177.982,-403.859,634,0.00!!END!456!X=1179.468,-403.643,662,0.00!!END!457!X=1180.954,-403.427,567,0.00!!END!458!X=1182.44,-403.21,579,0.00!!END!459!X=1183.926,-402.993,660,0.00!!END!460!X=1185.411,-402.776,878,0.00!!END!461!X=1186.897,-402.558,907,0.00!!END!462!X=1188.383,-402.34,955,0.00!!END!463!X=1189.868,-402.122,1048,0.00!!END!464!X=1191.354,-401.904,1056,0.00!!END!465!X=1192.839,-401.685,1333,0.00!!END!466!X=1194.325,-401.466,1223,0.00!!END!467!X=1195.81,-401.247,1411,0.00!!END!468!X=1197.296,-401.028,1106,0.00!!END!469!X=1198.781,-400.808,1347,0.00!!END!470!X=1200.267,-400.588,1222,0.00!!END!471!X=1201.752,-400.368,1524,0.00!!END!472!X=1203.237,-400.147,1386,0.00!!END!473!X=1204.722,-399.926,1198,0.00!!END!474!X=1206.207,-399.705,1242,0.00!!END!475!X=1207.693,-399.484,1415,0.00!!END!476!X=1209.178,-399.262,1358,0.00!!END!477!X=1210.663,-399.04,1355,0.00!!END!478!X=1212.148,-398.818,1403,0.00!!END!479!X=1213.633,-398.596,1712,0.00!!END!49INVCAM02.inp10/23/2006480!X=1215.118,-398.373,1431,0.00!!END!481!X=1216.603,-398.15,1422,0.00!!END!482!X=1218.087,-397.927,1236,0.00!!END!483!X=1219.572,-397.703,1228,0.00!!END!484!X=1221.057,-397.479,1492,0.00!!END!485!X=1222.542,-397.255,1372,0.00!!END!486!X=1224.026,-397.031,1181,0.00!!END!487!X=1225.511,-396.806,792,0.00!!END!488!X=1226.996,-396.581,939,0.00!!END!489!X=1228.48,-396.356,737,0.00!!END!490!X=1229.965,-396.131,1213,0.00!!END!491!X=1231.449,-395.905,1173,0.00!!END!492!X=1235.902,-395.226,1111,0.00!!END!493!X=1237.387,-395,1138,0.00!!END!494!X=1238.871,-394.773,1362,0.00!!END!495!X=1240.355,-394.545,1709,0.00!!END!496!X=1241.839,-394.318,1585,0.00!!END!497!X=1243.323,-394.09,1298,0.00!!END!498!X=1244.808,-393.862,1224,0.00!!END!499!X=1246.292,-393.633,1150,0.00!!END!500!X=1247.776,-393.404,1348,0.00!!END!501!X=1171.774,-402.894,383,0.00!!END!502!X=1173.26,-402.679,482,0.00!!END!503!X=1174.745,-402.464,533,0.00!!END!504!X=1176.231,-402.248,559,0.00!!END!505!X=1177.717,-402.032,598,0.00!!END!506!X=1179.202,-401.816,532,0.00!!END!507!X=1180.688,-401.6,525,0.00!!END!508!X=1182.173,-401.383,533,0.00!!END!509!X=1183.659,-401.166,543,0.00!!END!510!X=1185.144,-400.949,562,0.00!!END!511!X=1186.629,-400.731,602,0.00!!END!512!X=1188.115,-400.514,736,0.00!!END!513!X=1189.6,-400.296,817,0.00!!END!514!X=1191.085,-400.077,809,0.00!!END!515!X=1192.57,-399.859,920,0.00!!END!516!X=1194.056,-399.64,1017,0.00!!END!517!X=1195.541,-399.421,1006,0.00!!END!518!X=1197.026,-399.201,956,0.00!!END!519!X=1198.511,-398.982,1137,0.00!!END!520!X=1199.996,-398.762,982,0.00!!END!521!X=1201.481,-398.541,1187,0.00!!END!522!X=1202.966,-398.321,1365,0.00!!END!523!X=1204.451,-398.1,1245,0.00!!END!524!X=1205.935,-397.879,1074,0.00!!END!525!X=1207.42,-397.658,1365,0.00!!END!526!X=1208.905,-397.436,1401,0.00!!END!527!X=1210.39,-397.214,1080,0.00!!END!528!X=1211.874,-396.992,1260,0.00!!END!50INVCAM02.inp10/23/2006529!X=1213.359,-396.77,1660,0.00!!END!530!X=1214.844,-396.547,1703,0.00!!END!531!X=1216.328,-396.324,1525,0.00!!END!532!X=1217.813,-396.101,1299,0.00!!END!533!X=1219.297,-395.878,1389,0.00!!END!534!X=1220.782,-395.654,1084,0.00!!END!535!X=1222.266,-395.43,1048,0.00!!END!536!X=1223.75,-395.206,1002,0.00!!END!537!X=1225.235,-394.981,1374,0.00!!END!538!X=1226.719,-394.756,910,0.00!!END!539!X=1228.203,-394.531,1109,0.00!!END!540!X=1229.687,-394.306,1002,0.00!!END!541!X=1231.171,-394.08,1469,0.00!!END!542!X=1232.656,-393.854,1136,0.00!!END!543!X=1234.14,-393.628,1324,0.00!!END!544!X=1235.624,-393.401,912,0.00!!END!545!X=1237.108,-393.175,1427,0.00!!END!546!X=1238.592,-392.948,1487,0.00!!END!547!X=1240.075,-392.72,1681,0.00!!END!548!X=1241.559,-392.493,1310,0.00!!END!549!X=1243.043,-392.265,1080,0.00!!END!550!X=1244.527,-392.037,1029,0.00!!END!551!X=1246.011,-391.808,989,0.00!!END!552!X=1247.494,-391.58,1038,0.00!!END!553!X=1248.978,-391.351,1337,0.00!!END!554!X=1172.995,-400.852,368,0.00!!END!555!X=1174.481,-400.637,411,0.00!!END!556!X=1175.966,-400.421,485,0.00!!END!557!X=1177.451,-400.205,480,0.00!!END!558!X=1178.936,-399.989,569,0.00!!END!559!X=1180.421,-399.773,610,0.00!!END!560!X=1181.907,-399.556,585,0.00!!END!561!X=1183.392,-399.339,596,0.00!!END!562!X=1184.877,-399.122,591,0.00!!END!563!X=1186.362,-398.905,681,0.00!!END!564!X=1187.847,-398.687,787,0.00!!END!565!X=1189.332,-398.469,528,0.00!!END!566!X=1190.817,-398.251,700,0.00!!END!567!X=1192.302,-398.032,615,0.00!!END!568!X=1193.786,-397.813,905,0.00!!END!569!X=1195.271,-397.594,836,0.00!!END!570!X=1196.756,-397.375,827,0.00!!END!571!X=1198.241,-397.155,768,0.00!!END!572!X=1199.725,-396.935,983,0.00!!END!573!X=1201.21,-396.715,1281,0.00!!END!574!X=1202.694,-396.495,1378,0.00!!END!575!X=1204.179,-396.274,1371,0.00!!END!576!X=1205.663,-396.053,1135,0.00!!END!577!X=1207.148,-395.832,884,0.00!!END!51INVCAM02.inp10/23/2006578!X=1208.632,-395.61,907,0.00!!END!579!X=1210.117,-395.389,1249,0.00!!END!580!X=1211.601,-395.167,1528,0.00!!END!581!X=1213.085,-394.944,1552,0.00!!END!582!X=1214.57,-394.722,1473,0.00!!END!583!X=1216.054,-394.499,1677,0.00!!END!584!X=1217.538,-394.276,1553,0.00!!END!585!X=1219.022,-394.052,1572,0.00!!END!586!X=1220.506,-393.828,1526,0.00!!END!587!X=1221.99,-393.604,1261,0.00!!END!588!X=1223.474,-393.38,1217,0.00!!END!589!X=1224.958,-393.156,1247,0.00!!END!590!X=1226.442,-392.931,947,0.00!!END!591!X=1227.926,-392.706,1163,0.00!!END!592!X=1229.41,-392.48,1434,0.00!!END!593!X=1230.894,-392.255,1373,0.00!!END!594!X=1232.378,-392.029,1170,0.00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X=1215.231,-389.022,1569,0.00!!END!54INVCAM02.inp10/23/2006725!X=1216.714,-388.799,1595,0.00!!END!726!X=1218.197,-388.576,1195,0.00!!END!727!X=1219.68,-388.352,961,0.00!!END!728!X=1221.163,-388.128,1084,0.00!!END!729!X=1222.646,-387.904,1324,0.00!!END!730!X=1224.129,-387.68,1732,0.00!!END!731!X=1225.612,-387.455,1720,0.00!!END!732!X=1227.095,-387.23,1512,0.00!!END!733!X=1228.578,-387.005,1680,0.00!!END!734!X=1230.061,-386.78,1528,0.00!!END!735!X=1231.544,-386.554,1452,0.00!!END!736!X=1233.026,-386.328,1535,0.00!!END!737!X=1234.509,-386.102,1401,0.00!!END!738!X=1235.992,-385.875,1483,0.00!!END!739!X=1237.474,-385.648,1605,0.00!!END!740!X=1238.957,-385.421,1574,0.00!!END!741!X=1240.439,-385.194,1577,0.00!!END!742!X=1241.922,-384.966,1326,0.00!!END!743!X=1243.404,-384.738,1393,0.00!!END!744!X=1244.887,-384.51,1134,0.00!!END!745!X=1246.369,-384.282,971,0.00!!END!746!X=1247.851,-384.053,945,0.00!!END!747!X=1249.333,-383.824,1058,0.00!!END!748!X=1192.709,-390.508,492,0.00!!END!749!X=1194.193,-390.289,640,0.00!!END!750!X=1195.676,-390.07,587,0.00!!END!751!X=1197.159,-389.851,517,0.00!!END!752!X=1198.643,-389.631,876,0.00!!END!753!X=1200.126,-389.411,983,0.00!!END!754!X=1201.609,-389.191,850,0.00!!END!755!X=1203.092,-388.97,776,0.00!!END!756!X=1204.576,-388.749,518,0.00!!END!757!X=1206.059,-388.528,555,0.00!!END!758!X=1207.542,-388.307,487,0.00!!END!759!X=1209.025,-388.085,626,0.00!!END!760!X=1210.508,-387.864,794,0.00!!END!761!X=1211.991,-387.641,824,0.00!!END!762!X=1213.474,-387.419,1004,0.00!!END!763!X=1214.957,-387.196,1101,0.00!!END!764!X=1216.439,-386.973,1435,0.00!!END!765!X=1217.922,-386.75,1039,0.00!!END!766!X=1219.405,-386.527,765,0.00!!END!767!X=1220.888,-386.303,961,0.00!!END!768!X=1222.37,-386.079,963,0.00!!END!769!X=1223.853,-385.855,1391,0.00!!END!770!X=1225.336,-385.63,1485,0.00!!END!771!X=1226.818,-385.405,1332,0.00!!END!772!X=1228.301,-385.18,1520,0.00!!END!773!X=1229.783,-384.955,1705,0.00!!END!55INVCAM02.inp10/23/2006774!X=1231.266,-384.729,1572,0.00!!END!775!X=1232.748,-384.503,1802,0.00!!END!776!X=1234.23,-384.277,1371,0.00!!END!777!X=1235.713,-384.05,1674,0.00!!END!778!X=1237.195,-383.823,1676,0.00!!END!779!X=1238.677,-383.596,1586,0.00!!END!780!X=1240.159,-383.369,1727,0.00!!END!781!X=1241.641,-383.142,1516,0.00!!END!782!X=1243.123,-382.914,1359,0.00!!END!783!X=1244.606,-382.686,1097,0.00!!END!784!X=1246.088,-382.457,1022,0.00!!END!785!X=1247.569,-382.228,1016,0.00!!END!786!X=1249.051,-382,732,0.00!!END!787!X=1198.372,-387.805,652,0.00!!END!788!X=1199.855,-387.585,1164,0.00!!END!789!X=1201.338,-387.365,1129,0.00!!END!790!X=1202.821,-387.144,1070,0.00!!END!791!X=1204.304,-386.924,942,0.00!!END!792!X=1205.786,-386.703,668,0.00!!END!793!X=1207.269,-386.481,425,0.00!!END!794!X=1208.752,-386.26,532,0.00!!END!795!X=1210.235,-386.038,696,0.00!!END!796!X=1211.717,-385.816,673,0.00!!END!797!X=1213.2,-385.593,775,0.00!!END!798!X=1214.682,-385.371,1061,0.00!!END!799!X=1216.165,-385.148,939,0.00!!END!800!X=1217.647,-384.925,817,0.00!!END!801!X=1219.13,-384.701,763,0.00!!END!802!X=1220.612,-384.478,616,0.00!!END!803!X=1222.094,-384.254,877,0.00!!END!804!X=1223.577,-384.029,892,0.00!!END!805!X=1225.059,-383.805,910,0.00!!END!806!X=1226.541,-383.58,1134,0.00!!END!807!X=1228.023,-383.355,1358,0.00!!END!808!X=1229.505,-383.13,1512,0.00!!END!809!X=1230.988,-382.904,1674,0.00!!END!810!X=1232.47,-382.678,1806,0.00!!END!811!X=1233.952,-382.452,1678,0.00!!END!812!X=1235.434,-382.225,1725,0.00!!END!813!X=1236.916,-381.999,1256,0.00!!END!814!X=1238.397,-381.772,1160,0.00!!END!815!X=1239.879,-381.544,1382,0.00!!END!816!X=1241.361,-381.317,1289,0.00!!END!817!X=1242.843,-381.089,1584,0.00!!END!818!X=1244.325,-380.861,1317,0.00!!END!819!X=1245.806,-380.633,1170,0.00!!END!820!X=1211.444,-383.99,548,0.00!!END!821!X=1212.926,-383.768,730,0.00!!END!822!X=1214.408,-383.545,699,0.00!!END!56INVCAM02.inp10/23/2006823!X=1215.89,-383.323,749,0.00!!END!824!X=1217.372,-383.099,624,0.00!!END!825!X=1218.854,-382.876,608,0.00!!END!826!X=1220.336,-382.652,530,0.00!!END!827!X=1221.818,-382.428,797,0.00!!END!828!X=1223.3,-382.204,1103,0.00!!END!829!X=1224.782,-381.98,1110,0.00!!END!830!X=1226.264,-381.755,1130,0.00!!END!831!X=1227.746,-381.53,1499,0.00!!END!832!X=1229.228,-381.305,1742,0.00!!END!833!X=1230.71,-381.079,1769,0.00!!END!834!X=1232.191,-380.853,1639,0.00!!END!835!X=1233.673,-380.627,1342,0.00!!END!836!X=1235.155,-380.401,1247,0.00!!END!837!X=1236.636,-380.174,1168,0.00!!END!838!X=1238.118,-379.947,1012,0.00!!END!839!X=1239.599,-379.72,959,0.00!!END!840!X=1241.081,-379.492,1366,0.00!!END!841!X=1242.562,-379.265,1348,0.00!!END!842!X=1244.044,-379.037,1526,0.00!!END!843!X=1245.525,-378.808,1042,0.00!!END!844!X=1214.134,-381.72,488,0.00!!END!845!X=1215.616,-381.497,515,0.00!!END!846!X=1217.097,-381.274,491,0.00!!END!847!X=1218.579,-381.051,550,0.00!!END!848!X=1220.061,-380.827,579,0.00!!END!849!X=1221.542,-380.603,781,0.00!!END!850!X=1223.024,-380.379,900,0.00!!END!851!X=1224.506,-380.155,1059,0.00!!END!852!X=1225.987,-379.93,1123,0.00!!END!853!X=1227.469,-379.705,1307,0.00!!END!854!X=1228.95,-379.48,1166,0.00!!END!855!X=1230.432,-379.254,1302,0.00!!END!856!X=1231.913,-379.028,1672,0.00!!END!857!X=1233.394,-378.802,1533,0.00!!END!858!X=1234.876,-378.576,1429,0.00!!END!859!X=1236.357,-378.349,1457,0.00!!END!860!X=1237.838,-378.122,1391,0.00!!END!861!X=1239.319,-377.895,937,0.00!!END!862!X=1240.8,-377.668,1015,0.00!!END!863!X=1242.281,-377.44,1056,0.00!!END!864!X=1243.763,-377.212,1071,0.00!!END!865!X=1245.244,-376.984,1060,0.00!!END!866!X=1218.304,-379.225,427,0.00!!END!867!X=1219.785,-379.002,480,0.00!!END!868!X=1221.266,-378.778,488,0.00!!END!869!X=1222.748,-378.554,624,0.00!!END!870!X=1224.229,-378.33,761,0.00!!END!871!X=1225.71,-378.105,732,0.00!!END!57INVCAM02.inp10/23/2006872!X=1227.191,-377.88,881,0.00!!END!873!X=1228.673,-377.655,821,0.00!!END!874!X=1230.154,-377.429,1000,0.00!!END!875!X=1231.635,-377.204,1094,0.00!!END!876!X=1233.116,-376.978,1208,0.00!!END!877!X=1234.597,-376.751,860,0.00!!END!878!X=1236.078,-376.525,857,0.00!!END!879!X=1237.558,-376.298,1391,0.00!!END!880!X=1239.039,-376.071,1265,0.00!!END!881!X=1240.52,-375.843,1067,0.00!!END!882!X=1242.001,-375.616,921,0.00!!END!883!X=1243.482,-375.388,611,0.00!!END!884!X=1226.914,-376.055,608,0.00!!END!885!X=1229.876,-375.604,699,0.00!!END!886!X=1231.356,-375.379,785,0.00!!END!887!X=1232.837,-375.153,892,0.00!!END!888!X=1234.318,-374.927,622,0.00!!END!889!X=1235.798,-374.7,762,0.00!!END!890!X=1237.279,-374.473,1130,0.00!!END!891!X=1238.759,-374.246,1458,0.00!!END!892!X=1240.24,-374.019,1097,0.00!!END!893!X=1241.72,-373.791,823,0.00!!END!894!X=1243.201,-373.563,603,0.00!!END!895!X=1232.558,-373.328,534,0.00!!END!896!X=1234.039,-373.102,545,0.00!!END!897!X=1235.519,-372.875,582,0.00!!END!898!X=1236.999,-372.649,735,0.00!!END!899!X=1238.479,-372.422,885,0.00!!END!900!X=1239.959,-372.194,873,0.00!!END!901!X=1349.498,-350.859,468,0.00!!END!902!X=1350.236,-350.735,457,0.00!!END!903!X=1349.345,-349.949,478,0.00!!END!904!X=1350.083,-349.825,576,0.00!!END!905!X=1347.717,-349.286,550,0.00!!END!906!X=1348.455,-349.162,472,0.00!!END!907!X=1349.193,-349.039,721,0.00!!END!908!X=1349.931,-348.915,759,0.00!!END!909!X=1350.668,-348.791,600,0.00!!END!910!X=1351.406,-348.667,517,0.00!!END!911!X=1347.564,-348.376,641,0.00!!END!912!X=1348.302,-348.252,439,0.00!!END!913!X=1349.04,-348.129,607,0.00!!END!914!X=1349.778,-348.005,881,0.00!!END!915!X=1350.516,-347.881,758,0.00!!END!916!X=1347.412,-347.466,920,0.00!!END!917!X=1348.15,-347.342,665,0.00!!END!918!X=1348.887,-347.218,458,0.00!!END!919!X=1349.625,-347.095,585,0.00!!END!920!X=1350.363,-346.971,870,0.00!!END!58INVCAM02.inp10/23/2006921!X=1347.997,-346.432,826,0.00!!END!922!X=1348.735,-346.308,518,0.00!!END!923!X=1349.472,-346.185,525,0.00!!END!924!X=1350.21,-346.061,695,0.00!!END!925!X=1350.948,-345.937,892,0.00!!END!926!X=1347.845,-345.522,874,0.00!!END!927!X=1348.582,-345.398,581,0.00!!END!928!X=1349.32,-345.274,573,0.00!!END!929!X=1350.057,-345.151,664,0.00!!END!930!X=1348.43,-344.488,728,0.00!!END!931!X=1349.167,-344.364,694,0.00!!END!932!X=1349.905,-344.241,914,0.00!!END!933!X=1348.277,-343.578,756,0.00!!END!934!X=1349.014,-343.454,631,0.00!!END!935!X=1349.752,-343.331,944,0.00!!END!936!X=1348.124,-342.668,826,0.00!!END!937!X=1348.862,-342.544,624,0.00!!END!938!X=1349.599,-342.42,965,0.00!!END!939!X=1347.972,-341.758,732,0.00!!END!940!X=1348.709,-341.634,685,0.00!!END!941!X=1349.446,-341.51,889,0.00!!END!942!X=1347.819,-340.848,890,0.00!!END!943!X=1348.556,-340.724,697,0.00!!END!944!X=1349.294,-340.6,827,0.00!!END!945!X=1346.93,-340.061,1096,0.00!!END!946!X=1347.667,-339.938,749,0.00!!END!947!X=1348.404,-339.814,816,0.00!!END!948!X=1349.141,-339.69,1106,0.00!!END!949!X=1346.777,-339.151,1055,0.00!!END!950!X=1347.514,-339.027,762,0.00!!END!951!X=1348.251,-338.904,909,0.00!!END!952!X=1348.988,-338.78,1092,0.00!!END!953!X=1345.888,-338.364,941,0.00!!END!954!X=1346.625,-338.241,813,0.00!!END!955!X=1347.362,-338.117,953,0.00!!END!956!X=1348.098,-337.994,1097,0.00!!END!957!X=1348.835,-337.87,1083,0.00!!END!958!X=1345.735,-337.454,923,0.00!!END!959!X=1346.472,-337.331,924,0.00!!END!960!X=1347.209,-337.207,901,0.00!!END!961!X=1347.946,-337.084,1114,0.00!!END!962!X=1348.683,-336.96,1219,0.00!!END!963!X=1345.583,-336.544,946,0.00!!END!964!X=1346.32,-336.421,983,0.00!!END!965!X=1347.056,-336.297,1142,0.00!!END!966!X=1346.167,-335.511,1063,0.00!!END!967!X=1273.44,-416.507,1629,0.00!!END!968!X=1274.184,-416.39,1586,0.00!!END!969!X=1274.928,-416.274,1370,0.00!!END!59INVCAM02.inp10/23/2006970!X=1275.672,-416.157,1274,0.00!!END!971!X=1276.416,-416.04,1181,0.00!!END!972!X=1268.832,-416.294,1183,0.00!!END!973!X=1269.576,-416.178,1416,0.00!!END!974!X=1270.321,-416.062,1541,0.00!!END!975!X=1271.065,-415.945,1677,0.00!!END!976!X=1271.809,-415.828,1640,0.00!!END!977!X=1272.553,-415.712,1770,0.00!!END!978!X=1273.297,-415.595,1679,0.00!!END!979!X=1274.041,-415.478,1585,0.00!!END!980!X=1274.785,-415.361,1529,0.00!!END!981!X=1275.529,-415.244,1309,0.00!!END!982!X=1276.273,-415.127,1128,0.00!!END!983!X=1267.946,-415.498,1097,0.00!!END!984!X=1268.69,-415.382,1217,0.00!!END!985!X=1269.434,-415.266,1536,0.00!!END!986!X=1270.178,-415.149,1463,0.00!!END!987!X=1270.922,-415.033,1436,0.00!!END!988!X=1271.666,-414.916,1629,0.00!!END!989!X=1272.41,-414.8,1771,0.00!!END!990!X=1273.154,-414.683,1622,0.00!!END!991!X=1273.898,-414.566,1425,0.00!!END!992!X=1274.641,-414.449,1312,0.00!!END!993!X=1275.385,-414.332,1362,0.00!!END!994!X=1276.129,-414.215,1067,0.00!!END!995!X=1276.873,-414.098,1162,0.00!!END!996!X=1277.617,-413.981,1399,0.00!!END!997!X=1267.059,-414.702,1029,0.00!!END!998!X=1267.803,-414.586,1227,0.00!!END!999!X=1268.547,-414.47,1505,0.00!!END!1000!X=1269.291,-414.354,1347,0.00!!END!1001!X=1270.035,-414.237,1317,0.00!!END!1002!X=1270.779,-414.121,1536,0.00!!END!1003!X=1271.523,-414.004,1675,0.00!!END!1004!X=1272.267,-413.887,1729,0.00!!END!1005!X=1273.01,-413.771,1523,0.00!!END!1006!X=1273.754,-413.654,1544,0.00!!END!1007!X=1274.498,-413.537,1429,0.00!!END!1008!X=1275.242,-413.42,1315,0.00!!END!1009!X=1275.986,-413.303,1068,0.00!!END!1010!X=1276.73,-413.186,1066,0.00!!END!1011!X=1277.473,-413.069,1352,0.00!!END!1012!X=1266.173,-413.906,1024,0.00!!END!1013!X=1266.917,-413.79,1296,0.00!!END!1014!X=1267.661,-413.674,1404,0.00!!END!1015!X=1268.404,-413.558,1373,0.00!!END!1016!X=1269.148,-413.441,1198,0.00!!END!1017!X=1269.892,-413.325,1198,0.00!!END!1018!X=1270.636,-413.208,1419,0.00!!END!60INVCAM02.inp10/23/20061019!X=1271.38,-413.092,1571,0.00!!END!1020!X=1272.124,-412.975,1741,0.00!!END!1021!X=1272.867,-412.859,1717,0.00!!END!1022!X=1273.611,-412.742,1616,0.00!!END!1023!X=1274.355,-412.625,1569,0.00!!END!1024!X=1275.099,-412.508,1422,0.00!!END!1025!X=1275.842,-412.391,1161,0.00!!END!1026!X=1265.287,-413.11,968,0.00!!END!1027!X=1266.03,-412.994,1198,0.00!!END!1028!X=1266.774,-412.878,1362,0.00!!END!1029!X=1267.518,-412.762,1470,0.00!!END!1030!X=1268.262,-412.645,1248,0.00!!END!1031!X=1269.006,-412.529,1058,0.00!!END!1032!X=1269.749,-412.413,1170,0.00!!END!1033!X=1270.493,-412.296,1415,0.00!!END!1034!X=1271.237,-412.18,1689,0.00!!END!1035!X=1271.98,-412.063,1547,0.00!!END!1036!X=1272.724,-411.946,1550,0.00!!END!1037!X=1273.468,-411.83,1437,0.00!!END!1038!X=1274.212,-411.713,1508,0.00!!END!1039!X=1274.955,-411.596,1300,0.00!!END!1040!X=1275.699,-411.479,1176,0.00!!END!1041!X=1268.863,-411.617,1012,0.00!!END!1042!X=1269.606,-411.501,1285,0.00!!END!1043!X=1270.35,-411.384,1366,0.00!!END!1044!X=1271.094,-411.268,1566,0.00!!END!1045!X=1271.837,-411.151,1451,0.00!!END!1046!X=1272.581,-411.034,1359,0.00!!END!1047!X=1273.325,-410.918,1273,0.00!!END!1048!X=1274.068,-410.801,1274,0.00!!END!1049!X=1274.812,-410.684,1280,0.00!!END!1050!X=1275.555,-410.567,1155,0.00!!END!1051!X=1270.207,-410.472,1179,0.00!!END!1052!X=1270.951,-410.355,1348,0.00!!END!1053!X=1271.694,-410.239,1488,0.00!!END!1054!X=1270.808,-409.443,1442,0.00!!END!1055!X=1271.551,-409.327,1565,0.00!!END!1056!X=1272.295,-409.21,1505,0.00!!END!1057!X=1273.038,-409.093,1409,0.00!!END!1058!X=1273.782,-408.977,1380,0.00!!END!1059!X=1274.525,-408.86,1303,0.00!!END!1060!X=1275.268,-408.743,1104,0.00!!END!1061!X=1269.921,-408.648,1500,0.00!!END!1062!X=1271.408,-408.415,1678,0.00!!END!1063!X=1272.152,-408.298,1707,0.00!!END!1064!X=1272.895,-408.181,1515,0.00!!END!1065!X=1273.638,-408.065,1321,0.00!!END!1066!X=1274.382,-407.948,1219,0.00!!END!1067!X=1271.265,-407.502,1394,0.00!!END!61INVCAM02.inp10/23/20061068!X=1272.008,-407.386,1522,0.00!!END!1069!X=1272.752,-407.269,1411,0.00!!END!1070!X=1273.495,-407.152,1234,0.00!!END!1071!X=1271.122,-406.59,1189,0.00!!END!1072!X=1271.865,-406.474,1343,0.00!!END!1073!X=1272.609,-406.357,1265,0.00!!END!1074!X=1270.979,-405.678,1045,0.00!!END!1075!X=1271.722,-405.562,1235,0.00!!END!1076!X=1272.465,-405.445,1066,0.00!!END!-------------aDataforeachreceptoraretreatedasaseparateinputsubgroupandthereforemustendwithaninputgroupterminator.bReceptorheightabovegroundisoptional.Ifnovalueisentered,thereceptorisplacedontheground.62

# INVISTA Camden Plant B - 8 Trinity Consultants

BART Applicability Modeling Analysis 

# SAMPLE POSTUTIL INPUT FILE

STEP 1 RE-PARTITIONING

UTINVCAM02A1.INP

UTINVCAM02B1.INP

UTINVCAM02C1.INP

4-KM REFINED ANALYSIS YEAR 2002UTINVCAM02A1.inp10/23/2006INVISTACAMDEN-CombinePMSpeciesBARTREFINEDANALYSIS4KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006Update05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------POSTUTILMODELCONTROLFILE----------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames---------------------------Subgroup(0a)-------------OutputFiles------------FileDefaultFileName---------------------ListFilePOSTUTIL.LST!UTLLST=UTINVCAM02A1.lst!DataFileMODEL.DAT!UTLDAT=UTINVCAM02A1.con!InputFiles-----------Atime-varyingfileof"background"concentrationscanbeincludedwhentheammonia-limitingmethod(ALM)forsettingtheHNO3/NO3concentrationpartitionisaccomplishedin1step.ThisoptionisselectedbysettingMNITRATE=3inInputGroup1.Speciesrequiredinthe"background"concentrationfileare:SO4,NO3,HNO3andTNH3(totalNH3=NH3gaseous+NH3particulate).FileDefaultFileName---------------------BCKGFileBCKGALM.DAT*BCKGALM=BCKGALM.DAT*AnumberofCALPUFFdatafilesmaybeprocessedinthisapplication.ThefilesmayrepresentindividualCALPUFFsimulationsthatweremadeforaspecificsetofspeciesand/orsources.SpecifythetotalnumberofCALPUFFrunsyouwishtocombine,andprovidethefilenameforeachinsubgroup0b.NumberofCALPUFFdatafiles(NFILES)1UTINVCAM02A1.inp10/23/2006Default:1!NFILES=1!MeteorologicaldatafilesareneededfortheHNO3/NO3partitionoption.Threetypesofmeteorologicaldatafilescanbeused:METFM=0-CALMET.DATMETFM=1-1-DfilewithRH,TempandRhoairtimeseriesMETFM=2-2-DfileswitheitherRh,TemporRhoairineach(32_Dfilesareneeded)ThedefaultistouseCALMET.DATfiles.Default:0!METFM=0!Multiplemeteorologicaldatafilesmaybeusedinsequencetospantheprocessingperiod.Specifythenumberoftime-periodfiles(NMET)thatyouneedtouse,andprovideafilenameforeachinsubgroup0b.-NMETis0ifnometeorologicalfilesareprovided-NMETis1ifMETFM=1(multiplefilefeatureisnotavailable)-NMETis1ormoreifMETFM=0or2(multipleCALMETfilesor2DMETfiles)Numberofmeteorologicaldatafiletime-periods(NMET)Default:0!NMET=12!AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASEConvertfilenamestolowercase?Default:T!LCFILES=T!T=lowercaseF=UPPERCASE!END!-----------------------------------------------------------NOTE:file/pathnamescanbeupto70charactersinlength------------------------------------------------------------------------Subgroup(0b)-------------NMETCALMETDataFiles(METFM=0):InputFileDefaultFileName---------------------------1MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-01A.DAT!!END!2MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-01B.DAT!!END!2UTINVCAM02A1.inp10/23/20063MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-01C.DAT!!END!4MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-02A.DAT!!END!5MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-02B.DAT!!END!6MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-02C.DAT!!END!7MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-03A.DAT!!END!8MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-03B.DAT!!END!9MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-03C.DAT!!END!10MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-04A.DAT!!END!11MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-04B.DAT!!END!12MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-04C.DAT!!END!NMET1-DDataFiles(METFM=1):InputFileDefaultFileName---------------------------1MET_1D.DAT*MET1D=MET_1D.DAT**END*NMET2-DDataFilesofEachType(METFM=2):InputFileDefaultFileName---------------------------1RHUMD.DAT*M2DRHU=RELHUM.DAT**END*1TEMP.DAT*M2DTMP=TEMP.DAT**END*1RHOAIR.DAT*M2DRHO=RHOAIR.DAT**END*NFILESCALPUFFDataFiles:InputFileDefaultFileName---------------------------1CALPUFF.DAT!MODDAT=INVCAM02.con!!END!-------------Note:provideNMETlinesoftheform*UTLMET=name**END*or*MET1D=name**END*or*M2DRHU=name**END*(and)*M2DTMP=name**END*(and)*M2DRHO=name**END*andNFILESlinesoftheform*MODDAT=name**END*wherethe*shouldbereplacedwithanexclamationpoint,thespecialdelimitercharacter.3UTINVCAM02A1.inp10/23/2006--------------------------------------------------------------------------------INPUTGROUP:1--Generalruncontrolparameters--------------Startingdate:Year(ISYR)--Nodefault!ISYR=2002!Month(ISMO)--Nodefault!ISMO=1!Day(ISDY)--Nodefault!ISDY=1!Hour(ISHR)--Nodefault!ISHR=1!Numberofperiodstoprocess(NPER)--Nodefault!NPER=2880!NumberofspeciestoprocessfromCALPUFFruns(NSPECINP)--Nodefault!NSPECINP=19!Numberofspeciestowritetooutputfile(NSPECOUT)--Nodefault!NSPECOUT=19!Numberofspeciestocomputefromthosemodeled(mustbenogreaterthanNSPECOUT)(NSPECCMP)--Nodefault!NSPECCMP=0!Whenmultiplefilesareused,aspeciesnamemayappearinmorethanonefile.Dataforthisspecieswillbesummed(appropriateiftheCALPUFFrunsusedifferentsourcegroups).Ifthissummingisnotappropriate,removeduplicatespeciesfromthefile(s).Stoprunifduplicatespeciesnamesarefound?(MDUPLCT)Default:0!MDUPLCT=0!0=no(i.e.,duplicatespeciesaresummed)1=yes(i.e.,runishalted)DataforeachspeciesinaCALPUFFdatafilemayalsobescaledastheyareread.ThiscanbedonetoaltertheemissionrateofallsourcesthatweremodeledinaparticularCALPUFFapplication.ThescalingfactorforeachspeciesisenteredinSubgroup(2d),foreachfileforwhichscalingisrequested.NumberofCALPUFFdatafilesthatwillbescaled(mustbenogreaterthanNFILES)(NSCALED)Default:0!NSCALED=0!Ammonia-LimitingMethodOptiontorecomputetheHNO3/NO3concentrationpartitionpriortoperformingotheractionsiscontrolledbyMNITRATE.ThisoptionwillNOTalteranydepositionfluxescontainedintheCALPUFF4UTINVCAM02A1.inp10/23/2006file(s).Threepartitionselectionsareprovided.Thefirsttwoaretypicallyusedinsequence(POSTUTILisrunmorethanonce).Thefirstselection(MNITRATE=1)computesthepartitionfortheTOTAL(allsources)concentrationfields(SO4,NO3,HNO3;NH3),andthesecond(MNITRATE=2)usesthispartition(fromthepreviousapplicationofPOSTUTIL)tocomputethepartitionforindividualsourcegroups.Thethirdselection(MNITRATE=3)canbeusedinsteadinasinglePOSTUTILapplicationifafileofbackgroundconcentrationsisprovided(BCKGALMinInputGroup0).RequiredinformationforMNITRATE=1includes:speciesNO3,HNO3,andSO4NH3concentration(s)met.datafileforRHandTRequiredinformationforMNITRATE=2includes:speciesNO3andHNO3forasourcegroupspeciesNO3ALLandHNO3ALLforallsourcegroups,properlypartitionedRequiredinformationforMNITRATE=3includes:speciesNO3,HNO3,andSO4forasourcegroupspeciesNO3,HNO3,SO4andTNH3fromthebackgroundBCKGALMfileIfTNH3isnotinthebackgroundBCKGALMfile,monthlyTNH3concentrationsareused(BCKTNH3)TNH3=totalNH3=NH3gaseous+NH3particulateRecomputetheHNO3/NO3partitionforconcentrations?(MNITRATE)Default:0!MNITRATE=1!0=no1=yes,forallsourcescombined2=yes,forasourcegroup3=yes,ALMapplicationinonestepSOURCEOFAMMONIA:AmmoniamaybeavailableasamodeledspeciesintheCALPUFFfiles,anditmayormaynotbeappropriatetouseitforrepartitioningNO3/HNO3(inoptionMNITRATE=1orMNITRATE=3).ItsuseiscontolledbyNH3TYP.WhenNH3islistedasaprocessedspeciesinSubgroup(2a),asoneoftheNSPECINPASPECIentries,andtherightoptionischosenforNH3TYP,theNH3modeledvaluesfromtheCALPUFFconcentrationfileswillbeusedinthechemicalequilibriumcalculation.NH3TYPalsocontrolswhenmonthlybackgroundammoniavaluesareused.Bothgaseous(NH3)andtotal(TNH3=NH3gaseous+NH3particulate)ammoniacanbeprovidedmonthlyasBCKNH3/BCKTNH3.WhatistheinputsourceofAmmonia?5UTINVCAM02A1.inp10/23/2006(NH3TYP)NoDefault!NH3TYP=3!0=Nobackgroundwillbeused.ONLYNH3orTNH3fromtheconcentrationfileslistedinSubgroup(2a&2b)asaprocessedspecieswillbeused.(CannotbeusedwithMNITRATE=3)1=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a)2=NH3frombackgroundconcentrationfileBCKGALMwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a&2b)(ONLYpossibleforMNITRATE=3)3=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeusedalone.4=NH3frombackgroundconcentrationfileBCKGALMwillbeusedalone(ONLYpossibleforMNITRATE=3)|OPTION|NH3orTNH3CONC|BCKNH3orBCKTNH3|TNH3/BCKGALMorBCKTNH3||--------|------------------|-------------------|-------------------------||0|X|0|0||--------|------------------|-------------------|-------------------------||1|X|X|0||--------|------------------|-------------------|-------------------------||2|X|0|X||--------|------------------|-------------------|-------------------------||3|0|X|0||--------|------------------|-------------------|-------------------------||4|0|0|X||--------|------------------|-------------------|-------------------------|Defaultmonthly(12values)backgroundammoniaconcentration(ppb)usedforHNO3/NO3partition(needtochooseoneortheother):GaseousNH3(BCKNH3)Default:-999!BCKNH3=12*0.5!TotalTNH3(BCKTNH3)Default:-999*BCKTNH3=1.,1.,1.,1.1,1.4,1.3,1.3,1.2,4*1.*Ifasinglevalueisentered,thisisusedforall12months.Month1isJANUARY,Month12isDECEMBER.6UTINVCAM02A1.inp10/23/2006!END!-------------------------------------------------------------------------------INPUTGROUP:2--SpeciesProcessingInformation---------------------------Subgroup(2a)-------------ThefollowingNSPECINPspecieswillbeprocessed:!ASPECI=SO2!!END!!ASPECI=SO4!!END!!ASPECI=NOX!!END!!ASPECI=HNO3!!END!!ASPECI=NO3!!END!!ASPECI=POC081!!END!!ASPECI=POC056!!END!!ASPECI=PIC081!!END!!ASPECI=PIC056!!END!!ASPECI=PMC800!!END!!ASPECI=PMC425!!END!!ASPECI=PMF187!!END!!ASPECI=PMF112!!END!!ASPECI=PMF081!!END!!ASPECI=PMF056!!END!!ASPECI=EC187!!END!!ASPECI=EC112!!END!!ASPECI=EC081!!END!!ASPECI=EC056!!END!-------------Subgroup(2b)-------------ThefollowingNSPECOUTspecieswillbewritten:!ASPECO=SO2!!END!!ASPECO=SO4!!END!!ASPECO=NOX!!END!!ASPECO=HNO3!!END!!ASPECO=NO3!!END!!ASPECO=POC081!!END!!ASPECO=POC056!!END!!ASPECO=PIC081!!END!!ASPECO=PIC056!!END!7UTINVCAM02A1.inp10/23/2006!ASPECO=PMC800!!END!!ASPECO=PMC425!!END!!ASPECO=PMF187!!END!!ASPECO=PMF112!!END!!ASPECO=PMF081!!END!!ASPECO=PMF056!!END!!ASPECO=EC187!!END!!ASPECO=EC112!!END!!ASPECO=EC081!!END!!ASPECO=EC056!!END!-------------Subgroup(2c)-------------ThefollowingNSPECCMPspecieswillbecomputedbyscalingandsummingoneormoreoftheprocessedinputspecies.Identifythename(s)ofthecomputedspeciesandprovidethescalingfactorsforeachoftheNSPECINPinputspecies(NSPECCMPgroupsofNSPECINP+1lineseach):**-------------Subgroup(2d)-------------EachspeciesinNSCALEDCALPUFFdatafilesmaybescaledbeforebeingprocessed(e.g.,tochangetheemissionrateforallsourcesmodeledintherunthatproducedadatafile).Foreachfile,identifythefilenameandthenprovidethename(s)ofthescaledspeciesandthecorrespondingscalingfactors(A,Bwherex'=Ax+B).A(Default=1.0)B(Default=0.0)----------------------------*MODDAT=NOFILES.DAT**SO2=1.1,0.0**SO4=1.5,0.0**HNO3=0.8,0.0**NO3=0.1,0.0**END*8UTINVCAM02B1.inp10/23/2006INVISTACAMDEN-CombinePMSpeciesBARTREFINEDANALYSIS4KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006Update05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------POSTUTILMODELCONTROLFILE----------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames---------------------------Subgroup(0a)-------------OutputFiles------------FileDefaultFileName---------------------ListFilePOSTUTIL.LST!UTLLST=UTINVCAM02B1.lst!DataFileMODEL.DAT!UTLDAT=UTINVCAM02B1.con!InputFiles-----------Atime-varyingfileof"background"concentrationscanbeincludedwhentheammonia-limitingmethod(ALM)forsettingtheHNO3/NO3concentrationpartitionisaccomplishedin1step.ThisoptionisselectedbysettingMNITRATE=3inInputGroup1.Speciesrequiredinthe"background"concentrationfileare:SO4,NO3,HNO3andTNH3(totalNH3=NH3gaseous+NH3particulate).FileDefaultFileName---------------------BCKGFileBCKGALM.DAT*BCKGALM=BCKGALM.DAT*AnumberofCALPUFFdatafilesmaybeprocessedinthisapplication.ThefilesmayrepresentindividualCALPUFFsimulationsthatweremadeforaspecificsetofspeciesand/orsources.SpecifythetotalnumberofCALPUFFrunsyouwishtocombine,andprovidethefilenameforeachinsubgroup0b.NumberofCALPUFFdatafiles(NFILES)1UTINVCAM02B1.inp10/23/2006Default:1!NFILES=1!MeteorologicaldatafilesareneededfortheHNO3/NO3partitionoption.Threetypesofmeteorologicaldatafilescanbeused:METFM=0-CALMET.DATMETFM=1-1-DfilewithRH,TempandRhoairtimeseriesMETFM=2-2-DfileswitheitherRh,TemporRhoairineach(32_Dfilesareneeded)ThedefaultistouseCALMET.DATfiles.Default:0!METFM=0!Multiplemeteorologicaldatafilesmaybeusedinsequencetospantheprocessingperiod.Specifythenumberoftime-periodfiles(NMET)thatyouneedtouse,andprovideafilenameforeachinsubgroup0b.-NMETis0ifnometeorologicalfilesareprovided-NMETis1ifMETFM=1(multiplefilefeatureisnotavailable)-NMETis1ormoreifMETFM=0or2(multipleCALMETfilesor2DMETfiles)Numberofmeteorologicaldatafiletime-periods(NMET)Default:0!NMET=12!AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASEConvertfilenamestolowercase?Default:T!LCFILES=T!T=lowercaseF=UPPERCASE!END!-----------------------------------------------------------NOTE:file/pathnamescanbeupto70charactersinlength------------------------------------------------------------------------Subgroup(0b)-------------NMETCALMETDataFiles(METFM=0):InputFileDefaultFileName---------------------------1MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-05A.DAT!!END!2MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-05B.DAT!!END!2UTINVCAM02B1.inp10/23/20063MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-05C.DAT!!END!4MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-06A.DAT!!END!5MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-06B.DAT!!END!6MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-06C.DAT!!END!7MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-07A.DAT!!END!8MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-07B.DAT!!END!9MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-07C.DAT!!END!10MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-08A.DAT!!END!11MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-08B.DAT!!END!12MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-08C.DAT!!END!NMET1-DDataFiles(METFM=1):InputFileDefaultFileName---------------------------1MET_1D.DAT*MET1D=MET_1D.DAT**END*NMET2-DDataFilesofEachType(METFM=2):InputFileDefaultFileName---------------------------1RHUMD.DAT*M2DRHU=RELHUM.DAT**END*1TEMP.DAT*M2DTMP=TEMP.DAT**END*1RHOAIR.DAT*M2DRHO=RHOAIR.DAT**END*NFILESCALPUFFDataFiles:InputFileDefaultFileName---------------------------1CALPUFF.DAT!MODDAT=INVCAM02.con!!END!-------------Note:provideNMETlinesoftheform*UTLMET=name**END*or*MET1D=name**END*or*M2DRHU=name**END*(and)*M2DTMP=name**END*(and)*M2DRHO=name**END*andNFILESlinesoftheform*MODDAT=name**END*wherethe*shouldbereplacedwithanexclamationpoint,thespecialdelimitercharacter.3UTINVCAM02B1.inp10/23/2006--------------------------------------------------------------------------------INPUTGROUP:1--Generalruncontrolparameters--------------Startingdate:Year(ISYR)--Nodefault!ISYR=2002!Month(ISMO)--Nodefault!ISMO=5!Day(ISDY)--Nodefault!ISDY=1!Hour(ISHR)--Nodefault!ISHR=1!Numberofperiodstoprocess(NPER)--Nodefault!NPER=2952!NumberofspeciestoprocessfromCALPUFFruns(NSPECINP)--Nodefault!NSPECINP=19!Numberofspeciestowritetooutputfile(NSPECOUT)--Nodefault!NSPECOUT=19!Numberofspeciestocomputefromthosemodeled(mustbenogreaterthanNSPECOUT)(NSPECCMP)--Nodefault!NSPECCMP=0!Whenmultiplefilesareused,aspeciesnamemayappearinmorethanonefile.Dataforthisspecieswillbesummed(appropriateiftheCALPUFFrunsusedifferentsourcegroups).Ifthissummingisnotappropriate,removeduplicatespeciesfromthefile(s).Stoprunifduplicatespeciesnamesarefound?(MDUPLCT)Default:0!MDUPLCT=0!0=no(i.e.,duplicatespeciesaresummed)1=yes(i.e.,runishalted)DataforeachspeciesinaCALPUFFdatafilemayalsobescaledastheyareread.ThiscanbedonetoaltertheemissionrateofallsourcesthatweremodeledinaparticularCALPUFFapplication.ThescalingfactorforeachspeciesisenteredinSubgroup(2d),foreachfileforwhichscalingisrequested.NumberofCALPUFFdatafilesthatwillbescaled(mustbenogreaterthanNFILES)(NSCALED)Default:0!NSCALED=0!Ammonia-LimitingMethodOptiontorecomputetheHNO3/NO3concentrationpartitionpriortoperformingotheractionsiscontrolledbyMNITRATE.ThisoptionwillNOTalteranydepositionfluxescontainedintheCALPUFF4UTINVCAM02B1.inp10/23/2006file(s).Threepartitionselectionsareprovided.Thefirsttwoaretypicallyusedinsequence(POSTUTILisrunmorethanonce).Thefirstselection(MNITRATE=1)computesthepartitionfortheTOTAL(allsources)concentrationfields(SO4,NO3,HNO3;NH3),andthesecond(MNITRATE=2)usesthispartition(fromthepreviousapplicationofPOSTUTIL)tocomputethepartitionforindividualsourcegroups.Thethirdselection(MNITRATE=3)canbeusedinsteadinasinglePOSTUTILapplicationifafileofbackgroundconcentrationsisprovided(BCKGALMinInputGroup0).RequiredinformationforMNITRATE=1includes:speciesNO3,HNO3,andSO4NH3concentration(s)met.datafileforRHandTRequiredinformationforMNITRATE=2includes:speciesNO3andHNO3forasourcegroupspeciesNO3ALLandHNO3ALLforallsourcegroups,properlypartitionedRequiredinformationforMNITRATE=3includes:speciesNO3,HNO3,andSO4forasourcegroupspeciesNO3,HNO3,SO4andTNH3fromthebackgroundBCKGALMfileIfTNH3isnotinthebackgroundBCKGALMfile,monthlyTNH3concentrationsareused(BCKTNH3)TNH3=totalNH3=NH3gaseous+NH3particulateRecomputetheHNO3/NO3partitionforconcentrations?(MNITRATE)Default:0!MNITRATE=1!0=no1=yes,forallsourcescombined2=yes,forasourcegroup3=yes,ALMapplicationinonestepSOURCEOFAMMONIA:AmmoniamaybeavailableasamodeledspeciesintheCALPUFFfiles,anditmayormaynotbeappropriatetouseitforrepartitioningNO3/HNO3(inoptionMNITRATE=1orMNITRATE=3).ItsuseiscontolledbyNH3TYP.WhenNH3islistedasaprocessedspeciesinSubgroup(2a),asoneoftheNSPECINPASPECIentries,andtherightoptionischosenforNH3TYP,theNH3modeledvaluesfromtheCALPUFFconcentrationfileswillbeusedinthechemicalequilibriumcalculation.NH3TYPalsocontrolswhenmonthlybackgroundammoniavaluesareused.Bothgaseous(NH3)andtotal(TNH3=NH3gaseous+NH3particulate)ammoniacanbeprovidedmonthlyasBCKNH3/BCKTNH3.WhatistheinputsourceofAmmonia?5UTINVCAM02B1.inp10/23/2006(NH3TYP)NoDefault!NH3TYP=3!0=Nobackgroundwillbeused.ONLYNH3orTNH3fromtheconcentrationfileslistedinSubgroup(2a&2b)asaprocessedspecieswillbeused.(CannotbeusedwithMNITRATE=3)1=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a)2=NH3frombackgroundconcentrationfileBCKGALMwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a&2b)(ONLYpossibleforMNITRATE=3)3=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeusedalone.4=NH3frombackgroundconcentrationfileBCKGALMwillbeusedalone(ONLYpossibleforMNITRATE=3)|OPTION|NH3orTNH3CONC|BCKNH3orBCKTNH3|TNH3/BCKGALMorBCKTNH3||--------|------------------|-------------------|-------------------------||0|X|0|0||--------|------------------|-------------------|-------------------------||1|X|X|0||--------|------------------|-------------------|-------------------------||2|X|0|X||--------|------------------|-------------------|-------------------------||3|0|X|0||--------|------------------|-------------------|-------------------------||4|0|0|X||--------|------------------|-------------------|-------------------------|Defaultmonthly(12values)backgroundammoniaconcentration(ppb)usedforHNO3/NO3partition(needtochooseoneortheother):GaseousNH3(BCKNH3)Default:-999!BCKNH3=12*0.5!TotalTNH3(BCKTNH3)Default:-999*BCKTNH3=1.,1.,1.,1.1,1.4,1.3,1.3,1.2,4*1.*Ifasinglevalueisentered,thisisusedforall12months.Month1isJANUARY,Month12isDECEMBER.6UTINVCAM02B1.inp10/23/2006!END!-------------------------------------------------------------------------------INPUTGROUP:2--SpeciesProcessingInformation---------------------------Subgroup(2a)-------------ThefollowingNSPECINPspecieswillbeprocessed:!ASPECI=SO2!!END!!ASPECI=SO4!!END!!ASPECI=NOX!!END!!ASPECI=HNO3!!END!!ASPECI=NO3!!END!!ASPECI=POC081!!END!!ASPECI=POC056!!END!!ASPECI=PIC081!!END!!ASPECI=PIC056!!END!!ASPECI=PMC800!!END!!ASPECI=PMC425!!END!!ASPECI=PMF187!!END!!ASPECI=PMF112!!END!!ASPECI=PMF081!!END!!ASPECI=PMF056!!END!!ASPECI=EC187!!END!!ASPECI=EC112!!END!!ASPECI=EC081!!END!!ASPECI=EC056!!END!-------------Subgroup(2b)-------------ThefollowingNSPECOUTspecieswillbewritten:!ASPECO=SO2!!END!!ASPECO=SO4!!END!!ASPECO=NOX!!END!!ASPECO=HNO3!!END!!ASPECO=NO3!!END!!ASPECO=POC081!!END!!ASPECO=POC056!!END!!ASPECO=PIC081!!END!!ASPECO=PIC056!!END!7UTINVCAM02B1.inp10/23/2006!ASPECO=PMC800!!END!!ASPECO=PMC425!!END!!ASPECO=PMF187!!END!!ASPECO=PMF112!!END!!ASPECO=PMF081!!END!!ASPECO=PMF056!!END!!ASPECO=EC187!!END!!ASPECO=EC112!!END!!ASPECO=EC081!!END!!ASPECO=EC056!!END!-------------Subgroup(2c)-------------ThefollowingNSPECCMPspecieswillbecomputedbyscalingandsummingoneormoreoftheprocessedinputspecies.Identifythename(s)ofthecomputedspeciesandprovidethescalingfactorsforeachoftheNSPECINPinputspecies(NSPECCMPgroupsofNSPECINP+1lineseach):**-------------Subgroup(2d)-------------EachspeciesinNSCALEDCALPUFFdatafilesmaybescaledbeforebeingprocessed(e.g.,tochangetheemissionrateforallsourcesmodeledintherunthatproducedadatafile).Foreachfile,identifythefilenameandthenprovidethename(s)ofthescaledspeciesandthecorrespondingscalingfactors(A,Bwherex'=Ax+B).A(Default=1.0)B(Default=0.0)----------------------------*MODDAT=NOFILES.DAT**SO2=1.1,0.0**SO4=1.5,0.0**HNO3=0.8,0.0**NO3=0.1,0.0**END*8UTINVCAM02C1.inp10/23/2006INVISTACAMDEN-CombinePMSpeciesBARTREFINEDANALYSIS4KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006Update05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------POSTUTILMODELCONTROLFILE----------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames---------------------------Subgroup(0a)-------------OutputFiles------------FileDefaultFileName---------------------ListFilePOSTUTIL.LST!UTLLST=UTINVCAM02C1.lst!DataFileMODEL.DAT!UTLDAT=UTINVCAM02C1.con!InputFiles-----------Atime-varyingfileof"background"concentrationscanbeincludedwhentheammonia-limitingmethod(ALM)forsettingtheHNO3/NO3concentrationpartitionisaccomplishedin1step.ThisoptionisselectedbysettingMNITRATE=3inInputGroup1.Speciesrequiredinthe"background"concentrationfileare:SO4,NO3,HNO3andTNH3(totalNH3=NH3gaseous+NH3particulate).FileDefaultFileName---------------------BCKGFileBCKGALM.DAT*BCKGALM=BCKGALM.DAT*AnumberofCALPUFFdatafilesmaybeprocessedinthisapplication.ThefilesmayrepresentindividualCALPUFFsimulationsthatweremadeforaspecificsetofspeciesand/orsources.SpecifythetotalnumberofCALPUFFrunsyouwishtocombine,andprovidethefilenameforeachinsubgroup0b.NumberofCALPUFFdatafiles(NFILES)1UTINVCAM02C1.inp10/23/2006Default:1!NFILES=1!MeteorologicaldatafilesareneededfortheHNO3/NO3partitionoption.Threetypesofmeteorologicaldatafilescanbeused:METFM=0-CALMET.DATMETFM=1-1-DfilewithRH,TempandRhoairtimeseriesMETFM=2-2-DfileswitheitherRh,TemporRhoairineach(32_Dfilesareneeded)ThedefaultistouseCALMET.DATfiles.Default:0!METFM=0!Multiplemeteorologicaldatafilesmaybeusedinsequencetospantheprocessingperiod.Specifythenumberoftime-periodfiles(NMET)thatyouneedtouse,andprovideafilenameforeachinsubgroup0b.-NMETis0ifnometeorologicalfilesareprovided-NMETis1ifMETFM=1(multiplefilefeatureisnotavailable)-NMETis1ormoreifMETFM=0or2(multipleCALMETfilesor2DMETfiles)Numberofmeteorologicaldatafiletime-periods(NMET)Default:0!NMET=12!AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASEConvertfilenamestolowercase?Default:T!LCFILES=T!T=lowercaseF=UPPERCASE!END!-----------------------------------------------------------NOTE:file/pathnamescanbeupto70charactersinlength------------------------------------------------------------------------Subgroup(0b)-------------NMETCALMETDataFiles(METFM=0):InputFileDefaultFileName---------------------------1MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-09A.DAT!!END!2MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-09B.DAT!!END!2UTINVCAM02C1.inp10/23/20063MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-09C.DAT!!END!4MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-10A.DAT!!END!5MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-10B.DAT!!END!6MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-10C.DAT!!END!7MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-11A.DAT!!END!8MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-11B.DAT!!END!9MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-11C.DAT!!END!10MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-12A.DAT!!END!11MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-12B.DAT!!END!12MET.DAT!UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-12C.DAT!!END!NMET1-DDataFiles(METFM=1):InputFileDefaultFileName---------------------------1MET_1D.DAT*MET1D=MET_1D.DAT**END*NMET2-DDataFilesofEachType(METFM=2):InputFileDefaultFileName---------------------------1RHUMD.DAT*M2DRHU=RELHUM.DAT**END*1TEMP.DAT*M2DTMP=TEMP.DAT**END*1RHOAIR.DAT*M2DRHO=RHOAIR.DAT**END*NFILESCALPUFFDataFiles:InputFileDefaultFileName---------------------------1CALPUFF.DAT!MODDAT=INVCAM02.con!!END!-------------Note:provideNMETlinesoftheform*UTLMET=name**END*or*MET1D=name**END*or*M2DRHU=name**END*(and)*M2DTMP=name**END*(and)*M2DRHO=name**END*andNFILESlinesoftheform*MODDAT=name**END*wherethe*shouldbereplacedwithanexclamationpoint,thespecialdelimitercharacter.3UTINVCAM02C1.inp10/23/2006--------------------------------------------------------------------------------INPUTGROUP:1--Generalruncontrolparameters--------------Startingdate:Year(ISYR)--Nodefault!ISYR=2002!Month(ISMO)--Nodefault!ISMO=9!Day(ISDY)--Nodefault!ISDY=1!Hour(ISHR)--Nodefault!ISHR=1!Numberofperiodstoprocess(NPER)--Nodefault!NPER=2928!NumberofspeciestoprocessfromCALPUFFruns(NSPECINP)--Nodefault!NSPECINP=19!Numberofspeciestowritetooutputfile(NSPECOUT)--Nodefault!NSPECOUT=19!Numberofspeciestocomputefromthosemodeled(mustbenogreaterthanNSPECOUT)(NSPECCMP)--Nodefault!NSPECCMP=0!Whenmultiplefilesareused,aspeciesnamemayappearinmorethanonefile.Dataforthisspecieswillbesummed(appropriateiftheCALPUFFrunsusedifferentsourcegroups).Ifthissummingisnotappropriate,removeduplicatespeciesfromthefile(s).Stoprunifduplicatespeciesnamesarefound?(MDUPLCT)Default:0!MDUPLCT=0!0=no(i.e.,duplicatespeciesaresummed)1=yes(i.e.,runishalted)DataforeachspeciesinaCALPUFFdatafilemayalsobescaledastheyareread.ThiscanbedonetoaltertheemissionrateofallsourcesthatweremodeledinaparticularCALPUFFapplication.ThescalingfactorforeachspeciesisenteredinSubgroup(2d),foreachfileforwhichscalingisrequested.NumberofCALPUFFdatafilesthatwillbescaled(mustbenogreaterthanNFILES)(NSCALED)Default:0!NSCALED=0!Ammonia-LimitingMethodOptiontorecomputetheHNO3/NO3concentrationpartitionpriortoperformingotheractionsiscontrolledbyMNITRATE.ThisoptionwillNOTalteranydepositionfluxescontainedintheCALPUFF4UTINVCAM02C1.inp10/23/2006file(s).Threepartitionselectionsareprovided.Thefirsttwoaretypicallyusedinsequence(POSTUTILisrunmorethanonce).Thefirstselection(MNITRATE=1)computesthepartitionfortheTOTAL(allsources)concentrationfields(SO4,NO3,HNO3;NH3),andthesecond(MNITRATE=2)usesthispartition(fromthepreviousapplicationofPOSTUTIL)tocomputethepartitionforindividualsourcegroups.Thethirdselection(MNITRATE=3)canbeusedinsteadinasinglePOSTUTILapplicationifafileofbackgroundconcentrationsisprovided(BCKGALMinInputGroup0).RequiredinformationforMNITRATE=1includes:speciesNO3,HNO3,andSO4NH3concentration(s)met.datafileforRHandTRequiredinformationforMNITRATE=2includes:speciesNO3andHNO3forasourcegroupspeciesNO3ALLandHNO3ALLforallsourcegroups,properlypartitionedRequiredinformationforMNITRATE=3includes:speciesNO3,HNO3,andSO4forasourcegroupspeciesNO3,HNO3,SO4andTNH3fromthebackgroundBCKGALMfileIfTNH3isnotinthebackgroundBCKGALMfile,monthlyTNH3concentrationsareused(BCKTNH3)TNH3=totalNH3=NH3gaseous+NH3particulateRecomputetheHNO3/NO3partitionforconcentrations?(MNITRATE)Default:0!MNITRATE=1!0=no1=yes,forallsourcescombined2=yes,forasourcegroup3=yes,ALMapplicationinonestepSOURCEOFAMMONIA:AmmoniamaybeavailableasamodeledspeciesintheCALPUFFfiles,anditmayormaynotbeappropriatetouseitforrepartitioningNO3/HNO3(inoptionMNITRATE=1orMNITRATE=3).ItsuseiscontolledbyNH3TYP.WhenNH3islistedasaprocessedspeciesinSubgroup(2a),asoneoftheNSPECINPASPECIentries,andtherightoptionischosenforNH3TYP,theNH3modeledvaluesfromtheCALPUFFconcentrationfileswillbeusedinthechemicalequilibriumcalculation.NH3TYPalsocontrolswhenmonthlybackgroundammoniavaluesareused.Bothgaseous(NH3)andtotal(TNH3=NH3gaseous+NH3particulate)ammoniacanbeprovidedmonthlyasBCKNH3/BCKTNH3.WhatistheinputsourceofAmmonia?5UTINVCAM02C1.inp10/23/2006(NH3TYP)NoDefault!NH3TYP=3!0=Nobackgroundwillbeused.ONLYNH3orTNH3fromtheconcentrationfileslistedinSubgroup(2a&2b)asaprocessedspecieswillbeused.(CannotbeusedwithMNITRATE=3)1=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a)2=NH3frombackgroundconcentrationfileBCKGALMwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a&2b)(ONLYpossibleforMNITRATE=3)3=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeusedalone.4=NH3frombackgroundconcentrationfileBCKGALMwillbeusedalone(ONLYpossibleforMNITRATE=3)|OPTION|NH3orTNH3CONC|BCKNH3orBCKTNH3|TNH3/BCKGALMorBCKTNH3||--------|------------------|-------------------|-------------------------||0|X|0|0||--------|------------------|-------------------|-------------------------||1|X|X|0||--------|------------------|-------------------|-------------------------||2|X|0|X||--------|------------------|-------------------|-------------------------||3|0|X|0||--------|------------------|-------------------|-------------------------||4|0|0|X||--------|------------------|-------------------|-------------------------|Defaultmonthly(12values)backgroundammoniaconcentration(ppb)usedforHNO3/NO3partition(needtochooseoneortheother):GaseousNH3(BCKNH3)Default:-999!BCKNH3=12*0.5!TotalTNH3(BCKTNH3)Default:-999*BCKTNH3=1.,1.,1.,1.1,1.4,1.3,1.3,1.2,4*1.*Ifasinglevalueisentered,thisisusedforall12months.Month1isJANUARY,Month12isDECEMBER.6UTINVCAM02C1.inp10/23/2006!END!-------------------------------------------------------------------------------INPUTGROUP:2--SpeciesProcessingInformation---------------------------Subgroup(2a)-------------ThefollowingNSPECINPspecieswillbeprocessed:!ASPECI=SO2!!END!!ASPECI=SO4!!END!!ASPECI=NOX!!END!!ASPECI=HNO3!!END!!ASPECI=NO3!!END!!ASPECI=POC081!!END!!ASPECI=POC056!!END!!ASPECI=PIC081!!END!!ASPECI=PIC056!!END!!ASPECI=PMC800!!END!!ASPECI=PMC425!!END!!ASPECI=PMF187!!END!!ASPECI=PMF112!!END!!ASPECI=PMF081!!END!!ASPECI=PMF056!!END!!ASPECI=EC187!!END!!ASPECI=EC112!!END!!ASPECI=EC081!!END!!ASPECI=EC056!!END!-------------Subgroup(2b)-------------ThefollowingNSPECOUTspecieswillbewritten:!ASPECO=SO2!!END!!ASPECO=SO4!!END!!ASPECO=NOX!!END!!ASPECO=HNO3!!END!!ASPECO=NO3!!END!!ASPECO=POC081!!END!!ASPECO=POC056!!END!!ASPECO=PIC081!!END!!ASPECO=PIC056!!END!7UTINVCAM02C1.inp10/23/2006!ASPECO=PMC800!!END!!ASPECO=PMC425!!END!!ASPECO=PMF187!!END!!ASPECO=PMF112!!END!!ASPECO=PMF081!!END!!ASPECO=PMF056!!END!!ASPECO=EC187!!END!!ASPECO=EC112!!END!!ASPECO=EC081!!END!!ASPECO=EC056!!END!-------------Subgroup(2c)-------------ThefollowingNSPECCMPspecieswillbecomputedbyscalingandsummingoneormoreoftheprocessedinputspecies.Identifythename(s)ofthecomputedspeciesandprovidethescalingfactorsforeachoftheNSPECINPinputspecies(NSPECCMPgroupsofNSPECINP+1lineseach):**-------------Subgroup(2d)-------------EachspeciesinNSCALEDCALPUFFdatafilesmaybescaledbeforebeingprocessed(e.g.,tochangetheemissionrateforallsourcesmodeledintherunthatproducedadatafile).Foreachfile,identifythefilenameandthenprovidethename(s)ofthescaledspeciesandthecorrespondingscalingfactors(A,Bwherex'=Ax+B).A(Default=1.0)B(Default=0.0)----------------------------*MODDAT=NOFILES.DAT**SO2=1.1,0.0**SO4=1.5,0.0**HNO3=0.8,0.0**NO3=0.1,0.0**END*8

# INVISTA Camden Plant B - 9 Trinity Consultants

BART Applicability Modeling Analysis 

# SAMPLE POSTUTIL INPUT FILE

STEP 2 POSTUTIL

UTINVCAM02.INP

4-KM REFINED ANALYSIS YEAR 2002UTINVCAM02.inp10/23/2006INVISTACAMDEN-CombinePMSpeciesBARTREFINEDANALYSIS4KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006Update05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------POSTUTILMODELCONTROLFILE----------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames---------------------------Subgroup(0a)-------------OutputFiles------------FileDefaultFileName---------------------ListFilePOSTUTIL.LST!UTLLST=UTINVCAM02ALM.LST!DataFileMODEL.DAT!UTLDAT=UTINVCAM02ALM.CON!InputFiles-----------Atime-varyingfileof"background"concentrationscanbeincludedwhentheammonia-limitingmethod(ALM)forsettingtheHNO3/NO3concentrationpartitionisaccomplishedin1step.ThisoptionisselectedbysettingMNITRATE=3inInputGroup1.Speciesrequiredinthe"background"concentrationfileare:SO4,NO3,HNO3andTNH3(totalNH3=NH3gaseous+NH3particulate).FileDefaultFileName---------------------BCKGFileBCKGALM.DAT*BCKGALM=BCKGALM.DAT*AnumberofCALPUFFdatafilesmaybeprocessedinthisapplication.ThefilesmayrepresentindividualCALPUFFsimulationsthatweremadeforaspecificsetofspeciesand/orsources.SpecifythetotalnumberofCALPUFFrunsyouwishtocombine,andprovidethefilenameforeachinsubgroup0b.NumberofCALPUFFdatafiles(NFILES)1UTINVCAM02.inp10/23/2006Default:1!NFILES=1!MeteorologicaldatafilesareneededfortheHNO3/NO3partitionoption.Threetypesofmeteorologicaldatafilescanbeused:METFM=0-CALMET.DATMETFM=1-1-DfilewithRH,TempandRhoairtimeseriesMETFM=2-2-DfileswitheitherRh,TemporRhoairineach(32_Dfilesareneeded)ThedefaultistouseCALMET.DATfiles.Default:0!METFM=0!Multiplemeteorologicaldatafilesmaybeusedinsequencetospantheprocessingperiod.Specifythenumberoftime-periodfiles(NMET)thatyouneedtouse,andprovideafilenameforeachinsubgroup0b.-NMETis0ifnometeorologicalfilesareprovided-NMETis1ifMETFM=1(multiplefilefeatureisnotavailable)-NMETis1ormoreifMETFM=0or2(multipleCALMETfilesor2DMETfiles)Numberofmeteorologicaldatafiletime-periods(NMET)Default:0!NMET=0!AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASEConvertfilenamestolowercase?Default:T!LCFILES=T!T=lowercaseF=UPPERCASE!END!-----------------------------------------------------------NOTE:file/pathnamescanbeupto70charactersinlength------------------------------------------------------------------------Subgroup(0b)-------------NMETCALMETDataFiles(METFM=0):InputFileDefaultFileName---------------------------1MET.DAT*UTLMET=CALMET.DAT*2UTINVCAM02.inp10/23/2006NMET1-DDataFiles(METFM=1):InputFileDefaultFileName---------------------------1MET_1D.DAT*MET1D=MET_1D.DAT**END*NMET2-DDataFilesofEachType(METFM=2):InputFileDefaultFileName---------------------------1RHUMD.DAT*M2DRHU=RELHUM.DAT**END*1TEMP.DAT*M2DTMP=TEMP.DAT**END*1RHOAIR.DAT*M2DRHO=RHOAIR.DAT**END*NFILESCALPUFFDataFiles:InputFileDefaultFileName---------------------------1CALPUFF.DAT!MODDAT=UTINVCAM02S1.con!!END!-------------Note:provideNMETlinesoftheform*UTLMET=name**END*or*MET1D=name**END*or*M2DRHU=name**END*(and)*M2DTMP=name**END*(and)*M2DRHO=name**END*andNFILESlinesoftheform*MODDAT=name**END*wherethe*shouldbereplacedwithanexclamationpoint,thespecialdelimitercharacter.--------------------------------------------------------------------------------INPUTGROUP:1--Generalruncontrolparameters--------------Startingdate:Year(ISYR)--Nodefault!ISYR=2002!Month(ISMO)--Nodefault!ISMO=1!Day(ISDY)--Nodefault!ISDY=1!Hour(ISHR)--Nodefault!ISHR=1!3UTINVCAM02.inp10/23/2006Numberofperiodstoprocess(NPER)--Nodefault!NPER=8760!NumberofspeciestoprocessfromCALPUFFruns(NSPECINP)--Nodefault!NSPECINP=19!Numberofspeciestowritetooutputfile(NSPECOUT)--Nodefault!NSPECOUT=9!Numberofspeciestocomputefromthosemodeled(mustbenogreaterthanNSPECOUT)(NSPECCMP)--Nodefault!NSPECCMP=4!Whenmultiplefilesareused,aspeciesnamemayappearinmorethanonefile.Dataforthisspecieswillbesummed(appropriateiftheCALPUFFrunsusedifferentsourcegroups).Ifthissummingisnotappropriate,removeduplicatespeciesfromthefile(s).Stoprunifduplicatespeciesnamesarefound?(MDUPLCT)Default:0!MDUPLCT=0!0=no(i.e.,duplicatespeciesaresummed)1=yes(i.e.,runishalted)DataforeachspeciesinaCALPUFFdatafilemayalsobescaledastheyareread.ThiscanbedonetoaltertheemissionrateofallsourcesthatweremodeledinaparticularCALPUFFapplication.ThescalingfactorforeachspeciesisenteredinSubgroup(2d),foreachfileforwhichscalingisrequested.NumberofCALPUFFdatafilesthatwillbescaled(mustbenogreaterthanNFILES)(NSCALED)Default:0!NSCALED=0!Ammonia-LimitingMethodOptiontorecomputetheHNO3/NO3concentrationpartitionpriortoperformingotheractionsiscontrolledbyMNITRATE.ThisoptionwillNOTalteranydepositionfluxescontainedintheCALPUFFfile(s).Threepartitionselectionsareprovided.Thefirsttwoaretypicallyusedinsequence(POSTUTILisrunmorethanonce).Thefirstselection(MNITRATE=1)computesthepartitionfortheTOTAL(allsources)concentrationfields(SO4,NO3,HNO3;NH3),andthesecond(MNITRATE=2)usesthispartition(fromthepreviousapplicationofPOSTUTIL)tocomputethepartitionforindividualsourcegroups.Thethirdselection(MNITRATE=3)canbeusedinsteadinasinglePOSTUTILapplicationifafileofbackgroundconcentrationsisprovided(BCKGALMinInputGroup0).RequiredinformationforMNITRATE=1includes:speciesNO3,HNO3,andSO44UTINVCAM02.inp10/23/2006NH3concentration(s)met.datafileforRHandTRequiredinformationforMNITRATE=2includes:speciesNO3andHNO3forasourcegroupspeciesNO3ALLandHNO3ALLforallsourcegroups,properlypartitionedRequiredinformationforMNITRATE=3includes:speciesNO3,HNO3,andSO4forasourcegroupspeciesNO3,HNO3,SO4andTNH3fromthebackgroundBCKGALMfileIfTNH3isnotinthebackgroundBCKGALMfile,monthlyTNH3concentrationsareused(BCKTNH3)TNH3=totalNH3=NH3gaseous+NH3particulateRecomputetheHNO3/NO3partitionforconcentrations?(MNITRATE)Default:0!MNITRATE=0!0=no1=yes,forallsourcescombined2=yes,forasourcegroup3=yes,ALMapplicationinonestepSOURCEOFAMMONIA:AmmoniamaybeavailableasamodeledspeciesintheCALPUFFfiles,anditmayormaynotbeappropriatetouseitforrepartitioningNO3/HNO3(inoptionMNITRATE=1orMNITRATE=3).ItsuseiscontolledbyNH3TYP.WhenNH3islistedasaprocessedspeciesinSubgroup(2a),asoneoftheNSPECINPASPECIentries,andtherightoptionischosenforNH3TYP,theNH3modeledvaluesfromtheCALPUFFconcentrationfileswillbeusedinthechemicalequilibriumcalculation.NH3TYPalsocontrolswhenmonthlybackgroundammoniavaluesareused.Bothgaseous(NH3)andtotal(TNH3=NH3gaseous+NH3particulate)ammoniacanbeprovidedmonthlyasBCKNH3/BCKTNH3.WhatistheinputsourceofAmmonia?(NH3TYP)NoDefault!NH3TYP=3!0=Nobackgroundwillbeused.ONLYNH3orTNH3fromtheconcentrationfileslistedinSubgroup(2a&2b)asaprocessedspecieswillbeused.(CannotbeusedwithMNITRATE=3)1=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a)5UTINVCAM02.inp10/23/20062=NH3frombackgroundconcentrationfileBCKGALMwillbeaddedtoNH3fromconcentrationfileslistedinSubgroup(2a&2b)(ONLYpossibleforMNITRATE=3)3=NH3Monthlyaveragedbackground(BCKNH3)listedbelowwillbeusedalone.4=NH3frombackgroundconcentrationfileBCKGALMwillbeusedalone(ONLYpossibleforMNITRATE=3)|OPTION|NH3orTNH3CONC|BCKNH3orBCKTNH3|TNH3/BCKGALMorBCKTNH3||--------|------------------|-------------------|-------------------------||0|X|0|0||--------|------------------|-------------------|-------------------------||1|X|X|0||--------|------------------|-------------------|-------------------------||2|X|0|X||--------|------------------|-------------------|-------------------------||3|0|X|0||--------|------------------|-------------------|-------------------------||4|0|0|X||--------|------------------|-------------------|-------------------------|Defaultmonthly(12values)backgroundammoniaconcentration(ppb)usedforHNO3/NO3partition(needtochooseoneortheother):GaseousNH3(BCKNH3)Default:-999!BCKNH3=12*0.5!TotalTNH3(BCKTNH3)Default:-999*BCKTNH3=1.,1.,1.,1.1,1.4,1.3,1.3,1.2,4*1.*Ifasinglevalueisentered,thisisusedforall12months.Month1isJANUARY,Month12isDECEMBER.!END!-------------------------------------------------------------------------------INPUTGROUP:2--SpeciesProcessingInformation---------------------------Subgroup(2a)-------------ThefollowingNSPECINPspecieswillbeprocessed:6UTINVCAM02.inp10/23/2006!ASPECI=SO2!!END!!ASPECI=SO4!!END!!ASPECI=NOX!!END!!ASPECI=HNO3!!END!!ASPECI=NO3!!END!!ASPECI=POC081!!END!!ASPECI=POC056!!END!!ASPECI=PIC081!!END!!ASPECI=PIC056!!END!!ASPECI=PMC800!!END!!ASPECI=PMC425!!END!!ASPECI=PMF187!!END!!ASPECI=PMF112!!END!!ASPECI=PMF081!!END!!ASPECI=PMF056!!END!!ASPECI=EC187!!END!!ASPECI=EC112!!END!!ASPECI=EC081!!END!!ASPECI=EC056!!END!-------------Subgroup(2b)-------------ThefollowingNSPECOUTspecieswillbewritten:!ASPECO=SO2!!END!!ASPECO=SO4!!END!!ASPECO=NOX!!END!!ASPECO=HNO3!!END!!ASPECO=NO3!!END!!ASPECO=EC!!END!!ASPECO=SOIL!!END!!ASPECO=SOA!!END!!ASPECO=PMC!!END!-------------Subgroup(2c)-------------ThefollowingNSPECCMPspecieswillbecomputedbyscalingandsummingoneormoreoftheprocessedinputspecies.Identifythename(s)ofthecomputedspeciesandprovidethescalingfactorsforeachoftheNSPECINPinputspecies(NSPECCMPgroupsofNSPECINP+1lineseach):!CSPECCMP=EC!7UTINVCAM02.inp10/23/2006!EC187=1.0000!!EC112=1.0000!!EC081=1.0000!!EC056=1.0000!!END!!CSPECCMP=SOIL!!PMF187=1.0000!!PMF112=1.0000!!PMF081=1.0000!!PMF056=1.0000!!PIC081=1.0000!!PIC056=1.0000!!END!!CSPECCMP=SOA!!POC081=1.0000!!POC056=1.0000!!END!!CSPECCMP=PMC!!PMC800=1.0000!!PMC425=1.0000!!END!-------------Subgroup(2d)-------------EachspeciesinNSCALEDCALPUFFdatafilesmaybescaledbeforebeingprocessed(e.g.,tochangetheemissionrateforallsourcesmodeledintherunthatproducedadatafile).Foreachfile,identifythefilenameandthenprovidethename(s)ofthescaledspeciesandthecorrespondingscalingfactors(A,Bwherex'=Ax+B).A(Default=1.0)B(Default=0.0)----------------------------8

# INVISTA Camden Plant B - 10 Trinity Consultants

BART Applicability Modeling Analysis 

# SAMPLE CALPOST INPUT FILE

VANINVCAM02CR.INP

4-KM REFINED ANALYSIS YEAR 2002

CAPE ROMAIN ANNUAL AVE RAGE NATURAL BACKGROUNDVANINVCAM02CR.inp10/23/2006INVISTACAMDEN-VisibilitywithAnnualBackgroundCAPEROMAINBARTREFINEDANALYSIS4KMRUN2002SPECIATEDPMMJZ/FAH04.17.2006Update05.31.2006w/DHECITPGuidance----------------Runtitle(3lines)------------------------------------------CALPOSTMODELCONTROLFILE---------------------------------------------------------------------------------------------------------INPUTGROUP:0--InputandOutputFileNames--------------InputFiles-----------FileDefaultFileName---------------------Conc/DepFluxFileMODEL.DAT!MODDAT=UTINVCAM02ALM.con!RelativeHumidityFileVISB.DAT*VISDAT=*BackgroundDataFileBACK.DAT*BACKDAT=*TransmissometerorVSRN.DAT*VSRDAT=*NephelometerDataFileorDATSAVWeatherDataFileorPrognosticWeatherFileOutputFiles------------FileDefaultFileName---------------------ListFileCALPOST.LST!PSTLST=VANINVCAM02CR.lst!PathnameforTimeseriesFiles(blank)*TSPATH=*(activatewithexclamationpointsonlyifprovidingNON-BLANKcharacterstring)PathnameforPlotFiles(blank)*PLPATH=*(activatewithexclamationpointsonlyifprovidingNON-BLANKcharacterstring)UserCharacterString(U)toaugmentdefaultfilenames(activatewithexclamationpointsonlyifprovidingNON-BLANKcharacterstring)TimeseriesTSERIES_ASPEC_ttHR_CONC_TSUNAM.DATPeakValuePEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DAT*TSUNAM=*1VANINVCAM02CR.inp10/23/2006TopNthRankPlotRANK(ALL)_ASPEC_ttHR_CONC_TUNAM.DATorRANK(ii)_ASPEC_ttHR_CONC_TUNAM.GRD*TUNAM=*ExceedancePlotEXCEED_ASPEC_ttHR_CONC_XUNAM.DATorEXCEED_ASPEC_ttHR_CONC_XUNAM.GRD*XUNAM=*EchoPlot(SpecificDays)yyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.DAToryyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.GRDVisibilityPlotDAILY_VISIB_VUNAM.DAT*VUNAM=*(DailyPeakSummary)AuxiliaryOutputFiles----------------------FileDefaultFileName---------------------VisibilityChangeDELVIS.DAT*DVISDAT=*--------------------------------------------------------------------------------AllfilenameswillbeconvertedtolowercaseifLCFILES=TOtherwise,ifLCFILES=F,filenameswillbeconvertedtoUPPERCASET=lowercase!LCFILES=T!F=UPPERCASENOTE:(1)file/pathnamescanbeupto132charactersinlengthNOTE:(2)FilenamesforALLPLOTandTIMESERIESFILESareconstructedusingatemplatethatincludesapathname,user-suppliedcharacter(s),andcontext-specificstrings,whereASPEC=SpeciesNameCONC=CONCOrWFLXOrDFLXOrTFLXtt=AveragingPeriod(e.g.03)ii=Rank(e.g.02)hh=Hour(ending)inLSTszzzz=BasetimezoneshiftfromUTC(ESTis-0500)yyyy=Year(LST)mm=Month(LST)dd=dayofmonth(LST)aredeterminedinternallybasedonselectionsmadebelow.Ifapathoruser-suppliedcharacter(s)aresupplied,each2VANINVCAM02CR.inp10/23/2006mustcontainatleast1non-blankcharacter.!END!--------------------------------------------------------------------------------INPUTGROUP:1--Generalruncontrolparameters--------------Optiontorunallperiodsfoundinthemet.file(s)(METRUN)Default:0!METRUN=0!METRUN=0-RunperiodexplicitlydefinedbelowMETRUN=1-RunallperiodsinCALPUFFdatafile(s)Startingdate:Year(ISYR)--Nodefault!ISYR=2002!(usedonlyifMonth(ISMO)--Nodefault!ISMO=1!METRUN=0)Day(ISDY)--Nodefault!ISDY=1!Hour(ISHR)--Nodefault!ISHR=1!Numberofhourstoprocess(NHRS)--Nodefault!NHRS=8760!Processeveryhourofdata?(NREP)--Default:1!NREP=1!(1=everyhourprocessed,2=every2ndhourprocessed,5=every5thhourprocessed,etc.)Species&Concentration/DepositionInformation----------------------------------------------Speciestoprocess(ASPEC)--Nodefault!ASPEC=VISIB!(ASPEC=VISIBforvisibilityprocessing)Layer/depositioncode(ILAYER)--Default:1!ILAYER=1!'1'forCALPUFFconcentrations,'-1'fordrydepositionfluxes,'-2'forwetdepositionfluxes,'-3'forwet+drydepositionfluxes.Scalingfactorsoftheform:--Defaults:!A=0.0!X(new)=X(old)*A+BA=0.0!B=0.0!(NOTappliedifA=B=0.0)B=0.0AddHourlyBackgroundConcentrations/Fluxes?(LBACK)--Default:F!LBACK=F!Sourceinformation------------------Optiontoprocesssourcecontributions:3VANINVCAM02CR.inp10/23/20060=Processonlytotalreportedcontributions1=Sumallindividualsourcecontributionsandprocess2=RuninTRACEBACKmodetoidentifysourcecontributionsataSINGLEreceptor(MSOURCE)--Default:0!MSOURCE=0!Receptorinformation--------------------Griddedreceptorsprocessed?(LG)--Default:F!LG=F!Discretereceptorsprocessed?(LD)--Default:F!LD=T!CTSGComplexterrainreceptorsprocessed?(LCT)--Default:F!LCT=F!--ReportresultsbyDISCRETEreceptorRING?(onlyusedwhenLD=T)(LDRING)--Default:F!LDRING=F!--SelectrangeofDISCRETEreceptors(onlyusedwhenLD=T):SelectALLDISCRETEreceptorsbysettingNDRECPflagto-1;ORSelectSPECIFICDISCRETEreceptorsbyenteringaflag(0,1)foreach0=discretereceptornotprocessed1=discretereceptorprocessedusingrepeatedvaluenotationtoselectblocksofreceptors:Flagforallreceptorsafterthelastoneassignedissetto0(NDRECP)--Default:-1!NDRECP=164*1,736*0,66*0,110*0!--SelectrangeofGRIDDEDreceptors(onlyusedwhenLG=T):XindexofLLcorner(IBGRID)--Default:-1!IBGRID=-1!(-1OR1<=IBGRID<=NX)YindexofLLcorner(JBGRID)--Default:-1!JBGRID=-1!(-1OR1<=JBGRID<=NY)XindexofURcorner(IEGRID)--Default:-1!IEGRID=-1!(-1OR1<=IEGRID<=NX)YindexofURcorner(JEGRID)--Default:-1!JEGRID=-1!(-1OR1<=JEGRID<=NY)Note:EntiregridisprocessedifIBGRID=JBGRID=IEGRID=JEGRID=-1--SpecificgriddedreceptorscanalsobeexcludedfromCALPOST4VANINVCAM02CR.inp10/23/2006processingbyfillingaprocessinggridarraywith0sand1s.Iftheprocessingflagforreceptorindex(i,j)is1(ON),thatreceptorwillbeprocessedifitlieswithintherangedelineatedbyIBGRID,JBGRID,IEGRID,JEGRIDandifLG=T.Ifitis0(OFF),itwillnotbeprocessedintherun.Bydefault,allarrayvaluesaresetto1(ON).NumberofgriddedreceptorrowsprovidedinSubgroup(1a)toidentifyspecificgriddedreceptorstoprocess(NGONOFF)--Default:0!NGONOFF=0!!END!--------------Subgroup(1a)--Specificgriddedreceptorsincluded/excluded--------------SpecificgriddedreceptorsareexcludedfromCALPOSTprocessingbyfillingaprocessinggridarraywith0sand1s.AtotalofNGONOFFlinesarereadhere.Eachlinecorrespondstoone'row'inthesamplinggrid,startingwiththeNORTHERNMOSTrowthatcontainsreceptorsthatyouwishtoexclude,andfinishingwithrow1totheSOUTH(nointerveningrowsmaybeskipped).Withinarow,eachreceptorpositionisassignedeithera0or1,startingwiththewesternmostreceptor.0=griddedreceptornotprocessed1=griddedreceptorprocessedRepeatedvaluenotationmaybeusedtoselectblocksofreceptors:23*1,15*0,12*1Becauseallvaluesareinitiallysetto1,anyreceptorsnorthofthefirstrowentered,oreastofthelastvalueprovidedinarow,remainON.(NGXRECP)--Default:1-------------------------------------------------------------------------------INPUTGROUP:2--VisibilityParameters(ASPEC=VISIB)--------------IdentifytheBaseTimeZonefortheCALPUFFsimulation(BTZONE)--Nodefault!BTZONE=5.0!Particlegrowthcurvef(RH)forhygroscopicspecies(MFRH)--Default:2!MFRH=2!5VANINVCAM02CR.inp10/23/20061=IWAQM(1998)f(RH)curve(originallyusedwithMVISBK=1)2=FLAG(2000)f(RH)tabulation3=EPA(2003)f(RH)tabulationMaximumrelativehumidity(%)usedinparticlegrowthcurve(RHMAX)--Default:98!RHMAX=95.0!ModeledspeciestobeincludedincomputingthelightextinctionIncludeSULFATE?(LVSO4)--Default:T!LVSO4=T!IncludeNITRATE?(LVNO3)--Default:T!LVNO3=T!IncludeORGANICCARBON?(LVOC)--Default:T!LVOC=T!IncludeCOARSEPARTICLES?(LVPMC)--Default:T!LVPMC=T!IncludeFINEPARTICLES?(LVPMF)--Default:T!LVPMF=T!IncludeELEMENTALCARBON?(LVEC)--Default:T!LVEC=T!And,whenrankingforTOP-N,TOP-50,andExceedancetables,IncludeBACKGROUND?(LVBK)--Default:T!LVBK=T!SpeciesnameusedforparticulatesinMODEL.DATfileCOARSE(SPECPMC)--Default:PMC!SPECPMC=PMC!FINE(SPECPMF)--Default:PMF!SPECPMF=SOIL!ExtinctionEfficiency(1/Mmperug/m**3)----------------------------------------MODELEDparticulatespecies:PMCOARSE(EEPMC)--Default:0.6!EEPMC=0.6!PMFINE(EEPMF)--Default:1.0!EEPMF=1.0!BACKGROUNDparticulatespecies:PMCOARSE(EEPMCBK)--Default:0.6!EEPMCBK=0.6!Otherspecies:AMMONIUMSULFATE(EESO4)--Default:3.0!EESO4=3.0!AMMONIUMNITRATE(EENO3)--Default:3.0!EENO3=3.0!ORGANICCARBON(EEOC)--Default:4.0!EEOC=4.0!SOIL(EESOIL)--Default:1.0!EESOIL=1.0!ELEMENTALCARBON(EEEC)--Default:10.!EEEC=10.0!BackgroundExtinctionComputation---------------------------------Methodusedforthe24h-averageofpercentchangeoflightextinction:Hourlyratioofsourcelightextinction/backgroundlightextinctionisaveraged?(LAVER)--Default:F!LAVER=F!Methodusedforbackgroundlightextinction(MVISBK)--Default:2!MVISBK=6!1=Supplysinglelightextinctionandhygroscopicfraction-HourlyF(RH)adjustmentappliedtohygroscopicbackground6VANINVCAM02CR.inp10/23/2006andmodeledsulfateandnitrate2=ComputeextinctionfromspeciatedPMmeasurements(A)-HourlyF(RH)adjustmentappliedtoobservedandmodeledsulfateandnitrate-F(RH)factoriscappedatF(RHMAX)3=ComputeextinctionfromspeciatedPMmeasurements(B)-HourlyF(RH)adjustmentappliedtoobservedandmodeledsulfateandnitrate-Receptor-hourexcludedifRH>RHMAX-Receptor-dayexcludediffewerthan6validreceptor-hours4=Readhourlytransmissometerbackgroundextinctionmeasurements-HourlyF(RH)adjustmentappliedtomodeledsulfateandnitrate-Hourexcludedifmeasurementinvalid(missing,interference,orlargeRH)-Receptor-hourexcludedifRH>RHMAX-Receptor-dayexcludediffewerthan6validreceptor-hours5=Readhourlynephelometerbackgroundextinctionmeasurements-Rayleighextinctionvalue(BEXTRAY)addedtomeasurement-HourlyF(RH)adjustmentappliedtomodeledsulfateandnitrate-Hourexcludedifmeasurementinvalid(missing,interference,orlargeRH)-Receptor-hourexcludedifRH>RHMAX-Receptor-dayexcludediffewerthan6validreceptor-hours6=ComputeextinctionfromspeciatedPMmeasurements-FLAGmonthlyRHadjustmentfactorappliedtoobservedandmodeledsulfateandnitrate7=Useobservedweatherorprognosticweatherinformationforbackgroundextinctionduringweatherevents;otherwise,useMethod2-HourlyF(RH)adjustmentappliedtomodeledsulfateandnitrate-F(RH)factoriscappedatF(RHMAX)-Duringobservedweatherevents,computeBextfromvisualrangeifusinganobservedweatherdatafile,or-Duringprognosticweatherevents,useBextfromtheprognosticweatherfile-UseMethod2forhourswithoutaweathereventAdditionalinputsusedforMVISBK=1:--------------------------------------Backgroundlightextinction(1/Mm)(BEXTBK)--Nodefault!BEXTBK=0.0!Percentageofparticlesaffectedbyrelativehumidity(RHFRAC)--Nodefault!RHFRAC=0.0!AdditionalinputsusedforMVISBK=6:--------------------------------------Extinctioncoefficientsforhygroscopicspecies(modeledandbackground)arecomputedusingamonthlyRHadjustmentfactorinplaceofanhourlyRHfactor(VISB.DATfileisNOTneeded).Enterthe12monthlyfactorshere(RHFAC).Month1isJanuary.7VANINVCAM02CR.inp10/23/2006(RHFAC)--Nodefault!RHFAC=3.3,3.0,2.9,2.8,3.2,3.7,3.6,4.1,4.0,3.7,3.4,3.2!AdditionalinputsusedforMVISBK=7:--------------------------------------Theweatherdatafile(DATSAVabbreviatedspace-delimited)thatisidentifiedasVSRN.DATmaycontaindataformorethanonestation.Identifythestationsthatareneededintheorderinwhichtheywillbeusedtoobtainvalidweatherandvisualrange.Thefirststationthatcontainsvaliddataforanhourwillbeused.EnteruptoMXWSTA(setinPARAMSfile)integerstationIDsofupto6digitseachasvariableIDWSTA,andenterthecorrespondingtimezoneforeach,asvariableTZONE(=UTC-LST).AprognosticweatherdatafilewithBextforweathereventsmaybeusedinplaceoftheobservedweatherfile.IdentifythisastheVSRN.DATfileanduseastationIDofIDWSTA=999999,andTZONE=0.NOTE:TZONEidentifiesthetimezoneusedinthedataset.TheDATSAVabbreviatedspace-delimiteddatausuallyarepreparedwithUTCtimeratherthanlocaltime,soTZONEistypicallysettozero.(IDWSTA)--Nodefault!IDWSTA=999999!(TZONE)--Nodefault!TZONE=0.0!AdditionalinputsusedforMVISBK=2,3,6,7:--------------------------------------------BackgroundextinctioncoefficientsarecomputedfrommonthlyCONCENTRATIONSofammoniumsulfate(BKSO4),ammoniumnitrate(BKNO3),coarseparticulates(BKPMC),organiccarbon(BKOC),soil(BKSOIL),andelementalcarbon(BKEC).Month1isJanuary.(ug/m**3)(BKSO4)--Nodefault!BKSO4=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!(BKNO3)--Nodefault!BKNO3=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!(BKPMC)--Nodefault!BKPMC=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!(BKOC)--Nodefault!BKOC=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,8VANINVCAM02CR.inp10/23/20060.00,0.00,0.00,0.00!(BKSOIL)--Nodefault!BKSOIL=11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21,11.21!(BKEC)--Nodefault!BKEC=0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00,0.00!AdditionalinputsusedforMVISBK=2,3,5,6,7:----------------------------------------------ExtinctionduetoRayleighscatteringisadded(1/Mm)(BEXTRAY)--Default:10.0!BEXTRAY=10.0!!END!-------------------------------------------------------------------------------INPUTGROUP:3--Outputoptions--------------Documentation-------------DocumentationrecordscontainedintheheaderoftheCALPUFFoutputfilemaybewrittentothelistfile.Printdocumentationimage?(LDOC)--Default:F!LDOC=F!OutputUnits------------UnitsforAllOutput(IPRTU)--Default:1!IPRTU=3!forforConcentrationDeposition1=g/m**3g/m**2/s2=mg/m**3mg/m**2/s3=ug/m**3ug/m**2/s4=ng/m**3ng/m**2/s5=OdourUnitsVisibility:extinctionexpressedin1/Mega-meters(IPRTUisignored)Averagingtime(s)reported--------------------------1-hraverages(L1HR)--Default:T!L1HR=F!3-hraverages(L3HR)--Default:T!L3HR=F!24-hraverages(L24HR)--Default:T!L24HR=T!9VANINVCAM02CR.inp10/23/2006Run-lengthaverages(LRUNL)--Default:T!LRUNL=F!User-specifiedaveragingtimeinhours-resultsforanaveragingtimeofNAVGhoursarereportedforNAVGgreaterthan0:(NAVG)--Default:0!NAVG=0!Typesoftabulationsreported------------------------------1)Visibility:dailyvisibilitytabulationsarealwaysreportedfortheselectedreceptorswhenASPEC=VISIB.Inaddition,anyoftheothertabulationslistedbelowmaybechosentocharacterizethelightextinctioncoefficients.[ListfileorPlot/AnalysisFile]2)Top50tableforeachaveragingtimeselected[Listfileonly](LT50)--Default:T!LT50=F!3)Top'N'tableforeachaveragingtimeselected[ListfileorPlotfile](LTOPN)--Default:F!LTOPN=T!--Numberof'Top-N'valuesateachreceptorselected(NTOPmustbe<=4)(NTOP)--Default:4!NTOP=1!--Specificranksof'Top-N'valuesreported(NTOPvaluesmustbeentered)(ITOP(4)array)--Default:!ITOP=1!1,2,3,44)Thresholdexceedancecountsforeachreceptorandeachaveragingtimeselected[ListfileorPlotfile](LEXCD)--Default:F!LEXCD=F!--Identifythethresholdforeachaveragingtimebyassigninganon-negativevalue(outputunits).--Default:-1.0Thresholdfor1-hraverages(THRESH1)!THRESH1=-1.0!Thresholdfor3-hraverages(THRESH3)!THRESH3=-1.0!10VANINVCAM02CR.inp10/23/2006Thresholdfor24-hraverages(THRESH24)!THRESH24=-1.0!ThresholdforNAVG-hraverages(THRESHN)!THRESHN=-1.0!--Countsfortheshortestaveragingperiodselectedcanbetallieddaily,andreceptorsthatexperiencemorethanNCOUNTcountsoveranyNDAYperiodwillbereported.ThistypeofexceedanceviolationoutputistriggeredonlyifNDAY>0.Accumulationperiod(Days)(NDAY)--Default:0!NDAY=0!Numberofexceedancesallowed(NCOUNT)--Default:1!NCOUNT=1!5)Selecteddaytable(s)EchoOption--Manyrecordsarewritteneachaveragingperiodselectedandoutputisgroupedbyday[ListfileorPlotfile](LECHO)--Default:F!LECHO=F!TimeseriesOption--Averagesatallselectedreceptorsforeachselectedaveragingperiodarewrittentotimeseriesfiles.Eachfilecontainsoneaveragingperiod,andallreceptorsarewrittentoasinglerecordeachaveragingtime.[TSERIES_ASPEC_ttHR_CONC_TSUNAM.DATfiles](LTIME)--Default:F!LTIME=F!PeakValueOption--Averagesatallselectedreceptorsforeachselectedaveragingperiodarescreenedandthepeakvalueeachperiodiswrittentotimeseriesfiles.Eachfilecontainsoneaveragingperiod.[PEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DATfiles](LPEAK)--Default:F!LPEAK=F!--Daysselectedforoutput(IECHO(366))--Default:366*0!IECHO=366*0!(366valuesmustbeentered)Plotoutputoptions-------------------PlotfilescanbecreatedfortheTop-N,Exceedance,andEchotablesselectedabove.Twoformatsforthesefilesareavailable,DATAandGRID.IntheDATAformat,resultsatallreceptorsarelistedalongwiththereceptorlocation[x,y,val1,val2,...].IntheGRIDformat,resultsatonlygriddedreceptorsarewritten,11VANINVCAM02CR.inp10/23/2006usingacompactrepresentation.Thegriddedvaluesarewritteninrows(xvaries),startingwiththemostsouthernrowofthegrid.TheGRIDformatisgiventhe.GRDextension,andincludesheaderscompatiblewiththeSURFER(R)plottingsoftware.Aplottingandanalysisfilecanalsobecreatedforthedailypeakvisibilitysummaryoutput,inDATAformatonly.GeneratePlotfileoutputinadditiontowritingtablestoListfile?(LPLT)--Default:F!LPLT=F!UseGRIDformatratherthanDATAformat,whenavailable?(LGRD)--Default:F!LGRD=F!AuxiliaryOutputFiles(forsubsequentanalyses)------------------------------------------------VisibilityAseparateoutputfilemayberequestedthatcontainsthechangeinvisibilityateachselectedreceptorwhenASPEC=VISIB.ThisfilecanbeprocessedtoconstructvisibilitymeasuresthatarenotavailableinCALPOST.Outputfilewiththevisibilitychangeateachreceptor?(MDVIS)--Default:0!MDVIS=1!0=DoNotcreatefile1=CreatefileofDAILY(24hour)Delta-Deciview2=CreatefileofDAILY(24hour)ExtinctionChange(%)3=CreatefileofHOURLYDelta-Deciview4=CreatefileofHOURLYExtinctionChange(%)AdditionalDebugOutput-----------------------OutputselectedinformationtoListfilefordebugging?(LDEBUG)--Default:F!LDEBUG=F!OutputhourlyextinctioninformationtoREPORT.HRV?(VisibilityMethod7)(LVEXTHR)--Default:F!LVEXTHR=F!!END!12VANINVCAM02CR.inp10/23/200613

# INVISTA Camden Plant C - 1 Trinity Consultants

BART Applicability Modeling Analysis 

# A PPENDIX 

# C

C OMPARATIVE 

# A NALYSIS FOR 

# E XPLICIT 

# CALPUFF M ODELING

# INVISTA Camden Plant C - 2 Trinity Consultants

BART Applicability Modeling Analysis Sample model processing files provided by the VISTAS Technical Contractor demonstrate modeling

of a single point source using CALPUFF, POSTU TIL, and CALPOST to assess visibility change. 17



# The sample approach simulates actual emissi ons of each of three gaseous pollutants (SO 2 

# , SO 4 

# , and

NO X 

# ) and unit emissions (e.g., 1 g/s) of each of si x generic particle categories distinguished and

designated by size: PM800, PM425, PM187, PM112, PM081, and PM056, to represent PM 6-10 

# ,

PM 2.5-6 

# , PM 1.25-2.5 

# , PM 1-1.25 

# , PM 0.625 

# - 1 

# , and PM 0.5-0.625 

# , respectively. Because unit emission rates were

modeled from the single point source in the sample approach, actual emission rates were used in the

POSTUTIL postprocessing step to combine PM types and sizes into light scattering groups by scaling

the modeled concentrations up or down by the multip licative factor of the actual emission rate of each

PM size category, which includes multiple types of PM (e.g., coarse filterable PM, fine filterable PM,

organic condensable PM, inorganic condensable PM, and elemental carbon). The output

concentration file from POSTUTIL was then inpu t to CALPOST to calculate visibility change

attributable to emissions from the point source in the sample analysis.

The preceding approach is reasonable for modeling a single point source; however, for facilities with

multiple emission point sources, the preceding appro ach is not appropriate. Specifically, for sources

with multiple emission points that have different e xhaust characteristics (e.g., stack height, diameter,

velocity, and temperature) and/or different emissions profiles of speciated PM, the use of unit

emission rates is not appropriate since the CALPUFF output concentrations at particular receptors

will not distinguish which source(s) contribute to the PM concentrations. Therefore, the POSTUTIL

source profile technique cannot be applied. One alte rnative to this approach for sources with multiple

emission points is to model each emission point individually in multiple CALPUFF runs using unit

emission rates, then run POSTUTIL to assign the PM concentrations at each receptor for each

modeled emission point to each species, fina lly running the CALSUM postprocessing utility to

combine the impacts of all sources. This approach , though conceptually appropriate, is undesirable

due to substantial additional computer runtime required to model and post-process each emission

point individually.

As a computationally efficient alternative to the preceding approaches, the BART Applicability

Analysis for INVISTA’s Camden Plant was c onducted by explicitly modeling in CALPUFF the

actual emission rate of each of 14 particle species defined as described in Table C-1. The

nomenclature used in Table C-1 is analogous to th at used to describe the emissions from INVISTA’s

BART-eligible emission units in Section 2 of this report.

17 

# http://www.src.com/verio/downloa d/sample_files.htm#EXAMPLE_BART

# INVISTA Camden Plant C - 3 Trinity Consultants

BART Applicability Modeling Analysis T ABLE 

# C-1. E XPLICIT 

# M ODELING OF 

# PM T YPES AND 

# S IZE 

# C ATEGORIES



# Modeled PM

Category Components

PMC800

PMC425 Filterable coarse particles divided between two size categories

(PM 6-10 

# , PM 2.5-6 

# )

PMF187

PMF112

PMF081

PMF056 Filterable fine particles divided among four size categories

(PM 1.25-2.5 

# , PM 1-1.25 

# , PM 0.625-1 

# , PM 0.5-0.625 

# )

POC081

POC056 Primary condensable organic emissions divided between two size categories

(PM 0.625-1 

# and PM 0.5-0.625 

# )

PIC081

PIC056 Primary condensable inorganic emissions divided between two size categories

(PM 0.625-1 

# and PM 0.5-0.625 

# )

EC187

EC112

EC081

EC056 Primary elemental carbon emissions divided among four size categories

(PM 1.25-2.5 

# , PM 1-1.25 

# , PM 0.625-1 

# , PM 0.5-0.625 

# )



# So that explicit modeling of the 14 particle species and sizes could be conducted equivalently to the

unit emissions approach, identical model processing options for each PM size category were enabled

as summarized in Table C-2.

T ABLE 

# C-2. R EPRESENTATION OF 

# E XPLICITLY 

# M ODELED 

# PM S IZE 

# C ATEGORIES 

# IN CALPUFF

Computed Geometric Mass Geometric Standa rd Precipitation Scav enging Coefficient

Model Species Deposition

Mode Mean Diameter

(microns) Deviation

(microns)* Liquid

(s -1 

# ) Frozen

(s -1 

# )

PMC800 Particle 8.0 0 1.0 x 10 -4 

# 3.0 x 10 -5



# PMC425 Particle 4.25 0 1.0 x 10 -4 

# 3.0 x 10 -5



# PMF187

EC187 Particle 1.87 0 1.0 x 10 -4 

# 3.0 x 10 -5



# PMF112

EC112 Particle 1.12 0 1.0 x 10 -4 

# 3.0 x 10 -5



# PMF081

EC081

POC081

PIC081 Particle 0.81 0 1.0 x 10 -4 

# 3.0 x 10 -5



# PMF056

EC056

POC056

PIC056 Particle 0.56 0 1.0 x 10 -4 

# 3.0 x 10 -5



# * Zero geometric standard deviation indicates that CALPUFF utili zes the deposition velocity associ ated with the geometric mass mean

diameter.

# INVISTA Camden Plant C - 4 Trinity Consultants

BART Applicability Modeling Analysis To post-process the CALPUFF output concentrations that result from explicitly modeled multiple

emission points, POSTUTIL was used only to group modeled PM into light extinction groups. Unit

scaling factors were used in POSTUTIL and there was no adjustment to the explicitly modeled

emission rate. Table C-3 summarizes the POSTUTIL grouping of modeled PM species into light

extinction groups, and the light extinction coeffi cient subsequently used in CALPOST to compute

light extinction due to the multiple emission points at the source.

T ABLE 

# C-3. A SSIGNMENT OF 

# M ODELED 

# PM S PECIES TO 

# L IGHT 

# E XTINCTION 

# G ROUPS



# Modeled

Components CALPOST Light

Extinction Group Extinction Coefficient

(m 2 

# /g)

PMC800

PMC425 PMC 0.6

PMF187

PMF112

PMF081

PMF056

PIC081

PIC056 SOIL 1

POC081

POC056 SOA 4

EC187

EC112

EC081

EC056 EC 10



# Implementation of the explicit modeling approach required minor changes to the parameter

declaration file and re-compilation of the CALPUFF model executable file. Note that this approach

does not require changes to the FORTRAN model code, only the parameter declaration limits.

Explicit modeling of the 14 PM types and sizes plus the SO 2 

# , SO 4 

# , NO X 

# , HNO 3 

# , and NO 3 

# species

results in a total of 19 modeled species, which is within the default parameter limit of 20 species

modeled (MXSPEC). However, the parameter for particle species deposited (MXPDEP) was

increased from 9 to 20 to accommodate the greater number (16, including SO 4 

# and NO 3 

# ) of particle

species simulated in the model.

This modified approach follows conceptu ally the steps outlined in the revised 

# VISTAS BART

Modeling Protocol as evidenced between comparisons between the two methods. Results using the

explicit method for multiple emission points and th e sample method using a single point source with

PM speciation (PMF, PMC, SOA, EC) applied during the POSTUTIL step provides equivalent

results. The following example model input and outpu t files of a comparative analysis are presented

to illustrate this approach. The comparative analysis was performed using emissions from a

representative example BART-eligible facility located in South Carolina using the screening approach

for the data year 2002 to compute visibility impact s at the Cape Romain NWR Class I area using the

annual average natural background conditions.

# INVISTA Camden Plant C - 5 Trinity Consultants

BART Applicability Modeling Analysis To demonstrate the equivalent performance of both models, the following four example point sources

listed in Table C-4 were modeled.

T ABLE 

# C-4. C OMPARATIVE 

# A NALYSIS 

# E MISSIONS 

# S OURCES



# Emission Rates (g/s)

Modeled PM Category Source 1 Source 2 Source 3 Source 4

PMC800

PMC425 1.20 × 10 -3



# 2.50 × 10 -2 

# 1.20 × 10 -1



# 3.70 × 10 -1 

# 4.10 × 10 -2



# 2.60 × 10 -1 

# 4.10 × 10 -2



# 2.60 × 10 -1



# PMF187

PMF112

PMF081

PMF056 1.30 × 10 -1



# 7.00 × 10 -2



# 2.80 × 10 -1



# 6.20 × 10 -1 

# 3.40 × 10 -1



# 1.60 × 10 -1



# 3.10 × 10 -1



# 5.60 × 10 -1 

# 6.60 × 10 -1



# 3.30 × 10 -1



# 5.90 × 10 -1



# 1.40 6.60 × 10 -1



# 3.30 × 10 -1



# 5.90 × 10 -1



# 1.40

POC081

POC056 1.80 × 10 -3



# 1.80 × 10 -3 

# 8.40 × 10 -1



# 8.40 × 10 -1 

# 5.60 × 10 -2



# 5.60 × 10 -2 

# 5.60 × 10 -2



# 5.60 × 10 -2



# PIC081

PIC056 3.60 × 10 -2



# 3.60 × 10 -2 

# 7.70

7.70 2.50 × 10 -1



# 2.50 × 10 -1 

# 2.50 × 10 -1



# 2.50 × 10 -1



# EC187

EC112

EC081

EC056 --

--

--

-- --

--

--

-- --

--

--

-- --

--

--

--



# The emissions rates listed in Table C-4 for all sources were modeled exp licitly using Trinity’s

modified CALPUFF executable. Using the VISTAS Sample approach, unit PM emission rates were

modeled for each individual source in a separate CALPUFF run and the scaling factors listed in

Table C-5 were applied in POSTUTIL. Note that as described in Table C-3, emission rates for PMF

and PIC are combined in this approach.

T ABLE 

# C-5. VISTAS S AMPLE 

# A NALYSIS 

# POSTUITL S CALING 

# F ACTORS



# Emission Rates (g/s)

Modeled PM Category Source 1 Source 2 Source 3 Source 4

CSPECCMP = EC

PM187

PM112

PM081

PM056 0.00000

0.00000

0.00000

0.00000 0.00000

0.00000

0.00000

0.00000 0.00000

0.00000

0.00000

0.00000 0.00000

0.00000

0.00000

0.00000

CSPECCMP = SOIL

PM187

PM112

PM081

PM056 0.13000

0.07000

0.31600

0.65600 0.34000

0.16000

8.01000

8.26000 0.66000

0.33000

0.84000

1.65000 0.66000

0.33000

0.84000

1.65000

CSPECCMP = SOA

PM081

PM056 0.00180

0.00180 0.84000

0.84000 0.05600

0.05600 0.05600

0.05600

CSPECCMP = PMC

PM800

PM425 0.00120

0.02500 0.12000

0.37000 0.04100

0.26000 0.04100

0.26000

# INVISTA Camden Plant C - 6 Trinity Consultants

BART Applicability Modeling Analysis VISTAS SAMPLE ANALYSES

1. MS-DOS BATCH RUN FILE RUNCPUFF1.BAT

This MS-DOS batch file seque ntially runs the following analyses to simulate unit PM

emissions from four sources independently, a pply the actual emission rates using POSTUTIL,

combine the files using the CALSUM utility to add the concentrations at each receptor due to

each source, then finally run CALPOST to calculate the visibility impact.

2. CALPUFF INPUT FILE SOURCE “A” VISTAS02A.INP

3. CALPUFF INPUT FILE SOURCE “B” VISTAS02B.INP

4. CALPUFF INPUT FILE SOURCE “C” VISTAS02C.INP

5. CALPUFF INPUT FILE SOURCE “D” VISTAS02D.INP

These CALPUFF input files were used to run the model for each source individually, with all

PM emission rates modeled as 1.0 g/s. A total of 11 species are modeled. The standard

CALPUFFL.EXE CALPUFF executable file obtained from the VISTAS Technical

Contractor was used to perform the analysis. The output of the CALPUFF runs

“VISTAS02 

# x .CON” are the concentration files that are input to POSTUTIL in the next step.

6. POSTUTIL INPUT FILE SOURCE “A” VISTASUT02A.INP

7. POSTUTIL INPUT FILE SOURCE “B” VISTASUT02B.INP

8. POSTUTIL INPUT FILE SOURCE “C” VISTASUT02C.INP

9. POSTUTIL INPUT FILE SOURCE “D” VISTASUT02D.INP

The POSTUTIL input files were used to scale the PM concentrations modeled in CALPUFF

by the actual emission rates of each PM species. The sum of PM species factors applied in

POSTUTIL equals the total PM emission rate for the source (less contribution from primary

sulfate emissions), and the speciated factors represent those tabulated for each source in

Section 2 of this report. Note that scaling of “SOIL” concentrations include contributions

from emissions quantified as PIC and PMF as illustrated in Table C-3. A total of 9 species

are output from POSTUTIL, including the computed species (EC, SOIL, SOA, PMC)

integrated over the size categories in addition to the explicitly modeled species (SO2, SO4,

NOX, HNO3, NO3). The output of the POSTUTIL runs “VISTASUT02 

# x .CON” are the

grouped and scaled concentration files input to CALSUM in the next step.

10. CALSUM INPUT FILE VISTASSUM02.INP

This CALSUM input file, after being copied into the appropriate file name “CALSUM.INP”

for compatibility with the CALSUM.exe runstream, adds the scaled concentrations of the 9

output species from POSTUTIL for each receptor and averaging period. The output of

CALSUM in “VISTASUT02.CON”, which is subsequently passed to CALPOST.

11. CALPOST INPUT FILE VISTASVANCR02.INP

This CALPOST file calculates the visibility im pacts due to concentrations reported in

“VISTASUT02.CON” for the receptors representi ng Cape Romain using the annual average

natural background conditions. The results of the analysis are written to the file

“VISTASVANCR02.LST”.

# INVISTA Camden Plant C - 7 Trinity Consultants

BART Applicability Modeling Analysis TRINITY’S EXPLICIT ANALYSES

1. MS-DOS BATCH RUN FILE RUNCPUFF2.BAT

This MS-DOS batch file sequen tially runs the following analyses to simulate actual emissions

from four sources modeled in one CALPUFF run, combine the speciated PM size groups into

output species using POSTUTIL, then finally run CALPOST to calculate the visibility

impact.

2. CALPUFF INPUT FILE ALL SOURCES EXPLICIT02.INP

This CALPUFF input file was used to run the model for all sources using actual PM emission

rates speciated for type (e.g., PIC, PMF) and size distribution. A total of 19 species are

modeled, including speciated size categories of all PM. The sum of PM species emission

rates equals the total PM emission rate for the source (less contribution from primary sulfate

emissions), and the speciated factors represent t hose tabulated for each source in Section 2 of

this report. The output of the CALPUFF runs “EXPLICIT02.CON” is the concentration files

that are input to POSTUTIL in the next step.

3. POSTUTIL INPUT FILE ALL SOURCES EXPLICITUT02.INP

The POSTUTIL input file was used only to co mbine, not scale, the PM concentrations

modeled in CALPUFF. A total of 9 species are output from POSTUTIL, including the

computed species (EC, SOIL, SOA, PMC) integr ated over the size categories in addition to

the explicitly modeled species (SO2, SO4, NOX, HNO3, NO3). The output of the

POSTUTIL runs “EXPLICITUT02.CON” are th e grouped concentration files input to

CALSUM in the next step.

4. CALPOST INPUT FILE EXPLICITVANCR02.INP

This CALPOST file calculates the visibility im pacts due to concentrations reported in

“EXPLICITUT02.CON” for the receptors representing Cape Romain using the annual

average natural background conditions. The resu lts of the analysis are written to the file

“EXPLICITVANCR02.LST”.

# INVISTA Camden Plant C - 8 Trinity Consultants

BART Applicability Modeling Analysis COMPARATIVE ANALYSIS OUTPUT FILES

The output files from the VISTAS Sample and Tr inity’s explicit analyses follow and indicate

equivalent results. The primary benefit of this approach is time savings from running CALPUFF and

subsequent postprocessors once (albeit for a great er number of sources) than one time for each

source. Table C-6 compares computer runtime for these methods on Pentium-4 class desktop

computers. The differences in computer processing runtime are appreciable when integrated over

numerous runs for facilities with multiple emissions sources.

T ABLE 

# C-6. C OMPARISON OF 

# C OMPUTER 

# R UNTIME USING 

# S AMPLE AND 

# E XPLICIT 

# A PPROACHES



# Processing Step VISTAS Sample Analysis Runtime

(minutes) Trinity’s Explicit Analysis Runtime

(minutes)

CALPUFF 170 105

POSTUTIL 2 < 1

CALSUM < 1 --

CALPOST < 1 < 1

Total Time 2 hours, 54 minutes 1 hour, 47 minutes



# The computer modeling executable, input, and output files for the comparative analysis are provided

for review on the electronic media included with this BART Applicability Analysis report. Each

analysis is contained within a separate folder (i .e., “VISTAS” and “EXPLICIT”, respectively) which

includes the CALPUFF model executable file. The “PARAMS.PUF” parameter declaration file is

also included to demonstrate how Trinity modifi ed the parameters to accommodate the explicit

modeling approach as described in this appendix.

# INVISTA Camden Plant D - 1 Trinity Consultants

BART Applicability Modeling Analysis 

# A PPENDIX 

# D

E LECTRONIC 

# M EDIA 

# D ATA 

# F ILE 

# I NDEX

# INVISTA Camden Plant D - 2 Trinity Consultants

BART Applicability Modeling Analysis Electronic media enclosed with this report contain the input and output files from all CALPUFF,

POSUTIL, and CALPOST processing for the screening and refined analyses, as well as the

comparative analyses presented in Appendix C. Each analysis is cont ained within its own

appropriately name compressed file, which includes model executable files and batch files to manage

the runstream. A consistent file naming convention is used throughout, with the following general

structure. All filenames contain the INVCAM root to denote INVISTA – Camden, South Carolina.

Note that screening and refined mete orological data files are not provided due to file size. Note also

that path names in input files will need to be modi fied to represent the user’s directory structure when

replicating these analyses.

CALPUFF Runstream Files

INVCAM 

# yy

. 

# fff

yy = 01

, 02 , and 03 denotes data analysis years 2001, 2002, and 2003, respectively



# fff = inp denotes input files



# fff = lst denotes CALPUFF output summary files



# fff = con denotes CALPUFF output concentration files

Ozone Data Files

OZCAM 

# yy

. 

# dat

yy = 01

, 02 , and 03 denotes data analysis years 2001, 2002, and 2003, respectively

Screening Analyses POSTUTIL Processing Files

UTINVCAM 

# yy.fff

yy = 01

, 02 , and 03 denotes data analysis years 2001, 2002, and 2003, respectively



# fff = inp denotes input files



# fff = lst denotes POSTUTIL output summary files



# fff = con denotes POSTUTIL output concentration files

Refined Analysis POSTUTIL Processing Files

Note that in refined analyses, for which the ammonia limiting method was run, POSTUTIL is run in

two separate steps, the first of which calculat es the HNO3/NO3 re-partitioning, the second of which

groups PM species for analysis in CALPOST. The firs t step (S1) is run in three, 4-month blocks (A,

B, C) due to an inherent limitation in the number of meteorological periods that can be processed.

Therefore, the APPEND utility must be run to concatenate the output files comprising these three

blocks of data. CALPOST is subse quently run using this appended file.

# INVISTA Camden Plant D - 3 Trinity Consultants

BART Applicability Modeling Analysis UTINVCAM 

# yyb.fff

yy = 01

, 02 , and 03 denotes data analysis years 2001, 2002, and 2003, respectively



# b = A

, B , and C denoting 4-month blocks January-Apr il, May-August, September-December,

respectively



# fff = inp denotes input files



# fff = lst denotes POSTUTIL output summary files



# fff = con denotes POSTUTIL output concentration files

APPEND 

# yy

. 

# fff

yy = 01

, 02 , and 03 denotes data analysis years 2001, 2002, and 2003, respectively



# fff = inp denotes input files



# fff = lst denotes POSTUTIL output summary files

UTINVCAM 

# yy S1.con = POSTUTIL-ALM Step 1 concentration file for year 

# yy

.

UTINVCAM 

# yy.fff

yy = 01

, 02 , and 03 denotes data analysis years 2001, 2002, and 2003, respectively



# fff = inp denotes input files



# fff = lst denotes POSTUTIL output summary files



# fff = con denotes POSTUTIL output concentration files

CALPOST Runstream Files

INVCAM 

# mmmaayy

. 

# fff

yy = 01

, 02 , and 03 denotes data analysis years 2001, 2002, and 2003, respectively



# fff = inp denotes input files



# fff = lst denotes CALPOST output summary files



# fff = del denotes CALPOST auxiliary visibility change output files



# mmm denotes the following natural background conditions:

VAN = Annual Average using VISTAS approach of representing the natural background as

SOIL concentration (Option 1)

V20 = 20% Best Days (Option 2)



# aa denotes the Class I areas considered in the analyses:

CR = Cape Romain NWR

GS = Great Smoky Mountains National Park

LG = Linville Gorge Wilderness Area

SR = Shining Rock Wilderness Area

# FINAL



# Protocol for the Application of the

CALPUFF Model for Analyses of

Best Available Retrofit Technology

(BART)

International Paper

Georgetown, South Carolina



# Prepared by:

URS Corporation

1600 Perimeter Park Drive, Suite 400

Morrisville, North Carolina 27560

March 2006

# Protocol for the Application of the

CALPUFF Model for Analyses of Best

Available Retrofit Technology (BART)

International Paper

Georgetown, South Carolina

March 2006

Prepared for:



# Georgetown, South Carolina



# Prepared by:

URS Corporation

1600 Perimeter Park Drive, Suite 400

Morrisville, North Carolina 27560

March 2006

i

# ii 

# Table of Contents

1.0 ....................................................................................................................... 1 Introduction

1.1 .............................................................................................. 3 Objective of Protocol

1.2 ......................................................... 3 Facility Location and Relevant Class I Areas

1.3 .......................................................................... 1 Source Impact Evaluation Criteria

1.4 ......................................... 1 General Overview of the CALPUFF Modeling System

2.0 .............................................................................................. 2 BART Source Descriptions

2.1 ....................................................................................... 2 Unit Specific Source Data

2.2 ............................................................................................ 5 Tabulated Source Data

3.0 ............................................................................ 7 Geophysical and Meteorological Data

4.0 ................................................................................. 7 CALPUFF Modeling Methodology

4.1 ........................................................................................................... 8 Methodology

4.2 ................................................. 10 CALMET Model Configura tion and Application

4.3 ............................................... 10 CALPUFF Model Configur ation and Application

4.3.1 ............................................................................................ 10 Model Codes

4.3.2 ................................................................................... 10 Domain Definition

4.3.3 .......................................................................................... 12 Model Set-Up

4.3.4 ................................................................. 12 Emissions Input Development

4.3.5 ........................... 14 Additional CALPUFF Input Information and Settings

5.0 ........................................................................................... 15 POSTUTIL PROCESSING

6.0 ............................................................................................. 16 CALPOST PROCESSING

6.1 ............................................................................................ 16 Visibility Assessment

7.0 ................................................... 18 ALTERNATIVE MOD ELING METHODOLOGY

8.0 .................................................................................................................. 24 REPORTING

8.1 ......................................................................... 24 Presentation of Modeling Results

8.2 .......................................................... 24 Reporting of CALPUFF Modeling Results

9.0 ................................................................................................................ 25 REFERENCES

Tables

2-1. BART Eligible Emission Units – Point Source Parameters ................................................8

2-2. BART Eligible Emission Units – Volume Source Parameters............................................9

7-1. Example of LOS Modeling Results ...................................................................................26

Figures

1-1 Facility Location Relative to Class I Areas .........................................................................4

4-1. BART Modeling Flow Chart .............................................................................................13

4-2. VISTAS CALMET Domains with Proposed CALPUFF Sub-domains............................15

7-1. Example of LOS Modeling Approach ...............................................................................25

# iii Appendices

Appendix A CALPUFF Configuration

Appendix B POSTUTIL Screening Configuration

Appendix C CALPOST Sc reening Configuration

Appendix D Class I Receptors in Lambert Conformal Coordinates

Appendix E North Dakota Background Procedure

Appendix F EPA Natural Background Values

Appendix G EPA Monthly F(RH) Values

Appendix H Paper Describing the Deciview Metric

Appendix I CALPUFF Plots Showing Plume Distribution

# 1 

# 1.0 Introduction

International Paper (IP) has retained UR S Corporation (URS) to prepare this Protocol for the

Application of the CALPUFF Model in Support of the Best Available Retrofit Technology

(BART) Regulation – 40 CFR 51.300 and Appendix Y . This protocol was pr epared at the request

of the South Carolina Department of Health a nd Environmental Control (SCDHEC) in order to

document the modeling procedures that will be used to perform CALPUF F dispersion modeling

in support of the EPA BART regulation. IP is proposing to perform modeling analyses to

determine whether air emissions from potentiall y BART eligible emission units at the IP

Georgetown, South Carolina pulp and paper mill cau se or contribute to regional haze in any

Class I area within 300 kilometers of the mill as defined by 40 CFR 51, Appendix Y. The

following provides a regulatory background of the BART regulation and a summary of the

modeling procedures deta iled in this protocol.

The Clean Air Act established goals for visibility in many national parks and wilderness areas.

Through the 1977 amendments to the Clean Air Act, Congress set a national goal for visibility as

“the prevention of any future, and the remedying of any existing, impairment of visibility in

mandatory Class I Federal areas which impairment results from manmade air pollution.” The

Amendments required EPA to issue regulations to assure “reasonable progress” toward meeting

the national goal.

In 1980, EPA promulgated regulations to address the visibility issues that is “reasonably

attributable” to a single source or small gr oup of sources. In 1988, the States, Federal Land

Managers (e.g., National Park Service, U.S. Fore st Service, U.S. Fish and Wildlife Service,

Bureau of Land Management), and EPA began mon itoring of fine particle concentrations and

visibility in 30 national parks and wi lderness areas across the country.

The Clean Air Act Amendments of 1990 required EPA to take regulatory action on regional haze

and they proposed the Regional Haze Regulations in July 1997 in conjunction with issuing new

national ambient air quality standards for fine particulate matter.

On July 1, 1999, EPA promulgated the final Regi onal Haze Regulation. The final Regional Haze

Regulation calls for state and fede ral agencies to work together to improve visibility in 156

national parks and wilderness areas in the Un ited States by developing and implementing longterm air quality protection plans to reduce the pollution that causes visibility impairment in these

protected areas.

The Regional Haze regulation provides States fl exibility in determin ing reasonable progress

goals for protected areas by conducting certain an alyses to ensure that they consider the

possibility of setting an ambitious reasonable progress goal, one that is aimed at reaching natural

background conditions by the year 2064. The regulat ion requires States to establish goals for

each affected area to (1) improve visibility on the haziest days, and (2) ensure no degradation

occurs on the clearest days over the period of each implementation plan.

The Regional Haze regulation also requires States to develop long-term strategies including

enforceable measures designed to meet reasonabl e progress goals. The first long-term strategy

will cover 10 to 15 years, with reassessment a nd revision of those goals and strategies in 2018

# 2 and every 10 years thereafter. State’s strategi es will address their cont ribution to visibility

problems in Class I areas both w ithin and outside the State.

One of the principal elements of the visibili ty protection provisions of the Clean Air Act

addresses installation of best av ailable retrofit technology (BART) for certain existing sources.

“BART-eligible” sources are th ose sources built between 1962 a nd 1977 that have the potential

to emit more than 250 tons per year of one or more visibility-impairing compounds including

sulfur dioxide (SO 2 

# ), nitrogen oxides (NO

x 

# ), particulate matter (P M), and volatile organic

compounds (VOCs), and that fall within 26 indus trial source categories (i ncluding Kraft pulp and

paper manufacturing).

Soon after the Regional Haze Regulation was fina lized, several parties filed petitions to

challenge the rule with the U.S. Court of App eals for the D.C. Circuit. In April 2004, EPA

Administrator Mike Leavitt signed a propos ed amendment to the 1999 Regional Haze

Regulation. The proposed rule satisfied the te rms of a May 2002 ruling by the U.S. Court of

Appeals for the D.C. Circuit, which vacated pa rts of the BART provisions of the 1999 Regional

Haze Regulation ( American Corn Growers et. al. v. EPA , 291 F. 3d 1 (D.C. cir. 2002).

The rule requires states to consider the visibi lity impacts of an indi vidual facility when

determining whether they have to install controls, and what thos e controls would be. The final

BART implementation and guidance rule ( 40 CFR Part 51, Appendix Y) was published on

July 6, 2005 and it allows for a BART evaluation for any BART-eligible source that ‘‘emits any

air pollutant which may reasonably be anticipated to cause or contribute to any impairment of

visibility” in any mandatory Class I federal area.

Pursuant to the rule, States have the option of exempting a BART-eligible source from the

BART requirements based on dispersion mode ling demonstrating that the source cannot

reasonably be anticipated to cause or contribute to visibility impairment in a Class I area.

Regional Planning Organizations (RPOs), such as the Visibility Improvement State and Tribal

Association of the Southeast (V ISTAS) have prepared guidance for performing the dispersion

modeling analyses. According to 40 CFR Pa rt 51, Appendix Y, a BART-eligible source is

considered to “contribute” to visibility impa irment in a Class I area if the modeled 98 th 

# percentile

change in deciviews (dv) is equal to or grea ter than the “contribution threshold.” Any BARTeligible source determined to caus e or contribute to visibility impa irment in any Class I area is

subject to a BART evaluation.

The Application of the CALPUFF Model for Analys es of Best Available Retrofit Technology

(BART), December 22, 2005, was prepared by the VISTAS RPO to provide some common

protocol guidance for performing conservative BART exemption and determination modeling

evaluations as allowed by the regulation.

It should be noted that the final BART rule de fines a “contribution threshold” of 0.5 dv as the

value where a modeled BART eligible source may “contribute” to visi bility impairment and

the threshold to determine whether a single source “causes” visibility impairment is set at a 1.0 dv

change from natural conditions (background visual range) over a 24-hour averaging period in the

final BART rule (70 FR 39118). An approximate 1.0 deciview change was defined by Pitchford

and Malm (1992) as a “just noticeable change” to the observer when the background visual range

equals the line of sight of the ob server. According to L. Willard Richards in “Use of the Deciview

Haze Index as an Indicator for Regional Haze” if a shorter line of sight distance than the

# 3 background visual range (natural conditions) is us ed in performing the calculations then a higher

extinction value, or deciview, is needed to cause a “just noticeable change.” In other words, when

the line of sight is less than the background visual range, then it would require a higher deciview

value in order to be a “just no ticeable change.” However, this protocol uses a conservative

modeling approach as defined by the VISTAS protocol by compar ing the extinction changes from

a single source at Class I area receptors only (not along the line of sight) to the background visual

range (natural conditions) in order to compare to the 0.5 deciview change thres hold. We are also

proposing in this protocol to use the refined line-of -sight modeling approach if needed in order to

better determine the actual impact that a single source would have on natural visibility conditions

in a Class I area (Section 7.0).



# 1.1 Objective of Protocol

The VISTAS States have accepted EPA’s guidan ce to use the CALPUFF modeling system to

comply with the BART modeling requirements of the regional haze rule. This protocol is

intended to satisfy the BART requirement thata BART-eligible source must submit a sitespecific modeling protocol to the State for re view and approval prior to performing CALPUFF

modeling. Many of the methods and procedures recommended in the VISTAS common

modeling protocol will be followed for modeling and the results will be presented in the standard

recommended format.

IP is also proposing to conduct more refi ned CALPUFF modeling to better quantify the

estimated impact of the mill’s potentially BART-eligible units on regional haze as necessary.

The refined modeling procedures, including examples, and the justif ication for these procedures

are presented in this protocol. IP Georgeto wn requests that SCDHEC carefully evaluate and

approve these modeling procedures or provide detailed comments to IP of why these procedures

are not acceptable. IP Georgetown and our e nvironmental consultant, URS Corporation is

willing to discuss these procedur es in greater detail with th e SCDHEC and supply additional

material demonstrating why thes e modeling procedures are appr opriate for calculating changes

in regional haze from individual point sources.

The remainder of this document describes the CALPUFF modeling system and the application of

CALPUFF to two situations:

1) Air Quality modeling to determine whet her a potentially BART-eligible source is

exempt from a BART control technology evaluation.

2) Air Quality modeling of emissions from a ll BART-eligible sources that are required to

perform a BART control technology evaluati on for the purpose of determining the

relative benefits of potential alternative contro l options as it pertains to reducing regional

haze in Class I areas.



# 1.2 Facility Location and Relevant Class I Areas

The International Paper Georgeto wn, South Carolina pulp and paper mill is located at 700 South

Kaminski Street in Georgetow n, South Carolina. The Universa l Transverse Mercator (UTM)

coordinates, in kilometers (km), for the mill are Zone 17, 657.867 East and 3692.690 North. The

approximate Lambert Conformal Conic (LCC) coordinates are 1631.84339 km East and

-575.41938 km North. There are two (2) Class I areas within 300 kilometers of the Georgetown

Mill: Cape Romain and Wolf Island National Wild life Refuge Areas. Figure 1-1 displays the

# 4 location of the mill and the two Class I areas. Cape Romain is located approximately 29.5

kilometers south of the mill and Wolf Island is located approximately 290 kilometers southwest

of the mill.3132333435

Latitu d eMill SiteCape RomainWolf Island-85 -84 -83 -82 -81 -80 -79LongitudeFILE NO.31825142URS Corporation – North Carolina1600 Perimeter Park Drive Suite 400Morrisville, North Carolina 27560Telephone (919) 461-1100 Fax (919) 461-1415FIG. NO.SCALE:DRAWN BY:SCLDATE:2/10/061-1AS SHOWNCHECKED BY:DATE:International Paper – GeorgetownFacility LocationRelative to Class IAreas1

# 1 

# 1.3 Source Impact Evaluation Criteria

To assess whether the IP Georgetown Mill is exempt from performing a BART control

technology evaluation, a two-tiered modeling approach is being pr oposed. For the initial

exemption modeling, the CALPUFF model w ill be used with 12-km grid CALMET data in a

screening mode. If the initial modeling result s show haze impacts less than the recommended

visibility threshold value of 0.5 dv, no further mo deling would be necessary. If the initial 12-km

grid modeling results show haze impacts greater than the recommended visibility threshold of

0.5 dv, then a finer resolution 4-km CALMET meteor ological grid will be used in the CALPUFF

modeling. If the finer resolution modeling results show haze impacts less than the visibility

threshold on 0.5 dv, then no furthe r modeling would be necessary. All modeling results will be

presented in detail in a report that will be submitted to SCDHEC for review and approval.

If the initial 12-km grid m odel greatly exceeds the recommended threshold or finer grid

modeling results exceed the recommended thre shold then BART determination CALPUFF

modeling will be conducted using finer resolution CALMET data. It is expected that SCDHEC

will accept EPA guidance that the threshold value to establish that a source contributes to

visibility impairment is 0.5 deciview.

Since the EPA BART guidance rule specifically st ates that modeling resu lts should be based on

the 98 th 

# percentile value, we are proposing that the 98 th 

# percentile be applied to all CALPUFF

modeling results. Thus, for the 12-km initial modeling exemption analysis, the 24-hour 98 th



# percentile value across all receptors in the Cla ss I area will be compared to the threshold

value of 0.5 dv. If the 24-hour 98 th 

# percentile value is below 0.5 dv, then IP Georgetown will

be exempt from performing a BART evaluation. If the 24-hour 98 th 

# percentile value is greater

than 0.5 dv, then IP may choose to perform finer grid modeling for exemption purposes or

use the alternative modeling approaches de scribed in Section 7 of this protocol.

URS will use the 12-km modeling results to focu s finer grid modeling for exemption purposes

on only those Class I areas wher e impacts greater than 0.5 dv are projected in the 12-km

modeling.

For finer grid (4 km or less) analyses, the 98 th 

# percentile value for the 24-hour average will also

be used.



# 1.4 General Overview of the CALPUFF Modeling System

The CALPUFF modeling system consists of four main processors: CALMET, CALPUFF,

POSTUTIL and CALPOST. CALMET is the meteor ological model that generates hourly threedimensional meteorological fields of variable s such as wind and temperature. CALPUFF

simulates the transport, dispersion, and transf ormation of compounds emitted from a source and

calculates hourly concentration values for visibility impairing compounds at each receptor

located in the modeling domain. POSTUTIL can perform many post processing tasks on the

CALPUFF output data file. CALP OST calculates time-averaged concentration values from the

CALPUFF predictions and perfor ms regional haze calculations like those described in the

Section 6.1 of this protocol.

# 2 

# 2.0 BART Source Descriptions

The IP Georgetown Mill is located in Georgeto wn, South Carolina, along the Sampit River. The

primary activities at Georgetown Mill are pulp production (Standard Indu strial Classification

[SIC] code 2611) and paper production (SIC code 2621). The Mill began operations in 1937.

Primary operations at the mill include multiple fuel-fired boilers, chemical recovery operations,

wood pulping operations, bleached papermaking, and additional operations and equipment

necessary to support these operations. The current nominal annualized paper production

capacity of the mill is 1,950 scale weight tons per day (SWT/d).



# 2.1 Unit Specific Source Data

The emission estimates used in the CALPUFF model are intended to reflect steady-state operating

conditions during periods of high capacity utiliz ation. Consistent with the VISTAS common

protocol, modeled emissions will not include pe riods of start-up, shutdown, and malfunction.

The modeling will be based on the 24-hour aver age actual emission rate from the highest em itting

day during the most recent 3-year period. Th e following prioritization for developing the

emission estimates will be used for the IP Georgetown mill:

• Continuous Emissions Monitoring (CEM) data;

• Facility emissions tests;

• Emissions factors;

• Permit limits; or

• Potential to emit.

The Georgetown Mill will develop emission es timates based on source testing and accepted

emission factors used for routine annual emissi ons reporting. In general, the following emission

rates will be used:

• Short-term (24-hours) allowable emission ra tes (e.g., emission rates calculated using the

maximum rated capacity of the unit);

• Federally enforceable short-term limits (24-hours); or

• Peak 24-hour actual emission rates (or calculate d emission rates) from the most recent 3-

years of operation that account for “high capacity utilization” during normal operating

conditions and fuel/material flexibility a llowed under the existing air permit. In

situations where a unit is allowed to use more than one fuel, the fuel resulting in the

highest emission rates will be used for the modeling.

Short-term emission rates (24-hours) for SO 2 

# , NO

x 

# , H 2 

# SO 4 

# mist, and PM 10 

# (including

condensible and filterable direct PM 10 

# ) will be modeled since visibility changes are calculated for

a 24-hour averaging period. All BART-eligible emission units at the mill that emit these

compounds will be modeled together in the CALPUFF model.