ATTACHMENT 4
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Wisconsin Sources - BART Applicability and Requirements

A core federal requirement for addressing visibility impairment in the federal Class I areas is the 

implementation of a control program known as Best Available Retrofit Technology (BART) for 

certain older major sources directly impairing visibility. This BART control requirement 

addresses sources constructed in the decade before New Source Performance Standards (NSPS) 

first came into effect, and as a result have minimal or less than adequate emission controls. The 

federal requirements for identifying sources subject to BART, and the methods for determining 

appropriate emission control requirements, are set forth by the United States Environmental 

Protection Agency (U.S. EPA) under 40 CFR Part 51, Appendix Y, Guidelines for BART 

Determinations Under the Regional Haze Rule. 

In order to meet the federal requirements, Wisconsin implemented rules for BART as provided 

under NR Ch. 433, Wis. Adm. Code, that address emissions of particulate matter (PM), sulfur 

dioxide (SO2), and nitrogen oxide (NOx). 

The Wisconsin rules establish that electricity generating units (EGUs) meet BART requirements 

for SO2 and NOx by meeting the federal Clean Air Interstate Rule (CAIR) requirements. For all 

other cases, the Wisconsin rules establish a process for determining those sources subject to 

BART and applicable BART emission reduction requirements on a case-by-case basis. As part 

of this process, the source must submit an analysis of potential pollution control technologies and 

their installation cost and related issues. Sources must implement BART requirements by 

December 31, 2015. 

This document summarizes the determination of Wisconsin sources eligible and subject to 

BART and the determination of BART requirements for the affected sources. The finalized 

BART program is based on proposals provided for public comment & hearings in July 2010 and 

September 2011. 

1. Determination of BART Eligible and Affected Sources. 

Under the state rule, the CALPUFF air quality model is used to determine a source's visibility 

impairment on a Class I area for those sources found to be an appropriate age to be eligible under 

the BART program. The pollutants of concern emitted by boilers at the non-EGU facilities are 

SO2, NOx, and PM. If the modeled results show a significant reduction in visibility, the source 

is subject to BART or "BART-affected". An alternate CALPUFF analysis, which utilizes more 

specific data, is also allowed under the state rule. The protocols for the CALPUFF modeling and 

alternative modeling for determining if a source is subject to BART controls, along with 

additional details for modeling, are found in the Regional Haze SIP. 

Table 1 shows the EGUs found subject to BART. Details for modeling are found in “July 2011 

Draft BART Technical Support Document (TSD) for EGUs” within Wisconsin’s BART SIP. 
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Table 1 - Wisconsin EGU Sources Subject to BART

Source Name Emission Units 

(B = Boiler) County 

Alliant Energy – Columbia B-21, B-22 Columbia 

Alliant Energy – Edgewater B-24 Sheboygan 

Alliant Energy – Nelson Dewey B-22 Grant 

Wisconsin Energy – Oak Creek B-27,28 Milwaukee 

Wisconsin Energy – Pleasant Prairie B-21, B-22 Kenosha 

Wisconsin Public Service Corporation – 

JP Pulliam Plant B-27 Brown 

Dairyland Power Coop – Alma B-25,26 Buffalo 

Dairyland Power Coop – Genoa B-20 Vernon 

Wisconsin Energy – Valley B-21, B-22, B-23, B-24 Milwaukee 

The status of non-EGU sources as BART-subject is summarized in Table 2. The Department 

determined that four non-EGU facilities have sources that are potentially subject to BART based 

on source category and age criteria. Based on visibility modeling the Department determined 

that the Green Bay Georgia-Pacific facility is the only non-EGU source subject to BART. The 

BART determination for Georgia-Pacific is described below. The BART TSD for non-EGUs is 

located in Wisconsin’s BART SIP. 

Based on visibility modeling results, the three other BART eligible industrial facilities listed in 

Table 2 – International Paper Kaukauna facility (a.k.a. Thilmany), Packing Corporation of 

America-Tomahawk, and Mosinee Paper Corporation – do not exceed the threshold of 7-day 

visibility impact in any base year to any single Class I area. Therefore, the Department 

determined these sources are not subject to BART control requirements. The modeling 

evaluation for these facilities relied on the VISTAS protocol for utilizing more specific model 

inputs and smaller grid analysis for visibility impacts compared to the default approach. The 

details for these visibility modeling analyses are presented in Attachment 5 of Wisconsin’s 

BART Implementation SIP Submittal. 

Table 2 - Status of Wisconsin Non-EGU Sources Potentially Subject to BART 

Source Name 

Eligible Emission 

Units 

(B = Boiler) 

BART-subject 

Status County 

Georgia-Pacific – Green Bay B-26, B-27 Subject Brown 

International Paper Kaukauna facility 

(a.k.a. Thilmany) B-11 Not subject * Outagamie

Packing Corporation of America – 

Tomahawk B-24 Not subject * Lincoln 

Mosinee Paper Corporation B-20, B-21, B-24 Not subject * Marathon 

* Determination based on CALPUFF modeling using VISTAS modeling protocol. 
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2. Georgia-Pacific BART Determination

The Georgia-Pacific facility in Green Bay, Wisconsin operates two coal-fired power boilers 

subject to BART under the Clean Air Act. In July of 2011, the Department provided for external 

review a draft finding of BART requirements applicable to the affected Georgia-Pacific boilers. 

This document amends the draft BART finding and provides response to public comment 

(Attachment 3 of Wisconsin’s BART SIP). This BART requirement for Georgia-Pacific will 

comprise a component of Wisconsin's State Implementation Plan (SIP) addressing Regional 

Haze and will contribute to Reasonable Progress Goals (RPG) by the beginning of 2016 and 

after. Further requirements and contribution by industrial boilers to RPG, at Georgia-Pacific and 

sector-wide, will be evaluated for the next RPG evaluation in 2018 as described in the Regional 

Haze SIP document. 

The Georgia-Pacific BART requirements address emissions of PM, SO2, and NOx from two 

power boilers B26 and B27. The two affected boilers exhaust through common stack S10 along 

with the coal-fired boilers B25 and B28. The BART control requirement for each pollutant is 

summarized below. 

Particulate Matter (PM)

The July 2011 draft BART finding proposed PM requirements based on the existing control 

equipment and permit limitations. This finding was based on the following: insignificant 

visibility improvement for a zero-out of PM emissions from the maximum actual baseline PM10

emissions; a very high level of PM control achieving 0.025 lbs/mmBtu emission rates; and 

current compliance with malfunction and abatement plans. In responding to comments, the 

finalized PM BART determination has not been amended and consists of a PM emission 

limitation requirement of 0.30 Lb/mmBtu on BART boilers B26 and B27. Additional details 

regarding the Department’s BART determination for PM at Georgia-Pacific are found in the July 

2011 Draft BART TSD for Non-EGUs (Attachment 3 of Wisconsin’s BART Implementation 

SIP Submittal) and the Response to Comments for BART (Attachment 10 of Wisconsin’s BART 

Implementation SIP Submittal). 

Sulfur Dioxide (SO2) 

The Department compared wet flue gas desulfurization (FGD) and dry circulating fluidized bed 

(CFB) FGD in the July 2011 draft BART finding. The Department developed costs and control 

levels based on a commercially available CFB unit called Turbosorp. The wet FGD – dry CFB 

FGD comparison showed that the capital cost of wet FGD is over 30% higher than that of the dry 

CFB FGD, with both technologies achieving comparable control efficiencies (93% - 98%). The 

Department concluded in the draft BART finding that the incremental costs do not substantiate 

the application of wet FGD, and that SO2 BART should be based on the application of dry CFB 

FGD technology. The Department further concluded that long-term operation and compliance 

with dry CFB FGD is represented by 93% control efficiency. The draft finding also established 

"Base SO2 emissions" reflecting a presumptive fuel at a specified sulfur content. The BART 

compliance requirement was then established by applying 93% control to the "Base SO2 

emissions." 
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The finalized BART determination for SO2 is amended from the draft BART finding to reflect 

the use of actual BART baseline emissions (i.e. no adjustment for presumptive fuel) in assessing 

visibility improvement, control evaluations, and BART requirements. The fuel switched 

emissions are calculated for fuel switching petroleum coke to the bituminous coal as burned 

during the BART baseline years. The fuel switch alters the concentration of SO2 in the flue gas 

from ~ 3.6 lbs/mmbtu to 3.0 lbs/mmbtu. A dry scrubber control efficiency of 93% is then 

applied to the fuel switched emissions for BART boilers B26 and B27. The combination of fuel 

switching and dry scrubber control results in a 95.8% control efficiency for Boiler B26 and 

93.8% control efficiency for Boiler B27. 

The annualized cost for dry CFB FGD applied to boilers B26 and B27 was updated from the 

draft BART finding to reflect fuel switching petroleum coke to bituminous coal. The visibility 

improvements are estimated using the visibility improvement factors for SO2 reduction as 

developed in the Visibility Improvement section below. Table 3 shows a summary of the 

amended SO2 BART control and visibility improvement. Additional details regarding the 

Department’s BART determination for SO2 at Georgia-Pacific are found in the July 2011 Draft 

BART TSD for Non-EGUs (Attachment 3 of Wisconsin’s BART Implementation SIP Submittal) 

and the Response to Comments for BART (Attachment 10 of Wisconsin’s BART 

Implementation SIP Submittal). 

Table 3 - Summary of Final SO2 BART Control and Visibility Improvement at 

Northern Class I Areas1,2 

Control Efficiency

B26 = 95.8%

B27 = 93.8%

M$/year

18.1

Controlled grams/sec

416.9

maximum average maximum average

dv per gram/sec = 0.005 0.004 0.011 0.010 

dv improvement = 2.19 1.81 4.51 4.10 

M$/dv = 8.2 10.0 4.0 4.4 

Seney Northern Class I Areas

SO2 BART Boilers B26 & B27 - CFB FGD

1 Control efficiency based on combination of fuel switching and dry scrubber control at 93% at 

B26 and B27.

2 Northern Class I Areas = Isle Royale National Park, Seney Wilderness Area, Boundary Water 

Canoe Area, and Voyageurs National Park. 
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Nitrogen Oxides (NOx) 

The July 2011 draft BART finding proposed NOx requirements based on the application of 

combustion modifications, followed by either selective non-catalytic reduction technology 

(SNCR) or a type of tail-end selective catalytic reduction technology (RSCR). The requirement 

for B26, a stoker boiler, reflected combustion modifications followed by SNCR to achieve an 

overall 68% long-term reduction. For B27, a cyclone boiler, the requirement reflects overfire air 

(OFA) combustion modifications followed by one of several different available control options: 

RSCR, Rich Reagent Injection (RRI)/SNCR, and SNCR. These equipment configurations yield 

an 84% to 85% long-term control requirement for Boiler B27. 

After addressing comments, the finalized BART determination for NOx is 68% control for boiler 

B26 and 85% control for boiler B27. The 68% control efficiency on B26 is based on the use of 

OFA/Flue Gas Recirculation (FGR)/SNCR. The application of RSCR at 70% control yields no 

discernable improvement in visibility while requiring significant additional cost. The 85% 

control efficiency on B27 is based on RSCR or in-duct SCR based control approaches.

Table 4 shows a summary of the amended NOx BART control and visibility improvement. 

Additional details regarding the Department’s BART determination for NOx at Georgia-Pacific 

are found in the July 2011 Draft BART TSD for Non-EGUs (Attachment 3 of Wisconsin’s 

BART SIP) and the Response to Comments for BART (Attachment 10 of Wisconsin’s BART 

SIP). 

Table 4 - Summary of Final NOx BART Control and Visibility Improvement at Northern 

Class I Areas 

M$/year

3.5

Controlled grams/sec

99.9

maximum average maximum average

dv per gram/sec = 0.009 0.005 0.012 0.008 

dv improvement = 0.88 0.49 1.18 0.82 

M$/dv = 3.95 7.10 2.93 4.21 

Seney Northern Class I Areas

NOx BART Combined Boilers B26 & B27

Summary of BART Control Levels and Visibility Improvement

The Department performed CALPUFF modeling in the July 2011 draft BART finding to assess 

visibility improvement achieved under the BART requirements. The emission cases modeled 

were based on the day of maximum actual emissions from the combined stack S10 during the 

baseline years. The base uncontrolled emission rates identified for each pollutant, in grams per 

second, used for this modeling are provided in Appendix A. To assess the BART requirements, 

controlled emission rates were calculated and modeled. To do this the Department determined 

the percent reduction that would occur from the maximum day emission rate after applying 

BART. The Department calculated a reduction using the annual Stack S10 BART mass cap 

compliance requirement, compared to the base year average emissions before SO2 base fuel 
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adjustments. The stack S10 percent reduction applied to the uncontrolled grams per second 

emission rates in the July 2011 draft BART finding was 70% for NOx and 57% for SO2. The 

resulting maximum day controlled emission rates were then modeled for every day in 2002 to 

2004. Additional details of this modeling are found in the July 2011 Draft BART TSD for NonEGUs (Attachment 3 of Wisconsin’s BART SIP). 

Since the amended BART reflects actual instead of adjusted BART baseline emissions, along 

with slightly higher control levels for SO2 and NOx, the visibility modeling provided in the July 

2011 draft BART finding is updated accordingly. The Department first determined the percent 

reduction that would occur from the maximum day emission rate after applying the finalized 

BART controls. The Department then calculated a reduction using the annual Stack S10 BART 

mass cap compliance requirement (Tables 8 and 10 below) compared to the base year average 

emissions. The new stack S10 percent reduction applied to the uncontrolled grams per second 

emission rates is 71% for NOx and 81% for SO2. 

Table 5 shows the reduced number of days above the 0.1 and 0.5 dv thresholds due to BART 

(Reduced Days of Impact with BART). These values were calculated by applying the “Days 

reduced / gram per sec reduced” factor from the July 2011 draft BART modeling to the new 

controlled grams per second emission rates. Seney realizes the largest reduction of days for each 

case. Table 6 shows the maximum daily impact (dv) modeled in each year due to BART. These 

values were calculated by applying the “Days reduced / gram per sec reduced” factor from the 

July 2011 draft BART modeling to the new controlled grams per second emission rates. The 

results for the Seney Class I area are segregated as this area receives the highest impact. Also 

presented in Table 6 are visibility improvements under BART related to the individual 

pollutants, shown for SO2 and NOx. The draft BART control levels for BART boilers in the 

Stack S10 system and the resulting improvement to the average visibility impact are summarized 

in Table 7. 
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Table 5 - Days of Visibility Impact after BART for the Northern Class I Areas. 

Uncontrolled Emissions Uncontrolled Emissions

2002 2003 2004 2002 2003 2004

bowa 25 28 44 bowa 7 7 13

isle 34 51 52 isle 14 19 17

sene 107 118 113 sene 41 53 48

voya 10 13 20 voya 2 0 2

BART BART

2002 2003 2004 2002 2003 2004

bowa 15 12 18 bowa 0 0 0

isle 23 31 25 isle 3 1 0

sene 67 73 71 sene 1 11 2

voya 2 1 1 voya 0.00 0 0

Reduced Days of Impact with BART Reduced Days of Impact with BART

2002 2003 2004 2002 2003 2004

bowa 10 16 26 bowa 7 7 13

isle 11 20 27 isle 11 18 17

sene 40 45 42 sene 40 42 46

voya 8 12 19 voya 2 0 2

Days reduced / grams per sec reduced

2002 2003 2004 2002 2003 2004

bowa 0.018 0.032 0.050 bowa 0.013 0.013 0.029

isle 0.021 0.040 0.053 isle 0.021 0.034 0.037

sene 0.077 0.087 0.082 sene 0.077 0.082 0.090

voya 0.016 0.024 0.037 voya 0.005 0.000 0.005

Number of days with delta-deciview => 0.1 Number of days with delta-deciview => 0.5

Table 6 - Modeled Maximum Daily Impact (dv) for 2002, 2003, and 2004

Maximum Average Maximum Average

 4.14 5.38 9.67 8.12 

BART 1.72 1.38 2.81 2.41 

SO2 3.19 2.32 5.16 4.02 

NOx 4.50 3.65 8.49 7.30 

BART 3.66 2.76 6.86 5.72 

SO2 2.19 1.81 4.51 4.10 

NOx 0.88 0.49 1.18 0.82 

sum of SO2 & NOx 3.07 2.30 5.69 4.93 

BART 0.007 0.005 0.013 0.011

SO2 0.005 0.004 0.011 0.010

NOx 0.009 0.005 0.012 0.008

Residual Visibility Impact (RVI)

Visibility Improvement (VI) Result of 

"Uncontrolled" - "RVI"

Visibility Improvement / Gram Pollutant; 

Result of RVI / grams per sec reduced

Visibility Case / Paramenter Seney Northern Class I Areas 

Uncontrolled Emissions (max day)

Maximum = Maximum Daily Impact modeled for the base years (2002 – 2004) 

Average = Average of each base year maximum daily impact. 
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Table 7 - Draft BART Control Levels and Visibility Improvement for Boilers B26 and B27 

Visibility Improvement (dv)2,3

BART Technology and 

Control Efficiency Seney Northern Class I 

Areas 

Emission 

Unit 

SO2

1 NOx PM10 SO2 NOx PM SO2 NOx PM 

B26

Dry 

FGD 

– 93% 

OFA/FGR/SNCR 

– 68% 

Existing 

Baghouse - 

> 99% 

B27

Dry 

FGD 

– 93% 

OFA + RSCR – 

85% 

Existing 

Baghouse - 

> 99% 

1.81 0.49 N/A 4.10 0.82 N/A 

Total BART 2.76 5.72 

Notes: 

1

 Overall SO2 control efficiency, based on combination of fuel switching and dry scrubber 

control at 93%, is 95.8% for B26 and 93.8% for B27. 

2

 Visibility improvement values are the average of the maximum daily impact identified for each 

BART base year 2002 to 2004 

3

 Pollutants when reduced together yield a greater visibility improvement than visibility 

improvement modeled for each pollutant individually. 

BART Baseline Emissions and Calculation of Requirements

The following amended BART requirements are proposed for SO2 and NOx as 30-day mass caps 

and 12-month mass caps individually for each boiler B26 and B27. Furthermore, the emission 

limitations applicable to the common stack S10 are based on averaged emission requirements 

across boilers B25 through B28. The emission baseline and mass cap calculations exclude the 

operation of boiler B24 because it has been permanently shut down. Boiler B25 is included – 

even though it has not operated in recent years – because Georgia-Pacific was actively working 

with the U.S. EPA during that inoperative period to exempt B25 from the CAIR. 

The annual emission baseline used to calculate the 12-month mass caps is the BART baseline 3 

year average emission rate and heat input for 2002 to 2004. The 30-day emission baseline is 

calculated from the BART baseline 3-year average emission rate, multiplied by the actual 30-day 

maximum heat input which occurred during the BART baseline years. The NOx baseline 

emission rates for B26 and B27 are adjusted from the baseline data to reflect test data for actual 

emissions since 2007. The adjusted NOx emission rates are 0.68 lbs/mmBtu for B26 and 1.10 

lbs/mmBtu for B27. 

The 30-day and 12-month rolling BART mass caps for each boiler are calculated by applying the 

BART control efficiencies to the 30-day and annual emission baselines, respectively. A 10% 

additional reduction is then applied to the BART boiler controlled emissions to address the 
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environmental benefit. This is consistent with EPA’s economic incentive program (EIP) policy 

guidance in reducing emissions 10% below that which would occur through the BART 

requirement on the individual boilers. The mass cap over all boilers creates an additional 

environmental benefit (as outlined in the EIP) by limiting the amount of overall emissions, 

addressing any switch of capacity from one boiler to another, and precluding any future growth 

in emissions from the non-BART boilers. The resulting emissions for each boiler are summed to 

yield the 30-day and 12-month rolling emission caps for stack S10. 

Tables 8 through 11 show the baseline emissions and requirements for SO2 and NOx on a 30-day 

and 12-month basis. 

Table 8 - SO2 BART Annual Baseline Emissions and Requirements 

Emission 

Unit 

Baseline 

Heat 

Input 

(mmBtu) 

Baseline 

Emission 

Rate 

(Lb/mmBtu)

Baseline 

Emissions 

(Tons) 

BART 

Control 

Efficiency1

BART 

Mass 

Emissions 

(Tons) 

BART 

Mass 

Cap 

(Tons)2

B24 0 0 0 0 0 0 

B25 555,606 1.26 349 0 349 349 

B26 1,882,890 2.29 2,160 95.8% 90 81 

B27 4,366,721 3.99 8,715 93.8% 544 489 

B28 1,563,784 1.82 1,421 0 1421 1421 

S10 8,369,001 3.02 12,644 81.0% 2,404 2,340 

1 Based on combination of fuel switching and dry scrubber control at 93% at B26 and B27.

2 Includes 10% additional reduction applied to B26 and B27 controlled emissions.

Table 9 - SO2 BART 30 Day Baseline Emissions and Requirements 

Emission 

Unit 

Baseline 

Heat 

Input 

(mmBtu) 

Baseline 

Emission 

Rate 

(Lb/mmBtu)

Baseline 

Emissions 

(Tons) 

BART 

Control 

Efficiency1

BART 

Mass 

Emissions 

(Tons) 

BART 

Mass 

Cap 

(Tons)2

B24 0 0 0 0 0 0 

B25 107,015 1.26 67 0 67 67 

B26 219,325 2.29 252 95.8% 11 9 

B27 411,492 3.99 821 93.8% 51 46 

B28 159,515 1.82 145 0 145 145 

S10 897,347 2.86 1,285 78.7% 284 268 

1 Based on combination of fuel switching and dry scrubber control at 93% at B26 and B27.

2 Includes 10% additional reduction applied to B26 and B27 controlled emissions.
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Table 10 - NOx BART Annual Baseline Emissions and Requirements 

Emission 

Unit 

Baseline 

Heat 

Input 

(mmBtu) 

Baseline 

Emission 

Rate 

(Lb/mmBtu)

Baseline 

Emissions 

(Tons) 

BART 

Control 

Efficiency1

BART 

Mass 

Emissions 

(Tons) 

BART 

Mass 

Cap 

(Tons)2

B24 0 0 0 0 0 0 

B25 555,606 0.39 108 0 108 108 

B26 1,882,890 0.68 640 68% 205 184 

B27 4,366,721 1.1 2,402 85% 360 324 

B28 1,563,784 0.46 360 0 360 360 

S10 8,369,001 2.63 3,510 70.6% 1,033 977 

1 Based on combination of fuel switching and dry scrubber control at 93% at B26 and B27.

2 Includes 10% additional reduction applied to B26 and B27 controlled emissions.

Table 11 - NOx BART 30 Day Baseline Emissions and Requirements 

Emission 

Unit 

Baseline 

Heat 

Input 

(mmBtu) 

Baseline 

Emission 

Rate 

(Lb/mmBtu)

Baseline 

Emissions 

(Tons) 

BART 

Control 

Efficiency1

BART 

Mass 

Emissions 

(Tons) 

BART 

Mass 

Cap 

(Tons)2

B24 0 0 0 0 0 0 

B25 107,015 0.39 21 0 21 21 

B26 219,325 0.68 75 68% 24 21 

B27 411,492 1.1 226 85% 34 31 

B28 159,515 0.46 37 0 37 37 

S10 897,347 2.63 358 67.8% 115 110 

1 Based on combination of fuel switching and dry scrubber control at 93% at B26 and B27.

2 Includes 10% additional reduction applied to B26 and B27 controlled emissions.

BART Compliance Requirements

The July 2011 draft BART finding provided several compliance alternatives for meeting the SO2

and NOx BART requirements. These requirements were structured as either emission rate 

limitations or mass emission caps on either 30-day or 12-month rolling averages. GeorgiaPacific could comply with either the set of emission rate or mass cap limitations applicable to the 

individual BART boilers or to stack S10. In responding to comments, the BART compliance 

alternatives for meeting the BART requirements are amended to include only stack S10 mass 

emission caps on both a 30-day and 12-month basis (Table 12). The PM BART requirements for 

BART boilers B26 and B27 remain at the existing emission limitation of 0.30 Lb/mmBtu. These 

compliance requirements become effective January 1, 2016. 
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Table 12 - Summary of SO2 and NOx BART Compliance Requirements 

Pollutant Tons Emitted in any 30 Day Period 

at Stack S10 

Tons Emitted in any 12 Month Period 

at Stack S10 

SO2 268 2,340 

NOx 110 977 

SO2 and NOx Alternative Compliance Option

As previously described, the primary SO2 and NOx BART compliance requirement is to show 

total emissions are lower than both a 12-month rolling and 30-day rolling mass cap for emissions 

of each pollutant from stack S10. Since the target of reducing both SO2 and NOx is to reduce 

visibility impact in the Class I areas, an alternative compliance option is provided where SO2 can 

be traded for NOx reductions while still yielding the same visibility improvement as the primary 

BART requirement. Simply stated, this approach is a form of inter-pollutant trading for 

precursor emissions affecting visibility. 

The alternative compliance option sets forth several set combinations of SO2 and NOx emission 

mass caps for stack S10 as identified in the draft Georgia-Pacific BART Administrative Order 

(Attachment 6 of Wisconsin’s BART SIP). Georgia-Pacific can then elect one of these default 

mass cap combinations by July 15, 2013 through notification to the Department and the U.S. 

EPA. If Georgia-Pacific elects to choose a non-specified mass cap or choose any alternative 

mass cap later than July 15, 2013 then the election is subject to Department review with public 

comment and pursuant U.S. EPA approval of the SIP. The default combinations of SO2 and 

NOx emissions for election are provided in Table 13. 

Under all of the identified mass cap options, SO2 emissions are reduced below the primary 

BART mass cap in order to allow NOx emissions above its BART mass cap. A provision is also 

included which ensures that in no case, whether under an elected default or alternatively 

identified mass cap, that in no case NOx emissions can exceed a set cap of 1,522 tons on a 12-

month rolling basis and 172 tons on a 30-day rolling basis. 

Table 13 - Default SO2 and NOx Mass Caps Under the Alternative Compliance Option 

30-day rolling 12-month rolling 

SO2 NOx SO2 NOx 

BART 268 110 2,340 977 

Mass Cap 1 246 121 2,150 1,072 

Mass Cap 2 195 147 1,700 1,297 

Mass Cap 3 143 172 1,250 1,522 
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The mass cap options are identified by establishing potential NOx emission levels consistent 

with various control equipment applications. The NOx mass cap levels under the alternative 

compliance option are calculated placing these control assumptions against the BART baseline 

year average heat input for each boiler. Details of control equipment options and visibility 

improvement for boilers B26 and B27 are those identified and evaluated under the July 2011 

BART proposal. 

To ensure equivalent or greater visibility improvement, NOx is offset by two tons of SO2 (2:1 

trading ratio). As a result, at each NOx emission level the SO2 BART requirement is reduced by 

two tons for every ton of NOx over the primary BART mass cap. This 2:1 ratio is based on the 

analysis of SO2 and NOx trading included in the July 2011 draft BART finding, section 7. The 

analysis tested various combinations of SO2 and NOx trading for visibility improvement during 

the 20% best and worst days and on a 30-day rolling basis relative to the Seney Class I area. The 

results of the analysis show that a 2:1 trading ratio ensures equivalent or greater visibility. 

Further, the analysis establishes visibility improvement increases and the magnitude of 

individual day visibility impact decreases as more SO2 is removed in lieu of NOx control. The 

NOx control is evaluated for control levels from 70% down to 21%. However, to address 

individual days when the impact of NOx emissions can be larger than normal due to atmospheric 

chemistry, the minimum NOx reduction of approximately 50% overall control is reflected in the 

maximum NOx emission cap. 

Under the Wisconsin BART rule, s. NR 433.06, Wis. Adm. Code, and U.S. EPA's EIP policy, 

traded emissions must be in excess or surplus of other applicable emission requirements. 

Currently, the boilers in the stack S10 system are not subject to emission requirements which 

reduce SO2 emissions below the primary BART required emission cap. Therefore reductions of 

SO2 below the emission cap are excess and can be traded in lieu of the NOx BART requirement. 

Accordingly, the choice of an alternative mass cap at a future date is based on the assessment of 

current applicable requirements and as such those mass caps also reflect trading of excess SO2

emission reductions. 

i) Simplified Approach to an Alternative Compliance Option 

A simplified approach to implementing an alternative control option is to allow inter-pollutant 

trading by applying the established 2:1 trading ratio along with the "not to exceed" NOx mass 

cap. In this case, Georgia-Pacific does not need to elect one set of SO2 and NOx mass caps. In 

essence SO2 can be traded for NOx versus the primary BART mass caps. This approach allows 

the control levels to be varied over time based on the most effective option at that time. Further, 

this approach does not require an election of one set of mass caps by June 15, 2013 and or SIP 

approval for mass caps identified at a later date. 

The Department feels this simplified approach is justified in that it ensures equivalent visibility 

by employing the same criteria used in establishing the previously describe sets of mass caps. 

Further, even as other future NOx or SO2 requirements become applicable, the visibility 

improvement determined as BART cannot be lost. This is supported by the modeling of 

visibility improvement for the different SO2 : NOx trading cases at a 2:1 ratio where greater 

improvement is garnered from deeper SO2 reductions. On this premise, if a SO2 reduction level 
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is chosen for trading under BART and then a future regulation requires the same amount of SO2

reduction there is no loss of visibility improvement under inter-pollutant trading. Further, if the 

future regulation requires SO2 reduction beyond the chosen trading level, then applying these 

reductions to offset NOx reductions at the same 2:1 ratio will result in even greater visibility 

improvement. In all of these cases the visibility improvement realized under the primary BART 

requirement is kept whole at any time into the future. The Department also maintains that this 

trading, although variable over time, is based on the requirements when the BART is established 

and therefore excess to other emission requirements. If the U.S. EPA remains concerned that 

NOx emission levels may increase as future SO2 regulations come into place, a simple solution is 

to prohibit a change of "noticed" NOx mass caps to a lower level after that time. 

To note is that under any alternative compliance plan or even the primary BART mass cap 

requirements that any future evaluation of haze reasonable progress or NAAQS attainment 

demonstrations are based on the maximum emissions allowed under the BART compliance 

options. 

3. Electric Utility Generating Units

The July 2011 draft BART finding proposed PM requirements based on the existing control 

equipment and permit limitations. In responding to comments, the BART determination for PM 

has not been amended. A template (“EGU BART Permit Revisions for Implementation of 

BART”) is included as a separate attachment to the BART SIP submittal. Table 14 provides a 

summary of PM BART determinations for Wisconsin EGU sources. Additional details 

regarding the Department’s BART determination for PM at EGU’s are found in the July 2011 

Draft BART TSD for EGUs (Attachment 2 of Wisconsin’s BART SIP) and the Response to 

Comments for BART (Attachment 10 of Wisconsin’s BART SIP). 
14

Table 14 - PM BART Determination for Wisconsin EGU Sources 

Source Name Emission Units 

(B = Boiler) 

PM Permit Emission 

Limit 

(Lbs/mmBtu) 

County 

Electrostatic Precipitator Control 

Alliant Energy – Columbia B-21, B-22 0.60 (B-21) 

0.10 (B-22) Columbia 

Alliant Energy – Edgewater B-24 0.13 Sheboygan

Alliant Energy – Nelson Dewey B-22 0.10 Grant 

Wisconsin Energy – Oak Creek B-27,28 0.03 Milwaukee

Wisconsin Energy – Pleasant Prairie B-21, B-22 0.10 Kenosha 

Wisconsin Public Service 

Corporation – JP Pulliam Plant B-27 0.30 Brown 

Baghouse Control 

Dairyland Power Coop – Alma B-25,26 0.10 Buffalo 

Dairyland Power Coop – Genoa B-20 0.034 Vernon 

Wisconsin Energy – Valley B-21, B-22, B23, B-24 0.15 Milwaukee
15

Appendix A. Additional information for modeling of visibility impact for BART at 

Georgia-Pacific 

Table A1 - Individual Unit Baseline Emission Rates used for 

Modeling Results 

Emissions (grams/sec) a

Unit and 

Pollutant SO2 NOx PM10

B24 19.8 7.0 1.7 

B25 0 0 0 

B26 116.0 17.8 4.7 

B27 314.7 103.2 7.8 

B28 64.3 13.4 3.0 

a Emission rates are "max actual" data (Lbs/day) provided by GP. 

Table A2 - Source Parameters at GP, Stack S10 

Parameter Unit Value 

Location 

Latitude deg. 44.49 N 

Longitude deg. 88.03 W 

Datum - NAR-C 

Stack Height meters 121.9 

Base Elevation meters 179.5 

Diameter meters 3.81 

Gas Exit Velocity meters/sec 17 

Stack Gas Exit Temperature F 439 
ATTACHMENT 5
Updated CALPUFF Modeling 

Protocol and Final Report for the 

Subject to BART Analyses 

for PCA Tomahawk Mill 

Prepared by 

RTP Environmental Associates Inc. 

2031 Broadway, Suite 2 

Boulder, Colorado 80302 

December 2010 
Updated CALPUFF Modeling Protocol and Final Report for 

PCA “Subject to BART” Analysis 

TABLE OF CONTENTS 

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

2.0 VISTAS BART Protocol ........................................................................................................ 5 

3.0 CALMET Data and Procedures.............................................................................................. 7 

4.0 CALPUFF Procedures.......................................................................................................... 12 

5.0 POSTUTIL and CALPOST Procedures ............................................................................... 13 

6.0 Emissions Modeled............................................................................................................... 14 

7.0 Modeling Results.................................................................................................................. 15 

List of Figures

Figure 1 - WDNR Screening CALPUFF Domain .......................................................................... 2 

Figure 2 – Refined CALPUFF Modeling Domain and Locations of Class I Areas....................... 9 

Figure 3 – Locations of Observational Stations in Refined CALPUFF Modeling Domain......... 10 

Figure 4 – Land Use Data for Refined CALPUFF Modeling Domain......................................... 11 

List of Tables

Table 1 – PCA Speciated PM Emissions...................................................................................... 14 

Table 2 – PCA CALPUFF BART Exemption Results Summary................................................. 16 

Appendix A – Example CALMET Input File 

Appendix B – Example CALPUFF Input File 

 i 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

1 December 2010 

1.0 Introduction 

The Wisconsin Department of Natural Resources (DNR) performed single source screening 

modeling in 2006 to evaluate which Best Available Retrofit Technology (BART) eligible sources 

in the state may “cause or contribute” to visibility impairment and could therefore be subject to 

BART requirements. This type of analysis is referred to as the “subject to BART” or “BART 

exemption” analysis. The methods used by DNR are described in the “Single Source Modeling to 

Support Regional Haze BART Modeling Protocol”, March 21, 2006, prepared by Lake Michigan

Air Directors Consortium (LADCO). 

DNR applied CALPUFF to each BART eligible source for three annual periods, covering the 

calendar years 2002 to 2004. The CALPUFF/CALMET modeling domain consisted of ninetyseven 36-km spaced cells in the east-west direction and ninety 36-km spaced cells in the northsouth direction (see Figure 1). Meteorological data generated by the MM5 prognostic weather 

model (provided by LADCO in CALMM5 format) was used to develop the meteorological data 

for CALPUFF, without additional observational data input (i.e., NOOBS mode). This represents 

a coarse meteorological grid, suitable for an initial screening analysis. 

The results from DNR’s screening analysis indicated that, with the exception of some of the 

largest electric power stations in the state, the only Class I areas where BART eligible sources 

may contribute to visibility impairment are the three areas to the north of Wisconsin, the 

Boundary Waters Canoe Area, Isle Royal National Park, and Seney Wildlife Area. DNR’s 

screening analysis also indicated that the BART eligible emissions unit at the Packaging 

Corporation of America Tomahawk Mill (PCA) may “cause or contribute” to visibility 

impairment at the Seney Class I area (located approximately 280 km to the northeast of the mill), 

as defined by the 98th percentile visibility impacts being greater than 0.5 deciviews (dv) relative to 

natural background. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

2 December 2010 

Figure 1 - WDNR Screening CALPUFF Domain 

NOTE: Class I areas are identified by red marks. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

3 December 2010 

PCA has elected to refine the DNR screening analysis by conducting refined CALPUFF 

modeling with a 4 km meteorological grid, based on procedures described in the “Visibility 

Improvement – State and Tribal Association of the Southeast (VISTAS) BART CALPUFF” 

modeling protocol. The VISTAS protocol was developed by a large group of stakeholders, 

including EPA, the VISTAS member state agencies and tribes, the Federal Land Managers 

(FLMs), industry representatives, and consulting experts. Given the resources expended on the 

VISTAS protocol, it arguably represents the most comprehensive CALPUFF BART protocol ever 

developed. 

PCA had discussions with DNR and EPA Region 5 staff about refining the analysis, and 

submitted a refined CALPUFF BART modeling protocol in March 2007. EPA reviewed the 

protocol and provided minor comments to DNR in May 2010. Another facility undergoing 

Subject to BART review, Thilmany, responded to these comments in a letter “Response to EPA 

Comments on Thilmany BART Modeling Protocol” dated November 9, 2010. In addition, 

subsequent to the EPA protocol comments, the US Fish and Wildlife Service and US Forest 

Service reviewed the protocol and had additional discussions with DNR and EPA. The three EPA 

comments, and each response, are listed below. 

Comment 1

Information needs to be presented which clarifies how POSTUTIL was used for ammonia. 

Response 1

The VISTAS methodology was used, with a MNITRATE switch setting of one (1). 

Comment 2

The modeling must include a copy of the input and list files associated with runs. The protocol 

only offers some of the control file information. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

4 December 2010 

Response 2

All CALMET, CALPUFF, and CALPOST input and list files, as well as meteorological and 

geophysical data files, had been provided by PCA to DNR on a portable hard disk drive. PCA 

will again provide a portable hard disk drive of all modeling files to DNR for the updated BART 

analysis, for purposes of SIP documentation. 

Comment 3

The input file ... uses the background ammonia values that were produced for the LADCO 

protocol. These values are based on modeled estimates. Monitoring data has generally shown 

much higher ammonia than what was used from the model results. The refined modeling 

analyses ... must evaluate the visibility impacts using measured background ammonia values. 

Response 3

The US Fish and Wildlife Service proposed using a constant background ammonia concentration 

of 3.9 ppb, which was the highest concentration measured at the Mayville Wisconsin station 

during a mid-1990s EPA study. PCA has agreed to use this single, conservative background value 

in the absence of daily data. 

On November 29, 2010, DNR issued a letter that approved the CALPUFF BART protocol, as 

well as the emission rates to be used for the BART eligible emission units. DNR requested that 

the 2007 version of the protocol be updated to include the responses to EPA comments, and text 

that addresses current CALPUFF modeling guidance. In addition, the updated modeling results 

could be presented in the protocol (so that all information is located in one document). 

This document is the updated modeling protocol and final modeling report for the refined PCA 

“Subject to BART” analysis. This document does not duplicate the extensive information on 

visibility, CALPUFF, and EPA guidance on BART modeling procedures that are contained in the 

VISTAS protocol. Rather, this document describes how data specific to this setting will be used 

in the refined CALPUFF modeling. Section 1 of the protocol is this introduction. Section 2 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

5 December 2010 

briefly summarizes important concepts from the VISTAS protocol. Section 3 describes the 

specific CALMET data and procedures that were used to develop a refined, 4-km spaced 

meteorological grid for Wisconsin. Section 4 describes the CALPUFF input data and procedures, 

and Section 5 discusses the POSTUTIL and CALPOST processing, including the use of annual 

average natural background visibility. Section 6 presents the emission and stack data that were 

used for the BART eligible emission units, and Section 7 presents the modeling results. 

Appendices A and B present example CALMET and CALPUFF input file listings. A portable 

hard drive is also being submitted that contains all input data, control files, output files, and 

computer codes used in the analysis.

2.0 VISTAS BART Protocol 

The VISTAS member states have prepared a CALPUFF modeling protocol for BART 

determinations that is fully consistent with the EPA guidelines in 40 CFR Part 51 Appendix W

and Appendix Y. The VISTAS protocol describes a two-step CALPUFF analysis methodology 

for BART exemption analyses. The initial CALPUFF analysis uses a “screening” or coarse 

resolution meteorological grid to determine if a particular source may be exempted from further 

BART analyses. The screening results are also used to determine which Class I areas should be 

included in any refined analysis. Assumptions for the initial screening analysis are conservative 

so that a source that contributes to visibility impairment is not exempted in error. If a source is 

shown to contribute to visibility impairment using the initial screening assessment, the source has

the option to undertake refined CALPUFF modeling using finer meteorological grids to evaluate 

further whether it is subject to BART. 

VISTAS developed both coarse (12-km grid resolution) and refined (4-km grid resolution) 

CALMET files. The fine grid CALMET files utilized both MM5 prognostic data, as well as 

meteorological observational data for the CALMET “Step 2” calculations. Overwater (buoy) data 

were used in addition to the standard hourly surface meteorological observations, precipitation 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

6 December 2010 

observations, and twice-daily upper air sounding data. The VISTAS website provides detailed 

documentation and supporting information on the refined CALMET processing, including the 

CALMET and CALPUFF input files that contain model configuration options and settings that 

have been optimized after consultation with stakeholders and consulting experts. These same

CALMET and CALPUFF input files were used as the basis for the refined Wisconsin analyses. 

The VISTAS protocol discusses several options for defining the natural background visibility. 

These include use of the annual average natural background extinction or the background 

extinction for the 20% best natural conditions days. Based on an email survey of the state 

agencies from the VISTAS member states, all of the VISTAS states allowed the use of annual 

average natural background extinction for refined CALPUFF analyses. This is also the guidance 

provided by EPA Region 5 staff during discussions with DNR and the Wisconsin Paper Council, 

and the method approved by DNR in their November 29, 2010 letter. Therefore, the refined PCA 

CALPUFF modeling used the annual average natural background extinction for CALPOST 

processing. 

The VISTAS BART guidance recommends that the threshold value used to define whether a 

source “contributes” to visibility impairment is a 0.5 dv change from natural background 

conditions. The 98th percentile 24-hr average predicted impact at the Class I area (equal to the 8th

highest value) is to be compared to this contribution threshold value. According to clarification 

of the BART guidance received from EPA by the VISTAS workgroup, for a three-year simulation 

the modeling values to be compared with the threshold are the greatest of the three annual 8th

highest values, or the 22nd highest value over all three years combined, whichever is greater. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

7 December 2010 

3.0 CALMET Data and Procedures 

EPA has updated the versions of the approved CALPUFF programs since the 2007 modeling 

protocol was developed, and has provided additional guidance on CALMET “switch” settings. 

The current approved versions are CALPUFF version 5.8 (level 070623), and CALMET version 

5.8 (level 070623), and these versions were used for the updated refined BART CALPUFF 

analysis. On August 31, 2009, EPA published the memorandum “Clarification of EPA-FLM 

Recommended Settings for CALMET”. EPA stated that a 4 km fine CALMET grid size was 

acceptable, and provided recommended CALMET settings. The CALMET settings for the 

updated refined BART CALPUFF analysis meet all current EPA recommendations. 

The first step in development of the refined Wisconsin analysis was to define the CALMET 

refined modeling domain and grid. As discussed in Section 1, DNR’s screening analysis 

indicated that there are three Class I areas to the north of Wisconsin, the Boundary Waters Canoe 

Area, Isle Royal National Park, and Seney Wildlife Area, where the screening analysis predicts 

some level of visibility impact from Wisconsin BART eligible sources. Therefore, the 

meteorological grid was developed to ensure coverage for these three Class I areas, as well as for 

the BART eligible source locations throughout Wisconsin. Standard IWAQM guidance also 

recommends that the CALMET grid extend a minimum of 50 km beyond any Class I or emission 

source location, so that puff recirculation can be properly accounted for. 

The refined CALMET grid was defined as a 4-km spaced grid with 162 cells in the X-axis and 

191 in the Y-axis. The grid projection was Lambert Conformal Conic, using the same projection 

parameters as in the DNR screening analysis (this allows the use of the same source X and Y 

coordinates as in the DNR analysis). The projection parameters include RLAT0 = 40N, RLON0 

= 97W, XLAT1 = 33N, XLAT2 = 45N, XORIGKM = 247.0, YORIGKM = 240.0, and DATUM 

= NAS-C. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

8 December 2010 

The meteorological data that was input to CALMET included the same three years (2002-2004) 

of CALMM5 data used by DNR, which was provided by LADCO. However, the refined 

CALMET runs also considered observation data from 22 surface stations, 16 precipitation 

stations, 5 overwater buoy stations, and 3 upper air stations. Figure 2 is a plot of the refined 

CALPUFF modeling domain. Figure 3 presents a plot of the locations of the observation stations 

in the modeling domain. 

The CAMET program MAKEGEO uses USGS GTOPO30 digital terrain data (which includes 

coverage in Canada) and USGS Composite Theme Grid Land Use and Land Cover (LULC) data 

to create a gridded data file on geophysical parameters that is used by CALMET. The available 

USGS LULC coverage does not extend into the Canadian areas of the refined domain. These 

areas in Canada were assigned to the “forested land” category. Figure 4 presents a plot of the 

land use data for the modeling domain. 

The VISTAS refined CALMET input files discussed in section 2 were used as the basis for the 

refined Wisconsin CALMET input files. The same CALMET configuration settings and options 

were utilized, as they are representative of Wisconsin terrain and land use patterns. All settings 

conform with current EPA and FLM guidance. 

Appendix A presents a listing of a CALMET input file developed for the refined analysis. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

9 December 2010 

Figure 2 – Refined CALPUFF Modeling Domain and Locations of Class I Areas 

300 400 500 600 700 800

300

400

500

600

700

800

900

1000

1

-1

100

300

500

700

900

1100

1300

1500

1700

1900

2100

2300

2500

2700

2900

3100

3300

3500

3700

3900

4500

Terrain (m)

NOTE: The Class I area receptors are in red, the PCA Mill location is in blue, and the X and Y 

coordinates are the Lambert projection coordinates are in kms. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

10 December 2010 

Figure 3 – Locations of Observational Stations in Refined CALPUFF Modeling Domain 

300 400 500 600 700 800 900 1000

LCC East (km)

Wisconsin Refined CALMET

Location of Observation stations

300

400

500

600

700

800

900

1000

LCC N

orth (km)

MADI MILW

LAC

EAU 

GREE

MANI

WAUS STUR

MOSI CLIN

WISC

EAGL

MINE

HAYW

JUNE

DULT

MANI

SAWY

HOUG

IRNM ESCA

IRNW

MSUP

NMCH

ESUP

WSUP

SMCH

COPP

ESCA

HOUG

IRON

MANI

SAUL

CLIN

GREE

HAYW

LAC 

MADI

ME MARS NO

MILW

RAIN

MNNP GREE STURG

INTF

NOTES: Surface stations are in red, overwater (buoy) in blue, precipitation in green, and upper 

air in purple.
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

11 December 2010 

Figure 4 – Land Use Data for Refined CALPUFF Modeling Domain 

300 400 500 600 700 800

LCC East (km)

300

400

500

600

700

800

900

1000

LCC North (km)

Snow/Ice

Tundra

Barren

Wetland

Water

Forest

Range

Agriculture

Urban/Built-Up

Land Use

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

95

100

. .

. .

LCC Origin: 40N, 97W

Datum: NAS-C

Matching Parallels: 33N, 45N

False Easting: 0.0

False Northing: 0.0
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

12 December 2010 

Some of the notable CALMET configuration settings included: 

• CALMET vertical layers set to 10, with cell face heights at 20, 40, 80, 160, 320, 640, 

1200, 2000, 3000, and 4000 meters, 

• CALMET diagnostic options, including slope flow effects (ISLOPE = 1) with the radius 

of influence of terrain (TERRAD) set to 15 km, 

• EPA recommended CALMET settings for the radius of influence parameters (R1=50, 

R2=100, RMAX1=100, RMAX2=200, and RMAX3=200). 

4.0 CALPUFF Procedures 

Both the DNR screening and VISTAS refined CALPUFF input files were used as the basis for the 

refined Wisconsin CALPUFF input files. All CALPUFF settings and options are consistent with 

EPA and FLM guidance, and the refined VISTAS protocol recommendations. The background 

ozone (O3) concentrations were used directly from the DNR CALPUFF input files. Instead of 

using monthly background ammonia concentrations from the DNR screening analyses, a single 

conservative background ammonia concentration of 3.9 ppb was used. Appendix B presents a 

listing of a CALPUFF input file developed for the analysis. 

The DNR screening analysis considered three emitted pollutants, SO2, NOx, and PM2.5. The 

refined CALPUFF modeling will consider speciated particulate emissions, including coarse PM 

(PMC), fine PM equivalent to PM2.5 (PMF), sulfate (SO4), nitrate (NO3), elemental carbon (EC), 

and secondary organic aerosols (SOA or OC). Section 6 of this protocol describes how the 

speciated particulate emissions were calculated. 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

13 December 2010 

5.0 POSTUTIL and CALPOST Procedures 

In CALPUFF, the scavenging of the available ammonia for nitrate formation is computed on a 

puff-by-puff basis. Because of the possibility of multiple puff overlap, this approach may tend to 

overestimate the amount of ammonia available to form nitrate. In order to address the cumulative 

consumption of ammonia, the POSTUTIL program can be used to repartition nitric acid and 

nitrate. POSTUTIL calculates new NO3/HNO3 equilibrium concentrations for the sample source 

in the Class I area using the background ammonia. As recommended in the VISTAS procedures 

for refined CALPUFF modeling, the POSTUTIL “MNITRATE=1” method was used for the 

refined Wisconsin CALPUFF modeling. Instead of using the monthly values for background 

ammonia concentrations from the DNR screening analyses, a single conservative background 

ammonia concentration of 3.9 ppb was used. 

The modeling protocol submitted in 2007 proposed to use CALPOST Visibility Method 6 to 

calculate visibility impacts. However, since that time there have been revisions to CALPOST that 

allow the use of the updated IMPROVE extinction equation. CALPOST version 6.221 can 

implement the “Method 8 Mode 5” methodology to calculate visibility impacts, and the FLMs 

recommend its use in “Federal Land Managers’ Air Quality Related Values Work Group (FLAG) 

Phase I Report—Revised (2010)” (herein referred to as FLAG 2010). Therefore, this updated 

methodology will be used for the PCA BART analysis. The new CALPUFF Graphical Users 

Interface automatically enters the appropriate values, based on the Class I area being selected, for 

natural background species and relative humidity adjustment factors using the data in Tables 6 

through 9 of Section 3.3.5 of FLAG 2010 (which are based on “Guidance for Estimating Natural 

Visibility Conditions Under the Regional Haze Rule”, EPA-454/B-03-005, September 2003). 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

14 December 2010 

6.0 Emissions Modeled 

EPA’s BART modeling guidance state that the 24-hr maximum actual emissions rates for the 

period of the modeling simulation (2002-2004) should be used for the analysis. If this data is not 

available, then the short term “allowable” or “potential” emission rates should be used. PCA 

provided DNR with source information that has been reviewed to determine the 24-hr maximum 

actual emissions rates. On November 29, 2010, DNR issued a letter that approved the following 

emission rates to be used for the PCA BART eligible boiler: 166.3 g/sec (1320 lb/hr) SO2, 13.4 

g/sec (106 lb/hr) NOX, and 4.2 g/sec (33 lb/hr) for PM. The PM emissions have been speciated 

using the information for coal fired boilers developed by the National Park Service1

. The 

speciated PM emissions listed in Table 1 were used in the refined BART modeling. The stack 

parameters used in the modeling analysis were the same as those used by DNR in their screening 

analysis. 

Table 1 – PCA Speciated PM Emissions 

PM Species Emission Rate (lb/hr) 

Coarse PM 3.8 

Fine PM 7.8 

Elemental Carbon 0.3 

Condensable Inorganics (Sulfate) 17.2 

Condensable Organics (OC) 4.3 

 

1 http://www2.nature.nps.gov/air/permits/ect/index.cfm) 
 Updated BART Modeling Protocol and Report for 

 PCA Tomahawk Mill

15 December 2010 

7.0 Modeling Results 

CALPOST computes the daily maximum change in deciviews relative to the annual average 

natural background visibility, separately for each Class I area. For evaluating the source impact 

relative to the “Subject to BART” visibility impact threshold of 0.5 dv, the daily maximum

changes in visibility are sorted to determine the 98th percentile (8th highest) value for each of 

three years, and the 98th percentile (22nd highest) value for the completed three year period. If all 

98th percentile values are below the threshold of 0.5 dv based on the refined CALPUFF analysis, 

the source is exempt from the BART requirements. 

Another equivalent metric commonly used for BART exemption modeling is to sum the number 

of days per year that are above the 0.5 dv threshold for each Class I area separately; if there are 7 

or fewer days above the threshold for each year, then the 98th percentile value is also below the 

threshold. This is the metric approved by DNR for use in the BART modeling analysis. 

Specifically, for each Class I area separately, if there are less than 8 days per year that the 

predicted visibility impacts are greater than 0.5 deciviews relative to the annual average natural 

background visibility, then the BART eligible emission units at the modeled facility will be 

determined not to be Subject to BART. 

Table 2 presents the results from the refined CALPUFF BART exemption modeling. These 

results demonstrate that there are less than 8 days per year, at each individual Class I area, when 

the visibility impacts from the PCA BART eligible emission unit are above 0.5 dv. Therefore, the 

PCA BART eligible source is not Subject to BART requirements. 
Updated BART Modeling Protocol an

PCA Tom

Table 2 – PCA CALPUFF BART Exemption Results Summary 

Class I area Distance 

(km) from 

source to

Class I area 

boundary

# of days 

with impact

> 0.5 dv in 

Class I area:

2002

# of days with

impact > 0.5 

dv in Class I 

area: 2003

# of days 

with impact

> 0.5 dv in 

Class I area:

2004

# of days with

impact > 0.5 

dv in Class I 

area for 3 year

period

Maximum 98th

Percentile 

impact over 

either annual 

or 3-yr periods

Seney , MI ~ 280 0 0 1 1 0.18Isle Royal, MN ~ 320 0 0 0 0 0.14Boundary Waters, MN ~ 350 0 0 0 0 0.13

16 D
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

Appendix A – Example CALMET Input File 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

WI Refined CALMET - 4km Grid - Dec 2010 - with Updated EPA Settings 

---------------- Run title (3 lines) ------------------------------------------ 

 CALMET MODEL CONTROL FILE 

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

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

INPUT GROUP: 0 -- Input and Output File Names 

Subgroup (a) 

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

Default Name Type File Name 

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

GEO.DAT input ! GEODAT=geo.dat ! 

SURF.DAT input ! SRFDAT=SURF02Z.DAT ! 

CLOUD.DAT input * CLDDAT= * 

PRECIP.DAT input ! PRCDAT=PRECIP02.DAT ! 

MM4.DAT input * MM4DAT=E:\MRPO-calmm5\2002\MM5.020102.3D.DAT * 

MM4.DAT input ! MM4DAT=E:\MRPO-calmm5\2002\020102.MM5 ! 

WT.DAT input * WTDAT= * 

CALMET.LST output ! METLST=cal020102.lST ! 

CALMET.DAT output ! METDAT=E:\WI-Calmet\2002Output\cal020102.dat ! 

PACOUT.DAT output * PACDAT= * 

All file names will be converted to lower case if LCFILES = T 

Otherwise, if LCFILES = F, file names will be converted to UPPER CASE 

 T = lower case ! LCFILES = T ! 

 F = UPPER CASE 

NUMBER OF UPPER AIR & OVERWATER STATIONS: 

 Number of upper air stations (NUSTA) No default ! NUSTA = 3 ! 

 Number of overwater met stations 

 (NOWSTA) No default ! NOWSTA = 5 ! 

 !END! 

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

Subgroup (b) 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

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

Upper air files (one per station) 

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

Default Name Type File Name 

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

UP1.DAT input 1 ! UPDAT=UPGB0204.DAT! !END! 

UP2.DAT input 2 ! UPDAT=UPMN0204.DAT! !END! 

UP3.DAT input 3 ! UPDAT=UPIN0204.DAT! !END! 

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

Subgroup (c) 

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

Overwater station files (one per station) 

SEA1.DAT input 1 ! SEADAT=4500102.DAT! !END! 

SEA2.DAT input 2 ! SEADAT=4500202.DAT! !END! 

SEA3.DAT input 3 ! SEADAT=4500402.DAT! !END! 

SEA4.DAT input 4 ! SEADAT=4500602.DAT! !END! 

SEA5.DAT input 5 ! SEADAT=4500702.DAT! !END! 

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

Default Name Type File Name 

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

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

Subgroup (d) 

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

Other file names 

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

Default Name Type File Name 

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

DIAG.DAT input * DIADAT= * 

PROG.DAT input * PRGDAT= * 

TEST.PRT output * TSTPRT= * 

TEST.OUT output * TSTOUT= * 

TEST.KIN output * TSTKIN= * 

TEST.FRD output * TSTFRD= * 

TEST.SLP output * TSTSLP= * 

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

NOTES: (1) File/path names can be up to 70 characters in length 

 (2) Subgroups (a) and (d) must have ONE 'END' (surround by 

 delimiters) at the end of the group 

 (3) Subgroups (b) and (c) must have an 'END' (surround by 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 delimiters) at the end of EACH LINE 

 !END! 

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

INPUT GROUP: 1 -- General run control parameters 

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

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

 Month (IBMO) -- No default ! IBMO= 1 ! 

 Day (IBDY) -- No default ! IBDY= 2 ! 

 Hour (IBHR) -- No default ! IBHR= 0 ! 

 Base time zone (IBTZ) -- No default ! IBTZ= 6 ! 

 PST = 08, MST = 07 

 CST = 06, EST = 05 

 Length of run (hours) (IRLG) -- No default ! IRLG= 24 ! 

 Run type (IRTYPE) -- Default: 1 ! IRTYPE= 1 ! 

 0 = Computes wind fields only 

 1 = Computes wind fields and micrometeorological variables 

 (u*, w*, L, zi, etc.) 

 (IRTYPE must be 1 to run CALPUFF or CALGRID) 

 Compute special data fields required 

 by CALGRID (i.e., 3-D fields of W wind 

 components and temperature) 

 in additional to regular Default: T ! LCALGRD = T ! 

 fields ? (LCALGRD) 

 (LCALGRD must be T to run CALGRID) 

 Flag to stop run after 

 SETUP phase (ITEST) Default: 2 ! ITEST= 2 ! 

 (Used to allow checking 

 of the model inputs, files, etc.) 

 ITEST = 1 - STOPS program after SETUP phase 

 ITEST = 2 - Continues with execution of 

 COMPUTATIONAL phase after SETUP 

 Test options specified to see if 

 they conform to regulatory 

December 2010 
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 values? (MREG) No Default ! MREG = 1 ! 

 0 = NO checks are made 

 1 = Technical options must conform to USEPA guidance 

 IMIXH -1 Maul-Carson convective mixing height 

 over land; OCD mixing height overwater 

 ICOARE 0 OCD deltaT method for overwater fluxes 

 THRESHL 0.0 Threshold buoyancy flux over land needed 

 to sustain convective mixing height grow 

!END! 

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

INPUT GROUP: 2 -- Map Projection and Grid control parameters 

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

 Projection for all (X,Y): 

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

 Map projection 

 (PMAP) Default: UTM ! PMAP = LCC ! 

 UTM : Universal Transverse Mercator 

 TTM : Tangential Transverse Mercator 

 LCC : Lambert Conformal Conic 

 PS : Polar Stereographic 

 EM : 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 = -999 ! 

 Hemisphere for UTM projection? 

 (Used only if PMAP=UTM) 

 (UTMHEM) Default: N ! UTMHEM = N ! 

 N : Northern hemisphere projection 

 S : Southern hemisphere projection 

December 2010 
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 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 XLAT2 

 PS : 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, and 

 east or west longitude. For example, 

 35.9 N Latitude = 35.9N 

 118.7 E Longitude = 118.7E 

 Datum-region 

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

 The Datum-Region for the coordinates is identified by a character 

 string. Many mapping products currently available use the model of the 

 Earth known as the World Geodetic System 1984 (WGS-84). Other local 

 models may be in use, and their selection in CALMET will make its output 

 consistent with local mapping products. The list of Datum-Regions with 

 official transformation parameters is provided by the National Imagery and 

 Mapping Agency (NIMA). 

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 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, Sphere 

 ESR-S ESRI REFERENCE 6371KM Radius, Sphere 

 Datum-region for output coordinates 

 (DATUM) Default: WGS-84 ! DATUM = NAS-C ! 

 Horizontal grid definition: 

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

 Rectangular grid defined for projection PMAP, 

 with X the Easting and Y the Northing coordinate 

 No. X grid cells (NX) No default ! NX = 162 ! 

 No. Y grid cells (NY) No default ! NY = 191 ! 

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

 Units: km 

 Reference grid coordinate of 

 SOUTHWEST corner of grid cell (1,1) 

 X coordinate (XORIGKM) No default ! XORIGKM = 247.000 ! 

 Y coordinate (YORIGKM) No default ! YORIGKM = 240.000 ! 

 Units: km 

 Vertical grid definition: 

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

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

 Cell face heights in arbitrary 

 vertical grid (ZFACE(NZ+1)) No defaults 

 Units: m 

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

!END! 

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

INPUT GROUP: 3 -- Output Options 

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

 DISK OUTPUT OPTION 

 Save met. fields in an unformatted 

 output file ? (LSAVE) Default: T ! LSAVE = T ! 

 (F = Do not save, T = Save) 

 Type of unformatted output file: 

 (IFORMO) Default: 1 ! IFORMO = 1 ! 

 1 = CALPUFF/CALGRID type file (CALMET.DAT) 

 2 = MESOPUFF-II type file (PACOUT.DAT) 

 LINE PRINTER OUTPUT OPTIONS: 

 Print met. fields ? (LPRINT) Default: F ! LPRINT = T ! 

 (F = Do not print, T = Print) 

 (NOTE: parameters below control which 

 met. variables are printed) 

 Print interval 

 (IPRINF) in hours Default: 1 ! IPRINF = 1 ! 

 (Meteorological fields are printed 

 every 1 hours) 

 Specify which layers of U, V wind component 

 to print (IUVOUT(NZ)) -- NOTE: NZ values must be entered 

 (0=Do not print, 1=Print) 

 (used only if LPRINT=T) Defaults: NZ*0 

 ! IUVOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

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

 Specify which levels of the W wind component to print 

 (NOTE: W defined at TOP cell face -- 16 values) 

 (IWOUT(NZ)) -- NOTE: NZ values must be entered 

December 2010 
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 (0=Do not print, 1=Print) 

 (used only if LPRINT=T & LCALGRD=T) 

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

 Defaults: NZ*0 

 ! IWOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Specify which levels of the 3-D temperature field to print 

 (ITOUT(NZ)) -- NOTE: NZ values must be entered 

 (0=Do not print, 1=Print) 

 (used only if LPRINT=T & LCALGRD=T) 

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

 Defaults: NZ*0 

 ! ITOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Specify which meteorological fields 

 to print 

 (used only if LPRINT=T) Defaults: 0 (all variables) 

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

 Variable Print ? 

 (0 = do not print, 

 1 = print) 

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

 ! STABILITY = 0 ! - PGT stability class 

 ! USTAR = 0 ! - Friction velocity 

 ! MONIN = 0 ! - Monin-Obukhov length 

 ! MIXHT = 0 ! - Mixing height 

 ! WSTAR = 0 ! - Convective velocity scale 

 ! PRECIP = 0 ! - Precipitation rate 

 ! SENSHEAT = 0 ! - Sensible heat flux 

 ! CONVZI = 0 ! - Convective mixing ht. 

 Testing and debug print options for micrometeorological module 

 Print input meteorological data and 

 internal variables (LDB) Default: F ! LDB = F ! 

 (F = Do not print, T = print) 

 (NOTE: this option produces large amounts of output) 

 First time step for which debug data 

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 are printed (NN1) Default: 1 ! NN1 = 1 ! 

 Last time step for which debug data 

 are printed (NN2) Default: 1 ! NN2 = 2 ! 

 Testing and debug print options for wind field module 

 (all of the following print options control output to 

 wind field module's output files: TEST.PRT, TEST.OUT, 

 TEST.KIN, TEST.FRD, and TEST.SLP) 

 Control variable for writing the test/debug 

 wind fields to disk files (IOUTD) 

 (0=Do not write, 1=write) Default: 0 ! IOUTD = 0 ! 

 Number of levels, starting at the surface, 

 to print (NZPRN2) Default: 1 ! NZPRN2 = 1 ! 

 Print the INTERPOLATED wind components ? 

 (IPR0) (0=no, 1=yes) Default: 0 ! IPR0 = 0 ! 

 Print the TERRAIN ADJUSTED surface wind 

 components ? 

 (IPR1) (0=no, 1=yes) Default: 0 ! IPR1 = 0 ! 

 Print the SMOOTHED wind components and 

 the INITIAL DIVERGENCE fields ? 

 (IPR2) (0=no, 1=yes) Default: 0 ! IPR2 = 0 ! 

 Print the FINAL wind speed and direction 

 fields ? 

 (IPR3) (0=no, 1=yes) Default: 0 ! IPR3 = 0 ! 

 Print the FINAL DIVERGENCE fields ? 

 (IPR4) (0=no, 1=yes) Default: 0 ! IPR4 = 0 ! 

 Print the winds after KINEMATIC effects 

 are added ? 

 (IPR5) (0=no, 1=yes) Default: 0 ! IPR5 = 0 ! 

 Print the winds after the FROUDE NUMBER 

 adjustment is made ? 

 (IPR6) (0=no, 1=yes) Default: 0 ! IPR6 = 0 ! 

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 Print the winds after SLOPE FLOWS 

 are added ? 

 (IPR7) (0=no, 1=yes) Default: 0 ! IPR7 = 0 ! 

 Print the FINAL wind field components ? 

 (IPR8) (0=no, 1=yes) Default: 0 ! IPR8 = 0 ! 

!END! 

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

INPUT GROUP: 4 -- Meteorological data options 

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

 NO OBSERVATION MODE (NOOBS) Default: 0 ! NOOBS = 0 ! 

 0 = Use surface, overwater, and upper air stations 

 1 = Use surface and overwater stations (no upper air observations) 

 Use MM5 for upper air data 

 2 = No surface, overwater, or upper air observations 

 Use MM5 for surface, overwater, and upper air data 

 NUMBER OF SURFACE & PRECIP. METEOROLOGICAL STATIONS 

 Number of surface stations (NSSTA) No default ! NSSTA = 22 ! 

 Number of precipitation stations 

 (NPSTA=-1: flag for use of MM5 precip data) 

 (NPSTA) No default ! NPSTA = 16 ! 

 CLOUD DATA OPTIONS 

 Gridded cloud fields: 

 (ICLOUD) Default: 0 ! ICLOUD = 0 ! 

 ICLOUD = 0 - Gridded clouds not used 

 ICLOUD = 1 - Gridded CLOUD.DAT generated as OUTPUT 

 ICLOUD = 2 - Gridded CLOUD.DAT read as INPUT 

 ICLOUD = 3 - Gridded cloud cover from Prognostic Rel. Humidity 

 FILE FORMATS 

 Surface meteorological data file format 

 (IFORMS) Default: 2 ! IFORMS = 2 ! 

 (1 = unformatted (e.g., SMERGE output)) 

 (2 = formatted (free-formatted user input)) 

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 Precipitation data file format 

 (IFORMP) Default: 2 ! IFORMP = 2 ! 

 (1 = unformatted (e.g., PMERGE output)) 

 (2 = formatted (free-formatted user input)) 

 Cloud data file format 

 (IFORMC) Default: 2 ! IFORMC = 2 ! 

 (1 = unformatted - CALMET unformatted output) 

 (2 = formatted - free-formatted CALMET output or user input) 

!END! 

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

INPUT GROUP: 5 -- Wind Field Options and Parameters 

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

 WIND FIELD MODEL OPTIONS 

 Model selection variable (IWFCOD) Default: 1 ! IWFCOD = 1 ! 

 0 = Objective analysis only 

 1 = Diagnostic wind module 

 Compute Froude number adjustment 

 effects ? (IFRADJ) Default: 1 ! IFRADJ = 1 ! 

 (0 = NO, 1 = YES) 

 Compute kinematic effects ? (IKINE) Default: 0 ! IKINE = 0 ! 

 (0 = NO, 1 = YES) 

 Use O'Brien procedure for adjustment 

 of the vertical velocity ? (IOBR) Default: 0 ! IOBR = 0 ! 

 (0 = NO, 1 = YES) 

 Compute slope flow effects ? (ISLOPE) Default: 1 ! ISLOPE = 1 ! 

 (0 = NO, 1 = YES) 

 Extrapolate surface wind observations 

 to upper layers ? (IEXTRP) Default: -4 ! IEXTRP = -4 ! 

 (1 = no extrapolation is done, 

 2 = power law extrapolation used, 

 3 = user input multiplicative factors 

December 2010 
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 for layers 2 - NZ used (see FEXTRP array) 

 4 = similarity theory used 

 -1, -2, -3, -4 = same as above except layer 1 data 

 at upper air stations are ignored 

 Extrapolate surface winds even 

 if calm? (ICALM) Default: 0 ! ICALM = 0 ! 

 (0 = NO, 1 = YES) 

 Layer-dependent biases modifying the weights of 

 surface and upper air stations (BIAS(NZ)) 

 -1<=BIAS<=1 

 Negative BIAS reduces the weight of upper air stations 

 (e.g. BIAS=-0.1 reduces the weight of upper air stations 

 by 10%; BIAS= -1, reduces their weight by 100 %) 

 Positive BIAS reduces the weight of surface stations 

 (e.g. BIAS= 0.2 reduces the weight of surface stations 

 by 20%; BIAS=1 reduces their weight by 100%) 

 Zero BIAS leaves weights unchanged (1/R**2 interpolation) 

 Default: NZ*0 

 ! BIAS = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Minimum distance from nearest upper air station 

 to surface station for which extrapolation 

 of surface winds at surface station will be allowed 

 (RMIN2: Set to -1 for IEXTRP = 4 or other situations 

 where all surface stations should be extrapolated) 

 Default: 4. ! RMIN2 = -1.0 ! 

 Use gridded prognostic wind field model 

 output fields as input to the diagnostic 

 wind field model (IPROG) Default: 0 ! IPROG = 14 ! 

 (0 = No, [IWFCOD = 0 or 1] 

 1 = Yes, use CSUMM prog. winds as Step 1 field, [IWFCOD = 0] 

 2 = Yes, use CSUMM prog. winds as initial guess field [IWFCOD = 1] 

 3 = Yes, use winds from MM4.DAT file as Step 1 field [IWFCOD = 0] 

 4 = Yes, use winds from MM4.DAT file as initial guess field [IWFCOD = 1] 

 5 = Yes, use winds from MM4.DAT file as observations [IWFCOD = 1] 

 13 = Yes, use winds from MM5.DAT file as Step 1 field [IWFCOD = 0] 

 14 = Yes, use winds from MM5.DAT file as initial guess field [IWFCOD = 1] 

 15 = Yes, use winds from MM5.DAT file as observations [IWFCOD = 1] 

 Timestep (hours) of the prognostic 

 model input data (ISTEPPG) Default: 1 ! ISTEPPG = 1 ! 

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 RADIUS OF INFLUENCE PARAMETERS 

 Use varying radius of influence Default: F ! LVARY = F! 

 (if no stations are found within RMAX1,RMAX2, 

 or RMAX3, then the closest station will be used) 

 Maximum radius of influence over land 

 in the surface layer (RMAX1) No default ! RMAX1 = 100. ! 

 Units: km 

 Maximum radius of influence over land 

 aloft (RMAX2) No default ! RMAX2 = 200. ! 

 Units: km 

 Maximum radius of influence over water 

 (RMAX3) No default ! RMAX3 = 200. ! 

 Units: km 

 OTHER WIND FIELD INPUT PARAMETERS 

 Minimum radius of influence used in 

 the wind field interpolation (RMIN) Default: 0.1 ! RMIN = 0.1 ! 

 Units: km 

 Radius of influence of terrain 

 features (TERRAD) No default ! TERRAD = 15. ! 

 Units: km 

 Relative weighting of the first 

 guess field and observations in the 

 SURFACE layer (R1) No default ! R1 = 50. ! 

 (R1 is the distance from an Units: km 

 observational station at which the 

 observation and first guess field are 

 equally weighted) 

 Relative weighting of the first 

 guess field and observations in the 

 layers ALOFT (R2) No default ! R2 =100. ! 

 (R2 is applied in the upper layers Units: km 

 in the same manner as R1 is used in 

 the surface layer). 

 Relative weighting parameter of the 

 prognostic wind field data (RPROG) No default ! RPROG = 0. ! 

December 2010 
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 PCA Tomahawk Mill

 (Used only if IPROG = 1) Units: km 

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

 Maximum acceptable divergence in the 

 divergence minimization procedure 

 (DIVLIM) Default: 5.E-6 ! DIVLIM= 5.0E-06 ! 

 Maximum number of iterations in the 

 divergence min. procedure (NITER) Default: 50 ! NITER = 50 ! 

 Number of passes in the smoothing 

 procedure (NSMTH(NZ)) 

 NOTE: NZ values must be entered 

 Default: 2,(mxnz-1)*4 ! NSMTH = 

 2 , 4 , 4 , 4 , 4 , 4 , 4 , 4 , 4 , 4 ! 

 Maximum number of stations used in 

 each layer for the interpolation of 

 data to a grid point (NINTR2(NZ)) 

 NOTE: NZ values must be entered Default: 99. ! NINTR2 = 

 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 ! 

 Critical Froude number (CRITFN) Default: 1.0 ! CRITFN = 1. ! 

 Empirical factor controlling the 

 influence of kinematic effects 

 (ALPHA) Default: 0.1 ! ALPHA = 0.1 ! 

 Multiplicative scaling factor for 

 extrapolation of surface observations 

 to upper layers (FEXTR2(NZ)) Default: NZ*0.0 

 ! FEXTR2 = 0., 0., 0., 0., 0., 0., 0., 0., 0., 0. ! 

 (Used only if IEXTRP = 3 or -3) 

 BARRIER INFORMATION 

 Number of barriers to interpolation 

 of the wind fields (NBAR) Default: 0 ! NBAR = 0 ! 

 THE FOLLOWING 4 VARIABLES ARE INCLUDED 

 ONLY IF NBAR > 0 

 NOTE: NBAR values must be entered No defaults 

 for each variable Units: km 

December 2010 
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 PCA Tomahawk Mill

 X coordinate of BEGINNING 

 of each barrier (XBBAR(NBAR)) ! XBBAR = 0. ! 

 Y coordinate of BEGINNING 

 of each barrier (YBBAR(NBAR)) ! YBBAR = 0. ! 

 X coordinate of ENDING 

 of each barrier (XEBAR(NBAR)) ! XEBAR = 0. ! 

 Y coordinate of ENDING 

 of each barrier (YEBAR(NBAR)) ! YEBAR = 0. ! 

 DIAGNOSTIC MODULE DATA INPUT OPTIONS 

 Surface temperature (IDIOPT1) Default: 0 ! IDIOPT1 = 0 ! 

 0 = Compute internally from 

 hourly surface observations 

 1 = Read preprocessed values from 

 a data file (DIAG.DAT) 

 Surface met. station to use for 

 the surface temperature (ISURFT) No default ! ISURFT = 1 ! 

 (Must be a value from 1 to NSSTA) 

 (Used only if IDIOPT1 = 0) 

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

 Domain-averaged temperature lapse 

 rate (IDIOPT2) Default: 0 ! IDIOPT2 = 0 ! 

 0 = Compute internally from 

 twice-daily upper air observations 

 1 = Read hourly preprocessed values 

 from a data file (DIAG.DAT) 

 Upper air station to use for 

 the domain-scale lapse rate (IUPT) No default ! IUPT = 1 ! 

 (Must be a value from 1 to NUSTA) 

 (Used only if IDIOPT2 = 0) 

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

 Depth through which the domain-scale 

 lapse rate is computed (ZUPT) Default: 200. ! ZUPT = 200. ! 

 (Used only if IDIOPT2 = 0) Units: meters 

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

December 2010 
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 Domain-averaged wind components 

 (IDIOPT3) Default: 0 ! IDIOPT3 = 0 ! 

 0 = Compute internally from 

 twice-daily upper air observations 

 1 = Read hourly preprocessed values 

 a data file (DIAG.DAT) 

 Upper air station to use for 

 the domain-scale winds (IUPWND) Default: -1 ! IUPWND = -1 ! 

 (Must be a value from -1 to NUSTA) 

 (Used only if IDIOPT3 = 0) 

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

 Bottom and top of layer through 

 which the domain-scale winds 

 are computed 

 (ZUPWND(1), ZUPWND(2)) Defaults: 1., 1000. ! ZUPWND= 1., 1000. ! 

 (Used only if IDIOPT3 = 0) Units: meters 

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

 Observed surface wind components 

 for wind field module (IDIOPT4) Default: 0 ! IDIOPT4 = 0 ! 

 0 = Read WS, WD from a surface 

 data file (SURF.DAT) 

 1 = Read hourly preprocessed U, V from 

 a data file (DIAG.DAT) 

 Observed upper air wind components 

 for wind field module (IDIOPT5) Default: 0 ! IDIOPT5 = 0 ! 

 0 = Read WS, WD from an upper 

 air data file (UP1.DAT, UP2.DAT, etc.) 

 1 = Read hourly preprocessed U, V from 

 a data file (DIAG.DAT) 

 LAKE BREEZE INFORMATION 

 Use Lake Breeze Module (LLBREZE) 

 Default: F ! LLBREZE = F ! 

 Number of lake breeze regions (NBOX) ! NBOX = 0 ! 

 X Grid line 1 defining the region of interest 

 ! XG1 = 0. ! 

 X Grid line 2 defining the region of interest 

December 2010 
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 ! XG2 = 0. ! 

 Y Grid line 1 defining the region of interest 

 ! YG1 = 0. ! 

 Y Grid line 2 defining the region of interest 

 ! YG2 = 0. ! 

 X Point defining the coastline (Straight line) 

 (XBCST) (KM) Default: none ! XBCST = 0. ! 

 Y Point defining the coastline (Straight line) 

 (YBCST) (KM) Default: none ! YBCST = 0. ! 

 X Point defining the coastline (Straight line) 

 (XECST) (KM) Default: none ! XECST = 0. ! 

 Y Point defining the coastline (Straight line) 

 (YECST) (KM) Default: none ! YECST = 0. ! 

 Number of stations in the region Default: none ! NLB = 0 ! 

 (Surface stations + upper air stations) 

 Station ID's in the region (METBXID(NLB)) 

 (Surface stations first, then upper air stations) 

 ! METBXID = 0 ! 

!END! 

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

INPUT GROUP: 6 -- Mixing Height, Temperature and Precipitation Parameters 

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

 EMPIRICAL MIXING HEIGHT CONSTANTS 

 Neutral, mechanical equation 

 (CONSTB) Default: 1.41 ! CONSTB = 1.41 ! 

 Convective mixing ht. equation 

 (CONSTE) Default: 0.15 ! CONSTE = 0.15 ! 

 Stable mixing ht. equation 

 (CONSTN) Default: 2400. ! CONSTN = 2400.! 

 Overwater mixing ht. equation 

 (CONSTW) Default: 0.16 ! CONSTW = 0.16 ! 

December 2010 
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 PCA Tomahawk Mill

 Absolute value of Coriolis 

 parameter (FCORIOL) Default: 1.E-4 ! FCORIOL = 1.0E-04! 

 Units: (1/s) 

 SPATIAL AVERAGING OF MIXING HEIGHTS 

 Conduct spatial averaging 

 (IAVEZI) (0=no, 1=yes) Default: 1 ! IAVEZI = 1 ! 

 Max. search radius in averaging 

 process (MNMDAV) Default: 1 ! MNMDAV = 1 ! 

 Units: Grid 

 cells 

 Half-angle of upwind looking cone 

 for averaging (HAFANG) Default: 30. ! HAFANG = 30. ! 

 Units: deg. 

 Layer of winds used in upwind 

 averaging (ILEVZI) Default: 1 ! ILEVZI = 1 ! 

 (must be between 1 and NZ) 

 CONVECTIVE MIXING HEIGHT OPTIONS: 

 Method to compute the convective 

 mixing height(IMIHXH) Default: 1 ! IMIXH = -1 ! 

 1: Maul-Carson for land and water cells 

 -1: Maul-Carson for land cells only - 

 OCD mixing height overwater 

 2: Batchvarova and Gryning for land and water cells 

 -2: Batchvarova and Gryning for land cells only 

 OCD mixing height overwater 

 Threshold buoyancy flux required to 

 sustain convective mixing height growth 

 overland (THRESHL) Default: 0.05 ! THRESHL = 0.00 ! 

 (expressed as a heat flux units: W/m3 

 per meter of boundary layer) 

 Threshold buoyancy flux required to 

 sustain convective mixing height growth 

 overwater (THRESHW) Default: 0.05 ! THRESHW = 0.05 ! 

 (expressed as a heat flux units: W/m3 

 per meter of boundary layer) 

 Option for overwater lapse rates used 

 in convective mixing height growth 

December 2010 
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 PCA Tomahawk Mill

 (ITWPROG) Default: 0 ! ITWPROG = 0 ! 

 0 : use SEA.DAT lapse rates and deltaT (or assume neutral 

 conditions if missing) 

 1 : use prognostic lapse rates (only if IPROG>2) 

 and SEA.DAT deltaT (or neutral if missing) 

 2 : use prognostic lapse rates and prognostic delta T 

 (only if iprog>12 and 3D.DAT version# 2.0 or higher) 

 Land Use category ocean in 3D.DAT datasets 

 (ILUOC3D) Default: 16 ! ILUOC3D = 16 ! 

 Note: if 3D.DAT from MM5 version 3.0, iluoc3d = 16 

 if MM4.DAT, typically iluoc3d = 7 

 OTHER MIXING HEIGHT VARIABLES 

 Minimum potential temperature lapse 

 rate in the stable layer above the 

 current convective mixing ht. Default: 0.001 ! DPTMIN = 0.001 ! 

 (DPTMIN) Units: deg. K/m 

 Depth of layer above current conv. 

 mixing height through which lapse Default: 200. ! DZZI = 200. ! 

 rate is computed (DZZI) Units: meters 

 Minimum overland mixing height Default: 50. ! ZIMIN = 50. ! 

 (ZIMIN) Units: meters 

 Maximum overland mixing height Default: 3000. ! ZIMAX = 3000. ! 

 (ZIMAX) Units: meters 

 Minimum overwater mixing height Default: 50. ! ZIMINW = 50. ! 

 (ZIMINW) -- (Not used if observed Units: meters 

 overwater mixing hts. are used) 

 Maximum overwater mixing height Default: 3000. ! ZIMAXW = 3000. ! 

 (ZIMAXW) -- (Not used if observed Units: meters 

 overwater mixing hts. are used) 

 OVERWATER SURFACE FLUXES METHOD and PARAMETERS 

 (ICOARE) Default: 10 ! ICOARE = 0 ! 

 0: original deltaT method (OCD) 

 10: COARE with no wave parameterization (jwave=0, Charnock) 

 11: COARE with wave option jwave=1 (Oost et al.) 

 and default wave properties 

 -11: COARE with wave option jwave=1 (Oost et al.) 

 and observed wave properties (must be in SEA.DAT files) 

 12: COARE with wave option 2 (Taylor and Yelland) 

 and default wave properties 

December 2010 
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 PCA Tomahawk Mill

 -12: COARE with wave option 2 (Taylor and Yelland) 

 and observed wave properties (must be in SEA.DAT files) 

 Coastal/Shallow water length scale (DSHELF) 

 (for modified z0 in shallow water) 

 ( COARE fluxes only) 

 Default : 0. ! DSHELF = 0. ! 

 units: km 

 COARE warm layer computation (IWARM) ! IWARM = 0 ! 

 1: on - 0: off (must be off if SST measured with 

 IR radiometer) Default: 0 

 COARE cool skin layer computation (ICOOL) ! ICOOL = 0 ! 

 1: on - 0: off (must be off if SST measured with 

 IR radiometer) Default: 0 

 TEMPERATURE PARAMETERS 

 3D temperature from observations or 

 from prognostic data? (ITPROG) Default:0 !ITPROG = 0 ! 

 0 = Use Surface and upper air stations 

 (only if NOOBS = 0) 

 1 = Use Surface stations (no upper air observations) 

 Use MM5 for upper air data 

 (only if NOOBS = 0,1) 

 2 = No surface or upper air observations 

 Use MM5 for surface and upper air data 

 (only if NOOBS = 0,1,2) 

 Interpolation type 

 (1 = 1/R ; 2 = 1/R**2) Default:1 ! IRAD = 1 ! 

 Radius of influence for temperature 

 interpolation (TRADKM) Default: 500. ! TRADKM = 500. ! 

 Units: km 

 Maximum Number of stations to include 

 in temperature interpolation (NUMTS) Default: 5 ! NUMTS = 5 ! 

 Conduct spatial averaging of temp- 

 eratures (IAVET) (0=no, 1=yes) Default: 1 ! IAVET = 1 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 (will use mixing ht MNMDAV,HAFANG 

 so make sure they are correct) 

 Default temperature gradient Default: -.0098 ! TGDEFB = -0.0098 ! 

 below the mixing height over 

 water (K/m) (TGDEFB) 

 Default temperature gradient Default: -.0045 ! TGDEFA = -0.0045 ! 

 above the mixing height over 

 water (K/m) (TGDEFA) 

 Beginning (JWAT1) and ending (JWAT2) 

 land use categories for temperature ! JWAT1 = 55 ! 

 interpolation over water -- Make ! JWAT2 = 55 ! 

 bigger than largest land use to disable 

 PRECIP INTERPOLATION PARAMETERS 

 Method of interpolation (NFLAGP) Default = 2 ! NFLAGP = 2 ! 

 (1=1/R,2=1/R**2,3=EXP/R**2) 

 Radius of Influence (km) (SIGMAP) Default = 100.0 ! SIGMAP = 100. ! 

 (0.0 => use half dist. btwn 

 nearest stns w & w/out 

 precip when NFLAGP = 3) 

 Minimum Precip. Rate Cutoff (mm/hr) Default = 0.01 ! CUTP = 0.01 ! 

 (values < CUTP = 0.0 mm/hr) 

!END! 

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

INPUT GROUP: 7 -- Surface meteorological station parameters 

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

 SURFACE STATION VARIABLES 

 (One record per station -- 0 records in all) 

 1 2 

 Name ID X coord. Y coord. Time Anem. 

 (km) (km) zone Ht.(m) 

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

! SS1 ='MILW' 26400 739.061 363.200 6 10 ! 

! SS2 ='MADI' 26410 619.927 372.210 6 10 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

! SS3 ='LA C' 26430 461.012 442.705 6 10 ! 

! SS4 ='EAU ' 26435 435.857 552.352 6 10 ! 

! SS5 ='GREE' 26450 703.911 530.179 6 10 ! 

! SS6 ='MANI' 26455 743.477 495.113 6 10 ! 

! SS7 ='STUR' 26458 755.730 576.760 6 10 ! 

! SS8 ='WAUS' 26463 581.202 568.247 6 10 ! 

! SS9 ='MOSI' 26465 579.307 552.489 6 10 ! 

! SS10 ='CLIN' 26502 655.019 541.168 6 10 ! 

! SS11 ='WISC' 26503 582.532 412.498 6 10 ! 

! SS12 ='EAGL' 26504 599.980 682.545 6 10 ! 

! SS13 ='MINE' 26507 550.817 338.941 6 10 ! 

! SS14 ='HAYW' 26508 430.347 681.295 6 10 ! 

! SS15 ='JUNE' 26509 669.429 409.931 6 10 ! 

! SS16 ='dulu' 27450 366.011 766.977 6 10 ! 

! SS17 ='MANI' 25408 838.315 711.433 5 10 ! 

! SS18 ='SAWY' 26284 741.237 743.078 5 10 ! 

! SS19 ='HOUG' 26380 977.905 549.977 5 10 ! 

! SS20 ='ESCA' 26480 775.417 679.550 5 10 ! 

! SS21 ='IRNM' 27437 690.168 678.511 5 10 ! 

! SS22 ='IRNW' 27445 528.314 743.857 5 10 ! 

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Five digit integer for station ID 

!END! 

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

INPUT GROUP: 8 -- Upper air meteorological station parameters 

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

 UPPER AIR STATION VARIABLES 

 (One record per station -- 0 records in all) 

 1 2 

 Name ID X coord. Y coord. Time zone 

 (km) (km) 

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

! US1 ='GREE' 14898 703.911 539.179 6 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

! US2 ='MNNP' 94983 272.681 539.843 6 ! 

! US3 ='INTF' 14918 269.489 957.416 6 ! 

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Five digit integer for station ID 

!END! 

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

INPUT GROUP: 9 -- Precipitation station parameters 

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

 PRECIPITATION STATION VARIABLES 

 (One record per station -- 0 records in all) 

 (NOT INCLUDED IF NPSTA = 0) 

 1 2 

 Name Station X coord. Y coord. 

 Code (km) (km) 

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

! PS1 ='COPP' 201780 719.681 845.179 ! 

! PS2 ='ESCA' 202626 779.850 646.454 ! 

! PS3 ='HOUG' 203936 1001.500 536.427 ! 

! PS4 ='IRON' 204090 699.421 640.283 ! 

! PS5 ='MANI' 205073 845.933 667.499 ! 

! PS6 ='SAUL' 207366 985.172 765.448 ! 

! PS7 ='CLIN' 471667 696.889 290.151 ! 

! PS8 ='GREE' 473269 709.933 509.579 ! 

! PS9 ='HAYW' 473511 442.947 678.728 ! 

! PS10 ='LAC ' 474370 471.515 404.495 ! 

! PS11 ='MADI' 474961 631.719 367.656 ! 

! PS12 ='MARS' 475120 550.348 505.662 ! 

! PS13 ='MENO' 475335 431.807 514.277 ! 

! PS14 ='MILW' 475479 772.567 324.344 ! 

! PS15 ='RAIN' 476939 599.369 634.460 ! 

! PS16 ='STURG' 478267 776.964 542.174 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Six digit station code composed of state 

 code (first 2 digits) and station ID (last 

 4 digits) 

!END!

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

Appendix B – Example CALPUFF Input File 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

Example BART Modeling 

2010 Updated BART Modeling - for PCA, WI. 

Using Refined 4km CALMET Data File and SENE, ISLE, BOWA Class I Receptors 

---------------- 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 =PCARef02.lst ! 

CONC.DAT output ! CONDAT =PCARef02.dat ! 

DFLX.DAT output * DFDAT = * 

WFLX.DAT output * WFDAT = * 

VISB.DAT output * VISDAT =PCA02DNR.VIB * 

RESTARTE.DAT output * RSTARTE= * 

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

Emission Files 

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

PTEMARB.DAT input * PTDAT = * 

VOLEMARB.DAT input * VOLDAT = * 

BAEMARB.DAT input * ARDAT = * 

LNEMARB.DAT input * LNDAT = * 

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

Other Files 

----------- 

OZONE.DAT input * OZDAT = * 

VD.DAT input * VDDAT = * 

CHEM.DAT input * CHEMDAT= * 

H2O2.DAT input * H2O2DAT= * 

HILL.DAT input * HILDAT= * 

HILLRCT.DAT input * RCTDAT= * 

COASTLN.DAT input * CSTDAT= * 

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 = T 

Otherwise, 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 length 

Provision for multiple input files 

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

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 Number of CALMET.DAT files for run (NMETDAT) 

 Default: 1 ! NMETDAT = 364 ! 

 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=e:\WI-Calmet\2002output\cal020102.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020103.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020104.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020105.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020106.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020107.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020108.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020109.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020110.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020111.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020112.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020113.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020114.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020115.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020116.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020117.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020118.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020119.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020120.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020121.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020122.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020123.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020124.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020125.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020126.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020127.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020128.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020129.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020130.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020131.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020201.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020202.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020203.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020204.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020205.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020206.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020207.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020208.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020209.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020210.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020211.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020212.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020213.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020214.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020215.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020216.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020217.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020218.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020219.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020220.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020221.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020222.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020223.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020224.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020225.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020226.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020227.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020228.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020301.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020302.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020303.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020304.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020305.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020306.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020307.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020308.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020309.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020310.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020311.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020312.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020313.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020314.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020315.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020316.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020317.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020318.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020319.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020320.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020321.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020322.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020323.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020324.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020325.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020326.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020327.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020328.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020329.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020330.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020331.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020401.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020402.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020403.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020404.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020405.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020406.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020407.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020408.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020409.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020410.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020411.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020412.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020413.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020414.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020415.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020416.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020417.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020418.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020419.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020420.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020421.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020422.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020423.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020424.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020425.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020426.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020427.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020428.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020429.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020430.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020501.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020502.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020503.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020504.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020505.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020506.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020507.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020508.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020509.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020510.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020511.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020512.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020513.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020514.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020515.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020516.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020517.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020518.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020519.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020520.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020521.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020522.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020523.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020524.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020525.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020526.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020527.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020528.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020529.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020530.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020531.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020601.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020602.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020603.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020604.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020605.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020606.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020607.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020608.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020609.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020610.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020611.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020612.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020613.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020614.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020615.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020616.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020617.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020618.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020619.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020620.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020621.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020622.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020623.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020624.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020625.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020626.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020627.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020628.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020629.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020630.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020701.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020702.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020703.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020704.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020705.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020706.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020707.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020708.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020709.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020710.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020711.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020712.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020713.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020714.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020715.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020716.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020717.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020718.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020719.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020720.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020721.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020722.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020723.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020724.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020725.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020726.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020727.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020728.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020729.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020730.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020731.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020801.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020802.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020803.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020804.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020805.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020806.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020807.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020808.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020809.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020810.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020811.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020812.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020813.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020814.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020815.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020816.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020817.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020818.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020819.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020820.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020821.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020822.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020823.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020824.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020825.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020826.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020827.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020828.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020829.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020830.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020831.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020901.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020902.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020903.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020904.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020905.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020906.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020907.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020908.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020909.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020910.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020911.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020912.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020913.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020914.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020915.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020916.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020917.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020918.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020919.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020920.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020921.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020922.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020923.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020924.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020925.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020926.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020927.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020928.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020929.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020930.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021001.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021002.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021003.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021004.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021005.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021006.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021007.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021008.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021009.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021010.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021011.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021012.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021013.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021014.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021015.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021016.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021017.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021018.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021019.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021020.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021021.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021022.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021023.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021024.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021025.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021026.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021027.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021028.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021029.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021030.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal021031.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021101.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021102.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021103.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021104.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021105.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021106.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021107.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021108.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021109.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021110.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021111.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021112.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021113.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021114.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021115.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021116.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021117.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021118.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021119.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021120.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021121.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021122.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021123.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021124.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021125.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021126.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021127.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021128.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021129.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021130.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021201.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021202.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021203.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021204.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021205.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021206.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021207.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021208.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021209.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021210.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021211.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021212.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021213.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021214.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021215.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021216.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021217.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021218.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021219.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021220.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021221.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021222.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021223.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021224.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021225.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021226.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021227.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021228.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021229.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021230.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021231.DAT ! !END! 

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

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

INPUT GROUP: 1 -- General run control parameters 

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

 Option to run all periods found 

 in the met. file (METRUN) Default: 0 ! METRUN = 0 ! 

 METRUN = 0 - Run period explicitly defined below 

 METRUN = 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 = 02 ! 

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

 Base time zone (XBTZ) -- No default ! XBTZ = 6.0 ! 

 PST = 8., MST = 7. 

 CST = 6., EST = 5. 

 Length of run (hours) (IRLG) -- No default ! IRLG = 8784 ! 

 Number of chemical species (NSPEC) 

 Default: 5 ! NSPEC = 9 ! 

 Number of chemical species 

 to be emitted (NSE) Default: 3 ! NSE = 7 ! 

 Flag to stop run after 

 SETUP phase (ITEST) Default: 2 ! ITEST = 2 ! 

 (Used to allow checking 

 of the model inputs, files, etc.) 

 ITEST = 1 - STOPS program after SETUP phase 

 ITEST = 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 file 

 1 = Read a restart file at the beginning of 

 the run 

 2 = Write a restart file during run 

 3 = Read a restart file at beginning of run 

 and write a restart file during run 

 Number of periods in Restart 

 output 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) 

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

 Averaging Time (minutes) (AVET) 

 Default: 60.0 ! AVET = 60. ! 

 PG Averaging Time (minutes) (PGTIME) 

 Default: 60.0 ! PGTIME = 60. ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

!END! 

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

INPUT GROUP: 2 -- Technical options 

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

 Vertical distribution used in the 

 near field (MGAUSS) Default: 1 ! MGAUSS = 1 ! 

 0 = uniform 

 1 = Gaussian 

 Terrain adjustment method 

 (MCTADJ) Default: 3 ! MCTADJ = 3 ! 

 0 = no adjustment 

 1 = ISC-type of terrain adjustment 

 2 = simple, CALPUFF-type of terrain 

 adjustment 

 3 = partial plume path adjustment 

 Subgrid-scale complex terrain 

 flag (MCTSG) Default: 0 ! MCTSG = 0 ! 

 0 = not modeled 

 1 = modeled 

 Near-field puffs modeled as 

 elongated 0 (MSLUG) Default: 0 ! MSLUG = 0 ! 

 0 = no 

 1 = 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 building 

 downwash? (MBDW) Default: 1 ! MBDW = 1 ! 

 1 = ISC method 

 2 = PRIME method 

 Vertical wind shear modeled above 

 stack 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 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 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 = no 

 1 = yes 

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

 0 = no 

 1 = yes 

 (dry deposition method specified 

 for each species in Input Group 3) 

 Method used to compute dispersion 

 coefficients (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 in 

 urban 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 

 MDISP = 3, described above. MDISP = 5 assumes that 

 measured values are read 

 Sigma-v/sigma-theta, sigma-w measurements used? (MTURBVW) 

 (Used only if MDISP = 1 or 5) Default: 3 ! MTURBVW = 3 ! 

 1 = use sigma-v or sigma-theta measurements 

 from PROFILE.DAT to compute sigma-y 

 (valid for METFM = 1, 2, 3, 4) 

 2 = use sigma-w measurements 

 from PROFILE.DAT to compute sigma-z 

 (valid for METFM = 1, 2, 3, 4) 

 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) 

 4 = use sigma-theta measurements 

 from PLMMET.DAT to compute sigma-y 

 (valid only if METFM = 3) 

 Back-up method used to compute dispersion 

 when measured turbulence data are 

 missing (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 in 

 urban areas 

 4 = same as 3 except PG coefficients computed using 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 the MESOPUFF II eqns. 

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

 (MROUGH) 

 0 = no 

 1 = yes 

 Partial plume penetration of Default: 1 ! MPARTL = 1 ! 

 elevated inversion? 

 (MPARTL) 

 0 = no 

 1 = 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 = no 

 1 = yes 

 Sub-Grid TIBL module used for shore line? 

 Default: 0 ! MSGTIBL = 0 ! 

 (MSGTIBL) 

 0 = no 

 1 = yes 

 Boundary conditions (concentration) modeled? 

 Default: 0 ! MBCON = 0 ! 

 (MBCON) 

 0 = no 

 1 = yes, using formatted BCON.DAT file 

 2 = yes, using unformatted CONC.DAT file 

 Analyses of fogging and icing impacts due to emissions from 

 arrays of mechanically-forced cooling towers can be performed 

 using CALPUFF in conjunction with a cooling tower emissions 

 processor (CTEMISS) and its associated postprocessors. Hourly 

 emissions of water vapor and temperature from each cooling tower 

 cell are computed for the current cell configuration and ambient 

 conditions by CTEMISS. CALPUFF models the dispersion of these 

 emissions and provides cloud information in a specialized format 

 for 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 = no 

 1 = yes - report results in PLUME Mode format 

 2 = yes - report results in RECEPTOR Mode format 

 TEST options specified to see if 

 they conform to regulatory 

 values? (MREG) Default: 1 ! MREG = 0 ! 

 0 = NO checks are made 

 1 = Technical options must conform to USEPA 

 Long Range Transport (LRT) guidance 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 METFM 1 or 2 

 AVET 60. (min) 

 PGTIME 60. (min) 

 MGAUSS 1 

 MCTADJ 3 

 MTRANS 1 

 MTIP 1 

 MCHEM 1 or 3 (if modeling SOx, NOx) 

 MWET 1 

 MDRY 1 

 MDISP 2 or 3 

 MPDF 0 if MDISP=3 

 1 if MDISP=2 

 MROUGH 0 

 MPARTL 1 

 SYTDEP 550. (m) 

 MHFTSZ 0 

!END! 

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

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

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

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

Subgroup (3a) 

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

 The following species are modeled: 

 The following species are modeled: 

! CSPEC = SO2 ! !END! 

! CSPEC = SO4 ! !END! 

! CSPEC = NOX ! !END! 

! CSPEC = HNO3 ! !END! 

! CSPEC = NO3 ! !END! 

! CSPEC = PMC ! !END! 

! CSPEC = PMF ! !END! 

! CSPEC = EC ! !END! 

! CSPEC = SOA ! !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 ! 

! PMC = 1, 1, 2, 0 ! 

! PMF = 1, 1, 2, 0 ! 

! EC = 1, 1, 2, 0 ! 

! SOA = 1, 1, 2, 0 ! 

!END! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

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

Subgroup (3b) 

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

 The following names are used for Species-Groups in which results 

 for certain species are combined (added) prior to output. The 

 CGRUP name will be used as the species name in output files. 

 Use this feature to model specific particle-size distributions 

 by 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 Mercator 

 TTM : Tangential Transverse Mercator 

 LCC : Lambert Conformal Conic 

 PS : Polar Stereographic 

 EM : 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 

 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 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 (XLAT2) No Default ! XLAT2 = 45N ! 

 LCC : Projection cone slices through Earth's surface at XLAT1 and XLAT2 

 PS : 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, and 

 east or west longitude. For example, 

 35.9 N Latitude = 35.9N 

 118.7 E Longitude = 118.7E 

 Datum-region 

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

 The Datum-Region for the coordinates is identified by a character 

 string. Many mapping products currently available use the model of the 

 Earth known as the World Geodetic System 1984 (WGS-84). Other local 

 models may be in use, and their selection in CALMET will make its output 

 consistent with local mapping products. The list of Datum-Regions with 

 official transformation parameters is provided by the National Imagery and 

 Mapping 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, Sphere 

 ESR-S ESRI REFERENCE 6371KM Radius, Sphere 

 Datum-region for output coordinates 

 (DATUM) Default: WGS-84 ! DATUM = NAS-C ! 

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 = 162 ! 

 No. Y grid cells (NY) No default ! NY = 191 ! 

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

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

 Units: km 

 Cell face heights in arbitrary 

 vertical grid (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 = 247. ! 

 Y coordinate (YORIGKM) No default ! YORIGKM = 240. ! 

 Units: km 

COMPUTATIONAL Grid: 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 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 the 

 computational 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 = 1 ! 

 (1 <= IBCOMP <= NX) 

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

 (1 <= JBCOMP <= NY) 

 X index of UR corner (IECOMP) No default ! IECOMP = 162 ! 

 (1 <= IECOMP <= NX) 

 Y index of UR corner (JECOMP) No default ! JECOMP = 191 ! 

 (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 the 

 sampling grid is at grid point (IESAMP, JESAMP) of the MET. grid. 

 The sampling grid must be identical to or a subset of the computational 

 grid. It may be a nested grid inside the computational grid. 

 The grid spacing of the sampling grid is DGRIDKM/MESHDN. 

 Logical flag indicating if gridded 

 receptors 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 = 162 ! 

 (IBCOMP <= IESAMP <= IECOMP) 

 Y index of UR corner (JESAMP) No default ! JESAMP = 191 ! 

 (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 

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

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 Concentrations (ICON) 1 ! ICON = 1 ! 

 Dry Fluxes (IDRY) 1 ! IDRY = 0 ! 

 Wet Fluxes (IWET) 1 ! IWET = 0 ! 

 Relative Humidity (IVIS) 1 ! IVIS = 0 ! 

 (relative humidity file is 

 required for visibility 

 analysis) 

 Use data compression option in output file? 

 (LCOMPRS) Default: T ! LCOMPRS = T ! 

 * 

 0 = Do not create file, 1 = create file 

 DIAGNOSTIC MASS FLUX OUTPUT OPTIONS: 

 Mass flux across specified boundaries 

 for selected species reported hourly? 

 (IMFLX) Default: 0 ! IMFLX = 0 ! 

 0 = no 

 1 = yes (FLUXBDY.DAT and MASSFLX.DAT filenames 

 are specified in Input Group 0) 

 Mass balance for each species 

 reported hourly? 

 (IMBAL) Default: 0 ! IMBAL = 0 ! 

 0 = no 

 1 = 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/s 

 2 = mg/m**3 mg/m**2/s 

 3 = ug/m**3 ug/m**2/s 

 4 = ng/m**3 ng/m**2/s 

 5 = Odour Units 

 Messages tracking progress of run 

 written to the screen ? 

 (IMESG) Default: 2 ! IMESG = 2 ! 

 0 = no 

 1 = yes (advection step, puff ID) 

 2 = yes (YYYYJJJHH, # old puffs, # emitted puffs) 

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

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

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

-- MASS FLUX -- 

 SPECIES 

 /GROUP PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? 

SAVED ON DISK? 

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

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

! SO2 = 0, 1, 0, 0, 0, 0, 

0 ! 

! SO4 = 0, 1, 0, 0, 0, 0, 

0 ! 

! NOX = 0, 1, 0, 0, 0, 0, 

0 ! 

! HNO3 = 0, 1, 0, 0, 0, 0, 

0 ! 

! NO3 = 0, 1, 0, 0, 0, 0, 

0 ! 

! PMC = 0, 1, 0, 0, 0, 0, 

0 ! 

! PMF = 0, 1, 0, 0, 0, 0, 

0 ! 

! EC = 0, 1, 0, 0, 0, 0, 

0 ! 

! SOA = 0, 1, 0, 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 = 1 ! 

 Met. period to start output 

 (NN1) Default: 1 ! NN1 = 1 ! 

 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 terrain 

 receptors (NCTREC) Default: 0 ! NCTREC = 0 ! 

 Terrain and CTSG Receptor data for 

 CTSG hills input in CTDM format ? 

 (MHILL) No Default ! MHILL = 2 ! 

 1 = Hill and Receptor data created 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 by CTDM processors & read from 

 HILL.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 = 1. ! 

 to meters (MHILL=1) 

 Factor to convert vertical dimensions Default: 1.0 ! ZHILL2M = 1. ! 

 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 SCALE 2 

AMAX1 AMAX2 

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

 XC, YC = Coordinates of center of hill 

 THETAH = 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 elevation 

 EXPO 1 = Hill-shape exponent for the major axis 

 EXPO 2 = Hill-shape exponent for the major axis 

 SCALE 1 = Horizontal length scale along the major axis 

 SCALE 2 = Horizontal length scale along the minor axis 

 AMAX = Maximum allowed axis length for the major axis 

 BMAX = Maximum allowed axis length for the major axis 

 XRCT, YRCT = Coordinates of the complex terrain receptors 

 ZRCT = Height of the ground (MSL) at the complex terrain 

 Receptor 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 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 HENRY'S 

LAW COEFFICIENT 

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

(dimensionless) 

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

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

! SO2 = 0.1509, 1000., 8., 0., 

0.04 ! 

! NOX = 0.1656, 1., 8., 5., 

3.5 ! 

! HNO3 = 0.1628, 1., 18., 0., 

0.00000008 ! 

!END! 

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

INPUT GROUP: 8 -- Size parameters for dry deposition of particles 

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

 For SINGLE SPECIES, the mean and standard deviation are used to 

 compute 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 explicitly 

 specified (by the 'species' in the group), and the standard deviation 

 for each should be entered as 0. The model will then use the 

 deposition 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. ! 

! PMC = 2.0, 2.0 ! 

! PMF = 0.48, 2. ! 

! EC = 0.48, 2. ! 

! SOA = 0.48, 2. ! 

!END! 

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

INPUT GROUP: 9 -- Miscellaneous dry deposition parameters 

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

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

!END! 

 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 to 

 evaluate 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 vegetation 

 IVEG=2 for active and stressed vegetation 

 IVEG=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 ! 

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

INPUT GROUP: 11 -- Chemistry Parameters 

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

 Ozone data input option (MOZ) Default: 1 ! MOZ = 0 ! 

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

 0 = use a monthly background ozone value 

 1 = 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 = 31.00, 31.00, 31.00, 37.00, 37.00, 37.00, 33.00, 33.00, 33.00, 27.00, 27.00, 27.00 

! 

 Monthly ammonia concentrations 

 (Used only if MCHEM = 1, or 3) 

 (BCKNH3) in ppb Default: 12*10. 

 ! BCKNH3 = 12*3.9 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 * BCKNH3 = 00.30, 00.30, 00.30, 00.50, 00.50, 00.50, 00.50, 00.50, 00.50, 00.50, 00.50, 

00.50 * 

 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 value 

 1 = 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 * 

 ! BCKH2O2 = 0.50, 0.50, 0.50, 2.30, 2.30, 2.30, 3.50, 3.50, 3.50, 0.80, 0.80, 0.80 ! 

 --- 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 computing 

 the 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 .15 

 VCNX 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 .5 

 OFRAC .25 .25 .30 .30 .30 .30 .30 .30 .30 .30 .30 .25 

 VCNX 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 .20 

 VCNX 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 .25 

 VCNX 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 .20 

 VCNX 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 15. 

 Urban - no controls present 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 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 .30 

 VCNX 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, 50.00, 

50.00 ! 

!END! 

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

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

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

 Horizontal size of puff (m) beyond which 

 time-dependent dispersion equations (Heffter) 

 are used to determine sigma-y and 

 sigma-z (SYTDEP) Default: 550. ! SYTDEP = 5.5E02 ! 

 Switch for using Heffter equation for sigma z 

 as above (0 = Not use Heffter; 1 = use Heffter 

 (MHFTSZ) Default: 0 ! MHFTSZ = 0 ! 

 Stability class used to determine plume 

 growth rates for puffs above the boundary 

 layer (JSUP) Default: 5 ! JSUP = 5 ! 

 Vertical dispersion constant for stable 

 conditions (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 from 

 Schulman-Scire to Huber-Snyder Building Downwash 

 scheme (SS used for Hs < Hb + TBD * HL) 

 (TBD) Default: 0.5 ! TBD = .5 ! 

 TBD < 0 ==> always use Huber-Snyder 

 TBD = 1.5 ==> always use Schulman-Scire 

 TBD = 0.5 ==> ISC Transition-point 

 Range of land use categories for which 

 urban 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) 

 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 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 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 or MTURBVW = 1 or 3) 

 (ISIGMAV) Default: 1 ! ISIGMAV = 1 ! 

 0 = read sigma-theta 

 1 = read sigma-v 

 Choice of mixing heights (Used only if METFM = 4) 

 (IMIXCTDM) Default: 0 ! IMIXCTDM = 0 ! 

 0 = read PREDICTED mixing heights 

 1 = 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 (in 

 grid units) during one sampling step 

 (XSAMLEN) Default: 1.0 ! XSAMLEN = 1.0 ! 

 Maximum Number of slugs/puffs release from 

 one source during one time step 

 (MXNEW) Default: 99 ! MXNEW = 99 ! 

 Maximum Number of sampling steps for 

 one puff/slug during one time step 

 (MXSAM) Default: 99 ! MXSAM = 99 ! 

 Number of iterations used when computing 

 the transport wind for a sampling step 

 that includes gradual rise (for CALMET 

 and 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 for each 

 stability class (m/s) 

 (SVMIN(6) and SWMIN(6)) Default SVMIN : .50, .50, .50, .50, .50, .50 

 Default SWMIN : .20, .12, .08, .06, .03, .016 

 Stability Class : A B C D E F 

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

 ! SVMIN = 0.500, 0.500, 0.500, 0.500, 0.500, 0.500! 

 ! SWMIN = 0.200, 0.120, 0.080, 0.060, 0.030, 0.016! 

 Divergence criterion for dw/dz across puff 

 used to initiate adjustment for horizontal 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 convergence (1/s) 

 Partial adjustment starts at CDIV(1), and 

 full adjustment is reached at CDIV(2) 

 (CDIV(2)) Default: 0.0,0.0 ! CDIV = .0, .0 ! 

 Minimum wind speed (m/s) allowed for 

 non-calm conditions. Also used as minimum 

 speed returned when using power-law 

 extrapolation 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-law 

 exponents for stabilities 1-6 

 (PLX0(6)) Default : ISC RURAL values 

 ISC RURAL : .07, .07, .10, .15, .35, .55 

 ISC 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 gradient 

 for stable classes E, F (degK/m) 

 (PTG0(2)) Default: 0.020, 0.035 

 ! PTG0 = 0.020, 0.035 ! 

 Default plume path coefficients for 

 each stability class (used when option 

 for partial plume height terrain adjustment 

 is 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 factor 

 equal to sigma-y/length of slug 

 (SL2PF) Default: 10. ! SL2PF = 10.0 ! 

 Puff-splitting control variables ------------------------ 

 VERTICAL SPLIT 

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

 Number of puffs that result every time a puff 

 is split - nsplit=2 means that 1 puff splits 

 into 2 

 (NSPLIT) Default: 3 ! NSPLIT = 3 ! 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 Time(s) of a day when split puffs are eligible to 

 be split once again; this is typically set once 

 per 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 mixing 

 height (m) exceeds a minimum value 

 (ZISPLIT) Default: 100. ! ZISPLIT = 100.0 ! 

 Split is allowed only if ratio of last hour's 

 mixing ht to the maximum mixing ht experienced 

 by the puff is less than a maximum value (this 

 postpones a split until a nocturnal layer develops) 

 (ROLDMAX) Default: 0.25 ! ROLDMAX = 0.25 ! 

 HORIZONTAL SPLIT 

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

 Number of puffs that result every time a puff 

 is split - nsplith=5 means that 1 puff splits 

 into 5 

 (NSPLITH) Default: 5 ! NSPLITH = 5 ! 

 Minimum sigma-y (Grid Cells Units) of puff 

 before it may be split 

 (SYSPLITH) Default: 1.0 ! SYSPLITH = 1.0 ! 

 Minimum puff elongation rate (SYSPLITH/hr) due to 

 wind shear, before it may be split 

 (SHSPLITH) Default: 2. ! SHSPLITH = 2.0 ! 

 Minimum concentration (g/m^3) of each 

 species in puff before it may be split 

 Enter array of NSPEC values; if a single value is 

 entered, it will be used for ALL species 

 (CNSPLITH) Default: 1.0E-07 ! CNSPLITH = 1.0E-07 ! 

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

 Fractional convergence criterion for numerical SLUG 

 sampling integration 

 (EPSSLUG) Default: 1.0e-04 ! EPSSLUG = 1.0E-04 ! 

 Fractional convergence criterion for numerical AREA 

 source integration 

 (EPSAREA) Default: 1.0e-06 ! EPSAREA = 1.0E-06 ! 

 Trajectory step-length (m) used for numerical rise 

 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 height 

 at the release point if greater than this minimum. 

 (HTMINBC) Default: 500. ! HTMINBC = 500.0 ! 

 Search radius (in BC segment lengths) about a receptor for sampling 

 nearest BC puff. BC puffs are emitted with a spacing of one segment 

 length, so the search radius should be greater than 1. 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 (RSAMPBC) Default: 4. ! RSAMPBC = 10.0 ! 

 Near-Surface depletion adjustment to concentration profile used when 

 sampling BC puffs? 

 (MDEPBC) Default: 1 ! MDEPBC = 1 ! 

 0 = Concentration is NOT adjusted for depletion 

 1 = Adjust Concentration for depletion 

!END! 

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

INPUT GROUPS: 13a, 13b, 13c, 13d -- Point source parameters 

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

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

Subgroup (13a) 

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

 Number of point sources with 

 parameters provided below (NPT1) No default ! NPT1 = 1 ! 

 Units used for point source 

 emissions below (IPTU) Default: 1 ! IPTU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (13d) (NSPT1) Default: 0 ! NSPT1 = 0 ! 

 Number of point sources with 

 variable emission parameters 

 provided in external file (NPT2) No default ! NPT2 = 0 ! 

 (If NPT2 > 0, these point 

 source emissions are read from 

 the file: PTEMARB.DAT) 

!END! 

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

Subgroup (13b) 

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

 The following species are modeled: 

CSPEC = SO2 

CSPEC = SO4 

CSPEC = NOX 

CSPEC = HNO3 

CSPEC = NO3 

CSPEC = PMC 

CSPEC = PMF 

CSPEC = EC 

CSPEC = SOA 

 a 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 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 = P1 ! 

 1 ! X = 568.01, 625.9200, 60.700,360.00, 3.230, 17.0, 468.0, .0, 

 166.3E00, 2.17E00, 13.4E00, 0.0E00, 0.0E00, 0.47, 0.98, 0.04, 0.54 ! 

 1 ! FMFAC = 1.0 ! !END! 

 

-------- 

 a 

 Data for each source are treated as a separate input subgroup 

 and 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.) 

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

 the effect of rain-caps or other physical configurations that 

 reduce momentum rise associated with the actual exit velocity. 

 (Default: 1.0 -- full momentum used) 

 b 

 0. = No building downwash modeled, 1. = downwash modeled 

 NOTE: 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 are 

 modeled, 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 

 MBDW=2 (PRIME downwash option) 

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

-------- 

 a 

 Building height, width, length, and X/Y offset from the source are treated 

 as a separate input subgroup for each source and therefore must end with 

 an input group terminator. The X/Y offset is the position, relative to the 

 stack, of the center of the upwind face of the projected building, with the 

 x-axis pointing along the flow direction. 

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

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

Subgroup (13d) 

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

 a 

 POINT SOURCE: VARIABLE EMISSIONS DATA 

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

 Use this subgroup to describe temporal variations in the emission 

 rates given in 13b. Factors entered multiply the rates in 13b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use PTEMARB.DAT and NPT2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (14a) 

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

 Number of polygon area sources with 

 parameters specified below (NAR1) No default ! NAR1 = 0 ! 

 Units used for area source 

 emissions below (IARU) Default: 1 ! IARU = 1 ! 

 1 = g/m**2/s 

 2 = kg/m**2/hr 

 3 = lb/m**2/hr 

 4 = tons/m**2/yr 

 5 = Odour Unit * m/s (vol. flux/m**2 of odour compound) 

 6 = Odour Unit * m/min 

 7 = metric tons/m**2/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (14d) (NSAR1) Default: 0 ! NSAR1 = 0 ! 

 Number of buoyant polygon area sources 

 with variable location and emission 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 parameters (NAR2) No default ! NAR2 = 0 ! 

 (If NAR2 > 0, ALL parameter data for 

 these 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 subgroup 

 and 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 are 

 modeled, 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 subgroup 

 and 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 emission 

 rates given in 14b. Factors entered multiply the rates in 14b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use BAEMARB.DAT and NAR2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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) 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

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

 first group is Stability Class A, 

 and the speed classes have upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (15a) 

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

 Number of buoyant line sources 

 with variable location and emission 

 parameters (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 source 

 emissions below (ILNU) Default: 1 ! ILNU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (15c) (NSLN1) Default: 0 ! NSLN1 = 0 ! 

 Maximum number of segments used to model 

 each line (MXNSEG) Default: 7 ! MXNSEG = 7 ! 

 The following variables are required only if NLINES > 0. They are 

 used in the buoyant line source plume rise calculations. 

 Number of distances at which Default: 6 ! NLRISE = 6 ! 

 transitional rise is computed 

 Average building length (XL) No default ! XL = .0 ! 

 (in meters) 

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

 (in meters) 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 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 

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

 a 

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 subgroup 

 and 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 are 

 modeled, 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 emission 

 rates 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 

 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 upper 

 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+) 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

-------- 

 a 

 Data for each species are treated as a separate input subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (16a) 

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

 Number of volume sources with 

 parameters provided in 16b,c (NVL1) No default ! NVL1 = 0 ! 

 Units used for volume source 

 emissions below in 16b (IVLU) Default: 1 ! IVLU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (16c) (NSVL1) Default: 0 ! NSVL1 = 0 ! 

 Number of volume sources with 

 variable location and emission 

 parameters (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 subgroup 

 and therefore must end with an input group terminator. 

 b 

 An emission rate must be entered for every pollutant modeled. 

December 2010 
 Refined BART Modeling Protocol for 

 PCA Tomahawk Mill

 Enter emission rate of zero for secondary pollutants that are 

 modeled, 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 emission 

 rates given in 16b. Factors entered multiply the rates in 16b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use VOLEMARB.DAT and NVL2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and 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 = 1995 ! 

!END! 

Note - three Class I areas 

Seney SENE = 173 receptors 

Isle Royal ISLE = 966 receptors 

Boundary Waters BOWA = 856 receptors 

total number of receptors is 1995 

ALL RECEPTOR COORDINATES FOLLOW IN INPUT FILE 

December 2010 
Updated CALPUFF Modeling 

Protocol and Final Report for the 

Subject to BART Analyses 

for Thilmany Kaukauna Mill 

Prepared by 

RTP Environmental Associates Inc. 

2031 Broadway, Suite 2 

Boulder, Colorado 80302 

December 2010 
Updated CALPUFF Modeling Protocol and Final Report for 

Thilmany “Subject to BART” Analysis 

TABLE OF CONTENTS 

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

2.0 VISTAS BART Protocol ........................................................................................................ 5 

3.0 CALMET Data and Procedures.............................................................................................. 7 

4.0 CALPUFF Procedures.......................................................................................................... 12 

5.0 POSTUTIL and CALPOST Procedures ............................................................................... 13 

6.0 Emissions Modeled............................................................................................................... 14 

7.0 Modeling Results.................................................................................................................. 15 

List of Figures

Figure 1 - WDNR Screening CALPUFF Domain .......................................................................... 2 

Figure 2 – Refined CALPUFF Modeling Domain and Locations of Class I Areas....................... 9 

Figure 3 – Locations of Observational Stations in Refined CALPUFF Modeling Domain......... 10 

Figure 4 – Land Use Data for Refined CALPUFF Modeling Domain......................................... 11 

List of Tables

Table 1 – Thilmany Speciated PM Emissions.............................................................................. 14 

Table 2 – Thilmany CALPUFF BART Exemption Results Summary......................................... 16 

Appendix A – Example CALMET Input File 

Appendix B – Example CALPUFF Input File 

 i 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

1 December 2010 

1.0 Introduction 

The Wisconsin Department of Natural Resources (DNR) performed single source screening 

modeling in 2006 to evaluate which Best Available Retrofit Technology (BART) eligible sources 

in the state may “cause or contribute” to visibility impairment and could therefore be subject to 

BART requirements. This type of analysis is referred to as the “subject to BART” or “BART 

exemption” analysis. The methods used by DNR are described in the “Single Source Modeling to 

Support Regional Haze BART Modeling Protocol”, March 21, 2006, prepared by Lake Michigan

Air Directors Consortium (LADCO). 

DNR applied CALPUFF to each BART eligible source for three annual periods, covering the 

calendar years 2002 to 2004. The CALPUFF/CALMET modeling domain consisted of ninetyseven 36-km spaced cells in the east-west direction and ninety 36-km spaced cells in the northsouth direction (see Figure 1). Meteorological data generated by the MM5 prognostic weather 

model (provided by LADCO in CALMM5 format) was used to develop the meteorological data 

for CALPUFF, without additional observational data input (i.e., NOOBS mode). This represents 

a coarse meteorological grid, suitable for an initial screening analysis. 

The results from DNR’s screening analysis indicated that, with the exception of some of the 

largest electric power stations in the state, the only Class I areas where BART eligible sources 

may contribute to visibility impairment are the three areas to the north of Wisconsin, the 

Boundary Waters Canoe Area, Isle Royal National Park, and Seney Wildlife Area. DNR’s 

screening analysis also indicated that the BART eligible emissions unit at the Thilmany 

Kaukauna Mill (Thilmany) may “cause or contribute” to visibility impairment at the Seney Class

I area (located approximately 280 km to the northeast of the mill), as defined by the 98th

percentile visibility impacts being greater than 0.5 deciviews (dv) relative to natural background. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

2 December 2010 

Figure 1 - WDNR Screening CALPUFF Domain 

NOTE: Class I areas are identified by red marks. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

3 December 2010 

Thilmany has elected to refine the DNR screening analysis by conducting refined CALPUFF 

modeling with a 4 km meteorological grid, based on procedures described in the “Visibility 

Improvement – State and Tribal Association of the Southeast (VISTAS) BART CALPUFF” 

modeling protocol. The VISTAS protocol was developed by a large group of stakeholders, 

including EPA, the VISTAS member state agencies and tribes, the Federal Land Managers 

(FLMs), industry representatives, and consulting experts. Given the resources expended on the 

VISTAS protocol, it arguably represents the most comprehensive CALPUFF BART protocol ever 

developed. 

Thilmany had discussions with DNR and EPA Region 5 staff about refining the analysis, and 

submitted a refined CALPUFF BART modeling protocol in March 2007. EPA reviewed the 

protocol and provided minor comments to DNR in May 2010. Thilmany responded to these 

comments in a letter “Response to EPA Comments on Thilmany BART Modeling Protocol” dated 

November 9, 2010. In addition, subsequent to the EPA protocol comments, the US Fish and 

Wildlife Service and US Forest Service reviewed the protocol and had additional discussions with 

DNR and EPA. The three EPA comments, and each response, are listed below. 

Comment 1

Information needs to be presented which clarifies how POSTUTIL was used for ammonia. 

Response 1

The VISTAS methodology was used, with a MNITRATE switch setting of one (1). 

Comment 2

The modeling must include a copy of the input and list files associated with runs. The protocol 

only offers some of the control file information. 

Response 2

All CALMET, CALPUFF, and CALPOST input and list files, as well as meteorological and 

geophysical data files, had been provided by Thilmany to DNR on a portable hard disk drive. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

4 December 2010 

Thilmany will again provide a portable hard disk drive of all modeling files to DNR for the 

updated BART analysis, for purposes of SIP documentation. 

Comment 3

The Thilmany input file ... uses the background ammonia values that were produced for the 

LADCO protocol. These values are based on modeled estimates. Monitoring data has generally 

shown much higher ammonia than what was used from the model results. The refined modeling 

analyses for Thilmany ... must evaluate the visibility impacts using measured background 

ammonia values. 

Response 3

The US Fish and Wildlife Service proposed using a constant background ammonia concentration 

of 3.9 ppb, which was the highest concentration measured at the Mayville Wisconsin station 

during a mid-1990s EPA study. Thilmany has agreed to use this single, conservative background 

value in the absence of daily data. 

On November 29, 2010, DNR issued a letter that approved the Thilmany CALPUFF BART 

protocol, as well as the emission rates to be used for the BART eligible emission units. DNR 

requested that the 2007 version of the protocol be updated to include the responses to EPA 

comments, and text that addresses current CALPUFF modeling guidance. In addition, the 

updated modeling results could be presented in the protocol (so that all information is located in 

one document). 

This document is the updated modeling protocol and final modeling report for the refined 

Thilmany “Subject to BART” analysis. This document does not duplicate the extensive 

information on visibility, CALPUFF, and EPA guidance on BART modeling procedures that are 

contained in the VISTAS protocol. Rather, this document describes how data specific to this 

setting will be used in the refined CALPUFF modeling. Section 1 of the protocol is this 

introduction. Section 2 briefly summarizes important concepts from the VISTAS protocol. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

5 December 2010 

Section 3 describes the specific CALMET data and procedures that were used to develop a 

refined, 4-km spaced meteorological grid for Wisconsin. Section 4 describes the CALPUFF input 

data and procedures, and Section 5 discusses the POSTUTIL and CALPOST processing, 

including the use of annual average natural background visibility. Section 6 presents the emission 

and stack data that were used for the BART eligible emission units, and Section 7 presents the 

modeling results. Appendices A and B present example CALMET and CALPUFF input file 

listings. A portable hard drive is also being submitted that contains all input data, control files, 

output files, and computer codes used in the analysis. 

2.0 VISTAS BART Protocol 

The VISTAS member states have prepared a CALPUFF modeling protocol for BART 

determinations that is fully consistent with the EPA guidelines in 40 CFR Part 51 Appendix W

and Appendix Y. The VISTAS protocol describes a two-step CALPUFF analysis methodology 

for BART exemption analyses. The initial CALPUFF analysis uses a “screening” or coarse 

resolution meteorological grid to determine if a particular source may be exempted from further 

BART analyses. The screening results are also used to determine which Class I areas should be 

included in any refined analysis. Assumptions for the initial screening analysis are conservative 

so that a source that contributes to visibility impairment is not exempted in error. If a source is 

shown to contribute to visibility impairment using the initial screening assessment, the source has

the option to undertake refined CALPUFF modeling using finer meteorological grids to evaluate 

further whether it is subject to BART. 

VISTAS developed both coarse (12-km grid resolution) and refined (4-km grid resolution) 

CALMET files. The fine grid CALMET files utilized both MM5 prognostic data, as well as 

meteorological observational data for the CALMET “Step 2” calculations. Overwater (buoy) data 

were used in addition to the standard hourly surface meteorological observations, precipitation 

observations, and twice-daily upper air sounding data. The VISTAS website provides detailed 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

6 December 2010 

documentation and supporting information on the refined CALMET processing, including the 

CALMET and CALPUFF input files that contain model configuration options and settings that 

have been optimized after consultation with stakeholders and consulting experts. These same

CALMET and CALPUFF input files were used as the basis for the refined Wisconsin analyses. 

The VISTAS protocol discusses several options for defining the natural background visibility. 

These include use of the annual average natural background extinction or the background 

extinction for the 20% best natural conditions days. Based on an email survey of the state 

agencies from the VISTAS member states, all of the VISTAS states allowed the use of annual 

average natural background extinction for refined CALPUFF analyses. This is also the guidance 

provided by EPA Region 5 staff during discussions with DNR and the Wisconsin Paper Council, 

and the method approved by DNR in their November 29, 2010 letter. Therefore, the refined 

Thilmany CALPUFF modeling used the annual average natural background extinction for 

CALPOST processing. 

The VISTAS BART guidance recommends that the threshold value used to define whether a 

source “contributes” to visibility impairment is a 0.5 dv change from natural background 

conditions. The 98th percentile 24-hr average predicted impact at the Class I area (equal to the 8th

highest value) is to be compared to this contribution threshold value. According to clarification 

of the BART guidance received from EPA by the VISTAS workgroup, for a three-year simulation 

the modeling values to be compared with the threshold are the greatest of the three annual 8th

highest values, or the 22nd highest value over all three years combined, whichever is greater. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

7 December 2010 

3.0 CALMET Data and Procedures 

Since the 2007 version of the modeling protocol was developed, EPA has updated the versions of 

the approved CALPUFF programs, and has provided additional guidance on CALMET “switch” 

settings. The current approved versions are CALPUFF version 5.8 (level 070623), and 

CALMET version 5.8 (level 070623), and these versions were used for the updated refined BART 

CALPUFF analysis. On August 31, 2009, EPA published the memorandum “Clarification of 

EPA-FLM Recommended Settings for CALMET”. EPA stated that a 4 km fine CALMET grid 

size was acceptable, and provided recommended CALMET settings. The CALMET settings for 

the updated refined BART CALPUFF analysis meet all current EPA recommendations. 

The first step in development of the refined Wisconsin analysis was to define the CALMET 

refined modeling domain and grid. As discussed in Section 1, DNR’s screening analysis 

indicated that there are three Class I areas to the north of Wisconsin, the Boundary Waters Canoe 

Area, Isle Royal National Park, and Seney Wildlife Area, where the screening analysis predicts 

some level of visibility impact from Wisconsin BART eligible sources. Therefore, the 

meteorological grid was developed to ensure coverage for these three Class I areas, as well as for 

the BART eligible source locations throughout Wisconsin. Standard IWAQM guidance also 

recommends that the CALMET grid extend a minimum of 50 km beyond any Class I or emission 

source location, so that puff recirculation can be properly accounted for. 

The refined CALMET grid was defined as a 4-km spaced grid with 162 cells in the X-axis and 

191 in the Y-axis. The grid projection was Lambert Conformal Conic, using the same projection 

parameters as in the DNR screening analysis (this allows the use of the same source X and Y 

coordinates as in the DNR analysis). The projection parameters include RLAT0 = 40N, RLON0 

= 97W, XLAT1 = 33N, XLAT2 = 45N, XORIGKM = 247.0, YORIGKM = 240.0, and DATUM 

= NAS-C. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

8 December 2010 

The meteorological data that was input to CALMET included the same three years (2002-2004) 

of CALMM5 data used by DNR, which was provided by LADCO. However, the refined 

CALMET runs also considered observation data from 22 surface stations, 16 precipitation 

stations, 5 overwater buoy stations, and 3 upper air stations. Figure 2 is a plot of the refined 

CALPUFF modeling domain. Figure 3 presents a plot of the locations of the observation stations 

in the modeling domain. 

The CAMET program MAKEGEO uses USGS GTOPO30 digital terrain data (which includes 

coverage in Canada) and USGS Composite Theme Grid Land Use and Land Cover (LULC) data 

to create a gridded data file on geophysical parameters that is used by CALMET. The available 

USGS LULC coverage does not extend into the Canadian areas of the refined domain. These 

areas in Canada were assigned to the “forested land” category. Figure 4 presents a plot of the 

land use data for the modeling domain. 

The VISTAS refined CALMET input files discussed in section 2 were used as the basis for the 

refined Wisconsin CALMET input files. The same CALMET configuration settings and options 

were utilized, as they are representative of Wisconsin terrain and land use patterns. All settings 

conform with current EPA and FLM guidance. 

Appendix A presents a listing of a CALMET input file developed for the refined analysis. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

9 December 2010 

Figure 2 – Refined CALPUFF Modeling Domain and Locations of Class I Areas 

300 400 500 600 700 800

LCC East (km)

300

400

500

600

700

800

900

1000

LC

C North (k

m)

1

-1

100

300

500

700

900

1100

1300

1500

1700

1900

2100

2300

2500

2700

2900

3100

3300

3500

3700

3900

4500

Terrain (m)

LCC Origin: 40N, 97W

Matching Parallels: 33N, 45N

Boundary Waters 

Isle Royale

Seney 

NOTE: The Class I area receptors are in red, the Thilmany mill location is in blue, and the X and 

Y coordinates are the Lambert projection coordinates are in kms. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

10 December 2010 

Figure 3 – Locations of Observational Stations in Refined CALPUFF Modeling Domain 

300 400 500 600 700 800 900 1000

LCC East (km)

Wisconsin Refined CALMET

Location of Observation stations

300

400

500

600

700

800

900

1000

LCC N

orth (km)

MADI MILW

LAC

EAU 

GREE

MANI

WAUS STUR

MOSI CLIN

WISC

EAGL

MINE

HAYW

JUNE

DULT

MANI

SAWY

HOUG

IRNM ESCA

IRNW

MSUP

NMCH

ESUP

WSUP

SMCH

COPP

ESCA

HOUG

IRON

MANI

SAUL

CLIN

GREE

HAYW

LAC 

MADI

ME MARS NO

MILW

RAIN

MNNP GREE STURG

INTF

NOTES: Surface stations are in red, overwater (bouy) in blue, precipitation in green, and upper 

air in purple.
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

11 December 2010 

Figure 4 – Land Use Data for Refined CALPUFF Modeling Domain 

300 400 500 600 700 800

LCC East (km)

300

400

500

600

700

800

900

1000

LCC North (km)

Snow/Ice

Tundra

Barren

Wetland

Water

Forest

Range

Agriculture

Urban/Built-Up

Land Use

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

95

100

. .

. .

LCC Origin: 40N, 97W

Datum: NAS-C

Matching Parallels: 33N, 45N

False Easting: 0.0

False Northing: 0.0
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

12 December 2010 

Some of the notable CALMET configuration settings included: 

• CALMET vertical layers set to 10, with cell face heights at 20, 40, 80, 160, 320, 640, 

1200, 2000, 3000, and 4000 meters, 

• CALMET diagnostic options, including slope flow effects (ISLOPE = 1) with the radius 

of influence of terrain (TERRAD) set to 15 km, 

• EPA recommended CALMET settings for the radius of influence parameters (R1=50, 

R2=100, RMAX1=100, RMAX2=200, and RMAX3=200). 

4.0 CALPUFF Procedures 

Both the DNR screening and VISTAS refined CALPUFF input files were used as the basis for the 

refined Wisconsin CALPUFF input files. All CALPUFF settings and options are consistent with 

EPA and FLM guidance, and the refined VISTAS protocol recommendations. The background 

ozone (O3) concentrations were used directly from the DNR CALPUFF input files. Instead of 

using monthly background ammonia concentrations from the DNR screening analyses, a single 

conservative background ammonia concentration of 3.9 ppb was used. Appendix B presents a 

listing of a CALPUFF input file developed for the Thilmany analysis. 

The DNR screening analysis considered three emitted pollutants, SO2, NOx, and PM2.5. The 

refined CALPUFF modeling will consider speciated particulate emissions, including coarse PM 

(PMC), fine PM equivalent to PM2.5 (PMF), sulfate (SO4), nitrate (NO3), elemental carbon (EC), 

and secondary organic aerosols (SOA or OC). Section 6 of this protocol describes how the 

speciated particulate emissions were calculated. 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

13 December 2010 

5.0 POSTUTIL and CALPOST Procedures 

In CALPUFF, the scavenging of the available ammonia for nitrate formation is computed on a 

puff-by-puff basis. Because of the possibility of multiple puff overlap, this approach may tend to 

overestimate the amount of ammonia available to form nitrate. In order to address the cumulative 

consumption of ammonia, the POSTUTIL program can be used to repartition nitric acid and 

nitrate. POSTUTIL calculates new NO3/HNO3 equilibrium concentrations for the sample source 

in the Class I area using the background ammonia. As recommended in the VISTAS procedures 

for refined CALPUFF modeling, the POSTUTIL “MNITRATE=1” method was used for the 

refined Wisconsin CALPUFF modeling. Instead of using the monthly values for background 

ammonia concentrations from the DNR screening analyses, a single conservative background 

ammonia concentration of 3.9 ppb was used. 

The modeling protocol submitted in 2007 proposed to use CALPOST Visibility Method 6 to 

calculate visibility impacts. However, since that time there have been revisions to CALPOST that 

allow the use of the updated IMPROVE extinction equation. CALPOST version 6.221 can 

implement the “Method 8 Mode 5” methodology to calculate visibility impacts, and the FLMs 

recommend its use in “Federal Land Managers’ Air Quality Related Values Work Group (FLAG) 

Phase I Report—Revised (2010)” (herein referred to as FLAG 2010). Therefore, this updated 

methodology will be used for the Thilmany BART analysis. The new CALPUFF Graphical Users

Interface automatically enters the appropriate values, based on the Class I area being selected, for 

natural background species and relative humidity adjustment factors using the data in Tables 6 

through 9 of Section 3.3.5 of FLAG 2010 (which are based on “Guidance for Estimating Natural 

Visibility Conditions Under the Regional Haze Rule”, EPA-454/B-03-005, September 2003). 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

14 December 2010 

6.0 Emissions Modeled 

EPA’s BART modeling guidance state that the 24-hr maximum actual emissions rates for the 

period of the modeling simulation (2002-2004) should be used for the analysis. If this data is not 

available, then the short term “allowable” or “potential” emission rates should be used. Thilmany 

provided DNR with source information that has been reviewed to determine the 24-hr maximum 

actual emissions rates. The SO2 emissions are based on the maximum actual emission rate from

the CEMS during the 2002-04 time frame, and the PM and NOx emissions represent maximum 

potential emission rates (which is conservative). On November 29, 2010, DNR issued a letter that 

approved the following emission rates to be used for the Thilmany BART eligible boiler: 207.9 

g/sec (1650 lb/hr) SO2, 68.2 g/sec (541 lb/hr) NOX, and 11.1 g/sec (88 lb/hr) for PM. The PM 

emissions have been speciated using the information for coal fired boilers developed by the 

National Park Service1

. The speciated PM emissions listed in Table 1 were used in the refined 

BART modeling. The stack parameters used in the modeling analysis were the same as those 

used by DNR in their screening analysis. 

Table 1 – Thilmany Speciated PM Emissions 

PM Species Emission Rate (lb/hr) 

Coarse PM 2.9 

Fine PM 3.4 

Elemental Carbon 0.1 

Condensable Inorganics (Sulfate) 65.3 

Condensable Organics (OC) 16.3 

 

1 http://www2.nature.nps.gov/air/permits/ect/index.cfm) 
 Updated BART Modeling Protocol and Report for 

 Thilmany Kaukauna Mill

15 December 2010 

7.0 Modeling Results 

CALPOST computes the daily maximum change in deciviews relative to the annual average 

natural background visibility, separately for each Class I area. For evaluating the source impact 

relative to the “Subject to BART” visibility impact threshold of 0.5 dv, the daily maximum

changes in visibility are sorted to determine the 98th percentile (8th highest) value for each of 

three years, and the 98th percentile (22nd highest) value for the completed three year period. If all 

98th percentile values are below the threshold of 0.5 dv based on the refined CALPUFF analysis, 

the source is exempt from the BART requirements. 

Another equivalent metric commonly used for BART exemption modeling is to sum the number 

of days per year that are above the 0.5 dv threshold for each Class I area separately; if there are 7 

or fewer days above the threshold for each year, then the 98th percentile value is also below the 

threshold. This is the metric approved by DNR for use in the BART modeling analysis. 

Specifically, for each Class I area separately, if there are less than 8 days per year that the 

predicted visibility impacts are greater than 0.5 deciviews relative to the annual average natural 

background visibility, then the BART eligible emission units at the modeled facility will be 

determined not to be Subject to BART. 

Table 2 presents the results from the refined CALPUFF BART exemption modeling. These 

results demonstrate that there are less than 8 days per year, at each individual Class I area, when 

the visibility impacts from the Thilmany BART eligible source are above 0.5 dv. Therefore, the 

Thilmany BART eligible source is not Subject to BART requirements. 
Updated BART Modeling Protocol an

Thilmany Ka

Table 2 – Thilmany CALPUFF BART Exemption Results Summary 

Class I area Distance 

(km) from 

source to

Class I area 

boundary

# of days 

with impact

> 0.5 dv in 

Class I area:

2002

# of days with

impact > 0.5 

dv in Class I 

area: 2003

# of days 

with impact

> 0.5 dv in 

Class I area:

2004

# of days with

impact > 0.5 

dv in Class I 

area for 3 year

period

Maximum 98th

Percentile 

impact over 

either annual 

or 3-yr periods

Seney , MI ~ 280 2 0 1 3 0.34Isle Royal, MN ~ 400 0 0 0 0 0.14Boundary Waters, MN ~ 450 1 0 0 1 0.11

16 D
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

Appendix A – Example CALMET Input File 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

WI Refined CALMET - 4km Grid - Dec 2010 - with Updated EPA Settings 

---------------- Run title (3 lines) ------------------------------------------ 

 CALMET MODEL CONTROL FILE 

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

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

INPUT GROUP: 0 -- Input and Output File Names 

Subgroup (a) 

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

Default Name Type File Name 

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

GEO.DAT input ! GEODAT=geo.dat ! 

SURF.DAT input ! SRFDAT=SURF02Z.DAT ! 

CLOUD.DAT input * CLDDAT= * 

PRECIP.DAT input ! PRCDAT=PRECIP02.DAT ! 

MM4.DAT input * MM4DAT=E:\MRPO-calmm5\2002\MM5.020102.3D.DAT * 

MM4.DAT input ! MM4DAT=E:\MRPO-calmm5\2002\020102.MM5 ! 

WT.DAT input * WTDAT= * 

CALMET.LST output ! METLST=cal020102.lST ! 

CALMET.DAT output ! METDAT=E:\WI-Calmet\2002Output\cal020102.dat ! 

PACOUT.DAT output * PACDAT= * 

All file names will be converted to lower case if LCFILES = T 

Otherwise, if LCFILES = F, file names will be converted to UPPER CASE 

 T = lower case ! LCFILES = T ! 

 F = UPPER CASE 

NUMBER OF UPPER AIR & OVERWATER STATIONS: 

 Number of upper air stations (NUSTA) No default ! NUSTA = 3 ! 

 Number of overwater met stations 

 (NOWSTA) No default ! NOWSTA = 5 ! 

 !END! 

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

Subgroup (b) 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

Upper air files (one per station) 

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

Default Name Type File Name 

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

UP1.DAT input 1 ! UPDAT=UPGB0204.DAT! !END! 

UP2.DAT input 2 ! UPDAT=UPMN0204.DAT! !END! 

UP3.DAT input 3 ! UPDAT=UPIN0204.DAT! !END! 

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

Subgroup (c) 

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

Overwater station files (one per station) 

SEA1.DAT input 1 ! SEADAT=4500102.DAT! !END! 

SEA2.DAT input 2 ! SEADAT=4500202.DAT! !END! 

SEA3.DAT input 3 ! SEADAT=4500402.DAT! !END! 

SEA4.DAT input 4 ! SEADAT=4500602.DAT! !END! 

SEA5.DAT input 5 ! SEADAT=4500702.DAT! !END! 

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

Default Name Type File Name 

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

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

Subgroup (d) 

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

Other file names 

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

Default Name Type File Name 

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

DIAG.DAT input * DIADAT= * 

PROG.DAT input * PRGDAT= * 

TEST.PRT output * TSTPRT= * 

TEST.OUT output * TSTOUT= * 

TEST.KIN output * TSTKIN= * 

TEST.FRD output * TSTFRD= * 

TEST.SLP output * TSTSLP= * 

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

NOTES: (1) File/path names can be up to 70 characters in length 

 (2) Subgroups (a) and (d) must have ONE 'END' (surround by 

 delimiters) at the end of the group 

 (3) Subgroups (b) and (c) must have an 'END' (surround by 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 delimiters) at the end of EACH LINE 

 !END! 

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

INPUT GROUP: 1 -- General run control parameters 

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

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

 Month (IBMO) -- No default ! IBMO= 1 ! 

 Day (IBDY) -- No default ! IBDY= 2 ! 

 Hour (IBHR) -- No default ! IBHR= 0 ! 

 Base time zone (IBTZ) -- No default ! IBTZ= 6 ! 

 PST = 08, MST = 07 

 CST = 06, EST = 05 

 Length of run (hours) (IRLG) -- No default ! IRLG= 24 ! 

 Run type (IRTYPE) -- Default: 1 ! IRTYPE= 1 ! 

 0 = Computes wind fields only 

 1 = Computes wind fields and micrometeorological variables 

 (u*, w*, L, zi, etc.) 

 (IRTYPE must be 1 to run CALPUFF or CALGRID) 

 Compute special data fields required 

 by CALGRID (i.e., 3-D fields of W wind 

 components and temperature) 

 in additional to regular Default: T ! LCALGRD = T ! 

 fields ? (LCALGRD) 

 (LCALGRD must be T to run CALGRID) 

 Flag to stop run after 

 SETUP phase (ITEST) Default: 2 ! ITEST= 2 ! 

 (Used to allow checking 

 of the model inputs, files, etc.) 

 ITEST = 1 - STOPS program after SETUP phase 

 ITEST = 2 - Continues with execution of 

 COMPUTATIONAL phase after SETUP 

 Test options specified to see if 

 they conform to regulatory 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 values? (MREG) No Default ! MREG = 1 ! 

 0 = NO checks are made 

 1 = Technical options must conform to USEPA guidance 

 IMIXH -1 Maul-Carson convective mixing height 

 over land; OCD mixing height overwater 

 ICOARE 0 OCD deltaT method for overwater fluxes 

 THRESHL 0.0 Threshold buoyancy flux over land needed 

 to sustain convective mixing height grow 

!END! 

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

INPUT GROUP: 2 -- Map Projection and Grid control parameters 

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

 Projection for all (X,Y): 

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

 Map projection 

 (PMAP) Default: UTM ! PMAP = LCC ! 

 UTM : Universal Transverse Mercator 

 TTM : Tangential Transverse Mercator 

 LCC : Lambert Conformal Conic 

 PS : Polar Stereographic 

 EM : 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 = -999 ! 

 Hemisphere for UTM projection? 

 (Used only if PMAP=UTM) 

 (UTMHEM) Default: N ! UTMHEM = N ! 

 N : Northern hemisphere projection 

 S : Southern hemisphere projection 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 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 XLAT2 

 PS : 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, and 

 east or west longitude. For example, 

 35.9 N Latitude = 35.9N 

 118.7 E Longitude = 118.7E 

 Datum-region 

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

 The Datum-Region for the coordinates is identified by a character 

 string. Many mapping products currently available use the model of the 

 Earth known as the World Geodetic System 1984 (WGS-84). Other local 

 models may be in use, and their selection in CALMET will make its output 

 consistent with local mapping products. The list of Datum-Regions with 

 official transformation parameters is provided by the National Imagery and 

 Mapping Agency (NIMA). 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 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, Sphere 

 ESR-S ESRI REFERENCE 6371KM Radius, Sphere 

 Datum-region for output coordinates 

 (DATUM) Default: WGS-84 ! DATUM = NAS-C ! 

 Horizontal grid definition: 

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

 Rectangular grid defined for projection PMAP, 

 with X the Easting and Y the Northing coordinate 

 No. X grid cells (NX) No default ! NX = 162 ! 

 No. Y grid cells (NY) No default ! NY = 191 ! 

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

 Units: km 

 Reference grid coordinate of 

 SOUTHWEST corner of grid cell (1,1) 

 X coordinate (XORIGKM) No default ! XORIGKM = 247.000 ! 

 Y coordinate (YORIGKM) No default ! YORIGKM = 240.000 ! 

 Units: km 

 Vertical grid definition: 

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

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

 Cell face heights in arbitrary 

 vertical grid (ZFACE(NZ+1)) No defaults 

 Units: m 

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

!END! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

INPUT GROUP: 3 -- Output Options 

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

 DISK OUTPUT OPTION 

 Save met. fields in an unformatted 

 output file ? (LSAVE) Default: T ! LSAVE = T ! 

 (F = Do not save, T = Save) 

 Type of unformatted output file: 

 (IFORMO) Default: 1 ! IFORMO = 1 ! 

 1 = CALPUFF/CALGRID type file (CALMET.DAT) 

 2 = MESOPUFF-II type file (PACOUT.DAT) 

 LINE PRINTER OUTPUT OPTIONS: 

 Print met. fields ? (LPRINT) Default: F ! LPRINT = T ! 

 (F = Do not print, T = Print) 

 (NOTE: parameters below control which 

 met. variables are printed) 

 Print interval 

 (IPRINF) in hours Default: 1 ! IPRINF = 1 ! 

 (Meteorological fields are printed 

 every 1 hours) 

 Specify which layers of U, V wind component 

 to print (IUVOUT(NZ)) -- NOTE: NZ values must be entered 

 (0=Do not print, 1=Print) 

 (used only if LPRINT=T) Defaults: NZ*0 

 ! IUVOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

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

 Specify which levels of the W wind component to print 

 (NOTE: W defined at TOP cell face -- 16 values) 

 (IWOUT(NZ)) -- NOTE: NZ values must be entered 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 (0=Do not print, 1=Print) 

 (used only if LPRINT=T & LCALGRD=T) 

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

 Defaults: NZ*0 

 ! IWOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Specify which levels of the 3-D temperature field to print 

 (ITOUT(NZ)) -- NOTE: NZ values must be entered 

 (0=Do not print, 1=Print) 

 (used only if LPRINT=T & LCALGRD=T) 

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

 Defaults: NZ*0 

 ! ITOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Specify which meteorological fields 

 to print 

 (used only if LPRINT=T) Defaults: 0 (all variables) 

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

 Variable Print ? 

 (0 = do not print, 

 1 = print) 

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

 ! STABILITY = 0 ! - PGT stability class 

 ! USTAR = 0 ! - Friction velocity 

 ! MONIN = 0 ! - Monin-Obukhov length 

 ! MIXHT = 0 ! - Mixing height 

 ! WSTAR = 0 ! - Convective velocity scale 

 ! PRECIP = 0 ! - Precipitation rate 

 ! SENSHEAT = 0 ! - Sensible heat flux 

 ! CONVZI = 0 ! - Convective mixing ht. 

 Testing and debug print options for micrometeorological module 

 Print input meteorological data and 

 internal variables (LDB) Default: F ! LDB = F ! 

 (F = Do not print, T = print) 

 (NOTE: this option produces large amounts of output) 

 First time step for which debug data 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 are printed (NN1) Default: 1 ! NN1 = 1 ! 

 Last time step for which debug data 

 are printed (NN2) Default: 1 ! NN2 = 2 ! 

 Testing and debug print options for wind field module 

 (all of the following print options control output to 

 wind field module's output files: TEST.PRT, TEST.OUT, 

 TEST.KIN, TEST.FRD, and TEST.SLP) 

 Control variable for writing the test/debug 

 wind fields to disk files (IOUTD) 

 (0=Do not write, 1=write) Default: 0 ! IOUTD = 0 ! 

 Number of levels, starting at the surface, 

 to print (NZPRN2) Default: 1 ! NZPRN2 = 1 ! 

 Print the INTERPOLATED wind components ? 

 (IPR0) (0=no, 1=yes) Default: 0 ! IPR0 = 0 ! 

 Print the TERRAIN ADJUSTED surface wind 

 components ? 

 (IPR1) (0=no, 1=yes) Default: 0 ! IPR1 = 0 ! 

 Print the SMOOTHED wind components and 

 the INITIAL DIVERGENCE fields ? 

 (IPR2) (0=no, 1=yes) Default: 0 ! IPR2 = 0 ! 

 Print the FINAL wind speed and direction 

 fields ? 

 (IPR3) (0=no, 1=yes) Default: 0 ! IPR3 = 0 ! 

 Print the FINAL DIVERGENCE fields ? 

 (IPR4) (0=no, 1=yes) Default: 0 ! IPR4 = 0 ! 

 Print the winds after KINEMATIC effects 

 are added ? 

 (IPR5) (0=no, 1=yes) Default: 0 ! IPR5 = 0 ! 

 Print the winds after the FROUDE NUMBER 

 adjustment is made ? 

 (IPR6) (0=no, 1=yes) Default: 0 ! IPR6 = 0 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Print the winds after SLOPE FLOWS 

 are added ? 

 (IPR7) (0=no, 1=yes) Default: 0 ! IPR7 = 0 ! 

 Print the FINAL wind field components ? 

 (IPR8) (0=no, 1=yes) Default: 0 ! IPR8 = 0 ! 

!END! 

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

INPUT GROUP: 4 -- Meteorological data options 

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

 NO OBSERVATION MODE (NOOBS) Default: 0 ! NOOBS = 0 ! 

 0 = Use surface, overwater, and upper air stations 

 1 = Use surface and overwater stations (no upper air observations) 

 Use MM5 for upper air data 

 2 = No surface, overwater, or upper air observations 

 Use MM5 for surface, overwater, and upper air data 

 NUMBER OF SURFACE & PRECIP. METEOROLOGICAL STATIONS 

 Number of surface stations (NSSTA) No default ! NSSTA = 22 ! 

 Number of precipitation stations 

 (NPSTA=-1: flag for use of MM5 precip data) 

 (NPSTA) No default ! NPSTA = 16 ! 

 CLOUD DATA OPTIONS 

 Gridded cloud fields: 

 (ICLOUD) Default: 0 ! ICLOUD = 0 ! 

 ICLOUD = 0 - Gridded clouds not used 

 ICLOUD = 1 - Gridded CLOUD.DAT generated as OUTPUT 

 ICLOUD = 2 - Gridded CLOUD.DAT read as INPUT 

 ICLOUD = 3 - Gridded cloud cover from Prognostic Rel. Humidity 

 FILE FORMATS 

 Surface meteorological data file format 

 (IFORMS) Default: 2 ! IFORMS = 2 ! 

 (1 = unformatted (e.g., SMERGE output)) 

 (2 = formatted (free-formatted user input)) 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Precipitation data file format 

 (IFORMP) Default: 2 ! IFORMP = 2 ! 

 (1 = unformatted (e.g., PMERGE output)) 

 (2 = formatted (free-formatted user input)) 

 Cloud data file format 

 (IFORMC) Default: 2 ! IFORMC = 2 ! 

 (1 = unformatted - CALMET unformatted output) 

 (2 = formatted - free-formatted CALMET output or user input) 

!END! 

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

INPUT GROUP: 5 -- Wind Field Options and Parameters 

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

 WIND FIELD MODEL OPTIONS 

 Model selection variable (IWFCOD) Default: 1 ! IWFCOD = 1 ! 

 0 = Objective analysis only 

 1 = Diagnostic wind module 

 Compute Froude number adjustment 

 effects ? (IFRADJ) Default: 1 ! IFRADJ = 1 ! 

 (0 = NO, 1 = YES) 

 Compute kinematic effects ? (IKINE) Default: 0 ! IKINE = 0 ! 

 (0 = NO, 1 = YES) 

 Use O'Brien procedure for adjustment 

 of the vertical velocity ? (IOBR) Default: 0 ! IOBR = 0 ! 

 (0 = NO, 1 = YES) 

 Compute slope flow effects ? (ISLOPE) Default: 1 ! ISLOPE = 1 ! 

 (0 = NO, 1 = YES) 

 Extrapolate surface wind observations 

 to upper layers ? (IEXTRP) Default: -4 ! IEXTRP = -4 ! 

 (1 = no extrapolation is done, 

 2 = power law extrapolation used, 

 3 = user input multiplicative factors 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 for layers 2 - NZ used (see FEXTRP array) 

 4 = similarity theory used 

 -1, -2, -3, -4 = same as above except layer 1 data 

 at upper air stations are ignored 

 Extrapolate surface winds even 

 if calm? (ICALM) Default: 0 ! ICALM = 0 ! 

 (0 = NO, 1 = YES) 

 Layer-dependent biases modifying the weights of 

 surface and upper air stations (BIAS(NZ)) 

 -1<=BIAS<=1 

 Negative BIAS reduces the weight of upper air stations 

 (e.g. BIAS=-0.1 reduces the weight of upper air stations 

 by 10%; BIAS= -1, reduces their weight by 100 %) 

 Positive BIAS reduces the weight of surface stations 

 (e.g. BIAS= 0.2 reduces the weight of surface stations 

 by 20%; BIAS=1 reduces their weight by 100%) 

 Zero BIAS leaves weights unchanged (1/R**2 interpolation) 

 Default: NZ*0 

 ! BIAS = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Minimum distance from nearest upper air station 

 to surface station for which extrapolation 

 of surface winds at surface station will be allowed 

 (RMIN2: Set to -1 for IEXTRP = 4 or other situations 

 where all surface stations should be extrapolated) 

 Default: 4. ! RMIN2 = -1.0 ! 

 Use gridded prognostic wind field model 

 output fields as input to the diagnostic 

 wind field model (IPROG) Default: 0 ! IPROG = 14 ! 

 (0 = No, [IWFCOD = 0 or 1] 

 1 = Yes, use CSUMM prog. winds as Step 1 field, [IWFCOD = 0] 

 2 = Yes, use CSUMM prog. winds as initial guess field [IWFCOD = 1] 

 3 = Yes, use winds from MM4.DAT file as Step 1 field [IWFCOD = 0] 

 4 = Yes, use winds from MM4.DAT file as initial guess field [IWFCOD = 1] 

 5 = Yes, use winds from MM4.DAT file as observations [IWFCOD = 1] 

 13 = Yes, use winds from MM5.DAT file as Step 1 field [IWFCOD = 0] 

 14 = Yes, use winds from MM5.DAT file as initial guess field [IWFCOD = 1] 

 15 = Yes, use winds from MM5.DAT file as observations [IWFCOD = 1] 

 Timestep (hours) of the prognostic 

 model input data (ISTEPPG) Default: 1 ! ISTEPPG = 1 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 RADIUS OF INFLUENCE PARAMETERS 

 Use varying radius of influence Default: F ! LVARY = F! 

 (if no stations are found within RMAX1,RMAX2, 

 or RMAX3, then the closest station will be used) 

 Maximum radius of influence over land 

 in the surface layer (RMAX1) No default ! RMAX1 = 100. ! 

 Units: km 

 Maximum radius of influence over land 

 aloft (RMAX2) No default ! RMAX2 = 200. ! 

 Units: km 

 Maximum radius of influence over water 

 (RMAX3) No default ! RMAX3 = 200. ! 

 Units: km 

 OTHER WIND FIELD INPUT PARAMETERS 

 Minimum radius of influence used in 

 the wind field interpolation (RMIN) Default: 0.1 ! RMIN = 0.1 ! 

 Units: km 

 Radius of influence of terrain 

 features (TERRAD) No default ! TERRAD = 15. ! 

 Units: km 

 Relative weighting of the first 

 guess field and observations in the 

 SURFACE layer (R1) No default ! R1 = 50. ! 

 (R1 is the distance from an Units: km 

 observational station at which the 

 observation and first guess field are 

 equally weighted) 

 Relative weighting of the first 

 guess field and observations in the 

 layers ALOFT (R2) No default ! R2 =100. ! 

 (R2 is applied in the upper layers Units: km 

 in the same manner as R1 is used in 

 the surface layer). 

 Relative weighting parameter of the 

 prognostic wind field data (RPROG) No default ! RPROG = 0. ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 (Used only if IPROG = 1) Units: km 

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

 Maximum acceptable divergence in the 

 divergence minimization procedure 

 (DIVLIM) Default: 5.E-6 ! DIVLIM= 5.0E-06 ! 

 Maximum number of iterations in the 

 divergence min. procedure (NITER) Default: 50 ! NITER = 50 ! 

 Number of passes in the smoothing 

 procedure (NSMTH(NZ)) 

 NOTE: NZ values must be entered 

 Default: 2,(mxnz-1)*4 ! NSMTH = 

 2 , 4 , 4 , 4 , 4 , 4 , 4 , 4 , 4 , 4 ! 

 Maximum number of stations used in 

 each layer for the interpolation of 

 data to a grid point (NINTR2(NZ)) 

 NOTE: NZ values must be entered Default: 99. ! NINTR2 = 

 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 ! 

 Critical Froude number (CRITFN) Default: 1.0 ! CRITFN = 1. ! 

 Empirical factor controlling the 

 influence of kinematic effects 

 (ALPHA) Default: 0.1 ! ALPHA = 0.1 ! 

 Multiplicative scaling factor for 

 extrapolation of surface observations 

 to upper layers (FEXTR2(NZ)) Default: NZ*0.0 

 ! FEXTR2 = 0., 0., 0., 0., 0., 0., 0., 0., 0., 0. ! 

 (Used only if IEXTRP = 3 or -3) 

 BARRIER INFORMATION 

 Number of barriers to interpolation 

 of the wind fields (NBAR) Default: 0 ! NBAR = 0 ! 

 THE FOLLOWING 4 VARIABLES ARE INCLUDED 

 ONLY IF NBAR > 0 

 NOTE: NBAR values must be entered No defaults 

 for each variable Units: km 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 X coordinate of BEGINNING 

 of each barrier (XBBAR(NBAR)) ! XBBAR = 0. ! 

 Y coordinate of BEGINNING 

 of each barrier (YBBAR(NBAR)) ! YBBAR = 0. ! 

 X coordinate of ENDING 

 of each barrier (XEBAR(NBAR)) ! XEBAR = 0. ! 

 Y coordinate of ENDING 

 of each barrier (YEBAR(NBAR)) ! YEBAR = 0. ! 

 DIAGNOSTIC MODULE DATA INPUT OPTIONS 

 Surface temperature (IDIOPT1) Default: 0 ! IDIOPT1 = 0 ! 

 0 = Compute internally from 

 hourly surface observations 

 1 = Read preprocessed values from 

 a data file (DIAG.DAT) 

 Surface met. station to use for 

 the surface temperature (ISURFT) No default ! ISURFT = 1 ! 

 (Must be a value from 1 to NSSTA) 

 (Used only if IDIOPT1 = 0) 

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

 Domain-averaged temperature lapse 

 rate (IDIOPT2) Default: 0 ! IDIOPT2 = 0 ! 

 0 = Compute internally from 

 twice-daily upper air observations 

 1 = Read hourly preprocessed values 

 from a data file (DIAG.DAT) 

 Upper air station to use for 

 the domain-scale lapse rate (IUPT) No default ! IUPT = 1 ! 

 (Must be a value from 1 to NUSTA) 

 (Used only if IDIOPT2 = 0) 

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

 Depth through which the domain-scale 

 lapse rate is computed (ZUPT) Default: 200. ! ZUPT = 200. ! 

 (Used only if IDIOPT2 = 0) Units: meters 

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

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Domain-averaged wind components 

 (IDIOPT3) Default: 0 ! IDIOPT3 = 0 ! 

 0 = Compute internally from 

 twice-daily upper air observations 

 1 = Read hourly preprocessed values 

 a data file (DIAG.DAT) 

 Upper air station to use for 

 the domain-scale winds (IUPWND) Default: -1 ! IUPWND = -1 ! 

 (Must be a value from -1 to NUSTA) 

 (Used only if IDIOPT3 = 0) 

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

 Bottom and top of layer through 

 which the domain-scale winds 

 are computed 

 (ZUPWND(1), ZUPWND(2)) Defaults: 1., 1000. ! ZUPWND= 1., 1000. ! 

 (Used only if IDIOPT3 = 0) Units: meters 

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

 Observed surface wind components 

 for wind field module (IDIOPT4) Default: 0 ! IDIOPT4 = 0 ! 

 0 = Read WS, WD from a surface 

 data file (SURF.DAT) 

 1 = Read hourly preprocessed U, V from 

 a data file (DIAG.DAT) 

 Observed upper air wind components 

 for wind field module (IDIOPT5) Default: 0 ! IDIOPT5 = 0 ! 

 0 = Read WS, WD from an upper 

 air data file (UP1.DAT, UP2.DAT, etc.) 

 1 = Read hourly preprocessed U, V from 

 a data file (DIAG.DAT) 

 LAKE BREEZE INFORMATION 

 Use Lake Breeze Module (LLBREZE) 

 Default: F ! LLBREZE = F ! 

 Number of lake breeze regions (NBOX) ! NBOX = 0 ! 

 X Grid line 1 defining the region of interest 

 ! XG1 = 0. ! 

 X Grid line 2 defining the region of interest 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 ! XG2 = 0. ! 

 Y Grid line 1 defining the region of interest 

 ! YG1 = 0. ! 

 Y Grid line 2 defining the region of interest 

 ! YG2 = 0. ! 

 X Point defining the coastline (Straight line) 

 (XBCST) (KM) Default: none ! XBCST = 0. ! 

 Y Point defining the coastline (Straight line) 

 (YBCST) (KM) Default: none ! YBCST = 0. ! 

 X Point defining the coastline (Straight line) 

 (XECST) (KM) Default: none ! XECST = 0. ! 

 Y Point defining the coastline (Straight line) 

 (YECST) (KM) Default: none ! YECST = 0. ! 

 Number of stations in the region Default: none ! NLB = 0 ! 

 (Surface stations + upper air stations) 

 Station ID's in the region (METBXID(NLB)) 

 (Surface stations first, then upper air stations) 

 ! METBXID = 0 ! 

!END! 

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

INPUT GROUP: 6 -- Mixing Height, Temperature and Precipitation Parameters 

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

 EMPIRICAL MIXING HEIGHT CONSTANTS 

 Neutral, mechanical equation 

 (CONSTB) Default: 1.41 ! CONSTB = 1.41 ! 

 Convective mixing ht. equation 

 (CONSTE) Default: 0.15 ! CONSTE = 0.15 ! 

 Stable mixing ht. equation 

 (CONSTN) Default: 2400. ! CONSTN = 2400.! 

 Overwater mixing ht. equation 

 (CONSTW) Default: 0.16 ! CONSTW = 0.16 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Absolute value of Coriolis 

 parameter (FCORIOL) Default: 1.E-4 ! FCORIOL = 1.0E-04! 

 Units: (1/s) 

 SPATIAL AVERAGING OF MIXING HEIGHTS 

 Conduct spatial averaging 

 (IAVEZI) (0=no, 1=yes) Default: 1 ! IAVEZI = 1 ! 

 Max. search radius in averaging 

 process (MNMDAV) Default: 1 ! MNMDAV = 1 ! 

 Units: Grid 

 cells 

 Half-angle of upwind looking cone 

 for averaging (HAFANG) Default: 30. ! HAFANG = 30. ! 

 Units: deg. 

 Layer of winds used in upwind 

 averaging (ILEVZI) Default: 1 ! ILEVZI = 1 ! 

 (must be between 1 and NZ) 

 CONVECTIVE MIXING HEIGHT OPTIONS: 

 Method to compute the convective 

 mixing height(IMIHXH) Default: 1 ! IMIXH = -1 ! 

 1: Maul-Carson for land and water cells 

 -1: Maul-Carson for land cells only - 

 OCD mixing height overwater 

 2: Batchvarova and Gryning for land and water cells 

 -2: Batchvarova and Gryning for land cells only 

 OCD mixing height overwater 

 Threshold buoyancy flux required to 

 sustain convective mixing height growth 

 overland (THRESHL) Default: 0.05 ! THRESHL = 0.00 ! 

 (expressed as a heat flux units: W/m3 

 per meter of boundary layer) 

 Threshold buoyancy flux required to 

 sustain convective mixing height growth 

 overwater (THRESHW) Default: 0.05 ! THRESHW = 0.05 ! 

 (expressed as a heat flux units: W/m3 

 per meter of boundary layer) 

 Option for overwater lapse rates used 

 in convective mixing height growth 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 (ITWPROG) Default: 0 ! ITWPROG = 0 ! 

 0 : use SEA.DAT lapse rates and deltaT (or assume neutral 

 conditions if missing) 

 1 : use prognostic lapse rates (only if IPROG>2) 

 and SEA.DAT deltaT (or neutral if missing) 

 2 : use prognostic lapse rates and prognostic delta T 

 (only if iprog>12 and 3D.DAT version# 2.0 or higher) 

 Land Use category ocean in 3D.DAT datasets 

 (ILUOC3D) Default: 16 ! ILUOC3D = 16 ! 

 Note: if 3D.DAT from MM5 version 3.0, iluoc3d = 16 

 if MM4.DAT, typically iluoc3d = 7 

 OTHER MIXING HEIGHT VARIABLES 

 Minimum potential temperature lapse 

 rate in the stable layer above the 

 current convective mixing ht. Default: 0.001 ! DPTMIN = 0.001 ! 

 (DPTMIN) Units: deg. K/m 

 Depth of layer above current conv. 

 mixing height through which lapse Default: 200. ! DZZI = 200. ! 

 rate is computed (DZZI) Units: meters 

 Minimum overland mixing height Default: 50. ! ZIMIN = 50. ! 

 (ZIMIN) Units: meters 

 Maximum overland mixing height Default: 3000. ! ZIMAX = 3000. ! 

 (ZIMAX) Units: meters 

 Minimum overwater mixing height Default: 50. ! ZIMINW = 50. ! 

 (ZIMINW) -- (Not used if observed Units: meters 

 overwater mixing hts. are used) 

 Maximum overwater mixing height Default: 3000. ! ZIMAXW = 3000. ! 

 (ZIMAXW) -- (Not used if observed Units: meters 

 overwater mixing hts. are used) 

 OVERWATER SURFACE FLUXES METHOD and PARAMETERS 

 (ICOARE) Default: 10 ! ICOARE = 0 ! 

 0: original deltaT method (OCD) 

 10: COARE with no wave parameterization (jwave=0, Charnock) 

 11: COARE with wave option jwave=1 (Oost et al.) 

 and default wave properties 

 -11: COARE with wave option jwave=1 (Oost et al.) 

 and observed wave properties (must be in SEA.DAT files) 

 12: COARE with wave option 2 (Taylor and Yelland) 

 and default wave properties 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 -12: COARE with wave option 2 (Taylor and Yelland) 

 and observed wave properties (must be in SEA.DAT files) 

 Coastal/Shallow water length scale (DSHELF) 

 (for modified z0 in shallow water) 

 ( COARE fluxes only) 

 Default : 0. ! DSHELF = 0. ! 

 units: km 

 COARE warm layer computation (IWARM) ! IWARM = 0 ! 

 1: on - 0: off (must be off if SST measured with 

 IR radiometer) Default: 0 

 COARE cool skin layer computation (ICOOL) ! ICOOL = 0 ! 

 1: on - 0: off (must be off if SST measured with 

 IR radiometer) Default: 0 

 TEMPERATURE PARAMETERS 

 3D temperature from observations or 

 from prognostic data? (ITPROG) Default:0 !ITPROG = 0 ! 

 0 = Use Surface and upper air stations 

 (only if NOOBS = 0) 

 1 = Use Surface stations (no upper air observations) 

 Use MM5 for upper air data 

 (only if NOOBS = 0,1) 

 2 = No surface or upper air observations 

 Use MM5 for surface and upper air data 

 (only if NOOBS = 0,1,2) 

 Interpolation type 

 (1 = 1/R ; 2 = 1/R**2) Default:1 ! IRAD = 1 ! 

 Radius of influence for temperature 

 interpolation (TRADKM) Default: 500. ! TRADKM = 500. ! 

 Units: km 

 Maximum Number of stations to include 

 in temperature interpolation (NUMTS) Default: 5 ! NUMTS = 5 ! 

 Conduct spatial averaging of temp- 

 eratures (IAVET) (0=no, 1=yes) Default: 1 ! IAVET = 1 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 (will use mixing ht MNMDAV,HAFANG 

 so make sure they are correct) 

 Default temperature gradient Default: -.0098 ! TGDEFB = -0.0098 ! 

 below the mixing height over 

 water (K/m) (TGDEFB) 

 Default temperature gradient Default: -.0045 ! TGDEFA = -0.0045 ! 

 above the mixing height over 

 water (K/m) (TGDEFA) 

 Beginning (JWAT1) and ending (JWAT2) 

 land use categories for temperature ! JWAT1 = 55 ! 

 interpolation over water -- Make ! JWAT2 = 55 ! 

 bigger than largest land use to disable 

 PRECIP INTERPOLATION PARAMETERS 

 Method of interpolation (NFLAGP) Default = 2 ! NFLAGP = 2 ! 

 (1=1/R,2=1/R**2,3=EXP/R**2) 

 Radius of Influence (km) (SIGMAP) Default = 100.0 ! SIGMAP = 100. ! 

 (0.0 => use half dist. btwn 

 nearest stns w & w/out 

 precip when NFLAGP = 3) 

 Minimum Precip. Rate Cutoff (mm/hr) Default = 0.01 ! CUTP = 0.01 ! 

 (values < CUTP = 0.0 mm/hr) 

!END! 

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

INPUT GROUP: 7 -- Surface meteorological station parameters 

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

 SURFACE STATION VARIABLES 

 (One record per station -- 0 records in all) 

 1 2 

 Name ID X coord. Y coord. Time Anem. 

 (km) (km) zone Ht.(m) 

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

! SS1 ='MILW' 26400 739.061 363.200 6 10 ! 

! SS2 ='MADI' 26410 619.927 372.210 6 10 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

! SS3 ='LA C' 26430 461.012 442.705 6 10 ! 

! SS4 ='EAU ' 26435 435.857 552.352 6 10 ! 

! SS5 ='GREE' 26450 703.911 530.179 6 10 ! 

! SS6 ='MANI' 26455 743.477 495.113 6 10 ! 

! SS7 ='STUR' 26458 755.730 576.760 6 10 ! 

! SS8 ='WAUS' 26463 581.202 568.247 6 10 ! 

! SS9 ='MOSI' 26465 579.307 552.489 6 10 ! 

! SS10 ='CLIN' 26502 655.019 541.168 6 10 ! 

! SS11 ='WISC' 26503 582.532 412.498 6 10 ! 

! SS12 ='EAGL' 26504 599.980 682.545 6 10 ! 

! SS13 ='MINE' 26507 550.817 338.941 6 10 ! 

! SS14 ='HAYW' 26508 430.347 681.295 6 10 ! 

! SS15 ='JUNE' 26509 669.429 409.931 6 10 ! 

! SS16 ='dulu' 27450 366.011 766.977 6 10 ! 

! SS17 ='MANI' 25408 838.315 711.433 5 10 ! 

! SS18 ='SAWY' 26284 741.237 743.078 5 10 ! 

! SS19 ='HOUG' 26380 977.905 549.977 5 10 ! 

! SS20 ='ESCA' 26480 775.417 679.550 5 10 ! 

! SS21 ='IRNM' 27437 690.168 678.511 5 10 ! 

! SS22 ='IRNW' 27445 528.314 743.857 5 10 ! 

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Five digit integer for station ID 

!END! 

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

INPUT GROUP: 8 -- Upper air meteorological station parameters 

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

 UPPER AIR STATION VARIABLES 

 (One record per station -- 0 records in all) 

 1 2 

 Name ID X coord. Y coord. Time zone 

 (km) (km) 

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

! US1 ='GREE' 14898 703.911 539.179 6 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

! US2 ='MNNP' 94983 272.681 539.843 6 ! 

! US3 ='INTF' 14918 269.489 957.416 6 ! 

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Five digit integer for station ID 

!END! 

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

INPUT GROUP: 9 -- Precipitation station parameters 

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

 PRECIPITATION STATION VARIABLES 

 (One record per station -- 0 records in all) 

 (NOT INCLUDED IF NPSTA = 0) 

 1 2 

 Name Station X coord. Y coord. 

 Code (km) (km) 

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

! PS1 ='COPP' 201780 719.681 845.179 ! 

! PS2 ='ESCA' 202626 779.850 646.454 ! 

! PS3 ='HOUG' 203936 1001.500 536.427 ! 

! PS4 ='IRON' 204090 699.421 640.283 ! 

! PS5 ='MANI' 205073 845.933 667.499 ! 

! PS6 ='SAUL' 207366 985.172 765.448 ! 

! PS7 ='CLIN' 471667 696.889 290.151 ! 

! PS8 ='GREE' 473269 709.933 509.579 ! 

! PS9 ='HAYW' 473511 442.947 678.728 ! 

! PS10 ='LAC ' 474370 471.515 404.495 ! 

! PS11 ='MADI' 474961 631.719 367.656 ! 

! PS12 ='MARS' 475120 550.348 505.662 ! 

! PS13 ='MENO' 475335 431.807 514.277 ! 

! PS14 ='MILW' 475479 772.567 324.344 ! 

! PS15 ='RAIN' 476939 599.369 634.460 ! 

! PS16 ='STURG' 478267 776.964 542.174 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Six digit station code composed of state 

 code (first 2 digits) and station ID (last 

 4 digits) 

!END!

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

Appendix B – Example CALPUFF Input File 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

Thilmany BART Modeling - SO2, PM speciation 

Using Refined 4km CALMET Data File and SENE, ISLE, BOWA Class I Receptors 

---------------- 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 =ThilRef02.lst ! 

CONC.DAT output ! CONDAT =ThilRef02.dat ! 

DFLX.DAT output * DFDAT = * 

WFLX.DAT output * WFDAT = * 

VISB.DAT output * VISDAT =Thil02DNR.VIB * 

RESTARTE.DAT output * RSTARTE= * 

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

Emission Files 

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

PTEMARB.DAT input * PTDAT = * 

VOLEMARB.DAT input * VOLDAT = * 

BAEMARB.DAT input * ARDAT = * 

LNEMARB.DAT input * LNDAT = * 

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

Other Files 

----------- 

OZONE.DAT input * OZDAT = * 

VD.DAT input * VDDAT = * 

CHEM.DAT input * CHEMDAT= * 

H2O2.DAT input * H2O2DAT= * 

HILL.DAT input * HILDAT= * 

HILLRCT.DAT input * RCTDAT= * 

COASTLN.DAT input * CSTDAT= * 

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 = T 

Otherwise, 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 length 

Provision for multiple input files 

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

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Number of CALMET.DAT files for run (NMETDAT) 

 Default: 1 ! NMETDAT = 364 ! 

 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=e:\WI-Calmet\2002output\cal020102.DAT ! !END! 

NOTE: the remaining CALMET data files names are listed here ..... 

none input ! METDAT=e:\WI-Calmet\2002output\cal021231.DAT ! !END! 

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

INPUT GROUP: 1 -- General run control parameters 

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

 Option to run all periods found 

 in the met. file (METRUN) Default: 0 ! METRUN = 0 ! 

 METRUN = 0 - Run period explicitly defined below 

 METRUN = 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 = 02 ! 

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

 Base time zone (XBTZ) -- No default ! XBTZ = 6.0 ! 

 PST = 8., MST = 7. 

 CST = 6., EST = 5. 

 Length of run (hours) (IRLG) -- No default ! IRLG = 8736 ! 

 Number of chemical species (NSPEC) 

 Default: 5 ! NSPEC = 9 ! 

 Number of chemical species 

 to be emitted (NSE) Default: 3 ! NSE = 7 ! 

 Flag to stop run after 

 SETUP phase (ITEST) Default: 2 ! ITEST = 2 ! 

 (Used to allow checking 

 of the model inputs, files, etc.) 

 ITEST = 1 - STOPS program after SETUP phase 

 ITEST = 2 - Continues with execution of program 

 after SETUP 

 Restart Configuration: 

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

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 0 = Do not read or write a restart file 

 1 = Read a restart file at the beginning of 

 the run 

 2 = Write a restart file during run 

 3 = Read a restart file at beginning of run 

 and write a restart file during run 

 Number of periods in Restart 

 output 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) 

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

 Averaging 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 the 

 near field (MGAUSS) Default: 1 ! MGAUSS = 1 ! 

 0 = uniform 

 1 = Gaussian 

 Terrain adjustment method 

 (MCTADJ) Default: 3 ! MCTADJ = 3 ! 

 0 = no adjustment 

 1 = ISC-type of terrain adjustment 

 2 = simple, CALPUFF-type of terrain 

 adjustment 

 3 = partial plume path adjustment 

 Subgrid-scale complex terrain 

 flag (MCTSG) Default: 0 ! MCTSG = 0 ! 

 0 = not modeled 

 1 = modeled 

 Near-field puffs modeled as 

 elongated 0 (MSLUG) Default: 0 ! MSLUG = 0 ! 

 0 = no 

 1 = yes (slug model used) 

 Transitional plume rise modeled ? 

 (MTRANS) Default: 1 ! MTRANS = 1 ! 

 0 = no (i.e., final rise only) 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 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 building 

 downwash? (MBDW) Default: 1 ! MBDW = 1 ! 

 1 = ISC method 

 2 = PRIME method 

 Vertical wind shear modeled above 

 stack 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 = no 

 1 = yes 

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

 0 = no 

 1 = yes 

 (dry deposition method specified 

 for each species in Input Group 3) 

 Method used to compute dispersion 

 coefficients (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 in 

 urban 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 

 MDISP = 3, described above. MDISP = 5 assumes that 

December 2010 
 Refined BART Modeling Protocol for 

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 measured values are read 

 Sigma-v/sigma-theta, sigma-w measurements used? (MTURBVW) 

 (Used only if MDISP = 1 or 5) Default: 3 ! MTURBVW = 3 ! 

 1 = use sigma-v or sigma-theta measurements 

 from PROFILE.DAT to compute sigma-y 

 (valid for METFM = 1, 2, 3, 4) 

 2 = use sigma-w measurements 

 from PROFILE.DAT to compute sigma-z 

 (valid for METFM = 1, 2, 3, 4) 

 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) 

 4 = use sigma-theta measurements 

 from PLMMET.DAT to compute sigma-y 

 (valid only if METFM = 3) 

 Back-up method used to compute dispersion 

 when measured turbulence data are 

 missing (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 in 

 urban areas 

 4 = same as 3 except PG coefficients computed using 

 the MESOPUFF II eqns. 

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

 (MROUGH) 

 0 = no 

 1 = yes 

 Partial plume penetration of Default: 1 ! MPARTL = 1 ! 

 elevated inversion? 

 (MPARTL) 

 0 = no 

 1 = 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 = no 

 1 = yes 

 Sub-Grid TIBL module used for shore line? 

 Default: 0 ! MSGTIBL = 0 ! 

 (MSGTIBL) 

 0 = no 

 1 = yes 

 Boundary conditions (concentration) modeled? 

 Default: 0 ! MBCON = 0 ! 

 (MBCON) 

 0 = no 

 1 = yes, using formatted BCON.DAT file 

 2 = yes, using unformatted CONC.DAT file 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Analyses of fogging and icing impacts due to emissions from 

 arrays of mechanically-forced cooling towers can be performed 

 using CALPUFF in conjunction with a cooling tower emissions 

 processor (CTEMISS) and its associated postprocessors. Hourly 

 emissions of water vapor and temperature from each cooling tower 

 cell are computed for the current cell configuration and ambient 

 conditions by CTEMISS. CALPUFF models the dispersion of these 

 emissions and provides cloud information in a specialized format 

 for 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 = no 

 1 = yes - report results in PLUME Mode format 

 2 = yes - report results in RECEPTOR Mode format 

 TEST options specified to see if 

 they conform to regulatory 

 values? (MREG) Default: 1 ! MREG = 0 ! 

 0 = NO checks are made 

 1 = Technical options must conform to USEPA 

 Long Range Transport (LRT) guidance 

 METFM 1 or 2 

 AVET 60. (min) 

 PGTIME 60. (min) 

 MGAUSS 1 

 MCTADJ 3 

 MTRANS 1 

 MTIP 1 

 MCHEM 1 or 3 (if modeling SOx, NOx) 

 MWET 1 

 MDRY 1 

 MDISP 2 or 3 

 MPDF 0 if MDISP=3 

 1 if MDISP=2 

 MROUGH 0 

 MPARTL 1 

 SYTDEP 550. (m) 

 MHFTSZ 0 

!END! 

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

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

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

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

Subgroup (3a) 

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

 The following species are modeled: 

 The following species are modeled: 

! CSPEC = SO2 ! !END! 

! CSPEC = SO4 ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

! CSPEC = NOX ! !END! 

! CSPEC = HNO3 ! !END! 

! CSPEC = NO3 ! !END! 

! CSPEC = PMC ! !END! 

! CSPEC = PMF ! !END! 

! CSPEC = EC ! !END! 

! CSPEC = SOA ! !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 ! 

! PMC = 1, 1, 2, 0 ! 

! PMF = 1, 1, 2, 0 ! 

! EC = 1, 1, 2, 0 ! 

! SOA = 1, 1, 2, 0 ! 

!END! 

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

Subgroup (3b) 

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

 The following names are used for Species-Groups in which results 

 for certain species are combined (added) prior to output. The 

 CGRUP name will be used as the species name in output files. 

 Use this feature to model specific particle-size distributions 

 by 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 Mercator 

 TTM : Tangential Transverse Mercator 

 LCC : Lambert Conformal Conic 

 PS : Polar Stereographic 

 EM : 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) 

December 2010 
 Refined BART Modeling Protocol for 

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 (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 

 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 XLAT2 

 PS : 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, and 

 east or west longitude. For example, 

 35.9 N Latitude = 35.9N 

 118.7 E Longitude = 118.7E 

 Datum-region 

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

 The Datum-Region for the coordinates is identified by a character 

 string. Many mapping products currently available use the model of the 

 Earth known as the World Geodetic System 1984 (WGS-84). Other local 

 models may be in use, and their selection in CALMET will make its output 

 consistent with local mapping products. The list of Datum-Regions with 

 official transformation parameters is provided by the National Imagery and 

 Mapping 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, Sphere 

 ESR-S ESRI REFERENCE 6371KM Radius, Sphere 

 Datum-region for output coordinates 

 (DATUM) Default: WGS-84 ! DATUM = NAS-C ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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 = 162 ! 

 No. Y grid cells (NY) No default ! NY = 191 ! 

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

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

 Units: km 

 Cell face heights in arbitrary 

 vertical grid (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 = 247. ! 

 Y coordinate (YORIGKM) No default ! YORIGKM = 240. ! 

 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 the 

 computational 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 = 1 ! 

 (1 <= IBCOMP <= NX) 

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

 (1 <= JBCOMP <= NY) 

 X index of UR corner (IECOMP) No default ! IECOMP = 162 ! 

 (1 <= IECOMP <= NX) 

 Y index of UR corner (JECOMP) No default ! JECOMP = 191 ! 

 (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 the 

 sampling grid is at grid point (IESAMP, JESAMP) of the MET. grid. 

 The sampling grid must be identical to or a subset of the computational 

 grid. It may be a nested grid inside the computational grid. 

 The grid spacing of the sampling grid is DGRIDKM/MESHDN. 

 Logical flag indicating if gridded 

 receptors are used (LSAMP) Default: T ! LSAMP = F ! 

 (T=yes, F=no) 

 X index of LL corner (IBSAMP) No default ! IBSAMP = 1 ! 

 (IBCOMP <= IBSAMP <= IECOMP) 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

 (JBCOMP <= JBSAMP <= JECOMP) 

 X index of UR corner (IESAMP) No default ! IESAMP = 162 ! 

 (IBCOMP <= IESAMP <= IECOMP) 

 Y index of UR corner (JESAMP) No default ! JESAMP = 191 ! 

 (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 ! 

 (relative humidity file is 

 required for visibility 

 analysis) 

 Use data compression option in output file? 

 (LCOMPRS) Default: T ! LCOMPRS = T ! 

 * 

 0 = Do not create file, 1 = create file 

 DIAGNOSTIC MASS FLUX OUTPUT OPTIONS: 

 Mass flux across specified boundaries 

 for selected species reported hourly? 

 (IMFLX) Default: 0 ! IMFLX = 0 ! 

 0 = no 

 1 = yes (FLUXBDY.DAT and MASSFLX.DAT filenames 

 are specified in Input Group 0) 

 Mass balance for each species 

 reported hourly? 

 (IMBAL) Default: 0 ! IMBAL = 0 ! 

 0 = no 

 1 = 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) 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 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/s 

 2 = mg/m**3 mg/m**2/s 

 3 = ug/m**3 ug/m**2/s 

 4 = ng/m**3 ng/m**2/s 

 5 = Odour Units 

 Messages tracking progress of run 

 written to the screen ? 

 (IMESG) Default: 2 ! IMESG = 2 ! 

 0 = no 

 1 = 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 ------ 

-- MASS FLUX -- 

 SPECIES 

 /GROUP PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? 

SAVED ON DISK? 

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

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

! SO2 = 0, 1, 0, 0, 0, 0, 

0 ! 

! SO4 = 0, 1, 0, 0, 0, 0, 

0 ! 

! NOX = 0, 1, 0, 0, 0, 0, 

0 ! 

! HNO3 = 0, 1, 0, 0, 0, 0, 

0 ! 

! NO3 = 0, 1, 0, 0, 0, 0, 

0 ! 

! PMC = 0, 1, 0, 0, 0, 0, 

0 ! 

! PMF = 0, 1, 0, 0, 0, 0, 

0 ! 

! EC = 0, 1, 0, 0, 0, 0, 

0 ! 

! SOA = 0, 1, 0, 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 = 1 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Met. period to start output 

 (NN1) Default: 1 ! NN1 = 1 ! 

 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 terrain 

 receptors (NCTREC) Default: 0 ! NCTREC = 0 ! 

 Terrain and CTSG Receptor data for 

 CTSG hills input in CTDM format ? 

 (MHILL) No Default ! MHILL = 2 ! 

 1 = Hill and Receptor data created 

 by CTDM processors & read from 

 HILL.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 = 1. ! 

 to meters (MHILL=1) 

 Factor to convert vertical dimensions Default: 1.0 ! ZHILL2M = 1. ! 

 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 SCALE 2 

AMAX1 AMAX2 

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

(m) (m) 

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

----- ----- 

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

Subgroup (6c) 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

 COMPLEX TERRAIN RECEPTOR INFORMATION 

 XRCT YRCT ZRCT XHH 

 (km) (km) (m) 

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

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

1 

 Description of Complex Terrain Variables: 

 XC, YC = Coordinates of center of hill 

 THETAH = 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 elevation 

 EXPO 1 = Hill-shape exponent for the major axis 

 EXPO 2 = Hill-shape exponent for the major axis 

 SCALE 1 = Horizontal length scale along the major axis 

 SCALE 2 = Horizontal length scale along the minor axis 

 AMAX = Maximum allowed axis length for the major axis 

 BMAX = Maximum allowed axis length for the major axis 

 XRCT, YRCT = Coordinates of the complex terrain receptors 

 ZRCT = 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 HENRY'S 

LAW COEFFICIENT 

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

(dimensionless) 

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

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

! SO2 = 0.1509, 1000., 8., 0., 

0.04 ! 

! NOX = 0.1656, 1., 8., 5., 

3.5 ! 

! HNO3 = 0.1628, 1., 18., 0., 

0.00000008 ! 

!END! 

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

INPUT GROUP: 8 -- Size parameters for dry deposition of particles 

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

 For SINGLE SPECIES, the mean and standard deviation are used to 

 compute a deposition velocity for NINT (see group 9) size-ranges, 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 and these are then averaged to obtain a mean deposition velocity. 

 For GROUPED SPECIES, the size distribution should be explicitly 

 specified (by the 'species' in the group), and the standard deviation 

 for each should be entered as 0. The model will then use the 

 deposition 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. ! 

! PMC = 2.0, 2.0 ! 

! PMF = 0.48, 2. ! 

! EC = 0.48, 2. ! 

! SOA = 0.48, 2. ! 

!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 to 

 evaluate 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 vegetation 

 IVEG=2 for active and stressed vegetation 

 IVEG=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 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

!END! 

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

INPUT GROUP: 11 -- Chemistry Parameters 

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

 Ozone data input option (MOZ) Default: 1 ! MOZ = 0 ! 

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

 0 = use a monthly background ozone value 

 1 = 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 = 31.00, 31.00, 31.00, 37.00, 37.00, 37.00, 33.00, 33.00, 33.00, 27.00, 27.00, 27.00 

! 

 Monthly ammonia concentrations 

 (Used only if MCHEM = 1, or 3) 

 (BCKNH3) in ppb Default: 12*10. 

 ! BCKNH3 = 12*3.9 ! 

 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 value 

 1 = 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 * 

 ! BCKH2O2 = 0.50, 0.50, 0.50, 2.30, 2.30, 2.30, 3.50, 3.50, 3.50, 0.80, 0.80, 0.80 ! 

 --- 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 computing 

 the 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 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 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 .15 

 VCNX 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 .5 

 OFRAC .25 .25 .30 .30 .30 .30 .30 .30 .30 .30 .30 .25 

 VCNX 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 .20 

 VCNX 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 .25 

 VCNX 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 .20 

 VCNX 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 .30 

 VCNX 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, 50.00, 

50.00 ! 

!END! 

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

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

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

 Horizontal size of puff (m) beyond which 

 time-dependent dispersion equations (Heffter) 

 are used to determine sigma-y and 

 sigma-z (SYTDEP) Default: 550. ! SYTDEP = 5.5E02 ! 

 Switch for using Heffter equation for sigma z 

 as above (0 = Not use Heffter; 1 = use Heffter 

 (MHFTSZ) Default: 0 ! MHFTSZ = 0 ! 

 Stability class used to determine plume 

 growth rates for puffs above the boundary 

 layer (JSUP) Default: 5 ! JSUP = 5 ! 

 Vertical dispersion constant for stable 

 conditions (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) 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 (CONK2) Default: 0.1 ! CONK2 = .1 ! 

 Factor for determining Transition-point from 

 Schulman-Scire to Huber-Snyder Building Downwash 

 scheme (SS used for Hs < Hb + TBD * HL) 

 (TBD) Default: 0.5 ! TBD = .5 ! 

 TBD < 0 ==> always use Huber-Snyder 

 TBD = 1.5 ==> always use Schulman-Scire 

 TBD = 0.5 ==> ISC Transition-point 

 Range of land use categories for which 

 urban 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) 

 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 or MTURBVW = 1 or 3) 

 (ISIGMAV) Default: 1 ! ISIGMAV = 1 ! 

 0 = read sigma-theta 

 1 = read sigma-v 

 Choice of mixing heights (Used only if METFM = 4) 

 (IMIXCTDM) Default: 0 ! IMIXCTDM = 0 ! 

 0 = read PREDICTED mixing heights 

 1 = 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 (in 

 grid units) during one sampling step 

 (XSAMLEN) Default: 1.0 ! XSAMLEN = 1.0 ! 

 Maximum Number of slugs/puffs release from 

 one source during one time step 

 (MXNEW) Default: 99 ! MXNEW = 99 ! 

 Maximum Number of sampling steps for 

 one puff/slug during one time step 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 (MXSAM) Default: 99 ! MXSAM = 99 ! 

 Number of iterations used when computing 

 the transport wind for a sampling step 

 that includes gradual rise (for CALMET 

 and 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 for each 

 stability class (m/s) 

 (SVMIN(6) and SWMIN(6)) Default SVMIN : .50, .50, .50, .50, .50, .50 

 Default SWMIN : .20, .12, .08, .06, .03, .016 

 Stability Class : A B C D E F 

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

 ! SVMIN = 0.500, 0.500, 0.500, 0.500, 0.500, 0.500! 

 ! SWMIN = 0.200, 0.120, 0.080, 0.060, 0.030, 0.016! 

 Divergence criterion for dw/dz across puff 

 used to initiate adjustment for horizontal 

 convergence (1/s) 

 Partial adjustment starts at CDIV(1), and 

 full adjustment is reached at CDIV(2) 

 (CDIV(2)) Default: 0.0,0.0 ! CDIV = .0, .0 ! 

 Minimum wind speed (m/s) allowed for 

 non-calm conditions. Also used as minimum 

 speed returned when using power-law 

 extrapolation 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-law 

 exponents for stabilities 1-6 

 (PLX0(6)) Default : ISC RURAL values 

 ISC RURAL : .07, .07, .10, .15, .35, .55 

 ISC 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 gradient 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 for stable classes E, F (degK/m) 

 (PTG0(2)) Default: 0.020, 0.035 

 ! PTG0 = 0.020, 0.035 ! 

 Default plume path coefficients for 

 each stability class (used when option 

 for partial plume height terrain adjustment 

 is 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 factor 

 equal to sigma-y/length of slug 

 (SL2PF) Default: 10. ! SL2PF = 10.0 ! 

 Puff-splitting control variables ------------------------ 

 VERTICAL SPLIT 

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

 Number of puffs that result every time a puff 

 is split - nsplit=2 means that 1 puff splits 

 into 2 

 (NSPLIT) Default: 3 ! NSPLIT = 3 ! 

 Time(s) of a day when split puffs are eligible to 

 be split once again; this is typically set once 

 per 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 mixing 

 height (m) exceeds a minimum value 

 (ZISPLIT) Default: 100. ! ZISPLIT = 100.0 ! 

 Split is allowed only if ratio of last hour's 

 mixing ht to the maximum mixing ht experienced 

 by the puff is less than a maximum value (this 

 postpones a split until a nocturnal layer develops) 

 (ROLDMAX) Default: 0.25 ! ROLDMAX = 0.25 ! 

 HORIZONTAL SPLIT 

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

 Number of puffs that result every time a puff 

 is split - nsplith=5 means that 1 puff splits 

 into 5 

 (NSPLITH) Default: 5 ! NSPLITH = 5 ! 

 Minimum sigma-y (Grid Cells Units) of puff 

 before it may be split 

 (SYSPLITH) Default: 1.0 ! SYSPLITH = 1.0 ! 

 Minimum puff elongation rate (SYSPLITH/hr) due to 

 wind shear, before it may be split 

 (SHSPLITH) Default: 2. ! SHSPLITH = 2.0 ! 

 Minimum concentration (g/m^3) of each 

 species in puff before it may be split 

 Enter array of NSPEC values; if a single value is 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 entered, it will be used for ALL species 

 (CNSPLITH) Default: 1.0E-07 ! CNSPLITH = 1.0E-07 ! 

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

 Fractional convergence criterion for numerical SLUG 

 sampling integration 

 (EPSSLUG) Default: 1.0e-04 ! EPSSLUG = 1.0E-04 ! 

 Fractional convergence criterion for numerical AREA 

 source integration 

 (EPSAREA) Default: 1.0e-06 ! EPSAREA = 1.0E-06 ! 

 Trajectory step-length (m) used for numerical rise 

 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 height 

 at the release point if greater than this minimum. 

 (HTMINBC) Default: 500. ! HTMINBC = 500.0 ! 

 Search radius (in BC segment lengths) about a receptor for sampling 

 nearest BC puff. BC puffs are emitted with a spacing of one segment 

 length, so the search radius should be greater than 1. 

 (RSAMPBC) Default: 4. ! RSAMPBC = 10.0 ! 

 Near-Surface depletion adjustment to concentration profile used when 

 sampling BC puffs? 

 (MDEPBC) Default: 1 ! MDEPBC = 1 ! 

 0 = Concentration is NOT adjusted for depletion 

 1 = Adjust Concentration for depletion 

!END! 

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

INPUT GROUPS: 13a, 13b, 13c, 13d -- Point source parameters 

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

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

Subgroup (13a) 

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

 Number of point sources with 

 parameters provided below (NPT1) No default ! NPT1 = 1 ! 

 Units used for point source 

 emissions below (IPTU) Default: 1 ! IPTU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (13d) (NSPT1) Default: 0 ! NSPT1 = 0 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Number of point sources with 

 variable emission parameters 

 provided in external file (NPT2) No default ! NPT2 = 0 ! 

 (If NPT2 > 0, these point 

 source emissions are read from 

 the file: PTEMARB.DAT) 

!END! 

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

Subgroup (13b) 

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

 The following species are modeled: 

CSPEC = SO2 

CSPEC = SO4 

CSPEC = NOX 

CSPEC = HNO3 

CSPEC = NO3 

CSPEC = PMC 

CSPEC = PMF 

CSPEC = EC 

CSPEC = SOA 

 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 = P1 ! 

 1 ! X = 695.75, 507.2100, 88.390,216.46, 2.600, 20.0, 445.0, .0, 

 208.0E00, 8.23, 68.1E00, 0.0E00, 0.0E00, 0.37, 0.43, 0.02, 2.06 ! 

 1 ! FMFAC = 1.0 ! !END! 

-------- 

 a 

 Data for each source are treated as a separate input subgroup 

 and 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.) 

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

 the effect of rain-caps or other physical configurations that 

 reduce momentum rise associated with the actual exit velocity. 

 (Default: 1.0 -- full momentum used) 

 b 

 0. = No building downwash modeled, 1. = downwash modeled 

 NOTE: must be entered as a REAL number (i.e., with decimal point) 

 c 

 An emission rate must be entered for every pollutant modeled. 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 Enter emission rate of zero for secondary pollutants that are 

 modeled, 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 

 MBDW=2 (PRIME downwash option) 

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

-------- 

 a 

 Building height, width, length, and X/Y offset from the source are treated 

 as a separate input subgroup for each source and therefore must end with 

 an input group terminator. The X/Y offset is the position, relative to the 

 stack, of the center of the upwind face of the projected building, with the 

 x-axis pointing along the flow direction. 

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

Subgroup (13d) 

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

 a 

 POINT SOURCE: VARIABLE EMISSIONS DATA 

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

 Use this subgroup to describe temporal variations in the emission 

 rates given in 13b. Factors entered multiply the rates in 13b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use PTEMARB.DAT and NPT2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

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

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

Subgroup (14a) 

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

 Number of polygon area sources with 

 parameters specified below (NAR1) No default ! NAR1 = 0 ! 

 Units used for area source 

 emissions below (IARU) Default: 1 ! IARU = 1 ! 

 1 = g/m**2/s 

 2 = kg/m**2/hr 

 3 = lb/m**2/hr 

 4 = tons/m**2/yr 

 5 = Odour Unit * m/s (vol. flux/m**2 of odour compound) 

 6 = Odour Unit * m/min 

 7 = metric tons/m**2/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (14d) (NSAR1) Default: 0 ! NSAR1 = 0 ! 

 Number of buoyant polygon area sources 

 with variable location and emission 

 parameters (NAR2) No default ! NAR2 = 0 ! 

 (If NAR2 > 0, ALL parameter data for 

 these 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 subgroup 

 and 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 are 

 modeled, 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 

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

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

-------- 

 a 

 Data for each source are treated as a separate input subgroup 

 and 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 emission 

 rates given in 14b. Factors entered multiply the rates in 14b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use BAEMARB.DAT and NAR2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (15a) 

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

 Number of buoyant line sources 

 with variable location and emission 

 parameters (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 source 

 emissions below (ILNU) Default: 1 ! ILNU = 1 ! 

 1 = g/s 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (15c) (NSLN1) Default: 0 ! NSLN1 = 0 ! 

 Maximum number of segments used to model 

 each line (MXNSEG) Default: 7 ! MXNSEG = 7 ! 

 The following variables are required only if NLINES > 0. They are 

 used in the buoyant line source plume rise calculations. 

 Number of distances at which Default: 6 ! NLRISE = 6 ! 

 transitional rise is computed 

 Average 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 

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

 a 

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 subgroup 

 and 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 are 

 modeled, but not emitted. Units are specified by ILNTU 

 (e.g. 1 for g/s). 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

Subgroup (15c) 

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

 a 

 BUOYANT LINE SOURCE: VARIABLE EMISSIONS DATA 

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

 Use this subgroup to describe temporal variations in the emission 

 rates 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 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (16a) 

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

 Number of volume sources with 

 parameters provided in 16b,c (NVL1) No default ! NVL1 = 0 ! 

 Units used for volume source 

 emissions below in 16b (IVLU) Default: 1 ! IVLU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (16c) (NSVL1) Default: 0 ! NSVL1 = 0 ! 

 Number of volume sources with 

 variable location and emission 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

 parameters (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 subgroup 

 and 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 are 

 modeled, 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 emission 

 rates given in 16b. Factors entered multiply the rates in 16b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use VOLEMARB.DAT and NVL2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

December 2010 
 Refined BART Modeling Protocol for 

 Thilmany Kaukauna Mill

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

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

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

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

Subgroup (17a) 

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

 Number of non-gridded receptors (NREC) No default ! NREC = 1995 ! 

!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) 

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

Note - three Class I areas 

Seney SENE = 173 receptors 

Isle Royal ISLE = 966 receptors 

Boundary Waters BOWA = 856 receptors 

total number of receptors is 1995 

ALL RECEPTOR COORDINATES FOLLOW IN INPUT FILE 

December 2010 
Updated CALPUFF Modeling 

Protocol and Final Report for the 

Subject to BART Analyses 

for Wausau Paper Mills, LLC 

Mosinee Mill 

Prepared by 

RTP Environmental Associates Inc. 

2031 Broadway, Suite 2 

Boulder, Colorado 80302 

December 2010 
Updated CALPUFF Modeling Protocol and Final Report for 

Wausau “Subject to BART” Analysis 

TABLE OF CONTENTS 

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

2.0 VISTAS BART Protocol ........................................................................................................ 5

3.0 CALMET Data and Procedures.............................................................................................. 7 

4.0 CALPUFF Procedures.......................................................................................................... 12 

5.0 POSTUTIL and CALPOST Procedures ............................................................................... 13 

6.0 Emissions Modeled............................................................................................................... 14 

7.0 Modeling Results.................................................................................................................. 16 

List of Figures

Figure 1 - WDNR Screening CALPUFF Domain .......................................................................... 2 

Figure 2 – Refined CALPUFF Modeling Domain and Locations of Class I Areas....................... 9 

Figure 3 – Locations of Observational Stations in Refined CALPUFF Modeling Domain......... 10 

Figure 4 – Land Use Data for Refined CALPUFF Modeling Domain......................................... 11 

List of Tables

Table 1 – WAUSAU Speciated PM Emissions............................................................................ 15 

Table 2 – WAUSAU CALPUFF BART Exemption Results Summary....................................... 17 

Appendix A – Example CALMET Input File 

Appendix B – Example CALPUFF Input File 

 i 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

1 December 2010 

1.0 Introduction 

The Wisconsin Department of Natural Resources (DNR) performed single source screening 

modeling in 2006 to evaluate which Best Available Retrofit Technology (BART) eligible sources 

in the state may “cause or contribute” to visibility impairment and could therefore be subject to 

BART requirements. This type of analysis is referred to as the “subject to BART” or “BART 

exemption” analysis. The methods used by DNR are described in the “Single Source Modeling to 

Support Regional Haze BART Modeling Protocol”, March 21, 2006, prepared by Lake Michigan

Air Directors Consortium (LADCO). 

DNR applied CALPUFF to each BART eligible source for three annual periods, covering the 

calendar years 2002 to 2004. The CALPUFF/CALMET modeling domain consisted of ninetyseven 36-km spaced cells in the east-west direction and ninety 36-km spaced cells in the northsouth direction (see Figure 1). Meteorological data generated by the MM5 prognostic weather 

model (provided by LADCO in CALMM5 format) was used to develop the meteorological data 

for CALPUFF, without additional observational data input (i.e., NOOBS mode). This represents 

a coarse meteorological grid, suitable for an initial screening analysis. 

The results from DNR’s screening analysis indicated that, with the exception of some of the 

largest electric power stations in the state, the only Class I areas where BART eligible sources 

may contribute to visibility impairment are the three areas to the north of Wisconsin, the 

Boundary Waters Canoe Area, Isle Royal National Park, and Seney Wildlife Area. DNR’s 

screening analysis also indicated that the BART eligible emissions unit at the Wausau Paper Mills 

LLC Mosinee Mill (Wausau) may “cause or contribute” to visibility impairment at the Seney 

Class I area (located approximately 320 km to the northeast of the mill), as defined by the 98th

percentile visibility impacts being greater than 0.5 deciviews (dv) relative to natural background. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

2 December 2010 

Figure 1 - WDNR Screening CALPUFF Domain 

NOTE: Class I areas are identified by red marks. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

3 December 2010 

Wausau has elected to refine the DNR screening analysis by conducting refined CALPUFF 

modeling with a 4 km meteorological grid, based on procedures described in the “Visibility 

Improvement – State and Tribal Association of the Southeast (VISTAS) BART CALPUFF” 

modeling protocol. The VISTAS protocol was developed by a large group of stakeholders, 

including EPA, the VISTAS member state agencies and tribes, the Federal Land Managers 

(FLMs), industry representatives, and consulting experts. Given the resources expended on the 

VISTAS protocol, it arguably represents the most comprehensive CALPUFF BART protocol ever 

developed. 

Wausau had discussions with DNR and EPA Region 5 staff about refining the analysis, and 

submitted a refined CALPUFF BART modeling protocol in March 2007. EPA reviewed the 

protocol and provided minor comments to DNR in May 2010. Another facility undergoing 

Subject to BART review, Thilmany, responded to these comments in a letter “Response to EPA 

Comments on Thilmany BART Modeling Protocol” dated November 9, 2010. In addition, 

subsequent to the EPA protocol comments, the US Fish and Wildlife Service and US Forest 

Service reviewed the protocol and had additional discussions with DNR and EPA. The three EPA 

comments, and each response, are listed below. 

Comment 1

Information needs to be presented which clarifies how POSTUTIL was used for ammonia. 

Response 1

The VISTAS methodology was used, with a MNITRATE switch setting of one (1). 

Comment 2

The modeling must include a copy of the input and list files associated with runs. The protocol 

only offers some of the control file information. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

4 December 2010 

Response 2

All CALMET, CALPUFF, and CALPOST input and list files, as well as meteorological and 

geophysical data files, had been provided by Wausau to DNR on a portable hard disk drive. 

Wausau will again provide a portable hard disk drive of all modeling files to DNR for the updated 

BART analysis, for purposes of SIP documentation. 

Comment 3

The input file ... uses the background ammonia values that were produced for the LADCO 

protocol. These values are based on modeled estimates. Monitoring data has generally shown 

much higher ammonia than what was used from the model results. The refined modeling 

analyses ... must evaluate the visibility impacts using measured background ammonia values. 

Response 3

The US Fish and Wildlife Service proposed using a constant background ammonia concentration 

of 3.9 ppb, which was the highest concentration measured at the Mayville Wisconsin station 

during a mid-1990s EPA study. Wausau has agreed to use this single, conservative background 

value in the absence of daily data. 

On November 29, 2010, DNR issued a letter that approved the CALPUFF BART protocol, as 

well as the emission rates to be used for the BART eligible emission units. DNR requested that 

the 2007 version of the protocol be updated to include the responses to EPA comments, and text 

that addresses current CALPUFF modeling guidance. In addition, the updated modeling results 

could be presented in the protocol (so that all information is located in one document). 

This document is the updated modeling protocol and final modeling report for the refined Wausau 

“Subject to BART” analysis. This document does not duplicate the extensive information on 

visibility, CALPUFF, and EPA guidance on BART modeling procedures that are contained in the 

VISTAS protocol. Rather, this document describes how data specific to this setting will be used 

in the refined CALPUFF modeling. Section 1 of the protocol is this introduction. Section 2 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

5 December 2010 

briefly summarizes important concepts from the VISTAS protocol. Section 3 describes the 

specific CALMET data and procedures that were used to develop a refined, 4-km spaced 

meteorological grid for Wisconsin. Section 4 describes the CALPUFF input data and procedures, 

and Section 5 discusses the POSTUTIL and CALPOST processing, including the use of annual 

average natural background visibility. Section 6 presents the emission and stack data that were 

used for the BART eligible emission units, and Section 7 presents the modeling results. 

Appendices A and B present example CALMET and CALPUFF input file listings. A portable 

hard drive is also being submitted that contains all input data, control files, output files, and 

computer codes used in the analysis.

2.0 VISTAS BART Protocol 

The VISTAS member states have prepared a CALPUFF modeling protocol for BART 

determinations that is fully consistent with the EPA guidelines in 40 CFR Part 51 Appendix W

and Appendix Y. The VISTAS protocol describes a two-step CALPUFF analysis methodology 

for BART exemption analyses. The initial CALPUFF analysis uses a “screening” or coarse 

resolution meteorological grid to determine if a particular source may be exempted from further 

BART analyses. The screening results are also used to determine which Class I areas should be 

included in any refined analysis. Assumptions for the initial screening analysis are conservative 

so that a source that contributes to visibility impairment is not exempted in error. If a source is 

shown to contribute to visibility impairment using the initial screening assessment, the source has

the option to undertake refined CALPUFF modeling using finer meteorological grids to evaluate 

further whether it is subject to BART. 

VISTAS developed both coarse (12-km grid resolution) and refined (4-km grid resolution) 

CALMET files. The fine grid CALMET files utilized both MM5 prognostic data, as well as 

meteorological observational data for the CALMET “Step 2” calculations. Overwater (buoy) data 

were used in addition to the standard hourly surface meteorological observations, precipitation 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

6 December 2010 

observations, and twice-daily upper air sounding data. The VISTAS website provides detailed 

documentation and supporting information on the refined CALMET processing, including the 

CALMET and CALPUFF input files that contain model configuration options and settings that 

have been optimized after consultation with stakeholders and consulting experts. These same

CALMET and CALPUFF input files were used as the basis for the refined Wisconsin analyses. 

The VISTAS protocol discusses several options for defining the natural background visibility. 

These include use of the annual average natural background extinction or the background 

extinction for the 20% best natural conditions days. Based on an email survey of the state 

agencies from the VISTAS member states, all of the VISTAS states allowed the use of annual 

average natural background extinction for refined CALPUFF analyses. This is also the guidance 

provided by EPA Region 5 staff during discussions with DNR and the Wisconsin Paper Council, 

and the method approved by DNR in their November 29, 2010 letter. Therefore, the refined 

Wausau CALPUFF modeling used the annual average natural background extinction for 

CALPOST processing. 

The VISTAS BART guidance recommends that the threshold value used to define whether a 

source “contributes” to visibility impairment is a 0.5 dv change from natural background 

conditions. The 98th

 percentile 24-hr average predicted impact at the Class I area (equal to the 8th

highest value) is to be compared to this contribution threshold value. According to clarification 

of the BART guidance received from EPA by the VISTAS workgroup, for a three-year simulation 

the modeling values to be compared with the threshold are the greatest of the three annual 8th

highest values, or the 22nd highest value over all three years combined, whichever is greater. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

7 December 2010 

3.0 CALMET Data and Procedures 

EPA has updated the versions of the approved CALPUFF programs since the 2007 modeling 

protocol was developed, and has provided additional guidance on CALMET “switch” settings. 

The current approved versions are CALPUFF version 5.8 (level 070623), and CALMET version 

5.8 (level 070623), and these versions were used for the updated refined BART CALPUFF 

analysis. On August 31, 2009, EPA published the memorandum “Clarification of EPA-FLM 

Recommended Settings for CALMET”. EPA stated that a 4 km fine CALMET grid size was 

acceptable, and provided recommended CALMET settings. The CALMET settings for the 

updated refined BART CALPUFF analysis meet all current EPA recommendations. 

The first step in development of the refined Wisconsin analysis was to define the CALMET 

refined modeling domain and grid. As discussed in Section 1, DNR’s screening analysis 

indicated that there are three Class I areas to the north of Wisconsin, the Boundary Waters Canoe 

Area, Isle Royal National Park, and Seney Wildlife Area, where the screening analysis predicts 

some level of visibility impact from Wisconsin BART eligible sources. Therefore, the 

meteorological grid was developed to ensure coverage for these three Class I areas, as well as for 

the BART eligible source locations throughout Wisconsin. Standard IWAQM guidance also 

recommends that the CALMET grid extend a minimum of 50 km beyond any Class I or emission 

source location, so that puff recirculation can be properly accounted for. 

The refined CALMET grid was defined as a 4-km spaced grid with 162 cells in the X-axis and 

191 in the Y-axis. The grid projection was Lambert Conformal Conic, using the same projection 

parameters as in the DNR screening analysis (this allows the use of the same source X and Y 

coordinates as in the DNR analysis). The projection parameters include RLAT0 = 40N, RLON0 

= 97W, XLAT1 = 33N, XLAT2 = 45N, XORIGKM = 247.0, YORIGKM = 240.0, and DATUM 

= NAS-C. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

8 December 2010 

The meteorological data that was input to CALMET included the same three years (2002-2004) 

of CALMM5 data used by DNR, which was provided by LADCO. However, the refined 

CALMET runs also considered observation data from 22 surface stations, 16 precipitation 

stations, 5 overwater buoy stations, and 3 upper air stations. Figure 2 is a plot of the refined 

CALPUFF modeling domain. Figure 3 presents a plot of the locations of the observation stations 

in the modeling domain. 

The CAMET program MAKEGEO uses USGS GTOPO30 digital terrain data (which includes 

coverage in Canada) and USGS Composite Theme Grid Land Use and Land Cover (LULC) data 

to create a gridded data file on geophysical parameters that is used by CALMET. The available 

USGS LULC coverage does not extend into the Canadian areas of the refined domain. These 

areas in Canada were assigned to the “forested land” category. Figure 4 presents a plot of the 

land use data for the modeling domain. 

The VISTAS refined CALMET input files discussed in section 2 were used as the basis for the 

refined Wisconsin CALMET input files. The same CALMET configuration settings and options 

were utilized, as they are representative of Wisconsin terrain and land use patterns. All settings 

conform with current EPA and FLM guidance. 

Appendix A presents a listing of a CALMET input file developed for the refined analysis. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

9 December 2010 

Figure 2 – Refined CALPUFF Modeling Domain and Locations of Class I Areas 

NOTE: The Class I area receptors are in red, the Wausau Mill location is in blue, and the X and 

Y coordinates are the Lambert projection coordinates are in kms. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

10 December 2010 

Figure 3 – Locations of Observational Stations in Refined CALPUFF Modeling Domain 

300 400 500 600 700 800 900 1000

LCC East (km)

Wisconsin Refined CALMET

Location of Observation stations

300

400

500

600

700

800

900

1000

LCC N

orth (km)

MADI MILW

LAC

EAU 

GREE

MANI

WAUS STUR

MOSI CLIN

WISC

EAGL

MINE

HAYW

JUNE

DULT

MANI

SAWY

HOUG

IRNM ESCA

IRNW

MSUP

NMCH

ESUP

WSUP

SMCH

COPP

ESCA

HOUG

IRON

MANI

SAUL

CLIN

GREE

HAYW

LAC 

MADI

ME MARS NO

MILW

RAIN

MNNP GREE STURG

INTF

NOTES: Surface stations are in red, overwater (buoy) in blue, precipitation in green, and upper 

air in purple.
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

11 December 2010 

Figure 4 – Land Use Data for Refined CALPUFF Modeling Domain 

300 400 500 600 700 800

LCC East (km)

300

400

500

600

700

800

900

1000

LCC North (km)

Snow/Ice

Tundra

Barren

Wetland

Water

Forest

Range

Agriculture

Urban/Built-Up

Land Use

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

95

100

. .

. .

LCC Origin: 40N, 97W

Datum: NAS-C

Matching Parallels: 33N, 45N

False Easting: 0.0

False Northing: 0.0
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

12 December 2010 

Some of the notable CALMET configuration settings included: 

• CALMET vertical layers set to 10, with cell face heights at 20, 40, 80, 160, 320, 640, 

1200, 2000, 3000, and 4000 meters, 

• CALMET diagnostic options, including slope flow effects (ISLOPE = 1) with the radius 

of influence of terrain (TERRAD) set to 15 km, 

• EPA recommended CALMET settings for the radius of influence parameters (R1=50, 

R2=100, RMAX1=100, RMAX2=200, and RMAX3=200). 

4.0 CALPUFF Procedures 

Both the DNR screening and VISTAS refined CALPUFF input files were used as the basis for the 

refined Wisconsin CALPUFF input files. All CALPUFF settings and options are consistent with 

EPA and FLM guidance, and the refined VISTAS protocol recommendations. The background 

ozone (O3) concentrations were used directly from the DNR CALPUFF input files. Instead of 

using monthly background ammonia concentrations from the DNR screening analyses, a single 

conservative background ammonia concentration of 3.9 ppb was used. Appendix B presents a 

listing of a CALPUFF input file developed for the analysis. 

The DNR screening analysis considered three emitted pollutants, SO2, NOx, and PM2.5. The 

refined CALPUFF modeling will consider speciated particulate emissions, including coarse PM 

(PMC), fine PM equivalent to PM2.5 (PMF), sulfate (SO4), nitrate (NO3), elemental carbon (EC), 

and secondary organic aerosols (SOA or OC). Section 6 of this protocol describes how the 

speciated particulate emissions were calculated. 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

13 December 2010 

5.0 POSTUTIL and CALPOST Procedures 

In CALPUFF, the scavenging of the available ammonia for nitrate formation is computed on a 

puff-by-puff basis. Because of the possibility of multiple puff overlap, this approach may tend to 

overestimate the amount of ammonia available to form nitrate. In order to address the cumulative 

consumption of ammonia, the POSTUTIL program can be used to repartition nitric acid and 

nitrate. POSTUTIL calculates new NO3/HNO3 equilibrium concentrations for the sample source 

in the Class I area using the background ammonia. As recommended in the VISTAS procedures 

for refined CALPUFF modeling, the POSTUTIL “MNITRATE=1” method was used for the 

refined Wisconsin CALPUFF modeling. Instead of using the monthly values for background 

ammonia concentrations from the DNR screening analyses, a single conservative background 

ammonia concentration of 3.9 ppb was used. 

The modeling protocol submitted in 2007 proposed to use CALPOST Visibility Method 6 to 

calculate visibility impacts. However, since that time there have been revisions to CALPOST that 

allow the use of the updated IMPROVE extinction equation. CALPOST version 6.221 can 

implement the “Method 8 Mode 5” methodology to calculate visibility impacts, and the FLMs 

recommend its use in “Federal Land Managers’ Air Quality Related Values Work Group (FLAG) 

Phase I Report—Revised (2010)” (herein referred to as FLAG 2010). Therefore, this updated 

methodology will be used for the Wausau BART analysis. The new CALPUFF Graphical Users 

Interface automatically enters the appropriate values, based on the Class I area being selected, for 

natural background species and relative humidity adjustment factors using the data in Tables 6 

through 9 of Section 3.3.5 of FLAG 2010 (which are based on “Guidance for Estimating Natural 

Visibility Conditions Under the Regional Haze Rule”, EPA-454/B-03-005, September 2003). 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

14 December 2010 

 

6.0 Emissions Modeled 

EPA’s BART modeling guidance state that the 24-hr maximum actual emissions rates for the 

period of the modeling simulation (2002-2004) should be used for the analysis. If this data is not 

available, then the short term “allowable” or “potential” emission rates should be used. Wausau 

provided DNR with source information that has been reviewed to determine the 24-hr maximum 

actual emissions rates. 

There are a number of BART eligible emission units at the Wausau Mosinee mill. Stack S10 is a 

combined stack for the 3 boilers that are the primary source of the BART pollutants, and the 

recovery boiler (B21) vents to stack S11. In addition, although the BART eligibility is in 

question for some smaller emissions sources (the lime kiln, smelt tank, and slaker), these units 

were also included in the modeling to be conservative. Based on discussions between RMT 

(Wausau Paper’s consultant) and DNR on December 7 and 9, 2010, it was agreed to use PTE 

emissions for all emission units, as listed in Table 1. Note that the PTE for S10 was adjusted to 

reflect fuel oil usage limitations as specified in the air permit. The PM emissions have been 

speciated using the information for coal and oil fired boilers developed by the National Park 

Service1

. 

1 http://www2.nature.nps.gov/air/permits/ect/index.cfm) 
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

15 December 2010 

Table 1 – Wausau Emissions (in units of g/sec) 

Unit SO2 NOx PM PMC PMF EC SO4 SOA

S10 143.1 28.1 11.68 1.16 2.39 0.09 6.43 1.61

S11 13.1 5.4 2.32 0.73 1.26 0.10 0.19 0.04

S12 0.4 0.0 0.43 0.00 0.43 0.00 0.00 0.00

S52 0.0 0.0 0.43 0.00 0.43 0.00 0.00 0.00

S53 1.4 0.9 0.62 0.32 0.19 0.01 0.10 0.00

Total 158.0 34.4 15.5 2.2 4.7 0.2 6.7 1.7
 Updated BART Modeling Protocol and Report for 

 Wausau Mosinee Mill

16 December 2010 

7.0 Modeling Results 

CALPOST computes the daily maximum change in deciviews relative to the annual average 

natural background visibility, separately for each Class I area. For evaluating the source impact 

relative to the “Subject to BART” visibility impact threshold of 0.5 dv, the daily maximum

changes in visibility are sorted to determine the 98th percentile (8th

 highest) value for each of 

three years, and the 98th percentile (22nd highest) value for the completed three year period. If all 

98th percentile values are below the threshold of 0.5 dv based on the refined CALPUFF analysis, 

the source is exempt from the BART requirements. 

Another equivalent metric commonly used for BART exemption modeling is to sum the number 

of days per year that are above the 0.5 dv threshold for each Class I area separately; if there are 7 

or fewer days above the threshold for each year, then the 98th

 percentile value is also below the 

threshold. This is the metric approved by DNR for use in the BART modeling analysis. 

Specifically, for each Class I area separately, if there are less than 8 days per year that the 

predicted visibility impacts are greater than 0.5 deciviews relative to the annual average natural 

background visibility, then the BART eligible emission units at the modeled facility will be 

determined not to be Subject to BART. 

Table 2 presents the results from the refined CALPUFF BART exemption modeling. These 

results demonstrate that there are less than 8 days per year, at each individual Class I area, when 

the visibility impacts from the Wausau mill BART eligible emission unit are above 0.5 dv. 

Therefore, the Wausau mill BART eligible sources are not Subject to BART requirements. 
Updated BART Modeling Protocol an

Wausau M

Table 2 – Wausau CALPUFF BART Exemption Results Summary 

Class I area Distance 

(km) from 

source to

Class I area 

boundary

# of days 

with impact

> 0.5 dv in 

Class I area:

2002

# of days with

impact > 0.5 

dv in Class I 

area: 2003

# of days 

with impact

> 0.5 dv in 

Class I area:

2004

# of days with

impact > 0.5 

dv in Class I 

area for 3 year

period

Maximum 98th

Percentile 

impact over 

either annual 

or 3-yr periods

Seney , MI ~ 320 0 0 1 1 0.20Isle Royal, MN ~ 340 0 0 0 0 0.15Boundary Waters, MN ~ 360 2 0 0 2 0.13

17 D
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

Appendix A – Example CALMET Input File 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

WI Refined CALMET - 4km Grid - Dec 2010 - with Updated EPA Settings 

---------------- Run title (3 lines) ------------------------------------------ 

 CALMET MODEL CONTROL FILE 

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

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

INPUT GROUP: 0 -- Input and Output File Names 

Subgroup (a) 

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

Default Name Type File Name 

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

GEO.DAT input ! GEODAT=geo.dat ! 

SURF.DAT input ! SRFDAT=SURF02Z.DAT ! 

CLOUD.DAT input * CLDDAT= * 

PRECIP.DAT input ! PRCDAT=PRECIP02.DAT ! 

MM4.DAT input * MM4DAT=E:\MRPO-calmm5\2002\MM5.020102.3D.DAT * 

MM4.DAT input ! MM4DAT=E:\MRPO-calmm5\2002\020102.MM5 ! 

WT.DAT input * WTDAT= * 

CALMET.LST output ! METLST=cal020102.lST ! 

CALMET.DAT output ! METDAT=E:\WI-Calmet\2002Output\cal020102.dat ! 

PACOUT.DAT output * PACDAT= * 

All file names will be converted to lower case if LCFILES = T 

Otherwise, if LCFILES = F, file names will be converted to UPPER CASE 

 T = lower case ! LCFILES = T ! 

 F = UPPER CASE 

NUMBER OF UPPER AIR & OVERWATER STATIONS: 

 Number of upper air stations (NUSTA) No default ! NUSTA = 3 ! 

 Number of overwater met stations 

 (NOWSTA) No default ! NOWSTA = 5 ! 

 !END! 

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

Subgroup (b) 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

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

Upper air files (one per station) 

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

Default Name Type File Name 

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

UP1.DAT input 1 ! UPDAT=UPGB0204.DAT! !END! 

UP2.DAT input 2 ! UPDAT=UPMN0204.DAT! !END! 

UP3.DAT input 3 ! UPDAT=UPIN0204.DAT! !END! 

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

Subgroup (c) 

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

Overwater station files (one per station) 

SEA1.DAT input 1 ! SEADAT=4500102.DAT! !END! 

SEA2.DAT input 2 ! SEADAT=4500202.DAT! !END! 

SEA3.DAT input 3 ! SEADAT=4500402.DAT! !END! 

SEA4.DAT input 4 ! SEADAT=4500602.DAT! !END! 

SEA5.DAT input 5 ! SEADAT=4500702.DAT! !END! 

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

Default Name Type File Name 

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

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

Subgroup (d) 

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

Other file names 

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

Default Name Type File Name 

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

DIAG.DAT input * DIADAT= * 

PROG.DAT input * PRGDAT= * 

TEST.PRT output * TSTPRT= * 

TEST.OUT output * TSTOUT= * 

TEST.KIN output * TSTKIN= * 

TEST.FRD output * TSTFRD= * 

TEST.SLP output * TSTSLP= * 

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

NOTES: (1) File/path names can be up to 70 characters in length 

 (2) Subgroups (a) and (d) must have ONE 'END' (surround by 

 delimiters) at the end of the group 

 (3) Subgroups (b) and (c) must have an 'END' (surround by 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 delimiters) at the end of EACH LINE 

 !END! 

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

INPUT GROUP: 1 -- General run control parameters 

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

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

 Month (IBMO) -- No default ! IBMO= 1 ! 

 Day (IBDY) -- No default ! IBDY= 2 ! 

 Hour (IBHR) -- No default ! IBHR= 0 ! 

 Base time zone (IBTZ) -- No default ! IBTZ= 6 ! 

 PST = 08, MST = 07 

 CST = 06, EST = 05 

 Length of run (hours) (IRLG) -- No default ! IRLG= 24 ! 

 Run type (IRTYPE) -- Default: 1 ! IRTYPE= 1 ! 

 0 = Computes wind fields only 

 1 = Computes wind fields and micrometeorological variables 

 (u*, w*, L, zi, etc.) 

 (IRTYPE must be 1 to run CALPUFF or CALGRID) 

 Compute special data fields required 

 by CALGRID (i.e., 3-D fields of W wind 

 components and temperature) 

 in additional to regular Default: T ! LCALGRD = T ! 

 fields ? (LCALGRD) 

 (LCALGRD must be T to run CALGRID) 

 Flag to stop run after 

 SETUP phase (ITEST) Default: 2 ! ITEST= 2 ! 

 (Used to allow checking 

 of the model inputs, files, etc.) 

 ITEST = 1 - STOPS program after SETUP phase 

 ITEST = 2 - Continues with execution of 

 COMPUTATIONAL phase after SETUP 

 Test options specified to see if 

 they conform to regulatory 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 values? (MREG) No Default ! MREG = 1 ! 

 0 = NO checks are made 

 1 = Technical options must conform to USEPA guidance 

 IMIXH -1 Maul-Carson convective mixing height 

 over land; OCD mixing height overwater 

 ICOARE 0 OCD deltaT method for overwater fluxes 

 THRESHL 0.0 Threshold buoyancy flux over land needed 

 to sustain convective mixing height grow 

!END! 

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

INPUT GROUP: 2 -- Map Projection and Grid control parameters 

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

 Projection for all (X,Y): 

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

 Map projection 

 (PMAP) Default: UTM ! PMAP = LCC ! 

 UTM : Universal Transverse Mercator 

 TTM : Tangential Transverse Mercator 

 LCC : Lambert Conformal Conic 

 PS : Polar Stereographic 

 EM : 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 = -999 ! 

 Hemisphere for UTM projection? 

 (Used only if PMAP=UTM) 

 (UTMHEM) Default: N ! UTMHEM = N ! 

 N : Northern hemisphere projection 

 S : Southern hemisphere projection 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 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 XLAT2 

 PS : 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, and 

 east or west longitude. For example, 

 35.9 N Latitude = 35.9N 

 118.7 E Longitude = 118.7E 

 Datum-region 

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

 The Datum-Region for the coordinates is identified by a character 

 string. Many mapping products currently available use the model of the 

 Earth known as the World Geodetic System 1984 (WGS-84). Other local 

 models may be in use, and their selection in CALMET will make its output 

 consistent with local mapping products. The list of Datum-Regions with 

 official transformation parameters is provided by the National Imagery and 

 Mapping Agency (NIMA). 

December 2010 
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 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, Sphere 

 ESR-S ESRI REFERENCE 6371KM Radius, Sphere 

 Datum-region for output coordinates 

 (DATUM) Default: WGS-84 ! DATUM = NAS-C ! 

 Horizontal grid definition: 

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

 Rectangular grid defined for projection PMAP, 

 with X the Easting and Y the Northing coordinate 

 No. X grid cells (NX) No default ! NX = 162 ! 

 No. Y grid cells (NY) No default ! NY = 191 ! 

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

 Units: km 

 Reference grid coordinate of 

 SOUTHWEST corner of grid cell (1,1) 

 X coordinate (XORIGKM) No default ! XORIGKM = 247.000 ! 

 Y coordinate (YORIGKM) No default ! YORIGKM = 240.000 ! 

 Units: km 

 Vertical grid definition: 

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

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

 Cell face heights in arbitrary 

 vertical grid (ZFACE(NZ+1)) No defaults 

 Units: m 

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

!END! 

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

INPUT GROUP: 3 -- Output Options 

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

 DISK OUTPUT OPTION 

 Save met. fields in an unformatted 

 output file ? (LSAVE) Default: T ! LSAVE = T ! 

 (F = Do not save, T = Save) 

 Type of unformatted output file: 

 (IFORMO) Default: 1 ! IFORMO = 1 ! 

 1 = CALPUFF/CALGRID type file (CALMET.DAT) 

 2 = MESOPUFF-II type file (PACOUT.DAT) 

 LINE PRINTER OUTPUT OPTIONS: 

 Print met. fields ? (LPRINT) Default: F ! LPRINT = T ! 

 (F = Do not print, T = Print) 

 (NOTE: parameters below control which 

 met. variables are printed) 

 Print interval 

 (IPRINF) in hours Default: 1 ! IPRINF = 1 ! 

 (Meteorological fields are printed 

 every 1 hours) 

 Specify which layers of U, V wind component 

 to print (IUVOUT(NZ)) -- NOTE: NZ values must be entered 

 (0=Do not print, 1=Print) 

 (used only if LPRINT=T) Defaults: NZ*0 

 ! IUVOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

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

 Specify which levels of the W wind component to print 

 (NOTE: W defined at TOP cell face -- 16 values) 

 (IWOUT(NZ)) -- NOTE: NZ values must be entered 

December 2010 
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 (0=Do not print, 1=Print) 

 (used only if LPRINT=T & LCALGRD=T) 

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

 Defaults: NZ*0 

 ! IWOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Specify which levels of the 3-D temperature field to print 

 (ITOUT(NZ)) -- NOTE: NZ values must be entered 

 (0=Do not print, 1=Print) 

 (used only if LPRINT=T & LCALGRD=T) 

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

 Defaults: NZ*0 

 ! ITOUT = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Specify which meteorological fields 

 to print 

 (used only if LPRINT=T) Defaults: 0 (all variables) 

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

 Variable Print ? 

 (0 = do not print, 

 1 = print) 

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

 ! STABILITY = 0 ! - PGT stability class 

 ! USTAR = 0 ! - Friction velocity 

 ! MONIN = 0 ! - Monin-Obukhov length 

 ! MIXHT = 0 ! - Mixing height 

 ! WSTAR = 0 ! - Convective velocity scale 

 ! PRECIP = 0 ! - Precipitation rate 

 ! SENSHEAT = 0 ! - Sensible heat flux 

 ! CONVZI = 0 ! - Convective mixing ht. 

 Testing and debug print options for micrometeorological module 

 Print input meteorological data and 

 internal variables (LDB) Default: F ! LDB = F ! 

 (F = Do not print, T = print) 

 (NOTE: this option produces large amounts of output) 

 First time step for which debug data 

December 2010 
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 are printed (NN1) Default: 1 ! NN1 = 1 ! 

 Last time step for which debug data 

 are printed (NN2) Default: 1 ! NN2 = 2 ! 

 Testing and debug print options for wind field module 

 (all of the following print options control output to 

 wind field module's output files: TEST.PRT, TEST.OUT, 

 TEST.KIN, TEST.FRD, and TEST.SLP) 

 Control variable for writing the test/debug 

 wind fields to disk files (IOUTD) 

 (0=Do not write, 1=write) Default: 0 ! IOUTD = 0 ! 

 Number of levels, starting at the surface, 

 to print (NZPRN2) Default: 1 ! NZPRN2 = 1 ! 

 Print the INTERPOLATED wind components ? 

 (IPR0) (0=no, 1=yes) Default: 0 ! IPR0 = 0 ! 

 Print the TERRAIN ADJUSTED surface wind 

 components ? 

 (IPR1) (0=no, 1=yes) Default: 0 ! IPR1 = 0 ! 

 Print the SMOOTHED wind components and 

 the INITIAL DIVERGENCE fields ? 

 (IPR2) (0=no, 1=yes) Default: 0 ! IPR2 = 0 ! 

 Print the FINAL wind speed and direction 

 fields ? 

 (IPR3) (0=no, 1=yes) Default: 0 ! IPR3 = 0 ! 

 Print the FINAL DIVERGENCE fields ? 

 (IPR4) (0=no, 1=yes) Default: 0 ! IPR4 = 0 ! 

 Print the winds after KINEMATIC effects 

 are added ? 

 (IPR5) (0=no, 1=yes) Default: 0 ! IPR5 = 0 ! 

 Print the winds after the FROUDE NUMBER 

 adjustment is made ? 

 (IPR6) (0=no, 1=yes) Default: 0 ! IPR6 = 0 ! 

December 2010 
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 Print the winds after SLOPE FLOWS 

 are added ? 

 (IPR7) (0=no, 1=yes) Default: 0 ! IPR7 = 0 ! 

 Print the FINAL wind field components ? 

 (IPR8) (0=no, 1=yes) Default: 0 ! IPR8 = 0 ! 

!END! 

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

INPUT GROUP: 4 -- Meteorological data options 

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

 NO OBSERVATION MODE (NOOBS) Default: 0 ! NOOBS = 0 ! 

 0 = Use surface, overwater, and upper air stations 

 1 = Use surface and overwater stations (no upper air observations) 

 Use MM5 for upper air data 

 2 = No surface, overwater, or upper air observations 

 Use MM5 for surface, overwater, and upper air data 

 NUMBER OF SURFACE & PRECIP. METEOROLOGICAL STATIONS 

 Number of surface stations (NSSTA) No default ! NSSTA = 22 ! 

 Number of precipitation stations 

 (NPSTA=-1: flag for use of MM5 precip data) 

 (NPSTA) No default ! NPSTA = 16 ! 

 CLOUD DATA OPTIONS 

 Gridded cloud fields: 

 (ICLOUD) Default: 0 ! ICLOUD = 0 ! 

 ICLOUD = 0 - Gridded clouds not used 

 ICLOUD = 1 - Gridded CLOUD.DAT generated as OUTPUT 

 ICLOUD = 2 - Gridded CLOUD.DAT read as INPUT 

 ICLOUD = 3 - Gridded cloud cover from Prognostic Rel. Humidity 

 FILE FORMATS 

 Surface meteorological data file format 

 (IFORMS) Default: 2 ! IFORMS = 2 ! 

 (1 = unformatted (e.g., SMERGE output)) 

 (2 = formatted (free-formatted user input)) 

December 2010 
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 Precipitation data file format 

 (IFORMP) Default: 2 ! IFORMP = 2 ! 

 (1 = unformatted (e.g., PMERGE output)) 

 (2 = formatted (free-formatted user input)) 

 Cloud data file format 

 (IFORMC) Default: 2 ! IFORMC = 2 ! 

 (1 = unformatted - CALMET unformatted output) 

 (2 = formatted - free-formatted CALMET output or user input) 

!END! 

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

INPUT GROUP: 5 -- Wind Field Options and Parameters 

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

 WIND FIELD MODEL OPTIONS 

 Model selection variable (IWFCOD) Default: 1 ! IWFCOD = 1 ! 

 0 = Objective analysis only 

 1 = Diagnostic wind module 

 Compute Froude number adjustment 

 effects ? (IFRADJ) Default: 1 ! IFRADJ = 1 ! 

 (0 = NO, 1 = YES) 

 Compute kinematic effects ? (IKINE) Default: 0 ! IKINE = 0 ! 

 (0 = NO, 1 = YES) 

 Use O'Brien procedure for adjustment 

 of the vertical velocity ? (IOBR) Default: 0 ! IOBR = 0 ! 

 (0 = NO, 1 = YES) 

 Compute slope flow effects ? (ISLOPE) Default: 1 ! ISLOPE = 1 ! 

 (0 = NO, 1 = YES) 

 Extrapolate surface wind observations 

 to upper layers ? (IEXTRP) Default: -4 ! IEXTRP = -4 ! 

 (1 = no extrapolation is done, 

 2 = power law extrapolation used, 

 3 = user input multiplicative factors 

December 2010 
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 for layers 2 - NZ used (see FEXTRP array) 

 4 = similarity theory used 

 -1, -2, -3, -4 = same as above except layer 1 data 

 at upper air stations are ignored 

 Extrapolate surface winds even 

 if calm? (ICALM) Default: 0 ! ICALM = 0 ! 

 (0 = NO, 1 = YES) 

 Layer-dependent biases modifying the weights of 

 surface and upper air stations (BIAS(NZ)) 

 -1<=BIAS<=1 

 Negative BIAS reduces the weight of upper air stations 

 (e.g. BIAS=-0.1 reduces the weight of upper air stations 

 by 10%; BIAS= -1, reduces their weight by 100 %) 

 Positive BIAS reduces the weight of surface stations 

 (e.g. BIAS= 0.2 reduces the weight of surface stations 

 by 20%; BIAS=1 reduces their weight by 100%) 

 Zero BIAS leaves weights unchanged (1/R**2 interpolation) 

 Default: NZ*0 

 ! BIAS = 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 , 0 ! 

 Minimum distance from nearest upper air station 

 to surface station for which extrapolation 

 of surface winds at surface station will be allowed 

 (RMIN2: Set to -1 for IEXTRP = 4 or other situations 

 where all surface stations should be extrapolated) 

 Default: 4. ! RMIN2 = -1.0 ! 

 Use gridded prognostic wind field model 

 output fields as input to the diagnostic 

 wind field model (IPROG) Default: 0 ! IPROG = 14 ! 

 (0 = No, [IWFCOD = 0 or 1] 

 1 = Yes, use CSUMM prog. winds as Step 1 field, [IWFCOD = 0] 

 2 = Yes, use CSUMM prog. winds as initial guess field [IWFCOD = 1] 

 3 = Yes, use winds from MM4.DAT file as Step 1 field [IWFCOD = 0] 

 4 = Yes, use winds from MM4.DAT file as initial guess field [IWFCOD = 1] 

 5 = Yes, use winds from MM4.DAT file as observations [IWFCOD = 1] 

 13 = Yes, use winds from MM5.DAT file as Step 1 field [IWFCOD = 0] 

 14 = Yes, use winds from MM5.DAT file as initial guess field [IWFCOD = 1] 

 15 = Yes, use winds from MM5.DAT file as observations [IWFCOD = 1] 

 Timestep (hours) of the prognostic 

 model input data (ISTEPPG) Default: 1 ! ISTEPPG = 1 ! 

December 2010 
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 RADIUS OF INFLUENCE PARAMETERS 

 Use varying radius of influence Default: F ! LVARY = F! 

 (if no stations are found within RMAX1,RMAX2, 

 or RMAX3, then the closest station will be used) 

 Maximum radius of influence over land 

 in the surface layer (RMAX1) No default ! RMAX1 = 100. ! 

 Units: km 

 Maximum radius of influence over land 

 aloft (RMAX2) No default ! RMAX2 = 200. ! 

 Units: km 

 Maximum radius of influence over water 

 (RMAX3) No default ! RMAX3 = 200. ! 

 Units: km 

 OTHER WIND FIELD INPUT PARAMETERS 

 Minimum radius of influence used in 

 the wind field interpolation (RMIN) Default: 0.1 ! RMIN = 0.1 ! 

 Units: km 

 Radius of influence of terrain 

 features (TERRAD) No default ! TERRAD = 15. ! 

 Units: km 

 Relative weighting of the first 

 guess field and observations in the 

 SURFACE layer (R1) No default ! R1 = 50. ! 

 (R1 is the distance from an Units: km 

 observational station at which the 

 observation and first guess field are 

 equally weighted) 

 Relative weighting of the first 

 guess field and observations in the 

 layers ALOFT (R2) No default ! R2 =100. ! 

 (R2 is applied in the upper layers Units: km 

 in the same manner as R1 is used in 

 the surface layer). 

 Relative weighting parameter of the 

 prognostic wind field data (RPROG) No default ! RPROG = 0. ! 

December 2010 
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 Wausau Mosinee Mill

 (Used only if IPROG = 1) Units: km 

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

 Maximum acceptable divergence in the 

 divergence minimization procedure 

 (DIVLIM) Default: 5.E-6 ! DIVLIM= 5.0E-06 ! 

 Maximum number of iterations in the 

 divergence min. procedure (NITER) Default: 50 ! NITER = 50 ! 

 Number of passes in the smoothing 

 procedure (NSMTH(NZ)) 

 NOTE: NZ values must be entered 

 Default: 2,(mxnz-1)*4 ! NSMTH = 

 2 , 4 , 4 , 4 , 4 , 4 , 4 , 4 , 4 , 4 ! 

 Maximum number of stations used in 

 each layer for the interpolation of 

 data to a grid point (NINTR2(NZ)) 

 NOTE: NZ values must be entered Default: 99. ! NINTR2 = 

 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 , 99 ! 

 Critical Froude number (CRITFN) Default: 1.0 ! CRITFN = 1. ! 

 Empirical factor controlling the 

 influence of kinematic effects 

 (ALPHA) Default: 0.1 ! ALPHA = 0.1 ! 

 Multiplicative scaling factor for 

 extrapolation of surface observations 

 to upper layers (FEXTR2(NZ)) Default: NZ*0.0 

 ! FEXTR2 = 0., 0., 0., 0., 0., 0., 0., 0., 0., 0. ! 

 (Used only if IEXTRP = 3 or -3) 

 BARRIER INFORMATION 

 Number of barriers to interpolation 

 of the wind fields (NBAR) Default: 0 ! NBAR = 0 ! 

 THE FOLLOWING 4 VARIABLES ARE INCLUDED 

 ONLY IF NBAR > 0 

 NOTE: NBAR values must be entered No defaults 

 for each variable Units: km 

December 2010 
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 Wausau Mosinee Mill

 X coordinate of BEGINNING 

 of each barrier (XBBAR(NBAR)) ! XBBAR = 0. ! 

 Y coordinate of BEGINNING 

 of each barrier (YBBAR(NBAR)) ! YBBAR = 0. ! 

 X coordinate of ENDING 

 of each barrier (XEBAR(NBAR)) ! XEBAR = 0. ! 

 Y coordinate of ENDING 

 of each barrier (YEBAR(NBAR)) ! YEBAR = 0. ! 

 DIAGNOSTIC MODULE DATA INPUT OPTIONS 

 Surface temperature (IDIOPT1) Default: 0 ! IDIOPT1 = 0 ! 

 0 = Compute internally from 

 hourly surface observations 

 1 = Read preprocessed values from 

 a data file (DIAG.DAT) 

 Surface met. station to use for 

 the surface temperature (ISURFT) No default ! ISURFT = 1 ! 

 (Must be a value from 1 to NSSTA) 

 (Used only if IDIOPT1 = 0) 

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

 Domain-averaged temperature lapse 

 rate (IDIOPT2) Default: 0 ! IDIOPT2 = 0 ! 

 0 = Compute internally from 

 twice-daily upper air observations 

 1 = Read hourly preprocessed values 

 from a data file (DIAG.DAT) 

 Upper air station to use for 

 the domain-scale lapse rate (IUPT) No default ! IUPT = 1 ! 

 (Must be a value from 1 to NUSTA) 

 (Used only if IDIOPT2 = 0) 

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

 Depth through which the domain-scale 

 lapse rate is computed (ZUPT) Default: 200. ! ZUPT = 200. ! 

 (Used only if IDIOPT2 = 0) Units: meters 

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

December 2010 
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 Domain-averaged wind components 

 (IDIOPT3) Default: 0 ! IDIOPT3 = 0 ! 

 0 = Compute internally from 

 twice-daily upper air observations 

 1 = Read hourly preprocessed values 

 a data file (DIAG.DAT) 

 Upper air station to use for 

 the domain-scale winds (IUPWND) Default: -1 ! IUPWND = -1 ! 

 (Must be a value from -1 to NUSTA) 

 (Used only if IDIOPT3 = 0) 

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

 Bottom and top of layer through 

 which the domain-scale winds 

 are computed 

 (ZUPWND(1), ZUPWND(2)) Defaults: 1., 1000. ! ZUPWND= 1., 1000. ! 

 (Used only if IDIOPT3 = 0) Units: meters 

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

 Observed surface wind components 

 for wind field module (IDIOPT4) Default: 0 ! IDIOPT4 = 0 ! 

 0 = Read WS, WD from a surface 

 data file (SURF.DAT) 

 1 = Read hourly preprocessed U, V from 

 a data file (DIAG.DAT) 

 Observed upper air wind components 

 for wind field module (IDIOPT5) Default: 0 ! IDIOPT5 = 0 ! 

 0 = Read WS, WD from an upper 

 air data file (UP1.DAT, UP2.DAT, etc.) 

 1 = Read hourly preprocessed U, V from 

 a data file (DIAG.DAT) 

 LAKE BREEZE INFORMATION 

 Use Lake Breeze Module (LLBREZE) 

 Default: F ! LLBREZE = F ! 

 Number of lake breeze regions (NBOX) ! NBOX = 0 ! 

 X Grid line 1 defining the region of interest 

 ! XG1 = 0. ! 

 X Grid line 2 defining the region of interest 

December 2010 
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 Wausau Mosinee Mill

 ! XG2 = 0. ! 

 Y Grid line 1 defining the region of interest 

 ! YG1 = 0. ! 

 Y Grid line 2 defining the region of interest 

 ! YG2 = 0. ! 

 X Point defining the coastline (Straight line) 

 (XBCST) (KM) Default: none ! XBCST = 0. ! 

 Y Point defining the coastline (Straight line) 

 (YBCST) (KM) Default: none ! YBCST = 0. ! 

 X Point defining the coastline (Straight line) 

 (XECST) (KM) Default: none ! XECST = 0. ! 

 Y Point defining the coastline (Straight line) 

 (YECST) (KM) Default: none ! YECST = 0. ! 

 Number of stations in the region Default: none ! NLB = 0 ! 

 (Surface stations + upper air stations) 

 Station ID's in the region (METBXID(NLB)) 

 (Surface stations first, then upper air stations) 

 ! METBXID = 0 ! 

!END! 

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

INPUT GROUP: 6 -- Mixing Height, Temperature and Precipitation Parameters 

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

 EMPIRICAL MIXING HEIGHT CONSTANTS 

 Neutral, mechanical equation 

 (CONSTB) Default: 1.41 ! CONSTB = 1.41 ! 

 Convective mixing ht. equation 

 (CONSTE) Default: 0.15 ! CONSTE = 0.15 ! 

 Stable mixing ht. equation 

 (CONSTN) Default: 2400. ! CONSTN = 2400.! 

 Overwater mixing ht. equation 

 (CONSTW) Default: 0.16 ! CONSTW = 0.16 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 Absolute value of Coriolis 

 parameter (FCORIOL) Default: 1.E-4 ! FCORIOL = 1.0E-04! 

 Units: (1/s) 

 SPATIAL AVERAGING OF MIXING HEIGHTS 

 Conduct spatial averaging 

 (IAVEZI) (0=no, 1=yes) Default: 1 ! IAVEZI = 1 ! 

 Max. search radius in averaging 

 process (MNMDAV) Default: 1 ! MNMDAV = 1 ! 

 Units: Grid 

 cells 

 Half-angle of upwind looking cone 

 for averaging (HAFANG) Default: 30. ! HAFANG = 30. ! 

 Units: deg. 

 Layer of winds used in upwind 

 averaging (ILEVZI) Default: 1 ! ILEVZI = 1 ! 

 (must be between 1 and NZ) 

 CONVECTIVE MIXING HEIGHT OPTIONS: 

 Method to compute the convective 

 mixing height(IMIHXH) Default: 1 ! IMIXH = -1 ! 

 1: Maul-Carson for land and water cells 

 -1: Maul-Carson for land cells only - 

 OCD mixing height overwater 

 2: Batchvarova and Gryning for land and water cells 

 -2: Batchvarova and Gryning for land cells only 

 OCD mixing height overwater 

 Threshold buoyancy flux required to 

 sustain convective mixing height growth 

 overland (THRESHL) Default: 0.05 ! THRESHL = 0.00 ! 

 (expressed as a heat flux units: W/m3 

 per meter of boundary layer) 

 Threshold buoyancy flux required to 

 sustain convective mixing height growth 

 overwater (THRESHW) Default: 0.05 ! THRESHW = 0.05 ! 

 (expressed as a heat flux units: W/m3 

 per meter of boundary layer) 

 Option for overwater lapse rates used 

 in convective mixing height growth 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 (ITWPROG) Default: 0 ! ITWPROG = 0 ! 

 0 : use SEA.DAT lapse rates and deltaT (or assume neutral 

 conditions if missing) 

 1 : use prognostic lapse rates (only if IPROG>2) 

 and SEA.DAT deltaT (or neutral if missing) 

 2 : use prognostic lapse rates and prognostic delta T 

 (only if iprog>12 and 3D.DAT version# 2.0 or higher) 

 Land Use category ocean in 3D.DAT datasets 

 (ILUOC3D) Default: 16 ! ILUOC3D = 16 ! 

 Note: if 3D.DAT from MM5 version 3.0, iluoc3d = 16 

 if MM4.DAT, typically iluoc3d = 7 

 OTHER MIXING HEIGHT VARIABLES 

 Minimum potential temperature lapse 

 rate in the stable layer above the 

 current convective mixing ht. Default: 0.001 ! DPTMIN = 0.001 ! 

 (DPTMIN) Units: deg. K/m 

 Depth of layer above current conv. 

 mixing height through which lapse Default: 200. ! DZZI = 200. ! 

 rate is computed (DZZI) Units: meters 

 Minimum overland mixing height Default: 50. ! ZIMIN = 50. ! 

 (ZIMIN) Units: meters 

 Maximum overland mixing height Default: 3000. ! ZIMAX = 3000. ! 

 (ZIMAX) Units: meters 

 Minimum overwater mixing height Default: 50. ! ZIMINW = 50. ! 

 (ZIMINW) -- (Not used if observed Units: meters 

 overwater mixing hts. are used) 

 Maximum overwater mixing height Default: 3000. ! ZIMAXW = 3000. ! 

 (ZIMAXW) -- (Not used if observed Units: meters 

 overwater mixing hts. are used) 

 OVERWATER SURFACE FLUXES METHOD and PARAMETERS 

 (ICOARE) Default: 10 ! ICOARE = 0 ! 

 0: original deltaT method (OCD) 

 10: COARE with no wave parameterization (jwave=0, Charnock) 

 11: COARE with wave option jwave=1 (Oost et al.) 

 and default wave properties 

 -11: COARE with wave option jwave=1 (Oost et al.) 

 and observed wave properties (must be in SEA.DAT files) 

 12: COARE with wave option 2 (Taylor and Yelland) 

 and default wave properties 

December 2010 
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 Wausau Mosinee Mill

 -12: COARE with wave option 2 (Taylor and Yelland) 

 and observed wave properties (must be in SEA.DAT files) 

 Coastal/Shallow water length scale (DSHELF) 

 (for modified z0 in shallow water) 

 ( COARE fluxes only) 

 Default : 0. ! DSHELF = 0. ! 

 units: km 

 COARE warm layer computation (IWARM) ! IWARM = 0 ! 

 1: on - 0: off (must be off if SST measured with 

 IR radiometer) Default: 0 

 COARE cool skin layer computation (ICOOL) ! ICOOL = 0 ! 

 1: on - 0: off (must be off if SST measured with 

 IR radiometer) Default: 0 

 TEMPERATURE PARAMETERS 

 3D temperature from observations or 

 from prognostic data? (ITPROG) Default:0 !ITPROG = 0 ! 

 0 = Use Surface and upper air stations 

 (only if NOOBS = 0) 

 1 = Use Surface stations (no upper air observations) 

 Use MM5 for upper air data 

 (only if NOOBS = 0,1) 

 2 = No surface or upper air observations 

 Use MM5 for surface and upper air data 

 (only if NOOBS = 0,1,2) 

 Interpolation type 

 (1 = 1/R ; 2 = 1/R**2) Default:1 ! IRAD = 1 ! 

 Radius of influence for temperature 

 interpolation (TRADKM) Default: 500. ! TRADKM = 500. ! 

 Units: km 

 Maximum Number of stations to include 

 in temperature interpolation (NUMTS) Default: 5 ! NUMTS = 5 ! 

 Conduct spatial averaging of temp- 

 eratures (IAVET) (0=no, 1=yes) Default: 1 ! IAVET = 1 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 (will use mixing ht MNMDAV,HAFANG 

 so make sure they are correct) 

 Default temperature gradient Default: -.0098 ! TGDEFB = -0.0098 ! 

 below the mixing height over 

 water (K/m) (TGDEFB) 

 Default temperature gradient Default: -.0045 ! TGDEFA = -0.0045 ! 

 above the mixing height over 

 water (K/m) (TGDEFA) 

 Beginning (JWAT1) and ending (JWAT2) 

 land use categories for temperature ! JWAT1 = 55 ! 

 interpolation over water -- Make ! JWAT2 = 55 ! 

 bigger than largest land use to disable 

 PRECIP INTERPOLATION PARAMETERS 

 Method of interpolation (NFLAGP) Default = 2 ! NFLAGP = 2 ! 

 (1=1/R,2=1/R**2,3=EXP/R**2) 

 Radius of Influence (km) (SIGMAP) Default = 100.0 ! SIGMAP = 100. ! 

 (0.0 => use half dist. btwn 

 nearest stns w & w/out 

 precip when NFLAGP = 3) 

 Minimum Precip. Rate Cutoff (mm/hr) Default = 0.01 ! CUTP = 0.01 ! 

 (values < CUTP = 0.0 mm/hr) 

!END! 

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

INPUT GROUP: 7 -- Surface meteorological station parameters 

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

 SURFACE STATION VARIABLES 

 (One record per station -- 0 records in all) 

 1 2 

 Name ID X coord. Y coord. Time Anem. 

 (km) (km) zone Ht.(m) 

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

! SS1 ='MILW' 26400 739.061 363.200 6 10 ! 

! SS2 ='MADI' 26410 619.927 372.210 6 10 ! 

December 2010 
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 Wausau Mosinee Mill

! SS3 ='LA C' 26430 461.012 442.705 6 10 ! 

! SS4 ='EAU ' 26435 435.857 552.352 6 10 ! 

! SS5 ='GREE' 26450 703.911 530.179 6 10 ! 

! SS6 ='MANI' 26455 743.477 495.113 6 10 ! 

! SS7 ='STUR' 26458 755.730 576.760 6 10 ! 

! SS8 ='WAUS' 26463 581.202 568.247 6 10 ! 

! SS9 ='MOSI' 26465 579.307 552.489 6 10 ! 

! SS10 ='CLIN' 26502 655.019 541.168 6 10 ! 

! SS11 ='WISC' 26503 582.532 412.498 6 10 ! 

! SS12 ='EAGL' 26504 599.980 682.545 6 10 ! 

! SS13 ='MINE' 26507 550.817 338.941 6 10 ! 

! SS14 ='HAYW' 26508 430.347 681.295 6 10 ! 

! SS15 ='JUNE' 26509 669.429 409.931 6 10 ! 

! SS16 ='dulu' 27450 366.011 766.977 6 10 ! 

! SS17 ='MANI' 25408 838.315 711.433 5 10 ! 

! SS18 ='SAWY' 26284 741.237 743.078 5 10 ! 

! SS19 ='HOUG' 26380 977.905 549.977 5 10 ! 

! SS20 ='ESCA' 26480 775.417 679.550 5 10 ! 

! SS21 ='IRNM' 27437 690.168 678.511 5 10 ! 

! SS22 ='IRNW' 27445 528.314 743.857 5 10 ! 

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Five digit integer for station ID 

!END! 

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

INPUT GROUP: 8 -- Upper air meteorological station parameters 

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

 UPPER AIR STATION VARIABLES 

 (One record per station -- 0 records in all) 

 1 2 

 Name ID X coord. Y coord. Time zone 

 (km) (km) 

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

! US1 ='GREE' 14898 703.911 539.179 6 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

! US2 ='MNNP' 94983 272.681 539.843 6 ! 

! US3 ='INTF' 14918 269.489 957.416 6 ! 

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Five digit integer for station ID 

!END! 

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

INPUT GROUP: 9 -- Precipitation station parameters 

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

 PRECIPITATION STATION VARIABLES 

 (One record per station -- 0 records in all) 

 (NOT INCLUDED IF NPSTA = 0) 

 1 2 

 Name Station X coord. Y coord. 

 Code (km) (km) 

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

! PS1 ='COPP' 201780 719.681 845.179 ! 

! PS2 ='ESCA' 202626 779.850 646.454 ! 

! PS3 ='HOUG' 203936 1001.500 536.427 ! 

! PS4 ='IRON' 204090 699.421 640.283 ! 

! PS5 ='MANI' 205073 845.933 667.499 ! 

! PS6 ='SAUL' 207366 985.172 765.448 ! 

! PS7 ='CLIN' 471667 696.889 290.151 ! 

! PS8 ='GREE' 473269 709.933 509.579 ! 

! PS9 ='HAYW' 473511 442.947 678.728 ! 

! PS10 ='LAC ' 474370 471.515 404.495 ! 

! PS11 ='MADI' 474961 631.719 367.656 ! 

! PS12 ='MARS' 475120 550.348 505.662 ! 

! PS13 ='MENO' 475335 431.807 514.277 ! 

! PS14 ='MILW' 475479 772.567 324.344 ! 

! PS15 ='RAIN' 476939 599.369 634.460 ! 

! PS16 ='STURG' 478267 776.964 542.174 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

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

 1 

 Four character string for station name 

 (MUST START IN COLUMN 9) 

 2 

 Six digit station code composed of state 

 code (first 2 digits) and station ID (last 

 4 digits) 

!END!

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

Appendix B – Example CALPUFF Input File 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

Example BART Modeling 

2010 Updated BART Modeling for Wausau, WI - 

Using Refined 4km CALMET Data File and SENE, ISLE, BOWA Class I Receptors 

---------------- 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 =WausuaRef02.lst ! 

CONC.DAT output ! CONDAT =wausuaRef02.dat ! 

DFLX.DAT output * DFDAT = * 

WFLX.DAT output * WFDAT = * 

VISB.DAT output * VISDAT =wausua02DNR.VIB * 

RESTARTE.DAT output * RSTARTE= * 

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

Emission Files 

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

PTEMARB.DAT input * PTDAT = * 

VOLEMARB.DAT input * VOLDAT = * 

BAEMARB.DAT input * ARDAT = * 

LNEMARB.DAT input * LNDAT = * 

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

Other Files 

----------- 

OZONE.DAT input * OZDAT = * 

VD.DAT input * VDDAT = * 

CHEM.DAT input * CHEMDAT= * 

H2O2.DAT input * H2O2DAT= * 

HILL.DAT input * HILDAT= * 

HILLRCT.DAT input * RCTDAT= * 

COASTLN.DAT input * CSTDAT= * 

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 = T 

Otherwise, 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 length 

Provision for multiple input files 

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

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 Number of CALMET.DAT files for run (NMETDAT) 

 Default: 1 ! NMETDAT = 364 ! 

 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=e:\WI-Calmet\2002output\cal020102.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020103.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020104.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020105.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020106.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020107.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020108.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020109.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020110.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020111.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020112.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020113.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020114.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020115.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020116.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020117.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020118.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020119.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020120.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020121.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020122.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020123.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020124.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020125.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020126.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020127.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020128.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020129.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020130.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020131.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020201.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020202.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020203.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020204.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020205.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020206.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020207.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020208.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020209.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020210.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020211.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020212.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020213.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020214.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020215.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020216.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020217.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020218.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020219.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020220.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020221.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020222.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020223.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020224.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020225.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020226.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020227.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020228.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020301.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020302.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020303.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020304.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020305.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020306.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020307.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020308.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020309.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020310.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020311.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020312.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020313.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020314.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020315.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020316.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020317.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020318.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020319.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020320.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020321.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020322.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020323.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020324.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020325.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020326.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020327.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020328.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020329.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020330.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020331.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020401.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020402.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020403.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020404.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020405.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020406.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020407.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020408.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020409.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020410.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020411.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020412.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020413.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020414.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020415.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020416.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020417.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020418.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020419.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020420.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020421.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020422.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020423.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020424.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020425.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020426.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020427.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020428.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020429.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020430.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020501.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020502.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020503.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020504.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020505.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020506.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020507.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020508.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020509.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020510.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020511.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020512.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020513.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020514.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020515.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020516.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020517.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020518.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020519.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020520.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020521.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020522.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020523.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020524.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020525.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020526.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020527.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020528.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020529.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020530.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020531.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020601.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020602.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020603.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020604.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020605.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020606.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020607.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020608.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020609.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020610.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020611.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020612.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020613.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020614.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020615.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020616.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020617.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020618.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020619.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020620.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020621.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020622.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020623.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020624.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020625.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020626.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020627.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020628.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020629.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020630.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020701.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020702.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020703.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020704.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020705.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020706.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020707.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020708.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020709.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020710.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020711.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020712.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020713.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020714.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020715.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020716.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020717.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020718.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020719.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020720.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020721.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020722.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020723.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020724.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020725.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020726.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020727.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020728.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020729.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020730.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020731.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020801.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020802.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020803.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020804.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020805.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020806.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020807.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020808.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020809.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020810.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020811.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020812.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020813.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020814.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020815.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020816.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020817.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020818.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020819.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020820.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020821.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020822.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020823.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020824.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020825.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020826.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal020827.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020828.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020829.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020830.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020831.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020901.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020902.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020903.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020904.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020905.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020906.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020907.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020908.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020909.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020910.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020911.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020912.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020913.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020914.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020915.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020916.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020917.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020918.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020919.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020920.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020921.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020922.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020923.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020924.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020925.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020926.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020927.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020928.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020929.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal020930.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021001.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021002.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021003.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021004.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021005.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021006.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021007.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021008.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021009.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021010.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021011.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021012.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021013.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021014.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021015.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021016.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021017.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021018.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021019.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021020.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021021.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021022.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021023.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021024.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021025.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021026.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021027.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021028.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021029.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021030.DAT ! !END! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 none input ! METDAT=e:\WI-Calmet\2002output\cal021031.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021101.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021102.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021103.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021104.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021105.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021106.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021107.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021108.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021109.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021110.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021111.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021112.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021113.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021114.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021115.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021116.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021117.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021118.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021119.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021120.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021121.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021122.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021123.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021124.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021125.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021126.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021127.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021128.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021129.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021130.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021201.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021202.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021203.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021204.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021205.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021206.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021207.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021208.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021209.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021210.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021211.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021212.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021213.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021214.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021215.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021216.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021217.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021218.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021219.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021220.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021221.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021222.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021223.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021224.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021225.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021226.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021227.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021228.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021229.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021230.DAT ! !END! 

 none input ! METDAT=e:\WI-Calmet\2002output\cal021231.DAT ! !END! 

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

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

INPUT GROUP: 1 -- General run control parameters 

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

 Option to run all periods found 

 in the met. file (METRUN) Default: 0 ! METRUN = 0 ! 

 METRUN = 0 - Run period explicitly defined below 

 METRUN = 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 = 02 ! 

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

 Base time zone (XBTZ) -- No default ! XBTZ = 6.0 ! 

 PST = 8., MST = 7. 

 CST = 6., EST = 5. 

 Length of run (hours) (IRLG) -- No default ! IRLG = 8736 ! 

 Number of chemical species (NSPEC) 

 Default: 5 ! NSPEC = 9 ! 

 Number of chemical species 

 to be emitted (NSE) Default: 3 ! NSE = 7 ! 

 Flag to stop run after 

 SETUP phase (ITEST) Default: 2 ! ITEST = 2 ! 

 (Used to allow checking 

 of the model inputs, files, etc.) 

 ITEST = 1 - STOPS program after SETUP phase 

 ITEST = 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 file 

 1 = Read a restart file at the beginning of 

 the run 

 2 = Write a restart file during run 

 3 = Read a restart file at beginning of run 

 and write a restart file during run 

 Number of periods in Restart 

 output 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) 

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

 Averaging Time (minutes) (AVET) 

 Default: 60.0 ! AVET = 60. ! 

 PG Averaging Time (minutes) (PGTIME) 

 Default: 60.0 ! PGTIME = 60. ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

!END! 

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

INPUT GROUP: 2 -- Technical options 

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

 Vertical distribution used in the 

 near field (MGAUSS) Default: 1 ! MGAUSS = 1 ! 

 0 = uniform 

 1 = Gaussian 

 Terrain adjustment method 

 (MCTADJ) Default: 3 ! MCTADJ = 3 ! 

 0 = no adjustment 

 1 = ISC-type of terrain adjustment 

 2 = simple, CALPUFF-type of terrain 

 adjustment 

 3 = partial plume path adjustment 

 Subgrid-scale complex terrain 

 flag (MCTSG) Default: 0 ! MCTSG = 0 ! 

 0 = not modeled 

 1 = modeled 

 Near-field puffs modeled as 

 elongated 0 (MSLUG) Default: 0 ! MSLUG = 0 ! 

 0 = no 

 1 = 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 building 

 downwash? (MBDW) Default: 1 ! MBDW = 1 ! 

 1 = ISC method 

 2 = PRIME method 

 Vertical wind shear modeled above 

 stack 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 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 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 = no 

 1 = yes 

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

 0 = no 

 1 = yes 

 (dry deposition method specified 

 for each species in Input Group 3) 

 Method used to compute dispersion 

 coefficients (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 in 

 urban 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 

 MDISP = 3, described above. MDISP = 5 assumes that 

 measured values are read 

 Sigma-v/sigma-theta, sigma-w measurements used? (MTURBVW) 

 (Used only if MDISP = 1 or 5) Default: 3 ! MTURBVW = 3 ! 

 1 = use sigma-v or sigma-theta measurements 

 from PROFILE.DAT to compute sigma-y 

 (valid for METFM = 1, 2, 3, 4) 

 2 = use sigma-w measurements 

 from PROFILE.DAT to compute sigma-z 

 (valid for METFM = 1, 2, 3, 4) 

 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) 

 4 = use sigma-theta measurements 

 from PLMMET.DAT to compute sigma-y 

 (valid only if METFM = 3) 

 Back-up method used to compute dispersion 

 when measured turbulence data are 

 missing (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 in 

 urban areas 

 4 = same as 3 except PG coefficients computed using 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 the MESOPUFF II eqns. 

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

 (MROUGH) 

 0 = no 

 1 = yes 

 Partial plume penetration of Default: 1 ! MPARTL = 1 ! 

 elevated inversion? 

 (MPARTL) 

 0 = no 

 1 = 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 = no 

 1 = yes 

 Sub-Grid TIBL module used for shore line? 

 Default: 0 ! MSGTIBL = 0 ! 

 (MSGTIBL) 

 0 = no 

 1 = yes 

 Boundary conditions (concentration) modeled? 

 Default: 0 ! MBCON = 0 ! 

 (MBCON) 

 0 = no 

 1 = yes, using formatted BCON.DAT file 

 2 = yes, using unformatted CONC.DAT file 

 Analyses of fogging and icing impacts due to emissions from 

 arrays of mechanically-forced cooling towers can be performed 

 using CALPUFF in conjunction with a cooling tower emissions 

 processor (CTEMISS) and its associated postprocessors. Hourly 

 emissions of water vapor and temperature from each cooling tower 

 cell are computed for the current cell configuration and ambient 

 conditions by CTEMISS. CALPUFF models the dispersion of these 

 emissions and provides cloud information in a specialized format 

 for 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 = no 

 1 = yes - report results in PLUME Mode format 

 2 = yes - report results in RECEPTOR Mode format 

 TEST options specified to see if 

 they conform to regulatory 

 values? (MREG) Default: 1 ! MREG = 0 ! 

 0 = NO checks are made 

 1 = Technical options must conform to USEPA 

 Long Range Transport (LRT) guidance 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 METFM 1 or 2 

 AVET 60. (min) 

 PGTIME 60. (min) 

 MGAUSS 1 

 MCTADJ 3 

 MTRANS 1 

 MTIP 1 

 MCHEM 1 or 3 (if modeling SOx, NOx) 

 MWET 1 

 MDRY 1 

 MDISP 2 or 3 

 MPDF 0 if MDISP=3 

 1 if MDISP=2 

 MROUGH 0 

 MPARTL 1 

 SYTDEP 550. (m) 

 MHFTSZ 0 

!END! 

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

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

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

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

Subgroup (3a) 

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

 The following species are modeled: 

 The following species are modeled: 

! CSPEC = SO2 ! !END! 

! CSPEC = SO4 ! !END! 

! CSPEC = NOX ! !END! 

! CSPEC = HNO3 ! !END! 

! CSPEC = NO3 ! !END! 

! CSPEC = PMC ! !END! 

! CSPEC = PMF ! !END! 

! CSPEC = EC ! !END! 

! CSPEC = SOA ! !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 ! 

! PMC = 1, 1, 2, 0 ! 

! PMF = 1, 1, 2, 0 ! 

! EC = 1, 1, 2, 0 ! 

! SOA = 1, 1, 2, 0 ! 

!END! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

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

Subgroup (3b) 

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

 The following names are used for Species-Groups in which results 

 for certain species are combined (added) prior to output. The 

 CGRUP name will be used as the species name in output files. 

 Use this feature to model specific particle-size distributions 

 by 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 Mercator 

 TTM : Tangential Transverse Mercator 

 LCC : Lambert Conformal Conic 

 PS : Polar Stereographic 

 EM : 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 

 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 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 (XLAT2) No Default ! XLAT2 = 45N ! 

 LCC : Projection cone slices through Earth's surface at XLAT1 and XLAT2 

 PS : 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, and 

 east or west longitude. For example, 

 35.9 N Latitude = 35.9N 

 118.7 E Longitude = 118.7E 

 Datum-region 

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

 The Datum-Region for the coordinates is identified by a character 

 string. Many mapping products currently available use the model of the 

 Earth known as the World Geodetic System 1984 (WGS-84). Other local 

 models may be in use, and their selection in CALMET will make its output 

 consistent with local mapping products. The list of Datum-Regions with 

 official transformation parameters is provided by the National Imagery and 

 Mapping 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, Sphere 

 ESR-S ESRI REFERENCE 6371KM Radius, Sphere 

 Datum-region for output coordinates 

 (DATUM) Default: WGS-84 ! DATUM = NAS-C ! 

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 = 162 ! 

 No. Y grid cells (NY) No default ! NY = 191 ! 

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

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

 Units: km 

 Cell face heights in arbitrary 

 vertical grid (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 = 247. ! 

 Y coordinate (YORIGKM) No default ! YORIGKM = 240. ! 

 Units: km 

COMPUTATIONAL Grid: 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 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 the 

 computational 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 = 1 ! 

 (1 <= IBCOMP <= NX) 

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

 (1 <= JBCOMP <= NY) 

 X index of UR corner (IECOMP) No default ! IECOMP = 162 ! 

 (1 <= IECOMP <= NX) 

 Y index of UR corner (JECOMP) No default ! JECOMP = 191 ! 

 (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 the 

 sampling grid is at grid point (IESAMP, JESAMP) of the MET. grid. 

 The sampling grid must be identical to or a subset of the computational 

 grid. It may be a nested grid inside the computational grid. 

 The grid spacing of the sampling grid is DGRIDKM/MESHDN. 

 Logical flag indicating if gridded 

 receptors 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 = 162 ! 

 (IBCOMP <= IESAMP <= IECOMP) 

 Y index of UR corner (JESAMP) No default ! JESAMP = 191 ! 

 (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 

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

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 Concentrations (ICON) 1 ! ICON = 1 ! 

 Dry Fluxes (IDRY) 1 ! IDRY = 0 ! 

 Wet Fluxes (IWET) 1 ! IWET = 0 ! 

 Relative Humidity (IVIS) 1 ! IVIS = 0 ! 

 (relative humidity file is 

 required for visibility 

 analysis) 

 Use data compression option in output file? 

 (LCOMPRS) Default: T ! LCOMPRS = T ! 

 * 

 0 = Do not create file, 1 = create file 

 DIAGNOSTIC MASS FLUX OUTPUT OPTIONS: 

 Mass flux across specified boundaries 

 for selected species reported hourly? 

 (IMFLX) Default: 0 ! IMFLX = 0 ! 

 0 = no 

 1 = yes (FLUXBDY.DAT and MASSFLX.DAT filenames 

 are specified in Input Group 0) 

 Mass balance for each species 

 reported hourly? 

 (IMBAL) Default: 0 ! IMBAL = 0 ! 

 0 = no 

 1 = 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/s 

 2 = mg/m**3 mg/m**2/s 

 3 = ug/m**3 ug/m**2/s 

 4 = ng/m**3 ng/m**2/s 

 5 = Odour Units 

 Messages tracking progress of run 

 written to the screen ? 

 (IMESG) Default: 2 ! IMESG = 2 ! 

 0 = no 

 1 = yes (advection step, puff ID) 

 2 = yes (YYYYJJJHH, # old puffs, # emitted puffs) 

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

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

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

-- MASS FLUX -- 

 SPECIES 

 /GROUP PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? PRINTED? SAVED ON DISK? 

SAVED ON DISK? 

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

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

! SO2 = 0, 1, 0, 0, 0, 0, 

0 ! 

! SO4 = 0, 1, 0, 0, 0, 0, 

0 ! 

! NOX = 0, 1, 0, 0, 0, 0, 

0 ! 

! HNO3 = 0, 1, 0, 0, 0, 0, 

0 ! 

! NO3 = 0, 1, 0, 0, 0, 0, 

0 ! 

! PMC = 0, 1, 0, 0, 0, 0, 

0 ! 

! PMF = 0, 1, 0, 0, 0, 0, 

0 ! 

! EC = 0, 1, 0, 0, 0, 0, 

0 ! 

! SOA = 0, 1, 0, 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 = 1 ! 

 Met. period to start output 

 (NN1) Default: 1 ! NN1 = 1 ! 

 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 terrain 

 receptors (NCTREC) Default: 0 ! NCTREC = 0 ! 

 Terrain and CTSG Receptor data for 

 CTSG hills input in CTDM format ? 

 (MHILL) No Default ! MHILL = 2 ! 

 1 = Hill and Receptor data created 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 by CTDM processors & read from 

 HILL.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 = 1. ! 

 to meters (MHILL=1) 

 Factor to convert vertical dimensions Default: 1.0 ! ZHILL2M = 1. ! 

 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 SCALE 2 

AMAX1 AMAX2 

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

 XC, YC = Coordinates of center of hill 

 THETAH = 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 elevation 

 EXPO 1 = Hill-shape exponent for the major axis 

 EXPO 2 = Hill-shape exponent for the major axis 

 SCALE 1 = Horizontal length scale along the major axis 

 SCALE 2 = Horizontal length scale along the minor axis 

 AMAX = Maximum allowed axis length for the major axis 

 BMAX = Maximum allowed axis length for the major axis 

 XRCT, YRCT = Coordinates of the complex terrain receptors 

 ZRCT = Height of the ground (MSL) at the complex terrain 

 Receptor 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 NAME DIAMETER DEVIATION 

 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 HENRY'S 

LAW COEFFICIENT 

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

(dimensionless) 

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

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

! SO2 = 0.1509, 1000., 8., 0., 

0.04 ! 

! NOX = 0.1656, 1., 8., 5., 

3.5 ! 

! HNO3 = 0.1628, 1., 18., 0., 

0.00000008 ! 

!END! 

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

INPUT GROUP: 8 -- Size parameters for dry deposition of particles 

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

 For SINGLE SPECIES, the mean and standard deviation are used to 

 compute 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 explicitly 

 specified (by the 'species' in the group), and the standard deviation 

 for each should be entered as 0. The model will then use the 

 deposition velocity for the stated mean diameter. 

 SPECIES GEOMETRIC MASS MEAN GEOMETRIC STANDARD 

 (microns) (microns) 

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

! SO4 = 0.48, 2. ! 

! NO3 = 0.48, 2. ! 

! PMC = 2.0, 2.0 ! 

! PMF = 0.48, 2. ! 

! EC = 0.48, 2. ! 

! SOA = 0.48, 2. ! 

!END! 

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

INPUT GROUP: 9 -- Miscellaneous dry deposition parameters 

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

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 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 to 

 evaluate 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 vegetation 

 IVEG=2 for active and stressed vegetation 

 IVEG=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 ! 

!END! 

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

INPUT GROUP: 11 -- Chemistry Parameters 

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

 Ozone data input option (MOZ) Default: 1 ! MOZ = 0 ! 

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

 0 = use a monthly background ozone value 

 1 = 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 = 31.00, 31.00, 31.00, 37.00, 37.00, 37.00, 33.00, 33.00, 33.00, 27.00, 27.00, 27.00 

! 

 Monthly ammonia concentrations 

 (Used only if MCHEM = 1, or 3) 

 (BCKNH3) in ppb Default: 12*10. 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 ! BCKNH3 = 12*3.9 ! 

 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 value 

 1 = 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 * 

 ! BCKH2O2 = 0.50, 0.50, 0.50, 2.30, 2.30, 2.30, 3.50, 3.50, 3.50, 0.80, 0.80, 0.80 ! 

 --- 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 computing 

 the 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 .15 

 VCNX 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 .5 

 OFRAC .25 .25 .30 .30 .30 .30 .30 .30 .30 .30 .30 .25 

 VCNX 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 .20 

 VCNX 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 .25 

 VCNX 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 .20 

 VCNX 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. 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 OFRAC .30 .30 .35 .35 .35 .55 .55 .55 .35 .35 .35 .30 

 VCNX 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, 50.00, 

50.00 ! 

!END! 

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

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

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

 Horizontal size of puff (m) beyond which 

 time-dependent dispersion equations (Heffter) 

 are used to determine sigma-y and 

 sigma-z (SYTDEP) Default: 550. ! SYTDEP = 5.5E02 ! 

 Switch for using Heffter equation for sigma z 

 as above (0 = Not use Heffter; 1 = use Heffter 

 (MHFTSZ) Default: 0 ! MHFTSZ = 0 ! 

 Stability class used to determine plume 

 growth rates for puffs above the boundary 

 layer (JSUP) Default: 5 ! JSUP = 5 ! 

 Vertical dispersion constant for stable 

 conditions (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 from 

 Schulman-Scire to Huber-Snyder Building Downwash 

 scheme (SS used for Hs < Hb + TBD * HL) 

 (TBD) Default: 0.5 ! TBD = .5 ! 

 TBD < 0 ==> always use Huber-Snyder 

 TBD = 1.5 ==> always use Schulman-Scire 

 TBD = 0.5 ==> ISC Transition-point 

 Range of land use categories for which 

 urban 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) 

 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) 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 (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 or MTURBVW = 1 or 3) 

 (ISIGMAV) Default: 1 ! ISIGMAV = 1 ! 

 0 = read sigma-theta 

 1 = read sigma-v 

 Choice of mixing heights (Used only if METFM = 4) 

 (IMIXCTDM) Default: 0 ! IMIXCTDM = 0 ! 

 0 = read PREDICTED mixing heights 

 1 = 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 (in 

 grid units) during one sampling step 

 (XSAMLEN) Default: 1.0 ! XSAMLEN = 1.0 ! 

 Maximum Number of slugs/puffs release from 

 one source during one time step 

 (MXNEW) Default: 99 ! MXNEW = 99 ! 

 Maximum Number of sampling steps for 

 one puff/slug during one time step 

 (MXSAM) Default: 99 ! MXSAM = 99 ! 

 Number of iterations used when computing 

 the transport wind for a sampling step 

 that includes gradual rise (for CALMET 

 and 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 for each 

 stability class (m/s) 

 (SVMIN(6) and SWMIN(6)) Default SVMIN : .50, .50, .50, .50, .50, .50 

 Default SWMIN : .20, .12, .08, .06, .03, .016 

 Stability Class : A B C D E F 

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

 ! SVMIN = 0.500, 0.500, 0.500, 0.500, 0.500, 0.500! 

 ! SWMIN = 0.200, 0.120, 0.080, 0.060, 0.030, 0.016! 

 Divergence criterion for dw/dz across puff 

 used to initiate adjustment for horizontal 

 convergence (1/s) 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 Partial adjustment starts at CDIV(1), and 

 full adjustment is reached at CDIV(2) 

 (CDIV(2)) Default: 0.0,0.0 ! CDIV = .0, .0 ! 

 Minimum wind speed (m/s) allowed for 

 non-calm conditions. Also used as minimum 

 speed returned when using power-law 

 extrapolation 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-law 

 exponents for stabilities 1-6 

 (PLX0(6)) Default : ISC RURAL values 

 ISC RURAL : .07, .07, .10, .15, .35, .55 

 ISC 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 gradient 

 for stable classes E, F (degK/m) 

 (PTG0(2)) Default: 0.020, 0.035 

 ! PTG0 = 0.020, 0.035 ! 

 Default plume path coefficients for 

 each stability class (used when option 

 for partial plume height terrain adjustment 

 is 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 factor 

 equal to sigma-y/length of slug 

 (SL2PF) Default: 10. ! SL2PF = 10.0 ! 

 Puff-splitting control variables ------------------------ 

 VERTICAL SPLIT 

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

 Number of puffs that result every time a puff 

 is split - nsplit=2 means that 1 puff splits 

 into 2 

 (NSPLIT) Default: 3 ! NSPLIT = 3 ! 

 Time(s) of a day when split puffs are eligible to 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 be split once again; this is typically set once 

 per 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 mixing 

 height (m) exceeds a minimum value 

 (ZISPLIT) Default: 100. ! ZISPLIT = 100.0 ! 

 Split is allowed only if ratio of last hour's 

 mixing ht to the maximum mixing ht experienced 

 by the puff is less than a maximum value (this 

 postpones a split until a nocturnal layer develops) 

 (ROLDMAX) Default: 0.25 ! ROLDMAX = 0.25 ! 

 HORIZONTAL SPLIT 

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

 Number of puffs that result every time a puff 

 is split - nsplith=5 means that 1 puff splits 

 into 5 

 (NSPLITH) Default: 5 ! NSPLITH = 5 ! 

 Minimum sigma-y (Grid Cells Units) of puff 

 before it may be split 

 (SYSPLITH) Default: 1.0 ! SYSPLITH = 1.0 ! 

 Minimum puff elongation rate (SYSPLITH/hr) due to 

 wind shear, before it may be split 

 (SHSPLITH) Default: 2. ! SHSPLITH = 2.0 ! 

 Minimum concentration (g/m^3) of each 

 species in puff before it may be split 

 Enter array of NSPEC values; if a single value is 

 entered, it will be used for ALL species 

 (CNSPLITH) Default: 1.0E-07 ! CNSPLITH = 1.0E-07 ! 

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

 Fractional convergence criterion for numerical SLUG 

 sampling integration 

 (EPSSLUG) Default: 1.0e-04 ! EPSSLUG = 1.0E-04 ! 

 Fractional convergence criterion for numerical AREA 

 source integration 

 (EPSAREA) Default: 1.0e-06 ! EPSAREA = 1.0E-06 ! 

 Trajectory step-length (m) used for numerical rise 

 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 height 

 at the release point if greater than this minimum. 

 (HTMINBC) Default: 500. ! HTMINBC = 500.0 ! 

 Search radius (in BC segment lengths) about a receptor for sampling 

 nearest BC puff. BC puffs are emitted with a spacing of one segment 

 length, so the search radius should be greater than 1. 

 (RSAMPBC) Default: 4. ! RSAMPBC = 10.0 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 Near-Surface depletion adjustment to concentration profile used when 

 sampling BC puffs? 

 (MDEPBC) Default: 1 ! MDEPBC = 1 ! 

 0 = Concentration is NOT adjusted for depletion 

 1 = Adjust Concentration for depletion 

!END! 

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

INPUT GROUPS: 13a, 13b, 13c, 13d -- Point source parameters 

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

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

Subgroup (13a) 

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

 Number of point sources with 

 parameters provided below (NPT1) No default ! NPT1 = 5 ! 

 Units used for point source 

 emissions below (IPTU) Default: 1 ! IPTU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (13d) (NSPT1) Default: 0 ! NSPT1 = 0 ! 

 Number of point sources with 

 variable emission parameters 

 provided in external file (NPT2) No default ! NPT2 = 0 ! 

 (If NPT2 > 0, these point 

 source emissions are read from 

 the file: PTEMARB.DAT) 

!END! 

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

Subgroup (13b) 

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

 The following species are modeled: 

CSPEC = SO2 

CSPEC = SO4 

CSPEC = NOX 

CSPEC = HNO3 

CSPEC = NO3 

CSPEC = PMC 

CSPEC = PMF 

CSPEC = EC 

CSPEC = SOA 

 a 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 POINT SOURCE: CONSTANT DATA 

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

 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) SO2 SO4 NOX HNO3 

NO3 PMC PMF EC SOA 

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

 1 ! SRCNAM = S10 ! 

 1 ! X = 577.39257, 553.25636, 64.9, 352.7, 2.6 , 14.6, 449, .0, 143.1, 6.43, 28.1, 0, 0, 1.16, 

2.39, 0.09, 1.61 ! 

 1 ! FMFAC = 1.0 ! !END! 

 2 ! SRCNAM = S11 ! 

 2 ! X = 577.37101, 553.15432, 36 , 352.7, 1.64, 25.7, 457, .0, 13.12, 0.19, 5.35, 0, 0, 0.73, 

1.26, 0.10, 0.04 ! 

 2 ! FMFAC = 1.0 ! !END! 

 3 ! SRCNAM = S12 ! 

 3 ! X = 577.37292, 553.18169, 41.8, 352.7, 0.8 , 11.4, 347, .0, 0.40 , 0 , 0 , 0, 0, 0.00, 

0.43, 0.00, 0.00 ! 

 3 ! FMFAC = 1.0 ! !END! 

 4 ! SRCNAM = S52 ! 

 4 ! X = 577.32104, 553.10738, 23.4, 352.7, 0.51, 9.4 , 313, .0, 0 0 , 0 , 0 , 0, 0, 0.43, 

0.00, 0.00, 0.00 ! 

 4 ! FMFAC = 1.0 ! !END! 

 5 ! SRCNAM = S53 ! 

 5 ! X = 577.31194, 553.12545, 25.9, 352.7, 0.98, 8.8 , 347, .0, 1.35 , 0.10, 0.92, 0, 0, 0.32, 

0.19, 0.01, 0.00 ! 

 5 ! FMFAC = 1.0 ! !END! 

-------- 

 a 

 Data for each source are treated as a separate input subgroup 

 and 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.) 

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

 the effect of rain-caps or other physical configurations that 

 reduce momentum rise associated with the actual exit velocity. 

 (Default: 1.0 -- full momentum used) 

 b 

 0. = No building downwash modeled, 1. = downwash modeled 

 NOTE: 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 are 

 modeled, 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) 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 every 10 degrees. LENGTH, XBADJ, and YBADJ are only needed for 

 MBDW=2 (PRIME downwash option) 

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

-------- 

 a 

 Building height, width, length, and X/Y offset from the source are treated 

 as a separate input subgroup for each source and therefore must end with 

 an input group terminator. The X/Y offset is the position, relative to the 

 stack, of the center of the upwind face of the projected building, with the 

 x-axis pointing along the flow direction. 

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

Subgroup (13d) 

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

 a 

 POINT SOURCE: VARIABLE EMISSIONS DATA 

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

 Use this subgroup to describe temporal variations in the emission 

 rates given in 13b. Factors entered multiply the rates in 13b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use PTEMARB.DAT and NPT2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (14a) 

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

 Number of polygon area sources with 

 parameters specified below (NAR1) No default ! NAR1 = 0 ! 

 Units used for area source 

 emissions below (IARU) Default: 1 ! IARU = 1 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 1 = g/m**2/s 

 2 = kg/m**2/hr 

 3 = lb/m**2/hr 

 4 = tons/m**2/yr 

 5 = Odour Unit * m/s (vol. flux/m**2 of odour compound) 

 6 = Odour Unit * m/min 

 7 = metric tons/m**2/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (14d) (NSAR1) Default: 0 ! NSAR1 = 0 ! 

 Number of buoyant polygon area sources 

 with variable location and emission 

 parameters (NAR2) No default ! NAR2 = 0 ! 

 (If NAR2 > 0, ALL parameter data for 

 these 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 subgroup 

 and 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 are 

 modeled, 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 subgroup 

 and therefore must end with an input group terminator. 

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

Subgroup (14d) 

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

 a 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 AREA SOURCE: VARIABLE EMISSIONS DATA 

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

 Use this subgroup to describe temporal variations in the emission 

 rates given in 14b. Factors entered multiply the rates in 14b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use BAEMARB.DAT and NAR2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (15a) 

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

 Number of buoyant line sources 

 with variable location and emission 

 parameters (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 source 

 emissions below (ILNU) Default: 1 ! ILNU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (15c) (NSLN1) Default: 0 ! NSLN1 = 0 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 Maximum number of segments used to model 

 each line (MXNSEG) Default: 7 ! MXNSEG = 7 ! 

 The following variables are required only if NLINES > 0. They are 

 used in the buoyant line source plume rise calculations. 

 Number of distances at which Default: 6 ! NLRISE = 6 ! 

 transitional rise is computed 

 Average 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 

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

 a 

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 subgroup 

 and 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 are 

 modeled, 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 emission 

 rates 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: 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and therefore must end with an input group terminator. 

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

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

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

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

Subgroup (16a) 

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

 Number of volume sources with 

 parameters provided in 16b,c (NVL1) No default ! NVL1 = 0 ! 

 Units used for volume source 

 emissions below in 16b (IVLU) Default: 1 ! IVLU = 1 ! 

 1 = g/s 

 2 = kg/hr 

 3 = lb/hr 

 4 = tons/yr 

 5 = Odour Unit * m**3/s (vol. flux of odour compound) 

 6 = Odour Unit * m**3/min 

 7 = metric tons/yr 

 Number of source-species 

 combinations with variable 

 emissions scaling factors 

 provided below in (16c) (NSVL1) Default: 0 ! NSVL1 = 0 ! 

 Number of volume sources with 

 variable location and emission 

 parameters (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 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

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

 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 subgroup 

 and 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 are 

 modeled, 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 emission 

 rates given in 16b. Factors entered multiply the rates in 16b. 

 Skip sources here that have constant emissions. For more elaborate 

 variation in source parameters, use VOLEMARB.DAT and NVL2 > 0. 

 IVARY determines the type of variation, and is source-specific: 

 (IVARY) Default: 0 

 0 = Constant 

 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 upper 

 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 subgroup 

 and 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 = 1995 ! 

December 2010 
 Refined BART Modeling Protocol for 

 Wausau Mosinee Mill

!END! 

Note - three Class I areas 

Seney SENE = 173 receptors 

Isle Royal ISLE = 966 receptors 

Boundary Waters BOWA = 856 receptors 

total number of receptors is 1995 

ALL RECEPTOR COORDINATES FOLLOW IN INPUT FILE 

December 2010 

BEFORE THE 

STATE OF WISCONSIN 

DEPARTMENT OF NATURAL RESOURCES 

In the Matter of Applicable Best ) FID # 405032870 

Available Retrofit Technology ) 

Requirements for Georgia-Pacific ) 

Consumer Products LP Located at ) 

1919 South Broadway, Green Bay, ) 

Wisconsin 54304 ) 

FINDINGS OF FACT, CONCLUSIONS OF LAW, 

AND ADMINISTRATIVE CONSENT ORDER 

FINDINGS OF FACT 

The Wisconsin Department of Natural Resources (“Department” or “WDNR”) finds that: 

Regional Haze Rule Background

1. On July 6, 2005, the U.S. Environmental Protection Agency (EPA) published regulations 

to address visibility impairment in our nation’s largest national parks and wilderness 

(“Class I”) areas [70 FR 39103]. Collectively, these regulations are commonly known as 

the “Regional Haze Rule,” and are codified at 40 CFR §§ 51.300 – 51.309. 

2. Wisconsin has promulgated regulations relating to Protection of Visibility by Application of 

Best Available Retrofit Technology (“BART”) which are codified in ch. NR 433, Wis. Adm. 

Code. 

3. Wisconsin does not have any Class I Federal areas as listed in the Regional Haze Rule. 

However, Wisconsin contributes to visibility impairment in four Class I Federal areas in 

Michigan and Minnesota: Isle Royale National Park, Seney Wilderness Area, Boundary 

Water Canoe Area, and Voyageurs National Park. 

4. Wisconsin has been required under 40 CFR § 51.308(e) to submit a state implementation 

plan (SIP) addressing BART requirements for regional haze visibility impairment. This 

SIP must contain emission limits representing BART and schedules for compliance with 

BART for each BART-eligible source that may reasonably be anticipated to cause or 

contribute to any impairment of visibility in a mandatory Class I Federal area. 

5. The Wisconsin Department of Natural Resources submitted a Regional Haze SIP to U.S. 

EPA on July 1, 2011. 

Facility Specific Information

6. Georgia-Pacific Consumer Products LP, the “permittee,” operates a manufacturing facility 

located at 1919 South Broadway, Green Bay, Wisconsin 54304, (hereinafter, “the 

facility”) which is a “stationary source” as defined in s. 285.01(41), Wis. Stats. 
7. Georgia-Pacific Consumer Products LP currently operates the facility under a Part 70 

source operation permit number 40532870-P10, issued on July 26, 2011. 

8. The Georgia-Pacific Consumer Products LP facility qualifies as a BART-eligible source 

under s. NR 433.02(1), Wis. Adm. Code and Appendix Y in 40 CFR Part 51 because: 

a) One or more emission units at the facility fit within one of the twenty-six (26) 

categories listed under s. NR 433.02(1), Wis. Adm. Code and Appendix Y in 40 

CFR Part 51; 

b) The emission units were in existence on August 7, 1977 and began operation at 

some point on or after August 7, 1962; 

c) The sum of the potential emission from all emission units identified in the 

previous two bullets is greater than 250 tons per year of the visibility-impairing 

pollutants: SO2, NOx, and PM. 

9. The Georgia-Pacific Consumer Products LP facility qualifies as a BART-subject source 

under s. NR 433.03(3), Wis. Adm. Code and Appendix Y in 40 CFR Part 51, because it 

contributes to visibility impairment in a Class I Federal area. 

CONCLUSIONS OF LAW 

The Department concludes that: 

The Department of Natural Resources has the authority under sec. 285.29, Stats., to specify the 

best available retrofit technology (BART) for any existing major sources located in the area 

where visibility is identified as an important value under section 169A of the federal Clean Air Act. 

All BART analyses shall consider the terms under s. 285.29(2), Wis. Stats., and shall be 

evaluated and determined according to Department’s administrative rules in ch. NR 433, Wis. 

Adm. Code. 

1. In Chapter NR 433, Wis. Adm. Code, which was promulgated under the authority of 

chapter 285, Stats., the Department of Natural Resources has adopted regulations 

relating to the Protection of Visibility by Application of Best Available Retrofit Technology , 

the “BART” rules. 

2. Section NR 433.05, Wis. Adm. Code, of the BART rules requires the department to make 

a preliminary and final determination of the BART requirements for each emission unit at 

Georgia Pacific subject to BART. 

3. The Department has the authority under s 285.13(2) Stats. to issue administrative orders 

to effectuate the purposes of ch. 285, Stats., . 

4. This Order is reasonable and necessary to accomplish the purposes set forth in chapters 

285, Stats., and chapter NR 433, Wis. Adm. Code, and is enforceable under ss. 299.95, 

and 299.97, Stats. 

ADMINISTRATIVE CONSENT ORDER 

The parties to this Order hereby agree to the following provisions: 
1. The permittee, Georgia-Pacific, will install and operate any necessary control equipment 

and/or undertake any necessary work practices to meet the following BART requirements 

at the facility as required under s. NR 433.05, Wis. Adm. Code. 

Boilers B26 and B27 Best Available Retrofit Technology (BART) for Particulate Matter

2. Boilers B26 and B27 at the facility shall meet all of the following emission limitations and 

compliance methods related to emissions of particulate matter. 

(a) Effective January 1, 2011, the permittee shall meet BART requirements for 

particulate matter emissions. 

(b) The permittee shall comply with the particulate matter emission requirements of 

BART by meeting the following conditions: 

i. Emissions may not exceed 0.30 pounds of particulate matter from stack S10 per 

million Btu of heat input; 

ii. The operating permit conditions under limitations and requirements for firing of 

fuels and operating of baghouse control; 

iii. The operating permit conditions under limitations and requirements for visible 

emissions; 

iv. The permittee shall continue to implement the facility malfunction prevention and 

abatement plan as specified under s. NR 439.11, Wis. Adm. Code. 

(c) The permittee shall meet the corresponding compliance demonstration, 

recordkeeping, reporting, and monitoring requirements for the emission 

limitations in 2.(b) above as specified in the permittee’s operating permit. 

(d) The permittee shall meet the corresponding procedures and methods required 

for compliance demonstration and for performance testing required by condition 

2.(c) above as specified in the permittee’s operating permit. 

Boilers B26 and B27 Best Available Retrofit Technology (BART) for Sulfur Dioxide

3. Boilers B26 and B27 at the facility shall meet all of the following emission limitations and 

compliance methods related to emissions of sulfur dioxide. 

(a) Effective January 1, 2016 the permittee shall meet BART requirements for sulfur 

dioxide emissions. 

(b) The permittee shall comply with the sulfur dioxide emission requirements of BART by 

meeting one of the following limitations: 

i. total emissions of sulfur dioxide not to exceed 2,340 tons in any 12-month period 

and 268 tons in any 30-day period on stack S10; or 

ii. In lieu of complying with 3(b)i, the permittee can comply with an alternate 

requirement for sulfur dioxide emissions according to the following criteria: 

(1) the permittee notifies the Department and U.S. EPA Administrator by 

July 15, 2013 of complying with one of the alternative sulfur dioxide mass 

cap requirements for the designated periods as specified in 3(b)ii.(3). 

(2) nitrogen oxide emissions from stack S10 will not to exceed 1,522 tons in 

any 12-month period and 172 tons in any 30-day period; 

(3) the emission limitation on sulfur dioxides shall be met when the permittee 

elects one of the set combinations of sulfur dioxide and nitrogen oxides 
emission mass caps for stack S10 from the following table. Note: These 

alternative compliance mass caps are determined by allowing trading of 

2.0 tons sulfur dioxide reduced to one ton nitrogen oxides increased 

beyond the primary BART mass cap level: 

30-day rolling 12-month rolling

SO2 NOx SO2 NOx 

BART 268 110 2,340 977 

Mass Cap 1 246 121 2,150 1,072 

Mass Cap 2 195 147 1,700 1,297 

Mass Cap 3 143 172 1,250 1,522 

(c) The permittee must demonstrate compliance with the sulfur dioxide emission 

limitations in condition 3.(b) above as follows: 

i. The permittee shall determine sulfur dioxide emissions using emission data 

measured according to conditions in the permittee’s operating permit. 

ii. The permittee shall determine sulfur dioxide emissions for condition 3.(b)(i) as 

follows: 

(1) In calculating the total emissions, in tons per 12- month period and tons 

per 30-day period, the permittee shall not exclude emissions for any 

period of time for which flue gas is exiting Stack S10. 

(2) The total emissions, in tons per 12-month period and tons per 30-day 

period, shall be calculated as the sum of the daily emissions, in tons, 

obtained from the continuous emissions monitoring system over the days 

that any of the boilers B25, B26, B27 or B28 operated during the 

averaging period. The 12-month period shall consist of the month of 

monitoring and the previous 11 consecutive calendar months. A new 12-

month total emissions shall be calculated and recorded at the end of 

each month. The 30−day period shall consist of the day of monitoring 

and the previous 29 consecutive calendar days. A new 30−day total 

emissions shall be calculated and recorded at the end of each day. 

iii. The permittee shall determine sulfur dioxide emissions for condition 3.(b)(ii) as 

follows: 

(1) In calculating the total emissions, in tons per 12- month period and tons 

per 30-day period, the permittee shall not exclude emissions for any 

period of time for which flue gas is exiting Stack S10. 

(2) The total emissions, in tons per 12-month period and tons per 30-day 

period, shall be calculated as the sum of the daily emissions, in tons, 

obtained from the continuous emissions monitoring system over the days 

that any of the boilers B25, B26, B27 or B28 operated during the 

averaging period. The 12-month period shall consist of the month of 

monitoring and the previous 11 consecutive calendar months. A new 12-

month total emissions shall be calculated and recorded at the end of 

each month. The 30−day period shall consist of the day of monitoring 

and the previous 29 consecutive calendar days. A new 30−day total 

emissions shall be calculated and recorded at the end of each day. 

(d) The procedures and methods required for compliance demonstration and for 

performance testing required by conditions 3.(c)(ii), 3.(c)(iii) and 3.(c)(iv) above shall 

meet the following criteria: 
i. The procedures and methods shall be according to the applicable requirements 

of ch. NR 439. [ss. NR 433.06(1), NR 439 and NR 440, Wis. Adm. Code] 

ii. The permittee shall perform the following calculations: 

(1) Tons of emissions shall be calculated daily for use in calculating 

emissions over each 30-day period; 

(2) Monthly emissions shall be calculated by adding all daily emissions in 

that month. These monthly emissions shall be used to calculate 

emissions over each 12-month period. [ss. NR 433.05 and NR 433.06, 

Wis. Adm. Code] 

(e) Note: The sulfur dioxide BART emission limitation on boilers B26 and B27 is based 

on eliminating the firing of coke fuels, combined with continuous operation of a 

circulating fluidized bed sulfur dioxide scrubber system achieving a minimum 93% 

sulfur dioxide removal. This technology is noted to establish a basis for determining 

alternative emission requirements if constraints are encountered in implementing 

these specific technologies which warrant a revision of the individual boiler 

determined control level as allowed for under s. NR 433.05(5), Wis. Adm. Code.

Boilers B26 and B27 Best Available Retrofit Technology (BART) for Nitrogen Oxides

4. Boilers B26 and B27 shall meet all of the following emission limitations and compliance 

methods related to emission of nitrogen oxides. 

(a) Effective January 1, 2016 the permittee shall meet BART requirements for sulfur 

dioxide emissions. 

(b) The permittee shall comply with the nitrogen oxides emission requirements of BART 

by meeting one of the following limitations: 

i. except as provided in 4(b)ii, total nitrogen oxides emissions of 977 tons in any 

12-month period and 110 tons in any 30-day period on stack S10; or 

ii. In lieu of complying with 4(b)i, the permittee can comply with an alternate 

requirement for nitrogen oxide emissions according to the following criteria: 

(1) the permittee notify the Department and U.S. EPA Administrator by July 15, 

2013 of complying with one of the alternative nitrogen oxide emissions mass 

cap requirements for the designated periods as specified in 4(b)ii.(3). 

(2) nitrogen oxide emissions from stack S10 will not to exceed 1,522 tons in any 

12-month period and 172 tons in any 30-day period; 

(3) the emission limitation on nitrogen oxides shall be met when the permittee 

elects one of the set combinations of sulfur dioxide and nitrogen oxides 

emission mass caps for stack S10 from the following table. Note: These 

alternative compliance mass caps are determined by allowing trading of 2.0 

tons sulfur dioxide reduced to one ton nitrogen oxides increased beyond the 

primary BART mass cap level: 

30-day rolling 12-month rolling

SO2 NOx SO2 NOx 

BART 268 110 2,340 977 

Mass Cap 1 246 121 2,150 1,072 

Mass Cap 2 195 147 1,700 1,297 

Mass Cap 3 143 172 1,250 1,522 
(c) The permittee must demonstrate compliance with the nitrogen oxides emission 

limitations in condition 4.(b) above as follows: 

i. The permittee shall determine nitrogen oxides emissions using emission data 

measured according to conditions in the permittee’s operating permit. 

ii. The permittee shall determine nitrogen oxides emissions for condition 4.(b)(i) as 

follows: 

(1) In calculating the total emissions, in tons per 12- month period and tons 

per 30-day period, the permittee shall not exclude emissions for any 

period of time for which flue gas is exiting Stack S10. 

(2) The total emissions, in tons per 12-month period and tons per 30-day 

period, shall be calculated as the sum of the daily emissions, in tons, 

obtained from the continuous emissions monitoring system over the days 

that any of the boilers B25, B26, B27 or B28 operated during the 

averaging period. The 12-month period shall consist of the month of 

monitoring and the previous 11 consecutive calendar months. A new 12-

month total emissions shall be calculated and recorded at the end of 

each month. The 30−day period shall consist of the day of monitoring 

and the previous 29 consecutive calendar days. A new 30−day total 

emissions shall be calculated and recorded at the end of each day. 

iii. The permittee shall determine nitrogen oxides emissions for condition 4.(b)(ii) as 

follows: 

(1) In calculating the total emissions, in tons per 12- month period and tons 

per 30-day period, the permittee shall not exclude emissions for any 

period of time for which flue gas is exiting Stack S10. 

(2) The total emissions, in tons per 12-month period and tons per 30-day 

period, shall be calculated as the sum of the daily emissions, in tons, 

obtained from the continuous emissions monitoring system over the days 

that any of the boilers B25, B26, B27 or B28 operated during the 

averaging period. The 12-month period shall consist of the month of 

monitoring and the previous 11 consecutive calendar months. A new 12-

month total emissions shall be calculated and recorded at the end of 

each month. The 30−day period shall consist of the day of monitoring 

and the previous 29 consecutive calendar days. A new 30−day total 

emissions shall be calculated and recorded at the end of each day. 

iv. In demonstrating compliance with nitrogen oxides emission limitations of 

condition 4.(b) above, the permittee may propose an emissions trading program 

if the program achieves an improvement in visibility in the mandatory class I 

federal areas greater than would be achieved through the installation and 

operation of BART on each boiler subject to BART. The permittee proposing to 

use an emissions trading program shall submit an emissions trading plan to the 

department. The plan shall be subject to department and administrator approval 

and meet the following criteria: 

(1) The criteria under s. NR 433.05, Wis. Adm. Code; 

(2) The permittee shall submit one of the set combinations of sulfur dioxide 

and nitrogen oxides emission mass caps for stack S10 specified in 

condition 4.(b)(ii)(3) below to the department and the administrator by 

July 15, 2013; 

(3) If the permittee elects to choose a mass cap not specified under 

4.(b)(ii)(3) or choose any alternative mass cap later than July 15, 2013, 

then the election is subject to department review with public comment 

and pursuant U.S. EPA approval of the SIP. 
(d) The procedures and methods required for compliance demonstration and for 

performance testing required by conditions 4.(c)(ii), 4.(c)(iii) and 4.(c)(iv) above shall 

meet the following criteria: 

i. The procedures and methods shall be according to the applicable requirements 

of ch. NR 439. [ss. NR 433.06(1), NR 439 and NR 440, Wis. Adm. Code] 

ii. The permittee shall perform the following calculations: 

(1) Tons of emissions shall be calculated daily for use in calculating 

emissions over each 30-day period; 

(2) Monthly emissions shall be calculated by adding all daily emissions in 

that month. These monthly emissions shall be used to calculate 

emissions over each 12-month period. [ss. NR 433.05 and NR 433.06, 

Wis. Adm. Code] 

(e) Note: The nitrogen oxides BART emission limitation on boiler B26 is based on 

continuous operation of over-fire air and flue gas recirculation control designed 

specifically for NOx control and continuous operation of selective non-catalytic 

reduction. This technology is noted to establish a basis for determining alternative 

emission requirements if constraints in implementing these specific technologies are 

encountered as allowed for under s. NR 433.05(5) warrant a revision of the individual 

boiler determined control level. The nitrogen oxides BART emission limitation on 

boiler B27 is based on continuous operation of over-fire air designed specifically for 

NOx control and in combination with regenerative selective catalytic reduction 

equipment to achieve additional 70% control of nitrogen oxides beyond the over-fire 

air: This technology is noted to establish a basis for determining alternative emission 

requirements if constraints in implementing these specific technologies are 

encountered as allowed for under s. NR 433.05(5) warrant a revision of the individual 

boiler determined control level. 

WAIVER AND STIPULATION

Georgia-Pacific Consumer Products LP consents to, and agrees not to contest, the Department 

of Natural Resources’ jurisdiction to issue this Consent Order and to enforce its terms. To that 

end Georgia-Pacific Consumer Products LP stipulates to the issuance of this Consent Order and 

hereby waives further notice or hearing before the Department of Natural Resources regarding 

the forgoing Findings of Fact, Conclusions of Law and Administrative Consent Order and waives 

its rights, if any, to challenge this Administrative Consent Order in circuit court under ss. 227.52 

and 227.53, Stats., or any other provision of law. Georgia-Pacific Consumer Products LP further 

stipulates and agrees that this Consent Order is effective and enforceable after being signed by 

both parties and that it may be enforced in accordance with ss. 299.95, and 299.97, Stats. The 

undersigned further certifies that he or she is authorized to execute such Consent Order, Waiver 

and Stipulation on behalf of Georgia-Pacific Consumer Products LP. 

Nothing in this Consent Order, however, shall be construed as an admission on the part of 

Georgia-Pacific Consumer Products LP for any purpose other than for an action taken for failure 

to comply with the terms of this Order. This stipulation and waiver does not affect the right of 

Georgia-Pacific Consumer Products LP to assert any equitable or legal defense or to challenge 

the Department of Natural Resources’ interpretation or application of this Consent Order in any 

subsequent proceedings. 

STATE OF WISCONSIN DEPARTMENT OF NATURAL RESOURCES 
For the Secretary 

By _______________________________ __________________ 

William Baumann Date 

Acting Air Management Bureau Director 

 

 

_______________________________ __________________ 

Georgia-Pacific Consumer Products LP Date 

Title: 

 

Template for EGU BART Permit Revisions for Implementation of BART

Note: The template that follows will be used for proposed BART language within 

each permit. 

PART *X*: BEST AVAILABLE RETROFIT TECHNOLOGY (BART)

(Note: Text that is underlined and highlighted in gray varies between different boilers) 

1.0 Applicability 

A Best Available Retrofit Technology (BART) determination has been made for the 

BART-subject emission units at this facility to comply with the requirements of 40 CFR 

Part 51. These requirements are submitted as a Title V air permit revision. 

2.0 BART-affected Unit Description 

Boiler *X* was brought into service in *YEAR.* This boiler relies on *TYPE* coal. 

Boiler *X* is rated at *XX* mmBtu/hr and exhausts to *stack number*. The boiler has 

an *ESP/baghouse* currently in-use for controlling particles and meeting opacity 

requirements. 

3.0 BART Determination 

Best Available Retrofit Technology (BART) applies to boiler *X*. 

(a) BART shall be applied no later than December 31, 2015. 

(b) BART for particulate matter (PM) emissions has been determined to be: 

(i.) The existing PM emission limitations specified in Conditions *XX* and *XX*, as 

well as compliance with the visible emissions limitations specified in Condition *XX*; 

(ii) Compliance with the Compliance Assurance Monitoring (CAM) Plan in Part *X*, 

and the Malfunction Prevention and Abatement (MPA) Plan, located in Part *X*; 

[ss. NR 415.03 and NR 433.05, Wis. Adm. Code] 

Note: Any revisions to the CAM Plan will be part of future Title V permit renewals.