# A TTACHMENT 

# 4

## 1 

# 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 Sour ce Performance Standards (NSPS) first came into effect, and as a result have minima l or less than adequate emission controls. The federal requirements for identifying sources subj ect 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 implemen ted rules for BART as provided under NR Ch. 433, Wis. Adm. Code, that address emissions of pa rticulate matter (PM), sulfur dioxide (SO 2 

## ), and nitrogen oxide (NOx).
The Wisconsin rules establish that electricity generating units (EGUs) meet BART requirements for SO 2 

## and NOx by meeting the federal Clean Air Inters tate Rule (CAIR) requirements. For all other cases, the Wisconsin rules establish a pr ocess for determining t hose 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 anal ysis 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 requireme nts for the affected sources. The finalized BART program is based on proposals provided fo r public comment & hearings in July 2010 and September 2011.
1. Determination of BART Elig ible and Affected Sources.
Under the state rule, the CALPUFF air quality mode l 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 SO 2 

## , NOx, and PM. If the modeled results show a significant reduction in visibility, the source is subject to BART or "BART-af fected". An alternate CALPUFF analysis, which utilizes more specific data, is also allowed under the state rule. The protoc ols for the CALPUFF modeling and alternative modeling for determining if a source is subj ect to BART controls, along with additional details for modeling, ar e 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 Do cument (TSD) for EGUs” with in Wisconsin’s BART SIP.

## 2 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 sour ces 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-Paci fic facility is the only non-EGU source subject to BART. The BART determination for Georgia-Pacific is desc ribed below. The BART TSD for non-EGUs is located in Wisconsin’s BART SIP.
Based on visibility modeling results, the three ot her BART eligible industr ial facilities listed in Table 2 – International Paper Kaukauna facili ty (a.k.a. Thilmany), Packing Corporation of America-Tomahawk, and Mosinee Paper Corpora tion – 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 VIST AS 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 ar e presented in Attachment 5 of Wisconsin’s BART Implementation SIP Submittal.

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

Source Name Eligible Emission Units (B = Boiler) BART-subject Status County

Georgia-Pacific – Green Ba y 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 mode ling using VISTAS modeling protocol.

## 3 2. Georgia-Pacific BART Determination
The Georgia-Pacific facility in Green Bay, Wisc onsin operates two coal-fired power boilers subject to BART under the Clean Air Act. In Ju ly of 2011, the Department provided for external review a draft finding of BART requirements appli cable to the affected Georgia-Pacific boilers. This document amends the draft BART findi ng 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 Progr ess Goals (RPG) by the beginning of 2016 and after. Further requirements and contribution by i ndustrial boilers to RPG, at Georgia-Pacific and sector-wide, will be evaluated for the next RP G evaluation in 2018 as described in the Regional Haze SIP document.
The Georgia-Pacific BART requireme nts address emissions of PM, SO 2 

## , and NOx from two power boilers B26 and B27. The two affected boilers exhaust through common stack S10 along with the coal-fired boile rs 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 findi ng was based on the following: insignificant visibility improvement for a zero-out of PM emissions from the maximum actual baseline PM 10 

## emissions; a very high level of PM contro l achieving 0.025 lbs/mmBtu emission rates; and current compliance with malfunc tion and abatement plans. In responding to comments, the finalized PM BART determination has not b een 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 fo r PM at Georgia-Pacific are found in the July 2011 Draft BART TSD for Non-EG Us (Attachment 3 of Wiscons in’s BART Implementation SIP Submittal) and the Response to Comments fo r BART (Attachment 10 of Wisconsin’s BART Implementation SIP Submittal).

Sulfur Dioxide (SO 2 

## )
The Department compared wet flue gas desulfur ization (FGD) and dry ci rculating fluidized bed (CFB) FGD in the July 2011 draf t 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 e fficiencies (93% - 98%). The Department concluded in the draft BART finding that the incremental costs do not substantiate the application of wet FGD, and that SO 2 

## BART should be based on th e application of dry CFB FGD technology. The Department further conclu ded that long-term operation and compliance with dry CFB FGD is represented by 93% control efficiency. The draft finding also established "Base SO 2 

## emissions" reflecting a presumptive fuel at a specified sulfur c ontent. The BART compliance requirement was then establishe d by applying 93% cont rol to the "Base SO 2 

## emissions."

## 4 The finalized BART determination for SO 2 

## 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 petrol eum coke to the bituminous coal as burned during the BART baseline years. The fuel switch alters the concentration of SO 2 

## in the flue gas from ~ 3.6 lbs/mmbtu to 3.0 lbs/mmbtu. A dry sc rubber 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 contro l 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 vi sibility improvement factors for SO 2 

## reduction as developed in the Visibility Improvement sec tion below. Table 3 shows a summary of the amended SO 2 

## BART control and visibility improvemen t. Additional details regarding the Department’s BART determination for SO 2 

## at Georgia-Pacific are found in the July 2011 Draft BART TSD for Non-EGUs (Attachment 3 of Wi sconsin’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 SO 2 

## BART Control and Visibility Improvement at Northern Class I Areas 1,2



### 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 Nationa l Park, Seney Wilderness Area, Boundary Water Canoe Area, and Voyageurs National Park.

## 5 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 catalyt ic reduction technology (RSCR). The requirement for B26, a stoker boiler, reflect ed 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 ava ilable 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 de termination for NOx is 68% control for boiler B26 and 85% control for boiler B27. The 68% c ontrol 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 BA RT determination for NOx at Georgia-Pacific are found in the July 2011 Draft BART TSD fo r 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 Contro l and Visibility Impr ovement 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 Leve ls 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 emissi ons from the combined stack S10 during the baseline years. The base uncontrolled emission ra tes identified for each pollutant, in grams per second, used for this modeling are provided in A ppendix A. To assess the BART requirements, controlled emission rates were ca lculated and modeled. To do th is 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 SO 2 

## base fuel

## 6 adjustments. The stack S10 percent reducti on applied to the uncontrolled grams per second emission rates in the July 2011 draft BART finding was 70% for NOx and 57% for SO 2 

## . 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 Dr aft 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 SO 2 

## and NOx, the visibility m odeling provided in the July 2011 draft BART finding is updated accordingly. Th e Department first determined the percent reduction that would occur from the maximum da y emission rate after applying the finalized BART controls. The Department then calcula ted 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 reductio n applied to the uncontrolled grams per second emission rates is 71% for NOx and 81% for SO 2 

## . Table 5 shows the reduced number of days a bove the 0.1 and 0.5 dv thresholds due to BART (Reduced Days of Impact with BART). Thes e values were calculat ed 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 re duced / 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 improve ments under BART related to the individual pollutants, shown for SO 2 

## 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.

## 7 Table 5 - Days of Visibility Impact aft er 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

5.38 4.14 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 mode led for the base years (2002 – 2004) Average = Average of each base year maximum daily impact.

## 8 Table 7 - Draft BART Control Levels and Visi bility Improvement for Boilers B26 and B27
Visibility Improvement (dv) 2,3 

## BART Technology and Control Efficiency Seney Northern Class I Areas Emission Unit
SO 2 1 

## NOx PM 10 

## SO 2 

## NOx PM SO 2 

## 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 SO 2 

## control efficiency, based on combinati on 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 great er 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 SO 2 

## and NOx as 30-day mass caps and 12-month mass caps individually for each boi ler B26 and B27. Furthermore, the emission limitations applicable to the common stack S 10 are based on averaged emission requirements across boilers B25 through B28. The emission ba seline and mass cap calculations exclude the operation of boiler B24 because it has been perm anently 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 inoperativ e period to exempt B25 from the CAIR.

The annual emission baseline used to calculate th e 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 th e BART baseline years. The NOx baseline emission rates for B26 and B27 are adjusted from th e baseline data to reflect test data for actual emissions since 2007. The adjusted NOx emi ssion 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 calc ulated by applying the BART control efficiencies to the 30-day and annu al emission baselines, respectively. A 10% additional reduction is then applied to the BA RT boiler controlled emissions to address the

## 9 environmental benefit. This is consistent w ith 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 ma ss cap over all boilers creates an additional environmental benefit (as outlined in the EI P) 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 eac h boiler are summed to yield the 30-day and 12-month roll ing emission caps for stack S10.
Tables 8 through 11 show the baseline emissions and requirements for SO 2 

## and NOx on a 30-day and 12-month basis.

Table 8 - SO 2 

## BART Annual Baseline Emissions and Requirements

Emission Unit Baseline Heat Input (mmBtu) Baseline Emission Rate (Lb/mmBtu) Baseline Emissions

(Tons) BART Control Efficiency 1 

## 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 dr y scrubber control at 93% at B26 and B27. 2 

## Includes 10% additional reduction applie d to B26 and B27 controlled emissions.

Table 9 - SO 2 

## BART 30 Day Baseline Emissions and Requirements

Emission Unit Baseline Heat Input (mmBtu) Baseline Emission Rate (Lb/mmBtu) Baseline Emissions

(Tons) BART Control Efficiency 1 

## 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 dr y scrubber control at 93% at B26 and B27. 2 

## Includes 10% additional reduction applie d to B26 and B27 controlled emissions.

## 10 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 Efficiency 1 

## 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 dr y scrubber control at 93% at B26 and B27. 2 

## Includes 10% additional reduction applie d 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 Efficiency 1 

## 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 dr y scrubber control at 93% at B26 and B27. 2 

## Includes 10% additional reduction applie d to B26 and B27 controlled emissions.
BART Compliance Requirements
The July 2011 draft BART finding provided severa l compliance alternatives for meeting the SO 2 

## and NOx BART requirements. These requirements were structured as either emission rate limitations or mass emission caps on either 30-da y 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 requirement s are amended to include only stack S10 mass emission caps on both a 30-day and 12-month basis (T able 12). The PM BART requirements for BART boilers B26 and B27 remain at the exis ting emission limitation of 0.30 Lb/mmBtu. These compliance requirements become effective January 1, 2016.

## 11 Table 12 - Summary of SO 2 

## 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

SO 2 

## 268 2,340
NOx 110 977

SO 2 

## and NOx Alternative Compliance Option
As previously described, the primary SO 2 

## 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 SO 2 

## and NOx is to reduce visibility impact in the Cla ss I areas, an alternative comp liance option is provided where SO 2 

## can be traded for NOx reductions while still yielding the same visibility improvement as the primary BART requirement. Simply stated, this approa ch is a form of inter-pollutant trading for precursor emissions affecting visibility.
The alternative compliance option sets forth several set combinations of SO 2 

## and NOx emission mass caps for stack S10 as identified in the draf t Georgia-Pacific BART Administrative Order (Attachment 6 of Wisconsin’s BART SIP). Georgi a-Pacific can then elect one of these default mass cap combinations by July 15, 2013 through no tification to the Department and the U.S. EPA. If Georgia-Pacific elec ts to choose a non-specified mass cap or choose any alternative mass cap later than July 15, 2013 th en the election is subject to Department review with public comment and pursuant U.S. EPA approval of th e SIP. The default combinations of SO 2 

## and NOx emissions for election are provided in Table 13.

Under all of the identif ied mass cap options, SO 2 

## 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, whethe r under an elected defa ult or alternatively identified mass cap, that in no case NOx emissi ons 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 SO 2 

## and NOx Mass Caps Under the Alternative Compliance Option 30-day rolling 12-month rolling SO 2 

## NOx SO 2 

## 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

## 12 The mass cap options are identified by establis hing potential NOx emissi on levels consistent with various control equipment applications. The NOx mass cap levels under the alternative compliance option are calculated placing these control assumptions agai nst the BART baseline year average heat input for each boiler. Details of control equipment options and visibility improvement for boilers B26 and B27 are thos e identified and evalua ted under the July 2011 BART proposal.
To ensure equivalent or great er visibility improvement, NOx is offset by two tons of SO 2 

## (2:1 trading ratio). As a result, at each NOx emission level the SO 2 

## 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 SO 2 

## and NOx trading included in the July 2011 draft BART finding, section 7. The analysis tested various combinations of SO 2 

## and NOx trading for visibi lity improvement during the 20% best and worst days and on a 30-day rolli ng basis relative to the Se ney 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 im pact decreases as more SO 2 

## 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 approxima tely 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 SO 2 

## emissions below the primary BART require d emission cap. Therefore reductions of SO 2 

## below the emission cap are excess and can be tr aded in lieu of the NOx BART requirement. Accordingly, the choice of an alte rnative mass cap at a future date is based on the assessment of current applicable requirements and as such t hose mass caps also reflect trading of excess SO 2 

## emission reductions.
i) Simplified Approach to an Alternative Compliance Option
A simplified approach to implementing an alterna tive control option is to allow inter-pollutant trading by applying the es tablished 2:1 trading ratio along w ith the "not to exceed" NOx mass cap. In this case, Georgia-Pacific do es not need to elect one set of SO 2 

## and NOx mass caps. In essence SO 2 

## can be traded for NOx versus the primar y BART mass caps. This approach allows the control levels to be varied ov er 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 simplifie d 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 SO 2 

## requirements become applicable, the visibility improvement determined as BART cannot be lo st. This is suppor ted by the modeling of visibility improvement for the different SO 2 

## : NOx trading cases at a 2:1 ratio where greater improvement is garnered from deeper SO 2 

## reductions. On this premise, if a SO 2 

## reduction level

## 13 is chosen for trading under BART and then a fu ture regulation requires the same amount of SO 2 

## reduction there is no loss of visibility improvement under inter-pollutant trad ing. Further, if the future regulation requires SO 2 

## reduction beyond the chosen tradi ng 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 visibil ity improvement realized under the primary BART requirement is kept whole at any time into the fu ture. The Department also maintains that this trading, although variable over time , is based on the requirements wh en the BART is established and therefore excess to other emission requirement s. If the U.S. EPA remains concerned that NOx emission levels may increase as future SO 2 

## regulations come into place, a simple solution is to prohibit a change of "noticed" NOx ma ss caps to a lower level after that time.
To note is that under any altern ative 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 em issions 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 BA RT 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 determinatio n 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 Preci pitator 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 mo deling of visibility impact for BART at Georgia-Pacific

Table A1 - Individual Unit Base line Emission Rates used for Modeling Results Emissions (grams/sec) a



## Unit and Pollutant SO 2 

## NOx PM 10 

## 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

# A TTACHMENT 

# 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 Prot ocol and Final Report for PCA “Subject to BART” Analysis

TABLE OF CO NTENTS

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 Em issions Modeled

............................................................................................................... 14 7.0 Modeling R e sults

.................................................................................................................. 15

List of Figures Figure 1 - WDNR Screen ing CALPUFF Domain

.......................................................................... 2 Figure 2 – Refined CALPUFF Mode ling Dom a in and Locations of Class I Areas

....................... 9 Figure 3 – L o cations of Observational Stati ons in Refined CALPUFF M odeling Dom a in

......... 10 Figure 4 – L a nd Use Data for Refi ned CALPUFF Modeling Dom a in

......................................... 11

List of Tables
Table 1 – P C A Speciated PM Em issions

...................................................................................... 14
Table 2 – P C A CALPUFF BART Exem ption Results Sum m a ry

................................................. 16

Appendix A – Exam ple CALMET I nput File Appendix B – Exam ple CALPUFF I nput File

i

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## 1 Dece m b er 2010 

# 1.0 Introduct i on

The W i sconsin Departm e nt of Natural Resour ces (DNR) perform e d single source screening modeling in 2006 to evaluate which Best Availabl e Retrofit Technology (BAR T) eligible sources
in the s t ate m a y “cause or contri bute” to visibility im pairm e nt a nd could therefore b e subjec t to BART requirem e nts. This type of analysis is referred to as the “subj e c t to BART” or “BART

exem ption” analysis. The m e thods used by DNR ar e described in the “S in gle Source Modeling to Support Regional Haze BART Modeling Pro t ocol”, March 2 1, 2006, prepared by Lake Mich igan
Air Direc t ors Consortiu m (LADCO).

DNR applied CALPUFF to each B A RT eligible source for three annual periods, co vering the calendar years 2002 to 2004. The CALPUFF/CA LMET m o deling dom ain consisted of ninetyseven 36-k m spaced cells in the eas t -west d i rect ion and ninety 36-km spaced cells in the northsouth direction (see Figure 1) . Meteorological data genera ted by the MM5 prognostic weather model (provided by LADCO in CALMM5 for m at) wa s used to develop the m e teorological data for CALPUFF, without additional observational data input (i.e., NOOBS mode). This represents

a coars e m e teorolog ical gr id, suitable for an initial screening analysis.

The results from DNR’s screen i ng analysis indicated that, with the excep tion of som e of the larges t electric power s t ations in the state, the on ly Class I areas where B A RT eligible sources

m a y contribute to visibility im pairment are th e three areas to the nor th of W i sconsin, the Boundary Waters Canoe Area, Isle Royal Natio nal Park, and Seney W ildlife Area. DNR’s

screen ing an alysis also indicated that the BA RT elig ible em issions unit a t the Pack ag ing Corporation of Am erica Tom a hawk Mill (PCA ) m a y “cause or contribute” to visibility
im pair m e nt at the Sen e y Class I area (located ap proxim a tely 280 km to the northeast o f the m ill), as defined by the 98 th 

## percentile visibility im pacts being grea ter than 0.5 deciviews (dv) relative to natural background.

### Upd a te d B A R T Modeling P r otoc ol and Repor t for PCA T o ma hawk Mill



## 2 Dece m b er 2010 

## Figure 1 - WDNR Screening CALPUFF Do main

NOTE: Class I areas a re identified by red marks.

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## 3 Dece m b er 2010 

## PCA has elected to refine the DNR scr eening analysis by conduc ting refined CALPUFF modeling with a 4 km meteorologi cal grid, based on procedures descr i bed in the “Visibility

Im prove m e nt – State and Tribal Association of the Southeast (VISTA S) BART CAL P UFF” modeling protocol. The VISTAS pr otocol wa s developed by a large group of stakeholders,
includ ing EPA, the VISTAS m e mber state agen cies and tribes, the Federal Land Managers (FLMs), industry representatives, and consulting experts. Given the resources expended on the VISTAS protocol, it arguably represents the m o st com p rehensive CALPUFF BART protocol ever developed.

PCA had discussions with DNR and EPA Region 5 staff about refining the analysis, and
subm itted a refined CALPUFF BART m odeling pr otoco l in March 2007. EPA reviewed the
protoco l and provided m i nor comm ents to DNR in May 2010. Another facility und ergo ing Subject to BART review, Thilm any, responded to these com m e nts in a letter “Response to EPA
Comm ents on Thilm any BART Modeling Protoc ol” dated Novem b er 9, 2010. In addition, subsequent to the EPA protocol comm ents, the US Fish and W ildlife Service and US Forest Service reviewed the protocol and had additional discussions with DNR a nd EPA. The three EPA comments, and each resp onse, are lis ted below.

Comment 1
Inform ation needs to be presented which clar ifies how POSTUTIL was used for ammonia. Response 1
The VISTAS m e thodology was used, with a MNITRATE switch setting of one (1).

Comment 2
The m odeling m u st include a copy of the input and list files associated with runs. The protocol only offers som e of the control file infor m ation.

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## 4 Dece m b er 2010 

## Response 2 All CALMET, CALPUFF, and CALPOST input and list files, as well as m e teorological and geophysical data files, had been provided by PCA to DNR on a portable hard disk drive. PCA will again provide a portable hard dis k drive of all m odeling files to DNR for the updated BART analysis, for purposes of SIP docum e n tation.

Comment 3 The input file ... uses the background ammoni a values that were produced for the L ADCO protocol. These values are based on m odeled es tim a tes. Monitoring data has generally shown much higher ammonia than what was used fr om t h e m odel results. The refined m odeling analyses ... must evaluate the visibility im p acts using m easured background ammonia values. Response 3
The US Fish and W ildlif e Service proposed usin g a constant background ammonia concentration of 3.9 ppb, which was the highest concentration m easured at the Mayv ille W i sconsin station during a m i d-1990s EPA study. PCA has agreed to use this single, conservative background value in the absence of daily data.

On Nove m b er 29, 2010, DNR issued a letter that approved the CALPUFF BART prot ocol, as
well as the e m ission rate s to be used f o r the BA RT eligible em ission units. DNR requested that the 2007 version of the protocol be updated to in clude the responses to E P A comm ents, and text
that addresses current C A LPUFF modeling guidance. In additi on, the updated m odeling results could be presented in the prot oco l (so that a ll inf o rm ation is located in one docum ent).

This document is the updated m odeling protocol and final m o deling report for the refined PCA “Subject to BART” analysis. This docum e nt does not duplicate the extensive inform ation on visibility, CALPUFF, and EPA gui dance on BART modeling procedures that are contained in the VISTAS protocol. Rath e r , this do cu m e nt describe s how data specif i c to th is se tting will be us ed
in the refined CALPUFF m odeling. Section 1 of the protocol is this introduction. Section 2

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## 5 Dece m b er 2010 

## briefly sum m a rizes im portant concepts from th e VISTAS protocol. Section 3 describes the specific CALMET data and procedu r es that were used to develop a refined, 4-km spa ced

m e teorological grid for W i sconsin. Section 4 de scribes the CALPUFF i nput data and procedures,
and Section 5 discusses the POSTUTIL and CA LPOST processing, including the use of annual average natural background visibili ty. Section 6 p r esents the em i ssion and stack data that were
used f o r the BART eligible em ission units, a nd S ection 7 presents th e m o deling results. Appendices A and B present exam ple CALMET a nd CALPUFF input file listings. A portable
hard driv e is also being s u bm itted th at contains all input data, contro l files, output files, and

com puter codes used in the analys is.



# 2.0 VIST AS BART Pr otocol

The VISTAS m e m b er states hav e prepared a CA LPUFF modeling protocol for BART
determ inatio ns that is f u lly consis ten t with the EP A guidelines in 40 CFR Part 51 Appendix W and Appendix Y. The VISTAS protocol desc ribes a two-step CALPUFF analysis m e thodology
for BART exem ption analyses. The initial CALP UFF analysis uses a “s creen ing” or coarse
resolution m e teorological grid to determ ine if a particular source m a y be exem pted from further BART analyses. The screening results are also used to determ ine which Class I areas should be included in any refined analysis. Assum p tions for the initial screen ing a n al ysis are conservative
so that a sou r ce th at con t ributes to visibility im pa irm e nt is not exem pted in error. If a source is shown to contribute to visibility im pairm e nt us in g the in itial screen ing as sessm ent, the source h a s the option to undertake refined CA LPUFF modeling using finer m e te orological grids to evaluate further whether it is subject to BART.

VISTAS de veloped both coarse (12-km grid re solution) and refined (4-km grid resolution) CALMET files. The fine grid CALMET files ut ilized both MM5 prognostic data, as well as

m e teorological observational data for the CALMET “Step 2” calculations. Overwater (buoy) data were used in addition to the standard hourly su rface m e teorological obse rvations, precipitation

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## 6 Dece m b er 2010 

## observations, and twice-daily uppe r air sounding data. The VIST AS we bsite provides detailed
docum entation and supporting inform ation on th e refined C A LMET processing, including the
CALMET a nd CALPUFF input files th at contain model configurati on options and settings that have been optim ized after consultation with stak eholders and consulting experts. These sam e
CALMET a nd CALPUFF input files we re used as the basis for the refined W i sconsin analyses.

The VISTAS protocol discusses several options for defining the natural background visibility. These include use of the annual average na tural background extincti on or the background
extinction for the 20% best natu ral conditions days. Based on an em ail survey of the state agencies from the VISTAS m e mber states, all of the VISTAS states allowed the use of annual

average n a tu ral backgrou nd extinc tion for refined CALPUFF analyses . T h is is also the guidance provided by EPA Region 5 staff during discussions with DNR and the Wisconsin Paper Council,
and the m e thod approved by DNR i n their November 29, 2010 letter. T h erefore, the refined PCA CALPUFF modeling used the a nnual average natural backgr ound extinction for CALPOST processing.

The VISTAS BART guidance recomm ends that th e threshold value used to define whether a source “contributes” to visibility im pairm e nt is a 0.5 dv change from natural background
conditions. The 98 th 

## percentile 24-hr average predicted im pa ct at the Class I area (eq u al to the 8 th 

## highest value) is to be compared to th is contribu tion thresho l d value. Acc o rding to cla r if ica tion of the BART guidance received fro m EPA by t h e VISTAS workgroup, for a three-y ear sim u lation
the m odeling values to b e com p ared with the th reshold are the greatest of the three ann u al 8 th 

## highest values, or the 22 nd 

## highest value over all three years com b ined, whichever is greater.

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## 7 Dece m b er 2010 

# 3.0 CALMET Dat a an d Procedures

EPA has updated the versions of the appr oved CALPUFF program s since the 2007 modeling protocol was developed, and has provided addi tional guidance on CALMET “s witch” settings. The current approved versions are C A LPUFF version 5.8 (lev el 070623), and CALM ET version 5.8 (level 070623), and these versions were used for the updated refined B A RT CALPUFF analysis. On August 31, 2009, EPA published th e m e morandum “Clarification of EPA-FLM Recommended Settings for CALMET”. EPA stat ed that a 4 km fine CALMET grid size was acceptable, and provide d recomm ended CALM ET setting s . The CALMET setting s for the updated refined BART CALPUFF a n alysis m eet all current EPA recomm endations.

The first step in developm ent of the refined W i sconsin analysis was to define the CALMET
refined m o deling dom ain and grid. As discu ssed in Section 1, DNR’s screening analysis
indicated that there are three Cl ass I areas to the north of W i sc onsin, the Boundary Waters Canoe Area, Isle Royal National Park, and Seney W ildlife Area, where th e screening analy s is predic ts

som e level of visibility impact from W i sconsin BART eligible sources. Therefore, the

m e teorological grid was developed to ensure covera ge for th ese three Clas s I areas, as well as for the BART eligible source locations throughout W i sconsin. Standard IW AQM guidance also

recomm ends that the CALMET grid extend a m i ni m u m of 50 km beyond any Class I or em ission source location, so that puff recircula tion can be properly accounted for.

The refined CALMET grid was defined as a 4-k m spaced grid with 162 cells in the X

- axis and
191 in the Y

- axis. The grid projection was La m b ert Conformal Conic, us ing the sam e projection

param e ters as in the DNR screening analysis (t his allows the use of the sam e source X and Y
coordinates as in the DNR anal ysis). The projection param e te rs include R L AT0 = 40N, RLON0
= 97W
, XLAT1 = 33N, XLAT2 = 45N, XORIGKM = 247.0, YORIGKM = 240.0, and DATUM
= NAS-C.

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## 8 Dece m b er 2010 

## The m e teorological data that was input to CALMET included the sam e three years (2002-2004) of CALMM5 data used by DNR, which was pr ovided by LADCO. However, the refined
CALMET r uns also con s idered ob servation da ta from 22 surface station s , 16 precip itation stations, 5 overwater buoy stations , and 3 upper air stations. Figur e 2 is a plot of the refined CALPUFF modeling dom a in. Figure 3 presen ts a plot of the locati ons of the observation stations
in the m odeling dom ain.

The CAME T program MAKEGE O uses USGS GTOP O30 digital terrain data (which includes coverage in Canada) and USGS Composite Them e Grid Land Use and Land Cover (LULC) data to create a gridded data file on geophysical para m e ters that is used by CALMET. The available USGS LULC coverage does not extend into the Canadian areas of the refined dom ai n. These areas in Canada were assigned to the “forested land” category. Fi gure 4 presents a plot of the
land use data for the m o deling dom ain.

The VISTAS refined CALMET input files discussed in section 2 were used as the basis for the
refined W i sconsin CALMET input files. The sam e CALMET configuration settings and options were utilized, as they are repres entative of W i sconsin terrain and land use patterns. All settings
confor m with current EPA and FLM guidance.

Appendix A presents a listing of a CALMET input file developed for the refined analysis.

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## 9 Dece m b er 2010 

## Figure 2 – Refined CALPUFF Mode ling Dom a in and Locations of Class I Areas

300 400 50 0 600 700 8 0 0 300 400 500 600 700 800 900 1000

1



### -1 100 300 500 700 900 1100 1300 1500 1700 1900 2100 2300 2500 2700 2900 3100 3300 3500 3700 3900 4500

Te rr a i n (m)



## NOTE: The Class I a r ea recep tors a r e in red, th e PCA Mill lo cation is in blue, and th e X and Y
coordinates are th e Lambert pro j ection coordinates are in kms.

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## 10 Dece m b er 2010 

## Figure 3 – L o cations of Observational Stati ons in Refined CALPUF F M odeling Dom a in

30 0 400 50 0 600 7 0 0 8 0 0 900 1000 LCC East ( k m) Wiscons in Re fi ned C A LMET Loca t i on of Obse rvatio n statio ns

30 0 40 0 50 0 60 0 70 0 80 0 90 0 100 0LCC North (km)



## MIL W MADI LAC EAU GREE
M A N I

STUR WAUS MO S I CLIN

WISC

EAGL

MINE HAYW

JUNE DULT

MANI SAWY

HOUG ESCA IRN M IRNW MSUP

N M CH ESUP

WSUP

SMCH COPP

ES CA

HOUG IRON MANI SAUL

CLIN

GREE HA YW

LA C
MADI MARS ME NO

MILW RAIN

STURG GREE MN NP INTF



## NOTES: Surface station s are in red, overwater (b uoy) in blu e , precip itatio n in green, and upper air in purple.

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## 11 Dece m b er 2010 

## Figure 4 – L a nd Use Data for Refi ned CALPUFF Modeling Dom a in

300 400 500 60 0 7 0 0 80 0 LC C E a s t ( k m ) 300 400 500 600 700 800 900 1000LCC North(km) Snow/ I ce

T und ra

Bar r en

We tla n d

Wa te r

Fo r e s t

Ra ng e

Agr i cultur e

U r ban /Built -U p

Lan d U s e 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 . .

. . LCC Origin: 40N, 9 7 W

D a tum : NA S- C Matc hing Parallels: 33N, 45N False E a sting: 0.0 False Northing: 0.0

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## 12 Dece m b er 2010 

## Som e of the notable CA LMET c onfiguration settings included:

• CALMET vertical layers set to 10, with cell face heights at 20, 40, 80, 160, 320, 640, 1200, 2000, 3000, and 4000 m e ters,

• CALMET diagnostic options, includ ing slope flow effects (ISLOPE = 1) with the radius of influence of terrain (T ERRAD) set to 15 km
,

• EPA recomm ended CALMET settings for the ra dius 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 CALPUF F input files were used as the basis for the
refined W i sconsin CALPUFF input files. All C A LPUFF settings and op tions are con s isten t with EPA and FLM guidance, and the refined VISTAS protocol recomm endat i ons. The background ozone (O3) concentrations were used directly from the DNR CALPUFF input files. Instead of using m onthly 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 i nput file developed for the analysis.

The DNR screening analysis cons id e r ed thr ee em itted pollu ta nts, SO 2 

## , NOx, and PM 2. 5 

## . The refined CALPUFF modeling will co n s ider sp eciated particulate em issions, includ ing coarse PM (PMC), fine PM equivalent to PM 2. 5 

## (PMF), sulfate (SO4), nitrate (NO3), elem ental carbon (EC), and secondary organic aerosols (SOA or OC). Section 6 of this prot ocol describes how the speciated particulate em issions were calcu lated.

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## 13 Dece m b er 2010 

# 5.0 POSTUTIL and CALPOST Procedures

In CALPUFF, the scavenging of the available am monia for nitrate form ation is com p uted on a puf f

- by-puff basis. Beca use of the possibility of multiple puf f overlap, th is approa ch m a y tend to
overestim ate the am ount of a m m onia available to for m nitrate. In order to address the cum u lative

consum ption of a m m oni a, the POSTUTIL program can be used to repartition nitric acid and
nitrate. PO STUTIL calculates new NO3/HNO3 equi librium concentrations for the sam p le source in the Class I area using the b ackground ammonia. As recomm e nded in the VISTAS procedures for refined CALPUFF modeling, the POSTUTI L “MNITRATE=1” m e thod was used for the
refined W i sconsin CALPUFF modeling. Instead of using the m onthly values for background
ammonia concentrations from the DNR screen ing analyses, a single conservative background ammonia concentration of 3.9 ppb was used.

The m odeling protoco l s u bm itted in 2007 propos ed to use C A LPOST Vi sibility Method 6 to
calcu late v i s i bility im pacts. However, since that tim e there have been revisions to CALPOST that allow the use of the updated IMPROVE extin ction equation. CALP OST version 6.221 can
im ple m ent the “Method 8 Mode 5” m e thodology to calculate visibility impacts, and the FLMs

recomm end its use in “F ederal Land Managers’ Air Quality Related Values W o rk Group (FLAG) Phase I Report—Revised (2010)” (herein referred to as FLAG 2010). Therefore, this updated

m e thodology will be us ed for the PCA BART an alysis. Th e new CALPUFF Graphical Users
Interf ac e autom a tically e n ters the app r opria te va lues, based on the Class I area being selected, for natural background species and rela tive hum idity adjustm e nt factors using the data in T a bles 6 through 9 of Section 3.3.5 of FL AG 2010 (which are based on “Guidance for Estim ating Natural Visibility C onditions U nder the Reg i onal H aze Rule”, EPA-454/B-03-00 5, Septem be r 2003).

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## 14 Dece m b er 2010 

# 6.0 Emissions Modeled

EPA’s BART m odeling guidance state that the 24-hr m a xi mum actual em issions rates for the period of the m odeling simulation (2 002-2004) should be used for the anal ysis. If this data is not available, th en the short term “allowable” o r “po t ential” em ission rate s should be used. PCA provided D N R with source inform ation that has b een rev i ewed to determine the 24 -hr m a xim u m actual em issions rates. On Nove m b er 29, 2010, DNR issued a letter that approved the following

em ission rates to be used for the PCA BA RT eligible boiler: 166.3 g/sec (1320 lb/hr) SO 2 

## , 13.4 g/sec (106 lb/hr) NO X 

## , and 4.2 g/sec (33 lb/hr) for PM. The PM em issions have been speciated using the inform ation for coal fired boile rs developed by the National Park Service 1 

## . The speciated P M em issions listed in Table 1 were used in the refined BART m odeling. The stack

param e ters used in the modeling an alysis were the sam e as those used by DNR in their screening analys is.

Table 1 – P C A Speciated PM Em issions

PM Species Emission R a te (lb / hr)
Coarse PM 3.8

Fine PM 7.8
Elem ental Carbon 0.3 Condensable Inorganics (Sulfate) 17.2 Condensable Organics (OC) 4.3

1 

### h ttp ://www2 .natu r e.np s.g o v / air/p e rm its/ec t/i n d e x

. cfm )

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## 15 Dece m b er 2010 

# 7.0 Modeling Result s

CALPOST com putes the daily m a ximum change in deciviews relative to the annual average
natural back ground visib ility, separately for each Class I area. For evaluating the sou r ce im pact relative to the “Subject to BA RT” vi sibility im pa ct thres hold of 0.5 dv, the daily m a ximum changes in v i sibility are sorted to determ ine the 98th percentile (8 th 

## highest) value for each of three y ears, and the 98th percen tile (22 nd 

## highest) value for the com p leted 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 exem pt from the BART requirem e nts.

Another equivalent m e tric commonly used for BART exe m ption m odeling is to sum the num ber of days per year th at are above the 0. 5 dv thresh o l d for each Class I area se parately ; if there are 7 or fewer days above the threshold for each year, th en the 98 th 

## percentile value is also below the
threshold. T h is is the m e tric approved by DNR for use in the BART modeling analysis. Specifically, for each Class I area separately, if th ere are less than 8 days per year that the predicted visibility im pa cts are greater than 0.5 deciviews relative to th e annual average natural background visibility, th en the BART eligib le em ission units at th e m o deled facility will be
determ ined not to be Subject to BART.

Table 2 presents the results from the refi ned CALPUFF BART exem ption m odeling. These
results dem onstrate th at there are less than 8 days per year, at each ind i vi d u al Class I area, when
the vis i bility im pacts from the PCA BART eligible em ission unit are abo v e 0.5 dv. Therefore, th e PCA BART elig ible sou rce is not S ubject to B ART requirem e nts.Updated BARTModeling Protocol andReportforPCATomahawkMillTable 2 – PCA CALPUFF BART Exemption Results SummaryClass I areaDistance(km)fromsourcetoClass I areaboundary# of dayswith impact> 0.5 dv inClass I area:2002# of days withimpact > 0.5dv in Class Iarea: 2003# of dayswith impact> 0.5 dv inClass I area:2004# of days withimpact > 0.5dv in Class Iarea for 3 yearperiodMaximum 98thPercentileimpact overeither annualor 3-yr periodsSeney, MI~ 28000110.18Isle Royal, MN~ 32000000.14BoundaryWaters,MN~ 35000000.1316December 2010

### Refine d BAR T Modeling P r otoc ol for PCA T o ma hawk Mill



## Appendix A – Example CALMET Input File

Dece m b er 2010

### Refine d BAR T Modeling P r otoc ol for PCA T o ma hawk 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)

Dece m b er 2010

### Refine d BAR T Modeling P r otoc ol for PCA T o ma hawk 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

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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

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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

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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

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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

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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. !

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(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

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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

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

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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

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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 !

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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

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(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

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-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 !

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(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 !

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! 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 !

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! 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 !

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

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## Appendix B – Example CALP U FF Input File

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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

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

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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!

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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!

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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!

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### Refine d BAR T Modeling P r otoc ol for PCA T o ma hawk 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!

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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!

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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!

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

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### Refine d BAR T Modeling P r otoc ol for PCA T o ma hawk 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. !

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!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

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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

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### Refine d BAR T Modeling P r otoc ol for PCA T o ma hawk 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

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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!

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

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(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:

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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

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

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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

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---- 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

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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

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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

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

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!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 !

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* 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

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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 !

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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

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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 !

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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.

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(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

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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.

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

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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

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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)

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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)

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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+)

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-------- 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.

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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 RE CE PTOR COORDINAT ES FOLLOW I N INPUT FI LE

Dece m b er 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 Prot ocol and Final Report for Thilmany “Subject to BART” Analysis

TABLE OF CO NTENTS

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 Em issions Modeled

............................................................................................................... 14 7.0 Modeling R e sults

.................................................................................................................. 15

List of Figures Figure 1 - WDNR Screen ing CALPUFF Domain

.......................................................................... 2 Figure 2 – Refined CALPUFF Mode ling Dom a in and Locations of Class I Areas

....................... 9 Figure 3 – L o cations of Observational Stati ons in Refined CALPUFF M odeling Dom a in

......... 10 Figure 4 – L a nd Use Data for Refi ned CALPUFF Modeling Dom a in

......................................... 11

List of Tables
Table 1 – T h ilm any Speciated PM Em issions

.............................................................................. 14
Table 2 – T h ilm any CALPUFF BART Exe m ption Results S u mm ary

......................................... 16

Appendix A – Exam ple CALMET I nput File Appendix B – Exam ple CALPUFF I nput File

i

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## 1 Dece m b er 2010 

# 1.0 Introduct i on

The W i sconsin Departm e nt of Natural Resour ces (DNR) perform e d single source screening modeling in 2006 to evaluate which Best Availabl e Retrofit Technology (BAR T) eligible sources
in the s t ate m a y “cause or contri bute” to visibility im pairm e nt a nd could therefore b e subjec t to BART requirem e nts. This type of analysis is referred to as the “subj e c t to BART” or “BART

exem ption” analysis. The m e thods used by DNR ar e described in the “S in gle Source Modeling to Support Regional Haze BART Modeling Pro t ocol”, March 2 1, 2006, prepared by Lake Mich igan
Air Direc t ors Consortiu m (LADCO).

DNR applied CALPUFF to each B A RT eligible source for three annual periods, co vering the calendar years 2002 to 2004. The CALPUFF/CA LMET m o deling dom ain consisted of ninetyseven 36-k m spaced cells in the eas t -west d i rect ion and ninety 36-km spaced cells in the northsouth direction (see Figure 1) . Meteorological data genera ted by the MM5 prognostic weather model (provided by LADCO in CALMM5 for m at) wa s used to develop the m e teorological data for CALPUFF, without additional observational data input (i.e., NOOBS mode). This represents

a coars e m e teorolog ical gr id, suitable for an initial screening analysis.

The results from DNR’s screen i ng analysis indicated that, with the excep tion of som e of the larges t electric power s t ations in the state, the on ly Class I areas where B A RT eligible sources

m a y contribute to visibility im pairment are th e three areas to the nor th of W i sconsin, the Boundary Waters Canoe Area, Isle Royal Natio nal Park, and Seney W ildlife Area. DNR’s

screen ing an alysis also indicated that the BA RT eligible em issions unit at the Thilm a ny Kaukauna Mill (Thilmany) m a y “cause or con t ribute” to v i sibility im pairm e nt at the Seney Class I area (lo cated approxim a tely 280 k m to the northeas t of the m ill), as defined by the 98 th 

## percentile visibility im pa cts being greater than 0.5 deciviews ( dv) relative to natural background.

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## 2 Dece m b er 2010 

## Figure 1 - WDNR Screening CALPUFF Do main

NOTE: Class I areas a re identified by red marks.

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## 3 Dece m b er 2010 

## Thilm any has elected to refine the D N R scr eening analysis by conducting refined CALPUFF modeling with a 4 km meteorologi cal grid, based on procedures descr i bed in the “Visibility

Im prove m e nt – State and Tribal Association of the Southeast (VISTA S) BART CAL P UFF” modeling protocol. The VISTAS pr otocol wa s developed by a large group of stakeholders,
includ ing EPA, the VISTAS m e mber state agen cies and tribes, the Federal Land Managers (FLMs), industry representatives, and consulting experts. Given the resources expended on the VISTAS protocol, it arguably represents the m o st com p rehensive CALPUFF BART protocol ever developed.

Thilm any had discussions with DNR and EPA Re gion 5 staff about refining the analysis, and
subm itted a refined CALPUFF BART m odeling pr otoco l in March 2007. EPA reviewed the protocol and provided m i nor comm ents to DNR in May 2010. Thilm any responded to these comments in a letter “Response to E P A Comme nt s on Thilm any BART Modeling Protocol” dated

Nove m b er 9, 2010. In addition, s ubs equent to th e EPA protocol comm ents, the US Fish and

W ildlife Service and US Forest Serv ice rev i ewed the protocol and had addi tional discussions with
DNR and EPA. The three EPA comm ents, and each response, are listed below.

Comment 1
Inform ation needs to be presented which clar ifies how POSTUTIL was used for ammonia. Response 1
The VISTAS m e thodology was used, with a MNITRATE switch setting of one (1).

Comment 2
The m odeling m u st include a copy of the input and list files associated with runs. The protocol only offers som e of the control file infor m ation. Response 2 All CALMET, CALPUFF, and CALPOST input and list files, as well as m e teorological and geophysical data files, had been provided by Thil m a ny to DNR on a portable hard disk drive.

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## 4 Dece m b er 2010 

## Thilm any will again p r o v ide a por ta ble hard d i s k drive of all m odeling files to DNR f o r the updated BART analysis, for purposes of SIP docum entation.

Comment 3
The Thilm a ny input file ... uses the background ammonia values that were produced f o r the LADCO protocol. These values are based on m o deled estim ates. Monitoring data has generally
shown m u ch higher ammonia than w h at was used f r om the model resu lts. The refined m odeling analyses for Thilm any ... m u st evaluate the visibility im pacts using m easured background
ammonia values. Response 3
The US Fish and W ildlif e Service proposed usin g a constant background ammonia concentration of 3.9 ppb, which was the highest concentration m easured at the Mayv ille W i sconsin station during a m i d-1990s EPA study. Thilm any has agreed to use this single, conservative background value in the absence of daily data.

On Nove m b er 29, 2010, DNR issued a letter that approved the Thilm any CALPUFF BART protocol, as well as the em ission rates to be used for the BART eligible em ission units. DNR requested that the 2007 version of the protocol be updated to include the responses to EPA comments, and text that addr esses current CALPUFF m odeling guidance. In addition, the updated m o deling results could be pr esented in the protocol (so that all infor m ation is located in
one docum e n t).

This document is the updated m odeling protoc ol and final m o deling report for the refined
Thilm any “Subject to BART” analysis. This docum e nt does not duplicate the extensive
inform ation on visibility, CALPUFF, and EPA gu idance on B A RT modeling procedures that are contained in the VISTAS protocol . Rather, this docum ent describe s ho w data spec if ic to this setting will be used in the refined C A LPUFF modeling. Secti on 1 of the protocol is this introduction. Section 2 briefly sum m a rizes im po rtant concepts from the VISTAS protocol.

### Upd a te d B A R T Modeling P r otoc ol and Repor t for Thilma n y Kaukauna Mill



## 5 Dece m b er 2010 

## Section 3 describes the specific CALMET data a nd procedures that were used to develop a refined, 4-k m spaced meteoro l ogical grid for W i sc onsin. Se ction 4 describes th e CALPUFF input data and procedures, and Section 5 discu sses the POSTUTIL and CALPOST processing, including the use of annual averag e natural background visi bility. Section 6 pr esents the em ission and stack data that were used for the BART elig ible em ission units, and S ection 7 presents the modeling results. Appendices A and B presen t exam ple CALMET and CALPUFF i nput file listings. A p o rtab le hard drive is also being subm itted that con t ains all inp u t data, control f ile s, output files, and com put er c odes used in the analysis.



# 2.0 VIST AS BART Pr otocol

The VISTAS m e m b er states hav e prepared a CA LPUFF modeling protocol for BART
determ inatio ns that is f u lly consis ten t with the EP A guidelines in 40 CFR Part 51 Appendix W and Appendix Y. The VISTAS protocol desc ribes a two-step CALPUFF analysis m e thodology
for BART exem ption analyses. The initial CALP UFF analysis uses a “s creen ing” or coarse
resolution m e teorological grid to determ ine if a particular source m a y be exem pted from further BART analyses. The screening results are also used to determ ine which Class I areas should be included in any refined analysis. Assum p tions for the initial screen ing a n al ysis are conservative
so that a sou r ce th at con t ributes to visibility im pa irm e nt is not exem pted in error. If a source is shown to contribute to visibility im pairm e nt us in g the in itial screen ing as sessm ent, the source h a s the option to undertake refined CA LPUFF modeling using finer m e te orological grids to evaluate further whether it is subject to BART.

VISTAS de veloped both coarse (12-km grid re solution) and refined (4-km grid resolution) CALMET files. The fine grid CALMET files ut ilized both MM5 prognostic data, as well as

m e teorological observational data for the CALMET “Step 2” calculations. Overwater (buoy) data were used in addition to the standard hourly su rface m e teorological obse rvations, precipitation observations, and twice-daily uppe r air sounding data. The VIST AS we bsite provides detailed

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## 6 Dece m b er 2010 

## docum entation and supporting inform ation on th e refined C A LMET processing, including the
CALMET a nd CALPUFF input files th at contain model configurati on options and settings that have been optim ized after consultation with stak eholders and consulting experts. These sam e
CALMET a nd CALPUFF input files we re used as the basis for the refined W i sconsin analyses.

The VISTAS protocol discusses several options for defining the natural background visibility. These include use of the annual average na tural background extincti on or the background
extinction for the 20% best natu ral conditions days. Based on an em ail survey of the state agencies from the VISTAS m e mber states, all of the VISTAS states allowed the use of annual

average n a tu ral backgrou nd extinc tion for refined CALPUFF analyses . T h is is also the guidance provided by EPA Region 5 staff during discussions with DNR and the Wisconsin Paper Council,
and the m e thod approved by DNR i n their Novemb er 29, 2010 letter. T h erefore, the refined
Thilm any CALPUFF modeling used the annual average natura l background extinction for CALPOST processing.

The VISTAS BART guidance recomm ends that th e threshold value used to define whether a source “contributes” to visibility im pairm e nt is a 0.5 dv change from natural background
conditions. The 98 th 

## percentile 24-hr average predicted im pa ct at the Class I area (eq u al to the 8 th 

## highest value) is to be compared to th is contribu tion thresho l d value. Acc o rding to cla r if ica tion of the BART guidance received fro m EPA by t h e VISTAS workgroup, for a three-y ear sim u lation
the m odeling values to b e com p ared with the th reshold are the greatest of the three ann u al 8 th 

## highest values, or the 22 nd 

## highest value over all three years com b ined, whichever is greater.

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## 7 Dece m b er 2010 

# 3.0 CALMET Dat a an d Procedures

Since the 2007 version of the m odeling protocol was developed, EPA has updated the versions of the approved CALPUFF program s, and has prov ided additional guidance on CALMET “switch” settings. T h e 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 a n alysis. On August 31, 2009, EPA pub lished the m e morandum “Clarification of EPA-FLM Recommended Settings for CALMET”. EPA stated that a 4 km fine CALMET grid size was acceptable, and provide d recomm ended CALMET s e ttings . The CALMET s e ttings for the updated refined BART CALPUFF analysis m eet all current EPA recomm endations.

The first step in developm ent of the refined W i sconsin analysis was to define the CALMET
refined m o deling dom ain and grid. As discu ssed in Section 1, DNR’s screening analysis
indicated that there are three Cl ass I areas to the north of W i sc onsin, the Boundary Waters Canoe Area, Isle Royal National Park, and Seney W ildlife Area, where th e screening analy s is predic ts

som e level of visibility impact from W i sconsin BART eligible sources. Therefore, the

m e teorological grid was developed to ensure covera ge for th ese three Clas s I areas, as well as for the BART eligible source locations throughout W i sconsin. Standard IW AQM guidance also

recomm ends that the CALMET grid extend a m i ni m u m of 50 km beyond any Class I or em ission source location, so that puff recircula tion can be properly accounted for.

The refined CALMET grid was defined as a 4-k m spaced grid with 162 cells in the X

- axis and
191 in the Y

- axis. The grid projection was La m b ert Conformal Conic, us ing the sam e projection

param e ters as in the DNR screening analysis (t his allows the use of the sam e source X and Y
coordinates as in the DNR anal ysis). The projection param e te rs include R L AT0 = 40N, RLON0
= 97W
, XLAT1 = 33N, XLAT2 = 45N, XORIGKM = 247.0, YORIGKM = 240.0, and DATUM
= NAS-C.

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## 8 Dece m b er 2010 

## The m e teorological data that was input to CALMET included the sam e three years (2002-2004) of CALMM5 data used by DNR, which was pr ovided by LADCO. However, the refined
CALMET r uns also con s idered ob servation da ta from 22 surface station s , 16 precip itation stations, 5 overwater buoy stations , and 3 upper air stations. Figur e 2 is a plot of the refined CALPUFF modeling dom a in. Figure 3 presen ts a plot of the locati ons of the observation stations
in the m odeling dom ain.

The CAME T program MAKEGE O uses USGS GTOP O30 digital terrain data (which includes coverage in Canada) and USGS Composite Them e Grid Land Use and Land Cover (LULC) data to create a gridded data file on geophysical para m e ters that is used by CALMET. The available USGS LULC coverage does not extend into the Canadian areas of the refined dom ai n. These areas in Canada were assigned to the “forested land” category. Fi gure 4 presents a plot of the
land use data for the m o deling dom ain.

The VISTAS refined CALMET input files discussed in section 2 were used as the basis for the
refined W i sconsin CALMET input files. The sam e CALMET configuration settings and options were utilized, as they are repres entative of W i sconsin terrain and land use patterns. All settings
confor m with current EPA and FLM guidance.

Appendix A presents a listing of a CALMET input file developed for the refined analysis.

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## 9 Dece m b er 2010 

## Figure 2 – Refined CALPUFF Mode ling Dom a in and Locations of Class I Areas

30 0 4 0 0 5 0 0 6 0 0 70 0 8 00 LC C E a s t (k m ) 30 0 40 0 50 0 60 0 70 0 80 0 90 0 10 0 0LCCNorth(km)

1

-1 10 0 30 0 50 0 70 0 90 0 11 0 0 13 0 0 15 0 0 17 0 0 19 0 0 21 0 0 23 0 0 25 0 0 27 0 0 29 0 0 31 0 0 33 0 0 35 0 0 37 0 0 39 0 0 45 0 0

Te r r a i n ( m ) L C C O r ig in : 4 0 N
, 9 7 W M a t c hi ng P a r a l l e l s : 33 N
, 4 5 N



### Bounda ry Wa ters

Is le Royale

Seney



## NOTE: The Class I a r ea recep tors a r e in red, th e Thilm any mill loca tion is in blue, an d the X and Y coordinates are the Lambert proj ection coordinates are in km s.

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## 10 Dece m b er 2010 

## Figure 3 – L o cations of Observational Stati ons in Refined CALPUF F M odeling Dom a in

30 0 400 50 0 600 7 0 0 8 0 0 900 1000 LCC East ( k m) Wiscons in Re fi ned C A LMET Loca t i on of Obse rvatio n statio ns

30 0 40 0 50 0 60 0 70 0 80 0 90 0 100 0LCC North (km)



## MIL W MADI LAC EAU GREE
M A N I

STUR WAUS MO S I CLIN

WISC

EAGL

MINE HAYW

JUNE DULT

MANI SAWY

HOUG ESCA IRN M IRNW MSUP

N M CH ESUP

WSUP

SMCH COPP

ES CA

HOUG IRON MANI SAUL

CLIN

GREE HA YW

LA C
MADI MARS ME NO

MILW RAIN

STURG GREE MN NP INTF



## NOTES: Surface station s are in red, overwater (b ouy) in blu e , precip itatio n in green, and upper air in purple.

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## 11 Dece m b er 2010 

## Figure 4 – L a nd Use Data for Refi ned CALPUFF Modeling Dom a in

300 400 500 60 0 7 0 0 80 0 LC C E a s t ( k m ) 300 400 500 600 700 800 900 1000LCC North(km) Snow/ I ce

T und ra

Bar r en

We tla n d

Wa te r

Fo r e s t

Ra ng e

Agr i cultur e

U r ban /Built -U p

Lan d U s e 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 . .

. . LCC Origin: 40N, 9 7 W

D a tum : NA S- C Matc hing Parallels: 33N, 45N False E a sting: 0.0 False Northing: 0.0

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## 12 Dece m b er 2010 

## Som e of the notable CA LMET c onfiguration settings included:

• CALMET vertical layers set to 10, with cell face heights at 20, 40, 80, 160, 320, 640, 1200, 2000, 3000, and 4000 m e ters,

• CALMET diagnostic options, includ ing slope flow effects (ISLOPE = 1) with the radius of influence of terrain (T ERRAD) set to 15 km
,

• EPA recomm ended CALMET settings for the ra dius 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 CALPUF F input files were used as the basis for the
refined W i sconsin CALPUFF input files. All C A LPUFF settings and op tions are con s isten t with EPA and FLM guidance, and the refined VISTAS protocol recomm endat i ons. The background ozone (O3) concentrations were used directly from the DNR CALPUFF input files. Instead of using m onthly 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 i nput file de veloped for the Thilm any analysis.

The DNR screening analysis cons id e r ed thr ee em itted pollu ta nts, SO 2 

## , NOx, and PM 2. 5 

## . The refined CALPUFF modeling will co n s ider sp eciated particulate em issions, includ ing coarse PM (PMC), fine PM equivalent to PM 2. 5 

## (PMF), sulfate (SO4), nitrate (NO3), elem ental carbon (EC), and secondary organic aerosols (SOA or OC). Section 6 of this prot ocol describes how the speciated particulate em issions were calcu lated.

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## 13 Dece m b er 2010 

# 5.0 POSTUTIL and CALPOST Procedures

In CALPUFF, the scavenging of the available am monia for nitrate form ation is com p uted on a puf f

- by-puff basis. Beca use of the possibility of multiple puf f overlap, th is approa ch m a y tend to
overestim ate the am ount of a m m onia available to for m nitrate. In order to address the cum u lative

consum ption of a m m oni a, the POSTUTIL program can be used to repartition nitric acid and
nitrate. PO STUTIL calculates new NO3/HNO3 equi librium concentrations for the sam p le source in the Class I area using the b ackground ammonia. As recomm e nded in the VISTAS procedures for refined CALPUFF modeling, the POSTUTI L “MNITRATE=1” m e thod was used for the
refined W i sconsin CALPUFF modeling. Instead of using the m onthly values for background
ammonia concentrations from the DNR screen ing analyses, a single conservative background ammonia concentration of 3.9 ppb was used.

The m odeling protoco l s u bm itted in 2007 propos ed to use C A LPOST Vi sibility Method 6 to
calcu late v i s i bility im pacts. However, since that tim e there have been revisions to CALPOST that allow the use of the updated IMPROVE extin ction equation. CALP OST version 6.221 can
im ple m ent the “Method 8 Mode 5” m e thodology to calculate visibility impacts, and the FLMs

recomm end its use in “F ederal Land Managers’ Air Quality Related Values W o rk Group (FLAG) Phase I Report—Revised (2010)” (herein referred to as FLAG 2010). Therefore, this updated

m e thodology will be us ed for the Thilm a ny BART analysis. The new CA LPUFF Graphical Users
Interf ac e autom a tically e n ters the app r opria te va lu es, based on the Class I ar ea being selected, for natural background species and rela tive hum idity adjustm e nt factors using the data in T a bles 6 through 9 of Section 3.3.5 of FL AG 2010 (which are based on “Guidance for Estim ating Natural Visibility C onditions U nder the Reg i onal H aze Rule”, EPA-454/B-03-00 5, Septem be r 2003).

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## 14 Dece m b er 2010 

# 6.0 Emissions Modeled

EPA’s BART m odeling guidance state that the 24-hr m a xi mum actual em issions rates for the period of the m odeling simulation (2 002-2004) should be used for the anal ysis. If this data is not available, th en the short term “allowable” o r“p otential” em ission rates should be used. Thilm any provided D N R with source inform ation that has b een rev i ewed to determine the 24 -hr m a xim u m actual em issions rates. The SO2 e m issions are based on the m a xi m u m a c tual em ission rate from the CEMS during the 2002-04 tim e fram e , and the PM and NOx e m issions represent m a xi m u m potential em ission rates (which is conservative). On Nove m b er 29, 2010, DNR issued a letter that approved the following em ission rates to be used for the Thilm a ny BART eligible boiler: 207.9 g/sec (1650 lb/hr) SO 2 

## , 68.2 g/sec (541 lb/hr) NO X 

## , and 11.1 g/sec (88 lb/hr) for PM. The PM

em issions have been speciated using the inform ation for coal fired boi lers developed by the
National Pa r k Service 1 

## . The speciated PM em issions lis ted in Table 1 were used in the refined BART modeling. The stack param e ters used in the m odeling analysis were the sam e as those used by DNR in their screening analysis.

Table 1 – T h ilm any Speciated PM Em issions

PM Species Emission R a te (lb / hr)
Coarse PM 2.9

Fine PM 3.4
Elem ental Carbon 0.1 Condensable Inorganics (Sulfate) 65.3 Condensable Organics (OC) 16.3

1 

### h ttp ://www2 .natu r e.np s.g o v / air/p e rm its/ec t/i n d e x

. cfm )

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## 15 Dece m b er 2010 

# 7.0 Modeling Result s

CALPOST com putes the daily m a ximum change in deciviews relative to the annual average
natural back ground visib ility, separately for each Class I area. For evaluating the sou r ce im pact relative to the “Subject to BA RT” vi sibility im pa ct thres hold of 0.5 dv, the daily m a ximum changes in v i sibility are sorted to determ ine the 98th percentile (8 th 

## highest) value for each of three y ears, and the 98th percen tile (22 nd 

## highest) value for the com p leted 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 exem pt from the BART requirem e nts.

Another equivalent m e tric commonly used for BART exe m ption m odeling is to sum the num ber of days per year th at are above the 0. 5 dv thresh o l d for each Class I area se parately ; if there are 7 or fewer days above the threshold for each year, th en the 98 th 

## percentile value is also below the
threshold. T h is is the m e tric approved by DNR for use in the BART modeling analysis. Specifically, for each Class I area separately, if th ere are less than 8 days per year that the predicted visibility im pa cts are greater than 0.5 deciviews relative to th e annual average natural background visibility, th en the BART eligib le em ission units at th e m o deled facility will be
determ ined not to be Subject to BART.

Table 2 presents the results from the refi ned CALPUFF BART exem ption m odeling. These
results dem onstrate th at there are less than 8 days per year, at each ind i vi d u al Class I area, when
the vis i bility im pacts from the Thilmany BART e lig ib le sou r ce are abov e 0.5 dv. Therefore, the Thilmany BART eligible source is not Subject to BART re quirem e nts.Updated BARTModeling Protocol andReportforThilmanyKaukaunaMillTable 2 – Thilmany CALPUFF BART Exemption Results SummaryClass I areaDistance(km)fromsourcetoClass I areaboundary# of dayswith impact> 0.5 dv inClass I area:2002# of days withimpact > 0.5dv in Class Iarea: 2003# of dayswith impact> 0.5 dv inClass I area:2004# of days withimpact > 0.5dv in Class Iarea for 3 yearperiodMaximum 98thPercentileimpact overeither annualor 3-yr periodsSeney, MI~ 28020130.34Isle Royal, MN~ 40000000.14BoundaryWaters,MN~ 45010010.1116December 2010

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## Appendix A – Example CALMET Input File

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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)

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

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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

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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

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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

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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

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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. !

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(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

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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

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

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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

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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 !

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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

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(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

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-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 !

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(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 !

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! 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 !

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! 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 !

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

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## Appendix B – Example CALP U FF Input File

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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

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

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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 !

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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)

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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

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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

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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!

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! 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)

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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 !

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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)

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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)

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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 !

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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)

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

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,

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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 !

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!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

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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)

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(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

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(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

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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

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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 !

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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.

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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.

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

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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

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

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-------- 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

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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).

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

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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.

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-------------------------------------------------------------------------------
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 RE CE PTOR COORDINAT ES FOLLOW I N INPUT FI LE

Dece m b er 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 Prot ocol and Final Report for Wausau “Subject to BART” Analysis

TABLE OF CO NTENTS

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 Em issions Modeled

.......................................................................................................... ..... 14 7.0 Modeling R e sults

........................................................................................................... ....... 16

List of Figures Figure 1 - WDNR Screen ing CALPUFF Domain

.......................................................................... 2 Figure 2 – Refined CALPUFF Mode ling Dom a in and Locations of Class I Areas

....................... 9 Figure 3 – L o cations of Observational Stati ons in Refined CALPUFF M odeling Dom a in

......... 10 Figure 4 – L a nd Use Data for Refi ned CALPUFF Modeling Dom a in

......................................... 11

List of Tables Table 1 – WAUSAU Speciat ed PM Em issions

............................................................................ 15
Table 2 – WAUSAU CALPUFF BART Exe m ption Results S u mm ary

....................................... 17

Appendix A – Exam ple CALMET I nput File Appendix B – Exam ple CALPUFF I nput File

i

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## 1 Dece m b er 2010 

# 1.0 Introduct i on

The W i sconsin Departm e nt of Natural Resour ces (DNR) perform e d single source screening modeling in 2006 to evaluate which Best Availabl e Retrofit Technology (BAR T) eligible sources
in the s t ate m a y “cause or contri bute” to visibility im pairm e nt a nd could therefore b e subjec t to BART requirem e nts. This type of analysis is referred to as the “subj e c t to BART” or “BART

exem ption” analysis. The m e thods used by DNR ar e described in the “S in gle Source Modeling to Support Regional Haze BART Modeling Pro t ocol”, March 2 1, 2006, prepared by Lake Mich igan
Air Direc t ors Consortiu m (LADCO).

DNR applied CALPUFF to each B A RT eligible source for three annual periods, co vering the calendar years 2002 to 2004. The CALPUFF/CA LMET m o deling dom ain consisted of ninetyseven 36-k m spaced cells in the eas t -west d i rect ion and ninety 36-km spaced cells in the northsouth direction (see Figure 1) . Meteorological data genera ted by the MM5 prognostic weather model (provided by LADCO in CALMM5 for m at) wa s used to develop the m e teorological data for CALPUFF, without additional observational data input (i.e., NOOBS mode). This represents

a coars e m e teorolog ical gr id, suitable for an initial screening analysis.

The results from DNR’s screen i ng analysis indicated that, with the excep tion of som e of the larges t electric power s t ations in the state, the on ly Class I areas where B A RT eligible sources

m a y contribute to visibility im pairment are th e three areas to the nor th of W i sconsin, the Boundary Waters Canoe Area, Isle Royal Natio nal Park, and Seney W ildlife Area. DNR’s

screen ing an alysis also indicated that the BART eligible em issions unit at the W a usau Paper Mills LLC Mosinee Mill (W ausau) m a y “cause or con t ri bu te” to visibility im pairm e nt at the Seney
Class I a r ea (loca t ed app r oxim a tely 3 20 km to the northeas t of the m ill), as def i ned by the 98 t h 

## percentile visibility im pa cts being greater than 0.5 deciviews ( dv) relative to natural background.

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## 2 Dece m b er 2010 

## Figure 1 - WDNR Screening CALPUFF Do main

NOTE: Class I areas a re identified by red marks.

### Upd a te d B A R T Modeling P r otoc ol and Repor t for W

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## 3 Dece m b er 2010 

## Wausau has elected to refine the D N R scr eening analysis by conducting refined CALPUFF modeling with a 4 km meteorologi cal grid, based on procedures descr i bed in the “Visibility

Im prove m e nt – State and Tribal Association of the Southeast (VISTA S) BART CAL P UFF” modeling protocol. The VISTAS pr otocol wa s developed by a large group of stakeholders,
includ ing EPA, the VISTAS m e mber state agen cies and tribes, the Federal Land Managers (FLMs), industry representatives, and consulting experts. Given the resources expended on the VISTAS protocol, it arguably represents the m o st com p rehensive CALPUFF BART protocol ever developed.

Wausau had discussions with DNR a nd EPA Regi on 5 staff about refining the analysis, and
subm itted a refined CALPUFF BART m odeling pr otoco l in March 2007. EPA reviewed the
protoco l and provided m i nor comm ents to DNR in May 2010. Another facility und ergo ing Subject to BART review, Thilm any, responded to these com m e nts in a letter “Response to EPA
Comm ents on Thilm any BART Modeling Protoc ol” dated Novem b er 9, 2010. In addition, subsequent to the EPA protocol comm ents, the US Fish and W ildlife Service and US Forest Service reviewed the protocol and had additional discussions with DNR a nd EPA. The three EPA comments, and each resp onse, are lis ted below.

Comment 1
Inform ation needs to be presented which clar ifies how POSTUTIL was used for ammonia. Response 1
The VISTAS m e thodology was used, with a MNITRATE switch setting of one (1).

Comment 2
The m odeling m u st include a copy of the input and list files associated with runs. The protocol only offers som e of the control file infor m ation.

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## 4 Dece m b er 2010 

## Response 2 All CALMET, CALPUFF, and CALPOST input and list files, as well as m e teorological and geophysical data files, had been provided by W a us au to DNR on a portable hard disk drive. Wausau will again provide a portable hard disk drive of all modeling file s to DNR for the updated BART analysis, for purposes of SIP docum entation.

Comment 3 The input file ... uses the background ammoni a values that were produced for the L ADCO protocol. These values are based on m odeled es tim a tes. Monitoring data has generally shown much higher ammonia than what was used fr om t h e m odel results. The refined m odeling analyses ... must evaluate the visibility im p acts using m easured background ammonia values. Response 3
The US Fish and W ildlif e Service proposed usin g a constant background ammonia concentration of 3.9 ppb, which was the highest concentration m easured at the Mayv ille W i sconsin station during a m i d-1990s EPA study. W a us au has agreed to use this single, conservative background value in the absence of daily data.

On Nove m b er 29, 2010, DNR issued a letter that approved the CALPUFF BART prot ocol, as
well as the e m ission rate s to be used f o r the BA RT eligible em ission units. DNR requested that the 2007 version of the protocol be updated to in clude the responses to E P A comm ents, and text
that addresses current C A LPUFF modeling guidance. In additi on, the updated m odeling results could be presented in the prot oco l (so that a ll inf o rm ation is located in one docum ent).

This document is the updated m odeling protocol and final m o deling report for the refined W a usau “Subject to BART” analysis. This docum e nt does not duplicate the extensive inform ation on visibility, CALPUFF, and EPA gui dance on BART modeling procedures that are contained in the VISTAS protocol. Rath e r , this do cu m e nt describe s how data specif i c to th is se tting will be us ed
in the refined CALPUFF m odeling. Section 1 of the protocol is this introduction. Section 2

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## 5 Dece m b er 2010 

## briefly sum m a rizes im portant concepts from th e VISTAS protocol. Section 3 describes the specific CALMET data and procedu r es that were used to develop a refined, 4-km spa ced

m e teorological grid for W i sconsin. Section 4 de scribes the CALPUFF i nput data and procedures,
and Section 5 discusses the POSTUTIL and CA LPOST processing, including the use of annual average natural background visibili ty. Section 6 p r esents the em i ssion and stack data that were
used f o r the BART eligible em ission units, a nd S ection 7 presents th e m o deling results. Appendices A and B present exam ple CALMET a nd CALPUFF input file listings. A portable
hard driv e is also being s u bm itted th at contains all input data, contro l files, output files, and

com puter codes used in the analys is.



# 2.0 VIST AS BART Pr otocol

The VISTAS m e m b er states hav e prepared a CA LPUFF modeling protocol for BART
determ inatio ns that is f u lly consis ten t with the EP A guidelines in 40 CFR Part 51 Appendix W and Appendix Y. The VISTAS protocol desc ribes a two-step CALPUFF analysis m e thodology
for BART exem ption analyses. The initial CALP UFF analysis uses a “s creen ing” or coarse
resolution m e teorological grid to determ ine if a particular source m a y be exem pted from further BART analyses. The screening results are also used to determ ine which Class I areas should be included in any refined analysis. Assum p tions for the initial screen ing a n al ysis are conservative
so that a sou r ce th at con t ributes to visibility im pa irm e nt is not exem pted in error. If a source is shown to contribute to visibility im pairm e nt usin g the in itial screen ing as sessm ent, the source h a s the option to undertake refined CA LPUFF modeling using finer m e te orological grids to evaluate further whether it is subject to BART.

VISTAS de veloped both coarse (12-km grid re solution) and refined (4-km grid resolution) CALMET files. The fine grid CALMET files ut ilized both MM5 prognostic data, as well as

m e teorological observational data for the CALMET “Step 2” calculations. Overwater (buoy) data were used in addition to the standard hourly su rface m e teorological obse rvations, precipitation

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## 6 Dece m b er 2010 

## observations, and twice-daily uppe r air sounding data. The VIST AS we bsite provides detailed
docum entation and supporting inform ation on th e refined C A LMET processing, including the
CALMET a nd CALPUFF input files th at contain model configurati on options and settings that have been optim ized after consultation with stak eholders and consulting experts. These sam e
CALMET a nd CALPUFF input files we re used as the basis for the refined W i sconsin analyses.

The VISTAS protocol discusses several options for defining the natural background visibility. These include use of the annual average na tural background extincti on or the background
extinction for the 20% best natu ral conditions days. Based on an em ail survey of the state agencies from the VISTAS m e mber states, all of the VISTAS states allowed the use of annual

average n a tu ral backgrou nd extinc tion for refined CALPUFF analyses . T h is is also the guidance provided by EPA Region 5 staff during discussions with DNR and the Wisconsin Paper Council,
and the m e thod approved by DNR i n their Novemb er 29, 2010 letter. T h erefore, the refined Wausau CALPUFF modeling used the annual average natural bac kground extinction for CALPOST processing.

The VISTAS BART guidance recomm ends that th e threshold value used to define whether a source “contributes” to visibility im pairm e nt is a 0.5 dv change from natural background
conditions. The 98 t h 

## percentile 24-hr average predicted im pa ct at the Class I area (eq u al to the 8 t h 

## highest value) is to be compared to th is contribu tion thresho l d value. Acc o rding to cla r if ica tion of the BART guidance received fro m EPA by t h e VISTAS workgroup, for a three-y ear sim u lation
the m odeling values to b e com p ared with the th reshold are the greatest of the three ann u al 8 t h 

## highest values, or the 22 nd 

## highest value over all three years com b ined, whichever is greater.

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## 7 Dece m b er 2010 

# 3.0 CALMET Dat a an d Procedures

EPA has updated the versions of the appr oved CALPUFF program s since the 2007 modeling protocol was developed, and has provided addi tional guidance on CALMET “s witch” settings. The current approved versions are C A LPUFF version 5.8 (lev el 070623), and CALM ET version 5.8 (level 070623), and these versions were used for the updated refined B A RT CALPUFF analysis. On August 31, 2009, EPA published th e m e morandum “Clarification of EPA-FLM Recommended Settings for CALMET”. EPA stat ed that a 4 km fine CALMET grid size was acceptable, and provide d recomm ended CALM ET setting s . The CALMET setting s for the updated refined BART CALPUFF a n alysis m eet all current EPA recomm endations.

The first step in developm ent of the refined W i sconsin analysis was to define the CALMET
refined m o deling dom ain and grid. As discu ssed in Section 1, DNR’s screening analysis
indicated that there are three Cl ass I areas to the north of W i sc onsin, the Boundary Waters Canoe Area, Isle Royal National Park, and Seney W ildlife Area, where th e screening analy s is predic ts

som e level of visibility impact from W i sconsin BART eligible sources. Therefore, the

m e teorological grid was developed to ensure covera ge for th ese three Clas s I areas, as well as for the BART eligible source locations throughout W i sconsin. Standard IW AQM guidance also

recomm ends that the CALMET grid extend a m i ni m u m of 50 km beyond any Class I or em ission source location, so that puff recircula tion can be properly accounted for.

The refined CALMET grid was defined as a 4-k m spaced grid with 162 cells in the X

- axis and
191 in the Y

- axis. The grid projection was La m b ert Conformal Conic, us ing the sam e projection

param e ters as in the DNR screening analysis (t his allows the use of the sam e source X and Y
coordinates as in the DNR anal ysis). The projection param e te rs include R L AT0 = 40N, RLON0
= 97W
, XLAT1 = 33N, XLAT2 = 45N, XORIGKM = 247.0, YORIGKM = 240.0, and DATUM
= NAS-C.

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## 8 Dece m b er 2010 

## The m e teorological data that was input to CALMET included the sam e three years (2002-2004) of CALMM5 data used by DNR, which was pr ovided by LADCO. However, the refined
CALMET r uns also con s idered ob servation da ta from 22 surface station s , 16 precip itation stations, 5 overwater buoy stations , and 3 upper air stations. Figur e 2 is a plot of the refined CALPUFF modeling dom a in. Figure 3 presen ts a plot of the locati ons of the observation stations
in the m odeling dom ain.

The CAME T program MAKEGE O uses USGS GTOP O30 digital terrain data (which includes coverage in Canada) and USGS Composite Them e Grid Land Use and Land Cover (LULC) data to create a gridded data file on geophysical para m e ters that is used by CALMET. The available USGS LULC coverage does not extend into the Canadian areas of the refined dom ai n. These areas in Canada were assigned to the “forested land” category. Fi gure 4 presents a plot of the
land use data for the m o deling dom ain.

The VISTAS refined CALMET input files discussed in section 2 were used as the basis for the
refined W i sconsin CALMET input files. The sam e CALMET configuration settings and options were utilized, as they are repres entative of W i sconsin terrain and land use patterns. All settings
confor m with current EPA and FLM guidance.

Appendix A presents a listing of a CALMET input file developed for the refined analysis.

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## 9 Dece m b er 2010 

## Figure 2 – Refined CALPUFF Mode ling Dom a in and Locations of Class I Areas

NOTE: The Class I area recep tors are in red, the Wausau Mill location is in blue, and the X and Y coordinates are the Lambert proj ection coordinates are in km s.

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## 10 Dece m b er 2010 

## Figure 3 – L o cations of Observational Stati ons in Refined CALPUF F M odeling Dom a in

30 0 400 50 0 600 7 0 0 8 0 0 900 1000 LCC East ( k m) Wiscons in Re fi ned C A LMET Loca t i on of Obse rvatio n statio ns

30 0 40 0 50 0 60 0 70 0 80 0 90 0 100 0LCC North (km)



## MIL W MADI LAC EAU GREE
M A N I

STUR WAUS MO S I CLIN

WISC

EAGL

MINE HAYW

JUNE DULT

MANI SAWY

HOUG ESCA IRN M IRNW MSUP

N M CH ESUP

WSUP

SMCH COPP

ES CA

HOUG IRON MANI SAUL

CLIN

GREE HA YW

LA C
MADI MARS ME NO

MILW RAIN

STURG GREE MN NP INTF



## NOTES: Surface station s are in red, overwater (b uoy) in blu e , precip itatio n in green, and upper air in purple.

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## 11 Dece m b er 2010 

## Figure 4 – L a nd Use Data for Refi ned CALPUFF Modeling Dom a in

300 400 500 60 0 7 0 0 80 0 LC C E a s t ( k m ) 300 400 500 600 700 800 900 1000LCC North(km) Snow/ I ce

T und ra

Bar r en

We tla n d

Wa te r

Fo r e s t

Ra ng e

Agr i cultur e

U r ban /Built -U p

Lan d U s e 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 . .

. . LCC Origin: 40N, 9 7 W

D a tum : NA S- C Matc hing Parallels: 33N, 45N False E a sting: 0.0 False Northing: 0.0

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## 12 Dece m b er 2010 

## Som e of the notable CA LMET c onfiguration settings included:

• CALMET vertical layers set to 10, with cell face heights at 20, 40, 80, 160, 320, 640, 1200, 2000, 3000, and 4000 m e ters,

• CALMET diagnostic options, includ ing slope flow effects (ISLOPE = 1) with the radius of influence of terrain (T ERRAD) set to 15 km
,

• EPA recomm ended CALMET settings for the ra dius 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 CALPUF F input files were used as the basis for the
refined W i sconsin CALPUFF input files. All C A LPUFF settings and op tions are con s isten t with EPA and FLM guidance, and the refined VISTAS protocol recomm endat i ons. The background ozone (O3) concentrations were used directly from the DNR CALPUFF input files. Instead of using m onthly 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 i nput file developed for the analysis.

The DNR screening analysis cons id e r ed thr ee em itted pollu ta nts, SO 2 

## , NOx, and PM 2. 5 

## . The refined CALPUFF modeling will co n s ider sp eciated particulate em issions, includ ing coarse PM (PMC), fine PM equivalent to PM 2. 5 

## (PMF), sulfate (SO4), nitrat e (NO3), elem ental carbon (EC), and secondary organic aerosols (SOA or OC). Section 6 of this prot ocol describes how the speciated particulate em issions were calcu lated.

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## 13 Dece m b er 2010 

# 5.0 POSTUTIL and CALPOST Procedures

In CALPUFF, the scavenging of the available am monia for nitrate form ation is com p uted on a puf f

- by-puff basis. Beca use of the possibility of multiple puf f overlap, th is approa ch m a y tend to
overestim ate the am ount of a m m onia available to for m nitrate. In order to address the cum u lative

consum ption of a m m oni a, the POSTUTIL program can be used to repartition nitric acid and
nitrate. PO STUTIL calculates new NO3/HNO3 equi librium concentrations for the sam p le source in the Class I area using the b ackground ammonia. As recomm e nded in the VISTAS procedures for refined CALPUFF modeling, the POSTUTI L “MNITRATE=1” m e thod was used for the
refined W i sconsin CALPUFF modeling. Instead of using the m onthly values for background
ammonia concentrations from the DNR screen ing analyses, a single conservative background ammonia concentration of 3.9 ppb was used.

The m odeling protoco l s u bm itted in 2007 propos ed to use C A LPOST Vi sibility Method 6 to
calcu late v i s i bility im pacts. However, since that tim e there have been revisions to CALPOST that allow the use of the updated IMPROVE extin ction equation. CALP OST version 6.221 can
im ple m ent the “Method 8 Mode 5” m e thodology to calculate visibility impacts, and the FLMs

recomm end its use in “F ederal Land Managers’ Air Quality Related Values W o rk Group (FLAG) Phase I Report—Revised (2010)” (herein referred to as FLAG 2010). Therefore, this updated

m e thodology will be us ed for the W a usau BART analys is. Th e new CALPUFF Graphical Users
Interf ac e autom a tically e n ters the app r opria te va lu es, based on the Class I ar ea being selected, for natural background species and rela tive hum idity adjustm e nt factors using the data in T a bles 6 through 9 of Section 3.3.5 of FL AG 2010 (which are based on “Guidance for Estim ating Natural Visibility C onditions U nder the Reg i onal H aze Rule”, EPA-454/B-03-00 5, Septem be r 2003).

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## 14 Dece m b er 2010 

# 6.0 Emissions Modeled

EPA’s BART m odeling guidance state that the 24-hr m a xi mum actual em issions rates for the period of the m odeling simulation (2 002-2004) should be used for the anal ysis. If this data is not available, th en the short term “allowable” o r“p o t ential” em ission rates should be used. W a usau provided D N R with source inform ation that has b een rev i ewed to determine the 24 -hr m a xim u m actual em issions rates.

There ar e a num b er of BART eligible em ission units a t the W a usau Mosin e e m ill. Sta c k S10 is a

com b ined stack for the 3 boilers that are th e pr im ary source of the BART pollutants, and the recovery boiler (B21) vents to stack S11. In addition, although the BART eligibility is in question for som e s m aller em issions sources (the lim e kiln, sm elt tank, and slaker), these units
were also included in the m odeling to be c onservative. Based on discussions between RMT (W ausau Pa per’s consultant) and DNR on Dece mber 7 and 9, 2010, it was agreed to use PTE

em issions for all em ission units, as listed in Tabl e 1. Note that the PTE for S10 was adjusted to
reflect fuel o il usag e lim itations as sp ecified in th e air p e rm it. The PM emissions h a ve been speciated using the inform ation for coal and oi l fired boilers developed by the National Park
Service 1



## .

1 

### h ttp ://www2

. natu re.np s .g ov /air/p erm its/ec t/i n d e x

. cfm )

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## 15 Dece m b er 2010 

## Table 1 – Wausau Em issions (in units of g/sec)

U n i t S O 2 N O x P M P M C P M F E C S O 4 S O A S 1 0 1 4 3

. 1 2 8

. 1 1 1

. 6 8 1

. 1 6 2

. 3 9 0

. 0 9 6

. 4 3 1

. 6 1 S 1 1 1 3

. 1 5

. 4 2

. 3 2 0

. 7 3 1

. 2 6 0

. 1 0 0

. 1 9 0

. 0 4 S 1 2 0

. 4 0

. 0 0

. 4 3 0

. 0 0 0

. 4 3 0

. 0 0 0

. 0 0 0

. 0 0 S 5 2 0

. 0 0

. 0 0

. 4 3 0

. 0 0 0

. 4 3 0

. 0 0 0

. 0 0 0

. 0 0 S 5 3 1

. 4 0

. 9 0

. 6 2 0

. 3 2 0

. 1 9 0

. 0 1 0

. 1 0 0

. 0 0 T o t a l 1 5 8

. 0 3 4

. 4 1 5

. 5 2

. 2 4

. 7 0

. 2 6

. 7 1

. 7

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## 16 Dece m b er 2010 

# 7.0 Modeling Result s

CALPOST com putes the daily m a ximum change in deciviews relative to the annual average
natural back ground visib ility, separately for each Cl ass I area. For evaluating the sou r ce im pact relative to the “Subject to BA RT” vi sibility im pa ct thres hold of 0.5 dv, the daily m a ximum changes in v i sibility are sorted to determ ine the 98th percentile (8 t h 

## highest) value for each of three y ears, and the 98th percen tile (22 nd 

## highest) value for the com p lete d 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 exem pt from the BART requirem e nts.

Another equivalent m e tric commonly used for BART exe m ption m odeling is to sum the num ber of days per year th at are above the 0. 5 dv thresh o l d for each Class I area se parately ; if there are 7 or fewer days above the threshold for each year, th en the 98 t h 

## percentile value is also below the
threshold. T h is is the m e tric approved by DNR for use in the BART modeling analysis. Specifically, for each Class I area separately, if th ere are less than 8 days per year that the predicted visibility im pa cts are greater than 0.5 deciviews relative to th e annual average natural background visibility, th en the BART eligib le em ission units at th e m o deled facility will be
determ ined not to be Subject to BART.

Table 2 presents the results from the refi ned CALPUFF BART exem ption m odeling. These
results dem onstrate th at there are less than 8 days per yea r , at each ind i vid u al Class I area, when
the vis i bility im pacts from the W a usau m ill BART eligib le em ission unit are above 0. 5 dv. Therefore, the Wausau mill BART eligible so u rces are not Subject to BART requirem e nts.Updated BARTModeling Protocol andReportforWausauMosineeMillTable 2 – Wausau CALPUFF BARTExemption Results SummaryClass I areaDistance(km)fromsourcetoClass I areaboundary# of dayswith impact> 0.5 dv inClass I area:2002# of days withimpact > 0.5dv in Class Iarea: 2003# of dayswith impact> 0.5 dv inClass I area:2004# of days withimpact > 0.5dv in Class Iarea for 3 yearperiodMaximum 98thPercentileimpact overeither annualor 3-yr periodsSeney, MI~ 32000110.20Isle Royal, MN~ 34000000.15BoundaryWaters,MN~ 36020020.1317December 2010

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## Appendix A – Example CALMET Input File

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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)

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

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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

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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

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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

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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

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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. !

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(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

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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

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

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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

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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 !

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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

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(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

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-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 !

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(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 !

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! 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 !

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! 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 !

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

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## Appendix B – Example CALP U FF Input File

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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

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

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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!

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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!

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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!

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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!

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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!

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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!

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

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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. !

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!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

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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

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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

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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!

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

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(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:

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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

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

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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

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---- 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

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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

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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

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

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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.

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! 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.

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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)

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(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)

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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

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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 !

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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!

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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

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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)

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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 !

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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

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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 !

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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:

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(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

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

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!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 RE CE PTOR COORDINAT ES FOLLOW I N INPUT FI LE

Dece m b er 2010

# A TTACHMENT 

# 6

### 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 Reso urces (“Department” or “WDNR”) finds that:
Regional Haze Rule Background
1. On July 6, 2005, the U.S. Environmenta l Protection Agency (EPA) published regulations to address visibility impairment in our na tion’s largest national parks and wilderness (“Class I”) areas [70 FR 39103]. Collectivel y, 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”) wh ich 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 Nati onal 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 Reso urces submitted a Regional Haze SIP to U.S. EPA on July 1, 2011.

Facility Specific Information
6. Georgia-Pacific Consumer Products LP, t he “permittee,” operates a manufacturing facility located at 1919 South Broadway, Green Ba y, 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 cu rrently 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 fac ility 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 existenc e 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: SO 2 

### , NO x 

### , 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 Res ources 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 val ue 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, wh ich was promulgated under the authority of chapter 285, Stats., the Department of Natural Resources has adopted regulations relating to the Protection of Visibility by Applic ation 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 inst all and operate any necessary control equipment and/or undertake any necessary work practice s 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 em issions of particulate matter.
(a) Effective January 1, 2011, the permi ttee 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 cont inue to implement the facilit y malfunction prevention and

abatement plan as specified under s. NR 439.11, Wis. Adm. Code.
(c) The permittee shall meet the co rresponding compliance demonstration, recordkeeping, reporting, and monitoring requirements for the emission limitations in 2.(b) above as specif ied in the permittee’s operating permit.
(d) The permittee shall meet the corr esponding 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 sulf ur 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, t he permittee can comply with an alternate requirement for sulfur dioxide emission s according to the following criteria: (1) the permittee notifies the Departm ent and U.S. EPA Administrator by July 15, 2013 of complying with one of the alternative sulfur dioxide mass cap requirements for the designated pe riods 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 SO 2 

### NOx SO 2 

### 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 comp liance 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 emission s monitoring system over the days that any of the boilers B25, B 26, 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 consecut ive 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 di oxide 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 emission s monitoring system over the days that any of the boilers B25, B 26, 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 consecut ive 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 requi red 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 calc ulated daily for use in calculating emissions over each 30-day period; (2) Monthly emissions shall be calcul ated by adding all daily emissions in that month. These monthly emi ssions 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 co nstraints are encountered in implementing these specific technologies which warr ant a revision of the individual boiler determined control level as allowed for unde r s. NR 433.05(5), Wis. Adm. Code.

Boilers B26 and B27 Best Available Retrof it 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, t he 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 alte rnative nitrogen oxide emissions mass cap requirements for the designated pe riods as specified in 4(b)ii.(3). (2) nitrogen oxide emissions from stack S1 0 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 SO 2 

### NOx SO 2 

### 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 comp liance 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 emission s monitoring system over the days that any of the boilers B25, B 26, 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 consecut ive 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 ox ides 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 emission s monitoring system over the days that any of the boilers B25, B 26, 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 consecut ive calendar days. A new 30

− day total emissions shall be calculated and recorded at the end of each day. iv. In demonstrating compliance with nitr ogen oxides emission limitations of condition 4.(b) above, the permittee ma y 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 alternat ive mass cap later than July 15, 2013, then the election is subject to department review with public comment and pursuant U.S. EPA appr oval of the SIP.

### (d) The procedures and methods required for compliance demonstration and for performance testing requi red 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 calc ulated daily for use in calculating emissions over each 30-day period; (2) Monthly emissions shall be calcul ated by adding all daily emissions in that month. These monthly emi ssions 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 emis sion limitation on boiler B26 is based on continuous operation of over-fire air an d flue gas recirculation control designed specifically for NOx control and continuo us operation of selective non-catalytic reduction. This technology is noted to es tablish a basis for determining alternative emission requirements if constraints in im plementing 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 r egenerative selective catalytic reduction equipment to achieve additional 70% control of nitrogen oxides beyond the over-fire air: This technology is noted to establis h a basis for determining alternative emission requirements if constraints in implem enting 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 Co nsent Order and to enforce its terms. To that end Georgia-Pacific Consumer Products LP stipulat es 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 La w and Administrative Consent Order and waives its rights, if any, to challenge this Administrati ve Consent Order in circuit court under ss. 227.52 and 227.53, Stats., or any other pr ovision 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 accor dance with ss. 299.95, and 299.97, Stats. The undersigned further certifies that he or she is aut horized to execute such Consent Order, Waiver and Stipulation on behalf of Georgia-Pacific Consumer Products LP.
Nothing in this Consent Order, however, sha ll be construed as an admission on the part of Georgia-Pacific Consumer Products LP for any pu rpose 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 DEPARTM ENT OF NATURAL RESOURCES

### For the Secretary

By _______________________________ __________________ William Baumann Date Acting Air Management Bureau Director

_______________________________ __________________ Georgia-Pacific Consumer Products LP Date Title:

# A TTACHMENT 

# 7

## Template for EGU BART Permit Revi sions for Implementation of BART
Note: The template that follows will be used for proposed BART language within each permit.

PART *X* : BEST AVAILABLE RETROF IT TECHNOLOGY (BART) (Note: Text that is underlin ed and highlighted in gray varies between different boilers)
1.0 Applicability
A Best Available Retrofit Technology (BAR T) 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 controlli ng particles and meeting opacity requirements.

3.0 BART Determination

Best Available Retrofit Technol ogy (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 limita tions specified in Conditions *XX* and *XX* , as well as compliance with the visible emissions limitations specified in Condition *XX* ; (ii) Compliance with the Compliance Assura nce Monitoring (CAM) Plan in Part *X*
, and the Malfunction Preventi on 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.