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 number 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-km 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 inputs 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 Modeling 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.

- CALMET 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 data), 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. 

Appendix H.6 - 600
VISTAS’ Common Modeling Protocol 43

- TERRAD (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 

regional 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 terrain 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 Configuration (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 modeled: SO2, SO4, NOx, HNO3, NO3 and particulate matter in size categories of 

<0.625 μm, 0.625-1.0 μm, 1.0-1.25 μm, 1.25-2.5 μm, 2.5-6.0 μm and 6-10 μm aerodynamic 

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

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

fine PM or “soil” (< 2.5 μm in diameter), coarse PM (between 2.5-10 μm 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 

sometime 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 SO2, H2SO4, NOx and PM10. 

Condensable 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 

Appendix H.6 - 601
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 pollutants with plant-wide emissions less than de minimis

levels (40 tons per year for SO2 and NOx and 15 tons per year for PM10). De minimis levels 

are plant wide for each visibility-impairing pollutant, so individual units may be modeled 

even if they have emissions 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” (fine 

PM < 2.5 μm diameter), coarse particulate matter (2.5-10 μm 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 National 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 Emissions. (PMC is coarse particulate matter -- 2.5 to 10 μm 

diameter.)

PM-10

Filterable Condensable

EC PM-2.5 PMC PM

(including 

H2SO4)

As Prim. SO4)

Organic PM

(SOA)

EC Soil PMC SO4

f(RH)

Non-SO4

Inorganic

OC

Appendix H.6 - 602
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 

following:

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

VISTAS’ CMAQ regional air quality modeling (available at http://www.vistassesarm.org/BART/calpuff.asp).

 The approach described in a memo available at http://www.vistassesarm.org/BART/calpuff.asp, which provides reasonably conservative estimates 

in situations where data are incomplete.

- Class I receptors: Use 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 2001-2003 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 unless 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 visibility analysis: SO4, NO3, 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 average natural background as 

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

Appendix H.6 - 603
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 guidance 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 coefficients 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 necessary), subtract the Rayleigh scattering value of 

10 Mm-1, and enter a soil concentration (in μg/m3) into CALPOST that is numerically equal 

to this result. (Since the extinction efficiency of soil is 1 m2/g, Equation 3-1 shows that this 

process produces a background 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, the 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 

algorithm.)

- 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 area 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 two 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 excluded 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 treatment 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 98th percentile change in 

deciviews value rather than the more conservative 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 

Appendix H.6 - 604
VISTAS’ Common Modeling Protocol 47

emissions information (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 data 

- 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 by 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 configuration 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 Settings 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 resolution 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. 

Appendix H.6 - 605
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 for 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 

particular 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 terrain may be unaffected by the terrainforced 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 both 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-daily upper air sounding data. 

Appendix H.6 - 606
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 depends 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 define 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 

observations 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 accuracy 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 source 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 be 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 visibility impairment is based on the 98th 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 computes 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. Therefore 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 contains 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 aerosols (f(RH)), and the contribution of each species to light extinction 

(in percent of the total source contribution) for SO4, NO3, organics, elemental carbon, coarse and 

fine particulate matter.

Appendix H.6 - 607
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 5.08 

 .

 .

 .

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 48.12 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

Appendix H.6 - 608
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 98th percentile (8th highest value) in the 

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

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

visibility impact is below the contribution threshold of 0.5 dv. 

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

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 

98th percentile days in each year greater than 0.5 dv (total visibility impairment minus 

impairment 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 98th 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 initial 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 specific 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.

Appendix H.6 - 609
VISTAS’ Common Modeling Protocol 52

Table 4-2. Example of Visibility Impact Rankings at Six Class I Areas

Class I Area 2001 2002 2003

DeltaDeciview

Ranks 1-8

DeltaDeciview

Ranks 1-8

DeltaDeciview

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

Appendix H.6 - 610
VISTAS’ Common Modeling Protocol 53

Table 4-3. Format of Summary 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 days1

and # of 

receptors 

with impact 

> 0.5 dv in 

Class I area: 

2001

# of days1

and # of 

receptors 

with impact 

> 0.5 dv in 

Class I area: 

2002

# of days1

and # of 

receptors 

with impact 

> 0.5 dv in 

Class I area: 

2003

# of days1 and 

# of receptors 

with impact 

> 1.0 dv in 

Class I area 

for 3-yr 

period

Max. 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

Linville 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 98th percentile of days in each year or the three-year modeling period, as appropriate

Appendix H.6 - 611
VISTAS’ Common Modeling Protocol 54

4.6 VISTAS Contribution to CALPUFF Modeling of BART Eligible 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 version 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 dispersion, 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-eligible 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 settings 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 available 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.src.com/verio/download/sample_files.htm).

Appendix H.6 - 612
Source-Specific Modeling Protocol 55

5. SOURCE-SPECIFIC MODELING PROTOCOL

Sources are required to submit a source-specific protocol to the State for review and approval 

prior to source-specific modeling. States will provide the 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-detailed 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 (SO2, H2SO4, NOx and PM10).

Additional 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 building 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 projection origin, coordinate 

datum, and false Easting and Northing (if used) of the projection origin. Subregional and sourcespecific domains may be using either an LCC or UTM projection. 

The CALPUFF Graphical User Interface (GUI) system provides software (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 source 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”.

Appendix H.6 - 613
Source-Specific Modeling Protocol 56

Table 5-1. Sample Table of Contents of a Source-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 Concentrations – 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 Major 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 Modeling 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

Appendix H.6 - 614
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 format 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 for BART Eligible Source. 

Unit name 

and/or 

description

Start-up dates SO2 potential 

emissions (tpy)

NOx potential 

emissions (tpy)

Total PM 

potential 

emissions (tpy) 

Emissions source

name

...

Total emissions

Potential BARTeligible 

emissions

Appendix H.6 - 615
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 contribute 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 establish 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 most 

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 datasets 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 options 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 contains 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 

switches 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 detailed 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 versions 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 meteorological 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 will need to be actively involved in control 

Appendix H.6 - 616
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 that 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 

aspects 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 the whether a particular source or 

group of sources is subject to BART controls. In the initial application, the regional CALPUFFready meteorological data files will be provided by VISTAS. The amount of effort for end-users 

performing QA of these pre-defined 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 development 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 that 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 

judgment 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 refined 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 with 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

Appendix H.6 - 617
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 conditions 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, including 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 list 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 part 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 may 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 projection 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 regional grid system. For a source-specific domain, the grid parameters 

will be provided as part of the source-specific protocol.

Appendix H.6 - 618
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 

CALPUFF.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 interrelationships 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 modeling 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/postprocessor 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 model 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 domain 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 various 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 

Appendix H.6 - 619
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 that 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 structure. 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 Control 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 CALPOST 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 relative 

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 are 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 output 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 single 

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 98th percentile value (8th 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 such 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 Method 6

- Background light extinction values

Appendix H.6 - 620
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 

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

concentrations from different modeled species (e.g., different particle sizes) into speciesdependent size distributions for the particulate matter. For example, PM is often 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 limiting 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 the 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 visibility 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 

Appendix H.6 - 621
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 circulation 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 configuration 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 important 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-specific 

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-specific 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 included in both the base and sensitivity simulations. 

Appendix H.6 - 622
References 65

7. REFERENCES

Allwine, K.J. and C.D. Whiteman, 1985: MELSAR: A Mesoscale Air Quality Model for Complex 

Terrain: Volume 1--Overview, Technical Description and User's Guide. Pacific Northwest Laboratory, 

Richland, Washington.

Batchvarova, E. and S.-E. Gryning, 1991: Applied model for the growth of the daytime mixed layer. 

Boundary-Layer Meteorol., 56, 261-274.

Batchvarova, E. and S.-E. Gryning, 1994: An applied model for the height of the daytime mixed layer 

and the entrainment zone. Boundary-Layer Meteorol., 71, 311-323.

Benjamin, S.G, D. Devenyi, S.S. Weygandt, K.J. Brundage, J.M. Brown, G.A. Grell, D. Kim, B.E. 

Schwartz, T.G. Smirnova, T.L. Smith, and G.S. Manikin, 2004: An Hourly Assimilation Forecast Cycle: 

the RUC, Mon. Wea. Rev., 132, 495-518.

Carson, D.J., 1973: The development of a dry, inversion-capped, convectively unstable boundary layer. 

Quart. J. Roy. Meteor. Soc., 99, 450-467.

Chang, J.C. P. Franzese, K. Chayantrakom and S.R. Hanna, 2001: Evaluations of CALPUFF, HPAC and 

VLSTRACK with Two Mesoscale Field Datasets. J. Applied Meteorology, 42(4): 453-466.

Department of the Interior, 2003: Letter from the Assistant Secretary of the Interior to the Director of the 

Montana Department of Environmental Quality.

Douglas, S. and R. Kessler, 1988: User's Guide to the Diagnostic Wind Model. California Air Resources 

Board, Sacramento, California.

Edgerton, E., 2004: Natural Sources of PM2.5 and PMcoarse Observed in the SEARCH Network. 

Presented at the A&WMA Specialty Conference on Regional and Global Perspectives in Haze: Causes, 

Consequences and Controversies, Asheville, NC, October 2004.

Environmental Protection Agency, 2003a: Guidance for Tracking Progress under the Regional Haze Rule; 

EPA-54/B-03-004, U.S. Environmental Protection Agency, Research Triangle Park, NC.

Environmental Protection Agency, 2003b: Guidance for Estimating Natural Visibility Conditions under 

the Regional Haze Rule. EPA-454/B-03-005. U.S. Environmental Protection Agency, Research Triangle 

Park, NC.

Environmental Protection Agency, 1998: Phase 2 Summary Report and Recommendations for Modeling 

Long Range Transport and Impacts. Interagency Workgroup on Air Quality Modeling (IWAQM). EPA454/R-98-019, U.S. Environmental Protection Agency, RTP, NC.

Appendix H.6 - 623
References 66

Escoffier-Czaja, C., and J. Scire. 2002: The Effects of Ammonia Limitation on Nitrate Aerosol Formation 

and Visibility Impacts in Class I Areas. Paper J5.13, 12th AMS/A&WMA Conference on the Applications 

of Air Pollution Meteorology, Norfolk, VA. May 2002.

Fairall, C.W., E.F. Bradley, J.E. Hare, A.A. Grachev, and J.B. Edson, 2003: 

Bulk parameterization of air-sea fluxes: Updates and verification for

the COARE algorithm. Journal of Climate, 16, 571-591.

Fallon, S. and G. Bench, 2004: IMPROVE Special Study: Hi-Vol Sampling for Carbon-14 Analysis of 

PM 2.5 Aerosols. Draft Report, Lawrence Livermore National Laboratory. 

FLAG, 2000. Federal Land Managers’ Air Quality Related Values Workgroup (FLAG). Phase I Report. 

U.S. Forest Service, National Park Service, U.S. Fish and Wildlife Service.

Grell, G.A., J. Dudhia, and D.R. Stauffer, 1995: A Description of the Fifth Generation Penn State/NCAR 

MM5, NCAR TN-398-STR, NCAR Technical Note.

Grosjean, D., and J. Seinfeld, 1989: Parameterization of the Formation Potential of Secondary Organic 

Aerosols. Atmos. Environ., 23, 1733-1747.

Holtslag, A.A.M. and A.P. van Ulden, 1983: A simple scheme for daytime estimates of the surface fluxes 

from routine weather data. J. Clim. and Appl. Meteor., 22, 517-529.

Irwin, J.S., J.S. Scire and D.G. Strimaitis, 1996: A Comparison of CALPUFF Modeling Results with 

CAPTEX Field Data Results. In Air Pollution Modeling and Its Applications, XII. Edited by S.E. 

Gryning and F.A. Schiermeier. Plenum Press, New York, NY.

IWAQM, 1998: Interagency Workgroup on Air Quality Modeling (IWAQM) Phase 2 Summary Report 

and Recommendations for Modeling Long Range Transport Impacts. EPA-454/R-98-019.

Liu, M.K. and M. A. Yocke, 1980: Siting of wind turbine generators in complex terrain. J. Energy, 4, 

10:16.

Mahrt, L., 1982: Momentum Balance of Gravity Flows. J. Atmos. Sci., 39, 2701-2711.

Maul, P.R., 1980: Atmospheric transport of sulfur compound pollutants. Central Electricity Generating 

Bureau MID/SSD/80/0026/R. Nottingham, England.

Morris, R., C. Tang and G. Yarwood, 2003: Evaluation of the Sulfate and Nitrate Formation Mechanism 

in the CALPUFF Modeling System. Proceedings of the A&WMA Specialty Conference – Guideline on 

Air Quality Models: The Path Forward. Mystic, CT, 22-24 October 2003.

Morrison, K., Z-X Wu, J.S. Scire, J. Chenier and T. Jeffs-Schonewille, 2003: CALPUFF-Based 

Predictive and Reactive Emissions Control System. 96th A&WMA Annual Conference & Exhibition, 22-

26 June 2003, San Diego, CA.

Appendix H.6 - 624
References 67

O'Brien, J.J., 1970: A note on the vertical structure of the eddy exchange coefficient in the planetary 

boundary layer. J. Atmos. Sci., 27, 1213-1215.

Pitchford, M., W. Malm, B. Schichtel, N. Kumar, D. Lowenthal, and J. Hand, 2005: Revised IMPROVE 

Algorithm for Estimating Light Extinction from Particle Speciation Data. Report to IMPROVE Steering 

Committee, November 2005

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

Yamartino, E.M. Insley, 1989: User’s Guide to the Complex Terrain Dispersion Model Plus Algorithms 

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: Development 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. Environmental 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 & 

Exhibition, 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. Yamartino, 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.-X. Wu, 2003: Evaluation of the CALPUFF Model in Predicting Concentration, Visibility 

and deposition at Class I Areas in Wyoming. Presented at the A&WMA Specialty Conference, Guideline 

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 

offshore and coastal applications. Proceedings of the Tenth International Conference on Harmonisation 

within Atmospheric Dispersion Modelling for Regulatory Purposes. Sissi (Malia), Crete, Greece. 17-20 

October 2005.

Strimaitis, D.G., J.S. Scire and J.C. Chang, 1998: Evaluation of the CALPUFF Dispersion Model with 

Two Power Plant Data Sets. Tenth Joint Conference on the Applications of Air Pollution Meteorology, 

Phoenix, Arizona. American Meteorological Society. 11-16 January 1998.

Appendix H.6 - 625
References 68

Tanner, R., M. Zheng, K. Lim, J. Schauer, and A. P. McNichol, 2005. Contributions to the Organic 

Aerosol Fraction in the Tennessee Valley: Seasonal and Urban-Rural Differences. Paper presented at the 

AAAR International Specialty Conference, PM: Supersite Program and Related Studies, Atlanta, 7-11 

February 2005.

Appendix H.6 - 626
INVISTA Camden Plant B - 1 Trinity Consultants 

BART Applicability Modeling Analysis 

APPENDIX B 

SAMPLE CALPUFF, POSTUTIL, AND CALPOST INPUT FILES

Appendix H.6 - 627
INVISTA Camden Plant B - 2 Trinity Consultants 

BART Applicability Modeling Analysis 

CALPUFF BATCH PROCESSING FILE

12-KM SCREENING ANALYSES 

Appendix H.6 - 628
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

Appendix H.6 - 629
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

Appendix H.6 - 630
INVISTA Camden Plant B - 3 Trinity Consultants 

BART Applicability Modeling Analysis 

SAMPLE CALPUFF INPUT FILE

INVCAM02.INP 

12-KM SCREENING ANALYSIS YEAR 2002 

Appendix H.6 - 631
INVCAM02.inp 

INVISTA CAMDENBART SCREENING ANALYSIS 12 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 UPDATED 07.21.2006 w/revised 12KM MET---------------- Run title (3 lines) ------------------------------------------

CALPUFF MODEL CONTROL FILE--------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names--------------Default Name Type File Name------------ ---- ---------CALMET.DAT input * METDAT = *

or

ISCMET.DAT input * ISCDAT = *

or

PLMMET.DAT input * PLMDAT = *

or

PROFILE.DAT input * PRFDAT = *SURFACE.DAT input * SFCDAT = *RESTARTB.DAT input * RSTARTB= *--------------------------------------------------------------------------------CALPUFF.LST output ! PUFLST =INVCAM02.lst !CONC.DAT output ! CONDAT =INVCAM02.con !DFLX.DAT output * DFDAT =puff2002-sm.dry *WFLX.DAT output * WFDAT =puff2002-sm.wet *VISB.DAT output * VISDAT =puff2002-sm.vis *RESTARTE.DAT output * RSTARTE=puff2002-sm.res *--------------------------------------------------------------------------------Emission Files--------------PTEMARB.DAT input * PTDAT = *VOLEMARB.DAT input * VOLDAT = *BAEMARB.DAT input * ARDAT = *LNEMARB.DAT input * LNDAT = *--------------------------------------------------------------------------------Other Files-----------OZONE.DAT input ! OZDAT =OZCAM02.dat !VD.DAT input * VDDAT = *CHEM.DAT input * CHEMDAT= *H2O2.DAT input * H2O2DAT= *HILL.DAT input * HILDAT= *HILLRCT.DAT input * RCTDAT= *COASTLN.DAT input * CSTDAT= *

1
INVCAM02.inp 

FLUXBDY.DAT input * BDYDAT= *BCON.DAT input * BCNDAT= *DEBUG.DAT output * DEBUG = *MASSFLX.DAT output * FLXDAT= *MASSBAL.DAT output * BALDAT= *FOG.DAT output * FOGDAT= *--------------------------------------------------------------------------------All file names will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, file names will be converted to UPPER CASE

T = lower case ! LCFILES = T !F = UPPER CASE

NOTE: (1) file/path names can be up to 70 characters in lengthProvision for multiple input files----------------------------------

Number of CALMET.DAT files for run (NMETDAT)

Default: 1 ! NMETDAT = 12 !

Number of PTEMARB.DAT files for run (NPTDAT)

Default: 0 ! NPTDAT = 0 !

Number of BAEMARB.DAT files for run (NARDAT)

Default: 0 ! NARDAT = 0 !

Number of VOLEMARB.DAT files for run (NVOLDAT)

Default: 0 ! NVOLDAT = 0 !

!END!-------------Subgroup (0a)-------------

The following CALMET.DAT filenames are processed in sequence if NMETDAT>1

Default Name Type File Name------------ ---- ---------

none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-01r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-02r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-03r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-04r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-05r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-06r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-07r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-08r.dat ! !END!

2
INVCAM02.inp 

none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-09r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-10r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-11r.dat ! !END!none input ! METDAT=T:\VISTAS\Domain0-2002\met2002-12r.dat ! !END!

INPUT GROUP: 1 -- General run control parameters--------------

Option to run all periods foundin the met. file (METRUN) Default: 0 ! METRUN = 0 !

METRUN = 0 - Run period explicitly defined belowMETRUN = 1 - Run all periods in met. file

Starting date: Year (IBYR) -- No default ! IBYR = 2002 !(used only if Month (IBMO) -- No default ! IBMO = 1 !

METRUN = 0) Day (IBDY) -- No default ! IBDY = 1 !

Hour (IBHR) -- No default ! IBHR = 1 !

Base time zone (XBTZ) -- No default ! XBTZ = 5.0 !

PST = 8., MST = 7.CST = 6., EST = 5.

Length of run (hours) (IRLG) -- No default ! IRLG = 8760 !Number of chemical species (NSPEC)

Default: 5 ! NSPEC = 19 !

Number of chemical speciesto be emitted (NSE) Default: 3 ! NSE = 17 !Flag to stop run afterSETUP phase (ITEST) Default: 2 ! ITEST = 2 !(Used to allow checkingof the model inputs, files, etc.)

ITEST = 1 - STOPS program after SETUP phaseITEST = 2 - Continues with execution of program

after SETUP

Restart Configuration:

Control flag (MRESTART) Default: 0 ! MRESTART = 0 !

0 = Do not read or write a restart file1 = Read a restart file at the beginning of

the run

2 = Write a restart file during run

3
INVCAM02.inp 

3 = Read a restart file at beginning of run

and write a restart file during run

Number of periods in Restartoutput cycle (NRESPD) Default: 0 ! NRESPD = 0 !

0 = File written only at last period

>0 = File updated every NRESPD periods

Meteorological Data Format (METFM)

Default: 1 ! METFM = 1 !

METFM = 1 - CALMET binary file (CALMET.MET)METFM = 2 - ISC ASCII file (ISCMET.MET)METFM = 3 - AUSPLUME ASCII file (PLMMET.MET)METFM = 4 - CTDM plus tower file (PROFILE.DAT) and

surface parameters file (SURFACE.DAT)

METFM = 5 - AERMET tower file (PROFILE.DAT) and

surface parameters file (SURFACE.DAT)

Meteorological Profile Data Format (MPRFFM)

(used only for METFM = 1, 2, 3)

Default: 1 ! MPRFFM = 1 !

MPRFFM = 1 - CTDM plus tower file (PROFILE.DAT)MPRFFM = 2 - AERMET tower file (PROFILE.DAT)

PG sigma-y is adjusted by the factor (AVET/PGTIME)**0.2Averaging Time (minutes) (AVET)

Default: 60.0 ! AVET = 60. !

PG Averaging Time (minutes) (PGTIME)

Default: 60.0 ! PGTIME = 60. !

!END!-------------------------------------------------------------------------------INPUT GROUP: 2 -- Technical options--------------

Vertical distribution used in thenear field (MGAUSS) Default: 1 ! MGAUSS = 1 !

0 = uniform1 = Gaussian

Terrain adjustment method

4
INVCAM02.inp 

(MCTADJ) Default: 3 ! MCTADJ = 3 !

0 = no adjustment1 = ISC-type of terrain adjustment2 = simple, CALPUFF-type of terrain

adjustment

3 = partial plume path adjustment

Subgrid-scale complex terrainflag (MCTSG) Default: 0 ! MCTSG = 0 !

0 = not modeled1 = modeled

Near-field puffs modeled aselongated slugs? (MSLUG) Default: 0 ! MSLUG = 0 !

0 = no1 = yes (slug model used)

Transitional plume rise modeled?(MTRANS) Default: 1 ! MTRANS = 1 !

0 = no (i.e., final rise only)1 = yes (i.e., transitional rise computed)

Stack tip downwash? (MTIP) Default: 1 ! MTIP = 1 !

0 = no (i.e., no stack tip downwash)1 = yes (i.e., use stack tip downwash)

Method used to simulate buildingdownwash? (MBDW) Default: 1 ! MBDW = 1 !

1 = ISC method2 = PRIME method

Vertical wind shear modeled abovestack top? (MSHEAR) Default: 0 ! MSHEAR = 0 !

0 = no (i.e., vertical wind shear not modeled)1 = yes (i.e., vertical wind shear modeled)

Puff splitting allowed? (MSPLIT) Default: 0 ! MSPLIT = 0 !

0 = no (i.e., puffs not split)1 = yes (i.e., puffs are split)

Chemical mechanism flag (MCHEM) Default: 1 ! MCHEM = 1 !

0 = chemical transformation not

modeled

1 = transformation rates computed

internally (MESOPUFF II scheme)

2 = user-specified transformation

rates used

3 = transformation rates computed

internally (RIVAD/ARM3 scheme)

5
INVCAM02.inp 

4 = secondary organic aerosol formation

computed (MESOPUFF II scheme for OH)

Aqueous phase transformation flag (MAQCHEM)(Used only if MCHEM = 1, or 3) Default: 0 ! MAQCHEM = 0 !

0 = aqueous phase transformation

not modeled

1 = transformation rates adjusted

for aqueous phase reactions

Wet removal modeled ? (MWET) Default: 1 ! MWET = 1 !

0 = no1 = yes

Dry deposition modeled ? (MDRY) Default: 1 ! MDRY = 1 !

0 = no1 = yes(dry deposition method specified

for each species in Input Group 3)

Gravitational settling (plume tilt)modeled ? (MTILT) Default: 0 ! MTILT = 0 !

0 = no1 = yes(puff center falls at the gravitational

settling velocity for 1 particle species)

Restrictions:

- MDRY = 1- NSPEC = 1 (must be particle species as well)- sg = 0 GEOMETRIC STANDARD DEVIATION in Group 8 is

set to zero for a single particle diameter

Method used to compute dispersioncoefficients (MDISP) Default: 3 ! MDISP = 3 !

1 = dispersion coefficients computed from measured values

of turbulence, sigma v, sigma w

2 = dispersion coefficients from internally calculated

sigma v, sigma w using micrometeorological variables(u*, w*, L, etc.)

3 = PG dispersion coefficients for RURAL areas (computed using

the ISCST multi-segment approximation) and MP coefficients inurban areas

4 = same as 3 except PG coefficients computed using

the MESOPUFF II eqns.

5 = CTDM sigmas used for stable and neutral conditions.

For unstable conditions, sigmas are computed as in

6
INVCAM02.inp 

MDISP = 3, described above. MDISP = 5 assumes thatmeasured values are read

Sigma-v/sigma-theta, sigma-w measurements used? (MTURBVW)(Used only if MDISP = 1 or 5) Default: 3 ! MTURBVW = 0 !

1 = use sigma-v or sigma-theta measurements

from PROFILE.DAT to compute sigma-y(valid for METFM = 1, 2, 3, 4, 5)

2 = use sigma-w measurements

from PROFILE.DAT to compute sigma-z(valid for METFM = 1, 2, 3, 4, 5)

3 = use both sigma-(v/theta) and sigma-w

from PROFILE.DAT to compute sigma-y and sigma-z(valid for METFM = 1, 2, 3, 4, 5)

4 = use sigma-theta measurements

from PLMMET.DAT to compute sigma-y(valid only if METFM = 3)

Back-up method used to compute dispersionwhen measured turbulence data aremissing (MDISP2) Default: 3 ! MDISP2 = 3 !(used only if MDISP = 1 or 5)

2 = dispersion coefficients from internally calculated

sigma v, sigma w using micrometeorological variables(u*, w*, L, etc.)

3 = PG dispersion coefficients for RURAL areas (computed using

the ISCST multi-segment approximation) and MP coefficients inurban areas

4 = same as 3 except PG coefficients computed using

the MESOPUFF II eqns.

[DIAGNOSTIC FEATURE]Method used for Lagrangian timescale for Sigma-y(used only if MDISP=1,2 or MDISP2=1,2)(MTAULY) Default: 0 ! MTAULY = 0 !

0 = Draxler default 617.284 (s)1 = Computed as Lag. Length / (.75 q) -- after SCIPUFF

10 < Direct user input (s) -- e.g., 306.9

[DIAGNOSTIC FEATURE]Method used for Advective-Decay timescale for Turbulence(used only if MDISP=2 or MDISP2=2)(MTAUADV) Default: 0 ! MTAUADV = 0 !

0 = No turbulence advection1 = Computed (OPTION NOT IMPLEMENTED)

10 < Direct user input (s) -- e.g., 300

7
INVCAM02.inp 

Method used to compute turbulence sigma-v &sigma-w using micrometeorological variables(Used only if MDISP = 2 or MDISP2 = 2)(MCTURB) Default: 1 ! MCTURB = 1 !

1 = Standard CALPUFF subroutines2 = AERMOD subroutines

PG sigma-y,z adj. for roughness? Default: 0 ! MROUGH = 0 !(MROUGH)

0 = no1 = yes

Partial plume penetration of Default: 1 ! MPARTL = 1 !elevated inversion?(MPARTL)

0 = no1 = yes

Strength of temperature inversion Default: 0 ! MTINV = 0 !provided in PROFILE.DAT extended records?(MTINV)

0 = no (computed from measured/default gradients)1 = yes

PDF used for dispersion under convective conditions?

Default: 0 ! MPDF = 0 !

(MPDF)

0 = no1 = yes

Sub-Grid TIBL module used for shore line?

Default: 0 ! MSGTIBL = 0 !

(MSGTIBL)

0 = no1 = yes

Boundary conditions (concentration) modeled?

Default: 0 ! MBCON = 0 !

(MBCON)

0 = no1 = yes, using formatted BCON.DAT file2 = yes, using unformatted CONC.DAT file

Analyses of fogging and icing impacts due to emissions fromarrays of mechanically-forced cooling towers can be performedusing CALPUFF in conjunction with a cooling tower emissionsprocessor (CTEMISS) and its associated postprocessors. Hourlyemissions of water vapor and temperature from each cooling tower

8
INVCAM02.inp 

cell are computed for the current cell configuration and ambientconditions by CTEMISS. CALPUFF models the dispersion of theseemissions and provides cloud information in a specialized formatfor further analysis. Output to FOG.DAT is provided in either'plume mode' or 'receptor mode' format.Configure for FOG Model output?

Default: 0 ! MFOG = 0 !

(MFOG)

0 = no1 = yes - report results in PLUME Mode format2 = yes - report results in RECEPTOR Mode format

Test options specified to see ifthey conform to regulatoryvalues? (MREG) Default: 1 ! MREG = 0 !

0 = NO checks are made1 = Technical options must conform to USEPA

Long Range Transport (LRT) guidance

METFM 1 or 2AVET 60. (min)PGTIME 60. (min)MGAUSS 1MCTADJ 3MTRANS 1MTIP 1MCHEM 1 or 3 (if modeling SOx, NOx)MWET 1MDRY 1MDISP 2 or 3MPDF 0 if MDISP=3

1 if MDISP=2

MROUGH 0MPARTL 1SYTDEP 550. (m)MHFTSZ 0

!END!-------------------------------------------------------------------------------INPUT GROUP: 3a, 3b -- Species list-------------------------------

9
INVCAM02.inp 

Subgroup (3a)------------

The following species are modeled:

! 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!

Dry OUTPUT GROUP

SPECIES MODELED EMITTED DEPOSITED NUMBER

NAME (0=NO, 1=YES) (0=NO, 1=YES) (0=NO, (0=NONE,

(Limit: 12 1=COMPUTED-GAS 1=1st CGRUP,

Characters 2=COMPUTED-PARTICLE 2=2nd CGRUP,in length) 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 !

10
INVCAM02.inp 

! EC081 = 1, 1, 2, 0 !! EC056 = 1, 1, 2, 0 !!END!-------------Subgroup (3b)-------------

The following names are used for Species-Groups in which resultsfor certain species are combined (added) prior to output. TheCGRUP name will be used as the species name in output files.Use this feature to model specific particle-size distributionsby treating each size-range as a separate species.Order must be consistent with 3(a) above.

-------------------------------------------------------------------------------INPUT GROUP: 4 -- Map Projection and Grid control parameters--------------

Projection for all (X,Y):-------------------------Map projection(PMAP) Default: UTM ! PMAP = LCC !

UTM : Universal Transverse MercatorTTM : Tangential Transverse MercatorLCC : Lambert Conformal Conic

PS : Polar StereographicEM : Equatorial Mercator

LAZA : Lambert Azimuthal Equal Area

False Easting and Northing (km) at the projection origin(Used only if PMAP= TTM, LCC, or LAZA)(FEAST) Default=0.0 ! FEAST = 0.000 !(FNORTH) Default=0.0 ! FNORTH = 0.000 !UTM zone (1 to 60)(Used only if PMAP=UTM)(IUTMZN) No Default ! IUTMZN = 0 !Hemisphere for UTM projection?(Used only if PMAP=UTM)(UTMHEM) Default: N ! UTMHEM = N !

N : Northern hemisphere projection

11
INVCAM02.inp 

S : Southern hemisphere projection

Latitude and Longitude (decimal degrees) of projection origin(Used only if PMAP= TTM, LCC, PS, EM, or LAZA)(RLAT0) No Default ! RLAT0 = 40N !(RLON0) No Default ! RLON0 = 97W !

TTM : RLON0 identifies central (true N/S) meridian of projection

RLAT0 selected for convenience

LCC : RLON0 identifies central (true N/S) meridian of projection

RLAT0 selected for convenience

PS : RLON0 identifies central (grid N/S) meridian of projection

RLAT0 selected for convenience

EM : RLON0 identifies central meridian of projection

RLAT0 is REPLACED by 0.0N (Equator)

LAZA: RLON0 identifies longitude of tangent-point of mapping plane

RLAT0 identifies latitude of tangent-point of mapping plane

Matching parallel(s) of latitude (decimal degrees) for projection(Used only if PMAP= LCC or PS)(XLAT1) No Default ! XLAT1 = 33N !(XLAT2) No Default ! XLAT2 = 45N !

LCC : Projection cone slices through Earth's surface at XLAT1 and XLAT2PS : Projection plane slices through Earth at XLAT1

(XLAT2 is not used)

----------Note: Latitudes and longitudes should be positive, and include a

letter N,S,E, or W indicating north or south latitude, andeast or west longitude. For example,35.9 N Latitude = 35.9N118.7 E Longitude = 118.7E

Datum-region------------The Datum-Region for the coordinates is identified by a characterstring. Many mapping products currently available use the model of theEarth known as the World Geodetic System 1984 (WGS-84). Other localmodels may be in use, and their selection in CALMET will make its outputconsistent with local mapping products. The list of Datum-Regions withofficial transformation parameters is provided by the National Imagery andMapping Agency (NIMA).NIMA Datum - Regions(Examples)------------------------------------------------------------------------------WGS-84 WGS-84 Reference Ellipsoid and Geoid, Global coverage (WGS84)

12
INVCAM02.inp 

NAS-C NORTH AMERICAN 1927 Clarke 1866 Spheroid, MEAN FOR CONUS (NAD27)NAR-C NORTH AMERICAN 1983 GRS 80 Spheroid, MEAN FOR CONUS (NAD83)NWS-84 NWS 6370KM Radius, SphereESR-S ESRI REFERENCE 6371KM Radius, SphereDatum-region for output coordinates(DATUM) Default: WGS-84 ! DATUM = NWS-84 !

METEOROLOGICAL Grid:

Rectangular grid defined for projection PMAP,with X the Easting and Y the Northing coordinate

No. X grid cells (NX) No default ! NX = 160 !No. Y grid cells (NY) No default ! NY = 172 !

No. vertical layers (NZ) No default ! NZ = 10 !

Grid spacing (DGRIDKM) No default ! DGRIDKM = 12. !

Units: km

Cell face heights

(ZFACE(nz+1)) No defaults

Units: m

! ZFACE = 0., 20., 40., 80., 160., 320., 640., 1200., 2000., 3000., 4000. !

Reference Coordinates

of SOUTHWEST corner of

grid cell(1, 1):

X coordinate (XORIGKM) No default ! XORIGKM = 137.973 !Y coordinate (YORIGKM) No default ! YORIGKM = -1625.974 !

Units: km

COMPUTATIONAL Grid:

The computational grid is identical to or a subset of the MET. grid.The lower left (LL) corner of the computational grid is at grid point(IBCOMP, JBCOMP) of the MET. grid. The upper right (UR) corner of thecomputational grid is at grid point (IECOMP, JECOMP) of the MET. grid.The grid spacing of the computational grid is the same as the MET. grid.

X index of LL corner (IBCOMP) No default ! IBCOMP = 81 !

(1 <= IBCOMP <= NX)

13
INVCAM02.inp 

Y index of LL corner (JBCOMP) No default ! JBCOMP = 78 !

(1 <= JBCOMP <= NY)

X index of UR corner (IECOMP) No default ! IECOMP = 129 !

(1 <= IECOMP <= NX)

Y index of UR corner (JECOMP) No default ! JECOMP = 112 !

(1 <= JECOMP <= NY)

SAMPLING Grid (GRIDDED RECEPTORS):

The lower left (LL) corner of the sampling grid is at grid point(IBSAMP, JBSAMP) of the MET. grid. The upper right (UR) corner of thesampling grid is at grid point (IESAMP, JESAMP) of the MET. grid.The sampling grid must be identical to or a subset of the computationalgrid. It may be a nested grid inside the computational grid.The grid spacing of the sampling grid is DGRIDKM/MESHDN.

Logical flag indicating if griddedreceptors are used (LSAMP) Default: T ! LSAMP = F !(T=yes, F=no)X index of LL corner (IBSAMP) No default ! IBSAMP = 1 !

(IBCOMP <= IBSAMP <= IECOMP)

Y index of LL corner (JBSAMP) No default ! JBSAMP = 1 !

(JBCOMP <= JBSAMP <= JECOMP)

X index of UR corner (IESAMP) No default ! IESAMP = 1 !

(IBCOMP <= IESAMP <= IECOMP)

Y index of UR corner (JESAMP) No default ! JESAMP = 1 !

(JBCOMP <= JESAMP <= JECOMP)

Nesting factor of the sampling

grid (MESHDN) Default: 1 ! MESHDN = 1 !(MESHDN is an integer >= 1)

!END!-------------------------------------------------------------------------------

14
INVCAM02.inp 

INPUT GROUP: 5 -- Output Options--------------

* *

FILE DEFAULT VALUE VALUE THIS RUN---- ------------- --------------

Concentrations (ICON) 1 ! ICON = 1 !Dry Fluxes (IDRY) 1 ! IDRY = 0 !Wet Fluxes (IWET) 1 ! IWET = 0 !Relative Humidity (IVIS) 1 ! IVIS = 0 !

(RH file is required for

VISIBILITY analyses)

Use data compression option in output file?(LCOMPRS) Default: T ! LCOMPRS = T !*

0 = Do not create file, 1 = create fileQA PLOT FILE OUTPUT OPTION:

Create a standard series of output files (e.g.locations of sources, receptors, grids ...)suitable for plotting?(IQAPLOT) Default: 1 ! IQAPLOT = 1 !

0 = no1 = yes

DIAGNOSTIC MASS FLUX OUTPUT OPTIONS:

Mass flux across specified boundariesfor selected species reported hourly?(IMFLX) Default: 0 ! IMFLX = 0 !

0 = no1 = yes (FLUXBDY.DAT and MASSFLX.DAT filenames

are specified in Input Group 0)

Mass balance for each speciesreported hourly?(IMBAL) Default: 0 ! IMBAL = 0 !

0 = no1 = yes (MASSBAL.DAT filename is

specified in Input Group 0)

LINE PRINTER OUTPUT OPTIONS:

15
INVCAM02.inp 

Print concentrations (ICPRT) Default: 0 ! ICPRT = 0 !Print dry fluxes (IDPRT) Default: 0 ! IDPRT = 0 !Print wet fluxes (IWPRT) Default: 0 ! IWPRT = 0 !(0 = Do not print, 1 = Print)Concentration print interval(ICFRQ) in hours Default: 1 ! ICFRQ = 1 !Dry flux print interval(IDFRQ) in hours Default: 1 ! IDFRQ = 1 !Wet flux print interval(IWFRQ) in hours Default: 1 ! IWFRQ = 1 !Units for Line Printer Output(IPRTU) Default: 1 ! IPRTU = 3 !

for for

Concentration Deposition

1 = g/m**3 g/m**2/s2 = mg/m**3 mg/m**2/s3 = ug/m**3 ug/m**2/s4 = ng/m**3 ng/m**2/s5 = Odour Units

Messages tracking progress of runwritten to the screen ?(IMESG) Default: 2 ! IMESG = 2 !

0 = no1 = yes (advection step, puff ID)2 = yes (YYYYJJJHH, # old puffs, # emitted puffs)

SPECIES (or GROUP for combined species) LIST FOR OUTPUT OPTIONS

---- CONCENTRATIONS ---- ------ DRY FLUXES ------ ------ WET FLUXES -FLUX --

SPECIES/GROUP PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK?------- ------------------------ ------------------------ ----------------------------------

! SO2 = 0, 1, 0, 0, 0, 0, ! SO4 = 0, 1, 0, 0, 0, 0, ! NOX = 0, 1, 0, 0, 0, 0, ! HNO3 = 0, 1, 0, 0, 0, 0, ! NO3 = 0, 1, 0, 0, 0, 0, ! POC081 = 0, 1, 0, 0, 0, 0, ! POC056 = 0, 1, 0, 0, 0, 0, ! PIC081 = 0, 1, 0, 0, 0, 0, ! PIC056 = 0, 1, 0, 0, 0, 0, 

16
INVCAM02.inp 

! PMC800 = 0, 1, 0, 0, 0, 0, ! PMC425 = 0, 1, 0, 0, 0, 0, ! PMF187 = 0, 1, 0, 0, 0, 0, ! PMF112 = 0, 1, 0, 0, 0, 0, ! PMF081 = 0, 1, 0, 0, 0, 0, ! PMF056 = 0, 1, 0, 0, 0, 0, ! EC187 = 0, 1, 0, 0, 0, 0, ! EC112 = 0, 1, 0, 0, 0, 0, ! EC081 = 0, 1, 0, 0, 0, 0, ! EC056 = 0, 1, 0, 0, 0, 0, 

OPTIONS FOR PRINTING "DEBUG" QUANTITIES (much output)

Logical for debug output(LDEBUG) Default: F ! LDEBUG = F !First puff to track(IPFDEB) Default: 1 ! IPFDEB = 1 !Number of puffs to track(NPFDEB) Default: 1 ! NPFDEB = 10 !Met. period to start output(NN1) Default: 1 ! NN1 = 10 !Met. period to end output(NN2) Default: 10 ! NN2 = 10 !

!END!-------------------------------------------------------------------------------INPUT GROUP: 6a, 6b, & 6c -- Subgrid scale complex terrain inputs----------------------------------------Subgroup (6a)---------------

Number of terrain features (NHILL) Default: 0 ! NHILL = 0 !Number of special complex terrainreceptors (NCTREC) Default: 0 ! NCTREC = 0 !Terrain and CTSG Receptor data forCTSG hills input in CTDM format ?(MHILL) No Default ! MHILL = 0 !1 = Hill and Receptor data created

17
INVCAM02.inp 

by CTDM processors & read fromHILL.DAT and HILLRCT.DAT files

2 = Hill data created by OPTHILL &

input below in Subgroup (6b);Receptor data in Subgroup (6c)

Factor to convert horizontal dimensions Default: 1.0 ! XHILL2M = 0. !to meters (MHILL=1)Factor to convert vertical dimensions Default: 1.0 ! ZHILL2M = 0. !to meters (MHILL=1)X-origin of CTDM system relative to No Default ! XCTDMKM = 0.0E00 !CALPUFF coordinate system, in Kilometers (MHILL=1)Y-origin of CTDM system relative to No Default ! YCTDMKM = 0.0E00 !CALPUFF coordinate system, in Kilometers (MHILL=1)

! END !---------------Subgroup (6b)---------------

1 **

HILL information

HILL XC YC THETAH ZGRID RELIEF EXPO 1 EXPO 2 SCALE 1 SAMAX2

NO. (km) (km) (deg.) (m) (m) (m) (m) (m) (m)

---- ---- ---- ------ ----- ------ ------ ------ ------- ---------------------Subgroup (6c)---------------

COMPLEX TERRAIN RECEPTOR INFORMATION

XRCT YRCT ZRCT XHH(km) (km) (m)

------ ----- ------ ----

-------------------1

Description of Complex Terrain Variables:

18
INVCAM02.inp 

XC, YC = Coordinates of center of hillTHETAH = Orientation of major axis of hill (clockwise from

North)

ZGRID = Height of the 0 of the grid above mean sea

level

RELIEF = Height of the crest of the hill above the grid elevationEXPO 1 = Hill-shape exponent for the major axisEXPO 2 = Hill-shape exponent for the major axisSCALE 1 = Horizontal length scale along the major axisSCALE 2 = Horizontal length scale along the minor axisAMAX = Maximum allowed axis length for the major axisBMAX = Maximum allowed axis length for the major axisXRCT, YRCT = Coordinates of the complex terrain receptorsZRCT = Height of the ground (MSL) at the complex terrain

Receptor

XHH = Hill number associated with each complex terrain receptor

(NOTE: MUST BE ENTERED AS A REAL NUMBER)

**

NOTE: DATA for each hill and CTSG receptor are treated as a separate

input subgroup and therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUP: 7 -- Chemical parameters for dry deposition of gases--------------

SPECIES DIFFUSIVITY ALPHA STAR REACTIVITY MESOPHYLL RESISTANCE COEFFICIENT

NAME (cm**2/s) (s/cm)(dimensionless)

------- ----------- ---------- ---------- -------------------------------------------

! SO2 = 0.1509, 1000., 8., 0., ! NOX = 0.1656, 1., 8., 5., ! HNO3 = 0.1628, 1., 18., 0., 0!END!-------------------------------------------------------------------------------INPUT GROUP: 8 -- Size parameters for dry deposition of particles--------------

19
INVCAM02.inp 

For SINGLE SPECIES, the mean and standard deviation are used tocompute a deposition velocity for NINT (see group 9) size-ranges,and these are then averaged to obtain a mean deposition velocity.For GROUPED SPECIES, the size distribution should be explicitlyspecified (by the 'species' in the group), and the standard deviationfor each should be entered as 0. The model will then use thedeposition velocity for the stated mean diameter.

SPECIES GEOMETRIC MASS MEAN GEOMETRIC STANDARD

NAME DIAMETER DEVIATION

(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!-------------------------------------------------------------------------------INPUT GROUP: 9 -- Miscellaneous dry deposition parameters--------------

Reference cuticle resistance (s/cm)(RCUTR) Default: 30 ! RCUTR = 30.0 !Reference ground resistance (s/cm)(RGR) Default: 10 ! RGR = 10.0 !Reference pollutant reactivity(REACTR) Default: 8 ! REACTR = 8.0 !Number of particle-size intervals used toevaluate effective particle deposition velocity(NINT) Default: 9 ! NINT = 9 !

20
INVCAM02.inp 

Vegetation state in unirrigated areas(IVEG) Default: 1 ! IVEG = 1 !

IVEG=1 for active and unstressed vegetationIVEG=2 for active and stressed vegetationIVEG=3 for inactive vegetation

!END!-------------------------------------------------------------------------------INPUT GROUP: 10 -- Wet Deposition Parameters---------------

Scavenging Coefficient -- Units: (sec)**(-1)

Pollutant Liquid Precip. Frozen Precip.--------- -------------- --------------

! 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!-------------------------------------------------------------------------------INPUT GROUP: 11 -- Chemistry Parameters---------------

Ozone data input option (MOZ) Default: 1 ! MOZ = 1 !

21
INVCAM02.inp 

(Used only if MCHEM = 1, 3, or 4)

0 = use a monthly background ozone value1 = read hourly ozone concentrations from

the OZONE.DAT data file

Monthly ozone concentrations(Used only if MCHEM = 1, 3, or 4 and

MOZ = 0 or MOZ = 1 and all hourly O3 data missing)

(BCKO3) in ppb Default: 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 !

Monthly ammonia concentrations(Used only if MCHEM = 1, or 3)(BCKNH3) in ppb Default: 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 !Nighttime SO2 loss rate (RNITE1)in percent/hour Default: 0.2 ! RNITE1 = .2 !Nighttime NOx loss rate (RNITE2)in percent/hour Default: 2.0 ! RNITE2 = 2.0 !Nighttime HNO3 formation rate (RNITE3)in percent/hour Default: 2.0 ! RNITE3 = 2.0 !H2O2 data input option (MH2O2) Default: 1 ! MH2O2 = 1 !(Used only if MAQCHEM = 1)

0 = use a monthly background H2O2 value1 = read hourly H2O2 concentrations from

the H2O2.DAT data file

Monthly H2O2 concentrations(Used only if MQACHEM = 1 and

MH2O2 = 0 or MH2O2 = 1 and all hourly H2O2 data missing)

(BCKH2O2) in ppb Default: 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 !

--- Data for SECONDARY ORGANIC AEROSOL (SOA) Option

(used only if MCHEM = 4)The SOA module uses monthly values of:

Fine particulate concentration in ug/m^3 (BCKPMF)Organic fraction of fine particulate (OFRAC)VOC / NOX ratio (after reaction) (VCNX)

to characterize the air mass when computingthe formation of SOA from VOC emissions.Typical values for several distinct air mass types are:

22
INVCAM02.inp 

Month 1 2 3 4 5 6 7 8 9 10 11 12

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Clean Continental

BCKPMF 1. 1. 1. 1. 1. 1. 1. 1. 1. 1. 1. 1.OFRAC .15 .15 .20 .20 .20 .20 .20 .20 .20 .20 .20 .15VCNX 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50.

Clean Marine (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 .25VCNX 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50.

Urban - low biogenic (controls present)

BCKPMF 30. 30. 30. 30. 30. 30. 30. 30. 30. 30. 30. 30.OFRAC .20 .20 .25 .25 .25 .25 .25 .25 .20 .20 .20 .20VCNX 4. 4. 4. 4. 4. 4. 4. 4. 4. 4. 4. 4.

Urban - high biogenic (controls present)

BCKPMF 60. 60. 60. 60. 60. 60. 60. 60. 60. 60. 60. 60.OFRAC .25 .25 .30 .30 .30 .55 .55 .55 .35 .35 .35 .25VCNX 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15.

Regional Plume

BCKPMF 20. 20. 20. 20. 20. 20. 20. 20. 20. 20. 20. 20.OFRAC .20 .20 .25 .35 .25 .40 .40 .40 .30 .30 .30 .20VCNX 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15.

Urban - no controls present

BCKPMF 100. 100. 100. 100. 100. 100. 100. 100. 100. 100. 100. 100.OFRAC .30 .30 .35 .35 .35 .55 .55 .55 .35 .35 .35 .30VCNX 2. 2. 2. 2. 2. 2. 2. 2. 2. 2. 2. 2.

Default: Clean Continental! 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.

!END!-------------------------------------------------------------------------------INPUT GROUP: 12 -- Misc. Dispersion and Computational Parameters---------------

23
INVCAM02.inp 

Horizontal size of puff (m) beyond whichtime-dependent dispersion equations (Heffter)are used to determine sigma-y andsigma-z (SYTDEP) Default: 550. ! SYTDEP = 5.5E02 !Switch for using Heffter equation for sigma zas above (0 = Not use Heffter; 1 = use Heffter(MHFTSZ) Default: 0 ! MHFTSZ = 0 !Stability class used to determine plumegrowth rates for puffs above the boundarylayer (JSUP) Default: 5 ! JSUP = 5 !Vertical dispersion constant for stableconditions (k1 in Eqn. 2.7-3) (CONK1) Default: 0.01 ! CONK1 = .01 !Vertical dispersion constant for neutral/unstable conditions (k2 in Eqn. 2.7-4)(CONK2) Default: 0.1 ! CONK2 = .1 !Factor for determining Transition-point fromSchulman-Scire to Huber-Snyder Building Downwashscheme (SS used for Hs < Hb + TBD * HL)(TBD) Default: 0.5 ! TBD = .5 !

TBD < 0 ==> always use Huber-SnyderTBD = 1.5 ==> always use Schulman-ScireTBD = 0.5 ==> ISC Transition-point

Range of land use categories for whichurban dispersion is assumed(IURB1, IURB2) Default: 10 ! IURB1 = 10 !

19 ! IURB2 = 19 !

Site characterization parameters for single-point Met data files ---------(needed for METFM = 2,3,4,5)

Land use category for modeling domain(ILANDUIN) Default: 20 ! ILANDUIN = 20 !Roughness length (m) for modeling domain(Z0IN) Default: 0.25 ! Z0IN = .25 !Leaf area index for modeling domain(XLAIIN) Default: 3.0 ! XLAIIN = 3.0 !Elevation above sea level (m)(ELEVIN) Default: 0.0 ! ELEVIN = .0 !Latitude (degrees) for met location

24
INVCAM02.inp 

(XLATIN) Default: -999. ! XLATIN = -999.0 !Longitude (degrees) for met location(XLONIN) Default: -999. ! XLONIN = -999.0 !

Specialized information for interpreting single-point Met data files -----

Anemometer height (m) (Used only if METFM = 2,3)(ANEMHT) Default: 10. ! ANEMHT = 10.0 !Form of lateral turbulance data in PROFILE.DAT file(Used only if METFM = 4,5 or MTURBVW = 1 or 3)(ISIGMAV) Default: 1 ! ISIGMAV = 1 !

0 = read sigma-theta1 = read sigma-v

Choice of mixing heights (Used only if METFM = 4)(IMIXCTDM) Default: 0 ! IMIXCTDM = 0 !

0 = read PREDICTED mixing heights1 = read OBSERVED mixing heights

Maximum length of a slug (met. grid units)(XMXLEN) Default: 1.0 ! XMXLEN = 1.0 !Maximum travel distance of a puff/slug (ingrid units) during one sampling step(XSAMLEN) Default: 1.0 ! XSAMLEN = 1.0 !Maximum Number of slugs/puffs release fromone source during one time step(MXNEW) Default: 99 ! MXNEW = 99 !Maximum Number of sampling steps forone puff/slug during one time step(MXSAM) Default: 99 ! MXSAM = 99 !Number of iterations used when computingthe transport wind for a sampling stepthat includes gradual rise (for CALMETand PROFILE winds)(NCOUNT) Default: 2 ! NCOUNT = 2 !Minimum sigma y for a new puff/slug (m)(SYMIN) Default: 1.0 ! SYMIN = 1.0 !Minimum sigma z for a new puff/slug (m)(SZMIN) Default: 1.0 ! SZMIN = 1.0 !Default minimum turbulence velocities sigma-v and sigma-w

25
INVCAM02.inp 

for each stability class over land and over water (m/s)(SVMIN(12) and SWMIN(12))

---------- LAND ---------- --------- WATER ----------

Stab Class : A B C D E F A B C D E F

--- --- --- --- --- --- --- --- --- --- --- ---

Default SVMIN : .50, .50, .50, .50, .50, .50, .37, .37, .37, .37, .37, .37Default SWMIN : .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, ! SWMIN = 0.200, 0.120, 0.080, 0.060, 0.030, 0.016, 0.200, 0.120, 0.080, 0.060, 

Divergence criterion for dw/dz across puffused to initiate adjustment for horizontalconvergence (1/s)Partial adjustment starts at CDIV(1), andfull adjustment is reached at CDIV(2)(CDIV(2)) Default: 0.0,0.0 ! CDIV = .0, .0 !Minimum wind speed (m/s) allowed fornon-calm conditions. Also used as minimumspeed returned when using power-lawextrapolation toward surface(WSCALM) Default: 0.5 ! WSCALM = .5 !Maximum mixing height (m)(XMAXZI) Default: 3000. ! XMAXZI = 3000.0 !Minimum mixing height (m)(XMINZI) Default: 50. ! XMINZI = 50.0 !Default wind speed classes --5 upper bounds (m/s) are entered;the 6th class has no upper limit(WSCAT(5)) Default :

ISC RURAL : 1.54, 3.09, 5.14, 8.23, 10.8 (10.8+)

Wind Speed Class : 1 2 3 4 5

--- --- --- --- ---

! WSCAT = 1.54, 3.09, 5.14, 8.23, 10.80 !

Default wind speed profile power-lawexponents for stabilities 1-6(PLX0(6)) Default : ISC RURAL values

ISC RURAL : .07, .07, .10, .15, .35, .55ISC URBAN : .15, .15, .20, .25, .30, .30

Stability Class : A B C D E F

--- --- --- --- --- ---

26
INVCAM02.inp 

! PLX0 = 0.07, 0.07, 0.10, 0.15, 0.35, 0.55 !

Default potential temperature gradientfor stable classes E, F (degK/m)(PTG0(2)) Default: 0.020, 0.035

! PTG0 = 0.020, 0.035 !

Default plume path coefficients foreach stability class (used when optionfor partial plume height terrain adjustmentis selected -- MCTADJ=3)(PPC(6)) Stability Class : A B C D E F

Default PPC : .50, .50, .50, .50, .35, .35

--- --- --- --- --- ---

! PPC = 0.50, 0.50, 0.50, 0.50, 0.35, 0.35 !

Slug-to-puff transition criterion factorequal to sigma-y/length of slug(SL2PF) Default: 10. ! SL2PF = 5.0 !Puff-splitting control variables ------------------------

VERTICAL SPLIT--------------Number of puffs that result every time a puffis split - nsplit=2 means that 1 puff splitsinto 2(NSPLIT) Default: 3 ! NSPLIT = 3 !Time(s) of a day when split puffs are eligible tobe split once again; this is typically set onceper day, around sunset before nocturnal shear develops.24 values: 0 is midnight (00:00) and 23 is 11 PM (23:00)0=do not re-split 1=eligible for re-split(IRESPLIT(24)) Default: Hour 17 = 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 !Split is allowed only if last hour's mixingheight (m) exceeds a minimum value(ZISPLIT) Default: 100. ! ZISPLIT = 100.0 !Split is allowed only if ratio of last hour'smixing ht to the maximum mixing ht experiencedby the puff is less than a maximum value (thispostpones a split until a nocturnal layer develops)(ROLDMAX) Default: 0.25 ! ROLDMAX = 0.25 !

27
INVCAM02.inp 

HORIZONTAL SPLIT----------------Number of puffs that result every time a puffis split - nsplith=5 means that 1 puff splitsinto 5(NSPLITH) Default: 5 ! NSPLITH = 5 !Minimum sigma-y (Grid Cells Units) of puffbefore it may be split(SYSPLITH) Default: 1.0 ! SYSPLITH = 1.0 !Minimum puff elongation rate (SYSPLITH/hr) due towind shear, before it may be split(SHSPLITH) Default: 2. ! SHSPLITH = 2.0 !Minimum concentration (g/m^3) of eachspecies in puff before it may be splitEnter array of NSPEC values; if a single value isentered, it will be used for ALL species(CNSPLITH) Default: 1.0E-07 ! CNSPLITH = 1.0E-07 !

Integration control variables ------------------------

Fractional convergence criterion for numerical SLUGsampling integration(EPSSLUG) Default: 1.0e-04 ! EPSSLUG = 1.0E-04 !Fractional convergence criterion for numerical AREAsource integration(EPSAREA) Default: 1.0e-06 ! EPSAREA = 1.0E-06 !Trajectory step-length (m) used for numerical riseintegration(DSRISE) Default: 1.0 ! DSRISE = 1.0 !Boundary Condition (BC) Puff control variables ------------------------Minimum height (m) to which BC puffs are mixed as they are emitted(MBCON=2 ONLY). Actual height is reset to the current mixing heightat the release point if greater than this minimum.(HTMINBC) Default: 500. ! HTMINBC = 500.0 !Search radius (km) about a receptor for sampling nearest BC puff.BC puffs are typically emitted with a spacing of one grid celllength, so the search radius should be greater than DGRIDKM.(RSAMPBC) Default: 10. ! RSAMPBC = 15.0 !Near-Surface depletion adjustment to concentration profile used when

28
INVCAM02.inp 

sampling BC puffs?(MDEPBC) Default: 1 ! MDEPBC = 0 !

0 = Concentration is NOT adjusted for depletion1 = Adjust Concentration for depletion

!END!-------------------------------------------------------------------------------INPUT GROUPS: 13a, 13b, 13c, 13d -- Point source parameters-----------------------------------------------Subgroup (13a)---------------

Number of point sources withparameters provided below (NPT1) No default ! NPT1 = 3 !Units used for point sourceemissions below (IPTU) Default: 1 ! IPTU = 1 !

1 = g/s2 = kg/hr3 = lb/hr4 = tons/yr5 = Odour Unit * m**3/s (vol. flux of odour compound)6 = Odour Unit * m**3/min7 = metric tons/yr

Number of source-speciescombinations with variableemissions scaling factorsprovided below in (13d) (NSPT1) Default: 0 ! NSPT1 = 0 !Number of point sources withvariable emission parametersprovided in external file (NPT2) No default ! NPT2 = 0 !(If NPT2 > 0, these pointsource emissions are read fromthe file: PTEMARB.DAT)

!END!---------------Subgroup (13b)---------------

29
INVCAM02.inp 

a

POINT SOURCE: CONSTANT DATA-----------------------------

b c

Source X Y Stack Base Stack Exit Exit Bldg. Emission

No. Coordinate Coordinate Height Elevation Diameter Vel. Temp. Dwash Rates

(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!

--------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.SRCNAM is a 12-character name for a source

(No default)

X is an array holding the source data listed by the column headings

(No default)

SIGYZI is an array holding the initial sigma-y and sigma-z (m)

(Default: 0.,0.)

ZPLTFM is the platform height (m) for sources influenced by an isolated

30
INVCAM02.inp 

structure that has a significant open area between the surfaceand the bulk of the structure, such as an offshore oil platform.The Base Elevation is that of the surface (ground or ocean),and the Stack Height is the release height above the Base (notabove the platform). Building heights entered in Subgroup 13cmust be those of the buildings on the platform, measured fromthe platform deck. ZPLTFM is used only with MBDW=1 (ISCdownwash method) for sources with building downwash.(Default: 0.0)

FMFAC is a vertical momentum flux factor (0. or 1.0) used to represent

the effect of rain-caps or other physical configurations thatreduce momentum rise associated with the actual exit velocity.(Default: 1.0 -- full momentum used)

b

0. = No building downwash modeled, 1. = downwash modeledNOTE: must be entered as a REAL number (i.e., with decimal point)

c

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by IPTU(e.g. 1 for g/s).

---------------Subgroup (13c)---------------

BUILDING DIMENSION DATA FOR SOURCES SUBJECT TO DOWNWASH-------------------------------------------------------

Source a

No. Effective building height, width, length and X/Y offset (in meters)

every 10 degrees. LENGTH, XBADJ, and YBADJ are only needed forMBDW=2 (PRIME downwash option)

------ ----------------------------------------------------------------------------

a

Building height, width, length, and X/Y offset from the source are treatedas a separate input subgroup for each source and therefore must end withan input group terminator. The X/Y offset is the position, relative to thestack, of the center of the upwind face of the projected building, with thex-axis pointing along the flow direction.

---------------Subgroup (13d)---------------

31
INVCAM02.inp 

a

POINT SOURCE: VARIABLE EMISSIONS DATA---------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 13b. Factors entered multiply the rates in 13b.Skip sources here that have constant emissions. For more elaboratevariation in source parameters, use PTEMARB.DAT and NPT2 > 0.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant1 = Diurnal cycle (24 scaling factors: hours 1-24)2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upperbounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUPS: 14a, 14b, 14c, 14d -- Area source parameters-----------------------------------------------Subgroup (14a)---------------

Number of polygon area sources withparameters specified below (NAR1) No default ! NAR1 = 0 !Units used for area sourceemissions below (IARU) Default: 1 ! IARU = 1 !

1 = g/m**2/s

32
INVCAM02.inp 

2 = kg/m**2/hr3 = lb/m**2/hr4 = tons/m**2/yr5 = Odour Unit * m/s (vol. flux/m**2 of odour compound)6 = Odour Unit * m/min7 = metric tons/m**2/yr

Number of source-speciescombinations with variableemissions scaling factorsprovided below in (14d) (NSAR1) Default: 0 ! NSAR1 = 0 !Number of buoyant polygon area sourceswith variable location and emissionparameters (NAR2) No default ! NAR2 = 0 !(If NAR2 > 0, ALL parameter data forthese sources are read from the file: BAEMARB.DAT)

!END!---------------Subgroup (14b)---------------

a

AREA SOURCE: CONSTANT DATA----------------------------

b

Source Effect. Base Initial Emission

No. Height Elevation Sigma z Rates

(m) (m) (m)

------- ------ ------ -------- -----------------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

b

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by IARU(e.g. 1 for g/m**2/s).

---------------Subgroup (14c)---------------

COORDINATES (km) FOR EACH VERTEX(4) OF EACH POLYGON--------------------------------------------------------

33
INVCAM02.inp 

Source a

No. Ordered list of X followed by list of Y, grouped by source

------ --------------------------------------------------------------------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

---------------Subgroup (14d)---------------

a

AREA SOURCE: VARIABLE EMISSIONS DATA--------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 14b. Factors entered multiply the rates in 14b.Skip sources here that have constant emissions. For more elaboratevariation in source parameters, use BAEMARB.DAT and NAR2 > 0.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant1 = Diurnal cycle (24 scaling factors: hours 1-24)2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upperbounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

-------------------------------------------------------------------------------

34
INVCAM02.inp 

INPUT GROUPS: 15a, 15b, 15c -- Line source parameters------------------------------------------Subgroup (15a)---------------

Number of buoyant line sourceswith variable location and emissionparameters (NLN2) No default ! NLN2 = 0 !(If NLN2 > 0, ALL parameter data for

these sources are read from the file: LNEMARB.DAT)

Number of buoyant line sources (NLINES) No default ! NLINES = 0 !Units used for line sourceemissions below (ILNU) Default: 1 ! ILNU = 1 !

1 = g/s2 = kg/hr3 = lb/hr4 = tons/yr5 = Odour Unit * m**3/s (vol. flux of odour compound)6 = Odour Unit * m**3/min7 = metric tons/yr

Number of source-speciescombinations with variableemissions scaling factorsprovided below in (15c) (NSLN1) Default: 0 ! NSLN1 = 0 !Maximum number of segments used to modeleach line (MXNSEG) Default: 7 ! MXNSEG = 7 !The following variables are required only if NLINES > 0. They areused in the buoyant line source plume rise calculations.

Number of distances at which Default: 6 ! NLRISE = 6 !transitional rise is computedAverage building length (XL) No default ! XL = .0 !

(in meters)

Average building height (HBL) No default ! HBL = .0 !

(in meters)

Average building width (WBL) No default ! WBL = .0 !

(in meters)

35
INVCAM02.inp 

Average line source width (WML) No default ! WML = .0 !

(in meters)

Average separation between buildings (DXL) No default ! DXL = .0 !

(in meters)

Average buoyancy parameter (FPRIMEL) No default ! FPRIMEL = .0 !

(in m**4/s**3)

!END!---------------Subgroup (15b)---------------

BUOYANT LINE SOURCE: CONSTANT DATA----------------------------------

Source Beg. X Beg. Y End. X End. Y Release Base Emission

No. Coordinate Coordinate Coordinate Coordinate Height Elevation Rates

(km) (km) (km) (km) (m) (m)

------ ---------- ---------- --------- ---------- ------- --------- -----------------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

b

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by ILNTU(e.g. 1 for g/s).

---------------Subgroup (15c)---------------

a

BUOYANT LINE SOURCE: VARIABLE EMISSIONS DATA----------------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 15b. Factors entered multiply the rates in 15b.Skip sources here that have constant emissions.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant

36
INVCAM02.inp 

1 = Diurnal cycle (24 scaling factors: hours 1-24)2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upperbounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUPS: 16a, 16b, 16c -- Volume source parameters------------------------------------------Subgroup (16a)---------------

Number of volume sources withparameters provided in 16b,c (NVL1) No default ! NVL1 = 0 !Units used for volume sourceemissions below in 16b (IVLU) Default: 1 ! IVLU = 1 !

1 = g/s2 = kg/hr3 = lb/hr4 = tons/yr5 = Odour Unit * m**3/s (vol. flux of odour compound)6 = Odour Unit * m**3/min7 = metric tons/yr

Number of source-speciescombinations with variableemissions scaling factorsprovided below in (16c) (NSVL1) Default: 0 ! NSVL1 = 0 !

37
INVCAM02.inp 

Number of volume sources withvariable location and emissionparameters (NVL2) No default ! NVL2 = 0 !(If NVL2 > 0, ALL parameter data for

these sources are read from the VOLEMARB.DAT file(s) )

!END!---------------Subgroup (16b)---------------

a

VOLUME SOURCE: CONSTANT DATA------------------------------

b

X Y Effect. Base Initial Initial Emission

Coordinate Coordinate Height Elevation Sigma y Sigma z Rates

(km) (km) (m) (m) (m) (m)

---------- ---------- ------ ------ -------- -------- --------

--------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

b

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by IVLU(e.g. 1 for g/s).

---------------Subgroup (16c)---------------

a

VOLUME SOURCE: VARIABLE EMISSIONS DATA----------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 16b. Factors entered multiply the rates in 16b.Skip sources here that have constant emissions. For more elaboratevariation in source parameters, use VOLEMARB.DAT and NVL2 > 0.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant1 = Diurnal cycle (24 scaling factors: hours 1-24)

38
INVCAM02.inp 

2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upperbounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUPS: 17a & 17b -- Non-gridded (discrete) receptor information--------------------------------------Subgroup (17a)---------------

Number of non-gridded receptors (NREC) No default ! NREC = 1076 !

!END!---------------Subgroup (17b)---------------

a

NON-GRIDDED (DISCRETE) RECEPTOR DATA------------------------------------

X Y Ground Height b

Receptor Coordinate Coordinate Elevation Above Ground

No. (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!

39
INVCAM02.inp 

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!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!

40
INVCAM02.inp 

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!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!

41
INVCAM02.inp 

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!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!

42
INVCAM02.inp 

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!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!

43
INVCAM02.inp 

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!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!

44
INVCAM02.inp 

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!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!

45
INVCAM02.inp 

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!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!

46
INVCAM02.inp 

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!382 ! 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!

47
INVCAM02.inp 

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!431 ! 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!

48
INVCAM02.inp 

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!480 ! 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!

49
INVCAM02.inp 

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!529 ! 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!

50
INVCAM02.inp 

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!578 ! 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!

51
INVCAM02.inp 

594 ! X = 1232.378, -392.029, 1170, 0.00 ! !END!595 ! X = 1233.861, -391.803, 1293, 0.00 ! !END!596 ! X = 1235.345, -391.576, 1077, 0.00 ! !END!597 ! X = 1236.829, -391.35, 953, 0.00 ! !END!598 ! X = 1238.312, -391.123, 1202, 0.00 ! !END!599 ! X = 1239.796, -390.895, 1602, 0.00 ! !END!600 ! X = 1241.279, -390.668, 1433, 0.00 ! !END!601 ! X = 1242.763, -390.44, 1106, 0.00 ! !END!602 ! X = 1244.246, -390.212, 966, 0.00 ! !END!603 ! X = 1245.73, -389.984, 1077, 0.00 ! !END!604 ! X = 1247.213, -389.755, 884, 0.00 ! !END!605 ! X = 1248.696, -389.526, 1096, 0.00 ! !END!606 ! X = 1174.216, -398.81, 459, 0.00 ! !END!607 ! X = 1175.701, -398.594, 516, 0.00 ! !END!608 ! X = 1177.185, -398.378, 579, 0.00 ! !END!609 ! X = 1178.67, -398.162, 576, 0.00 ! !END!610 ! X = 1180.155, -397.946, 656, 0.00 ! !END!611 ! X = 1181.64, -397.729, 718, 0.00 ! !END!612 ! X = 1183.125, -397.513, 760, 0.00 ! !END!613 ! X = 1184.609, -397.295, 994, 0.00 ! !END!614 ! X = 1187.579, -396.86, 782, 0.00 ! !END!615 ! X = 1189.063, -396.642, 618, 0.00 ! !END!616 ! X = 1190.548, -396.424, 489, 0.00 ! !END!617 ! X = 1192.033, -396.206, 549, 0.00 ! !END!618 ! X = 1193.517, -395.987, 598, 0.00 ! !END!619 ! X = 1195.001, -395.768, 577, 0.00 ! !END!620 ! X = 1196.486, -395.549, 809, 0.00 ! !END!621 ! X = 1197.97, -395.329, 899, 0.00 ! !END!622 ! X = 1199.455, -395.109, 1006, 0.00 ! !END!623 ! X = 1200.939, -394.889, 1262, 0.00 ! !END!624 ! X = 1202.423, -394.669, 988, 0.00 ! !END!625 ! X = 1203.907, -394.448, 1120, 0.00 ! !END!626 ! X = 1205.392, -394.227, 1054, 0.00 ! !END!627 ! X = 1206.876, -394.006, 860, 0.00 ! !END!628 ! X = 1208.36, -393.784, 1013, 0.00 ! !END!629 ! X = 1209.844, -393.563, 1203, 0.00 ! !END!630 ! X = 1211.328, -393.341, 1212, 0.00 ! !END!631 ! X = 1212.812, -393.118, 1380, 0.00 ! !END!632 ! X = 1214.296, -392.896, 1300, 0.00 ! !END!633 ! X = 1215.78, -392.673, 1206, 0.00 ! !END!634 ! X = 1217.263, -392.45, 1581, 0.00 ! !END!635 ! X = 1218.747, -392.227, 1457, 0.00 ! !END!636 ! X = 1220.231, -392.003, 1699, 0.00 ! !END!637 ! X = 1221.715, -391.779, 1543, 0.00 ! !END!638 ! X = 1223.198, -391.555, 1640, 0.00 ! !END!639 ! X = 1224.682, -391.33, 1476, 0.00 ! !END!640 ! X = 1226.166, -391.106, 1036, 0.00 ! !END!641 ! X = 1227.649, -390.881, 1315, 0.00 ! !END!642 ! X = 1229.133, -390.655, 1504, 0.00 ! !END!

52
INVCAM02.inp 

643 ! X = 1230.616, -390.43, 1469, 0.00 ! !END!644 ! X = 1232.1, -390.204, 1242, 0.00 ! !END!645 ! X = 1233.583, -389.978, 1453, 0.00 ! !END!646 ! X = 1235.066, -389.751, 1414, 0.00 ! !END!647 ! X = 1236.55, -389.525, 1012, 0.00 ! !END!648 ! X = 1238.033, -389.298, 1127, 0.00 ! !END!649 ! X = 1239.516, -389.071, 1352, 0.00 ! !END!650 ! X = 1240.999, -388.843, 1189, 0.00 ! !END!651 ! X = 1242.482, -388.615, 1257, 0.00 ! !END!652 ! X = 1243.965, -388.387, 1048, 0.00 ! !END!653 ! X = 1245.449, -388.159, 856, 0.00 ! !END!654 ! X = 1246.932, -387.931, 825, 0.00 ! !END!655 ! X = 1248.415, -387.702, 1060, 0.00 ! !END!656 ! X = 1249.897, -387.473, 1125, 0.00 ! !END!657 ! X = 1175.435, -396.767, 429, 0.00 ! !END!658 ! X = 1176.92, -396.551, 537, 0.00 ! !END!659 ! X = 1178.404, -396.335, 459, 0.00 ! !END!660 ! X = 1179.889, -396.119, 575, 0.00 ! !END!661 ! X = 1181.373, -395.903, 564, 0.00 ! !END!662 ! X = 1182.858, -395.686, 646, 0.00 ! !END!663 ! X = 1188.795, -394.816, 609, 0.00 ! !END!664 ! X = 1190.279, -394.598, 535, 0.00 ! !END!665 ! X = 1191.764, -394.379, 489, 0.00 ! !END!666 ! X = 1193.248, -394.161, 408, 0.00 ! !END!667 ! X = 1194.732, -393.942, 669, 0.00 ! !END!668 ! X = 1196.216, -393.722, 675, 0.00 ! !END!669 ! X = 1197.7, -393.503, 789, 0.00 ! !END!670 ! X = 1199.184, -393.283, 834, 0.00 ! !END!671 ! X = 1200.668, -393.063, 852, 0.00 ! !END!672 ! X = 1202.152, -392.843, 817, 0.00 ! !END!673 ! X = 1203.636, -392.622, 823, 0.00 ! !END!674 ! X = 1205.12, -392.401, 750, 0.00 ! !END!675 ! X = 1206.603, -392.18, 930, 0.00 ! !END!676 ! X = 1208.087, -391.959, 1127, 0.00 ! !END!677 ! X = 1209.571, -391.737, 726, 0.00 ! !END!678 ! X = 1211.054, -391.515, 1065, 0.00 ! !END!679 ! X = 1212.538, -391.293, 1323, 0.00 ! !END!680 ! X = 1214.022, -391.07, 1448, 0.00 ! !END!681 ! X = 1215.505, -390.847, 1548, 0.00 ! !END!682 ! X = 1216.989, -390.624, 1772, 0.00 ! !END!683 ! X = 1218.472, -390.401, 1416, 0.00 ! !END!684 ! X = 1219.956, -390.177, 1198, 0.00 ! !END!685 ! X = 1221.439, -389.954, 1225, 0.00 ! !END!686 ! X = 1222.922, -389.729, 1580, 0.00 ! !END!687 ! X = 1224.406, -389.505, 1529, 0.00 ! !END!688 ! X = 1225.889, -389.28, 1165, 0.00 ! !END!689 ! X = 1227.372, -389.055, 1418, 0.00 ! !END!690 ! X = 1228.855, -388.83, 1635, 0.00 ! !END!691 ! X = 1230.338, -388.605, 1459, 0.00 ! !END!

53
INVCAM02.inp 

692 ! X = 1231.822, -388.379, 1310, 0.00 ! !END!693 ! X = 1233.305, -388.153, 1441, 0.00 ! !END!694 ! X = 1234.788, -387.926, 1391, 0.00 ! !END!695 ! X = 1236.271, -387.7, 1337, 0.00 ! !END!696 ! X = 1237.754, -387.473, 1455, 0.00 ! !END!697 ! X = 1239.236, -387.246, 1336, 0.00 ! !END!698 ! X = 1240.719, -387.018, 1223, 0.00 ! !END!699 ! X = 1242.202, -386.791, 1226, 0.00 ! !END!700 ! X = 1243.685, -386.563, 979, 0.00 ! !END!701 ! X = 1245.168, -386.335, 1079, 0.00 ! !END!702 ! X = 1246.65, -386.106, 1104, 0.00 ! !END!703 ! X = 1248.133, -385.877, 858, 0.00 ! !END!704 ! X = 1249.615, -385.648, 1030, 0.00 ! !END!705 ! X = 1178.138, -394.509, 475, 0.00 ! !END!706 ! X = 1179.623, -394.292, 440, 0.00 ! !END!707 ! X = 1181.107, -394.076, 640, 0.00 ! !END!708 ! X = 1191.495, -392.553, 369, 0.00 ! !END!709 ! X = 1192.978, -392.334, 478, 0.00 ! !END!710 ! X = 1194.462, -392.115, 570, 0.00 ! !END!711 ! X = 1195.946, -391.896, 552, 0.00 ! !END!712 ! X = 1197.43, -391.677, 843, 0.00 ! !END!713 ! X = 1198.913, -391.457, 604, 0.00 ! !END!714 ! X = 1200.397, -391.237, 605, 0.00 ! !END!715 ! X = 1201.881, -391.017, 652, 0.00 ! !END!716 ! X = 1203.364, -390.796, 770, 0.00 ! !END!717 ! X = 1204.848, -390.575, 834, 0.00 ! !END!718 ! X = 1206.331, -390.354, 725, 0.00 ! !END!719 ! X = 1207.814, -390.133, 608, 0.00 ! !END!720 ! X = 1209.298, -389.911, 656, 0.00 ! !END!721 ! X = 1210.781, -389.689, 1126, 0.00 ! !END!722 ! X = 1212.264, -389.467, 1115, 0.00 ! !END!723 ! X = 1213.748, -389.245, 1387, 0.00 ! !END!724 ! X = 1215.231, -389.022, 1569, 0.00 ! !END!725 ! 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!

54
INVCAM02.inp 

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!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!

55
INVCAM02.inp 

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!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!

56
INVCAM02.inp 

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!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!

57
INVCAM02.inp 

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!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!

58
INVCAM02.inp 

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!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!

59
INVCAM02.inp 

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!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!

60
INVCAM02.inp 

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!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!-------------

a

Data for each receptor are treated as a separate input subgroupand therefore must end with an input group terminator.

61
INVCAM02.inp 

b

Receptor height above ground is optional. If no value is entered,the receptor is placed on the ground.

62
INVISTA Camden Plant B - 4 Trinity Consultants 

BART Applicability Modeling Analysis 

SAMPLE POSTUTIL INPUT FILE

UTINVCAM02.INP 

12-KM SCREENING ANALYSIS YEAR 2002 

Appendix H.6 - 694
UTINVCAM02.inp 

INVISTA CAMDEN - Combine PM SpeciesBART ANALYSIS 12 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 UPDATED 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

POSTUTIL MODEL CONTROL FILE---------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names---------------------------Subgroup (0a)-------------Output Files------------

File Default File Name---- -----------------List File POSTUTIL.LST ! UTLLST =UTINVCAM02.lst !Data File MODEL.DAT ! UTLDAT =UTINVCAM02.con !

Input Files-----------

Meteorological data files are needed for the HNO3/NO3 partition option.The met data file is the 'CALMET.DAT' format file used in the CALPUFFsimulation. If multiple CALMET files had been used in sequence, youmay list all of these files in subgroup 0b. Specify the total numberof CALMET files runs you need to use, and provide the filename for eachin subgroup 0b.

Number of CALMET data files (NFILES)

Default: 0 ! NMET = 0 !

A number of CALPUFF data files may be processed in this application.The files may represent individual CALPUFF simulations that were madefor a specific set of species and/or sources. Specify the total numberof CALPUFF runs you wish to combine, and provide the filename for eachin subgroup 0b.

Number of CALPUFF data files (NFILES)

Default: 1 ! NFILES = 1 !

1
UTINVCAM02.inp 

All filenames will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, filenames will be converted to UPPER CASE

Convert filenames to lower case? Default: T ! LCFILES = T !

T = lower caseF = UPPER CASE

!END!-----------------------------------------------------------

NOTE: file/path names can be up to 70 characters in length

------------------------------------------------------------------------Subgroup (0b)-------------NMET CALMET Data Files:Input File Default File Name---------- -----------------

1 MET.DAT * UTLMET =CALMET.DAT *

Input File Default File Name---------- -----------------

1 CALPUFF.DAT ! MODDAT =INVCAM02.con ! !END!

-------------Note: provide NMET lines of the form * UTLMET = name * *END*

and NFILES lines of the form * MODDAT = name * *END*where the * should be replaced with an exclamation point,the special delimiter character.

--------------------------------------------------------------------------------INPUT GROUP: 1 -- General run control parameters--------------

Starting date: Year (ISYR) -- No default ! ISYR = 2002 !

Month (ISMO) -- No default ! ISMO = 1 !Day (ISDY) -- No default ! ISDY = 1 !Hour (ISHR) -- No default ! ISHR = 1 !

Number of periods to process

(NPER) -- No default ! NPER = 8760 !

2
UTINVCAM02.inp 

Number of species to process from CALPUFF runs

(NSPECINP) -- No default ! NSPECINP = 19 !

Number of species to write to output file

(NSPECOUT) -- No default ! NSPECOUT = 9 !

Number of species to compute from those modeled(must be no greater than NSPECOUT)

(NSPECCMP) -- No default ! NSPECCMP = 4 !

When multiple files are used, a species name may appear in more thanone file. Data for this species will be summed (appropriate if theCALPUFF runs use different source groups). If this summing is notappropriate, remove duplicate species from the file(s).

Stop run if duplicate species namesare found? (MDUPLCT) Default: 0 ! MDUPLCT = 0 !

0 = no (i.e., duplicate species are summed)1 = yes (i.e., run is halted)

Data for each species in a CALPUFF data file may also be scaled asthey are read. This can be done to alter the emission rate of allsources that were modeled in a particular CALPUFF application.The scaling factor for each species is entered in Subgroup (2d), foreach file for which scaling is requested.

Number of CALPUFF data files that will be scaled(must be no greater than NFILES)(NSCALED) Default: 0 ! NSCALED = 0 !

Option to recompute the HNO3/NO3 concentration partition prior toperforming other actions. This option will NOT alter any depositionfluxes contained in the CALPUFF file(s). Two partition selectionsare provided. The first (MNITRATE=1) computes the partition for theTOTAL (all sources) concentration fields (SO4, NO3, HNO3; NH3), andthe second (MNITRATE=2) uses this partition (from a previous applicationof POSTUTIL) to compute the partition for individual source groups.Required information for MNITRATE=1 includes:

species NO3, HNO3, and SO4NH3 concentration(s)met. data file for RH and T

Required information for MNITRATE=2 includes:

species NO3 and HNO3 for a source groupspecies NO3ALL and HNO3ALL for all source groups, properly

3
UTINVCAM02.inp 

partitioned

Recompute the HNO3/NO3 partition for concentrations?(MNITRATE) Default: 0 ! MNITRATE = 0 !

0 = no1 = yes, for all sources combined2 = yes, for a source group

Ammonia concentrations may be available as a modeled species inthe CALPUFF files. When NH3 is listed as a processed species inSubgroup (2a) (as one of the NSPECINP ASPECI entries), themodeled values will be used in the chemical equilibrium calculation.If NH3 is not on this list, the default monthly background valueslisted below will be used. If a single value is entered, this isused for all 12 months. Month 1 is JANUARY, Month 12 is DECEMBER.Default ammonia concentration (ppb) used for HNO3/NO3 partition:(BCKNH3) in ppb Default: 12*10.! BCKNH3 =12*0.5 !

!END!-------------------------------------------------------------------------------INPUT GROUP: 2 -- Species Processing Information---------------------------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!

4
UTINVCAM02.inp 

-------------Subgroup (2b)-------------

The following NSPECOUT species will be written:

! 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)-------------

The following NSPECCMP species will be computed by scaling and summingone or more of the processed input species. Identify the name(s) ofthe computed species and provide the scaling factors for each of theNSPECINP input species (NSPECCMP groups of NSPECINP+1 lines each):

! 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 !

5
UTINVCAM02.inp 

!END!-------------Subgroup (2d)-------------

Each species in NSCALED CALPUFF data files may be scaled before beingprocessed (e.g., to change the emission rate for all sources modeledin the run that produced a data file). For each file, identify thefile name and then provide the name(s) of the scaled species and thecorresponding scaling factors (A,B where x' = 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 ANALYSIS YEAR 2002 

CAPE ROMAIN ANNUAL AVERAGE NATURAL BACKGROUND 

Appendix H.6 - 701
VANINVCAM02CR.inp 

INVISTA CAMDEN - Visibility with Annual Background CAPE ROMAINBART SCREENING ANALYSIS 12 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 UPDATED 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

CALPOST MODEL CONTROL FILE--------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names--------------Input Files-----------File Default File Name---- -----------------Conc/Dep Flux File MODEL.DAT ! MODDAT =UTINVCAM02.con !Relative Humidity File VISB.DAT * VISDAT = *Background Data File BACK.DAT * BACKDAT = *Transmissometer or VSRN.DAT * VSRDAT = *Nephelometer Data File orDATSAV Weather Data File orPrognostic Weather FileOutput Files------------File Default File Name---- -----------------List File CALPOST.LST ! PSTLST =VANINVCAM02CR.lst !Pathname for Timeseries Files (blank) * TSPATH = *(activate with exclamation points only ifproviding NON-BLANK character string)Pathname for Plot Files (blank) * PLPATH = *(activate with exclamation points only if

providing NON-BLANK character string)

User Character String (U) to augment default filenames(activate with exclamation points only if

providing NON-BLANK character string)

Timeseries TSERIES_ASPEC_ttHR_CONC_TSUNAM.DATPeak Value PEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DAT

* TSUNAM = *

1
VANINVCAM02CR.inp 

Top Nth Rank Plot RANK(ALL)_ASPEC_ttHR_CONC_TUNAM.DAT

or RANK(ii)_ASPEC_ttHR_CONC_TUNAM.GRD

* TUNAM = *

Exceedance Plot EXCEED_ASPEC_ttHR_CONC_XUNAM.DAT

or EXCEED_ASPEC_ttHR_CONC_XUNAM.GRD

* XUNAM = *

Echo Plot(Specific Days)

yyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.DAT

or yyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.GRD

Visibility Plot DAILY_VISIB_VUNAM.DAT * VUNAM = *(Daily Peak Summary)Auxiliary Output Files----------------------File Default File Name---- -----------------Visibility Change DELVIS.DAT * DVISDAT = *--------------------------------------------------------------------------------All file names will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, file names will be converted to UPPER CASE

T = lower case ! LCFILES = T !F = UPPER CASE

NOTE: (1) file/path names can be up to 132 characters in lengthNOTE: (2) Filenames for ALL PLOT and TIMESERIES FILES are constructed

using a template that includes a pathname, user-suppliedcharacter(s), and context-specific strings, where

ASPEC = Species Name

CONC = CONC Or WFLX Or DFLX Or TFLX

tt = Averaging Period (e.g. 03)ii = Rank (e.g. 02)hh = Hour(ending) in LST

szzzz = Base time zone shift from UTC (EST is -0500)

yyyy = Year(LST)

mm = Month(LST)dd = day of month (LST)

are determined internally based on selections made below.If a path or user-supplied character(s) are supplied, each

2
VANINVCAM02CR.inp 

must contain at least 1 non-blank character.

!END!--------------------------------------------------------------------------------INPUT GROUP: 1 -- General run control parameters--------------

Option to run all periods foundin the met. file(s) (METRUN) Default: 0 ! METRUN = 0 !

METRUN = 0 - Run period explicitly defined belowMETRUN = 1 - Run all periods in CALPUFF data file(s)

Starting date: Year (ISYR) -- No default ! ISYR = 2002 !(used only if Month (ISMO) -- No default ! ISMO = 1 !

METRUN = 0) Day (ISDY) -- No default ! ISDY = 1 !

Hour (ISHR) -- No default ! ISHR = 1 !

Number of hours to process (NHRS) -- No default ! NHRS = 8760 !Process every hour of data?(NREP) -- Default: 1 ! NREP = 1 !

(1 = every hour processed,

2 = every 2nd hour processed,5 = every 5th hour processed, etc.)

Species & Concentration/Deposition Information----------------------------------------------

Species to process (ASPEC) -- No default ! ASPEC = VISIB !(ASPEC = VISIB for visibility processing)Layer/deposition code (ILAYER) -- Default: 1 ! ILAYER = 1 !

'1' for CALPUFF concentrations,'-1' for dry deposition fluxes,'-2' for wet deposition fluxes,'-3' for wet+dry deposition fluxes.

Scaling factors of the form: -- Defaults: ! A = 0.0 !

X(new) = X(old) * A + B A = 0.0 ! B = 0.0 !

(NOT applied if A = B = 0.0) B = 0.0

Add Hourly Background Concentrations/Fluxes?

(LBACK) -- Default: F ! LBACK = F !

Source information------------------

Option to process source contributions:

3
VANINVCAM02CR.inp 

0 = Process only total reported contributions1 = Sum all individual source contributions and process2 = Run in TRACEBACK mode to identify source

contributions at a SINGLE receptor

(MSOURCE) -- Default: 0 ! MSOURCE = 0 !

Receptor information--------------------

Gridded receptors processed? (LG) -- Default: F ! LG = F !Discrete receptors processed? (LD) -- Default: F ! LD = T !CTSG Complex terrain receptors processed?

(LCT) -- Default: F ! LCT = F !

--Report results by DISCRETE receptor RING?

(only used when LD = T) (LDRING) -- Default: F ! LDRING = F !

--Select range of DISCRETE receptors (only used when LD = T):

Select ALL DISCRETE receptors by setting NDRECP flag to -1;

OR

Select SPECIFIC DISCRETE receptors by entering a flag (0,1) for each

0 = discrete receptor not processed1 = discrete receptor processed

using repeated value notation to select blocks of receptors:Flag for all receptors after the last one assigned is set to 0(NDRECP) -- Default: -1

! NDRECP = 164*1, 736*0, 66*0, 110*0 !

--Select range of GRIDDED receptors (only used when LG = T):

X index of LL corner (IBGRID) -- Default: -1 ! IBGRID = -1 !

(-1 OR 1 <= IBGRID <= NX)

Y index of LL corner (JBGRID) -- Default: -1 ! JBGRID = -1 !

(-1 OR 1 <= JBGRID <= NY)

X index of UR corner (IEGRID) -- Default: -1 ! IEGRID = -1 !

(-1 OR 1 <= IEGRID <= NX)

Y index of UR corner (JEGRID) -- Default: -1 ! JEGRID = -1 !

(-1 OR 1 <= JEGRID <= NY)

Note: Entire grid is processed if IBGRID=JBGRID=IEGRID=JEGRID=-1

--Specific gridded receptors can also be excluded from CALPOST

4
VANINVCAM02CR.inp 

processing by filling a processing grid array with 0s and 1s. If theprocessing flag for receptor index (i,j) is 1 (ON), that receptorwill be processed if it lies within the range delineated by IBGRID,JBGRID,IEGRID,JEGRID and if LG=T. If it is 0 (OFF), it will not beprocessed in the run. By default, all array values are set to 1 (ON).Number of gridded receptor rows provided in Subgroup (1a) toidentify specific gridded receptors to process

(NGONOFF) -- Default: 0 ! NGONOFF = 0 !

!END!--------------Subgroup (1a) -- Specific gridded receptors included/excluded--------------

Specific gridded receptors are excluded from CALPOST processingby filling a processing grid array with 0s and 1s. A total ofNGONOFF lines are read here. Each line corresponds to one 'row'in the sampling grid, starting with the NORTHERNMOST row thatcontains receptors that you wish to exclude, and finishing withrow 1 to the SOUTH (no intervening rows may be skipped). Withina row, each receptor position is assigned either a 0 or 1,starting with the westernmost receptor.

0 = gridded receptor not processed1 = gridded receptor processed

Repeated value notation may be used to select blocks of receptors:

23*1, 15*0, 12*1

Because all values are initially set to 1, any receptors north ofthe first row entered, or east of the last value provided in a row,remain ON.(NGXRECP) -- Default: 1

-------------------------------------------------------------------------------INPUT GROUP: 2 -- Visibility Parameters (ASPEC = VISIB)--------------

Identify the Base Time Zone for the CALPUFF simulation

(BTZONE) -- No default ! BTZONE = 5.0 !

Particle growth curve f(RH) for hygroscopic species

(MFRH) -- Default: 2 ! MFRH = 2 !

5
VANINVCAM02CR.inp 

1 = IWAQM (1998) f(RH) curve (originally used with MVISBK=1)2 = FLAG (2000) f(RH) tabulation3 = EPA (2003) f(RH) tabulation

Maximum relative humidity (%) used in particle growth curve

(RHMAX) -- Default: 98 ! RHMAX = 95.0 !

Modeled species to be included in computing the light extinction

Include SULFATE? (LVSO4) -- Default: T ! LVSO4 = T !Include NITRATE? (LVNO3) -- Default: T ! LVNO3 = T !Include ORGANIC CARBON? (LVOC) -- Default: T ! LVOC = T !Include COARSE PARTICLES? (LVPMC) -- Default: T ! LVPMC = T !Include FINE PARTICLES? (LVPMF) -- Default: T ! LVPMF = T !Include ELEMENTAL CARBON? (LVEC) -- Default: T ! LVEC = T !

And, when ranking for TOP-N, TOP-50, and Exceedance tables,

Include BACKGROUND? (LVBK) -- Default: T ! LVBK = T !

Species name used for particulates in MODEL.DAT file

COARSE (SPECPMC) -- Default: PMC ! SPECPMC = PMC !FINE (SPECPMF) -- Default: PMF ! SPECPMF = SOIL !

Extinction Efficiency (1/Mm per ug/m**3)----------------------------------------

MODELED particulate species:

PM COARSE (EEPMC) -- Default: 0.6 ! EEPMC = 0.6 !PM FINE (EEPMF) -- Default: 1.0 ! EEPMF = 1.0 !

BACKGROUND particulate species:

PM COARSE (EEPMCBK) -- Default: 0.6 ! EEPMCBK = 0.6 !

Other species:

AMMONIUM SULFATE (EESO4) -- Default: 3.0 ! EESO4 = 3.0 !AMMONIUM NITRATE (EENO3) -- Default: 3.0 ! EENO3 = 3.0 !ORGANIC CARBON (EEOC) -- Default: 4.0 ! EEOC = 4.0 !SOIL (EESOIL)-- Default: 1.0 ! EESOIL = 1.0 !ELEMENTAL CARBON (EEEC) -- Default: 10. ! EEEC = 10.0 !

Background Extinction Computation---------------------------------

Method used for the 24h-average of percent change of light extinction:Hourly ratio of source light extinction / background light extinctionis averaged? (LAVER) -- Default: F ! LAVER = F !Method used for background light extinction

(MVISBK) -- Default: 2 ! MVISBK = 6 !

1 = Supply single light extinction and hygroscopic fraction

- Hourly F(RH) adjustment applied to hygroscopic background

6
VANINVCAM02CR.inp 

and modeled sulfate and nitrate

2 = Compute extinction from speciated PM measurements (A)

- Hourly F(RH) adjustment applied to observed and modeled sulfate

and nitrate

- F(RH) factor is capped at F(RHMAX)

3 = Compute extinction from speciated PM measurements (B)

- Hourly F(RH) adjustment applied to observed and modeled sulfate

and nitrate

- Receptor-hour excluded if RH>RHMAX- Receptor-day excluded if fewer than 6 valid receptor-hours

4 = Read hourly transmissometer background extinction measurements

- Hourly F(RH) adjustment applied to modeled sulfate and nitrate- Hour excluded if measurement invalid (missing, interference,

or large RH)

- Receptor-hour excluded if RH>RHMAX- Receptor-day excluded if fewer than 6 valid receptor-hours

5 = Read hourly nephelometer background extinction measurements

- Rayleigh extinction value (BEXTRAY) added to measurement- Hourly F(RH) adjustment applied to modeled sulfate and nitrate- Hour excluded if measurement invalid (missing, interference,

or large RH)

- Receptor-hour excluded if RH>RHMAX- Receptor-day excluded if fewer than 6 valid receptor-hours

6 = Compute extinction from speciated PM measurements

- FLAG monthly RH adjustment factor applied to observed and

modeled sulfate and nitrate

7 = Use observed weather or prognostic weather information for

background extinction during weather events; otherwise, use Method 2- Hourly F(RH) adjustment applied to modeled sulfate and nitrate- F(RH) factor is capped at F(RHMAX)- During observed weather events, compute Bext from visual range

if using an observed weather data file, or

- During prognostic weather events, use Bext from the prognostic

weather file

- Use Method 2 for hours without a weather event

Additional inputs used for MVISBK = 1:--------------------------------------

Background light extinction (1/Mm)

(BEXTBK) -- No default ! BEXTBK = 0.0 !

Percentage of particles affected by relative humidity

(RHFRAC) -- No default ! RHFRAC = 0.0 !

Additional inputs used for MVISBK = 6:--------------------------------------

Extinction coefficients for hygroscopic species (modeled andbackground) are computed using a monthly RH adjustment factorin place of an hourly RH factor (VISB.DAT file is NOT needed).Enter the 12 monthly factors here (RHFAC). Month 1 is January.

7
VANINVCAM02CR.inp 

(RHFAC) -- No default ! 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 !

Additional inputs used for MVISBK = 7:--------------------------------------

The weather data file (DATSAV abbreviated space-delimited) thatis identified as VSRN.DAT may contain data for more than onestation. Identify the stations that are needed in the order inwhich they will be used to obtain valid weather and visual range.The first station that contains valid data for an hour will beused. Enter up to MXWSTA (set in PARAMS file) integer station IDsof up to 6 digits each as variable IDWSTA, and enter the correspondingtime zone for each, as variable TZONE (= UTC-LST).A prognostic weather data file with Bext for weather events may be usedin place of the observed weather file. Identify this as the VSRN.DATfile and use a station ID of IDWSTA = 999999, and TZONE = 0.NOTE: TZONE identifies the time zone used in the dataset. The

DATSAV abbreviated space-delimited data usually are preparedwith UTC time rather than local time, so TZONE is typicallyset to zero.

(IDWSTA) -- No default

! IDWSTA = 999999 !

(TZONE) -- No default

! TZONE = 0.0 !Additional inputs used for MVISBK = 2,3,6,7:--------------------------------------------

Background extinction coefficients are computed from monthlyCONCENTRATIONS of ammonium sulfate (BKSO4), ammonium nitrate (BKNO3),coarse particulates (BKPMC), organic carbon (BKOC), soil (BKSOIL), andelemental carbon (BKEC). Month 1 is January.(ug/m**3)

(BKSO4) -- No default ! 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) -- No default ! 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) -- No default ! 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) -- No default ! BKOC = 0.00, 0.00, 0.00, 0.00,

0.00, 0.00, 0.00, 0.00,

8
VANINVCAM02CR.inp 

0.00, 0.00, 0.00, 0.00 !

(BKSOIL) -- No default ! 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) -- No default ! 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 !

Additional inputs used for MVISBK = 2,3,5,6,7:----------------------------------------------

Extinction due to Rayleigh scattering is added (1/Mm)

(BEXTRAY) -- Default: 10.0 ! BEXTRAY = 10.0 !

!END!-------------------------------------------------------------------------------INPUT GROUP: 3 -- Output options--------------Documentation-------------

Documentation records contained in the header of theCALPUFF output file may be written to the list file.Print documentation image?

(LDOC) -- Default: F ! LDOC = F !

Output Units------------

Units for All Output (IPRTU) -- Default: 1 ! IPRTU = 3 !

for for

Concentration Deposition

1 = g/m**3 g/m**2/s2 = mg/m**3 mg/m**2/s3 = ug/m**3 ug/m**2/s4 = ng/m**3 ng/m**2/s5 = Odour Units

Visibility: extinction expressed in 1/Mega-meters (IPRTU is ignored)

Averaging time(s) reported--------------------------

1-hr averages (L1HR) -- Default: T ! L1HR = F !3-hr averages (L3HR) -- Default: T ! L3HR = F !24-hr averages (L24HR) -- Default: T ! L24HR = T !

9
VANINVCAM02CR.inp 

Run-length averages (LRUNL) -- Default: T ! LRUNL = F !User-specified averaging time in hours - results foran averaging time of NAVG hours are reported forNAVG greater than 0:

(NAVG) -- Default: 0 ! NAVG = 0 !

Types of tabulations reported------------------------------

1) Visibility: daily visibility tabulations are always reported

for the selected receptors when ASPEC = VISIB.In addition, any of the other tabulations listedbelow may be chosen to characterize the lightextinction coefficients.[List file or Plot/Analysis File]

2) Top 50 table for each averaging time selected

[List file only]

(LT50) -- Default: T ! LT50 = F !

3) Top 'N' table for each averaging time selected

[List file or Plot file]

(LTOPN) -- Default: F ! LTOPN = T !

-- Number of 'Top-N' values at each receptor

selected (NTOP must be <= 4)

(NTOP) -- Default: 4 ! NTOP = 1 !

-- Specific ranks of 'Top-N' values reported

(NTOP values must be entered)

(ITOP(4) array) -- Default: ! ITOP = 1 !

1,2,3,4

4) Threshold exceedance counts for each receptor and each averaging

time selected[List file or Plot file]

(LEXCD) -- Default: F ! LEXCD = F !

-- Identify the threshold for each averaging time by assigning a

non-negative value (output units).

-- Default: -1.0

Threshold for 1-hr averages (THRESH1) ! THRESH1 = -1.0 !Threshold for 3-hr averages (THRESH3) ! THRESH3 = -1.0 !

10
VANINVCAM02CR.inp 

Threshold for 24-hr averages (THRESH24) ! THRESH24 = -1.0 !Threshold for NAVG-hr averages (THRESHN) ! THRESHN = -1.0 !

-- Counts for the shortest averaging period selected can be

tallied daily, and receptors that experience more than NCOUNTcounts over any NDAY period will be reported. This type ofexceedance violation output is triggered only if NDAY > 0.Accumulation period(Days)

(NDAY) -- Default: 0 ! NDAY = 0 !

Number of exceedances allowed

(NCOUNT) -- Default: 1 ! NCOUNT = 1 !

5) Selected day table(s)

Echo Option -- Many records are written each averaging periodselected and output is grouped by day[List file or Plot file]

(LECHO) -- Default: F ! LECHO = F !

Timeseries Option -- Averages at all selected receptors foreach selected averaging period are written to timeseries files.Each file contains one averaging period, and all receptors arewritten to a single record each averaging time.[TSERIES_ASPEC_ttHR_CONC_TSUNAM.DAT files]

(LTIME) -- Default: F ! LTIME = F !

Peak Value Option -- Averages at all selected receptors foreach selected averaging period are screened and the peak valueeach period is written to timeseries files.Each file contains one averaging period.[PEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DAT files]

(LPEAK) -- Default: F ! LPEAK = F !

-- Days selected for output

(IECHO(366)) -- Default: 366*0

! IECHO = 366*0 !(366 values must be entered)

Plot output options-------------------

Plot files can be created for the Top-N, Exceedance, and Echotables selected above. Two formats for these files are available,DATA and GRID. In the DATA format, results at all receptors arelisted along with the receptor location [x,y,val1,val2,...].In the GRID format, results at only gridded receptors are written,

11
VANINVCAM02CR.inp 

using a compact representation. The gridded values are written inrows (x varies), starting with the most southern row of the grid.The GRID format is given the .GRD extension, and includes headerscompatible with the SURFER(R) plotting software.A plotting and analysis file can also be created for the dailypeak visibility summary output, in DATA format only.Generate Plot file output in addition to writing tablesto List file?

(LPLT) -- Default: F ! LPLT = F !

Use GRID format rather than DATA format,when available?

(LGRD) -- Default: F ! LGRD = F !

Auxiliary Output Files (for subsequent analyses)------------------------------------------------

VisibilityA separate output file may be requested that contains the changein visibility at each selected receptor when ASPEC = VISIB. Thisfile can be processed to construct visibility measures that arenot available in CALPOST.Output file with the visibility change at each receptor?

(MDVIS) -- Default: 0 ! MDVIS = 1 !

0 = Do Not create file1 = Create file of DAILY (24 hour) Delta-Deciview2 = Create file of DAILY (24 hour) Extinction Change (%)3 = Create file of HOURLY Delta-Deciview4 = Create file of HOURLY Extinction Change (%)

Additional Debug Output-----------------------

Output selected information to List file

for debugging?

(LDEBUG) -- Default: F ! LDEBUG = F !

Output hourly extinction information to REPORT.HRV?

(Visibility Method 7)

(LVEXTHR) -- Default: F ! LVEXTHR = F !

!END!

12
VANINVCAM02CR.inp 

13
INVISTA Camden Plant B - 6 Trinity Consultants 

BART Applicability Modeling Analysis 

CALPUFF BATCH PROCESSING FILE

4-KM REFINED ANALYSES 

Appendix H.6 - 715
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

Appendix H.6 - 716
INVISTA Camden Plant B - 7 Trinity Consultants 

BART Applicability Modeling Analysis 

SAMPLE CALPUFF INPUT FILE

INVCAM02.INP 

4-KM REFINED ANALYSIS YEAR 2002 

Appendix H.6 - 717
INVCAM02.inp 

INVISTA CAMDENBART REFINED ANALYSIS 4 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 Update 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

CALPUFF MODEL CONTROL FILE--------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names--------------Default Name Type File Name------------ ---- ---------CALMET.DAT input * METDAT = *

or

ISCMET.DAT input * ISCDAT = *

or

PLMMET.DAT input * PLMDAT = *

or

PROFILE.DAT input * PRFDAT = *SURFACE.DAT input * SFCDAT = *RESTARTB.DAT input * RSTARTB= *--------------------------------------------------------------------------------CALPUFF.LST output ! PUFLST =INVCAM02.lst !CONC.DAT output ! CONDAT =INVCAM02.con !DFLX.DAT output * DFDAT =puff2002-sm.dry *WFLX.DAT output * WFDAT =puff2002-sm.wet *VISB.DAT output * VISDAT =puff2002-sm.vis *RESTARTE.DAT output * RSTARTE=puff2002-sm.res *--------------------------------------------------------------------------------Emission Files--------------PTEMARB.DAT input * PTDAT = *VOLEMARB.DAT input * VOLDAT = *BAEMARB.DAT input * ARDAT = *LNEMARB.DAT input * LNDAT = *--------------------------------------------------------------------------------Other Files-----------OZONE.DAT input ! OZDAT =OZCAM02.dat !VD.DAT input * VDDAT = *CHEM.DAT input * CHEMDAT= *H2O2.DAT input * H2O2DAT= *HILL.DAT input * HILDAT= *HILLRCT.DAT input * RCTDAT= *COASTLN.DAT input * CSTDAT= *

1
INVCAM02.inp 

FLUXBDY.DAT input * BDYDAT= *BCON.DAT input * BCNDAT= *DEBUG.DAT output * DEBUG = *MASSFLX.DAT output * FLXDAT= *MASSBAL.DAT output * BALDAT= *FOG.DAT output * FOGDAT= *--------------------------------------------------------------------------------All file names will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, file names will be converted to UPPER CASE

T = lower case ! LCFILES = T !F = UPPER CASE

NOTE: (1) file/path names can be up to 70 characters in lengthProvision for multiple input files----------------------------------

Number of CALMET.DAT files for run (NMETDAT)

Default: 1 ! NMETDAT = 36 !

Number of PTEMARB.DAT files for run (NPTDAT)

Default: 0 ! NPTDAT = 0 !

Number of BAEMARB.DAT files for run (NARDAT)

Default: 0 ! NARDAT = 0 !

Number of VOLEMARB.DAT files for run (NVOLDAT)

Default: 0 ! NVOLDAT = 0 !

!END!-------------Subgroup (0a)-------------

The following CALMET.DAT filenames are processed in sequence if NMETDAT>1

Default Name Type File Name------------ ---- ---------

none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-01a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-01b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-01c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-02a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-02b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-02c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-03a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-03b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-03c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-04a.DAT ! !END!

2
INVCAM02.inp 

none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-04b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-04c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-05a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-05b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-05c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-06a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-06b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-06c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-07a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-07b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-07c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-08a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-08b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-08c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-09a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-09b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-09c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-10a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-10b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-10c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-11a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-11b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-11c.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-12a.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-12b.DAT ! !END!none input ! METDAT=T:\VISTAS\Domain4-2002\met2002-dom4-12c.DAT ! !END!

INPUT GROUP: 1 -- General run control parameters--------------

Option to run all periods foundin the met. file (METRUN) Default: 0 ! METRUN = 0 !

METRUN = 0 - Run period explicitly defined belowMETRUN = 1 - Run all periods in met. file

Starting date: Year (IBYR) -- No default ! IBYR = 2002 !(used only if Month (IBMO) -- No default ! IBMO = 1 !

METRUN = 0) Day (IBDY) -- No default ! IBDY = 1 !

Hour (IBHR) -- No default ! IBHR = 1 !

Base time zone (XBTZ) -- No default ! XBTZ = 5.0 !

PST = 8., MST = 7.CST = 6., EST = 5.

Length of run (hours) (IRLG) -- No default ! IRLG = 8760 !Number of chemical species (NSPEC)

Default: 5 ! NSPEC = 19 !

3
INVCAM02.inp 

Number of chemical speciesto be emitted (NSE) Default: 3 ! NSE = 17 !Flag to stop run afterSETUP phase (ITEST) Default: 2 ! ITEST = 2 !(Used to allow checkingof the model inputs, files, etc.)

ITEST = 1 - STOPS program after SETUP phaseITEST = 2 - Continues with execution of program

after SETUP

Restart Configuration:

Control flag (MRESTART) Default: 0 ! MRESTART = 0 !

0 = Do not read or write a restart file1 = Read a restart file at the beginning of

the run

2 = Write a restart file during run3 = Read a restart file at beginning of run

and write a restart file during run

Number of periods in Restartoutput cycle (NRESPD) Default: 0 ! NRESPD = 0 !

0 = File written only at last period

>0 = File updated every NRESPD periods

Meteorological Data Format (METFM)

Default: 1 ! METFM = 1 !

METFM = 1 - CALMET binary file (CALMET.MET)METFM = 2 - ISC ASCII file (ISCMET.MET)METFM = 3 - AUSPLUME ASCII file (PLMMET.MET)METFM = 4 - CTDM plus tower file (PROFILE.DAT) and

surface parameters file (SURFACE.DAT)

METFM = 5 - AERMET tower file (PROFILE.DAT) and

surface parameters file (SURFACE.DAT)

Meteorological Profile Data Format (MPRFFM)

(used only for METFM = 1, 2, 3)

Default: 1 ! MPRFFM = 1 !

MPRFFM = 1 - CTDM plus tower file (PROFILE.DAT)MPRFFM = 2 - AERMET tower file (PROFILE.DAT)

PG sigma-y is adjusted by the factor (AVET/PGTIME)**0.2Averaging Time (minutes) (AVET)

4
INVCAM02.inp 

Default: 60.0 ! AVET = 60. !

PG Averaging Time (minutes) (PGTIME)

Default: 60.0 ! PGTIME = 60. !

!END!-------------------------------------------------------------------------------INPUT GROUP: 2 -- Technical options--------------

Vertical distribution used in thenear field (MGAUSS) Default: 1 ! MGAUSS = 1 !

0 = uniform1 = Gaussian

Terrain adjustment method(MCTADJ) Default: 3 ! MCTADJ = 3 !

0 = no adjustment1 = ISC-type of terrain adjustment2 = simple, CALPUFF-type of terrain

adjustment

3 = partial plume path adjustment

Subgrid-scale complex terrainflag (MCTSG) Default: 0 ! MCTSG = 0 !

0 = not modeled1 = modeled

Near-field puffs modeled aselongated slugs? (MSLUG) Default: 0 ! MSLUG = 0 !

0 = no1 = yes (slug model used)

Transitional plume rise modeled?(MTRANS) Default: 1 ! MTRANS = 1 !

0 = no (i.e., final rise only)1 = yes (i.e., transitional rise computed)

Stack tip downwash? (MTIP) Default: 1 ! MTIP = 1 !

0 = no (i.e., no stack tip downwash)1 = yes (i.e., use stack tip downwash)

Method used to simulate buildingdownwash? (MBDW) Default: 1 ! MBDW = 1 !

1 = ISC method

5
INVCAM02.inp 

2 = PRIME method

Vertical wind shear modeled abovestack top? (MSHEAR) Default: 0 ! MSHEAR = 0 !

0 = no (i.e., vertical wind shear not modeled)1 = yes (i.e., vertical wind shear modeled)

Puff splitting allowed? (MSPLIT) Default: 0 ! MSPLIT = 0 !

0 = no (i.e., puffs not split)1 = yes (i.e., puffs are split)

Chemical mechanism flag (MCHEM) Default: 1 ! MCHEM = 1 !

0 = chemical transformation not

modeled

1 = transformation rates computed

internally (MESOPUFF II scheme)

2 = user-specified transformation

rates used

3 = transformation rates computed

internally (RIVAD/ARM3 scheme)

4 = secondary organic aerosol formation

computed (MESOPUFF II scheme for OH)

Aqueous phase transformation flag (MAQCHEM)(Used only if MCHEM = 1, or 3) Default: 0 ! MAQCHEM = 0 !

0 = aqueous phase transformation

not modeled

1 = transformation rates adjusted

for aqueous phase reactions

Wet removal modeled ? (MWET) Default: 1 ! MWET = 1 !

0 = no1 = yes

Dry deposition modeled ? (MDRY) Default: 1 ! MDRY = 1 !

0 = no1 = yes(dry deposition method specified

for each species in Input Group 3)

Gravitational settling (plume tilt)modeled ? (MTILT) Default: 0 ! MTILT = 0 !

0 = no1 = yes(puff center falls at the gravitational

settling velocity for 1 particle species)

Restrictions:

6
INVCAM02.inp 

- MDRY = 1- NSPEC = 1 (must be particle species as well)- sg = 0 GEOMETRIC STANDARD DEVIATION in Group 8 is

set to zero for a single particle diameter

Method used to compute dispersioncoefficients (MDISP) Default: 3 ! MDISP = 3 !

1 = dispersion coefficients computed from measured values

of turbulence, sigma v, sigma w

2 = dispersion coefficients from internally calculated

sigma v, sigma w using micrometeorological variables(u*, w*, L, etc.)

3 = PG dispersion coefficients for RURAL areas (computed using

the ISCST multi-segment approximation) and MP coefficients inurban areas

4 = same as 3 except PG coefficients computed using

the MESOPUFF II eqns.

5 = CTDM sigmas used for stable and neutral conditions.

For unstable conditions, sigmas are computed as inMDISP = 3, described above. MDISP = 5 assumes thatmeasured values are read

Sigma-v/sigma-theta, sigma-w measurements used? (MTURBVW)(Used only if MDISP = 1 or 5) Default: 3 ! MTURBVW = 0 !

1 = use sigma-v or sigma-theta measurements

from PROFILE.DAT to compute sigma-y(valid for METFM = 1, 2, 3, 4, 5)

2 = use sigma-w measurements

from PROFILE.DAT to compute sigma-z(valid for METFM = 1, 2, 3, 4, 5)

3 = use both sigma-(v/theta) and sigma-w

from PROFILE.DAT to compute sigma-y and sigma-z(valid for METFM = 1, 2, 3, 4, 5)

4 = use sigma-theta measurements

from PLMMET.DAT to compute sigma-y(valid only if METFM = 3)

Back-up method used to compute dispersionwhen measured turbulence data aremissing (MDISP2) Default: 3 ! MDISP2 = 3 !(used only if MDISP = 1 or 5)

2 = dispersion coefficients from internally calculated

sigma v, sigma w using micrometeorological variables(u*, w*, L, etc.)

3 = PG dispersion coefficients for RURAL areas (computed using

the ISCST multi-segment approximation) and MP coefficients inurban areas

4 = same as 3 except PG coefficients computed using

7
INVCAM02.inp 

the MESOPUFF II eqns.

[DIAGNOSTIC FEATURE]Method used for Lagrangian timescale for Sigma-y(used only if MDISP=1,2 or MDISP2=1,2)(MTAULY) Default: 0 ! MTAULY = 0 !

0 = Draxler default 617.284 (s)1 = Computed as Lag. Length / (.75 q) -- after SCIPUFF

10 < Direct user input (s) -- e.g., 306.9

[DIAGNOSTIC FEATURE]Method used for Advective-Decay timescale for Turbulence(used only if MDISP=2 or MDISP2=2)(MTAUADV) Default: 0 ! MTAUADV = 0 !

0 = No turbulence advection1 = Computed (OPTION NOT IMPLEMENTED)

10 < Direct user input (s) -- e.g., 300

Method used to compute turbulence sigma-v &sigma-w using micrometeorological variables(Used only if MDISP = 2 or MDISP2 = 2)(MCTURB) Default: 1 ! MCTURB = 1 !

1 = Standard CALPUFF subroutines2 = AERMOD subroutines

PG sigma-y,z adj. for roughness? Default: 0 ! MROUGH = 0 !(MROUGH)

0 = no1 = yes

Partial plume penetration of Default: 1 ! MPARTL = 1 !elevated inversion?(MPARTL)

0 = no1 = yes

Strength of temperature inversion Default: 0 ! MTINV = 0 !provided in PROFILE.DAT extended records?(MTINV)

0 = no (computed from measured/default gradients)1 = yes

PDF used for dispersion under convective conditions?

Default: 0 ! MPDF = 0 !

(MPDF)

0 = no1 = yes

8
INVCAM02.inp 

Sub-Grid TIBL module used for shore line?

Default: 0 ! MSGTIBL = 0 !

(MSGTIBL)

0 = no1 = yes

Boundary conditions (concentration) modeled?

Default: 0 ! MBCON = 0 !

(MBCON)

0 = no1 = yes, using formatted BCON.DAT file2 = yes, using unformatted CONC.DAT file

Analyses of fogging and icing impacts due to emissions fromarrays of mechanically-forced cooling towers can be performedusing CALPUFF in conjunction with a cooling tower emissionsprocessor (CTEMISS) and its associated postprocessors. Hourlyemissions of water vapor and temperature from each cooling towercell are computed for the current cell configuration and ambientconditions by CTEMISS. CALPUFF models the dispersion of theseemissions and provides cloud information in a specialized formatfor further analysis. Output to FOG.DAT is provided in either'plume mode' or 'receptor mode' format.Configure for FOG Model output?

Default: 0 ! MFOG = 0 !

(MFOG)

0 = no1 = yes - report results in PLUME Mode format2 = yes - report results in RECEPTOR Mode format

Test options specified to see ifthey conform to regulatoryvalues? (MREG) Default: 1 ! MREG = 0 !

0 = NO checks are made1 = Technical options must conform to USEPA

Long Range Transport (LRT) guidance

METFM 1 or 2AVET 60. (min)PGTIME 60. (min)MGAUSS 1MCTADJ 3MTRANS 1MTIP 1MCHEM 1 or 3 (if modeling SOx, NOx)

9
INVCAM02.inp 

MWET 1MDRY 1MDISP 2 or 3MPDF 0 if MDISP=3

1 if MDISP=2

MROUGH 0MPARTL 1SYTDEP 550. (m)MHFTSZ 0

!END!-------------------------------------------------------------------------------INPUT GROUP: 3a, 3b -- Species list-------------------------------Subgroup (3a)------------

The following species are modeled:

! 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!

Dry OUTPUT GROUP

SPECIES MODELED EMITTED DEPOSITED NUMBER

NAME (0=NO, 1=YES) (0=NO, 1=YES) (0=NO, (0=NONE,

(Limit: 12 1=COMPUTED-GAS 1=1st CGRUP,

10
INVCAM02.inp 

Characters 2=COMPUTED-PARTICLE 2=2nd CGRUP,in length) 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)-------------

The following names are used for Species-Groups in which resultsfor certain species are combined (added) prior to output. TheCGRUP name will be used as the species name in output files.Use this feature to model specific particle-size distributionsby treating each size-range as a separate species.Order must be consistent with 3(a) above.

-------------------------------------------------------------------------------INPUT GROUP: 4 -- Map Projection and Grid control parameters--------------

Projection for all (X,Y):-------------------------Map projection(PMAP) Default: UTM ! PMAP = LCC !

11
INVCAM02.inp 

UTM : Universal Transverse MercatorTTM : Tangential Transverse MercatorLCC : Lambert Conformal Conic

PS : Polar StereographicEM : Equatorial Mercator

LAZA : Lambert Azimuthal Equal Area

False Easting and Northing (km) at the projection origin(Used only if PMAP= TTM, LCC, or LAZA)(FEAST) Default=0.0 ! FEAST = 0.000 !(FNORTH) Default=0.0 ! FNORTH = 0.000 !UTM zone (1 to 60)(Used only if PMAP=UTM)(IUTMZN) No Default ! IUTMZN = 0 !Hemisphere for UTM projection?(Used only if PMAP=UTM)(UTMHEM) Default: N ! UTMHEM = N !

N : Northern hemisphere projectionS : Southern hemisphere projection

Latitude and Longitude (decimal degrees) of projection origin(Used only if PMAP= TTM, LCC, PS, EM, or LAZA)(RLAT0) No Default ! RLAT0 = 40N !(RLON0) No Default ! RLON0 = 97W !

TTM : RLON0 identifies central (true N/S) meridian of projection

RLAT0 selected for convenience

LCC : RLON0 identifies central (true N/S) meridian of projection

RLAT0 selected for convenience

PS : RLON0 identifies central (grid N/S) meridian of projection

RLAT0 selected for convenience

EM : RLON0 identifies central meridian of projection

RLAT0 is REPLACED by 0.0N (Equator)

LAZA: RLON0 identifies longitude of tangent-point of mapping plane

RLAT0 identifies latitude of tangent-point of mapping plane

Matching parallel(s) of latitude (decimal degrees) for projection(Used only if PMAP= LCC or PS)(XLAT1) No Default ! XLAT1 = 33N !(XLAT2) No Default ! XLAT2 = 45N !

LCC : Projection cone slices through Earth's surface at XLAT1 and XLAT2PS : Projection plane slices through Earth at XLAT1

(XLAT2 is not used)

----------Note: Latitudes and longitudes should be positive, and include a

12
INVCAM02.inp 

letter N,S,E, or W indicating north or south latitude, andeast or west longitude. For example,35.9 N Latitude = 35.9N118.7 E Longitude = 118.7E

Datum-region------------The Datum-Region for the coordinates is identified by a characterstring. Many mapping products currently available use the model of theEarth known as the World Geodetic System 1984 (WGS-84). Other localmodels may be in use, and their selection in CALMET will make its outputconsistent with local mapping products. The list of Datum-Regions withofficial transformation parameters is provided by the National Imagery andMapping Agency (NIMA).NIMA Datum - Regions(Examples)------------------------------------------------------------------------------WGS-84 WGS-84 Reference Ellipsoid and Geoid, Global coverage (WGS84)NAS-C NORTH AMERICAN 1927 Clarke 1866 Spheroid, MEAN FOR CONUS (NAD27)NAR-C NORTH AMERICAN 1983 GRS 80 Spheroid, MEAN FOR CONUS (NAD83)NWS-84 NWS 6370KM Radius, SphereESR-S ESRI REFERENCE 6371KM Radius, SphereDatum-region for output coordinates(DATUM) Default: WGS-84 ! DATUM = NWS-84 !

METEOROLOGICAL Grid:

Rectangular grid defined for projection PMAP,with X the Easting and Y the Northing coordinate

No. X grid cells (NX) No default ! NX = 248 !No. Y grid cells (NY) No default ! NY = 257 !

No. vertical layers (NZ) No default ! NZ = 10 !

Grid spacing (DGRIDKM) No default ! DGRIDKM = 4. !

Units: km

Cell face heights

(ZFACE(nz+1)) No defaults

Units: m

! ZFACE = 0.,20.,40.,80.,160.,320.,640.,1200.,2000.,3000.,4000. !

Reference Coordinates

of SOUTHWEST corner of

grid cell(1, 1):

13
INVCAM02.inp 

X coordinate (XORIGKM) No default ! XORIGKM = 718.005 !Y coordinate (YORIGKM) No default ! YORIGKM = -1214.003 !

Units: km

COMPUTATIONAL Grid:

The computational grid is identical to or a subset of the MET. grid.The lower left (LL) corner of the computational grid is at grid point(IBCOMP, JBCOMP) of the MET. grid. The upper right (UR) corner of thecomputational grid is at grid point (IECOMP, JECOMP) of the MET. grid.The grid spacing of the computational grid is the same as the MET. grid.

X index of LL corner (IBCOMP) No default ! IBCOMP = 100 !

(1 <= IBCOMP <= NX)

Y index of LL corner (JBCOMP) No default ! JBCOMP = 132 !

(1 <= JBCOMP <= NY)

X index of UR corner (IECOMP) No default ! IECOMP = 242 !

(1 <= IECOMP <= NX)

Y index of UR corner (JECOMP) No default ! JECOMP = 233 !

(1 <= JECOMP <= NY)

SAMPLING Grid (GRIDDED RECEPTORS):

The lower left (LL) corner of the sampling grid is at grid point(IBSAMP, JBSAMP) of the MET. grid. The upper right (UR) corner of thesampling grid is at grid point (IESAMP, JESAMP) of the MET. grid.The sampling grid must be identical to or a subset of the computationalgrid. It may be a nested grid inside the computational grid.The grid spacing of the sampling grid is DGRIDKM/MESHDN.

Logical flag indicating if griddedreceptors are used (LSAMP) Default: T ! LSAMP = F !(T=yes, F=no)X index of LL corner (IBSAMP) No default ! IBSAMP = 1 !

(IBCOMP <= IBSAMP <= IECOMP)

Y index of LL corner (JBSAMP) No default ! JBSAMP = 1 !

(JBCOMP <= JBSAMP <= JECOMP)

14
INVCAM02.inp 

X index of UR corner (IESAMP) No default ! IESAMP = 1 !

(IBCOMP <= IESAMP <= IECOMP)

Y index of UR corner (JESAMP) No default ! JESAMP = 1 !

(JBCOMP <= JESAMP <= JECOMP)

Nesting factor of the sampling

grid (MESHDN) Default: 1 ! MESHDN = 1 !(MESHDN is an integer >= 1)

!END!-------------------------------------------------------------------------------INPUT GROUP: 5 -- Output Options--------------

* *

FILE DEFAULT VALUE VALUE THIS RUN---- ------------- --------------

Concentrations (ICON) 1 ! ICON = 1 !Dry Fluxes (IDRY) 1 ! IDRY = 0 !Wet Fluxes (IWET) 1 ! IWET = 0 !Relative Humidity (IVIS) 1 ! IVIS = 0 !

(RH file is required for

VISIBILITY analyses)

Use data compression option in output file?(LCOMPRS) Default: T ! LCOMPRS = T !*

0 = Do not create file, 1 = create fileQA PLOT FILE OUTPUT OPTION:

Create a standard series of output files (e.g.locations of sources, receptors, grids ...)suitable for plotting?(IQAPLOT) Default: 1 ! IQAPLOT = 1 !

0 = no1 = yes

DIAGNOSTIC MASS FLUX OUTPUT OPTIONS:

15
INVCAM02.inp 

Mass flux across specified boundariesfor selected species reported hourly?(IMFLX) Default: 0 ! IMFLX = 0 !

0 = no1 = yes (FLUXBDY.DAT and MASSFLX.DAT filenames

are specified in Input Group 0)

Mass balance for each speciesreported hourly?(IMBAL) Default: 0 ! IMBAL = 0 !

0 = no1 = yes (MASSBAL.DAT filename is

specified in Input Group 0)

LINE PRINTER OUTPUT OPTIONS:

Print concentrations (ICPRT) Default: 0 ! ICPRT = 0 !Print dry fluxes (IDPRT) Default: 0 ! IDPRT = 0 !Print wet fluxes (IWPRT) Default: 0 ! IWPRT = 0 !(0 = Do not print, 1 = Print)Concentration print interval(ICFRQ) in hours Default: 1 ! ICFRQ = 1 !Dry flux print interval(IDFRQ) in hours Default: 1 ! IDFRQ = 1 !Wet flux print interval(IWFRQ) in hours Default: 1 ! IWFRQ = 1 !Units for Line Printer Output(IPRTU) Default: 1 ! IPRTU = 3 !

for for

Concentration Deposition

1 = g/m**3 g/m**2/s2 = mg/m**3 mg/m**2/s3 = ug/m**3 ug/m**2/s4 = ng/m**3 ng/m**2/s5 = Odour Units

Messages tracking progress of runwritten to the screen ?(IMESG) Default: 2 ! IMESG = 2 !

0 = no1 = yes (advection step, puff ID)2 = yes (YYYYJJJHH, # old puffs, # emitted puffs)

SPECIES (or GROUP for combined species) LIST FOR OUTPUT OPTIONS

16
INVCAM02.inp 

---- CONCENTRATIONS ---- ------ DRY FLUXES ------ ------ WET FLUXES -FLUX --

SPECIES/GROUP PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK?------- ------------------------ ------------------------ ----------------------------------

! SO2 = 0, 1, 0, 0, 0, 0, ! SO4 = 0, 1, 0, 0, 0, 0, ! NOX = 0, 1, 0, 0, 0, 0, ! HNO3 = 0, 1, 0, 0, 0, 0, ! NO3 = 0, 1, 0, 0, 0, 0, ! POC081 = 0, 1, 0, 0, 0, 0, ! POC056 = 0, 1, 0, 0, 0, 0, ! PIC081 = 0, 1, 0, 0, 0, 0, ! PIC056 = 0, 1, 0, 0, 0, 0, ! PMC800 = 0, 1, 0, 0, 0, 0, ! PMC425 = 0, 1, 0, 0, 0, 0, ! PMF187 = 0, 1, 0, 0, 0, 0, ! PMF112 = 0, 1, 0, 0, 0, 0, ! PMF081 = 0, 1, 0, 0, 0, 0, ! PMF056 = 0, 1, 0, 0, 0, 0, ! EC187 = 0, 1, 0, 0, 0, 0, ! EC112 = 0, 1, 0, 0, 0, 0, ! EC081 = 0, 1, 0, 0, 0, 0, ! EC056 = 0, 1, 0, 0, 0, 0, 

OPTIONS FOR PRINTING "DEBUG" QUANTITIES (much output)

Logical for debug output(LDEBUG) Default: F ! LDEBUG = F !First puff to track(IPFDEB) Default: 1 ! IPFDEB = 1 !Number of puffs to track(NPFDEB) Default: 1 ! NPFDEB = 10 !Met. period to start output(NN1) Default: 1 ! NN1 = 10 !Met. period to end output(NN2) Default: 10 ! NN2 = 10 !

!END!-------------------------------------------------------------------------------

17
INVCAM02.inp 

INPUT GROUP: 6a, 6b, & 6c -- Subgrid scale complex terrain inputs----------------------------------------Subgroup (6a)---------------

Number of terrain features (NHILL) Default: 0 ! NHILL = 0 !Number of special complex terrainreceptors (NCTREC) Default: 0 ! NCTREC = 0 !Terrain and CTSG Receptor data forCTSG hills input in CTDM format ?(MHILL) No Default ! MHILL = 0 !1 = Hill and Receptor data created

by CTDM processors & read fromHILL.DAT and HILLRCT.DAT files

2 = Hill data created by OPTHILL &

input below in Subgroup (6b);Receptor data in Subgroup (6c)

Factor to convert horizontal dimensions Default: 1.0 ! XHILL2M = 0. !to meters (MHILL=1)Factor to convert vertical dimensions Default: 1.0 ! ZHILL2M = 0. !to meters (MHILL=1)X-origin of CTDM system relative to No Default ! XCTDMKM = 0.0E00 !CALPUFF coordinate system, in Kilometers (MHILL=1)Y-origin of CTDM system relative to No Default ! YCTDMKM = 0.0E00 !CALPUFF coordinate system, in Kilometers (MHILL=1)

! END !---------------Subgroup (6b)---------------

1 **

HILL information

HILL XC YC THETAH ZGRID RELIEF EXPO 1 EXPO 2 SCALE 1 SAMAX2

NO. (km) (km) (deg.) (m) (m) (m) (m) (m) (m)

---- ---- ---- ------ ----- ------ ------ ------ ------- -

18
INVCAM02.inp 

--------------------Subgroup (6c)---------------

COMPLEX TERRAIN RECEPTOR INFORMATION

XRCT YRCT ZRCT XHH(km) (km) (m)

------ ----- ------ ----

-------------------1

Description of Complex Terrain Variables:

XC, YC = Coordinates of center of hillTHETAH = Orientation of major axis of hill (clockwise from

North)

ZGRID = Height of the 0 of the grid above mean sea

level

RELIEF = Height of the crest of the hill above the grid elevationEXPO 1 = Hill-shape exponent for the major axisEXPO 2 = Hill-shape exponent for the major axisSCALE 1 = Horizontal length scale along the major axisSCALE 2 = Horizontal length scale along the minor axisAMAX = Maximum allowed axis length for the major axisBMAX = Maximum allowed axis length for the major axisXRCT, YRCT = Coordinates of the complex terrain receptorsZRCT = Height of the ground (MSL) at the complex terrain

Receptor

XHH = Hill number associated with each complex terrain receptor

(NOTE: MUST BE ENTERED AS A REAL NUMBER)

**

NOTE: DATA for each hill and CTSG receptor are treated as a separate

input subgroup and therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUP: 7 -- Chemical parameters for dry deposition of gases--------------

SPECIES DIFFUSIVITY ALPHA STAR REACTIVITY MESOPHYLL RESISTANCE COEFFICIENT

NAME (cm**2/s) (s/cm)(dimensionless)

19
INVCAM02.inp 

------- ----------- ---------- ---------- -------------------------------------------

! SO2 = 0.1509, 1000., 8., 0., ! NOX = 0.1656, 1., 8., 5., ! HNO3 = 0.1628, 1., 18., 0., 0!END!-------------------------------------------------------------------------------INPUT GROUP: 8 -- Size parameters for dry deposition of particles--------------

For SINGLE SPECIES, the mean and standard deviation are used tocompute a deposition velocity for NINT (see group 9) size-ranges,and these are then averaged to obtain a mean deposition velocity.For GROUPED SPECIES, the size distribution should be explicitlyspecified (by the 'species' in the group), and the standard deviationfor each should be entered as 0. The model will then use thedeposition velocity for the stated mean diameter.

SPECIES GEOMETRIC MASS MEAN GEOMETRIC STANDARD

NAME DIAMETER DEVIATION

(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!-------------------------------------------------------------------------------

20
INVCAM02.inp 

INPUT GROUP: 9 -- Miscellaneous dry deposition parameters--------------

Reference cuticle resistance (s/cm)(RCUTR) Default: 30 ! RCUTR = 30.0 !Reference ground resistance (s/cm)(RGR) Default: 10 ! RGR = 10.0 !Reference pollutant reactivity(REACTR) Default: 8 ! REACTR = 8.0 !Number of particle-size intervals used toevaluate effective particle deposition velocity(NINT) Default: 9 ! NINT = 9 !Vegetation state in unirrigated areas(IVEG) Default: 1 ! IVEG = 1 !

IVEG=1 for active and unstressed vegetationIVEG=2 for active and stressed vegetationIVEG=3 for inactive vegetation

!END!-------------------------------------------------------------------------------INPUT GROUP: 10 -- Wet Deposition Parameters---------------

Scavenging Coefficient -- Units: (sec)**(-1)

Pollutant Liquid Precip. Frozen Precip.--------- -------------- --------------

! 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 !

21
INVCAM02.inp 

! 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!-------------------------------------------------------------------------------INPUT GROUP: 11 -- Chemistry Parameters---------------

Ozone data input option (MOZ) Default: 1 ! MOZ = 1 !(Used only if MCHEM = 1, 3, or 4)

0 = use a monthly background ozone value1 = read hourly ozone concentrations from

the OZONE.DAT data file

Monthly ozone concentrations(Used only if MCHEM = 1, 3, or 4 and

MOZ = 0 or MOZ = 1 and all hourly O3 data missing)

(BCKO3) in ppb Default: 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 !

Monthly ammonia concentrations(Used only if MCHEM = 1, or 3)(BCKNH3) in ppb Default: 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 !Nighttime SO2 loss rate (RNITE1)in percent/hour Default: 0.2 ! RNITE1 = .2 !Nighttime NOx loss rate (RNITE2)in percent/hour Default: 2.0 ! RNITE2 = 2.0 !Nighttime HNO3 formation rate (RNITE3)in percent/hour Default: 2.0 ! RNITE3 = 2.0 !H2O2 data input option (MH2O2) Default: 1 ! MH2O2 = 1 !(Used only if MAQCHEM = 1)

0 = use a monthly background H2O2 value1 = read hourly H2O2 concentrations from

the H2O2.DAT data file

Monthly H2O2 concentrations

22
INVCAM02.inp 

(Used only if MQACHEM = 1 and

MH2O2 = 0 or MH2O2 = 1 and all hourly H2O2 data missing)

(BCKH2O2) in ppb Default: 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 !

--- Data for SECONDARY ORGANIC AEROSOL (SOA) Option

(used only if MCHEM = 4)The SOA module uses monthly values of:

Fine particulate concentration in ug/m^3 (BCKPMF)Organic fraction of fine particulate (OFRAC)VOC / NOX ratio (after reaction) (VCNX)

to characterize the air mass when computingthe formation of SOA from VOC emissions.Typical values for several distinct air mass types are:

Month 1 2 3 4 5 6 7 8 9 10 11 12

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Clean Continental

BCKPMF 1. 1. 1. 1. 1. 1. 1. 1. 1. 1. 1. 1.OFRAC .15 .15 .20 .20 .20 .20 .20 .20 .20 .20 .20 .15VCNX 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50.

Clean Marine (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 .25VCNX 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50. 50.

Urban - low biogenic (controls present)

BCKPMF 30. 30. 30. 30. 30. 30. 30. 30. 30. 30. 30. 30.OFRAC .20 .20 .25 .25 .25 .25 .25 .25 .20 .20 .20 .20VCNX 4. 4. 4. 4. 4. 4. 4. 4. 4. 4. 4. 4.

Urban - high biogenic (controls present)

BCKPMF 60. 60. 60. 60. 60. 60. 60. 60. 60. 60. 60. 60.OFRAC .25 .25 .30 .30 .30 .55 .55 .55 .35 .35 .35 .25VCNX 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15.

Regional Plume

BCKPMF 20. 20. 20. 20. 20. 20. 20. 20. 20. 20. 20. 20.OFRAC .20 .20 .25 .35 .25 .40 .40 .40 .30 .30 .30 .20VCNX 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15.

Urban - no controls present

BCKPMF 100. 100. 100. 100. 100. 100. 100. 100. 100. 100. 100. 100.OFRAC .30 .30 .35 .35 .35 .55 .55 .55 .35 .35 .35 .30VCNX 2. 2. 2. 2. 2. 2. 2. 2. 2. 2. 2. 2.

23
INVCAM02.inp 

Default: Clean Continental! 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.

!END!-------------------------------------------------------------------------------INPUT GROUP: 12 -- Misc. Dispersion and Computational Parameters---------------

Horizontal size of puff (m) beyond whichtime-dependent dispersion equations (Heffter)are used to determine sigma-y andsigma-z (SYTDEP) Default: 550. ! SYTDEP = 5.5E02 !Switch for using Heffter equation for sigma zas above (0 = Not use Heffter; 1 = use Heffter(MHFTSZ) Default: 0 ! MHFTSZ = 0 !Stability class used to determine plumegrowth rates for puffs above the boundarylayer (JSUP) Default: 5 ! JSUP = 5 !Vertical dispersion constant for stableconditions (k1 in Eqn. 2.7-3) (CONK1) Default: 0.01 ! CONK1 = .01 !Vertical dispersion constant for neutral/unstable conditions (k2 in Eqn. 2.7-4)(CONK2) Default: 0.1 ! CONK2 = .1 !Factor for determining Transition-point fromSchulman-Scire to Huber-Snyder Building Downwashscheme (SS used for Hs < Hb + TBD * HL)(TBD) Default: 0.5 ! TBD = .5 !

TBD < 0 ==> always use Huber-SnyderTBD = 1.5 ==> always use Schulman-ScireTBD = 0.5 ==> ISC Transition-point

Range of land use categories for whichurban dispersion is assumed(IURB1, IURB2) Default: 10 ! IURB1 = 10 !

19 ! IURB2 = 19 !

24
INVCAM02.inp 

Site characterization parameters for single-point Met data files ---------(needed for METFM = 2,3,4,5)

Land use category for modeling domain(ILANDUIN) Default: 20 ! ILANDUIN = 20 !Roughness length (m) for modeling domain(Z0IN) Default: 0.25 ! Z0IN = .25 !Leaf area index for modeling domain(XLAIIN) Default: 3.0 ! XLAIIN = 3.0 !Elevation above sea level (m)(ELEVIN) Default: 0.0 ! ELEVIN = .0 !Latitude (degrees) for met location(XLATIN) Default: -999. ! XLATIN = -999.0 !Longitude (degrees) for met location(XLONIN) Default: -999. ! XLONIN = -999.0 !

Specialized information for interpreting single-point Met data files -----

Anemometer height (m) (Used only if METFM = 2,3)(ANEMHT) Default: 10. ! ANEMHT = 10.0 !Form of lateral turbulance data in PROFILE.DAT file(Used only if METFM = 4,5 or MTURBVW = 1 or 3)(ISIGMAV) Default: 1 ! ISIGMAV = 1 !

0 = read sigma-theta1 = read sigma-v

Choice of mixing heights (Used only if METFM = 4)(IMIXCTDM) Default: 0 ! IMIXCTDM = 0 !

0 = read PREDICTED mixing heights1 = read OBSERVED mixing heights

Maximum length of a slug (met. grid units)(XMXLEN) Default: 1.0 ! XMXLEN = 1.0 !Maximum travel distance of a puff/slug (ingrid units) during one sampling step(XSAMLEN) Default: 1.0 ! XSAMLEN = 1.0 !Maximum Number of slugs/puffs release fromone source during one time step(MXNEW) Default: 99 ! MXNEW = 99 !Maximum Number of sampling steps for

25
INVCAM02.inp 

one puff/slug during one time step(MXSAM) Default: 99 ! MXSAM = 99 !Number of iterations used when computingthe transport wind for a sampling stepthat includes gradual rise (for CALMETand PROFILE winds)(NCOUNT) Default: 2 ! NCOUNT = 2 !Minimum sigma y for a new puff/slug (m)(SYMIN) Default: 1.0 ! SYMIN = 1.0 !Minimum sigma z for a new puff/slug (m)(SZMIN) Default: 1.0 ! SZMIN = 1.0 !Default minimum turbulence velocities sigma-v and sigma-wfor each stability class over land and over water (m/s)(SVMIN(12) and SWMIN(12))

---------- LAND ---------- --------- WATER ----------

Stab Class : A B C D E F A B C D E F

--- --- --- --- --- --- --- --- --- --- --- ---

Default SVMIN : .50, .50, .50, .50, .50, .50, .37, .37, .37, .37, .37, .37Default SWMIN : .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, ! SWMIN = 0.200, 0.120, 0.080, 0.060, 0.030, 0.016, 0.200, 0.120, 0.080, 0.060, 

Divergence criterion for dw/dz across puffused to initiate adjustment for horizontalconvergence (1/s)Partial adjustment starts at CDIV(1), andfull adjustment is reached at CDIV(2)(CDIV(2)) Default: 0.0,0.0 ! CDIV = .0, .0 !Minimum wind speed (m/s) allowed fornon-calm conditions. Also used as minimumspeed returned when using power-lawextrapolation toward surface(WSCALM) Default: 0.5 ! WSCALM = .5 !Maximum mixing height (m)(XMAXZI) Default: 3000. ! XMAXZI = 3000.0 !Minimum mixing height (m)(XMINZI) Default: 50. ! XMINZI = 50.0 !Default wind speed classes --5 upper bounds (m/s) are entered;

26
INVCAM02.inp 

the 6th class has no upper limit(WSCAT(5)) Default :

ISC RURAL : 1.54, 3.09, 5.14, 8.23, 10.8 (10.8+)

Wind Speed Class : 1 2 3 4 5

--- --- --- --- ---

! WSCAT = 1.54, 3.09, 5.14, 8.23, 10.80 !

Default wind speed profile power-lawexponents for stabilities 1-6(PLX0(6)) Default : ISC RURAL values

ISC RURAL : .07, .07, .10, .15, .35, .55ISC URBAN : .15, .15, .20, .25, .30, .30

Stability Class : A B C D E F

--- --- --- --- --- ---

! PLX0 = 0.07, 0.07, 0.10, 0.15, 0.35, 0.55 !

Default potential temperature gradientfor stable classes E, F (degK/m)(PTG0(2)) Default: 0.020, 0.035

! PTG0 = 0.020, 0.035 !

Default plume path coefficients foreach stability class (used when optionfor partial plume height terrain adjustmentis selected -- MCTADJ=3)(PPC(6)) Stability Class : A B C D E F

Default PPC : .50, .50, .50, .50, .35, .35

--- --- --- --- --- ---

! PPC = 0.50, 0.50, 0.50, 0.50, 0.35, 0.35 !

Slug-to-puff transition criterion factorequal to sigma-y/length of slug(SL2PF) Default: 10. ! SL2PF = 5.0 !Puff-splitting control variables ------------------------

VERTICAL SPLIT--------------Number of puffs that result every time a puffis split - nsplit=2 means that 1 puff splitsinto 2(NSPLIT) Default: 3 ! NSPLIT = 3 !Time(s) of a day when split puffs are eligible tobe split once again; this is typically set onceper day, around sunset before nocturnal shear develops.

27
INVCAM02.inp 

24 values: 0 is midnight (00:00) and 23 is 11 PM (23:00)0=do not re-split 1=eligible for re-split(IRESPLIT(24)) Default: Hour 17 = 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 !Split is allowed only if last hour's mixingheight (m) exceeds a minimum value(ZISPLIT) Default: 100. ! ZISPLIT = 100.0 !Split is allowed only if ratio of last hour'smixing ht to the maximum mixing ht experiencedby the puff is less than a maximum value (thispostpones a split until a nocturnal layer develops)(ROLDMAX) Default: 0.25 ! ROLDMAX = 0.25 !HORIZONTAL SPLIT----------------Number of puffs that result every time a puffis split - nsplith=5 means that 1 puff splitsinto 5(NSPLITH) Default: 5 ! NSPLITH = 5 !Minimum sigma-y (Grid Cells Units) of puffbefore it may be split(SYSPLITH) Default: 1.0 ! SYSPLITH = 1.0 !Minimum puff elongation rate (SYSPLITH/hr) due towind shear, before it may be split(SHSPLITH) Default: 2. ! SHSPLITH = 2.0 !Minimum concentration (g/m^3) of eachspecies in puff before it may be splitEnter array of NSPEC values; if a single value isentered, it will be used for ALL species(CNSPLITH) Default: 1.0E-07 ! CNSPLITH = 1.0E-07 !

Integration control variables ------------------------

Fractional convergence criterion for numerical SLUGsampling integration(EPSSLUG) Default: 1.0e-04 ! EPSSLUG = 1.0E-04 !Fractional convergence criterion for numerical AREAsource integration(EPSAREA) Default: 1.0e-06 ! EPSAREA = 1.0E-06 !Trajectory step-length (m) used for numerical rise

28
INVCAM02.inp 

integration(DSRISE) Default: 1.0 ! DSRISE = 1.0 !Boundary Condition (BC) Puff control variables ------------------------Minimum height (m) to which BC puffs are mixed as they are emitted(MBCON=2 ONLY). Actual height is reset to the current mixing heightat the release point if greater than this minimum.(HTMINBC) Default: 500. ! HTMINBC = 500.0 !Search radius (km) about a receptor for sampling nearest BC puff.BC puffs are typically emitted with a spacing of one grid celllength, so the search radius should be greater than DGRIDKM.(RSAMPBC) Default: 10. ! RSAMPBC = 15.0 !Near-Surface depletion adjustment to concentration profile used whensampling BC puffs?(MDEPBC) Default: 1 ! MDEPBC = 0 !

0 = Concentration is NOT adjusted for depletion1 = Adjust Concentration for depletion

!END!-------------------------------------------------------------------------------INPUT GROUPS: 13a, 13b, 13c, 13d -- Point source parameters-----------------------------------------------Subgroup (13a)---------------

Number of point sources withparameters provided below (NPT1) No default ! NPT1 = 3 !Units used for point sourceemissions below (IPTU) Default: 1 ! IPTU = 1 !

1 = g/s2 = kg/hr3 = lb/hr4 = tons/yr5 = Odour Unit * m**3/s (vol. flux of odour compound)6 = Odour Unit * m**3/min7 = metric tons/yr

Number of source-speciescombinations with variable

29
INVCAM02.inp 

emissions scaling factorsprovided below in (13d) (NSPT1) Default: 0 ! NSPT1 = 0 !Number of point sources withvariable emission parametersprovided in external file (NPT2) No default ! NPT2 = 0 !(If NPT2 > 0, these pointsource emissions are read fromthe file: PTEMARB.DAT)

!END!---------------Subgroup (13b)---------------

a

POINT SOURCE: CONSTANT DATA-----------------------------

b c

Source X Y Stack Base Stack Exit Exit Bldg. Emission

No. Coordinate Coordinate Height Elevation Diameter Vel. Temp. Dwash Rates

(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 !

30
INVCAM02.inp 

3 ! FMFAC = 1.0 ! !END!

--------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.SRCNAM is a 12-character name for a source

(No default)

X is an array holding the source data listed by the column headings

(No default)

SIGYZI is an array holding the initial sigma-y and sigma-z (m)

(Default: 0.,0.)

ZPLTFM is the platform height (m) for sources influenced by an isolated

structure that has a significant open area between the surfaceand the bulk of the structure, such as an offshore oil platform.The Base Elevation is that of the surface (ground or ocean),and the Stack Height is the release height above the Base (notabove the platform). Building heights entered in Subgroup 13cmust be those of the buildings on the platform, measured fromthe platform deck. ZPLTFM is used only with MBDW=1 (ISCdownwash method) for sources with building downwash.(Default: 0.0)

FMFAC is a vertical momentum flux factor (0. or 1.0) used to represent

the effect of rain-caps or other physical configurations thatreduce momentum rise associated with the actual exit velocity.(Default: 1.0 -- full momentum used)

b

0. = No building downwash modeled, 1. = downwash modeledNOTE: must be entered as a REAL number (i.e., with decimal point)

c

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by IPTU(e.g. 1 for g/s).

---------------Subgroup (13c)---------------

BUILDING DIMENSION DATA FOR SOURCES SUBJECT TO DOWNWASH-------------------------------------------------------

Source a

No. Effective building height, width, length and X/Y offset (in meters)

every 10 degrees. LENGTH, XBADJ, and YBADJ are only needed for

31
INVCAM02.inp 

MBDW=2 (PRIME downwash option)

------ ----------------------------------------------------------------------------

a

Building height, width, length, and X/Y offset from the source are treatedas a separate input subgroup for each source and therefore must end withan input group terminator. The X/Y offset is the position, relative to thestack, of the center of the upwind face of the projected building, with thex-axis pointing along the flow direction.

---------------Subgroup (13d)---------------

a

POINT SOURCE: VARIABLE EMISSIONS DATA---------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 13b. Factors entered multiply the rates in 13b.Skip sources here that have constant emissions. For more elaboratevariation in source parameters, use PTEMARB.DAT and NPT2 > 0.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant1 = Diurnal cycle (24 scaling factors: hours 1-24)2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upperbounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

32
INVCAM02.inp 

-------------------------------------------------------------------------------INPUT GROUPS: 14a, 14b, 14c, 14d -- Area source parameters-----------------------------------------------Subgroup (14a)---------------

Number of polygon area sources withparameters specified below (NAR1) No default ! NAR1 = 0 !Units used for area sourceemissions below (IARU) Default: 1 ! IARU = 1 !

1 = g/m**2/s2 = kg/m**2/hr3 = lb/m**2/hr4 = tons/m**2/yr5 = Odour Unit * m/s (vol. flux/m**2 of odour compound)6 = Odour Unit * m/min7 = metric tons/m**2/yr

Number of source-speciescombinations with variableemissions scaling factorsprovided below in (14d) (NSAR1) Default: 0 ! NSAR1 = 0 !Number of buoyant polygon area sourceswith variable location and emissionparameters (NAR2) No default ! NAR2 = 0 !(If NAR2 > 0, ALL parameter data forthese sources are read from the file: BAEMARB.DAT)

!END!---------------Subgroup (14b)---------------

a

AREA SOURCE: CONSTANT DATA----------------------------

b

Source Effect. Base Initial Emission

No. Height Elevation Sigma z Rates

(m) (m) (m)

------- ------ ------ -------- ---------

33
INVCAM02.inp 

--------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

b

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by IARU(e.g. 1 for g/m**2/s).

---------------Subgroup (14c)---------------

COORDINATES (km) FOR EACH VERTEX(4) OF EACH POLYGON--------------------------------------------------------

Source a

No. Ordered list of X followed by list of Y, grouped by source

------ --------------------------------------------------------------------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

---------------Subgroup (14d)---------------

a

AREA SOURCE: VARIABLE EMISSIONS DATA--------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 14b. Factors entered multiply the rates in 14b.Skip sources here that have constant emissions. For more elaboratevariation in source parameters, use BAEMARB.DAT and NAR2 > 0.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant1 = Diurnal cycle (24 scaling factors: hours 1-24)2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upper

34
INVCAM02.inp 

bounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUPS: 15a, 15b, 15c -- Line source parameters------------------------------------------Subgroup (15a)---------------

Number of buoyant line sourceswith variable location and emissionparameters (NLN2) No default ! NLN2 = 0 !(If NLN2 > 0, ALL parameter data for

these sources are read from the file: LNEMARB.DAT)

Number of buoyant line sources (NLINES) No default ! NLINES = 0 !Units used for line sourceemissions below (ILNU) Default: 1 ! ILNU = 1 !

1 = g/s2 = kg/hr3 = lb/hr4 = tons/yr5 = Odour Unit * m**3/s (vol. flux of odour compound)6 = Odour Unit * m**3/min7 = metric tons/yr

Number of source-speciescombinations with variableemissions scaling factorsprovided below in (15c) (NSLN1) Default: 0 ! NSLN1 = 0 !Maximum number of segments used to modeleach line (MXNSEG) Default: 7 ! MXNSEG = 7 !

35
INVCAM02.inp 

The following variables are required only if NLINES > 0. They areused in the buoyant line source plume rise calculations.

Number of distances at which Default: 6 ! NLRISE = 6 !transitional rise is computedAverage building length (XL) No default ! XL = .0 !

(in meters)

Average building height (HBL) No default ! HBL = .0 !

(in meters)

Average building width (WBL) No default ! WBL = .0 !

(in meters)

Average line source width (WML) No default ! WML = .0 !

(in meters)

Average separation between buildings (DXL) No default ! DXL = .0 !

(in meters)

Average buoyancy parameter (FPRIMEL) No default ! FPRIMEL = .0 !

(in m**4/s**3)

!END!---------------Subgroup (15b)---------------

BUOYANT LINE SOURCE: CONSTANT DATA----------------------------------

Source Beg. X Beg. Y End. X End. Y Release Base Emission

No. Coordinate Coordinate Coordinate Coordinate Height Elevation Rates

(km) (km) (km) (km) (m) (m)

------ ---------- ---------- --------- ---------- ------- --------- -----------------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

b

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by ILNTU

36
INVCAM02.inp 

(e.g. 1 for g/s).

---------------Subgroup (15c)---------------

a

BUOYANT LINE SOURCE: VARIABLE EMISSIONS DATA----------------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 15b. Factors entered multiply the rates in 15b.Skip sources here that have constant emissions.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant1 = Diurnal cycle (24 scaling factors: hours 1-24)2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upperbounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUPS: 16a, 16b, 16c -- Volume source parameters------------------------------------------Subgroup (16a)---------------

Number of volume sources withparameters provided in 16b,c (NVL1) No default ! NVL1 = 0 !

37
INVCAM02.inp 

Units used for volume sourceemissions below in 16b (IVLU) Default: 1 ! IVLU = 1 !

1 = g/s2 = kg/hr3 = lb/hr4 = tons/yr5 = Odour Unit * m**3/s (vol. flux of odour compound)6 = Odour Unit * m**3/min7 = metric tons/yr

Number of source-speciescombinations with variableemissions scaling factorsprovided below in (16c) (NSVL1) Default: 0 ! NSVL1 = 0 !Number of volume sources withvariable location and emissionparameters (NVL2) No default ! NVL2 = 0 !(If NVL2 > 0, ALL parameter data for

these sources are read from the VOLEMARB.DAT file(s) )

!END!---------------Subgroup (16b)---------------

a

VOLUME SOURCE: CONSTANT DATA------------------------------

b

X Y Effect. Base Initial Initial Emission

Coordinate Coordinate Height Elevation Sigma y Sigma z Rates

(km) (km) (m) (m) (m) (m)

---------- ---------- ------ ------ -------- -------- --------

--------

a

Data for each source are treated as a separate input subgroupand therefore must end with an input group terminator.

b

An emission rate must be entered for every pollutant modeled.Enter emission rate of zero for secondary pollutants that aremodeled, but not emitted. Units are specified by IVLU(e.g. 1 for g/s).

38
INVCAM02.inp 

---------------Subgroup (16c)---------------

a

VOLUME SOURCE: VARIABLE EMISSIONS DATA----------------------------------------

Use this subgroup to describe temporal variations in the emissionrates given in 16b. Factors entered multiply the rates in 16b.Skip sources here that have constant emissions. For more elaboratevariation in source parameters, use VOLEMARB.DAT and NVL2 > 0.IVARY determines the type of variation, and is source-specific:(IVARY) Default: 0

0 = Constant1 = Diurnal cycle (24 scaling factors: hours 1-24)2 = Monthly cycle (12 scaling factors: months 1-12)3 = Hour & Season (4 groups of 24 hourly scaling factors,

where first group is DEC-JAN-FEB)

4 = Speed & Stab. (6 groups of 6 scaling factors, where

first group is Stability Class A,and the speed classes have upperbounds (m/s) defined in Group 12

5 = Temperature (12 scaling factors, where temperature

classes have upper bounds (C) of:0, 5, 10, 15, 20, 25, 30, 35, 40,45, 50, 50+)

--------

a

Data for each species are treated as a separate input subgroupand therefore must end with an input group terminator.

-------------------------------------------------------------------------------INPUT GROUPS: 17a & 17b -- Non-gridded (discrete) receptor information--------------------------------------Subgroup (17a)---------------

Number of non-gridded receptors (NREC) No default ! NREC = 1076 !

!END!

39
INVCAM02.inp 

---------------Subgroup (17b)---------------

a

NON-GRIDDED (DISCRETE) RECEPTOR DATA------------------------------------

X Y Ground Height b

Receptor Coordinate Coordinate Elevation Above Ground

No. (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!

40
INVCAM02.inp 

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!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!

41
INVCAM02.inp 

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!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!

42
INVCAM02.inp 

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!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!

43
INVCAM02.inp 

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!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!

44
INVCAM02.inp 

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!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!

45
INVCAM02.inp 

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!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!

46
INVCAM02.inp 

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!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!

47
INVCAM02.inp 

382 ! 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!

48
INVCAM02.inp 

431 ! 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!

49
INVCAM02.inp 

480 ! 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!

50
INVCAM02.inp 

529 ! 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!

51
INVCAM02.inp 

578 ! 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 ! !END!595 ! X = 1233.861, -391.803, 1293, 0.00 ! !END!596 ! X = 1235.345, -391.576, 1077, 0.00 ! !END!597 ! X = 1236.829, -391.35, 953, 0.00 ! !END!598 ! X = 1238.312, -391.123, 1202, 0.00 ! !END!599 ! X = 1239.796, -390.895, 1602, 0.00 ! !END!600 ! X = 1241.279, -390.668, 1433, 0.00 ! !END!601 ! X = 1242.763, -390.44, 1106, 0.00 ! !END!602 ! X = 1244.246, -390.212, 966, 0.00 ! !END!603 ! X = 1245.73, -389.984, 1077, 0.00 ! !END!604 ! X = 1247.213, -389.755, 884, 0.00 ! !END!605 ! X = 1248.696, -389.526, 1096, 0.00 ! !END!606 ! X = 1174.216, -398.81, 459, 0.00 ! !END!607 ! X = 1175.701, -398.594, 516, 0.00 ! !END!608 ! X = 1177.185, -398.378, 579, 0.00 ! !END!609 ! X = 1178.67, -398.162, 576, 0.00 ! !END!610 ! X = 1180.155, -397.946, 656, 0.00 ! !END!611 ! X = 1181.64, -397.729, 718, 0.00 ! !END!612 ! X = 1183.125, -397.513, 760, 0.00 ! !END!613 ! X = 1184.609, -397.295, 994, 0.00 ! !END!614 ! X = 1187.579, -396.86, 782, 0.00 ! !END!615 ! X = 1189.063, -396.642, 618, 0.00 ! !END!616 ! X = 1190.548, -396.424, 489, 0.00 ! !END!617 ! X = 1192.033, -396.206, 549, 0.00 ! !END!618 ! X = 1193.517, -395.987, 598, 0.00 ! !END!619 ! X = 1195.001, -395.768, 577, 0.00 ! !END!620 ! X = 1196.486, -395.549, 809, 0.00 ! !END!621 ! X = 1197.97, -395.329, 899, 0.00 ! !END!622 ! X = 1199.455, -395.109, 1006, 0.00 ! !END!623 ! X = 1200.939, -394.889, 1262, 0.00 ! !END!624 ! X = 1202.423, -394.669, 988, 0.00 ! !END!625 ! X = 1203.907, -394.448, 1120, 0.00 ! !END!626 ! X = 1205.392, -394.227, 1054, 0.00 ! !END!

52
INVCAM02.inp 

627 ! X = 1206.876, -394.006, 860, 0.00 ! !END!628 ! X = 1208.36, -393.784, 1013, 0.00 ! !END!629 ! X = 1209.844, -393.563, 1203, 0.00 ! !END!630 ! X = 1211.328, -393.341, 1212, 0.00 ! !END!631 ! X = 1212.812, -393.118, 1380, 0.00 ! !END!632 ! X = 1214.296, -392.896, 1300, 0.00 ! !END!633 ! X = 1215.78, -392.673, 1206, 0.00 ! !END!634 ! X = 1217.263, -392.45, 1581, 0.00 ! !END!635 ! X = 1218.747, -392.227, 1457, 0.00 ! !END!636 ! X = 1220.231, -392.003, 1699, 0.00 ! !END!637 ! X = 1221.715, -391.779, 1543, 0.00 ! !END!638 ! X = 1223.198, -391.555, 1640, 0.00 ! !END!639 ! X = 1224.682, -391.33, 1476, 0.00 ! !END!640 ! X = 1226.166, -391.106, 1036, 0.00 ! !END!641 ! X = 1227.649, -390.881, 1315, 0.00 ! !END!642 ! X = 1229.133, -390.655, 1504, 0.00 ! !END!643 ! X = 1230.616, -390.43, 1469, 0.00 ! !END!644 ! X = 1232.1, -390.204, 1242, 0.00 ! !END!645 ! X = 1233.583, -389.978, 1453, 0.00 ! !END!646 ! X = 1235.066, -389.751, 1414, 0.00 ! !END!647 ! X = 1236.55, -389.525, 1012, 0.00 ! !END!648 ! X = 1238.033, -389.298, 1127, 0.00 ! !END!649 ! X = 1239.516, -389.071, 1352, 0.00 ! !END!650 ! X = 1240.999, -388.843, 1189, 0.00 ! !END!651 ! X = 1242.482, -388.615, 1257, 0.00 ! !END!652 ! X = 1243.965, -388.387, 1048, 0.00 ! !END!653 ! X = 1245.449, -388.159, 856, 0.00 ! !END!654 ! X = 1246.932, -387.931, 825, 0.00 ! !END!655 ! X = 1248.415, -387.702, 1060, 0.00 ! !END!656 ! X = 1249.897, -387.473, 1125, 0.00 ! !END!657 ! X = 1175.435, -396.767, 429, 0.00 ! !END!658 ! X = 1176.92, -396.551, 537, 0.00 ! !END!659 ! X = 1178.404, -396.335, 459, 0.00 ! !END!660 ! X = 1179.889, -396.119, 575, 0.00 ! !END!661 ! X = 1181.373, -395.903, 564, 0.00 ! !END!662 ! X = 1182.858, -395.686, 646, 0.00 ! !END!663 ! X = 1188.795, -394.816, 609, 0.00 ! !END!664 ! X = 1190.279, -394.598, 535, 0.00 ! !END!665 ! X = 1191.764, -394.379, 489, 0.00 ! !END!666 ! X = 1193.248, -394.161, 408, 0.00 ! !END!667 ! X = 1194.732, -393.942, 669, 0.00 ! !END!668 ! X = 1196.216, -393.722, 675, 0.00 ! !END!669 ! X = 1197.7, -393.503, 789, 0.00 ! !END!670 ! X = 1199.184, -393.283, 834, 0.00 ! !END!671 ! X = 1200.668, -393.063, 852, 0.00 ! !END!672 ! X = 1202.152, -392.843, 817, 0.00 ! !END!673 ! X = 1203.636, -392.622, 823, 0.00 ! !END!674 ! X = 1205.12, -392.401, 750, 0.00 ! !END!675 ! X = 1206.603, -392.18, 930, 0.00 ! !END!

53
INVCAM02.inp 

676 ! X = 1208.087, -391.959, 1127, 0.00 ! !END!677 ! X = 1209.571, -391.737, 726, 0.00 ! !END!678 ! X = 1211.054, -391.515, 1065, 0.00 ! !END!679 ! X = 1212.538, -391.293, 1323, 0.00 ! !END!680 ! X = 1214.022, -391.07, 1448, 0.00 ! !END!681 ! X = 1215.505, -390.847, 1548, 0.00 ! !END!682 ! X = 1216.989, -390.624, 1772, 0.00 ! !END!683 ! X = 1218.472, -390.401, 1416, 0.00 ! !END!684 ! X = 1219.956, -390.177, 1198, 0.00 ! !END!685 ! X = 1221.439, -389.954, 1225, 0.00 ! !END!686 ! X = 1222.922, -389.729, 1580, 0.00 ! !END!687 ! X = 1224.406, -389.505, 1529, 0.00 ! !END!688 ! X = 1225.889, -389.28, 1165, 0.00 ! !END!689 ! X = 1227.372, -389.055, 1418, 0.00 ! !END!690 ! X = 1228.855, -388.83, 1635, 0.00 ! !END!691 ! X = 1230.338, -388.605, 1459, 0.00 ! !END!692 ! X = 1231.822, -388.379, 1310, 0.00 ! !END!693 ! X = 1233.305, -388.153, 1441, 0.00 ! !END!694 ! X = 1234.788, -387.926, 1391, 0.00 ! !END!695 ! X = 1236.271, -387.7, 1337, 0.00 ! !END!696 ! X = 1237.754, -387.473, 1455, 0.00 ! !END!697 ! X = 1239.236, -387.246, 1336, 0.00 ! !END!698 ! X = 1240.719, -387.018, 1223, 0.00 ! !END!699 ! X = 1242.202, -386.791, 1226, 0.00 ! !END!700 ! X = 1243.685, -386.563, 979, 0.00 ! !END!701 ! X = 1245.168, -386.335, 1079, 0.00 ! !END!702 ! X = 1246.65, -386.106, 1104, 0.00 ! !END!703 ! X = 1248.133, -385.877, 858, 0.00 ! !END!704 ! X = 1249.615, -385.648, 1030, 0.00 ! !END!705 ! X = 1178.138, -394.509, 475, 0.00 ! !END!706 ! X = 1179.623, -394.292, 440, 0.00 ! !END!707 ! X = 1181.107, -394.076, 640, 0.00 ! !END!708 ! X = 1191.495, -392.553, 369, 0.00 ! !END!709 ! X = 1192.978, -392.334, 478, 0.00 ! !END!710 ! X = 1194.462, -392.115, 570, 0.00 ! !END!711 ! X = 1195.946, -391.896, 552, 0.00 ! !END!712 ! X = 1197.43, -391.677, 843, 0.00 ! !END!713 ! X = 1198.913, -391.457, 604, 0.00 ! !END!714 ! X = 1200.397, -391.237, 605, 0.00 ! !END!715 ! X = 1201.881, -391.017, 652, 0.00 ! !END!716 ! X = 1203.364, -390.796, 770, 0.00 ! !END!717 ! X = 1204.848, -390.575, 834, 0.00 ! !END!718 ! X = 1206.331, -390.354, 725, 0.00 ! !END!719 ! X = 1207.814, -390.133, 608, 0.00 ! !END!720 ! X = 1209.298, -389.911, 656, 0.00 ! !END!721 ! X = 1210.781, -389.689, 1126, 0.00 ! !END!722 ! X = 1212.264, -389.467, 1115, 0.00 ! !END!723 ! X = 1213.748, -389.245, 1387, 0.00 ! !END!724 ! X = 1215.231, -389.022, 1569, 0.00 ! !END!

54
INVCAM02.inp 

725 ! 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!

55
INVCAM02.inp 

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!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!

56
INVCAM02.inp 

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!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!

57
INVCAM02.inp 

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!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!

58
INVCAM02.inp 

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!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!

59
INVCAM02.inp 

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!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!

60
INVCAM02.inp 

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!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!

61
INVCAM02.inp 

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!-------------

a

Data for each receptor are treated as a separate input subgroupand therefore must end with an input group terminator.

b

Receptor height above ground is optional. If no value is entered,the receptor is placed on the ground.

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 2002 

Appendix H.6 - 780
UTINVCAM02A1.inp 

INVISTA CAMDEN - Combine PM SpeciesBART REFINED ANALYSIS 4 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 Update 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

POSTUTIL MODEL CONTROL FILE---------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names---------------------------Subgroup (0a)-------------Output Files------------

File Default File Name---- -----------------List File POSTUTIL.LST ! UTLLST =UTINVCAM02A1.lst !Data File MODEL.DAT ! UTLDAT =UTINVCAM02A1.con !

Input Files-----------

A time-varying file of "background" concentrations can be includedwhen the ammonia-limiting method (ALM) for setting the HNO3/NO3concentration partition is accomplished in 1 step. This optionis selected by setting MNITRATE=3 in Input Group 1.Species required in the "background" concentration file are:SO4, NO3, HNO3 and TNH3 (total NH3 = NH3gaseous + NH3particulate).File Default File Name---- -----------------BCKG File BCKGALM.DAT * BCKGALM =BCKGALM.DAT *A number of CALPUFF data files may be processed in this application.The files may represent individual CALPUFF simulations that were madefor a specific set of species and/or sources. Specify the total numberof CALPUFF runs you wish to combine, and provide the filename for eachin subgroup 0b.

Number of CALPUFF data files (NFILES)

1
UTINVCAM02A1.inp 

Default: 1 ! NFILES = 1 !

Meteorological data files are needed for the HNO3/NO3 partition option.Three types of meteorological data files can be used:

METFM= 0 - CALMET.DATMETFM= 1 - 1-D file with RH, Temp and Rhoair timeseriesMETFM= 2 - 2-D files with either Rh, Temp or Rhoair in each

(3 2_D files are needed)

The default is to use CALMET.DAT files.

Default: 0 ! METFM = 0 !

Multiple meteorological data files may be used in sequence to span theprocessing period. Specify the number of time-period files (NMET) thatyou need to use, and provide a filename for each in subgroup 0b.- NMET is 0 if no meteorological files are provided- NMET is 1 if METFM=1 (multiple file feature is not available)- NMET is 1 or more if METFM=0 or 2 (multiple CALMET files or 2DMET files)

Number of meteorological data file time-periods (NMET)

Default: 0 ! NMET = 12 !

All filenames will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, filenames will be converted to UPPER CASE

Convert filenames to lower case? Default: T ! LCFILES = T !

T = lower caseF = UPPER CASE

!END!-----------------------------------------------------------

NOTE: file/path names can be up to 70 characters in length

------------------------------------------------------------------------Subgroup (0b)-------------NMET CALMET Data Files (METFM=0):Input File Default File Name---------- -----------------

1 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-01A.DAT ! !EN2 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-01B.DAT ! !EN

2
UTINVCAM02A1.inp 

3 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-01C.DAT ! !EN4 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-02A.DAT ! !EN5 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-02B.DAT ! !EN6 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-02C.DAT ! !EN7 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-03A.DAT ! !EN8 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-03B.DAT ! !EN9 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-03C.DAT ! !EN

10 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-04A.DAT ! !EN11 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-04B.DAT ! !EN12 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-04C.DAT ! !EN

NMET 1-D Data Files (METFM=1):Input File Default File Name---------- -----------------

1 MET_1D.DAT * MET1D = MET_1D.DAT * *END*

NMET 2-D Data Files of Each Type (METFM=2):Input File Default File Name---------- -----------------

1 RHUMD.DAT * M2DRHU = RELHUM.DAT * *END*1 TEMP.DAT * M2DTMP = TEMP.DAT * *END*1 RHOAIR.DAT * M2DRHO = RHOAIR.DAT * *END*

NFILES CALPUFF Data Files:Input File Default File Name---------- -----------------

1 CALPUFF.DAT ! MODDAT =INVCAM02.con ! !END!

-------------Note: provide NMET lines of the form * UTLMET = name * *END*

or * MET1D = name * *END*or * M2DRHU = name * *END*

(and) * M2DTMP = name * *END*(and) * M2DRHO = name * *END*

and NFILES lines of the form * MODDAT = name * *END*where the * should be replaced with an exclamation point,the special delimiter character.

3
UTINVCAM02A1.inp 

--------------------------------------------------------------------------------INPUT GROUP: 1 -- General run control parameters--------------

Starting date: Year (ISYR) -- No default ! ISYR = 2002 !

Month (ISMO) -- No default ! ISMO = 1 !Day (ISDY) -- No default ! ISDY = 1 !Hour (ISHR) -- No default ! ISHR = 1 !

Number of periods to process

(NPER) -- No default ! NPER = 2880 !

Number of species to process from CALPUFF runs

(NSPECINP) -- No default ! NSPECINP = 19 !

Number of species to write to output file

(NSPECOUT) -- No default ! NSPECOUT = 19 !

Number of species to compute from those modeled(must be no greater than NSPECOUT)

(NSPECCMP) -- No default ! NSPECCMP = 0 !

When multiple files are used, a species name may appear in more thanone file. Data for this species will be summed (appropriate if theCALPUFF runs use different source groups). If this summing is notappropriate, remove duplicate species from the file(s).

Stop run if duplicate species namesare found? (MDUPLCT) Default: 0 ! MDUPLCT = 0 !

0 = no (i.e., duplicate species are summed)1 = yes (i.e., run is halted)

Data for each species in a CALPUFF data file may also be scaled asthey are read. This can be done to alter the emission rate of allsources that were modeled in a particular CALPUFF application.The scaling factor for each species is entered in Subgroup (2d), foreach file for which scaling is requested.

Number of CALPUFF data files that will be scaled(must be no greater than NFILES)(NSCALED) Default: 0 ! NSCALED = 0 !

Ammonia-Limiting Method Option to recompute the HNO3/NO3 concentrationpartition prior to performing other actions is controlled by MNITRATE.This option will NOT alter any deposition fluxes contained in the CALPUFF

4
UTINVCAM02A1.inp 

file(s). Three partition selections are provided. The first two aretypically used in sequence (POSTUTIL is run more than once). The firstselection (MNITRATE=1) computes the partition for the TOTAL (all sources)concentration fields (SO4, NO3, HNO3; NH3), and the second (MNITRATE=2)uses this partition (from the previous application of POSTUTIL) tocompute the partition for individual source groups. The third selection(MNITRATE=3) can be used instead in a single POSTUTIL application if afile of background concentrations is provided (BCKGALM in Input Group 0).Required information for MNITRATE=1 includes:

species NO3, HNO3, and SO4NH3 concentration(s)met. data file for RH and T

Required information for MNITRATE=2 includes:

species NO3 and HNO3 for a source groupspecies NO3ALL and HNO3ALL for all source groups, properlypartitioned

Required information for MNITRATE=3 includes:

species NO3, HNO3, and SO4 for a source groupspecies NO3, HNO3, SO4 and TNH3 from the background BCKGALM fileIf TNH3 is not in the background BCKGALM file, monthly TNH3concentrations are used (BCKTNH3)TNH3= total NH3 = NH3gaseous+NH3particulate

Recompute the HNO3/NO3 partition for concentrations?(MNITRATE) Default: 0 ! MNITRATE = 1 !

0 = no1 = yes, for all sources combined2 = yes, for a source group3 = yes, ALM application in one step

SOURCE OF AMMONIA:Ammonia may be available as a modeled species in the CALPUFF files,and it may or may not be appropriate to use it for repartitioning NO3/HNO3(in option MNITRATE=1 or MNITRATE=3). Its use is contolled by NH3TYP.When NH3 is listed as a processed species in Subgroup (2a), as one ofthe NSPECINP ASPECI entries, and the right option is chosen for NH3TYP,the NH3 modeled values from the CALPUFF concentration files will be usedin the chemical equilibrium calculation.NH3TYP also controls when monthly background ammonia values are used. Bothgaseous (NH3) and total (TNH3=NH3gaseous+NH3particulate) ammonia can be providedmonthly as BCKNH3/BCKTNH3.

What is the input source of Ammonia?

5
UTINVCAM02A1.inp 

(NH3TYP) No Default ! NH3TYP = 3 !

0 = No background will be used.

ONLY NH3 or TNH3 from the concentrationfiles listed in Subgroup (2a&2b) asa processed species will be used.(Cannot be used with MNITRATE=3)

1 = NH3 Monthly averaged background (BCKNH3)

listed below will be added to NH3 fromconcentration files listed in Subgroup (2a)

2 = NH3 from background concentration file BCKGALM

will be added to NH3 from concentration fileslisted in Subgroup (2a&2b)(ONLY possible for MNITRATE=3)

3 = NH3 Monthly averaged background (BCKNH3)

listed below will be used alone.

4 = NH3 from background concentration file BCKGALM

will be used alone(ONLY possible for MNITRATE=3)

| OPTION | NH3 or TNH3 CONC | BCKNH3 or BCKTNH3 | TNH3/BCKGALM or BCKTNH3 ||--------|------------------|-------------------|-------------------------|| 0 | X | 0 | 0 ||--------|------------------|-------------------|-------------------------|| 1 | X | X | 0 ||--------|------------------|-------------------|-------------------------|| 2 | X | 0 | X ||--------|------------------|-------------------|-------------------------|| 3 | 0 | X | 0 ||--------|------------------|-------------------|-------------------------|| 4 | 0 | 0 | X ||--------|------------------|-------------------|-------------------------|

Default monthly (12 values) background ammonia concentration (ppb)used for HNO3/NO3 partition (need to choose one or the other):

Gaseous NH3 (BCKNH3) Default: -999! BCKNH3 = 12*0.5 !Total TNH3 (BCKTNH3) Default: -999* BCKTNH3 = 1., 1., 1., 1.1, 1.4, 1.3, 1.3, 1.2, 4*1. *

If a single value is entered, this is used for all 12 months.Month 1 is JANUARY, Month 12 is DECEMBER.

6
UTINVCAM02A1.inp 

!END!-------------------------------------------------------------------------------INPUT GROUP: 2 -- Species Processing Information---------------------------Subgroup (2a)-------------

The following NSPECINP species will be processed:

! 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)-------------

The following NSPECOUT species will be written:

! 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!

7
UTINVCAM02A1.inp 

! 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)-------------

The following NSPECCMP species will be computed by scaling and summingone or more of the processed input species. Identify the name(s) ofthe computed species and provide the scaling factors for each of theNSPECINP input species (NSPECCMP groups of NSPECINP+1 lines each):

* *-------------Subgroup (2d)-------------

Each species in NSCALED CALPUFF data files may be scaled before beingprocessed (e.g., to change the emission rate for all sources modeledin the run that produced a data file). For each file, identify thefile name and then provide the name(s) of the scaled species and thecorresponding scaling factors (A,B where x' = 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
UTINVCAM02B1.inp 

INVISTA CAMDEN - Combine PM SpeciesBART REFINED ANALYSIS 4 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 Update 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

POSTUTIL MODEL CONTROL FILE---------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names---------------------------Subgroup (0a)-------------Output Files------------

File Default File Name---- -----------------List File POSTUTIL.LST ! UTLLST =UTINVCAM02B1.lst !Data File MODEL.DAT ! UTLDAT =UTINVCAM02B1.con !

Input Files-----------

A time-varying file of "background" concentrations can be includedwhen the ammonia-limiting method (ALM) for setting the HNO3/NO3concentration partition is accomplished in 1 step. This optionis selected by setting MNITRATE=3 in Input Group 1.Species required in the "background" concentration file are:SO4, NO3, HNO3 and TNH3 (total NH3 = NH3gaseous + NH3particulate).File Default File Name---- -----------------BCKG File BCKGALM.DAT * BCKGALM =BCKGALM.DAT *A number of CALPUFF data files may be processed in this application.The files may represent individual CALPUFF simulations that were madefor a specific set of species and/or sources. Specify the total numberof CALPUFF runs you wish to combine, and provide the filename for eachin subgroup 0b.

Number of CALPUFF data files (NFILES)

1
UTINVCAM02B1.inp 

Default: 1 ! NFILES = 1 !

Meteorological data files are needed for the HNO3/NO3 partition option.Three types of meteorological data files can be used:

METFM= 0 - CALMET.DATMETFM= 1 - 1-D file with RH, Temp and Rhoair timeseriesMETFM= 2 - 2-D files with either Rh, Temp or Rhoair in each

(3 2_D files are needed)

The default is to use CALMET.DAT files.

Default: 0 ! METFM = 0 !

Multiple meteorological data files may be used in sequence to span theprocessing period. Specify the number of time-period files (NMET) thatyou need to use, and provide a filename for each in subgroup 0b.- NMET is 0 if no meteorological files are provided- NMET is 1 if METFM=1 (multiple file feature is not available)- NMET is 1 or more if METFM=0 or 2 (multiple CALMET files or 2DMET files)

Number of meteorological data file time-periods (NMET)

Default: 0 ! NMET = 12 !

All filenames will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, filenames will be converted to UPPER CASE

Convert filenames to lower case? Default: T ! LCFILES = T !

T = lower caseF = UPPER CASE

!END!-----------------------------------------------------------

NOTE: file/path names can be up to 70 characters in length

------------------------------------------------------------------------Subgroup (0b)-------------NMET CALMET Data Files (METFM=0):Input File Default File Name---------- -----------------

1 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-05A.DAT ! !EN2 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-05B.DAT ! !EN

2
UTINVCAM02B1.inp 

3 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-05C.DAT ! !EN4 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-06A.DAT ! !EN5 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-06B.DAT ! !EN6 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-06C.DAT ! !EN7 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-07A.DAT ! !EN8 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-07B.DAT ! !EN9 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-07C.DAT ! !EN

10 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-08A.DAT ! !EN11 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-08B.DAT ! !EN12 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-08C.DAT ! !EN

NMET 1-D Data Files (METFM=1):Input File Default File Name---------- -----------------

1 MET_1D.DAT * MET1D = MET_1D.DAT * *END*

NMET 2-D Data Files of Each Type (METFM=2):Input File Default File Name---------- -----------------

1 RHUMD.DAT * M2DRHU = RELHUM.DAT * *END*1 TEMP.DAT * M2DTMP = TEMP.DAT * *END*1 RHOAIR.DAT * M2DRHO = RHOAIR.DAT * *END*

NFILES CALPUFF Data Files:Input File Default File Name---------- -----------------

1 CALPUFF.DAT ! MODDAT =INVCAM02.con ! !END!

-------------Note: provide NMET lines of the form * UTLMET = name * *END*

or * MET1D = name * *END*or * M2DRHU = name * *END*

(and) * M2DTMP = name * *END*(and) * M2DRHO = name * *END*

and NFILES lines of the form * MODDAT = name * *END*where the * should be replaced with an exclamation point,the special delimiter character.

3
UTINVCAM02B1.inp 

--------------------------------------------------------------------------------INPUT GROUP: 1 -- General run control parameters--------------

Starting date: Year (ISYR) -- No default ! ISYR = 2002 !

Month (ISMO) -- No default ! ISMO = 5 !Day (ISDY) -- No default ! ISDY = 1 !Hour (ISHR) -- No default ! ISHR = 1 !

Number of periods to process

(NPER) -- No default ! NPER = 2952 !

Number of species to process from CALPUFF runs

(NSPECINP) -- No default ! NSPECINP = 19 !

Number of species to write to output file

(NSPECOUT) -- No default ! NSPECOUT = 19 !

Number of species to compute from those modeled(must be no greater than NSPECOUT)

(NSPECCMP) -- No default ! NSPECCMP = 0 !

When multiple files are used, a species name may appear in more thanone file. Data for this species will be summed (appropriate if theCALPUFF runs use different source groups). If this summing is notappropriate, remove duplicate species from the file(s).

Stop run if duplicate species namesare found? (MDUPLCT) Default: 0 ! MDUPLCT = 0 !

0 = no (i.e., duplicate species are summed)1 = yes (i.e., run is halted)

Data for each species in a CALPUFF data file may also be scaled asthey are read. This can be done to alter the emission rate of allsources that were modeled in a particular CALPUFF application.The scaling factor for each species is entered in Subgroup (2d), foreach file for which scaling is requested.

Number of CALPUFF data files that will be scaled(must be no greater than NFILES)(NSCALED) Default: 0 ! NSCALED = 0 !

Ammonia-Limiting Method Option to recompute the HNO3/NO3 concentrationpartition prior to performing other actions is controlled by MNITRATE.This option will NOT alter any deposition fluxes contained in the CALPUFF

4
UTINVCAM02B1.inp 

file(s). Three partition selections are provided. The first two aretypically used in sequence (POSTUTIL is run more than once). The firstselection (MNITRATE=1) computes the partition for the TOTAL (all sources)concentration fields (SO4, NO3, HNO3; NH3), and the second (MNITRATE=2)uses this partition (from the previous application of POSTUTIL) tocompute the partition for individual source groups. The third selection(MNITRATE=3) can be used instead in a single POSTUTIL application if afile of background concentrations is provided (BCKGALM in Input Group 0).Required information for MNITRATE=1 includes:

species NO3, HNO3, and SO4NH3 concentration(s)met. data file for RH and T

Required information for MNITRATE=2 includes:

species NO3 and HNO3 for a source groupspecies NO3ALL and HNO3ALL for all source groups, properlypartitioned

Required information for MNITRATE=3 includes:

species NO3, HNO3, and SO4 for a source groupspecies NO3, HNO3, SO4 and TNH3 from the background BCKGALM fileIf TNH3 is not in the background BCKGALM file, monthly TNH3concentrations are used (BCKTNH3)TNH3= total NH3 = NH3gaseous+NH3particulate

Recompute the HNO3/NO3 partition for concentrations?(MNITRATE) Default: 0 ! MNITRATE = 1 !

0 = no1 = yes, for all sources combined2 = yes, for a source group3 = yes, ALM application in one step

SOURCE OF AMMONIA:Ammonia may be available as a modeled species in the CALPUFF files,and it may or may not be appropriate to use it for repartitioning NO3/HNO3(in option MNITRATE=1 or MNITRATE=3). Its use is contolled by NH3TYP.When NH3 is listed as a processed species in Subgroup (2a), as one ofthe NSPECINP ASPECI entries, and the right option is chosen for NH3TYP,the NH3 modeled values from the CALPUFF concentration files will be usedin the chemical equilibrium calculation.NH3TYP also controls when monthly background ammonia values are used. Bothgaseous (NH3) and total (TNH3=NH3gaseous+NH3particulate) ammonia can be providedmonthly as BCKNH3/BCKTNH3.

What is the input source of Ammonia?

5
UTINVCAM02B1.inp 

(NH3TYP) No Default ! NH3TYP = 3 !

0 = No background will be used.

ONLY NH3 or TNH3 from the concentrationfiles listed in Subgroup (2a&2b) asa processed species will be used.(Cannot be used with MNITRATE=3)

1 = NH3 Monthly averaged background (BCKNH3)

listed below will be added to NH3 fromconcentration files listed in Subgroup (2a)

2 = NH3 from background concentration file BCKGALM

will be added to NH3 from concentration fileslisted in Subgroup (2a&2b)(ONLY possible for MNITRATE=3)

3 = NH3 Monthly averaged background (BCKNH3)

listed below will be used alone.

4 = NH3 from background concentration file BCKGALM

will be used alone(ONLY possible for MNITRATE=3)

| OPTION | NH3 or TNH3 CONC | BCKNH3 or BCKTNH3 | TNH3/BCKGALM or BCKTNH3 ||--------|------------------|-------------------|-------------------------|| 0 | X | 0 | 0 ||--------|------------------|-------------------|-------------------------|| 1 | X | X | 0 ||--------|------------------|-------------------|-------------------------|| 2 | X | 0 | X ||--------|------------------|-------------------|-------------------------|| 3 | 0 | X | 0 ||--------|------------------|-------------------|-------------------------|| 4 | 0 | 0 | X ||--------|------------------|-------------------|-------------------------|

Default monthly (12 values) background ammonia concentration (ppb)used for HNO3/NO3 partition (need to choose one or the other):

Gaseous NH3 (BCKNH3) Default: -999! BCKNH3 = 12*0.5 !Total TNH3 (BCKTNH3) Default: -999* BCKTNH3 = 1., 1., 1., 1.1, 1.4, 1.3, 1.3, 1.2, 4*1. *

If a single value is entered, this is used for all 12 months.Month 1 is JANUARY, Month 12 is DECEMBER.

6
UTINVCAM02B1.inp 

!END!-------------------------------------------------------------------------------INPUT GROUP: 2 -- Species Processing Information---------------------------Subgroup (2a)-------------

The following NSPECINP species will be processed:

! 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)-------------

The following NSPECOUT species will be written:

! 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!

7
UTINVCAM02B1.inp 

! 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)-------------

The following NSPECCMP species will be computed by scaling and summingone or more of the processed input species. Identify the name(s) ofthe computed species and provide the scaling factors for each of theNSPECINP input species (NSPECCMP groups of NSPECINP+1 lines each):

* *-------------Subgroup (2d)-------------

Each species in NSCALED CALPUFF data files may be scaled before beingprocessed (e.g., to change the emission rate for all sources modeledin the run that produced a data file). For each file, identify thefile name and then provide the name(s) of the scaled species and thecorresponding scaling factors (A,B where x' = 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
UTINVCAM02C1.inp 

INVISTA CAMDEN - Combine PM SpeciesBART REFINED ANALYSIS 4 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 Update 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

POSTUTIL MODEL CONTROL FILE---------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names---------------------------Subgroup (0a)-------------Output Files------------

File Default File Name---- -----------------List File POSTUTIL.LST ! UTLLST =UTINVCAM02C1.lst !Data File MODEL.DAT ! UTLDAT =UTINVCAM02C1.con !

Input Files-----------

A time-varying file of "background" concentrations can be includedwhen the ammonia-limiting method (ALM) for setting the HNO3/NO3concentration partition is accomplished in 1 step. This optionis selected by setting MNITRATE=3 in Input Group 1.Species required in the "background" concentration file are:SO4, NO3, HNO3 and TNH3 (total NH3 = NH3gaseous + NH3particulate).File Default File Name---- -----------------BCKG File BCKGALM.DAT * BCKGALM =BCKGALM.DAT *A number of CALPUFF data files may be processed in this application.The files may represent individual CALPUFF simulations that were madefor a specific set of species and/or sources. Specify the total numberof CALPUFF runs you wish to combine, and provide the filename for eachin subgroup 0b.

Number of CALPUFF data files (NFILES)

1
UTINVCAM02C1.inp 

Default: 1 ! NFILES = 1 !

Meteorological data files are needed for the HNO3/NO3 partition option.Three types of meteorological data files can be used:

METFM= 0 - CALMET.DATMETFM= 1 - 1-D file with RH, Temp and Rhoair timeseriesMETFM= 2 - 2-D files with either Rh, Temp or Rhoair in each

(3 2_D files are needed)

The default is to use CALMET.DAT files.

Default: 0 ! METFM = 0 !

Multiple meteorological data files may be used in sequence to span theprocessing period. Specify the number of time-period files (NMET) thatyou need to use, and provide a filename for each in subgroup 0b.- NMET is 0 if no meteorological files are provided- NMET is 1 if METFM=1 (multiple file feature is not available)- NMET is 1 or more if METFM=0 or 2 (multiple CALMET files or 2DMET files)

Number of meteorological data file time-periods (NMET)

Default: 0 ! NMET = 12 !

All filenames will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, filenames will be converted to UPPER CASE

Convert filenames to lower case? Default: T ! LCFILES = T !

T = lower caseF = UPPER CASE

!END!-----------------------------------------------------------

NOTE: file/path names can be up to 70 characters in length

------------------------------------------------------------------------Subgroup (0b)-------------NMET CALMET Data Files (METFM=0):Input File Default File Name---------- -----------------

1 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-09A.DAT ! !EN2 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-09B.DAT ! !EN

2
UTINVCAM02C1.inp 

3 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-09C.DAT ! !EN4 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-10A.DAT ! !EN5 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-10B.DAT ! !EN6 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-10C.DAT ! !EN7 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-11A.DAT ! !EN8 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-11B.DAT ! !EN9 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-11C.DAT ! !EN

10 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-12A.DAT ! !EN11 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-12B.DAT ! !EN12 MET.DAT ! UTLMET=T:\VISTAS\Domain4-2002\MET2002-DOM4-12C.DAT ! !EN

NMET 1-D Data Files (METFM=1):Input File Default File Name---------- -----------------

1 MET_1D.DAT * MET1D = MET_1D.DAT * *END*

NMET 2-D Data Files of Each Type (METFM=2):Input File Default File Name---------- -----------------

1 RHUMD.DAT * M2DRHU = RELHUM.DAT * *END*1 TEMP.DAT * M2DTMP = TEMP.DAT * *END*1 RHOAIR.DAT * M2DRHO = RHOAIR.DAT * *END*

NFILES CALPUFF Data Files:Input File Default File Name---------- -----------------

1 CALPUFF.DAT ! MODDAT =INVCAM02.con ! !END!

-------------Note: provide NMET lines of the form * UTLMET = name * *END*

or * MET1D = name * *END*or * M2DRHU = name * *END*

(and) * M2DTMP = name * *END*(and) * M2DRHO = name * *END*

and NFILES lines of the form * MODDAT = name * *END*where the * should be replaced with an exclamation point,the special delimiter character.

3
UTINVCAM02C1.inp 

--------------------------------------------------------------------------------INPUT GROUP: 1 -- General run control parameters--------------

Starting date: Year (ISYR) -- No default ! ISYR = 2002 !

Month (ISMO) -- No default ! ISMO = 9 !Day (ISDY) -- No default ! ISDY = 1 !Hour (ISHR) -- No default ! ISHR = 1 !

Number of periods to process

(NPER) -- No default ! NPER = 2928 !

Number of species to process from CALPUFF runs

(NSPECINP) -- No default ! NSPECINP = 19 !

Number of species to write to output file

(NSPECOUT) -- No default ! NSPECOUT = 19 !

Number of species to compute from those modeled(must be no greater than NSPECOUT)

(NSPECCMP) -- No default ! NSPECCMP = 0 !

When multiple files are used, a species name may appear in more thanone file. Data for this species will be summed (appropriate if theCALPUFF runs use different source groups). If this summing is notappropriate, remove duplicate species from the file(s).

Stop run if duplicate species namesare found? (MDUPLCT) Default: 0 ! MDUPLCT = 0 !

0 = no (i.e., duplicate species are summed)1 = yes (i.e., run is halted)

Data for each species in a CALPUFF data file may also be scaled asthey are read. This can be done to alter the emission rate of allsources that were modeled in a particular CALPUFF application.The scaling factor for each species is entered in Subgroup (2d), foreach file for which scaling is requested.

Number of CALPUFF data files that will be scaled(must be no greater than NFILES)(NSCALED) Default: 0 ! NSCALED = 0 !

Ammonia-Limiting Method Option to recompute the HNO3/NO3 concentrationpartition prior to performing other actions is controlled by MNITRATE.This option will NOT alter any deposition fluxes contained in the CALPUFF

4
UTINVCAM02C1.inp 

file(s). Three partition selections are provided. The first two aretypically used in sequence (POSTUTIL is run more than once). The firstselection (MNITRATE=1) computes the partition for the TOTAL (all sources)concentration fields (SO4, NO3, HNO3; NH3), and the second (MNITRATE=2)uses this partition (from the previous application of POSTUTIL) tocompute the partition for individual source groups. The third selection(MNITRATE=3) can be used instead in a single POSTUTIL application if afile of background concentrations is provided (BCKGALM in Input Group 0).Required information for MNITRATE=1 includes:

species NO3, HNO3, and SO4NH3 concentration(s)met. data file for RH and T

Required information for MNITRATE=2 includes:

species NO3 and HNO3 for a source groupspecies NO3ALL and HNO3ALL for all source groups, properlypartitioned

Required information for MNITRATE=3 includes:

species NO3, HNO3, and SO4 for a source groupspecies NO3, HNO3, SO4 and TNH3 from the background BCKGALM fileIf TNH3 is not in the background BCKGALM file, monthly TNH3concentrations are used (BCKTNH3)TNH3= total NH3 = NH3gaseous+NH3particulate

Recompute the HNO3/NO3 partition for concentrations?(MNITRATE) Default: 0 ! MNITRATE = 1 !

0 = no1 = yes, for all sources combined2 = yes, for a source group3 = yes, ALM application in one step

SOURCE OF AMMONIA:Ammonia may be available as a modeled species in the CALPUFF files,and it may or may not be appropriate to use it for repartitioning NO3/HNO3(in option MNITRATE=1 or MNITRATE=3). Its use is contolled by NH3TYP.When NH3 is listed as a processed species in Subgroup (2a), as one ofthe NSPECINP ASPECI entries, and the right option is chosen for NH3TYP,the NH3 modeled values from the CALPUFF concentration files will be usedin the chemical equilibrium calculation.NH3TYP also controls when monthly background ammonia values are used. Bothgaseous (NH3) and total (TNH3=NH3gaseous+NH3particulate) ammonia can be providedmonthly as BCKNH3/BCKTNH3.

What is the input source of Ammonia?

5
UTINVCAM02C1.inp 

(NH3TYP) No Default ! NH3TYP = 3 !

0 = No background will be used.

ONLY NH3 or TNH3 from the concentrationfiles listed in Subgroup (2a&2b) asa processed species will be used.(Cannot be used with MNITRATE=3)

1 = NH3 Monthly averaged background (BCKNH3)

listed below will be added to NH3 fromconcentration files listed in Subgroup (2a)

2 = NH3 from background concentration file BCKGALM

will be added to NH3 from concentration fileslisted in Subgroup (2a&2b)(ONLY possible for MNITRATE=3)

3 = NH3 Monthly averaged background (BCKNH3)

listed below will be used alone.

4 = NH3 from background concentration file BCKGALM

will be used alone(ONLY possible for MNITRATE=3)

| OPTION | NH3 or TNH3 CONC | BCKNH3 or BCKTNH3 | TNH3/BCKGALM or BCKTNH3 ||--------|------------------|-------------------|-------------------------|| 0 | X | 0 | 0 ||--------|------------------|-------------------|-------------------------|| 1 | X | X | 0 ||--------|------------------|-------------------|-------------------------|| 2 | X | 0 | X ||--------|------------------|-------------------|-------------------------|| 3 | 0 | X | 0 ||--------|------------------|-------------------|-------------------------|| 4 | 0 | 0 | X ||--------|------------------|-------------------|-------------------------|

Default monthly (12 values) background ammonia concentration (ppb)used for HNO3/NO3 partition (need to choose one or the other):

Gaseous NH3 (BCKNH3) Default: -999! BCKNH3 = 12*0.5 !Total TNH3 (BCKTNH3) Default: -999* BCKTNH3 = 1., 1., 1., 1.1, 1.4, 1.3, 1.3, 1.2, 4*1. *

If a single value is entered, this is used for all 12 months.Month 1 is JANUARY, Month 12 is DECEMBER.

6
UTINVCAM02C1.inp 

!END!-------------------------------------------------------------------------------INPUT GROUP: 2 -- Species Processing Information---------------------------Subgroup (2a)-------------

The following NSPECINP species will be processed:

! 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)-------------

The following NSPECOUT species will be written:

! 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!

7
UTINVCAM02C1.inp 

! 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)-------------

The following NSPECCMP species will be computed by scaling and summingone or more of the processed input species. Identify the name(s) ofthe computed species and provide the scaling factors for each of theNSPECINP input species (NSPECCMP groups of NSPECINP+1 lines each):

* *-------------Subgroup (2d)-------------

Each species in NSCALED CALPUFF data files may be scaled before beingprocessed (e.g., to change the emission rate for all sources modeledin the run that produced a data file). For each file, identify thefile name and then provide the name(s) of the scaled species and thecorresponding scaling factors (A,B where x' = 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 2002 

Appendix H.6 - 805
UTINVCAM02.inp 

INVISTA CAMDEN - Combine PM SpeciesBART REFINED ANALYSIS 4 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 Update 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

POSTUTIL MODEL CONTROL FILE---------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names---------------------------Subgroup (0a)-------------Output Files------------

File Default File Name---- -----------------List File POSTUTIL.LST ! UTLLST =UTINVCAM02ALM.LST !Data File MODEL.DAT ! UTLDAT =UTINVCAM02ALM.CON !

Input Files-----------

A time-varying file of "background" concentrations can be includedwhen the ammonia-limiting method (ALM) for setting the HNO3/NO3concentration partition is accomplished in 1 step. This optionis selected by setting MNITRATE=3 in Input Group 1.Species required in the "background" concentration file are:SO4, NO3, HNO3 and TNH3 (total NH3 = NH3gaseous + NH3particulate).File Default File Name---- -----------------BCKG File BCKGALM.DAT * BCKGALM =BCKGALM.DAT *A number of CALPUFF data files may be processed in this application.The files may represent individual CALPUFF simulations that were madefor a specific set of species and/or sources. Specify the total numberof CALPUFF runs you wish to combine, and provide the filename for eachin subgroup 0b.

Number of CALPUFF data files (NFILES)

1
UTINVCAM02.inp 

Default: 1 ! NFILES = 1 !

Meteorological data files are needed for the HNO3/NO3 partition option.Three types of meteorological data files can be used:

METFM= 0 - CALMET.DATMETFM= 1 - 1-D file with RH, Temp and Rhoair timeseriesMETFM= 2 - 2-D files with either Rh, Temp or Rhoair in each

(3 2_D files are needed)

The default is to use CALMET.DAT files.

Default: 0 ! METFM = 0 !

Multiple meteorological data files may be used in sequence to span theprocessing period. Specify the number of time-period files (NMET) thatyou need to use, and provide a filename for each in subgroup 0b.- NMET is 0 if no meteorological files are provided- NMET is 1 if METFM=1 (multiple file feature is not available)- NMET is 1 or more if METFM=0 or 2 (multiple CALMET files or 2DMET files)

Number of meteorological data file time-periods (NMET)

Default: 0 ! NMET = 0 !

All filenames will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, filenames will be converted to UPPER CASE

Convert filenames to lower case? Default: T ! LCFILES = T !

T = lower caseF = UPPER CASE

!END!-----------------------------------------------------------

NOTE: file/path names can be up to 70 characters in length

------------------------------------------------------------------------Subgroup (0b)-------------NMET CALMET Data Files (METFM=0):Input File Default File Name---------- -----------------

1 MET.DAT * UTLMET =CALMET.DAT *

2
UTINVCAM02.inp 

NMET 1-D Data Files (METFM=1):Input File Default File Name---------- -----------------

1 MET_1D.DAT * MET1D = MET_1D.DAT * *END*

NMET 2-D Data Files of Each Type (METFM=2):Input File Default File Name---------- -----------------

1 RHUMD.DAT * M2DRHU = RELHUM.DAT * *END*1 TEMP.DAT * M2DTMP = TEMP.DAT * *END*1 RHOAIR.DAT * M2DRHO = RHOAIR.DAT * *END*

NFILES CALPUFF Data Files:Input File Default File Name---------- -----------------

1 CALPUFF.DAT ! MODDAT =UTINVCAM02S1.con ! !END!

-------------Note: provide NMET lines of the form * UTLMET = name * *END*

or * MET1D = name * *END*or * M2DRHU = name * *END*

(and) * M2DTMP = name * *END*(and) * M2DRHO = name * *END*

and NFILES lines of the form * MODDAT = name * *END*where the * should be replaced with an exclamation point,the special delimiter character.

--------------------------------------------------------------------------------INPUT GROUP: 1 -- General run control parameters--------------

Starting date: Year (ISYR) -- No default ! ISYR = 2002 !

Month (ISMO) -- No default ! ISMO = 1 !Day (ISDY) -- No default ! ISDY = 1 !Hour (ISHR) -- No default ! ISHR = 1 !

3
UTINVCAM02.inp 

Number of periods to process

(NPER) -- No default ! NPER = 8760 !

Number of species to process from CALPUFF runs

(NSPECINP) -- No default ! NSPECINP = 19 !

Number of species to write to output file

(NSPECOUT) -- No default ! NSPECOUT = 9 !

Number of species to compute from those modeled(must be no greater than NSPECOUT)

(NSPECCMP) -- No default ! NSPECCMP = 4 !

When multiple files are used, a species name may appear in more thanone file. Data for this species will be summed (appropriate if theCALPUFF runs use different source groups). If this summing is notappropriate, remove duplicate species from the file(s).

Stop run if duplicate species namesare found? (MDUPLCT) Default: 0 ! MDUPLCT = 0 !

0 = no (i.e., duplicate species are summed)1 = yes (i.e., run is halted)

Data for each species in a CALPUFF data file may also be scaled asthey are read. This can be done to alter the emission rate of allsources that were modeled in a particular CALPUFF application.The scaling factor for each species is entered in Subgroup (2d), foreach file for which scaling is requested.

Number of CALPUFF data files that will be scaled(must be no greater than NFILES)(NSCALED) Default: 0 ! NSCALED = 0 !

Ammonia-Limiting Method Option to recompute the HNO3/NO3 concentrationpartition prior to performing other actions is controlled by MNITRATE.This option will NOT alter any deposition fluxes contained in the CALPUFFfile(s). Three partition selections are provided. The first two aretypically used in sequence (POSTUTIL is run more than once). The firstselection (MNITRATE=1) computes the partition for the TOTAL (all sources)concentration fields (SO4, NO3, HNO3; NH3), and the second (MNITRATE=2)uses this partition (from the previous application of POSTUTIL) tocompute the partition for individual source groups. The third selection(MNITRATE=3) can be used instead in a single POSTUTIL application if afile of background concentrations is provided (BCKGALM in Input Group 0).Required information for MNITRATE=1 includes:

species NO3, HNO3, and SO4

4
UTINVCAM02.inp 

NH3 concentration(s)met. data file for RH and T

Required information for MNITRATE=2 includes:

species NO3 and HNO3 for a source groupspecies NO3ALL and HNO3ALL for all source groups, properlypartitioned

Required information for MNITRATE=3 includes:

species NO3, HNO3, and SO4 for a source groupspecies NO3, HNO3, SO4 and TNH3 from the background BCKGALM fileIf TNH3 is not in the background BCKGALM file, monthly TNH3concentrations are used (BCKTNH3)TNH3= total NH3 = NH3gaseous+NH3particulate

Recompute the HNO3/NO3 partition for concentrations?(MNITRATE) Default: 0 ! MNITRATE = 0 !

0 = no1 = yes, for all sources combined2 = yes, for a source group3 = yes, ALM application in one step

SOURCE OF AMMONIA:Ammonia may be available as a modeled species in the CALPUFF files,and it may or may not be appropriate to use it for repartitioning NO3/HNO3(in option MNITRATE=1 or MNITRATE=3). Its use is contolled by NH3TYP.When NH3 is listed as a processed species in Subgroup (2a), as one ofthe NSPECINP ASPECI entries, and the right option is chosen for NH3TYP,the NH3 modeled values from the CALPUFF concentration files will be usedin the chemical equilibrium calculation.NH3TYP also controls when monthly background ammonia values are used. Bothgaseous (NH3) and total (TNH3=NH3gaseous+NH3particulate) ammonia can be providedmonthly as BCKNH3/BCKTNH3.

What is the input source of Ammonia?(NH3TYP) No Default ! NH3TYP = 3 !

0 = No background will be used.

ONLY NH3 or TNH3 from the concentrationfiles listed in Subgroup (2a&2b) asa processed species will be used.(Cannot be used with MNITRATE=3)

1 = NH3 Monthly averaged background (BCKNH3)

listed below will be added to NH3 fromconcentration files listed in Subgroup (2a)

5
UTINVCAM02.inp 

2 = NH3 from background concentration file BCKGALM

will be added to NH3 from concentration fileslisted in Subgroup (2a&2b)(ONLY possible for MNITRATE=3)

3 = NH3 Monthly averaged background (BCKNH3)

listed below will be used alone.

4 = NH3 from background concentration file BCKGALM

will be used alone(ONLY possible for MNITRATE=3)

| OPTION | NH3 or TNH3 CONC | BCKNH3 or BCKTNH3 | TNH3/BCKGALM or BCKTNH3 ||--------|------------------|-------------------|-------------------------|| 0 | X | 0 | 0 ||--------|------------------|-------------------|-------------------------|| 1 | X | X | 0 ||--------|------------------|-------------------|-------------------------|| 2 | X | 0 | X ||--------|------------------|-------------------|-------------------------|| 3 | 0 | X | 0 ||--------|------------------|-------------------|-------------------------|| 4 | 0 | 0 | X ||--------|------------------|-------------------|-------------------------|

Default monthly (12 values) background ammonia concentration (ppb)used for HNO3/NO3 partition (need to choose one or the other):

Gaseous NH3 (BCKNH3) Default: -999! BCKNH3 = 12*0.5 !Total TNH3 (BCKTNH3) Default: -999* BCKTNH3 = 1., 1., 1., 1.1, 1.4, 1.3, 1.3, 1.2, 4*1. *

If a single value is entered, this is used for all 12 months.Month 1 is JANUARY, Month 12 is DECEMBER.

!END!-------------------------------------------------------------------------------INPUT GROUP: 2 -- Species Processing Information---------------------------Subgroup (2a)-------------

The following NSPECINP species will be processed:

6
UTINVCAM02.inp 

! 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)-------------

The following NSPECOUT species will be written:

! 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)-------------

The following NSPECCMP species will be computed by scaling and summingone or more of the processed input species. Identify the name(s) ofthe computed species and provide the scaling factors for each of theNSPECINP input species (NSPECCMP groups of NSPECINP+1 lines each):

! CSPECCMP = EC !

7
UTINVCAM02.inp 

! 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)-------------

Each species in NSCALED CALPUFF data files may be scaled before beingprocessed (e.g., to change the emission rate for all sources modeledin the run that produced a data file). For each file, identify thefile name and then provide the name(s) of the scaled species and thecorresponding scaling factors (A,B where x' = 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 AVERAGE NATURAL BACKGROUND 

Appendix H.6 - 814
VANINVCAM02CR.inp 

INVISTA CAMDEN - Visibility with Annual Background CAPE ROMAINBART REFINED ANALYSIS 4 KM RUN 2002SPECIATED PM MJZ/FAH 04.17.2006 Update 05.31.2006 w/DHEC ITP Guidance---------------- Run title (3 lines) ------------------------------------------

CALPOST MODEL CONTROL FILE--------------------------

-------------------------------------------------------------------------------INPUT GROUP: 0 -- Input and Output File Names--------------Input Files-----------File Default File Name---- -----------------Conc/Dep Flux File MODEL.DAT ! MODDAT =UTINVCAM02ALM.con !Relative Humidity File VISB.DAT * VISDAT = *Background Data File BACK.DAT * BACKDAT = *Transmissometer or VSRN.DAT * VSRDAT = *Nephelometer Data File orDATSAV Weather Data File orPrognostic Weather FileOutput Files------------File Default File Name---- -----------------List File CALPOST.LST ! PSTLST =VANINVCAM02CR.lst !Pathname for Timeseries Files (blank) * TSPATH = *(activate with exclamation points only ifproviding NON-BLANK character string)Pathname for Plot Files (blank) * PLPATH = *(activate with exclamation points only if

providing NON-BLANK character string)

User Character String (U) to augment default filenames(activate with exclamation points only if

providing NON-BLANK character string)

Timeseries TSERIES_ASPEC_ttHR_CONC_TSUNAM.DATPeak Value PEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DAT

* TSUNAM = *

1
VANINVCAM02CR.inp 

Top Nth Rank Plot RANK(ALL)_ASPEC_ttHR_CONC_TUNAM.DAT

or RANK(ii)_ASPEC_ttHR_CONC_TUNAM.GRD

* TUNAM = *

Exceedance Plot EXCEED_ASPEC_ttHR_CONC_XUNAM.DAT

or EXCEED_ASPEC_ttHR_CONC_XUNAM.GRD

* XUNAM = *

Echo Plot(Specific Days)

yyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.DAT

or yyyy_Mmm_Ddd_hh00(UTCszzzz)_L00_ASPEC_ttHR_CONC.GRD

Visibility Plot DAILY_VISIB_VUNAM.DAT * VUNAM = *(Daily Peak Summary)Auxiliary Output Files----------------------File Default File Name---- -----------------Visibility Change DELVIS.DAT * DVISDAT = *--------------------------------------------------------------------------------All file names will be converted to lower case if LCFILES = TOtherwise, if LCFILES = F, file names will be converted to UPPER CASE

T = lower case ! LCFILES = T !F = UPPER CASE

NOTE: (1) file/path names can be up to 132 characters in lengthNOTE: (2) Filenames for ALL PLOT and TIMESERIES FILES are constructed

using a template that includes a pathname, user-suppliedcharacter(s), and context-specific strings, where

ASPEC = Species Name

CONC = CONC Or WFLX Or DFLX Or TFLX

tt = Averaging Period (e.g. 03)ii = Rank (e.g. 02)hh = Hour(ending) in LST

szzzz = Base time zone shift from UTC (EST is -0500)

yyyy = Year(LST)

mm = Month(LST)dd = day of month (LST)

are determined internally based on selections made below.If a path or user-supplied character(s) are supplied, each

2
VANINVCAM02CR.inp 

must contain at least 1 non-blank character.

!END!--------------------------------------------------------------------------------INPUT GROUP: 1 -- General run control parameters--------------

Option to run all periods foundin the met. file(s) (METRUN) Default: 0 ! METRUN = 0 !

METRUN = 0 - Run period explicitly defined belowMETRUN = 1 - Run all periods in CALPUFF data file(s)

Starting date: Year (ISYR) -- No default ! ISYR = 2002 !(used only if Month (ISMO) -- No default ! ISMO = 1 !

METRUN = 0) Day (ISDY) -- No default ! ISDY = 1 !

Hour (ISHR) -- No default ! ISHR = 1 !

Number of hours to process (NHRS) -- No default ! NHRS = 8760 !Process every hour of data?(NREP) -- Default: 1 ! NREP = 1 !

(1 = every hour processed,

2 = every 2nd hour processed,5 = every 5th hour processed, etc.)

Species & Concentration/Deposition Information----------------------------------------------

Species to process (ASPEC) -- No default ! ASPEC = VISIB !(ASPEC = VISIB for visibility processing)Layer/deposition code (ILAYER) -- Default: 1 ! ILAYER = 1 !

'1' for CALPUFF concentrations,'-1' for dry deposition fluxes,'-2' for wet deposition fluxes,'-3' for wet+dry deposition fluxes.

Scaling factors of the form: -- Defaults: ! A = 0.0 !

X(new) = X(old) * A + B A = 0.0 ! B = 0.0 !

(NOT applied if A = B = 0.0) B = 0.0

Add Hourly Background Concentrations/Fluxes?

(LBACK) -- Default: F ! LBACK = F !

Source information------------------

Option to process source contributions:

3
VANINVCAM02CR.inp 

0 = Process only total reported contributions1 = Sum all individual source contributions and process2 = Run in TRACEBACK mode to identify source

contributions at a SINGLE receptor

(MSOURCE) -- Default: 0 ! MSOURCE = 0 !

Receptor information--------------------

Gridded receptors processed? (LG) -- Default: F ! LG = F !Discrete receptors processed? (LD) -- Default: F ! LD = T !CTSG Complex terrain receptors processed?

(LCT) -- Default: F ! LCT = F !

--Report results by DISCRETE receptor RING?

(only used when LD = T) (LDRING) -- Default: F ! LDRING = F !

--Select range of DISCRETE receptors (only used when LD = T):

Select ALL DISCRETE receptors by setting NDRECP flag to -1;

OR

Select SPECIFIC DISCRETE receptors by entering a flag (0,1) for each

0 = discrete receptor not processed1 = discrete receptor processed

using repeated value notation to select blocks of receptors:Flag for all receptors after the last one assigned is set to 0(NDRECP) -- Default: -1

! NDRECP = 164*1, 736*0, 66*0, 110*0 !

--Select range of GRIDDED receptors (only used when LG = T):

X index of LL corner (IBGRID) -- Default: -1 ! IBGRID = -1 !

(-1 OR 1 <= IBGRID <= NX)

Y index of LL corner (JBGRID) -- Default: -1 ! JBGRID = -1 !

(-1 OR 1 <= JBGRID <= NY)

X index of UR corner (IEGRID) -- Default: -1 ! IEGRID = -1 !

(-1 OR 1 <= IEGRID <= NX)

Y index of UR corner (JEGRID) -- Default: -1 ! JEGRID = -1 !

(-1 OR 1 <= JEGRID <= NY)

Note: Entire grid is processed if IBGRID=JBGRID=IEGRID=JEGRID=-1

--Specific gridded receptors can also be excluded from CALPOST

4
VANINVCAM02CR.inp 

processing by filling a processing grid array with 0s and 1s. If theprocessing flag for receptor index (i,j) is 1 (ON), that receptorwill be processed if it lies within the range delineated by IBGRID,JBGRID,IEGRID,JEGRID and if LG=T. If it is 0 (OFF), it will not beprocessed in the run. By default, all array values are set to 1 (ON).Number of gridded receptor rows provided in Subgroup (1a) toidentify specific gridded receptors to process

(NGONOFF) -- Default: 0 ! NGONOFF = 0 !

!END!--------------Subgroup (1a) -- Specific gridded receptors included/excluded--------------

Specific gridded receptors are excluded from CALPOST processingby filling a processing grid array with 0s and 1s. A total ofNGONOFF lines are read here. Each line corresponds to one 'row'in the sampling grid, starting with the NORTHERNMOST row thatcontains receptors that you wish to exclude, and finishing withrow 1 to the SOUTH (no intervening rows may be skipped). Withina row, each receptor position is assigned either a 0 or 1,starting with the westernmost receptor.

0 = gridded receptor not processed1 = gridded receptor processed

Repeated value notation may be used to select blocks of receptors:

23*1, 15*0, 12*1

Because all values are initially set to 1, any receptors north ofthe first row entered, or east of the last value provided in a row,remain ON.(NGXRECP) -- Default: 1

-------------------------------------------------------------------------------INPUT GROUP: 2 -- Visibility Parameters (ASPEC = VISIB)--------------

Identify the Base Time Zone for the CALPUFF simulation

(BTZONE) -- No default ! BTZONE = 5.0 !

Particle growth curve f(RH) for hygroscopic species

(MFRH) -- Default: 2 ! MFRH = 2 !

5
VANINVCAM02CR.inp 

1 = IWAQM (1998) f(RH) curve (originally used with MVISBK=1)2 = FLAG (2000) f(RH) tabulation3 = EPA (2003) f(RH) tabulation

Maximum relative humidity (%) used in particle growth curve

(RHMAX) -- Default: 98 ! RHMAX = 95.0 !

Modeled species to be included in computing the light extinction

Include SULFATE? (LVSO4) -- Default: T ! LVSO4 = T !Include NITRATE? (LVNO3) -- Default: T ! LVNO3 = T !Include ORGANIC CARBON? (LVOC) -- Default: T ! LVOC = T !Include COARSE PARTICLES? (LVPMC) -- Default: T ! LVPMC = T !Include FINE PARTICLES? (LVPMF) -- Default: T ! LVPMF = T !Include ELEMENTAL CARBON? (LVEC) -- Default: T ! LVEC = T !

And, when ranking for TOP-N, TOP-50, and Exceedance tables,

Include BACKGROUND? (LVBK) -- Default: T ! LVBK = T !

Species name used for particulates in MODEL.DAT file

COARSE (SPECPMC) -- Default: PMC ! SPECPMC = PMC !FINE (SPECPMF) -- Default: PMF ! SPECPMF = SOIL !

Extinction Efficiency (1/Mm per ug/m**3)----------------------------------------

MODELED particulate species:

PM COARSE (EEPMC) -- Default: 0.6 ! EEPMC = 0.6 !PM FINE (EEPMF) -- Default: 1.0 ! EEPMF = 1.0 !

BACKGROUND particulate species:

PM COARSE (EEPMCBK) -- Default: 0.6 ! EEPMCBK = 0.6 !

Other species:

AMMONIUM SULFATE (EESO4) -- Default: 3.0 ! EESO4 = 3.0 !AMMONIUM NITRATE (EENO3) -- Default: 3.0 ! EENO3 = 3.0 !ORGANIC CARBON (EEOC) -- Default: 4.0 ! EEOC = 4.0 !SOIL (EESOIL)-- Default: 1.0 ! EESOIL = 1.0 !ELEMENTAL CARBON (EEEC) -- Default: 10. ! EEEC = 10.0 !

Background Extinction Computation---------------------------------

Method used for the 24h-average of percent change of light extinction:Hourly ratio of source light extinction / background light extinctionis averaged? (LAVER) -- Default: F ! LAVER = F !Method used for background light extinction

(MVISBK) -- Default: 2 ! MVISBK = 6 !

1 = Supply single light extinction and hygroscopic fraction

- Hourly F(RH) adjustment applied to hygroscopic background

6
VANINVCAM02CR.inp 

and modeled sulfate and nitrate

2 = Compute extinction from speciated PM measurements (A)

- Hourly F(RH) adjustment applied to observed and modeled sulfate

and nitrate

- F(RH) factor is capped at F(RHMAX)

3 = Compute extinction from speciated PM measurements (B)

- Hourly F(RH) adjustment applied to observed and modeled sulfate

and nitrate

- Receptor-hour excluded if RH>RHMAX- Receptor-day excluded if fewer than 6 valid receptor-hours

4 = Read hourly transmissometer background extinction measurements

- Hourly F(RH) adjustment applied to modeled sulfate and nitrate- Hour excluded if measurement invalid (missing, interference,

or large RH)

- Receptor-hour excluded if RH>RHMAX- Receptor-day excluded if fewer than 6 valid receptor-hours

5 = Read hourly nephelometer background extinction measurements

- Rayleigh extinction value (BEXTRAY) added to measurement- Hourly F(RH) adjustment applied to modeled sulfate and nitrate- Hour excluded if measurement invalid (missing, interference,

or large RH)

- Receptor-hour excluded if RH>RHMAX- Receptor-day excluded if fewer than 6 valid receptor-hours

6 = Compute extinction from speciated PM measurements

- FLAG monthly RH adjustment factor applied to observed and

modeled sulfate and nitrate

7 = Use observed weather or prognostic weather information for

background extinction during weather events; otherwise, use Method 2- Hourly F(RH) adjustment applied to modeled sulfate and nitrate- F(RH) factor is capped at F(RHMAX)- During observed weather events, compute Bext from visual range

if using an observed weather data file, or

- During prognostic weather events, use Bext from the prognostic

weather file

- Use Method 2 for hours without a weather event

Additional inputs used for MVISBK = 1:--------------------------------------

Background light extinction (1/Mm)

(BEXTBK) -- No default ! BEXTBK = 0.0 !

Percentage of particles affected by relative humidity

(RHFRAC) -- No default ! RHFRAC = 0.0 !

Additional inputs used for MVISBK = 6:--------------------------------------

Extinction coefficients for hygroscopic species (modeled andbackground) are computed using a monthly RH adjustment factorin place of an hourly RH factor (VISB.DAT file is NOT needed).Enter the 12 monthly factors here (RHFAC). Month 1 is January.

7
VANINVCAM02CR.inp 

(RHFAC) -- No default ! 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 !

Additional inputs used for MVISBK = 7:--------------------------------------

The weather data file (DATSAV abbreviated space-delimited) thatis identified as VSRN.DAT may contain data for more than onestation. Identify the stations that are needed in the order inwhich they will be used to obtain valid weather and visual range.The first station that contains valid data for an hour will beused. Enter up to MXWSTA (set in PARAMS file) integer station IDsof up to 6 digits each as variable IDWSTA, and enter the correspondingtime zone for each, as variable TZONE (= UTC-LST).A prognostic weather data file with Bext for weather events may be usedin place of the observed weather file. Identify this as the VSRN.DATfile and use a station ID of IDWSTA = 999999, and TZONE = 0.NOTE: TZONE identifies the time zone used in the dataset. The

DATSAV abbreviated space-delimited data usually are preparedwith UTC time rather than local time, so TZONE is typicallyset to zero.

(IDWSTA) -- No default

! IDWSTA = 999999 !

(TZONE) -- No default

! TZONE = 0.0 !Additional inputs used for MVISBK = 2,3,6,7:--------------------------------------------

Background extinction coefficients are computed from monthlyCONCENTRATIONS of ammonium sulfate (BKSO4), ammonium nitrate (BKNO3),coarse particulates (BKPMC), organic carbon (BKOC), soil (BKSOIL), andelemental carbon (BKEC). Month 1 is January.(ug/m**3)

(BKSO4) -- No default ! 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) -- No default ! 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) -- No default ! 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) -- No default ! BKOC = 0.00, 0.00, 0.00, 0.00,

0.00, 0.00, 0.00, 0.00,

8
VANINVCAM02CR.inp 

0.00, 0.00, 0.00, 0.00 !

(BKSOIL) -- No default ! 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) -- No default ! 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 !

Additional inputs used for MVISBK = 2,3,5,6,7:----------------------------------------------

Extinction due to Rayleigh scattering is added (1/Mm)

(BEXTRAY) -- Default: 10.0 ! BEXTRAY = 10.0 !

!END!-------------------------------------------------------------------------------INPUT GROUP: 3 -- Output options--------------Documentation-------------

Documentation records contained in the header of theCALPUFF output file may be written to the list file.Print documentation image?

(LDOC) -- Default: F ! LDOC = F !

Output Units------------

Units for All Output (IPRTU) -- Default: 1 ! IPRTU = 3 !

for for

Concentration Deposition

1 = g/m**3 g/m**2/s2 = mg/m**3 mg/m**2/s3 = ug/m**3 ug/m**2/s4 = ng/m**3 ng/m**2/s5 = Odour Units

Visibility: extinction expressed in 1/Mega-meters (IPRTU is ignored)

Averaging time(s) reported--------------------------

1-hr averages (L1HR) -- Default: T ! L1HR = F !3-hr averages (L3HR) -- Default: T ! L3HR = F !24-hr averages (L24HR) -- Default: T ! L24HR = T !

9
VANINVCAM02CR.inp 

Run-length averages (LRUNL) -- Default: T ! LRUNL = F !User-specified averaging time in hours - results foran averaging time of NAVG hours are reported forNAVG greater than 0:

(NAVG) -- Default: 0 ! NAVG = 0 !

Types of tabulations reported------------------------------

1) Visibility: daily visibility tabulations are always reported

for the selected receptors when ASPEC = VISIB.In addition, any of the other tabulations listedbelow may be chosen to characterize the lightextinction coefficients.[List file or Plot/Analysis File]

2) Top 50 table for each averaging time selected

[List file only]

(LT50) -- Default: T ! LT50 = F !

3) Top 'N' table for each averaging time selected

[List file or Plot file]

(LTOPN) -- Default: F ! LTOPN = T !

-- Number of 'Top-N' values at each receptor

selected (NTOP must be <= 4)

(NTOP) -- Default: 4 ! NTOP = 1 !

-- Specific ranks of 'Top-N' values reported

(NTOP values must be entered)

(ITOP(4) array) -- Default: ! ITOP = 1 !

1,2,3,4

4) Threshold exceedance counts for each receptor and each averaging

time selected[List file or Plot file]

(LEXCD) -- Default: F ! LEXCD = F !

-- Identify the threshold for each averaging time by assigning a

non-negative value (output units).

-- Default: -1.0

Threshold for 1-hr averages (THRESH1) ! THRESH1 = -1.0 !Threshold for 3-hr averages (THRESH3) ! THRESH3 = -1.0 !

10
VANINVCAM02CR.inp 

Threshold for 24-hr averages (THRESH24) ! THRESH24 = -1.0 !Threshold for NAVG-hr averages (THRESHN) ! THRESHN = -1.0 !

-- Counts for the shortest averaging period selected can be

tallied daily, and receptors that experience more than NCOUNTcounts over any NDAY period will be reported. This type ofexceedance violation output is triggered only if NDAY > 0.Accumulation period(Days)

(NDAY) -- Default: 0 ! NDAY = 0 !

Number of exceedances allowed

(NCOUNT) -- Default: 1 ! NCOUNT = 1 !

5) Selected day table(s)

Echo Option -- Many records are written each averaging periodselected and output is grouped by day[List file or Plot file]

(LECHO) -- Default: F ! LECHO = F !

Timeseries Option -- Averages at all selected receptors foreach selected averaging period are written to timeseries files.Each file contains one averaging period, and all receptors arewritten to a single record each averaging time.[TSERIES_ASPEC_ttHR_CONC_TSUNAM.DAT files]

(LTIME) -- Default: F ! LTIME = F !

Peak Value Option -- Averages at all selected receptors foreach selected averaging period are screened and the peak valueeach period is written to timeseries files.Each file contains one averaging period.[PEAKVAL_ASPEC_ttHR_CONC_TSUNAM.DAT files]

(LPEAK) -- Default: F ! LPEAK = F !

-- Days selected for output

(IECHO(366)) -- Default: 366*0

! IECHO = 366*0 !(366 values must be entered)

Plot output options-------------------

Plot files can be created for the Top-N, Exceedance, and Echotables selected above. Two formats for these files are available,DATA and GRID. In the DATA format, results at all receptors arelisted along with the receptor location [x,y,val1,val2,...].In the GRID format, results at only gridded receptors are written,

11
VANINVCAM02CR.inp 

using a compact representation. The gridded values are written inrows (x varies), starting with the most southern row of the grid.The GRID format is given the .GRD extension, and includes headerscompatible with the SURFER(R) plotting software.A plotting and analysis file can also be created for the dailypeak visibility summary output, in DATA format only.Generate Plot file output in addition to writing tablesto List file?

(LPLT) -- Default: F ! LPLT = F !

Use GRID format rather than DATA format,when available?

(LGRD) -- Default: F ! LGRD = F !

Auxiliary Output Files (for subsequent analyses)------------------------------------------------

VisibilityA separate output file may be requested that contains the changein visibility at each selected receptor when ASPEC = VISIB. Thisfile can be processed to construct visibility measures that arenot available in CALPOST.Output file with the visibility change at each receptor?

(MDVIS) -- Default: 0 ! MDVIS = 1 !

0 = Do Not create file1 = Create file of DAILY (24 hour) Delta-Deciview2 = Create file of DAILY (24 hour) Extinction Change (%)3 = Create file of HOURLY Delta-Deciview4 = Create file of HOURLY Extinction Change (%)

Additional Debug Output-----------------------

Output selected information to List file

for debugging?

(LDEBUG) -- Default: F ! LDEBUG = F !

Output hourly extinction information to REPORT.HRV?

(Visibility Method 7)

(LVEXTHR) -- Default: F ! LVEXTHR = F !

!END!

12
VANINVCAM02CR.inp 

13
INVISTA Camden Plant C - 1 Trinity Consultants 

BART Applicability Modeling Analysis 

APPENDIX C 

COMPARATIVE ANALYSIS FOR EXPLICIT CALPUFF MODELING

Appendix H.6 - 828
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, POSTUTIL, and CALPOST to assess visibility change.17 

The sample approach simulates actual emissions of each of three gaseous pollutants (SO2, SO4, and 

NOX) and unit emissions (e.g., 1 g/s) of each of six generic particle categories distinguished and 

designated by size: PM800, PM425, PM187, PM112, PM081, and PM056, to represent PM6-10, 

PM2.5-6, PM1.25-2.5, PM1-1.25, PM0.625-1, and PM0.5-0.625, 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 multiplicative 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 input 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 approach is not appropriate. Specifically, for sources 

with multiple emission points that have different exhaust 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 alternative 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, finally 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 conducted 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 that used to describe the emissions from INVISTA’s 

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

 

17 http://www.src.com/verio/download/sample_files.htm#EXAMPLE_BART 

Appendix H.6 - 829
INVISTA Camden Plant C - 3 Trinity Consultants 

BART Applicability Modeling Analysis 

TABLE C-1. EXPLICIT MODELING OF PM TYPES AND SIZE CATEGORIES

 

Modeled PM 

Category Components 

 

PMC800 

PMC425 

Filterable coarse particles divided between two size categories 

(PM6-10, PM2.5-6) 

PMF187 

PMF112 

PMF081 

PMF056 

Filterable fine particles divided among four size categories 

(PM1.25-2.5, PM1-1.25, PM0.625-1, PM0.5-0.625) 

POC081 

POC056 

Primary condensable organic emissions divided between two size categories 

(PM0.625-1 and PM0.5-0.625) 

PIC081 

PIC056 

Primary condensable inorganic emissions divided between two size categories 

(PM0.625-1 and PM0.5-0.625) 

EC187 

EC112 

EC081 

EC056 

Primary elemental carbon emissions divided among four size categories 

(PM1.25-2.5, PM1-1.25, PM0.625-1, PM0.5-0.625) 

 

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. 

TABLE C-2. REPRESENTATION OF EXPLICITLY MODELED PM SIZE CATEGORIES IN CALPUFF 

 

 Computed Geometric Mass Geometric Standard Precipitation Scavenging 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 utilizes the deposition velocity associated with the geometric mass mean 

diameter. 

Appendix H.6 - 830
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 coefficient subsequently used in CALPOST to compute 

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

TABLE C-3. ASSIGNMENT OF MODELED PM SPECIES TO LIGHT EXTINCTION GROUPS

 

Modeled 

Components 

CALPOST Light 

Extinction Group 

Extinction Coefficient 

(m2

/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 SO2, SO4, NOX, HNO3, and NO3 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 SO4 and NO3) of particle 

species simulated in the model. 

This modified approach follows conceptually 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 the 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 output 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 impacts at the Cape Romain NWR Class I area using the 

annual average natural background conditions. 

Appendix H.6 - 831
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. 

TABLE C-4. COMPARATIVE ANALYSIS EMISSIONS SOURCES

 

 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 explicitly 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. 

TABLE C-5. VISTAS SAMPLE ANALYSIS POSTUITL SCALING FACTORS

 

 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 

Appendix H.6 - 832
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 sequentially runs the following analyses to simulate unit PM 

emissions from four sources independently, apply 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 

“VISTAS02x.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 “VISTASUT02x.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 impacts due to concentrations reported in 

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

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

“VISTASVANCR02.LST”. 

Appendix H.6 - 833
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 sequentially 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 those 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 combine, 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) integrated 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 the grouped concentration files input to 

CALSUM in the next step.

4. CALPOST INPUT FILE EXPLICITVANCR02.INP

This CALPOST file calculates the visibility impacts due to concentrations reported in 

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

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

“EXPLICITVANCR02.LST”. 

Appendix H.6 - 834
INVISTA Camden Plant C - 8 Trinity Consultants 

BART Applicability Modeling Analysis 

COMPARATIVE ANALYSIS OUTPUT FILES

The output files from the VISTAS Sample and Trinity’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 greater 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. 

TABLE C-6. COMPARISON OF COMPUTER RUNTIME USING SAMPLE AND EXPLICIT APPROACHES

 

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 modified the parameters to accommodate the explicit 

modeling approach as described in this appendix. 

Appendix H.6 - 835
INVISTA Camden Plant D - 1 Trinity Consultants 

BART Applicability Modeling Analysis 

APPENDIX D 

ELECTRONIC MEDIA DATA FILE INDEX

Appendix H.6 - 836
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 contained 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 meteorological data files are not provided due to file size. Note also 

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

replicating these analyses. 

CALPUFF Runstream Files

INVCAMyy.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

OZCAMyy.dat

yy = 01, 02, and 03 denotes data analysis years 2001, 2002, and 2003, respectively 

Screening Analyses POSTUTIL Processing Files

UTINVCAMyy.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 calculates the HNO3/NO3 re-partitioning, the second of which 

groups PM species for analysis in CALPOST. The first 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 subsequently run using this appended file. 

Appendix H.6 - 837
INVISTA Camden Plant D - 3 Trinity Consultants 

BART Applicability Modeling Analysis 

UTINVCAMyyb.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-April, May-August, September-December, 

respectively 

fff = inp denotes input files 

fff = lst denotes POSTUTIL output summary files 

fff = con denotes POSTUTIL output concentration files 

APPENDyy.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 

UTINVCAMyyS1.con = POSTUTIL-ALM Step 1 concentration file for year yy. 

UTINVCAMyy.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

INVCAMmmmaayy.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 

Appendix H.6 - 838
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 

Appendix H.6 - 839
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 

Appendix H.6 - 840
ii 

Table of Contents 

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

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

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

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

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

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

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

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

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

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

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

4.2 CALMET Model Configuration and Application................................................. 10 

4.3 CALPUFF Model Configuration and Application ............................................... 10 

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

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

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

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

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

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

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

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

7.0 ALTERNATIVE MODELING METHODOLOGY ................................................... 18

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

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

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

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

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 

Appendix H.6 - 841
iii 

Appendices 

Appendix A CALPUFF Configuration 

Appendix B POSTUTIL Screening Configuration 

Appendix C CALPOST Screening 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 

Appendix H.6 - 842
1 

1.0 Introduction 

International Paper (IP) has retained URS 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 prepared at the request 

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

document the modeling procedures that will be used to perform CALPUFF dispersion modeling 

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

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

Georgetown, South Carolina pulp and paper mill cause 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 detailed 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 group of sources. In 1988, the States, Federal Land 

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

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

visibility in 30 national parks and wilderness 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 Regional Haze Regulation. The final Regional Haze 

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

national parks and wilderness areas in the United 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 flexibility in determining reasonable progress 

goals for protected areas by conducting certain analyses 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 regulation 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 reasonable progress goals. The first long-term strategy 

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

Appendix H.6 - 843
2 

and every 10 years thereafter. State’s strategies will address their contribution to visibility 

problems in Class I areas both within and outside the State. 

One of the principal elements of the visibility protection provisions of the Clean Air Act 

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

“BART-eligible” sources are those sources built between 1962 and 1977 that have the potential 

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

sulfur dioxide (SO2), nitrogen oxides (NOx), particulate matter (PM), and volatile organic 

compounds (VOCs), and that fall within 26 industrial source categories (including Kraft pulp and 

paper manufacturing). 

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

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

Administrator Mike Leavitt signed a proposed amendment to the 1999 Regional Haze 

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

Appeals for the D.C. Circuit, which vacated parts 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 visibility impacts of an individual facility when 

determining whether they have to install controls, and what those 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 modeling 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 (VISTAS) have prepared guidance for performing the dispersion 

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

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

change in deciviews (dv) is equal to or greater than the “contribution threshold.” Any BARTeligible source determined to cause or contribute to visibility impairment in any Class I area is 

subject to a BART evaluation. 

The Application of the CALPUFF Model for Analyses 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 defines a “contribution threshold” of 0.5 dv as the 

value where a modeled BART eligible source may “contribute” to visibility 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 observer. 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 

Appendix H.6 - 844
3 

background visual range (natural conditions) is used 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 noticeable change.” However, this protocol uses a conservative 

modeling approach as defined by the VISTAS protocol by comparing 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 threshold. 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 guidance 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 that a BART-eligible source must submit a sitespecific modeling protocol to the State for review 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 refined 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 justification for these procedures 

are presented in this protocol. IP Georgetown 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 environmental consultant, URS Corporation is 

willing to discuss these procedures in greater detail with the SCDHEC and supply additional 

material demonstrating why these modeling procedures are appropriate 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 whether a potentially BART-eligible source is 

exempt from a BART control technology evaluation. 

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

perform a BART control technology evaluation for the purpose of determining the 

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

haze in Class I areas. 

1.2 Facility Location and Relevant Class I Areas 

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

Kaminski Street in Georgetown, South Carolina. The Universal 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 Wildlife Refuge Areas. Figure 1-1 displays the 

Appendix H.6 - 845
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. 

Appendix H.6 - 846
31

32333435

Latitude

-85 -84 -83 -82 

Longitude

URS Corporation – North Carolina 

1600 Perimeter Park Drive Suite 400 

Morrisville, North Carolina 27560 

Telephone (919) 461-1100 Fax (919) 461-1415

SCALE: DRAWN BY: SCL DATE: 2/10/06 AS SHOWN CHECKED BY: DATE:

International Pap

Facility L

Relative t

Are

1 
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 proposed. For the initial 

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

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

visibility threshold value of 0.5 dv, no further modeling 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 meteorological 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 further 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 model greatly exceeds the recommended threshold or finer grid 

modeling results exceed the recommended threshold 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 states that modeling results should be based on 

the 98th percentile value, we are proposing that the 98th percentile be applied to all CALPUFF 

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

percentile value across all receptors in the Class I area will be compared to the threshold 

value of 0.5 dv. If the 24-hour 98th percentile value is below 0.5 dv, then IP Georgetown will 

be exempt from performing a BART evaluation. If the 24-hour 98th 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 described in Section 7 of this protocol. 

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

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

modeling. 

For finer grid (4 km or less) analyses, the 98th 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 meteorological model that generates hourly threedimensional meteorological fields of variables such as wind and temperature. CALPUFF 

simulates the transport, dispersion, and transformation 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. CALPOST calculates time-averaged concentration values from the 

CALPUFF predictions and performs regional haze calculations like those described in the 

Section 6.1 of this protocol. 

Appendix H.6 - 848
2 

2.0 BART Source Descriptions 

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

primary activities at Georgetown Mill are pulp production (Standard Industrial 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 utilization. Consistent with the VISTAS common 

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

The modeling will be based on the 24-hour average actual emission rate from the highest emitting 

day during the most recent 3-year period. The 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 estimates based on source testing and accepted 

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

rates will be used: 

• Short-term (24-hours) allowable emission rates (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 calculated emission rates) from the most recent 3-

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

conditions and fuel/material flexibility allowed 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 SO2, NOx, H2SO4 mist, and PM10 (including

condensible and filterable direct PM10) 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. 

Appendix H.6 - 849