# 1 

# Technical Report

on



# Dry Sorbent Injection (DSI) and Its Applicability to TVA’s Shawnee Fossil Plant (SHF)

by

Dr. Ranajit (Ron) Sahu 1 

# Consultant sahuron@earthlink.net Ph: 702.683.5466

Commissioned by the Southern Alliance for Clean Energy P.O. Box 1842 | Knoxville, TN 37901 | 865.637.6055 http://www.cleanenergy.org/

April 2013!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 1 

# Resume provided in Attachment A. 2 

# Comparison of Sodium Bicarbonate and Trona for Multi

-Pollutant Control, Yougen Kong and Stan Carpenter, Solvay Chemicals, Electric Power 2010.

# 2 1.0 Summary

This report presents background and general technical information that may be useful in
assessments of the implementation of Dry Sorbent Injection (DSI) technology at coal

-fired generation units for the purposes of sulfur dioxide (SO2) emission reduction. While the costs of installing, operating and maintaining a DSI system at a typical coal

-fired generation unit,
if feasible at all, will depend on factors that can only be properly addressed using site

specific factors , the general question of whether or not it DSI is likely to be effective at reducing SO2 emissions can be addressed in broad terms. Implementation details at particular plants and specific coal

-fired boiler units will depend on numerous site

- specific factors including the type of sorbent used and the specific design of the DSI system.

DSI technology was originally designed to reduce the amount of sulfur trioxide (SO3) and acid gas emissions at sources such as coal

-fired boilers. Since the amount of SO2 removal achieved by DSI has always been less than other, more effective means of SO2 removal (such as via wet or dry flue gas desulfurization (FGD) systems specifically designed for
sulfur dioxide removal) the technology was not previously marketed for SO2 removal, per se

. However, recent regulatory drivers , such as the EPA Mercury and Air Toxics (MATS) Rule, have created renewed interest in DSI as a means of SO2 removal due to the considerably lower capital costs of DSI compared to the more conventional wet or dry FGD systems. Thus , many utilities are actively analyzing whether or not it would be feasible to install DSI, rather than FGD, at their coal

-fired generation units in order to comply with stricter air
emission standards . As more utilities begin to consider or implement DSI, it becomes increasingly important to understand the total costs (including capital costs, operation and
maintenance costs) as well as the long

-term environmental impacts of DSI.

As detailed in this report, the effectiveness of DSI technology at removing SO2 from a coal plant’s air emission stream depends on many factors including sorbent type, sorbent particle
size and the rate/amounts at which the sorbent is injected into the flue gas stream. The type of particulate matter controls in place at any given generation unit and the presence of other

# 3 air pollutants in the flue gases will also affect the ability of a DSI system to remove SO2. Furthermore, increased SO2 removal using the most common sodium

-based sorbent (trona)
will result in the increase of other known air pollutants from the unit, including carbon dioxide (CO2) and possibly nitrogen oxides (NOx)

.

The choice of sorbent used in the DSI system will also alter the composition and properties
of the boiler’ s solid waste streams. If a DSI system uses sodium

-based sorbent, certain constituents in coal combustion waste (CCW or “coal ash”) , such as arsenic, become more
mobile and are more likely to leach into groundwater or adjacent surface waters , given that the vast majority of CCW disposal facilities are either unlined or do not have adequately designed liners. This increase in leachability represents not only a potential threat to water quality and public health but also additional future liabilities and operational costs for owners and operators of coal plants

– costs that are presently not being factored into the conventional

cost

-analyses that are often used to justify technology assessments and technology selection

. Since most coal plants do not already have properly designed lined coal ash impoundments located on site, they will either have to incur significant costs to construct new lined ash impoundments, retrofit existing unlined impoundments or risk discharging toxic metals into groundwater or nearby surface waters. Furthermore, the change of the coal ash’s chemical composition can also render it unsuitable for use in concrete or structural fill

– eliminating a

potential revenue source for coal plants and further driving up the costs of DSI implementation.

We hope this report provides readers background knowledge on how DSI works and identify areas of potential concern regarding its implementation at coal

-fired power plants. Although the costs and benefits of DSI vary wildly depending on design and implementation, and can only be properly addressed via site

- specific analyses, this report attempts to provide information that may be useful to all stakeholders that are considering DSI as well as are likely to be affected or impacted by its use at coal

-fired power plant units.

# 4 2.0 Dry Sorbent Injection

2.1 Basics and Elements of a DSI System

A Dry Sorbent Injection (DSI) system is, as the name implies, a dry process in which a sorbent is pneumatically injected either directly into a coal

-fired boiler or into ducting downstream of where the coal is combusted and exhaust (flue) gas is produced. This discussion will focus on the latter, more common, implementation of D SI. The goal of the sorbent injection is to interact the sorbent with various pollutants in the flue gases (such as sulfur trioxide (SO3), various acid gases including hydrochloric acid (HCl), and sulfur dioxide (SO2), such that some fractions of these pollutants are removed from the gas stream.

Figure A, 2 

# below shows a simple schematic of the DSI process. We will discuss the sorbents that are used in more detail below. For now, Figure A shows that the sorbents can be injected at a number of locations, all prior to the particulate control device.

Figure A

– Simple DSI Schematic!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 2 

# Comparison of Sodium Bicarbonate and Trona for Multi

-Pollutant Control, Yougen Kong and Stan Carpenter, Solvay Chemicals, Electric Power 2010.

# 5 After the appropriate chemical interactions between the pollutants in the flue gas and the sorbent, the dry waste product of reaction is removed at the (typically) existing particulate control device downstream of the injection point

– which is typically either an electrostatic precipitator (ESP) or a fabric filter baghouse.

Historically, DSI was used to remove SO3 and acid gases

– and these pollutants are usually present in far lower concentrations in the flue gases as compared to SO2. However, some SO2 was also invariably and unavoidably removed as well. As regulatory pressures have focused increasingly on SO2 removal, DSI vendors have increasingly targeted their systems at this pollutant. SO2 removal via DSI is the focus of this technical report.

Historically, SO2 removal was effected using various types of scrubbers, whether wet or dry. These technologies have roughly 40 years of field implementation and can routinely achieve SO2 reductions ranging from 90%+ to 99%, depending on various factors. However, they have significant capital costs.

In contrast, DSI systems have two distinct advantages that have, heretofore, propelled their acceptance as a suitable SO2 control technology. First, the capital cost of DSI systems is much lower compared to wet or dry scrubbers. Second, DSI systems take up much less physical space, which is especially important when considering retrofit or upgrades to existing units.

The expected SO2 control efficiency of DSI (and at what overall cost) is a matter of some controversy. We will explore that in more detail later in this section. However, it is rare that DSI SO2 efficiency is 90% or greater

. Thus, if the SO2 efficiency requirement is 90% or greater, DSI is not likely to be an appropriate technology. For lower efficiencies, it is possible to remove SO2 via DSI but various factors including capital cost, operating costs (of which sorbent

costs are a significant part), waste handling issues, etc. need to be considered before a proper
decision can be made. Although several current units are using DSI in some capacity at this time, actual hard operational data are not available. Similarly it is reported that additional plants/units are considering DSI for meeting compliance needs but the extent of additional DSI adoption will not be fully clear until 2015

-2016. The typical timeline for the installation and implementation of DSI, including initial assessments and permit requirements are of the order of

# 6 12

-24 months. This does not include time for building a new landfill/impoundment or retrofitting an existing landfill, if that is feasible, which could significantly increase the amount of time needed to implement DSI.

2.2 Sorbents

Two primary sorbents are utilized in DSI systems: sodium sesquicarbonate, or trona, and sodium bicarbonate. Both of these, as their names suggest, are sodium based sorbents. Less frequently, a calcium based sorbent, hydrated lime, can also be used although rarely so if the goal is SO2
removal.

There are several notable differences between these materials. First, sodium bicarbonate is more effective in removing sulfur dioxide emissions than trona. Hence, less sodium bicarbonate is required for an equivalent amount of removal. But, sodium bicarbonate is more expensive than
trona in the United States on a per

-pound basis

. Therefore these factors need to be considered in their totality before site

- specific cost estimates can be made. The focus of this report, however, is Trona, since it seems to have garnered the most interest from likely DSI adopters. Trona is a naturally occurring mineral and a substantial amount of it is mined primarily from a vast formation in the Green River, WY area3 

# and certain areas of California. Sodium bicarbonate, on the other hand, is a chemical compound primarily manufactured using the Solvay Process. This salt is obtained from a reaction of calcium carbonate, sodium chloride, ammonia, and carbon dioxide in water, and is more expensive than the mined trona.

Hydrated lime is not as effective as either of the sodium based sorbents so greater quantities of hydrated lime are required, making operational costs significantly greater. The reader should keep in mind that not all operational costs are properly accounted for in many situations. Thus,
in actual site

- specific implementation, the final economics may favor any one of these three
sorbents.!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 3 

# The largest deposit of trona in the world is in the Green River Basin in Wyoming, where seams of trona vary in depth from 600 to 3500 f t and are spread over approximately 2500 square miles. Known deposits of trona in the Green River Basin exceed 100 billion tons. Four companies currently mine trona in the Green River Basin, but only two, Solvay Chemicals and FMC market trona for SO2 control.

# 7 It should also be noted that, in addition to SO2 removal, each of these sorbents is more or less
ef

fective on other pollutants that may be of interest.

For example, trona is effective for SO2, SO3, condensable particulate matter (mostly sulfuric acid mist) and HCl. Sodium bicarbonate for is effective for SO2 and HCl. Hydrated lime is
most effective for SO3, condensable PM and HCl.

2.3 Sorbent Particle Size

The effectiveness of SO2 reduction is based on many factors, including, in no particular order: sorbent mass injection rate, sorbent residence time in flue gas stream (which depends or dictates the injection location), sorbent penetration and mixing with flue gases, the type of particulate control device, flue gas temperature profile, and, finally, the sorbent particle size. Typically, the finer the sorbent particle size, the greater the sorbent surface area available for reactions. All of the other factors remaining constant, finer particle size will yield greater the SO2 removal efficiency for a given quantity of sorbent injected. Looked at another way, finer particle size requires less sorbent mass required for a specified SO2 removal efficiency.

The drawback, however, is that finer sorbent particles usually involves additional milling equipment, which, though promising reasonably quick payback, adds to initial capital cost and
increases operating costs.

# 8 2.4 Reactions

The various reactions that can occur between the DSI sorbent and the pollutants in the flue gases are summarized below in Figure B. 4



# Figure B

– DSI Reactions

It is important to note that CO2, a greenhouse gas, is a by

-product of many of these reactions
when sodium

-based sorbents are used in DSI. While use of hydrated lime will not create CO2
emissions during the pollution control process it should be noted that the production of hydrated
lime elsewhere can create CO2 emissions as well. It should be noted that CO2 emissions can also result when limestone is used as the reagent in wet FGDs for conventional SO2 removal. Actual quantities of CO2 that can be produced as a result of SO2 removal reactions will depend on the type and quantity of reagents used as well as the quantity of SO2 removed, which, in turn, depends on the coal sulfur content and the SO2 removal efficiency via DSI or a scrubber.!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 4 

# Comparison of Sodium Bicarbonate and Trona for Multi

-Pollutant Control, Yougen Kong and Stan Carpenter, Solvay Chemicals, Electric Power 2010.

# 9 Of course, it should also be noted that the reaction products are collected in the fly

-ash, which is, along with the unreacted sorbent, collected in the particulate control device downstream. Thus, the chemical and physical properties of the collected particulates from either the baghouse or the ESP change when DSI is added. Since these particulates must be disposed of, typically in existing landfills, understanding the nature of these changes is important. We will discuss this in
a little more detail later.

2.5 SO2 Removal Efficiency and Factors

As noted above, SO2 removal efficiency depends on numerous factors. Briefly, these include: 5



# - sorbent injection rate or Normalized Stoichiometric Ratio (NSR);

- sorbent particle size;

- residence time of the sorbent in the flue gas stream (before capture in the PM control device);

- extent of dispersion and mixing of the sorbent and the flue gas;

- the type of PM controls device (ESP versus baghouse). A baghouse allows for longer contact time of the sorbent and the pollutant gases, given the filter cake present in the baghouse. With an ESP, there is no filter cake and hence particle size is a more important variable ;

- flue gas temperature

- presence of other competing pollutants in the flue gases!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 5 

# Dry Sorbent Injection of Sodium Sorbents for Acid Gas Mitigation, Heidi E. Davidson, Solvay Chemicals, Inc., International Biomass Expo and Conference, 2010.

# 10 In this subsection we will present some of the more important factors and their impact of the expected SO2 removal efficiency.

In one recent study, 6 

# the authors evaluated the sensitivity of SO2 removal to trona injection rate, particle size, and injection location. The predicted SO2 reduction ranged from 45

- 80% and was highly dependent on a parameter called the Normalized Stoichiometric Ratio (NSR) 7 

# and trona particle size distribution.

When a trona particle is introduced into the hot flue gas stream, upon decomposition to sodium carbonate, the surface area of the particle increases significantly. This behavior is commonly referred as the “popcorn effect”. Figure C below shows the particle surface area as a function of temperature. As seen in the figure, the surface area begins to increase at approximately 300F, peaks at approximately 500F , and then decreases for increasing temperature above 500F where
the internal structure of the particles begins to change

. Adding trona at temperatures greater than
800F is not advisable.!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 6 

# Cremer, M. A., et. al., Testing and Model Based Optimization of SO2 Removal With Trona in Coal Fired Utility Boilers, Paper #137. 7 

# NSR represents the multiple by which sorbent must be injected as compared to the theoretical or stoichiometric amount required based on the amount of SO2 present.

# 11 Figure C

– Trona Particle Surface Area versus Temperature

Field tests have been carried out by various vendors and researchers in order to evaluate trona performance for SO2 reduction. In one set of studies the impacts of injection location were evaluated. In particular, trona was injected at the economizer inlet, the air heater inlet, and the ESP inlet. Average gas temperatures at these locations under full load conditions were reported to be 705FF, 550FF, and 230FF. These tests were primarily carried out using the as

-received, unmilled Solvay T200 material (D50 = 30 μm). Figure D shows the measured SO2 reductions for these tests. The data show the best performance was achieved for trona injection at the economizer inlet and the worst performance was seen for injection at the ESP inlet. It should be
noted that performance is a function of not only particle surface area discussed above but also the residence time available for the gases to mix with the injected trona, which, in turn, can depend on the flue gas flow rate, the temperature, and the geometry of the duct that transports the flue

gas . Thus finding the optimal injection location is a complex function of several site

- specific

# 12 variables. Most of these tests were carried out for a trona NSR of approximately 2.5 (i.e., 2.5
times more trona than would be needed based on theoretical calculations).

Figure D

– Effect of Injection Location on SO2 Removal Efficiency

Another set of tests focused on particle size and the effect of milling (i.e., reducing the particle size of the trona using a “mill”) the trona. Two pin mills were used either in series or in parallel to supply trona to injectors or lances at the economizer inlet. When used in series, the trona was
milled to a median particle size, D50 , of approximately 11.6 μm. When used in parallel, the D50 was approximately 13.7 μm. Tests were carried out for NSRs ranging from approximately 1 to 3.5. These results were compared against earlier results using unmilled trona and are shown in Figure E.

Although the data are limited, the results indicate, as expected, improved SO2 reduction using the milled trona compared to the unmilled trona. As seen in the figure, measured SO2 reduction up to 74% was observed, but at a high trona injection rate (NSR of 3.5).

# 13 Figure E

– Effect of Trona Particle Size and NSR on SO2 Removal Efficiency

Figure F below combined the effects of various factors into one chart, showing how SO2 removal efficiency is affected by these factors. As can be seen in the figure, achieving 90% or greater SO2 removal efficiency is not generally feasible. It should also be noted that even achieving SO2 removal efficiencies of 70% or greater requires significantly greater quantities of trona injection (high NSR values). This increases the operating cost of DSI since it requires purchasing of greater quantities of trona, increased milling costs, and also higher costs of waste disposal. The effect of greater quantities of unreacted sorbents in the ash on ash properties will
be discussed later.

# 14 Figure F

– SO2 Removal Efficiency and Various Factors

2.6 DSI Challenges

While the DSI process appears relatively straightforward, is easy to understand, and is lower in capital cost as compared to the other SO2 removal options such as scrubbers , it is not without significant challenges.

As noted earlier, this report does not discuss DSI using calcium based sorbents such as hydrated lime, mainly because of its low SO2 removal efficiency (as compared with the sodium based
sorbents such as trona or sodium bicarbonate), so it will not discuss myriad issues and challenges
associated with calcium based sorbents.

# 15 For sodium based sorbents, the following should be noted.

- plugging and caking

– historically, sodium sorbent injection systems have been beset by plugging and caking in the insides of the ducts, leading to blockages ;

- dehydration

– sodium sorbents can dehydrate in the conveying system, making water available for agglomeration and caking;

- thus, heat gain should be minimized in the conveying system. It is critical to use high efficiency compressors in the pneumatic systems and to properly manage the temperature of the conveying fluid since higher temperatures will increase fouling in the conveyance systems ;

- increased SO2 removal with sodium may result in some NOx formation;

- ash sales may be negatively affected by sodium addition since the ash may not be suitable for applications in concrete or structural fill. Of course, loss of ash sales will affect plant economics and operation costs; and

- ash landfilling may be negatively impacted due to solubility of sodium compounds in the fly ash (i.e., Na2SO4 or Na2CO3). 8



# The last impact is significant and as yet generally unrecognized. Yet, it clearly has the potential for significantly increasing the disposal cost and/or creating significant adverse environmental impacts. Thus, some additional discussion is provided in the next subsection.!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 8 

# Designing and Operating a Reliable DSI System, Greg Filippelli, ADA

-ES, 2012

# 16 2.7 Impact on Ash Solubility

The impact of trona

-based ash has been recently evaluated in industry

- sponsored studies. 9 

# Key conclusions include the following:

- trona injection for SO2 emission control significantly changed the fly ash physical characteristics, including reduced specific surface area, and changed particle morphology and microstructure;

- trona injection for SO2 emission control significantly increased the bulk contents of sodium, sulfur, and carbonate in the fly ash, and brought great amount of soluble materials into the fly ash;

- trona injection for SO2 emission control greatly increased the fly ash solubility, pH, and leachability of anionic elements including fluoride, sulfate, chloride, and trace oxyanions of concern especially As and Se. Compared to the conventional fly ash, trona ash leached significantly more As and Se in all conditions, including varying leaching time, pH, storage time conditions. Multiple factors may contribute to the enhanced As and Se leaching from trona ash, including more alkaline pH, greater ash solubility, presence of high concentrations of competing
anions (such as sulfate and carbonate), and a greater Se(VI) fraction in trona ash.

The implications are obvious. Since most plants, even including those that are able to sell some of their fly ash, dispose of the bulk of their fly ash in already existing local, unlined landfills, increased solubility of this fly ash, with trona injection, will likely increase the leachability of metals such as arsenic and selenium into groundwater below such landfills. Lining existing landfills, to the extent it can even be done, would be prohibitively expensive, even for the
smaller landfills. Thus, this impact should be carefully evaluated before DSI is considered as a proper or appropriate SO2 reduction technology.!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 9 

# Jianmin Wang, et. al., Leaching Behavior of Coal Combustion Products and the Environmental Implication in Road Construction, A National University Transportation Center at Missouri University of Science and Technology, NUTC R214, April 2011. This work is sponsored by, among others, the Electric Power Research Institute (EPRI).

# 17 In summary, there are potentially adverse air quality as well as water quality impacts that can result from the implementation of DSI to mitigate SO2 emissions. Since the likelihood and extent of these adverse impacts will be site specific, they should be addressed during the permitting/regulatory approval stages, if this technology is evaluated/contemplated. When considering the impacts of DSI implementation on air, it is critical that any additional emissions of pollutants , such as various sizes of particulate matter from handling/processing of the sorbents and from the additional loading of sorbent on the existing particulate control devices , as well as increased emissions of greenhouse gases , such as CO2 , be considered and addressed during the permitting process

.

To the extent the regulatory approval process allows for a consideration of off

- site environmental
assessments, incremental adverse impacts from the mining, refining, transport, and storage or sorbents should also be addressed. With regards to impacts on water quality, particularly groundwater impacts, the issue of disposal of the sodium containing ash on existing landfills is paramount. This should be considered as part of the landfill permit at a site, as applicable.

# 18 3.0 The Shawnee Fossil Plant and Possible DSI Implementation

3.1 Description

Shawnee Fossil Plant is located about 10 miles northwest of Paducah, Ky., on the Ohio River. It is located approximately 13 miles downstream from the mouth of the Tennessee River. The plant consists of 10 pulverized coal

-fired units, of which 9 are identical dry

-bottom, wall

-fired units (Units 1

-9). Each of these units is rated at 175 MW. Shawnee Unit 10, which was converted to an atmospheric fluidized

-bed boiler in the early 1980s and was the first such unit in the country, was idled by TVA in October 2010. 10 

# We will not be discussing Unit 10 further in this report.

Construction of the station was authorized in 1951 . Unit 1 was placed in service in April 1953 and the last Unit 10 went into operation in October 1956. So, each unit is approximately 55 years old or more

.
As far as environmental controls, Units 1 through 9 burn a blend of low

- sulfur coal sourced from
the Power River Basin and use low

-NOx burners to reduce emissions of nitrogen oxides. None of these 9 units has any additional SO2 removal capability. Particulate matter controls at each of
Units 1

-9 have evolved over the years. Initially they were only equipped with mechanical dust collectors, mainly to protect the induced draft fans. In 1968, TVA initiated a program of
retrofitting each unit with ESPs in order to comply with a Federal Executive Order issued in 1966. The ESPs were operational in 1973. Each unit exhausted its flue gas via a separate stack. Then, in 1974, in an effort to improve ambient air quality and reduce ground concentration of SO2 purely using dilution as the approach to pollution control, TVA built two large 800 foot tall stacks serving all ten units (5 units connected to each stack). In April 1976, the Supreme Court ruled against the tall

- stack approach to “controlling” SO2 emissions. At that point, TVA decided to retrofit each unit with a baghouse. The baghouses were installed between 1978

- 1981. While they do not control SO2 emissions, the baghouses provided better control of particulate matter
emissions from the various units. It is assumed that the old ESPs are still in place and deenergized.!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 10 

# http://www.tva.com/sites/shawnee.htm

# 19 As noted above, initially each unit exhausted its flue in to the atmosphere via its own stack. When the baghouses were installed, the flue gas arrangement was changed. Currently, flue gases
from Units 1

-5 are combined and discharged to the atmosphere via a common stack and flue gases from Units 6

- 10 are combined and discharged to the atmosphere via a second stack.

Figure 3

-A shows a general location map of the station. The Ohio River is visible at the top right hand corner of the figure.

The next series of photographs below show increasing resolutions of the plant.

# 20

# 21 The last photo above clearly shows the two current large stacks, at either end as well as shadows of the 10 existing stacks. While the boilers themselves are not seen directly since they are within the two long white buildings at the bottom of the figure, the ten, individual unit baghouses and the two common flue gas ducts are clearly visible. The units are numbered from right (Unit 1) to left (Unit 10).

# 22 The next photo below shows a close up of the baghouses of Units 1

-5, the common flue gas duct for these units and the stack. Also clearly visible are the older stacks which were left in place when the baghouses were installed. As is clearly seen, the exhaust gases from each unit emerge
from the air

-preheaters and are split into two parallel paths, one on either side of each old stack, before entering the respective baghouses.

Similarly, the photo below shows the close

-up of Units 6

- 10, their respective baghouses, and the common flue gas duct, but not the stack, which is shown in the next photo. Unit 10 is located at the extreme left. Historically, Unit 10 was the test unit for the developments of various types of early scrubber designs. Facilities associated with these can be seen off to the left in the photograph.

# 23 The next series of photos shows close

-ups and more detail of the duct arrangement and baghouses for Units 1 (to the extreme right) as well as partial views of adjoining Units 2 and 3.

The final set of figures, shown below, are different views of a typical baghouse for any of the
Units 1

-9, since these are identical.

# 24

# 25

# 26

# 27 While we do have the above drawings for the baghouses, we do not have all of the operational parameters for these baghouses as they are currently operated. Nor do we have any design or operational data on the cyclones, old remnants of the ESPs (both of which provide some particulate matter control), or the air preheater. Importantly, we do not know the flu gas temperatures at specific points in the gas path.

Nonetheless, it is obvious from a conceptual standpoint that if DSI is implemented, it would likely be into the two parallel ducts that lead from each unit’s air preheater to its baghouse. Any mixing would occur in the duct before capture of the particles in the baghouses.

# 28 3.2 Permit Requirements

The station is subject to a Title V permit issued by the Commonwealth of Kentucky. 11



# Focusing on SO2 and PM requirements, each of Units 1

-9 is subject to the following conditions:

“2a. Pursuant to 401 KAR 61:015, Section 4 (1), particulate matter emissions shall not exceed
0.11 lb/MMBtu based on three

-hour average for each unit.

b . Pursuant to 401 KAR 61:015, Section 5 (1), sulfur dioxide emissions shall not exceed 1.2 lbs/MMBtu based on a twenty

-four hour average for each unit.” 12



# In addition, Section J of the permit contains the Acid Rain SO2 allowance requirements for the
various units as follows 13 

# :!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!!! 11 

# Commonwealth of Kentucky, Energy and Environment Cabinet, Department for Environmental Protection, Division for Air Quality, Air Quality Permit Issued under 401 KAR 52:020, Source ID: 21

- 145

-00006, Permit: V

09

-002 R1. Issuance Date: October 22, 2009; Revision Date: February 7, 2011; Expiration Date: October 22, 2014

. 12 

# Ibid. 13 

# In addition, the TVA has fleet wide SO2 limits set by the 2011 Consent Decree that can also affect the decision of how to retrofit units at Shawnee.

# 29 3.3 Current Emissions

Summary information from one recent stack test conducted in May 2011 was available and reviewed at the time of preparation of this report. Results indicated that the 3

-run average of
filterable PM emissions from combined Units 1

-5 were 0.01 lb/MMBtu

. Similarly, the 3

-run average of filterable PM emissions from combined Units 6

-9 were 0.004 lb/MMBtu. The reason for the substantially smaller emissions from combined Units 6

-9 as compared to Units 1

-5 is not
clear since data on how each unit was operating was not available in the summary information
reviewed.

SO2 emissions from each unit are monitored by CEMS and are reported to the EPA. These data, on a monthly basis, are summarized in Attachment B.

Attachment B shows that monthly

-average SO2 emissions are generally around 0.7 lb/MMBtu
on a 30

-day average.

3.4 New Rules and Regulations

The units, if intended to be operational in the future using coal as the fuel, will need to meet the requirements of at least two recent regulations affecting SO2, PM and mercury emissions.

First, these units are subject to the electric utility Mercury and Air Toxics (MATS) rule. In the next few years, upon implementation, this rule will require either a reduction in acid gas (HCl) emissions or SO2 emissions as a surrogate for acid gases. The SO2 requirement is 0.2 lb/MMBtu, on a 30

-day rolling average. In addition, either specified metal emissions limits or a filterable PM emissions limit will also need to be met. Finally, this rule requires that a mercury
emissions limit will also need to be met.

In addition, emissions from the Shawnee plant cannot cause or contribute to the violation of the recently promulgated 1

-hour SO2 National Ambient Air Quality Standard (NAAQS) and the PM2.5 NAAQS.

# 30 3.5 SO2 Control Efficiency Required

Based on the above, it is clear that, while the current permit limits do not pose any constraints to SO2 emissions from any of the units now, the MATS rule will impose further reductions in SO2
emissions

. For these units, using current SO2 emissions levels of around 0.7 lb/MMBtu, the
MATS rule requirements imply that a roughly 70% reduction in SO2 emissions will be required, assuming that the same type of coal continues to be burned in the future

.

3.6 DSI Implementation Feasibility and Issues

The earlier discussion on DSI indicated that SO2 emissions could be reduced by 70%; however, in order to do so, it is likely that trona would be used as the sorbent, likely milled on site to reduce particle size, and that a relatively high NSR of around 2

-3 would be needed.

Some of the key questions that need to be further investigated include:

- capability of the baghouses for Units 1

-9 to handle the significantly greater expected PM load as a result of trona injection at a high NSR;

- whether the gas temperature after the air preheater is suitable for trona injection (it is likely that it is);

- based on the gas temperature, what is the ideal particle size of the trona that must be injected;

- what is the residence time of the gas in the duct length connecting the air preheater and the baghouse, and whether the residence time is sufficient to assure proper mixing needed for the 70% removal of SO2, even including the beneficial effects of the baghouses;

- design details on the current onsite active ash disposal area and ash pond;

- what is the impact of ash sales, if any from the station

.

# 31 It is clear that a proper assessment of these issues and others depends on the availability of more operational and engineering data than is currently available. Only then can these feasibility/cost impact issues be more thoroughly vetted and the true cost DSI at any or all of these units be properly assessed.

# 32 ATTACHMENT A

- RESUME

RANAJIT (RON) SAHU, Ph.D, QEP, CEM (Nevada)

CONSULTANT, ENVIRONMENTAL AND ENERGY ISSUE S


# 311 North Story Place Alhambra, CA 91801 Phone: 626

-382

-0001

e-mail (preferred): sahuron@earthlink.net

EXPERIENCE 

# SUMMARY 

# Dr. Sahu has over twenty one years of experience in the fields of environmental, mechanical, and chemical engineering including: program and project management services; design and specification of pollution control equipment; soils and groundwater remediation; combustion engineering evaluations; energy studies; multimedia environmental regulatory compliance (involving statutes and regulations such as the Federal CAA and its Amendments, Clean Water Act, TSCA, RCRA, CERCLA, SARA, OSHA, NEPA as well as various related state statutes); transportation air quality impact analysis; multimedia compliance audits; multimedia permitting (including air quality NSR/PSD permitting, Title V permitting, NPDES permitting for industrial and storm water discharges, RCRA permitting, etc.), multimedia/multi

-pathway human health risk assessments for toxics; air dispersion modeling; and regulatory strategy development and support including negotiation of consent agreements and orders. He has over nineteen years of project management experience and has successfully managed and executed numerous projects in this time period. This includes basic and applied research projects, design projects, regulatory compliance projects, permitting projects, energy studies, risk assessment projects, and projects involving the communication of environmental data and information to the public. Notably, he has successfully managed a complex soils and groundwater remediation project with a value of over $140 million involving soils characterization, development and implementation of the remediation strategy, regulatory and public interactions and other challenges. He has provided consulting services to numerous private sector, public sector and public interest group clients. His major clients over the past twenty one years include various steel mills, petroleum refineries, cement companies , aerospace companies, power generation facilities, lawn and garden equipment manufacturers, spa manufacturers, chemical distribution facilities, and various entities in the public sector including EPA, the US Dept. of Justice, California DTSC, various municipalities, etc.). Dr. Sahu has performed projects in over 44 states, numerous local jurisdictions and internationally. Dr. Sahu’s experience includes various projects in relation to industrial waste water as well as storm water pollution compliance include obtaining appropriate permits (such as point source NPDES permits) as well development of plans, assessment of remediation technologies, development of monitoring reports, and regulatory interactions. In addition to consulting, Dr. Sahu has taught numerous courses in several Southern California universities including UCLA (air pollution), UC Riverside (air pollution, process hazard analysis), and Loyola Marymount University (air pollution, risk assessment, hazardous waste management) for the past seventeen years. In this time period he has also taught at Caltech, his alma mater (various engineering courses), at the University of Southern California (air pollution controls) and at California State University, Fullerton (transportation and air quality).

# 33 Dr. Sahu has and continues to provide expert witness services in a number of environmental areas discussed above in both state and Federal courts as well as before administrative bodies (please see Annex A).

EXPERIENCE RECORD


# 2000

-present Independent Consultant. Providing a variety of private sector (industrial companies, land development companies, law firms, etc.) public sector (such as the US Department of Justice) and public interest group clients with project management, air quality consulting, waste remediation and management consulting, as well as regulatory and engineering support consulting services.
1995

-2000 Parsons ES, Associate, Senior Project Manager and Department Manager for Air Quality/Geosciences/Hazardous Waste Groups, Pasadena. Responsible for the management of a group of approximately 24 air quality and environmental professionals, 15 geoscience, and 10 hazardous waste professionals providing full

- service consulting, project management, regulatory compliance and A/E design assistance in all areas. Parsons ES, Manager for Air Source Testing Services . Responsible for the management of 8 individuals in the area of air source testing and air regulatory permitting projects located in Bakersfield, California.
1992

- 1995 Engineering

- Science, Inc. Principal Engineer and Senior Project Manager in the air quality department. Responsibilities included multimedia regulatory compliance and permitting (including hazardous and nuclear materials), air pollution engineering (emissions from stationary

and mobile sources, control of criteria and air toxics, dispersion modeling, risk assessment, visibility analysis, odor analysis), supervisory functions and project management.
1990

- 1992 Engineering

- Science, Inc. Principal Engineer and Project Manager in the air quality department. Responsibilities included permitting, tracking regulatory issues, technical analysis, and supervisory functions on numerous air, water, and hazardous waste projects. Responsibilities also include client and agency interfacing, project cost and schedule control, and reporting to internal and external upper management regarding project status.
1989

- 1990 Kinetics Technology International, Corp. Development Engineer. Involved in thermal engineering R&D and project work related to low

-NOx ceramic radiant burners, fired heater NOx reduction, SCR design, and fired heater retrofitting.
1988

- 1989 Heat Transfer Research, Inc. Research Engineer . Involved in the design of fired heaters, heat exchangers, air coolers, and other non

-fired equipment. Also did research in the area of heat exchanger tube vibrations.

EDUCATION


# 1984

- 1988 Ph.D., Mechanical Engineering, California Institute of Technology (Caltech), Pasadena, CA.
1984 M. S., Mechanical Engineering, Caltech, Pasadena, CA.
1978

- 1983 B. Tech (Honors), Mechanical Engineering, Indian Institute of Technology (IIT) Kharagpur, India

TEACHING 

# EXPERIENCE


# Caltech "Thermodynamics," Teaching Assistant, California Institute of Technology, 1983, 1987. "Air Pollution Control," Teaching Assistant, C alifornia Institute of Technology, 1985. "Caltech Secondary and High School Saturday Program,"

- taught various mathematics (algebra through

calculus) and science (physics and chemistry) courses to high school students, 1983

- 1989.

# 34 "Heat Transfer,"

- taught this course in the Fall and Winter terms of 1994

- 1995 in the Division of Engineering

and Applied Science. “Thermodynamics and Heat Transfer,” Fall and Winter Terms of 1996

- 1997. U.C. Riverside, Extension "Toxic and Hazardous Air Contaminants," University of California Extension Program, Riverside, California.

Various years since 1992. "Prevention and Management of Accidental Air Emissions," University of California Extension Program,

Riverside, California. Various years since 1992.
"Air Pollution Control Systems and Strategies," University of California Extension Program, Riverside,

California, Summer 1992

-93, Summer 1993

- 1994. "Air Pollution Calculations," University of California Extension Program, Riverside, California, Fall 1993

-94,

Winter 1993

-94, Fall 1994

-95. "Process Safety Management," University of California Extension Program, Riverside, California. Various years

since 1992

-2010. "Process Safety Management," University of California Extension Program, Riverside, California, at SCAQMD,

Spring 1993

-94. "Advanced Hazard Analysis

- A Special Course for LEPCs," University of California Extension Program,

Riverside, California, taught at San Diego, California, Spring 1993

- 1994. “Advanced Hazardous Waste Management” University of California Extension Program, Riverside, California.

2005. Loyola Marymount University
"Fundamentals of Air Pollution

- Regulations, Controls and Engineering," Loyola Marymount University, Dept.

of Civil Engineering. Various years since 1993. "Air Pollution Control," Loyola Marymount University, Dept. of Civil Engineering, Fall 1994. “Environmental Risk Assessment,” Loyola Marymount University, Dept. of Civil Engineering. Various years

since 1998. “Hazardous Waste Remediation” Loyola Marymount University, Dept. of Civil Engineering. Various years

since 2006. University of Southern California "Air Pollution Controls," University of Southern California, Dept. of Civil Engineering, Fall 1993, Fall 1994. "Air Pollution Fundamentals," University of Southern California, Dept. of Civil Engineering, Winter 1994. University of California, Los Angeles "Air Pollution Fundamentals," University of California, Los Angeles, Dept. of Civil and Environmental

Engineering, Spring 1994, Spring 1999, Spring 2000, Spring 2003, Spring 2006, Spring 2007, Spring 2008, Spring 2009. International Programs “Environmental Planning and Management,” 5 week program for visiting Chinese delegation, 1994. “Environmental Planning and Management,” 1 day program for visiting Russian delegation, 1995.
“Air Pollution Planning and Management,” IEP, UCR, Spring 1996. “Environmental Issues and Air Pollution,” IEP, UCR, October 1996.

# 35 PROFESSIONAL AFFILIATIONS AND HONORS 

# President of India Gold Medal, IIT Kharagpur, India, 1983.
Member of the Alternatives Assessment Committee of the Grand Canyon Visibility Transport Commission,

established by the Clean Air Act Amendments of 1990, 1992

-present. American Society of Mechanical Engineers: Los Angeles Section Executive Committee, Heat Transfer Division,

and Fuels and Combustion Technology Division, 1987

-present. Air and Waste Management Association, West Coast Section, 1989

-present.

PROFESSIONAL 

# C ERTIFICATIONS 

# EIT, California (# XE088305), 1993. REA I, California (#07438), 2000. Certified Permitting Professional, South Coast AQMD (#C 8320), since 1993. QEP, Institute of Professional Environmental Practice, since 2000. CEM, State of Nevada (#EM

- 1699). Expiration 10/07/2011.

PUBLICATIONS 

# (PARTIAL 

# LIST

# ) "Physical Properties and Oxidation Rates of Chars from Bituminous Coals," with Y.A. Levendis, R.C. Flagan and G.R. Gavalas, Fuel, 67, 275

-283 (1988). "Char Combustion: Measurement and Analysis of Particle Temperature Histories," with R.C. Flagan, G.R. Gavalas and P.S. Northrop, Comb. Sci. Tech. 60 , 215

-230 (1988).
"On the Combustion of B ituminous Coal Chars," PhD Thesis, California Institute of Technology (1988). "Optical Pyrometry: A Powerful Tool for Coal Combustion Diagnostics," J. Coal Quality, 8 , 17

-22 (1989).
"Post

-Ignition Transients in the Combustion of Single Char Particles," with Y.A. Levendis, R.C.Flagan and G.R. Gavalas, Fuel, 68 , 849

- 855 (1989). "A Model for Single Particle Combustion of Bituminous Coal Char." Proc. ASME National Heat Transfer Conference, Philadelphia, HTD

-Vol. 106 , 505

- 513 (1989).
"Discrete Simulation of Cenospheric Coal

-Char Combustion," with R.C. Flagan and G.R.Gavalas, Combust. Flame, 77, 337

-346 (1989). "Particle Measurements in Coal Combustion," with R.C. Flagan, in " Combustion Measurements " (ed. N. Chigier), Hemisphere Publishing Corp. (1991).
"Cross Linking in Pore Structures and Its Effect on Reactivity," with G.R. Gavalas in preparation. "Natural Frequencies and Mode Shapes of Straight Tubes," Proprietary Report for Heat Transfer Research Institute, Alhambra, CA (1990). "Optimal Tube Layouts for Kamui SL

- Series Exchangers," with K. Ishihara, Proprietary Report for Kamui Company Limited, Tokyo, Japan (1990). "HTRI Process Heater Conceptual Design," Proprietary Report for Heat Transfer Research Institute, Alhambra, CA (1990). "Asymptotic Theory of Transonic Wind Tunnel Wall Interference," with N.D. Malmuth and others, Arnold Engineering Development Center, Air Force Systems Command, USAF (1990). "Gas Radiation in a Fired Heater Convection Section," Proprietary Report for Heat Transfer Research Institute, College Station, TX (1990).

# 36 "Heat Transfer and Pressure Drop in NTIW Heat Exchangers," Proprietary Report for Heat Transfer Research Institute, College Station, TX (1991). "NOx Control and Thermal Design," Thermal Engineering Tech Briefs, (1994).
“From Puchase of Landmark Environmental Insurance to Remediation: Case Study in Henderson, Nevada,” with Robin E. Bain and Jill Quillin, presented at the AQMA Annual Meeting, Florida, 2001. “The Jones Act Contribution to Global Warming, Acid Rain and Toxic Air Contaminants,” with Charles W. Botsford, presented at the AQMA Annual Meeting, Florida, 2001.

PRESENTATIONS 

# (PARTIAL LIST

# )
"Pore Structure and Combustion Kinetics

- Interpretation of Single Particle Temperature

-Time Histories," with P.S. Northrop, R.C. Flagan and G.R. Gavalas, presented at the AIChE Annual Meeting, New York (1987). "Measurement of Temperature

-Time Histories of Burning Single Coal Char Particles," with R.C. Flagan, presented at the American Flame Research Committee Fall International Symposium, Pittsburgh, (1988). "Physical Characterization of a Cenospheric Coal Char Burned at High Temperatures," with R.C. Flagan and G.R. Gavalas, presented at the Fall Meeting of the Western States Section of the Combustion Institute, Laguna Beach, California (19 88). "Control of Nitrogen Oxide Emissions in Gas Fired Heaters

- The Retrofit Experience," with G. P. Croce and R. Patel, presented at the International Conference on Environmental Control of Combustion Processes (Jointly sponsored by the American Flame Research Committee and the Japan Flame Research Committee), Honolulu, Hawaii (1991).
"Air Toxics

- Past, Present and the Future," presented at the Joint AIChE/AAEE Breakfast Meeting at the AIChE 1991 Annual Meeting, Los Angeles, California, November 17

-22 ( 1991). "Air Toxics Emissions and Risk Impacts from Automobiles Using Reformulated Gasolines," presented at the Third Annual Current Issues in Air Toxics Conference, Sacramento, California, November 9

- 10 (1992). "Air Toxics from Mobile Sources," presented at the Environmental Health Sciences (ESE) Seminar Series, UCLA, Los Angeles, California, November 12, (1992). "Kilns, Ovens, and Dryers

- Present and Future," presented at the Gas Company Air Quality Permit Assistance Seminar, Industry Hills Sheraton, California, November 20, (1992). "The Design and Implementation of Vehicle Scrapping Programs," presented at the 86th Annual Meeting of the Air and Waste Management Association, Denver, Colorado, June 12, 1993. "Air Quality Planning and Control in Beijing, China," presented at the 87th Annual Meeting of the Air and Waste Management Association, Cincinnati, Ohio, June 19

-24, 1994.

# 37 Annex A

Expert Litigation Support

1. Matters for which Dr. Sahu has have provided depositions and affidavits/expert reports include:

(a) Deposition on behalf of Rocky Mountain Steel Mills, Inc. located in Pueblo, Colorado

– dealing with the manufacture of steel in mini

-mills including methods of air pollution control and BACT in steel mini

-mills and opacity issues at this steel mini

-mill (b) Affidavit for Rocky Mountain Steel Mills, Inc. located in Pueblo Colorado

– dealing with the technical uncertainties associated with night

-time opacity measurements in general and at this steel mini

-mill. (c) Expert reports and depositions (2/28/2002 and 3/ 1/2002; 12/2/2003 and 12/3/2003; 5/24/2004) on behalf of the US Department of Justice in connection with the Ohio Edison NSR Cases. United States, et al. v. Ohio Edison Co., et al. , C2

-99

- 1181 (S.D. Ohio). (d) Expert reports and depositions (5/23/2002 and 5/24/2002) on behalf of the US Department of Justice in connection with the Illinois Power NSR Case. United States v. Illinois Power Co., et al. , 99

- 833

-MJR (S.D. Ill.). (e) Expert reports and depositions (11/25/2002 and 11/26/2002) on behalf of the US Department of Justice in connection with the Duke Power NSR Case. United States, et al. v. Duke Energy Corp. , 1:00

-CV

- 1262 (M.D.N.C.). (f) Expert reports and depositions (10/6/2004 and 10/7/2004; 7/10/2006) on behalf of the US Department of Justice in connection with the American Electric Power NSR Cases. United States, et al. v. American Electric Power Service Corp., et al. , C2

-99

- 1182, C2

-99

- 1250 (S.D. Ohio). (g) Affidavit (March 2005) on behalf of the Minnesota Center for Environmental Advocacy and others in the matter of the Application of Heron Lake BioEnergy LLC to construct and operate an ethanol production facility

– submitted to the Minnesota Pollution Control Agency. (h) Expert reports and depositions (10/31/2005 and 11/1/2005) on behalf of the US Department of Justice in connection with the East Kentucky Power Cooperative NSR Case. United States v. East Kentucky Power Cooperative, Inc ., 5:04

-cv

-00034

-KSF (E.D. KY). (i) Deposition (10/20/2005) on behalf of the US Department of Justice in connection with the Cinergy NSR Case. United States, et al. v. Cinergy Corp., et al. , IP 99

- 1693

-C

-M/S (S.D. Ind.). (j) Affidavits and deposition on behalf of Basic Management Inc. (BMI) Companies in connection with the BMI vs. USA remediation cost recovery Case. (k) Expert report on behalf of Penn Future and others in the Cambria Coke plant permit challenge in Pennsylvania. (l) Expert report on behalf of the Appalachian Center for the Economy and the Environment and others in the Western Greenbrier permit challenge in West Virginia. (m) Expert report, deposition (via telephone on January 26, 2007) on behalf of various Montana petitioners (Citizens Awareness Network (CAN), Women’s Voices for the Earth (WVE) and the Clark Fork Coalition (CFC)) in the Thompson River Cogeneration LLC Permit No. 3175

-04 challenge.

# 38 (n) Expert report and deposition (2/2/07) on behalf of the Texas Clean Air Cities Coalition at the Texas State Office of Administrative Hearings (SOAH) in the matter of the permit challenges to TXU Project Apollo’s eight new proposed PRB

-fired PC boilers located at seven TX sites. (o) Expert testimony (July 2007) on behalf of the Izaak Walton League of America and others in connection with the acquisition of power by Xcel Energy from the proposed Gascoyne Power Plant

– at the State of Minnesota, Office of Administrative Hearings for the Minnesota PUC (MPUC No. E002/CN

-06

- 1518; OAH No. 12

-2500

- 17857

-2). (p) Affidavit (July 2007) Comments on the Big Cajun I Draft Permit on behalf of the Sierra Club

– submitted to the Louisiana DEQ. (q) Expert reports and deposition (12/ 13/2007) on behalf of Commonwealth of Pennsylvania

– Dept. of Environmental Protection, State of Connecticut, State of New York, and State of New Jersey (Plaintiffs) in connection with the Allegheny Energy NSR Case. Plaintiffs v. Allegheny Energy Inc., et al., 2:05cv0885 (W.D. Pennsylvania). (r) Expert reports and pre

-filed testimony before the Utah Air Quality Board on behalf of Sierra Club in the Sevier Power Plant permit challenge. (s) Expert reports and deposition (October 2007) on behalf of MTD Products Inc. , in connection with General Power Products, LLC v MTD Products Inc., 1:06 CVA 0143 (S.D. Ohio, Western Division) (t) Experts report and deposition (June 2008) on behalf of Sierra Club and others in the matter of permit challenges (Title V: 28.0801

-29 and PSD : 28.0803

-PSD) for the Big Stone II unit, proposed to be located near Milbank, South Dakota. (u) Expert reports, affidavit, and deposition (August 15, 2008) on behalf of Earthjustice in the matter of air permit challenge (CT

-4631) for the Basin Electric Dry Fork station, under construction near Gillette, Wyoming before the Environmental Quality Council of the State of Wyoming. (v) Affidavits (May 2010/June 2010 in the Office of Administrative Hearings))/Declaration and Expert Report (November 2009 in the Office of Administrative Hearings) on behalf of NRDC and the Southern Environmental Law Center in the matter of the air permit challenge for Duke Cliffside Unit 6. Office of Administrative Hearing Matters 08 EHR 0771, 0835 and 0836 and 09 HER 3102, 3174, and 3176 (consolidated). (w) Declaration (August 2008), Expert Report (January 2009), and Declaration (May 2009) on behalf of Southern Alliance for Clean Energy et al., v Duke Energy Carolinas, LLC. in the matter of the air permit challenge for Duke Cliffside Unit 6. S outhern Alliance for Clean Energy et al., v. Duke Energy Carolinas, LLC, Case No. 1:08

-cv

-00318

-LHT

-DLH (Western District of North Carolina, Asheville Division). (x) Dominion Wise County MACT Declaration (August 2008) (y) Expert Report on behalf of Sierra Club for the Green Energy Resource Recovery Project, MACT Analysis (June 13, 2008). (z) Expert Report on behalf of Sierra Club and the Environmental Integrity Project in the matter of the air permit challenge for NRG Limestone’s proposed Unit 3 in Texas (February 2009). (aa) Expert Report and deposition on behalf of MTD Products, Inc., in the matter of Alice Holmes and Vernon Holmes v. Home Depot USA, Inc., et al. (June 2009, July 2009). (bb) Expert Report on behalf of Sierra Club and the Southern Environmental Law Center in the matter of the air permit challenge for Santee Cooper’s proposed Pee Dee plant in South Carolina (August 2009). (cc) Statements (May 2008 and September 2009) on behalf of the Minnesota Center for Environmental Advocacy to the Minnesota Pollution Control Agency in the matter of the Minnesota Haze State Implementation Plans. (dd) Expert Report (August 2009) and Deposition (October 2009) on behalf of Environmental Defense, in the matter of permit challenges to the proposed Las Brisas coal fired power plant project at t he Texas State Office of Administrative Hearings (SOAH).

# 39 (ee) Deposition (October 2009) on behalf of Environmental Defense and others, in the matter of challenges to the proposed Coleto Creek coal fired power plant project at the Texas State Office of Administrative Hearings (SOAH). (October 2009). (ff) Expert Report, Rebuttal Report (September 2009) and Deposition (October 2009) on behalf of the Sierra Club, in the matter of challenges to the proposed Medicine Bow Fuel and Power IGL plant in Cheyenne, Wyoming. (gg) Expert Report (December 2009), Rebuttal reports (May 2010 and June 2010) and depositions (June 2010) on behalf of the US Department of Justice in connection with the Alabama Power Company NSR Case. United States v. Alabama Power Company, CV

-01

-HS

- 152

- S (Northern District of Alabama, Southern Division). (hh) Prefiled testimony (October 2009) and Deposition (December 2009) on behalf of Environmental Defense and others, in the matter of challenges to the proposed White Stallion Energy Center coal fired power plant project at the Texas State Office of Administrative Hearings (SOAH). (ii) Deposition (October 2009) on behalf of Environmental Defense and others, in the matter of challenges to the proposed Tenaska coal fired power plant project at the Texas State Office of Administrative Hearings (SOAH). (April 2010). (jj) Written Direct Testimony (July 2010) and Written Rebuttal Testimony (August 2010) on behalf of the State of New Mexico Environment Department in the matter of Proposed Regulation 20.2.350 NMAC

– Greenhouse Gas Cap and Trade Provisions, No. EIB 10

-04 (R), to the State of New Mexico, Environmental Improvement Board. (kk) Expert report (August 2010) and Rebuttal Expert Report (October 2010) on behalf of the US Department of Justice in connection with the Louisiana Generating NSR Case. United States v. Louisiana Generating, LLC, 09

-CV100

-RET

-CN (Middle District of Louisiana)

– Liability Phase. (ll) Declaration (August 2010), Reply Declaration (November 2010), Expert Report (April 2011), Supplemental and Rebuttal Expert Report (July 2011) on behalf of the US EPA and US Department of Justice in the matter of DTE Energy Company and Detroit Edison Company (Monroe Unit 2). United States of America v. DTE Energy Company and Detroit Edison Company, Civil Action No. 2:10

-cv

- 13101

-BAF

-RSW (US District Court for the Eastern District of Michigan). (mm) Expert Report and Deposition (August 2010) as well as Affidavit (September 2010) on behalf of Kentucky Waterways Alliance, Sierra Club, and Valley Watch in the matter of challenges to the NPDES permit issued for the Trimble County power plant by the Kentucky Energy and Environment Cabinet to Louisville Gas and Electric, File No. DOW

-41106

-047. (nn) Expert Report (August 2010), Rebuttal Expert Report (September 2010), Supplemental Expert Report (September 2011), and Declaration (November 2011) on behalf of Wild Earth Guardians in the matter of opacity exceedances and monitor downtime at the Public Service Company of Colorado (Xcel)’s Cherokee power plant. No. 09

-cv

- 1862 (D. Colo.). (oo) Written Direct Expert Testimony (August 2010) and Affidavit (February 2012) on behalf of Fall

-Line Alliance for a Clean Environment and others in the matter of the PSD Air Permit for Plant Washington issued by Georgia DNR at the Office of State Administrative Hearing, State of Georgia (OSAH

-BNR

-AQ

- 1031707

-98

- WALKER). (pp) Deposition (August 2010) on behalf of Environmental Defense, in the matter of the remanded permit challenge to the proposed Las Brisas coal fired power plant project at the Texas State Office of Administrative Hearings (SOAH). (qq) Expert Report, Supplemental/Rebuttal Expert Report, and Declarations (October 2010, September 2012) on behalf of New Mexico Environment Department (Plaintiff

-Intervenor), Grand Canyon Trust and Sierra Club (Plaintiffs) in the matter of Public Ser vice Company of New Mexico (PNM)’s Mercury Report for the San Juan Generating Station, CIVIL NO. 1:02

-CV

-0552 BB/ATC (ACE). US District Court for the District of New Mexico. (rr) Comment Report (October 2010) on the Draft Permit Issued by the Kansas DHE to Sunflower Electric for Holcomb Unit 2. Prepared on behalf of the Sierra Club and Earthjustice.

# 40 (ss) Expert Report (October 2010) and Rebuttal Expert Report (November 2010) (BART Determinations for PSCo Hayden and CSU Martin Drake units) to the Colorado Air Quality Commission on behalf of Coalition of Environmental Organizations. (tt) Expert Report (November 2010) (BART Determinations for TriState Craig Units, CSU Nixon Unit, and PRPA Rawhide Unit) to the Colorado Air Quality Commission on behalf of Coalition of Environmental Organizations. (uu) Declaration (November 2010) on behalf of the Sierra Club in connection with the Martin Lake Station Units 1, 2, and 3. Sierra Club v. Energy Future Holdings Corporation and Luminant Generation Company LLC, Case No. 5:10

-cv

-00156

-DF

-CMC (US District Court for the Eastern District of Texas, Texarkana Division). (vv) Comment Report (December 2010) on the Pennsylvania Department of Environmental Protection (PADEP)’s Proposal to grant Plan Approval for the Wellington Green Energy Resource Recovery Facility on behalf of the Chesapeake Bay Foundation, Group Against Smog and Pollution (GASP), National Park Conservation Association (NPCA), and the Sierra Club. (ww) Written Expert Testimony (January 2011) and Declaration (February 2011) to the Georgia Off ice of State Administrative Hearings (OSAH) in the matter of Minor Source HAPs status for the proposed Longleaf Energy Associates power plant (OSAH

-BNR

-AQ

- 1115157

- 60

-HOWELLS) on behalf of the Friends of the Chattahoochee and the Sierra Club). (xx) Declaration (February 2011) in the matter of the Draft Title V Permit for RRI Energy MidAtlantic Power Holdings LLC Shawville Generating Station (Pennsylvania), ID No. 17

-00001 on behalf of the Sierra Club. (yy) Expert Report (March 2011), Rebuttal Expert Report (Jue 2011) on behalf of the United States in United States of America v. Cemex, Inc. , Civil Action No. 09

-cv

-00019

-MSK

-MEH (US District Court for the District of Colorado). (zz) Declaration (April 2011) and Expert Report (July 16, 2012) in the matter of the Lower Colorado River Authority (LCRA)’s Fayette (Sam Seymour) Power Plant on behalf of the Texas Campaign for the Environment. Texas Campaign for the Environment v. Lower Colorado River Authority, Civil Action No. 4:11

-cv

-00791 (US District Court for the Southern District of Texas, Houston Division). (aaa) Declaration (June 2011) on behalf of the Plaintiffs MYTAPN in the matter of Microsoft

-Yes, Toxic Air Pollution

-No (MYTAPN) v. State of Washington, Department of Ecology and Microsoft Corporation Columbia Data Center to the Pollution Control Hearings Board, State of Washington, Matter No. PCHB No. 10

- 162. (bbb) Expert Report (June 2011) on behalf of the New Hampshire Sierra Club at the State of New Hampshire Public Utilities Commission, Docket No. 10

-261

– the 2010 Least Cost Integrated Resource Plan (LCIRP) submitted by the Public Service Company of New Hampshire (re. Merrimack Station Units 1 and 2). (ccc) Declaration (August 2011) in the matter of the Sandy Creek Energy Associates L.P. Sandy Creek Power Plant on behalf of Sierra Club and Public Citizen. Sierra Club, Inc. and Public Citizen, Inc. v. Sandy Creek Energy Associates, L.P., Civil Action No. A

-08

-CA

- 648

-LY (US District Court for the Western District of Texas, Austin Division). (ddd) Expert Report (October 2011) on behalf of the Defendants in the matter of John Quiles and Jeanette Quiles et al. v. Bradford

- White Corporation, MTD Products, Inc., Kohler Co., et al., Case No. 3:10

-cv

-747 (TJM/DEP) (US District Court for the Northern District of New York). (eee) Declaration (February 2012) and Second Declaration (February 2012) in the matter of Washington Environmental Council and Sierra Club Washington State Chapter v. Washington State Department of Ecology and Western States Petroleum Association, Case No. 11

-417

-MJP (US District Court for the Western District of Washington). (fff) Expert Report (March 2012) in the matter of Environment Texas Citizen Lobby, Inc and Sierra Club v. ExxonMobil Corporation et al., Civil Action No. 4:10

-cv

-4969 (US District Court for the Southern District of Texas, Houston Division). (ggg) Declaration (March 2012) in the matter of Center for Biological Diversity, et al. v. United States Environmental Protection Agency, Case No. 11

- 1101 (consolidated with 11

- 1285, 11

- 1328 and 11

- 1336) (US Court of Appeals for the District of Columbia Circuit).

# 41 (hhh) Declaration (March 2012) in the matter of Sierra Club v. The Kansas Department of Health and Environment, Case No. 11

- 105,493

-AS (Holcomb power plan) (Supreme Court of the State of Kansas). (iii) Declaration (March 2012) in the matter of the Las Brisas Energy Center Environmental Defense Fund et al., v. Texas Commission on Environmental Quality, Cause No. D

- 1

-GN

- 11

-001364 (District Court of Travis County, Texas, 261 st 

# Judicial District). (jjj) Expert Report (April 2012), Supplemental and Rebuttal Expert Report (July 2012), and Supplemental Rebuttal Expert Report (August 2012) in the matter of the Portland Power plant State of New Jersey and State of Connecticut (Intervenor

-Plaintiff) v. RRI Energy Mid

- Atlantic Power Holdings et al., Civil Action No. 07

-CV

5298 (JKG) (US District Court for the Eastern District of Pennsylvania). (kkk) Declaration (April 2012) in the matter of the EPA’s EGU MATS Rule, on behalf of the Environmental Integrity Project (lll) Declaration (September 2012) in the Matter of the Application of Energy Answers Incinerator, Inc. for a Certificate of Public Convenience and Necessity to Construct a 120 MW Generating Facility in Baltimore City, Maryland, before the Public Service Commission of Maryland, Case No. 9199. (mmm) Expert report (August 2012) on behalf of the US Department of Justice in connection with the Louisiana Generating NSR Case. United States v. Louisiana Generating, LLC, 09

-CV100

-RET

-CN (Middle District of Louisiana)

– Harm Phase.

2. Occasions where Dr. Sahu has provided Written or Oral testimony before Congress :

(nnn) In July 2012, provided expert written and oral testimony to the House Subcommittee on Energy and the Environment, Committee on Science, Space, and Technology at a Hearing entitled “Hitting the Ethanol Blend Wall

– Examining the Science on E15.”

3. Occasions where Dr. Sahu has provided oral testimony at trial or in similar proceedings include the following:

(ooo) In February, 2002, provided expert witness testimony on emissions data on behalf of Rocky Mountain Steel Mills, Inc. in Denver District Court. (ppp) In February 2003, provided expert witness testimony on regulatory framework and emissions calculation methodology issues on behalf of the US Department of Justice in the Ohio Edison NSR Case in the US District Court for the Southern District of Ohio. (qqq) In June 2003, provided expert witness testimony on regulatory framework, emissions calculation methodology, and emissions calculations on behalf of the US Department of Justice in the Illinois Power NSR Case in the US District Court for the Southern District of Illinois. (rrr) In August 2006, provided expert witness testimony regarding power plant emissions and BACT issues on a permit challenge (Western Greenbrier) on behalf of the Appalachian Center for the Economy and the Environment in West Virginia. (sss) In May 2007, provided expert witness testimony regarding power plant emissions and BACT issues on a permit challenge (Thompson River Cogeneration) on behalf of various Montana petitioners (Citizens Awareness Network (CAN), Women’s Voices for the Earth (WVE) and the Clark Fork Coalition (CFC)) before the Montana Board of Environmental Review. (ttt) In October 2007, provided expert witness testimony regarding power plant emissions and BACT issues on a permit challenge (Sevier Power Plant) on behalf of the Sierra Club before the Utah Air Quality Board.

# 42 (uuu) In August 2008, provided expert witness testimony regarding power plant emissions and BACT issues on a permit challenge (Big Stone Unit II) on behalf of the Sierra Club and Clean Water before the South Dakota Board of Minerals and the Environment. (vvv) In February 2009, provided expert witness testimony regarding power plant emissions and BACT issues on a permit challenge (Santee Cooper Pee Dee units) on behalf of the Sierra Club and the Southern Environmental Law Center before the South Carolina Board of Health and Environmental Control. (www) In February 2009, provided expert witness testimony regarding power plant emissions, BACT issues and MACT issues on a permit challenge (NRG Limestone Unit 3) on behalf of the Sierra Club and the Environmental Integrity Project before the Texas State Office of Administrative Hearings (SOAH) Administrative Law Judges. (xxx) In November 2009, provided expert witness testimony regarding power plant emissions, BACT issues and MACT issues on a permit challenge (Las Brisas Energy Center) on behalf of the Environmental Defense Fund before the Texas State Office of Administrative Hearings (SOAH) Administrative Law Judges. (yyy) In February 2010, provided expert witness testimony regarding power plant emissions, BACT issues and MACT issues on a permit challenge (White Stallion Energy Center) on behalf of the Environmental Defense Fund before the Texas State Office of Administrative Hearings (SOAH) Administrative Law Judges. (zzz) In September 2010 provided oral trial testimony on behalf of Commonwealth of Pennsylvania

– Dept. of Environmental Protection, State of Connecticut, State of New York, State of Maryland, and State of New Jersey (Plaintiffs) in connection with the Allegheny Energy NSR Case in US District Court in the Western District of Pennsylvania. Plaintiffs v. Allegheny Energy Inc., et al., 2:05cv0885 (W.D. Pennsylvania). (aaaa) Oral Direct and Rebuttal Expert Testimony (September 2010) on behalf of Fall

-Line Alliance for a Clean Environment and others in the matter of the PSD Air Permit for Plant Washington issued by Georgia DNR at the Office of State Administrative Hearing, State of Georgia (OSAH

-BNR

-AQ

- 1031707

-98

-WALKER). (bbbb) Oral Testimony (September 2010) on behalf of the State of New Mexico Environment D epartment in the matter of Proposed Regulation 20.2.350 NMAC

– Greenhouse Gas Cap and Trade Provisions, No. EIB 10

-04 (R), to the State of New Mexico, Environmental Improvement Board. (cccc) Oral Testimony (October 2010) regarding mercury and total PM/PM10 emissions and other issues on a remanded permit challenge (Las Brisas Energy Center) on behalf of the Environmental Defense Fund before the Texas State Office of Administrative Hearings (SOAH) Administrative Law Judges. (dddd) Oral Testimony (November 2010) regarding BART for PSCo Hayden, CSU Martin Drake units before the Colorado Air Quality Commission on behalf of the Coalition of Environmental Organizations. (eeee) Oral Testimony (December 2010) regarding BART for TriState Craig Units, CSU Nixon Unit, and PRPA Rawhide Unit) before the Colorado Air Quality Commission on behalf of the Coalition of Environmental Organizations. (ffff) Deposition (December 2010) on behalf of the US Department of Justice in connection with the Louisiana Generating NSR Case. United States v. Louisiana Generating, LLC, 09

-CV100

-RET

-CN (Middle District of Louisiana). (gggg) Deposition (February 2011 and January 2012) on behalf of Wild Earth Guardians in the matter of opacity exceedances and monitor downtime at the Public Service Company of Colorado (Xcel)’s Cherokee power plant. No. 09

-cv

- 1862 (D. Colo.). (hhhh) Oral Expert Testimony (February 2011) to the Georgia Office of State Administrative Hearings (OSAH) in the matter of Minor Source HAPs status for the proposed Longleaf Energy Associates power plant (OSAH

BNR

-AQ

- 11 15157

- 60

-HOWELLS) on behalf of the Friends of the Chattahoochee and the Sierra Club). (iiii) Deposition (August 2011) on behalf of the United States in United States of America v. Cemex, Inc. , Civil Action No. 09

-cv

-00019

-MSK

-MEH (US District Court for the District of Colorado). (jjjj) Deposition (July 2011) and Oral Testimony at Hearing (February 2012) on behalf of the Plaintiffs MYTAPN in the matter of Microsoft

-Yes, Toxic Air Pollution

-No (MYTAPN) v. State of Washington, Department of

# 43 Ecology and Microsoft Corporation Columbia Data Center to the Pollution Control Hearings Board, State of Washington, Matter No. PCHB No. 10

- 162. (kkkk) Oral Testimony at Hearing (March 2012) on behalf of the US Department of Justice in connection with the Louisiana Generating NSR Case. United States v. Louisiana Generating, LLC, 09

-CV100

-RET

-CN (Middle District of Louisiana). (llll) Oral Testimony at Hearing (April 2012) on behalf of the New Hampshire Sierra Club at the State of New Hampshire Public Utilities Commission, Docket No. 10

-261

– the 2010 Least Cost Integrated Resource Plan (LCIRP) submitted by the Public Service Company of New Hampshire (re. Merrimack Station Units 1 and 2).

# ATTACHMENT B

SUMMARY OF EPA AIR MARKET PROGRAM DATA
2006

-2011 EMISSIONS DATA FOR SHAWNEE FOSSIL PLANTST Plant Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control KY Shawnee 1 CSSH15 2006 1 308.0 0.752 149.3 0.365 84011.2 2090 818824 744 80406 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 2 305.0 0.743 150.2 0.366 84301.7 2086 821653 672 80833 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 3 363.0 0.782 176.6 0.380 95228.3 2057 928151 744 92604 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 4 337.7 0.725 184.3 0.396 95589.1 2059 931669 720 92868 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 5 343.1 0.753 164.0 0.360 93469.9 2090 911014 744 89444 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 6 319.7 0.730 161.4 0.369 89830.6 2103 875540 720 85431 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 7 347.2 0.737 181.1 0.384 96735.4 2120 942838 744 91256 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 8 343.7 0.727 183.4 0.388 96948.6 2085 944918 744 93000 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 9 316.2 0.733 161.5 0.375 88477.4 2037 862355 720 86888 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 10 327.6 0.742 170.2 0.386 90592.1 1975 882963 744 91762 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 11 308.1 0.722 162.8 0.382 87534.0 2001 853157 720 87504 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2006 12 323.2 0.772 160.7 0.384 85854.1 1964 836783 744 87445 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 1 309.7 0.746 158.5 0.382 85220.6 1959 830609 744 87015 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 2 287.6 0.742 144.2 0.372 79555.0 1969 775390 644 80805 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 3 337.0 0.710 172.8 0.364 97457.8 2015 949880 744 96753 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 4 300.5 0.721 149.4 0.358 85545.0 2000 833771 672 85538 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 5 327.6 0.728 145.6 0.324 92288.8 2059 899501 744 89654 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 6 319.7 0.722 163.2 0.369 90871.9 2086 885690 720 87133 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 7 356.1 0.758 179.0 0.381 96435.2 2063 939913 744 93505 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 8 368.9 0.771 205.6 0.430 98193.7 2076 957053 744 94598 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 9 300.0 0.713 158.8 0.377 86361.8 2107 841735 680 81973 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 10 332.6 0.715 173.6 0.373 95522.4 2062 931016 744 92647 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 11 320.0 0.736 165.0 0.380 89199.0 2012 869386 720 88684 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2007 12 331.3 0.745 172.1 0.387 91182.7 2000 888719 744 91191 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 1 350.0 0.778 189.2 0.421 92280.2 1965 899420 744 93931 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 2 324.4 0.804 175.7 0.435 82795.7 1944 806977 696 85200 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 3 350.8 0.791 187.2 0.422 91038.1 1964 887312 744 92725 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 4 336.9 0.747 205.7 0.456 92940.7 2018 901846 720 92119 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 5 335.4 0.757 198.7 0.448 91343.7 2007 886351 744 91042 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 6 267.0 0.718 146.4 0.393 76681.5 2048 744073 720 74902 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 7 304.3 0.733 158.0 0.381 85566.4 2116 830289 744 80864 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 8 307.7 0.761 169.4 0.419 83317.7 2056 808471 744 81046 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 9 280.9 0.721 161.4 0.414 80277.3 2026 778965 720 79246 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 10 310.2 0.749 175.4 0.424 85365.8 2004 828342 744 85179 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 11 336.4 0.801 184.8 0.440 86555.2 1976 839886 720 87587 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2008 12 320.5 0.844 153.5 0.404 78254.1 1982 759336 739 78948 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 1 185.3 0.737 88.0 0.350 51795.9 2023 502599 519 51211 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 2 0 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 3 224.3 0.668 101.8 0.303 69195.2 2078 671431 586 66609 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 4 283.6 0.688 161.8 0.392 84960.8 2045 824411 720 83102 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 5 262.9 0.685 140.6 0.366 79095.7 2048 767500 744 77246 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 6 256.6 0.682 140.7 0.374 77590.4 2060 752894 720 75341 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 7 291.9 0.753 161.1 0.416 79842.7 2050 774750 744 77886 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 8 262.2 0.756 138.6 0.400 71495.5 2090 693753 695 68403 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 9 183.5 0.729 97.7 0.388 51875.8 2126 503377 447 48808 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 10 286.2 0.720 149.4 0.376 81894.6 2051 794661 744 79874 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 11 218.2 0.658 111.4 0.336 68347.3 2073 663202 720 65935 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2009 12 269.1 0.637 145.7 0.344 87147.5 2023 845632 744 86170 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 1 227.4 0.664 122.0 0.356 70610.9 2024 685171 679 69783 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 2 263.6 0.680 140.3 0.362 79924.5 1999 775543 672 79963 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 3 255.2 0.632 144.5 0.358 83265.3 2001 807963 744 83244 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 4 223.2 0.616 130.3 0.360 74700.2 2008 724848 720 74401 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 5 260.0 0.662 143.7 0.366 80981.3 1994 785801 744 81207 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 6 257.1 0.695 142.8 0.386 76201.1 2081 739415 720 73231 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 7 254.0 0.704 150.3 0.417 74378.6 2096 721735 744 70988 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 8 217.3 0.689 135.9 0.431 64962.1 2093 630357 674 62080 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 9 244.4 0.684 156.6 0.439 73587.2 2054 714051 720 71642 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 10 232.5 0.671 136.9 0.396 71356.6 1996 692403 743 71503 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 11 96.9 0.706 51.5 0.375 28298.4 1978 274592 312 28606 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2010 12 349.6 0.765 216.1 0.473 94164.4 1921 913721 744 98044 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 1 342.9 0.737 202.9 0.436 95844.5 1956 930026 744 98005 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 2 271.6 0.701 160.9 0.415 79828.1 1979 774607 672 80691 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 3 270.8 0.626 172.9 0.400 89184.8 2023 865401 744 88187 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 4 259.8 0.601 168.4 0.389 89173.2 2069 865291 720 86215 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 5 258.3 0.603 169.2 0.395 88343.0 2073 857230 744 85219 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 6 249.3 0.598 142.4 0.342 85902.5 2068 833551 720 83094 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 7 281.8 0.646 177.3 0.407 89854.6 2060 871899 744 87245 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 8 286.4 0.681 175.9 0.418 86739.9 2045 841678 744 84846 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 9 253.5 0.663 149.6 0.391 78780.8 2034 764447 720 77454 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 10 280.1 0.688 159.8 0.392 83911.6 1972 814229 744 85118 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 11 259.1 0.680 143.2 0.376 78587.1 2030 762570 720 77421 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2011 12 108.9 0.676 56.1 0.348 33218.4 1987 322333 312 33440 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 1 142.9 0.642 82.6 0.371 45853.9 1970 444941 434 46552 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 2 0 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 3 109.7 0.697 59.4 0.377 32476.5 1998 315135 295 32505 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 4 194.8 0.794 121.5 0.495 50541.6 1904 490429 435 53101 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 5 314.4 0.797 176.3 0.447 81306.9 1924 788958 744 84499 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 6 260.7 0.743 120.6 0.344 72351.4 2024 702058 692 71506 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 7 286.9 0.779 124.9 0.339 76571.6 2046 736493 744 74844 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 8 266.0 0.707 127.9 0.340 78273.1 2042 752859 744 76660 DB-WF LNB Baghouse KY Shawnee 1 CSSH15 2012 9 258.7 0.737 110.3 0.314 72987.4 2036 702019 720 71689 DB-WF LNB Baghouse

0.717Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control 2 CSSH15 2006 1 318.5 0.752 154.3 0.364 86913.2 2090 847109 744 83190 DB-WF LNB Baghouse 2 CSSH15 2006 2 294.2 0.743 144.9 0.366 81306.3 2086 792457 672 77958 DB-WF LNB Baghouse 2 CSSH15 2006 3 355.1 0.784 172.5 0.381 92972.4 2056 906163 744 90436 DB-WF LNB Baghouse 2 CSSH15 2006 4 335.4 0.725 183.1 0.396 94924.8 2058 925195 720 92231 DB-WF LNB Baghouse 2 CSSH15 2006 5 348.5 0.754 166.5 0.360 94892.9 2090 924883 744 90800 DB-WF LNB Baghouse 2 CSSH15 2006 6 324.0 0.730 163.7 0.369 91033.5 2103 887265 720 86564 DB-WF LNB Baghouse 2 CSSH15 2006 7 347.9 0.737 181.3 0.384 96919.2 2120 944630 744 91417 DB-WF LNB Baghouse 2 CSSH15 2006 8 348.7 0.727 186.1 0.388 98356.6 2085 958641 744 94359 DB-WF LNB Baghouse 2 CSSH15 2006 9 274.4 0.728 138.9 0.369 77291.0 2044 753326 641 75642 DB-WF LNB Baghouse 2 CSSH15 2006 10 314.2 0.742 163.1 0.385 86881.2 1975 846795 744 87999 DB-WF LNB Baghouse 2 CSSH15 2006 11 315.5 0.722 166.6 0.381 89651.9 2001 873799 720 89608 DB-WF LNB Baghouse 2 CSSH15 2006 12 316.0 0.772 157.3 0.384 83955.5 1964 818279 744 85512 DB-WF LNB Baghouse 2 CSSH15 2007 1 312.0 0.746 159.7 0.382 85821.8 1959 836468 744 87630 DB-WF LNB Baghouse 2 CSSH15 2007 2 308.3 0.742 154.8 0.373 85240.2 1971 830800 658 86489 DB-WF LNB Baghouse 2 CSSH15 2007 3 337.7 0.710 173.0 0.364 97582.7 2015 951098 744 96876 DB-WF LNB Baghouse 2 CSSH15 2007 4 329.1 0.720 164.3 0.360 93772.1 2001 913956 720 93733 DB-WF LNB Baghouse 2 CSSH15 2007 5 330.5 0.728 147.0 0.324 93097.4 2059 907381 744 90435 DB-WF LNB Baghouse 2 CSSH15 2007 6 303.8 0.722 155.1 0.368 86391.6 2086 842022 720 82849 DB-WF LNB Baghouse 2 CSSH15 2007 7 359.2 0.758 180.5 0.381 97179.3 2063 947166 744 94234 DB-WF LNB Baghouse 2 CSSH15 2007 8 364.2 0.771 203.4 0.431 96866.2 2075 944114 744 93373 DB-WF LNB Baghouse 2 CSSH15 2007 9 308.9 0.714 162.9 0.376 88791.2 2108 865413 682 84242 DB-WF LNB Baghouse 2 CSSH15 2007 10 339.0 0.715 176.8 0.373 97345.2 2062 948783 744 94432 DB-WF LNB Baghouse 2 CSSH15 2007 11 331.2 0.736 170.7 0.379 92328.0 2012 899883 720 91785 DB-WF LNB Baghouse 2 CSSH15 2007 12 320.4 0.745 166.4 0.387 88230.1 2000 859941 730 88231 DB-WF LNB Baghouse 2 CSSH15 2008 1 359.7 0.779 193.7 0.420 94715.5 1965 923155 733 96422 DB-WF LNB Baghouse 2 CSSH15 2008 2 350.9 0.803 189.8 0.435 89641.8 1944 873704 696 92219 DB-WF LNB Baghouse 2 CSSH15 2008 3 372.6 0.791 198.5 0.422 96611.4 1964 941633 744 98364 DB-WF LNB Baghouse 2 CSSH15 2008 4 345.5 0.748 210.3 0.455 95218.0 2018 923944 720 94385 DB-WF LNB Baghouse 2 CSSH15 2008 5 345.7 0.757 204.9 0.449 94150.6 2006 913587 744 93852 DB-WF LNB Baghouse 2 CSSH15 2008 6 283.3 0.717 156.3 0.396 81412.9 2046 789984 720 79568 DB-WF LNB Baghouse 2 CSSH15 2008 7 320.5 0.733 166.7 0.381 90113.6 2115 874412 744 85200 DB-WF LNB Baghouse 2 CSSH15 2008 8 320.4 0.762 176.8 0.420 86702.4 2056 841314 744 84361 DB-WF LNB Baghouse 2 CSSH15 2008 9 302.0 0.722 173.9 0.416 86250.6 2025 836927 720 85183 DB-WF LNB Baghouse 2 CSSH15 2008 10 278.9 0.751 157.1 0.423 76554.9 2004 742848 639 76409 DB-WF LNB Baghouse 2 CSSH15 2008 11 355.1 0.801 195.2 0.440 91347.9 1977 886392 720 92434 DB-WF LNB Baghouse 2 CSSH15 2008 12 296.9 0.848 143.1 0.409 72182.5 1979 700420 696 72945 DB-WF LNB Baghouse 2 CSSH15 2009 1 244.8 0.740 117.0 0.353 68218.7 2016 661957 646 67674 DB-WF LNB Baghouse 2 CSSH15 2009 2 215.2 0.698 108.0 0.350 63571.1 2038 616858 596 62392 DB-WF LNB Baghouse 2 CSSH15 2009 3 254.8 0.675 115.4 0.306 77832.5 2121 755241 709 73396 DB-WF LNB Baghouse 2 CSSH15 2009 4 242.9 0.690 136.9 0.389 72576.2 2046 704237 663 70941 DB-WF LNB Baghouse 2 CSSH15 2009 5 245.8 0.685 131.5 0.366 74001.9 2049 718072 744 72240 DB-WF LNB Baghouse 2 CSSH15 2009 6 235.1 0.682 129.0 0.374 71105.0 2061 689963 720 69016 DB-WF LNB Baghouse 2 CSSH15 2009 7 274.6 0.754 150.9 0.414 75108.1 2052 728808 744 73219 DB-WF LNB Baghouse 2 CSSH15 2009 8 280.0 0.758 147.5 0.399 76166.5 2092 739078 744 72830 DB-WF LNB Baghouse 2 CSSH15 2009 9 292.3 0.750 153.1 0.393 80312.3 2113 779310 720 76008 DB-WF LNB Baghouse 2 CSSH15 2009 10 171.5 0.735 89.9 0.385 48118.6 2055 466916 468 46829 DB-WF LNB Baghouse 2 CSSH15 2009 11 82.1 0.655 42.1 0.336 25839.0 2046 250727 292 25263 DB-WF LNB Baghouse 2 CSSH15 2009 12 238.2 0.640 129.7 0.349 76730.5 2018 744551 669 76049 DB-WF LNB Baghouse 2 CSSH15 2010 1 245.7 0.664 131.5 0.355 76331.8 2030 740683 744 75204 DB-WF LNB Baghouse 2 CSSH15 2010 2 260.0 0.680 138.6 0.363 78794.9 1999 764582 672 78849 DB-WF LNB Baghouse 2 CSSH15 2010 3 266.8 0.632 151.0 0.358 86976.9 2000 843979 744 86973 DB-WF LNB Baghouse 2 CSSH15 2010 4 247.3 0.616 144.7 0.360 82771.7 2007 803170 720 82475 DB-WF LNB Baghouse 2 CSSH15 2010 5 273.6 0.662 151.6 0.366 85241.6 1994 827141 744 85497 DB-WF LNB Baghouse 2 CSSH15 2010 6 297.3 0.696 166.2 0.389 88068.9 2079 854574 720 84717 DB-WF LNB Baghouse 2 CSSH15 2010 7 327.9 0.704 195.3 0.419 96060.2 2095 932123 744 91723 DB-WF LNB Baghouse 2 CSSH15 2010 8 289.8 0.691 183.0 0.436 86484.5 2089 839200 744 82786 DB-WF LNB Baghouse 2 CSSH15 2010 9 285.8 0.685 184.3 0.441 86057.7 2053 835057 720 83853 DB-WF LNB Baghouse 2 CSSH15 2010 10 275.5 0.673 163.2 0.399 84409.7 1993 819063 744 84691 DB-WF LNB Baghouse 2 CSSH15 2010 11 281.0 0.691 160.1 0.394 83873.2 1970 813859 720 85166 DB-WF LNB Baghouse 2 CSSH15 2010 12 341.4 0.765 210.6 0.472 91985.7 1921 892580 744 95788 DB-WF LNB Baghouse 2 CSSH15 2011 1 321.7 0.737 190.8 0.437 89962.2 1956 872947 744 92007 DB-WF LNB Baghouse 2 CSSH15 2011 2 254.9 0.702 151.5 0.417 74820.6 1978 726017 672 75646 DB-WF LNB Baghouse 2 CSSH15 2011 3 238.9 0.626 152.4 0.399 78660.7 2024 763280 744 77738 DB-WF LNB Baghouse 2 CSSH15 2011 4 249.2 0.600 161.4 0.389 85552.2 2069 830154 720 82689 DB-WF LNB Baghouse 2 CSSH15 2011 5 249.1 0.603 163.0 0.395 85072.6 2073 825495 744 82073 DB-WF LNB Baghouse 2 CSSH15 2011 6 240.5 0.598 137.5 0.342 82893.4 2067 804352 720 80187 DB-WF LNB Baghouse 2 CSSH15 2011 7 274.4 0.647 172.9 0.407 87477.8 2060 848836 744 84946 DB-WF LNB Baghouse 2 CSSH15 2011 8 286.0 0.681 175.7 0.418 86534.1 2045 839681 744 84648 DB-WF LNB Baghouse 2 CSSH15 2011 9 249.2 0.663 147.2 0.392 77432.7 2035 751366 720 76099 DB-WF LNB Baghouse 2 CSSH15 2011 10 278.0 0.687 159.4 0.394 83448.1 1971 809732 744 84682 DB-WF LNB Baghouse 2 CSSH15 2011 11 192.6 0.661 107.7 0.370 60031.9 2029 582520 543 59173 DB-WF LNB Baghouse 2 CSSH15 2011 12 264.7 0.652 156.9 0.387 83691.9 2004 812101 744 83522 DB-WF LNB Baghouse 2 CSSH15 2012 1 236.8 0.651 136.4 0.375 74976.8 2009 727535 744 74636 DB-WF LNB Baghouse 2 CSSH15 2012 2 262.6 0.664 155.4 0.393 81503.7 2037 790870 696 80014 DB-WF LNB Baghouse 2 CSSH15 2012 3 268.6 0.702 142.9 0.374 78824.9 2019 764876 744 78071 DB-WF LNB Baghouse 2 CSSH15 2012 4 313.6 0.785 209.7 0.525 82322.2 1929 798813 720 85367 DB-WF LNB Baghouse 2 CSSH15 2012 5 308.1 0.797 173.0 0.448 79696.0 1924 773327 744 82829 DB-WF LNB Baghouse 2 CSSH15 2012 6 271.2 0.738 126.0 0.343 75745.5 2026 734993 720 74779 DB-WF LNB Baghouse 2 CSSH15 2012 7 288.6 0.778 125.6 0.339 77073.4 2048 741319 744 75281 DB-WF LNB Baghouse 2 CSSH15 2012 8 152.1 0.724 72.8 0.347 43663.9 2031 419975 413 43003 DB-WF LNB Baghouse 2 CSSH15 2012 9 257.3 0.735 110.2 0.315 72793.9 2037 700158 720 71485 DB-WF LNB Baghouse

### 0.716 Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control 3 CSSH15 2006 1 331.8 0.752 160.5 0.364 90505.9 2090 882125 744 86590 DB-WF LNB Baghouse 3 CSSH15 2006 2 310.6 0.743 153.1 0.366 85839.2 2086 836638 672 82292 DB-WF LNB Baghouse 3 CSSH15 2006 3 364.2 0.781 177.2 0.380 95737.7 2057 933116 744 93072 DB-WF LNB Baghouse 3 CSSH15 2006 4 340.2 0.726 185.4 0.396 96180.9 2058 937437 720 93476 DB-WF LNB Baghouse 3 CSSH15 2006 5 356.7 0.754 170.2 0.360 97064.6 2091 946050 744 92853 DB-WF LNB Baghouse 3 CSSH15 2006 6 339.8 0.730 171.6 0.369 95524.1 2104 931033 720 90801 DB-WF LNB Baghouse 3 CSSH15 2006 7 359.2 0.737 186.9 0.383 100070.0 2121 975339 744 94358 DB-WF LNB Baghouse 3 CSSH15 2006 8 355.4 0.727 190.0 0.389 100321.2 2084 977789 744 96269 DB-WF LNB Baghouse 3 CSSH15 2006 9 312.0 0.732 160.0 0.375 87436.6 2038 852210 720 85816 DB-WF LNB Baghouse 3 CSSH15 2006 10 327.2 0.742 170.0 0.385 90505.6 1975 882120 744 91665 DB-WF LNB Baghouse 3 CSSH15 2006 11 315.7 0.722 166.9 0.382 89742.3 2001 874680 720 89717 DB-WF LNB Baghouse 3 CSSH15 2006 12 329.3 0.772 163.8 0.384 87485.8 1964 852687 744 89090 DB-WF LNB Baghouse 3 CSSH15 2007 1 323.4 0.746 165.5 0.382 89003.7 1960 867481 744 90835 DB-WF LNB Baghouse 3 CSSH15 2007 2 278.0 0.742 139.9 0.373 76889.7 1967 749413 591 78182 DB-WF LNB Baghouse 3 CSSH15 2007 3 342.6 0.710 175.4 0.364 98962.5 2015 964546 744 98247 DB-WF LNB Baghouse 3 CSSH15 2007 4 330.4 0.720 164.9 0.359 94138.5 2001 917528 720 94094 DB-WF LNB Baghouse 3 CSSH15 2007 5 312.9 0.728 139.1 0.323 88225.4 2066 859896 744 85424 DB-WF LNB Baghouse 3 CSSH15 2007 6 321.1 0.721 163.7 0.368 91380.6 2088 890647 720 87541 DB-WF LNB Baghouse 3 CSSH15 2007 7 363.0 0.758 182.3 0.381 98239.0 2063 957493 744 95241 DB-WF LNB Baghouse 3 CSSH15 2007 8 364.1 0.771 203.4 0.431 96907.3 2075 944514 744 93388 DB-WF LNB Baghouse 3 CSSH15 2007 9 324.9 0.713 171.2 0.376 93447.7 2109 910798 720 88625 DB-WF LNB Baghouse 3 CSSH15 2007 10 340.6 0.715 177.7 0.373 97804.3 2062 953257 744 94872 DB-WF LNB Baghouse 3 CSSH15 2007 11 339.1 0.736 174.8 0.379 94514.0 2012 921189 720 93970 DB-WF LNB Baghouse 3 CSSH15 2007 12 343.7 0.745 178.5 0.387 94633.1 2000 922349 744 94628 DB-WF LNB Baghouse 3 CSSH15 2008 1 360.4 0.778 194.7 0.420 95034.1 1965 926261 744 96723 DB-WF LNB Baghouse 3 CSSH15 2008 2 334.4 0.803 181.2 0.435 85422.4 1944 832579 696 87890 DB-WF LNB Baghouse 3 CSSH15 2008 3 361.4 0.791 192.9 0.422 93780.7 1964 914044 744 95482 DB-WF LNB Baghouse 3 CSSH15 2008 4 338.4 0.748 206.3 0.456 93305.6 2018 905386 720 92487 DB-WF LNB Baghouse 3 CSSH15 2008 5 352.5 0.757 209.2 0.449 96019.4 2006 931721 744 95719 DB-WF LNB Baghouse 3 CSSH15 2008 6 304.5 0.717 167.3 0.394 87536.2 2048 849401 720 85479 DB-WF LNB Baghouse 3 CSSH15 2008 7 329.5 0.731 170.9 0.379 92854.9 2120 901012 744 87597 DB-WF LNB Baghouse 3 CSSH15 2008 8 336.4 0.759 185.1 0.418 91359.6 2061 886505 744 88658 DB-WF LNB Baghouse 3 CSSH15 2008 9 322.6 0.721 184.9 0.414 92178.2 2027 894444 720 90958 DB-WF LNB Baghouse 3 CSSH15 2008 10 66.9 0.764 38.3 0.437 18047.8 1994 175127 170 18100 DB-WF LNB Baghouse 3 CSSH15 2008 11 336.9 0.802 185.5 0.441 86636.9 1976 840679 695 87710 DB-WF LNB Baghouse 3 CSSH15 2008 12 360.2 0.841 173.3 0.405 88282.4 1983 856645 744 89023 DB-WF LNB Baghouse 3 CSSH15 2009 1 261.3 0.739 125.0 0.354 72892.7 2020 707312 646 72172 DB-WF LNB Baghouse 3 CSSH15 2009 2 217.4 0.699 109.1 0.351 64126.5 2038 622247 597 62935 DB-WF LNB Baghouse 3 CSSH15 2009 3 256.9 0.671 118.3 0.309 78936.3 2118 765953 648 74529 DB-WF LNB Baghouse 3 CSSH15 2009 4 278.1 0.688 158.7 0.393 83309.1 2046 808384 720 81444 DB-WF LNB Baghouse 3 CSSH15 2009 5 266.9 0.685 143.1 0.367 80324.9 2049 779428 744 78407 DB-WF LNB Baghouse 3 CSSH15 2009 6 239.5 0.682 131.9 0.375 72406.4 2060 702591 720 70296 DB-WF LNB Baghouse 3 CSSH15 2009 7 293.7 0.755 162.3 0.417 80151.5 2050 777746 744 78205 DB-WF LNB Baghouse 3 CSSH15 2009 8 305.1 0.757 161.3 0.400 83100.3 2092 806359 744 79440 DB-WF LNB Baghouse 3 CSSH15 2009 9 288.4 0.751 151.1 0.393 79177.9 2112 768303 720 74994 DB-WF LNB Baghouse 3 CSSH15 2009 10 296.6 0.720 155.0 0.376 84876.5 2050 823595 744 82792 DB-WF LNB Baghouse 3 CSSH15 2009 11 231.6 0.658 118.4 0.336 72550.1 2074 703985 720 69948 DB-WF LNB Baghouse 3 CSSH15 2009 12 264.3 0.636 143.1 0.344 85666.8 2025 831265 744 84608 DB-WF LNB Baghouse 3 CSSH15 2010 1 246.9 0.663 132.0 0.355 76720.6 2031 744456 744 75537 DB-WF LNB Baghouse 3 CSSH15 2010 2 250.7 0.679 133.5 0.362 76092.9 2000 738363 672 76075 DB-WF LNB Baghouse 3 CSSH15 2010 3 263.3 0.632 149.0 0.358 85843.9 2001 832984 744 85802 DB-WF LNB Baghouse 3 CSSH15 2010 4 240.5 0.615 140.7 0.360 80587.0 2009 781970 720 80230 DB-WF LNB Baghouse 3 CSSH15 2010 5 258.3 0.662 142.8 0.366 80400.6 1995 780166 744 80602 DB-WF LNB Baghouse 3 CSSH15 2010 6 263.7 0.697 147.4 0.390 77949.8 2080 756383 720 74938 DB-WF LNB Baghouse 3 CSSH15 2010 7 299.5 0.704 177.9 0.418 87747.5 2095 851460 744 83786 DB-WF LNB Baghouse 3 CSSH15 2010 8 291.4 0.691 184.5 0.438 86901.7 2089 843248 744 83204 DB-WF LNB Baghouse 3 CSSH15 2010 9 258.1 0.685 166.7 0.443 77614.8 2052 753132 720 75648 DB-WF LNB Baghouse 3 CSSH15 2010 10 250.9 0.672 149.1 0.399 76934.7 1993 746530 744 77186 DB-WF LNB Baghouse 3 CSSH15 2010 11 267.7 0.691 152.3 0.393 79821.3 1970 774543 720 81017 DB-WF LNB Baghouse 3 CSSH15 2010 12 330.3 0.765 204.4 0.473 88999.8 1921 863606 744 92658 DB-WF LNB Baghouse 3 CSSH15 2011 1 302.0 0.741 178.6 0.438 83956.3 1954 814669 744 85913 DB-WF LNB Baghouse 3 CSSH15 2011 2 240.8 0.699 143.3 0.416 71013.0 1980 689071 672 71731 DB-WF LNB Baghouse 3 CSSH15 2011 3 252.5 0.626 161.2 0.400 83134.8 2024 806695 744 82162 DB-WF LNB Baghouse 3 CSSH15 2011 4 248.8 0.600 161.4 0.389 85409.5 2069 828770 720 82549 DB-WF LNB Baghouse 3 CSSH15 2011 5 204.2 0.602 133.1 0.392 69906.1 2079 678329 612 67238 DB-WF LNB Baghouse 3 CSSH15 2011 6 217.5 0.599 124.3 0.342 74881.8 2069 726612 720 72400 DB-WF LNB Baghouse 3 CSSH15 2011 7 245.3 0.642 157.3 0.412 78701.8 2060 763679 658 76396 DB-WF LNB Baghouse 3 CSSH15 2011 8 253.4 0.679 157.6 0.422 76924.2 2042 746430 683 75340 DB-WF LNB Baghouse 3 CSSH15 2011 9 248.3 0.664 147.2 0.394 77088.9 2033 748030 720 75826 DB-WF LNB Baghouse 3 CSSH15 2011 10 260.4 0.688 150.2 0.397 77961.2 1970 756490 744 79139 DB-WF LNB Baghouse 3 CSSH15 2011 11 246.5 0.677 137.2 0.377 75000.7 2028 727768 720 73965 DB-WF LNB Baghouse 3 CSSH15 2011 12 244.1 0.652 144.7 0.386 77210.6 2006 749210 744 76982 DB-WF LNB Baghouse 3 CSSH15 2012 1 238.7 0.651 137.8 0.376 75551.5 2009 733112 744 75230 DB-WF LNB Baghouse 3 CSSH15 2012 2 140.5 0.675 83.0 0.399 42907.7 2064 416355 380 41580 DB-WF LNB Baghouse 3 CSSH15 2012 3 56.2 0.715 32.1 0.409 16199.9 2004 157196 158 16170 DB-WF LNB Baghouse 3 CSSH15 2012 4 300.7 0.785 202.7 0.529 78948.9 1927 766079 716 81957 DB-WF LNB Baghouse 3 CSSH15 2012 5 306.8 0.797 172.4 0.448 79384.1 1926 770300 744 82443 DB-WF LNB Baghouse 3 CSSH15 2012 6 269.4 0.739 125.2 0.344 75097.5 2025 728705 720 74176 DB-WF LNB Baghouse 3 CSSH15 2012 7 286.9 0.779 125.1 0.340 76581.8 2047 736591 744 74841 DB-WF LNB Baghouse 3 CSSH15 2012 8 262.2 0.707 126.0 0.340 77129.6 2043 741860 744 75518 DB-WF LNB Baghouse 3 CSSH15 2012 9 253.5 0.736 108.5 0.315 71671.7 2036 689364 720 70407 DB-WF LNB Baghouse

### 0.716 Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control 4 CSSH15 2006 1 323.7 0.752 156.9 0.364 88352.2 2089 861134 744 84604 DB-WF LNB Baghouse 4 CSSH15 2006 2 304.2 0.742 149.9 0.366 84113.6 2086 819819 672 80658 DB-WF LNB Baghouse 4 CSSH15 2006 3 361.9 0.781 175.9 0.380 95039.7 2057 926313 744 92401 DB-WF LNB Baghouse 4 CSSH15 2006 4 341.3 0.725 186.1 0.395 96554.1 2058 941075 720 93814 DB-WF LNB Baghouse 4 CSSH15 2006 5 352.1 0.753 168.1 0.360 95909.0 2091 934786 744 91750 DB-WF LNB Baghouse 4 CSSH15 2006 6 337.6 0.730 170.5 0.369 94906.9 2104 925017 720 90216 DB-WF LNB Baghouse 4 CSSH15 2006 7 355.8 0.736 185.0 0.383 99146.7 2121 966340 744 93469 DB-WF LNB Baghouse 4 CSSH15 2006 8 133.8 0.754 66.9 0.377 36427.4 2121 355043 273 34350 DB-WF LNB Baghouse 4 CSSH15 2006 9 276.4 0.736 139.7 0.372 77047.5 2033 750952 620 75807 DB-WF LNB Baghouse 4 CSSH15 2006 10 329.5 0.742 171.2 0.385 91142.3 1974 888325 744 92320 DB-WF LNB Baghouse 4 CSSH15 2006 11 271.7 0.726 141.5 0.378 76844.2 2002 748968 634 76755 DB-WF LNB Baghouse 4 CSSH15 2006 12 304.8 0.772 151.6 0.384 81009.8 1963 789569 744 82527 DB-WF LNB Baghouse 4 CSSH15 2007 1 308.0 0.746 157.4 0.381 84737.3 1959 825899 744 86529 DB-WF LNB Baghouse 4 CSSH15 2007 2 290.0 0.742 145.7 0.373 80216.7 1967 781839 618 81562 DB-WF LNB Baghouse 4 CSSH15 2007 3 341.0 0.710 174.6 0.364 98551.6 2015 960542 744 97835 DB-WF LNB Baghouse 4 CSSH15 2007 4 330.4 0.720 164.9 0.359 94114.9 2001 917298 720 94077 DB-WF LNB Baghouse 4 CSSH15 2007 5 325.2 0.728 144.4 0.323 91620.5 2059 892987 744 88992 DB-WF LNB Baghouse 4 CSSH15 2007 6 307.2 0.722 156.7 0.368 87319.3 2086 851065 720 83708 DB-WF LNB Baghouse 4 CSSH15 2007 7 347.0 0.758 174.4 0.381 93933.3 2063 915528 744 91081 DB-WF LNB Baghouse 4 CSSH15 2007 8 363.6 0.771 202.9 0.430 96826.9 2076 943731 744 93269 DB-WF LNB Baghouse 4 CSSH15 2007 9 292.5 0.711 154.3 0.375 84375.0 2109 822370 652 80026 DB-WF LNB Baghouse 4 CSSH15 2007 10 321.0 0.714 167.5 0.373 92209.3 2062 898725 744 89416 DB-WF LNB Baghouse 4 CSSH15 2007 11 294.0 0.736 151.1 0.378 81916.2 2012 798403 720 81443 DB-WF LNB Baghouse 4 CSSH15 2007 12 322.8 0.745 167.8 0.387 88923.7 2000 866701 744 88944 DB-WF LNB Baghouse 4 CSSH15 2008 1 282.7 0.775 152.1 0.417 74899.2 1969 730013 598 76075 DB-WF LNB Baghouse 4 CSSH15 2008 2 0 DB-WF LNB Baghouse 4 CSSH15 2008 3 303.2 0.787 161.6 0.419 79062.9 1965 770596 607 80467 DB-WF LNB Baghouse 4 CSSH15 2008 4 326.5 0.743 201.0 0.457 90574.7 2018 878888 720 89768 DB-WF LNB Baghouse 4 CSSH15 2008 5 378.0 0.757 224.3 0.449 102932.2 2007 998800 744 102586 DB-WF LNB Baghouse 4 CSSH15 2008 6 315.4 0.717 174.0 0.395 90726.0 2047 880353 720 88655 DB-WF LNB Baghouse 4 CSSH15 2008 7 338.7 0.733 176.2 0.382 95186.6 2115 923638 744 90001 DB-WF LNB Baghouse 4 CSSH15 2008 8 338.8 0.761 187.7 0.422 91743.5 2057 890230 744 89196 DB-WF LNB Baghouse 4 CSSH15 2008 9 311.2 0.721 180.0 0.417 88954.0 2025 863160 720 87863 DB-WF LNB Baghouse 4 CSSH15 2008 10 347.4 0.749 197.1 0.425 95639.3 2005 928029 744 95422 DB-WF LNB Baghouse 4 CSSH15 2008 11 244.6 0.800 133.9 0.438 62998.7 1981 611306 486 63612 DB-WF LNB Baghouse 4 CSSH15 2008 12 381.8 0.843 184.1 0.407 93354.3 1981 905859 744 94239 DB-WF LNB Baghouse 4 CSSH15 2009 1 280.2 0.740 134.9 0.356 78060.1 2011 757453 699 77628 DB-WF LNB Baghouse 4 CSSH15 2009 2 269.9 0.698 136.9 0.354 79707.1 2039 773433 672 78175 DB-WF LNB Baghouse 4 CSSH15 2009 3 55.2 0.685 26.4 0.328 16606.4 2190 161140 119 15168 DB-WF LNB Baghouse 4 CSSH15 2009 4 127.5 0.684 74.1 0.397 38440.2 2047 373001 328 37563 DB-WF LNB Baghouse 4 CSSH15 2009 5 61.8 0.686 33.3 0.370 18555.1 2069 180048 191 17933 DB-WF LNB Baghouse 4 CSSH15 2009 6 267.7 0.683 147.0 0.375 80764.5 2058 783693 699 78501 DB-WF LNB Baghouse 4 CSSH15 2009 7 311.9 0.753 173.1 0.418 85365.8 2049 828343 744 83312 DB-WF LNB Baghouse 4 CSSH15 2009 8 302.4 0.757 160.2 0.401 82293.7 2090 798533 744 78753 DB-WF LNB Baghouse 4 CSSH15 2009 9 295.6 0.749 155.3 0.393 81371.5 2113 789588 720 77002 DB-WF LNB Baghouse 4 CSSH15 2009 10 300.4 0.720 157.0 0.376 85981.0 2050 834313 744 83891 DB-WF LNB Baghouse 4 CSSH15 2009 11 224.0 0.658 114.5 0.336 70143.9 2071 680636 720 67723 DB-WF LNB Baghouse 4 CSSH15 2009 12 271.1 0.637 147.1 0.345 87743.2 2023 851412 744 86767 DB-WF LNB Baghouse 4 CSSH15 2010 1 253.3 0.663 135.4 0.355 78711.8 2030 763778 744 77533 DB-WF LNB Baghouse 4 CSSH15 2010 2 273.6 0.680 145.8 0.362 82964.0 1999 805037 672 83003 DB-WF LNB Baghouse 4 CSSH15 2010 3 263.9 0.632 149.5 0.358 86061.5 2001 835096 744 86024 DB-WF LNB Baghouse 4 CSSH15 2010 4 208.1 0.614 122.1 0.360 69863.3 2009 677914 720 69565 DB-WF LNB Baghouse 4 CSSH15 2010 5 243.7 0.662 135.2 0.367 75850.1 1995 736011 744 76045 DB-WF LNB Baghouse 4 CSSH15 2010 6 284.4 0.696 158.7 0.389 84205.2 2081 817082 720 80912 DB-WF LNB Baghouse 4 CSSH15 2010 7 321.5 0.704 191.8 0.420 94091.4 2094 913018 744 89859 DB-WF LNB Baghouse 4 CSSH15 2010 8 296.1 0.692 187.7 0.439 88186.1 2088 855711 744 84461 DB-WF LNB Baghouse 4 CSSH15 2010 9 280.0 0.685 181.1 0.443 84309.8 2051 818097 720 82214 DB-WF LNB Baghouse 4 CSSH15 2010 10 265.7 0.673 157.5 0.399 81408.3 1993 789938 744 81693 DB-WF LNB Baghouse 4 CSSH15 2010 11 272.4 0.691 155.0 0.393 81260.9 1971 788512 720 82474 DB-WF LNB Baghouse 4 CSSH15 2010 12 349.0 0.765 215.8 0.473 94023.4 1921 912353 744 97876 DB-WF LNB Baghouse 4 CSSH15 2011 1 325.8 0.738 193.5 0.438 90973.0 1955 882756 744 93072 DB-WF LNB Baghouse 4 CSSH15 2011 2 278.6 0.701 165.9 0.418 81856.2 1977 794287 672 82789 DB-WF LNB Baghouse 4 CSSH15 2011 3 267.7 0.626 171.1 0.400 88206.7 2023 855909 744 87212 DB-WF LNB Baghouse 4 CSSH15 2011 4 267.2 0.600 173.5 0.390 91746.4 2069 890260 720 88696 DB-WF LNB Baghouse 4 CSSH15 2011 5 262.1 0.602 171.8 0.395 89671.4 2074 870119 744 86489 DB-WF LNB Baghouse 4 CSSH15 2011 6 241.3 0.598 138.0 0.342 83149.0 2067 806832 720 80454 DB-WF LNB Baghouse 4 CSSH15 2011 7 266.7 0.646 168.7 0.409 85045.5 2059 825234 744 82591 DB-WF LNB Baghouse 4 CSSH15 2011 8 219.6 0.674 137.7 0.422 67182.3 2044 651902 573 65748 DB-WF LNB Baghouse 4 CSSH15 2011 9 252.4 0.663 149.7 0.393 78409.9 2031 760848 720 77210 DB-WF LNB Baghouse 4 CSSH15 2011 10 268.4 0.689 154.3 0.396 80334.0 1970 779515 744 81569 DB-WF LNB Baghouse 4 CSSH15 2011 11 242.0 0.678 134.3 0.376 73602.3 2030 714199 720 72526 DB-WF LNB Baghouse 4 CSSH15 2011 12 112.7 0.676 58.1 0.348 34375.4 1987 333560 310 34605 DB-WF LNB Baghouse 4 CSSH15 2012 1 131.6 0.643 75.6 0.369 42194.4 1970 409432 404 42828 DB-WF LNB Baghouse 4 CSSH15 2012 2 0.0 0.548 0.0 0.548 0.4 2089 4 0 0 DB-WF LNB Baghouse 4 CSSH15 2012 3 111.1 0.704 60.7 0.384 32550.5 1989 315853 296 32728 DB-WF LNB Baghouse 4 CSSH15 2012 4 324.4 0.784 218.8 0.529 85334.3 1928 828040 720 88537 DB-WF LNB Baghouse 4 CSSH15 2012 5 324.6 0.797 182.5 0.448 83898.2 1924 814102 744 87200 DB-WF LNB Baghouse 4 CSSH15 2012 6 271.3 0.739 127.2 0.346 75677.7 2020 734335 716 74941 DB-WF LNB Baghouse 4 CSSH15 2012 7 308.3 0.779 134.9 0.341 82292.1 2044 791515 744 80524 DB-WF LNB Baghouse 4 CSSH15 2012 8 284.4 0.708 137.2 0.341 83579.5 2040 803898 744 81934 DB-WF LNB Baghouse 4 CSSH15 2012 9 268.2 0.735 115.0 0.315 75831.0 2035 729369 720 74523 DB-WF LNB Baghouse

0.713

### Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control 5 CSSH15 2006 1 313.8 0.751 152.2 0.364 85738.3 2090 835657 744 82052 DB-WF LNB Baghouse 5 CSSH15 2006 2 304.0 0.742 150.0 0.366 84033.4 2086 819037 672 80574 DB-WF LNB Baghouse 5 CSSH15 2006 3 357.8 0.782 174.1 0.380 93913.1 2057 915332 744 91328 DB-WF LNB Baghouse 5 CSSH15 2006 4 331.9 0.725 181.2 0.396 93897.0 2059 915177 720 91224 DB-WF LNB Baghouse 5 CSSH15 2006 5 332.7 0.756 158.7 0.360 90313.6 2090 880251 739 86405 DB-WF LNB Baghouse 5 CSSH15 2006 6 295.8 0.729 150.0 0.370 83294.7 2104 811838 635 79186 DB-WF LNB Baghouse 5 CSSH15 2006 7 351.2 0.736 182.9 0.383 97861.2 2121 953812 744 92297 DB-WF LNB Baghouse 5 CSSH15 2006 8 352.3 0.727 188.1 0.388 99404.0 2085 968850 744 95360 DB-WF LNB Baghouse 5 CSSH15 2006 9 325.8 0.734 166.7 0.375 91138.9 2037 888296 720 89497 DB-WF LNB Baghouse 5 CSSH15 2006 10 332.3 0.742 172.6 0.385 91905.9 1975 895768 744 93076 DB-WF LNB Baghouse 5 CSSH15 2006 11 312.9 0.722 165.4 0.382 88905.6 2001 866526 720 88876 DB-WF LNB Baghouse 5 CSSH15 2006 12 320.7 0.772 159.5 0.384 85211.2 1963 830517 744 86797 DB-WF LNB Baghouse 5 CSSH15 2007 1 312.4 0.745 159.9 0.382 85987.8 1959 838086 744 87786 DB-WF LNB Baghouse 5 CSSH15 2007 2 292.5 0.742 146.7 0.372 80844.9 1968 787962 635 82142 DB-WF LNB Baghouse 5 CSSH15 2007 3 333.9 0.710 170.9 0.364 96465.6 2015 940210 744 95762 DB-WF LNB Baghouse 5 CSSH15 2007 4 328.5 0.720 164.0 0.360 93570.8 2001 911994 720 93528 DB-WF LNB Baghouse 5 CSSH15 2007 5 329.8 0.728 146.4 0.323 92908.2 2060 905537 744 90223 DB-WF LNB Baghouse 5 CSSH15 2007 6 270.8 0.727 136.9 0.367 76455.5 2085 745178 664 73328 DB-WF LNB Baghouse 5 CSSH15 2007 7 361.7 0.758 181.9 0.381 97913.6 2063 954322 744 94944 DB-WF LNB Baghouse 5 CSSH15 2007 8 374.2 0.770 208.6 0.430 99673.2 2076 971472 744 96015 DB-WF LNB Baghouse 5 CSSH15 2007 9 332.9 0.713 175.5 0.376 95761.6 2108 933351 720 90856 DB-WF LNB Baghouse 5 CSSH15 2007 10 331.0 0.714 173.0 0.373 95101.1 2061 926910 744 92274 DB-WF LNB Baghouse 5 CSSH15 2007 11 331.7 0.736 171.1 0.380 92475.2 2012 901317 720 91937 DB-WF LNB Baghouse 5 CSSH15 2007 12 337.1 0.745 175.2 0.387 92830.1 2000 904776 744 92846 DB-WF LNB Baghouse 5 CSSH15 2008 1 365.5 0.778 197.2 0.420 96351.1 1965 939097 744 98056 DB-WF LNB Baghouse 5 CSSH15 2008 2 340.9 0.803 184.6 0.435 87138.0 1944 849300 696 89650 DB-WF LNB Baghouse 5 CSSH15 2008 3 83.1 0.810 44.3 0.432 21054.0 1958 205205 168 21504 DB-WF LNB Baghouse 5 CSSH15 2008 4 332.2 0.745 204.5 0.459 91860.5 2018 891365 699 91063 DB-WF LNB Baghouse 5 CSSH15 2008 5 353.4 0.757 210.4 0.450 96273.8 2006 934190 744 95975 DB-WF LNB Baghouse 5 CSSH15 2008 6 308.1 0.717 170.3 0.396 88530.1 2046 859046 720 86539 DB-WF LNB Baghouse 5 CSSH15 2008 7 345.6 0.734 179.7 0.381 97104.1 2115 942245 744 91831 DB-WF LNB Baghouse 5 CSSH15 2008 8 337.4 0.761 186.4 0.421 91339.0 2057 886305 744 88816 DB-WF LNB Baghouse 5 CSSH15 2008 9 286.0 0.721 165.4 0.417 81800.0 2028 793741 672 80654 DB-WF LNB Baghouse 5 CSSH15 2008 10 338.8 0.749 192.0 0.424 93304.0 2005 905369 744 93089 DB-WF LNB Baghouse 5 CSSH15 2008 11 353.6 0.802 194.2 0.440 90856.6 1975 881625 720 91997 DB-WF LNB Baghouse 5 CSSH15 2008 12 360.6 0.843 173.6 0.406 88212.0 1982 855962 744 89008 DB-WF LNB Baghouse 5 CSSH15 2009 1 294.3 0.742 140.5 0.355 81703.3 2011 792804 744 81271 DB-WF LNB Baghouse 5 CSSH15 2009 2 272.0 0.699 137.8 0.354 80247.2 2038 778674 672 78743 DB-WF LNB Baghouse 5 CSSH15 2009 3 305.0 0.672 140.2 0.309 93566.0 2107 907910 744 88815 DB-WF LNB Baghouse 5 CSSH15 2009 4 270.1 0.688 154.6 0.394 80908.2 2044 785087 696 79160 DB-WF LNB Baghouse 5 CSSH15 2009 5 269.0 0.685 143.9 0.366 80948.0 2049 785474 744 79008 DB-WF LNB Baghouse 5 CSSH15 2009 6 264.4 0.682 145.0 0.374 79949.6 2061 775786 720 77585 DB-WF LNB Baghouse 5 CSSH15 2009 7 304.0 0.754 168.0 0.416 83157.5 2050 806916 744 81126 DB-WF LNB Baghouse 5 CSSH15 2009 8 300.0 0.757 158.7 0.401 81645.7 2090 792245 744 78136 DB-WF LNB Baghouse 5 CSSH15 2009 9 264.3 0.751 138.0 0.392 72498.9 2114 703493 720 68576 DB-WF LNB Baghouse 5 CSSH15 2009 10 282.2 0.721 147.3 0.376 80681.1 2050 782885 744 78700 DB-WF LNB Baghouse 5 CSSH15 2009 11 222.0 0.658 113.5 0.336 69544.8 2071 674824 720 67149 DB-WF LNB Baghouse 5 CSSH15 2009 12 274.2 0.637 148.6 0.346 88637.8 2022 860093 744 87693 DB-WF LNB Baghouse 5 CSSH15 2010 1 253.3 0.663 135.5 0.355 78696.7 2030 763631 744 77549 DB-WF LNB Baghouse 5 CSSH15 2010 2 274.3 0.680 146.1 0.362 83200.7 1999 807333 672 83239 DB-WF LNB Baghouse 5 CSSH15 2010 3 273.5 0.632 154.9 0.358 89163.3 2000 865195 744 89145 DB-WF LNB Baghouse 5 CSSH15 2010 4 248.6 0.616 145.4 0.360 83210.0 2007 807423 720 82924 DB-WF LNB Baghouse 5 CSSH15 2010 5 283.5 0.661 156.6 0.365 88394.9 1995 857739 744 88624 DB-WF LNB Baghouse 5 CSSH15 2010 6 282.4 0.695 156.9 0.386 83708.8 2081 812265 720 80456 DB-WF LNB Baghouse 5 CSSH15 2010 7 25.7 0.673 15.6 0.409 7876.7 2086 76432 84 7551 DB-WF LNB Baghouse 5 CSSH15 2010 8 307.7 0.691 196.7 0.442 91769.2 2085 890480 718 88008 DB-WF LNB Baghouse 5 CSSH15 2010 9 291.3 0.685 188.3 0.442 87710.5 2053 851095 720 85463 DB-WF LNB Baghouse 5 CSSH15 2010 10 288.6 0.672 171.2 0.398 88578.6 1995 859515 744 88818 DB-WF LNB Baghouse 5 CSSH15 2010 11 304.5 0.692 173.2 0.393 90741.0 1970 880501 720 92100 DB-WF LNB Baghouse 5 CSSH15 2010 12 349.8 0.764 216.4 0.473 94322.6 1921 915256 744 98198 DB-WF LNB Baghouse 5 CSSH15 2011 1 330.9 0.737 196.3 0.437 92602.7 1956 898570 744 94703 DB-WF LNB Baghouse 5 CSSH15 2011 2 270.3 0.700 161.5 0.418 79574.1 1980 772142 651 80363 DB-WF LNB Baghouse 5 CSSH15 2011 3 260.9 0.620 169.1 0.402 86734.7 2029 841625 693 85484 DB-WF LNB Baghouse 5 CSSH15 2011 4 280.3 0.600 181.5 0.388 96292.3 2071 934371 720 93009 DB-WF LNB Baghouse 5 CSSH15 2011 5 249.5 0.603 164.3 0.397 85341.0 2077 828100 645 82188 DB-WF LNB Baghouse 5 CSSH15 2011 6 0 DB-WF LNB Baghouse 5 CSSH15 2011 7 265.6 0.654 169.1 0.416 83704.5 2060 812221 625 81254 DB-WF LNB Baghouse 5 CSSH15 2011 8 314.8 0.680 193.9 0.419 95425.3 2044 925957 744 93368 DB-WF LNB Baghouse 5 CSSH15 2011 9 261.3 0.663 155.3 0.394 81198.5 2033 787908 720 79891 DB-WF LNB Baghouse 5 CSSH15 2011 10 283.5 0.688 163.5 0.397 84882.6 1970 823652 744 86174 DB-WF LNB Baghouse 5 CSSH15 2011 11 284.4 0.678 158.0 0.377 86411.1 2029 838489 720 85178 DB-WF LNB Baghouse 5 CSSH15 2011 12 292.0 0.652 172.6 0.386 92283.1 2005 895465 744 92052 DB-WF LNB Baghouse 5 CSSH15 2012 1 261.7 0.651 151.9 0.378 82813.1 2005 803575 744 82616 DB-WF LNB Baghouse 5 CSSH15 2012 2 279.1 0.664 166.1 0.395 86609.8 2036 840418 696 85069 DB-WF LNB Baghouse 5 CSSH15 2012 3 300.6 0.703 159.8 0.373 88199.5 2019 855841 744 87380 DB-WF LNB Baghouse 5 CSSH15 2012 4 334.9 0.785 223.7 0.524 87969.7 1931 853612 720 91136 DB-WF LNB Baghouse 5 CSSH15 2012 5 300.2 0.799 170.3 0.453 77457.9 1920 751609 663 80686 DB-WF LNB Baghouse 5 CSSH15 2012 6 291.5 0.740 135.8 0.345 81187.4 2024 787797 720 80237 DB-WF LNB Baghouse 5 CSSH15 2012 7 315.8 0.779 138.1 0.341 84314.0 2044 810961 744 82496 DB-WF LNB Baghouse 5 CSSH15 2012 8 182.6 0.721 88.6 0.350 52647.6 2029 506382 469 51903 DB-WF LNB Baghouse 5 CSSH15 2012 9 270.6 0.736 115.9 0.315 76429.6 2036 735127 720 75085 DB-WF LNB Baghouse

0.717ST Plant Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control KY Shawnee 6 CSSH60 2006 1 306.5 0.700 143.1 0.327 89791.4 2187 875160 744 82113 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 2 292.0 0.700 136.8 0.328 85550.3 2124 833821 672 80574 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 3 332.4 0.732 157.4 0.347 93189.4 2109 908279 744 88384 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 4 320.6 0.684 163.5 0.349 96198.2 2079 937601 720 92536 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 5 327.7 0.712 154.2 0.335 94467.2 2062 920732 744 91613 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 6 300.3 0.694 151.0 0.349 88798.5 2035 865481 720 87277 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 7 331.3 0.691 178.0 0.371 98376.8 2095 958836 744 93915 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 8 340.9 0.740 172.5 0.374 94543.7 1969 921481 744 96010 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 9 309.1 0.761 142.9 0.352 83339.2 1902 812272 720 87619 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 10 325.3 0.744 160.9 0.368 89667.4 2005 873951 744 89451 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 11 317.1 0.713 157.8 0.355 91224.4 2089 889125 720 87352 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2006 12 328.1 0.748 143.2 0.326 90077.5 2120 877944 744 84985 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 1 298.2 0.710 139.2 0.331 86230.3 2131 840448 744 80935 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 2 286.0 0.744 141.3 0.368 78836.4 2095 768382 622 75255 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 3 344.0 0.714 166.9 0.347 98805.0 2167 963012 744 91202 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 4 350.0 0.746 171.2 0.365 96239.5 2196 938007 720 87641 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 5 334.2 0.683 167.7 0.343 100410.9 2334 978666 744 86039 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 6 313.5 0.675 163.3 0.351 95348.3 2244 929317 720 84996 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 7 355.9 0.701 190.6 0.375 104154.6 2284 1015155 744 91217 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 8 395.5 0.729 226.7 0.418 111264.7 2327 1084451 744 95612 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 9 82.5 0.694 42.2 0.355 24362.0 2297 237447 166 21213 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 10 80.9 0.709 42.1 0.369 23413.4 2051 228198 198 22828 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 11 337.3 0.714 177.8 0.376 96927.7 2068 944711 720 93755 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2007 12 333.2 0.710 169.5 0.361 96235.7 2082 937965 744 92459 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 1 340.9 0.753 172.3 0.381 92909.5 1933 905534 744 96141 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 2 315.6 0.776 155.2 0.382 83431.7 1954 813168 696 85416 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 3 334.5 0.783 167.5 0.392 87612.0 1902 853923 744 92147 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 4 350.6 0.759 199.4 0.432 95225.2 1952 923500 720 97587 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 5 344.8 0.760 172.2 0.379 93647.7 1877 907552 744 99759 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 6 292.3 0.718 143.0 0.351 84013.8 1953 814237 720 86030 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 7 300.4 0.677 160.4 0.361 91648.7 2042 888177 744 89754 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 8 299.6 0.710 155.1 0.368 87070.7 1977 843714 744 88103 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 9 284.7 0.683 149.2 0.358 86049.5 2027 834094 720 84918 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 10 307.6 0.728 147.2 0.348 87164.5 1969 844772 744 88558 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 11 344.9 0.789 161.9 0.370 90254.3 1945 874871 720 92808 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2008 12 339.6 0.832 133.1 0.326 84234.2 1944 816622 744 86675 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 1 274.0 0.735 115.8 0.310 76931.6 1977 745892 744 77833 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 2 234.3 0.725 99.0 0.306 66735.4 1919 646789 634 69557 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 3 79.4 0.661 34.0 0.283 24758.7 2140 240245 255 23140 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 4 217.3 0.673 78.6 0.243 66598.6 2005 645458 720 66420 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 5 244.2 0.673 103.5 0.285 74916.3 1991 725940 744 75258 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 6 269.1 0.674 115.8 0.290 82444.2 2043 799116 720 80715 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 7 317.1 0.747 150.3 0.354 87566.2 2101 849493 744 83359 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 8 288.2 0.767 125.2 0.333 77499.9 2057 751447 744 75364 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 9 287.7 0.758 126.0 0.332 78283.3 2087 758945 719 75031 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 10 304.3 0.749 143.4 0.353 83695.0 2069 812114 744 80919 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 11 235.3 0.660 115.6 0.324 73537.3 2130 713567 720 69057 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2009 12 260.8 0.615 135.3 0.319 87408.6 2042 847640 744 85627 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 1 241.4 0.654 120.9 0.328 76131.6 2013 737931 677 75623 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 2 274.6 0.659 143.8 0.345 85998.2 2056 834071 672 83644 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 3 288.5 0.607 170.9 0.360 97901.4 2131 949980 744 91893 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 4 213.4 0.605 112.4 0.319 72695.1 2119 705396 588 68600 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 5 292.5 0.637 141.1 0.307 94731.3 2102 919222 744 90153 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 6 302.6 0.703 147.0 0.341 88775.7 2111 861352 720 84121 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 7 191.6 0.700 113.5 0.415 56463.3 2030 547234 470 55642 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 8 315.4 0.681 176.2 0.380 95539.5 2129 926800 744 89754 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 9 290.1 0.690 171.4 0.408 86679.0 2086 841084 720 83115 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 10 177.1 0.658 100.8 0.375 55447.7 2145 538034 469 51688 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 11 29.8 0.694 12.4 0.288 8860.0 2095 85973 102 8459 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2010 12 369.7 0.765 185.9 0.385 99581.4 1984 966287 744 100407 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 1 349.5 0.757 164.4 0.356 95143.2 1969 923216 744 96639 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 2 280.8 0.695 129.0 0.319 83265.9 2015 807968 672 82638 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 3 277.8 0.602 145.3 0.315 95089.7 2130 922700 744 89275 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 4 284.8 0.601 151.0 0.319 97678.4 2137 947819 720 91399 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 5 288.9 0.599 165.3 0.343 99364.7 2143 964182 744 92750 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 6 273.2 0.591 150.8 0.326 95335.1 2196 925076 720 86834 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 7 315.4 0.639 174.3 0.353 101746.4 2191 987294 744 92856 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 8 309.0 0.670 167.3 0.363 95031.9 2151 922141 744 88354 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 9 274.3 0.661 137.1 0.330 85574.8 2149 830370 720 79653 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 10 278.8 0.674 139.6 0.337 85305.0 2092 827755 744 81544 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 11 183.7 0.657 96.6 0.346 57647.0 2067 559374 481 55791 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2011 12 0 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 1 158.5 0.627 79.0 0.313 52067.2 2080 505234 438 50072 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 2 54.1 0.650 26.8 0.322 17141.5 2043 166331 140 16779 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 3 299.5 0.696 132.3 0.308 88693.5 2096 860635 744 84641 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 4 348.0 0.773 177.8 0.395 92800.4 2066 900486 720 89829 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 5 334.5 0.773 155.0 0.358 89143.3 2114 864999 744 84334 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 6 283.2 0.727 125.2 0.321 80255.0 2217 778751 719 72390 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 7 317.2 0.768 139.1 0.337 85894.7 2209 826163 744 77771 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 8 271.7 0.675 130.6 0.324 83683.5 2174 804895 744 77001 DB-WF LNB Baghouse KY Shawnee 6 CSSH60 2012 9 263.7 0.720 116.6 0.318 76119.8 2159 732143 720 70510 DB-WF LNB Baghouse

0.702ST Plant Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control KY Shawnee 7 CSSH60 2006 1 308.5 0.700 144.1 0.327 90385.1 2187 880946 744 82667 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 2 289.3 0.702 135.1 0.328 84567.9 2122 824246 672 79712 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 3 339.2 0.733 160.5 0.347 94994.0 2107 925868 744 90160 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 4 317.7 0.684 161.5 0.348 95290.7 2079 928757 720 91669 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 5 322.5 0.712 151.6 0.335 92911.2 2062 905567 744 90121 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 6 305.2 0.693 153.4 0.348 90373.4 2034 880831 720 88880 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 7 323.9 0.691 173.5 0.370 96144.1 2094 937074 744 91829 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 8 329.2 0.740 166.5 0.374 91253.3 1967 889410 744 92804 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 9 300.0 0.761 138.4 0.351 80845.4 1903 787966 720 84974 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 10 311.3 0.744 154.5 0.369 85881.1 2006 837047 744 85608 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 11 329.4 0.713 164.1 0.355 94852.5 2088 924486 720 90848 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2006 12 334.3 0.748 146.1 0.327 91734.4 2119 894094 744 86563 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 1 312.3 0.709 145.7 0.331 90360.3 2129 880703 738 84891 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 2 322.8 0.746 160.1 0.370 88826.6 2094 865752 664 84858 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 3 343.9 0.715 166.9 0.347 98718.6 2166 962169 728 91153 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 4 352.6 0.745 172.6 0.365 97075.3 2196 946153 720 88393 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 5 351.1 0.684 175.5 0.342 105335.9 2333 1026668 744 90319 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 6 316.4 0.675 164.8 0.351 96223.4 2245 937847 720 85734 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 7 367.6 0.702 196.5 0.375 107487.2 2284 1047637 744 94135 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 8 395.9 0.730 225.8 0.416 111296.4 2328 1084759 744 95632 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 9 323.2 0.660 166.6 0.340 100525.0 2344 979773 670 85778 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 10 358.8 0.712 175.4 0.348 103430.1 2142 1008088 744 96594 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 11 342.0 0.714 179.8 0.376 98218.1 2068 957289 720 94975 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2007 12 351.0 0.710 178.5 0.361 101454.4 2082 988829 744 97458 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 1 341.3 0.754 172.5 0.381 92886.1 1932 905305 744 96155 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 2 335.0 0.776 165.2 0.383 88606.8 1953 863607 696 90754 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 3 370.7 0.782 185.7 0.392 97235.9 1901 947723 744 102274 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 4 349.6 0.760 198.8 0.432 94905.1 1953 920403 720 97212 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 5 333.3 0.760 166.2 0.379 90457.4 1877 876642 744 96367 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 6 291.9 0.718 142.4 0.350 83891.3 1953 813051 720 85922 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 7 284.0 0.677 151.0 0.360 86578.8 2043 839042 744 84772 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 8 291.5 0.711 150.3 0.366 84633.9 1975 820107 738 85693 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 9 290.9 0.683 152.0 0.357 87864.1 2027 851683 720 86675 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 10 323.0 0.728 154.4 0.348 91509.6 1969 886885 744 92948 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 11 349.2 0.789 163.9 0.370 91298.7 1946 884994 720 93851 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2008 12 291.1 0.843 115.2 0.333 71276.9 1928 690932 659 73937 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 1 218.9 0.733 94.0 0.315 61585.4 1969 597060 705 62543 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 2 237.6 0.725 100.1 0.306 67626.4 1918 655398 672 70530 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 3 258.6 0.677 106.1 0.278 78732.0 2062 763595 672 76355 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 4 250.2 0.675 90.4 0.244 76530.1 2007 741734 720 76265 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 5 243.8 0.673 103.2 0.285 74782.7 1991 724642 744 75113 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 6 259.4 0.674 111.6 0.290 79465.0 2043 770245 720 77777 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 7 310.9 0.747 147.1 0.353 85842.9 2102 832774 744 81670 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 8 265.7 0.765 116.0 0.334 71646.9 2055 694628 672 69722 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 9 0 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 10 59.7 0.742 27.8 0.346 16583.1 2031 160914 145 16329 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 11 212.9 0.655 104.9 0.323 67009.7 2122 650225 667 63167 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2009 12 267.5 0.617 137.8 0.318 89445.2 2041 867414 744 87634 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 1 247.6 0.654 123.0 0.325 78159.8 2017 757564 744 77499 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 2 268.5 0.659 140.3 0.344 84013.4 2055 814818 672 81762 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 3 275.8 0.608 163.7 0.361 93528.5 2130 907548 744 87832 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 4 247.7 0.609 129.1 0.317 83896.3 2123 814085 720 79046 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 5 267.6 0.636 129.1 0.307 86742.7 2101 841704 744 82566 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 6 294.6 0.702 142.7 0.340 86518.5 2112 839452 720 81912 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 7 319.4 0.699 173.8 0.380 94309.1 2051 913895 744 91971 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 8 309.5 0.680 173.1 0.380 93853.9 2107 910443 744 89099 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 9 290.7 0.689 171.3 0.406 87001.7 2072 844215 720 83982 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 10 279.7 0.661 153.6 0.363 87148.4 2134 845641 744 81673 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 11 303.6 0.679 141.8 0.317 92223.9 2078 894888 720 88763 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2010 12 335.0 0.769 171.2 0.393 89773.3 1976 871114 744 90852 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 1 344.6 0.756 162.2 0.356 93891.6 1971 911072 744 95286 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 2 271.8 0.695 125.1 0.320 80589.0 2017 781992 672 79927 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 3 267.0 0.601 140.1 0.316 91495.0 2134 887819 744 85740 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 4 262.7 0.601 139.0 0.318 90089.2 2137 874178 720 84299 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 5 277.5 0.600 159.0 0.344 95352.2 2144 925246 744 88940 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 6 262.8 0.591 144.3 0.324 91704.3 2200 889845 720 83368 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 7 285.0 0.640 157.2 0.353 91862.6 2193 891387 744 83761 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 8 294.0 0.670 158.5 0.361 90447.2 2154 877654 744 83980 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 9 264.0 0.661 131.6 0.330 82312.4 2151 798714 720 76526 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 10 274.1 0.673 137.1 0.337 83912.1 2089 814240 744 80336 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 11 184.5 0.663 94.2 0.339 57340.0 2065 556396 533 55546 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2011 12 243.1 0.646 112.0 0.298 77534.0 2045 752347 744 75838 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 1 252.0 0.642 116.0 0.295 80949.4 2087 785493 744 77559 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 2 216.5 0.670 91.9 0.284 66647.3 2060 646703 574 64721 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 3 257.9 0.701 112.3 0.305 75834.3 2097 735858 668 72330 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 4 347.7 0.774 178.2 0.396 92652.4 2065 899049 720 89757 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 5 337.1 0.773 156.0 0.358 89847.6 2115 871833 744 84973 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 6 279.7 0.727 123.5 0.321 79276.7 2215 769258 720 71582 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 7 313.2 0.768 136.9 0.336 84853.1 2210 816146 744 76777 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 8 278.1 0.675 133.4 0.324 85624.6 2173 823565 744 78794 DB-WF LNB Baghouse KY Shawnee 7 CSSH60 2012 9 267.6 0.720 118.3 0.318 77307.4 2159 743567 720 71630 DB-WF LNB Baghouse

0.701ST Plant Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control KY Shawnee 8 CSSH60 2006 1 311.5 0.700 145.4 0.327 91280.5 2187 889673 744 83463 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 2 245.9 0.710 113.4 0.328 71044.9 2123 692445 572 66927 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 3 0.4 0.659 0.2 0.323 125.7 2131 1225 113 118 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 4 195.9 0.686 98.2 0.344 58630.9 2077 571452 441 56448 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 5 339.3 0.712 159.6 0.335 97737.9 2062 952610 744 94819 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 6 314.0 0.693 157.7 0.348 92959.1 2033 906033 720 91429 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 7 333.9 0.691 178.9 0.370 99116.0 2094 966040 744 94680 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 8 341.9 0.740 172.8 0.374 94805.1 1967 924027 744 96381 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 9 317.9 0.762 146.5 0.351 85639.7 1903 834694 720 90000 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 10 339.9 0.743 167.9 0.367 93827.1 2003 914495 744 93702 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 11 333.7 0.713 166.2 0.355 96092.7 2088 936574 720 92052 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2006 12 347.1 0.748 151.9 0.327 95268.3 2119 928536 744 89897 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 1 317.2 0.709 148.1 0.331 91808.4 2128 894816 725 86299 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 2 317.6 0.744 157.3 0.369 87558.4 2093 853390 646 83662 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 3 346.8 0.715 167.6 0.346 99493.5 2165 969723 708 91930 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 4 372.5 0.746 181.9 0.364 102463.1 2196 998666 720 93301 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 5 351.5 0.684 175.8 0.342 105417.6 2333 1027464 744 90376 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 6 322.0 0.676 167.6 0.352 97802.2 2243 953235 720 87221 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 7 348.5 0.701 184.9 0.372 101973.4 2276 993896 712 89603 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 8 392.0 0.730 223.4 0.416 110123.4 2326 1073327 740 94678 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 9 279.3 0.666 143.7 0.343 86012.2 2322 838328 580 74080 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 10 351.2 0.712 171.7 0.348 101217.9 2141 986527 744 94534 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 11 335.6 0.714 176.6 0.376 96430.1 2067 939861 720 93289 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2007 12 338.6 0.710 172.2 0.361 97782.9 2083 953045 744 93907 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 1 343.7 0.754 173.6 0.381 93578.9 1933 912058 744 96836 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 2 327.5 0.777 161.2 0.383 86480.2 1953 842880 696 88540 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 3 353.4 0.782 177.2 0.392 92742.8 1902 903931 744 97547 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 4 340.5 0.760 193.5 0.432 92349.3 1953 895622 720 94573 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 5 334.1 0.760 166.7 0.379 90740.4 1877 879382 744 96662 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 6 294.3 0.718 143.7 0.351 84584.7 1952 819769 720 86646 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 7 289.0 0.677 153.9 0.361 88083.3 2042 853625 744 86253 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 8 303.0 0.712 156.3 0.367 87895.6 1976 851717 738 88960 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 9 286.7 0.683 149.7 0.356 86663.6 2026 840036 720 85551 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 10 305.7 0.729 146.3 0.349 86537.9 1968 838701 744 87959 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 11 342.1 0.789 160.7 0.370 89506.2 1946 867620 720 92010 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2008 12 345.8 0.833 135.5 0.326 85640.6 1942 830256 744 88185 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 1 254.8 0.736 107.5 0.310 71437.7 1978 692644 744 72223 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 2 238.2 0.723 100.1 0.304 68011.0 1918 659128 672 70922 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 3 283.1 0.678 114.3 0.274 86086.6 2062 834933 744 83487 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 4 186.3 0.675 70.7 0.256 56919.5 2026 551838 499 56200 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 5 246.3 0.673 104.2 0.284 75591.2 1991 732478 744 75918 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 6 260.4 0.673 112.1 0.290 79793.8 2045 773433 720 78051 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 7 310.6 0.746 146.7 0.352 85813.4 2102 832483 744 81636 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 8 304.8 0.767 131.8 0.332 81982.6 2054 794900 744 79827 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 9 294.9 0.758 128.5 0.330 80244.0 2087 777959 720 76915 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 10 189.1 0.745 87.7 0.346 52309.7 2071 507547 483 50511 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 11 217.6 0.659 106.8 0.324 68020.8 2126 660037 720 63984 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2009 12 232.3 0.615 120.1 0.318 77933.2 2042 755749 744 76340 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 1 235.8 0.654 116.5 0.323 74374.8 2020 720866 744 73623 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 2 91.6 0.688 43.2 0.324 27456.7 1986 266188 227 27653 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 3 0.0 0.670 0.0 0.335 1.2 2071 12 1 1 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 4 0.0 0.000 0.0 0.000 0.2 2186 1 0 0 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 5 234.5 0.629 114.1 0.306 76849.5 2097 745705 626 73307 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 6 280.1 0.700 135.9 0.340 82511.7 2114 800584 719 78054 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 7 201.6 0.705 105.0 0.367 59047.3 2040 572225 552 57880 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 8 76.6 0.693 40.3 0.365 22783.5 2138 221077 221 21317 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 9 301.0 0.689 177.5 0.407 90011.3 2085 873418 720 86331 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 10 293.9 0.662 161.2 0.363 91498.3 2133 887850 744 85789 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 11 319.0 0.679 149.0 0.317 96845.3 2078 939732 720 93208 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2010 12 315.0 0.771 161.7 0.396 84205.8 1971 817088 640 85452 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 1 355.5 0.757 167.4 0.356 96835.0 1972 939632 744 98220 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 2 270.3 0.695 124.7 0.320 80198.3 2016 778202 672 79553 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 3 278.1 0.602 145.8 0.315 95274.0 2134 924489 744 89297 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 4 110.0 0.601 57.0 0.311 37734.8 2148 366158 310 35143 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 5 190.0 0.604 111.9 0.356 64842.4 2139 629196 478 60630 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 6 274.5 0.591 151.3 0.326 95755.5 2195 929155 720 87245 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 7 316.6 0.638 175.2 0.353 102201.5 2192 991710 744 93262 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 8 311.6 0.672 168.4 0.363 95557.7 2149 927244 744 88923 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 9 273.9 0.661 137.1 0.331 85401.3 2147 828686 720 79554 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 10 293.7 0.674 147.0 0.337 89865.7 2088 872011 744 86085 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 11 272.1 0.678 132.7 0.330 82778.1 2062 803234 720 80307 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2011 12 263.4 0.648 120.3 0.296 83856.4 2043 813696 744 82109 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 1 177.2 0.628 88.7 0.314 58171.5 2084 564468 503 55827 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 2 123.0 0.650 59.3 0.313 38982.2 2065 378261 329 37757 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 3 322.2 0.698 140.7 0.305 95136.3 2097 923153 744 90751 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 4 356.2 0.773 181.8 0.395 94972.1 2066 921559 720 91939 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 5 346.2 0.773 160.9 0.359 92287.2 2112 895505 744 87400 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 6 292.4 0.727 129.1 0.321 82897.5 2216 804393 716 74807 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 7 316.9 0.769 138.3 0.335 85744.1 2210 824716 744 77589 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 8 157.0 0.693 75.2 0.332 47101.6 2182 453039 415 43165 DB-WF LNB Baghouse KY Shawnee 8 CSSH60 2012 9 229.1 0.713 101.4 0.316 66783.8 2161 642348 611 61812 DB-WF LNB BaghouseST Plant Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control KY Shawnee 9 CSSH60 2006 1 312.0 0.700 145.8 0.327 91426.7 2187 891099 744 83597 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 2 283.4 0.699 132.8 0.328 83161.3 2123 810537 672 78327 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 3 334.9 0.732 158.5 0.346 93849.1 2108 914709 744 89035 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 4 305.3 0.685 155.4 0.349 91449.5 2080 891317 720 87937 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 5 280.6 0.717 129.8 0.332 80257.2 2048 782234 678 78385 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 6 314.4 0.692 158.1 0.348 93159.5 2033 907986 720 91647 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 7 325.8 0.691 174.5 0.370 96721.6 2095 942703 744 92355 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 8 335.4 0.740 169.7 0.374 92976.2 1968 906202 744 94512 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 9 313.2 0.761 144.7 0.351 84462.2 1902 823217 720 88815 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 10 336.2 0.744 166.3 0.368 92762.9 2004 904121 744 92565 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 11 305.2 0.713 151.7 0.354 87880.5 2084 856533 682 84319 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2006 12 123.0 0.735 58.4 0.349 34316.3 2100 334464 270 32687 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 1 112.8 0.717 49.6 0.315 32288.9 2127 314706 303 30367 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 2 0.3 0.626 0.2 0.317 109.5 1067 6 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 3 337.4 0.713 163.8 0.346 97129.7 2167 946681 693 89660 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 4 359.8 0.750 175.8 0.366 98466.3 2194 959709 683 89776 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 5 350.9 0.684 175.7 0.342 105264.7 2333 1025973 744 90246 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 6 329.9 0.675 171.5 0.351 100325.2 2245 977825 720 89387 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 7 364.0 0.701 194.5 0.375 106540.7 2284 1038412 744 93297 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 8 403.8 0.730 230.2 0.416 113548.5 2328 1106710 744 97535 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 9 345.5 0.653 180.2 0.340 108613.1 2364 1058605 720 91900 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 10 314.7 0.717 151.2 0.345 90040.5 2150 877587 682 83747 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 11 321.1 0.714 168.9 0.376 92239.5 2058 899017 719 89619 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2007 12 330.5 0.710 168.2 0.361 95514.2 2081 930933 744 91778 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 1 340.5 0.753 171.8 0.380 92720.6 1933 903693 744 95947 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 2 317.0 0.778 156.0 0.383 83631.4 1953 815114 696 85630 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 3 354.4 0.783 177.6 0.392 92946.5 1901 905916 744 97769 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 4 324.6 0.760 184.4 0.432 88105.3 1953 854467 720 90243 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 5 338.7 0.760 168.5 0.378 91935.5 1877 890959 744 97951 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 6 289.6 0.718 141.6 0.351 83268.9 1952 807015 720 85327 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 7 296.7 0.677 158.0 0.361 90428.3 2041 876350 744 88606 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 8 283.7 0.711 147.0 0.368 82397.7 1976 798440 744 83405 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 9 280.3 0.683 146.6 0.357 84681.7 2027 820847 720 83565 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 10 316.4 0.729 151.1 0.348 89539.6 1968 867793 744 90989 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 11 352.0 0.789 165.1 0.370 92074.7 1946 892515 720 94614 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2008 12 341.4 0.830 133.7 0.325 84797.0 1944 822078 744 87252 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 1 271.3 0.735 114.6 0.310 76155.2 1975 738357 744 77131 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 2 241.3 0.724 101.7 0.305 68788.3 1918 666659 672 71735 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 3 277.1 0.678 112.1 0.275 84230.2 2062 816923 744 81715 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 4 244.1 0.675 87.4 0.242 74571.0 2003 722704 720 74472 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 5 237.3 0.673 100.2 0.284 72783.9 1991 705276 744 73109 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 6 231.9 0.673 99.8 0.290 71067.0 2042 688856 720 69606 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 7 250.5 0.743 116.7 0.346 69534.0 2101 674532 670 66202 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 8 287.0 0.768 124.1 0.332 77133.7 2051 747863 744 75224 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 9 287.0 0.758 125.1 0.330 78135.5 2087 757514 720 74892 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 10 191.9 0.748 89.2 0.348 52856.0 2055 512853 486 51451 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 11 225.7 0.659 110.7 0.323 70558.7 2123 684664 720 66460 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2009 12 262.4 0.617 135.5 0.319 87761.9 2042 851087 744 85970 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 1 240.5 0.655 118.9 0.324 75809.5 2019 734779 744 75084 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 2 250.9 0.659 130.5 0.343 78499.3 2055 761328 672 76387 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 3 251.6 0.606 148.0 0.356 85585.4 2131 830473 697 80306 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 4 255.9 0.611 133.0 0.318 86291.1 2124 837323 720 81268 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 5 272.6 0.637 131.2 0.307 88179.4 2101 855646 744 83923 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 6 277.8 0.702 134.7 0.340 81538.8 2112 791134 720 77220 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 7 261.9 0.699 142.5 0.380 77318.6 2044 749262 744 75661 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 8 270.8 0.680 151.4 0.380 82065.2 2109 796078 744 77809 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 9 271.9 0.689 159.7 0.405 81293.2 2074 788822 720 78391 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 10 30.6 0.678 15.9 0.351 9306.3 2087 90304 97 8919 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 11 271.9 0.679 126.3 0.315 82545.3 2078 800973 714 79464 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2010 12 301.0 0.763 148.2 0.376 81319.8 1988 789086 697 81800 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 1 326.5 0.755 154.1 0.356 89197.5 1968 865523 733 90636 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 2 257.9 0.695 118.4 0.319 76444.3 2016 741774 672 75843 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 3 248.1 0.602 129.5 0.314 84913.5 2130 823957 739 79714 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 4 264.4 0.601 140.1 0.319 90654.4 2138 879662 720 84821 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 5 266.5 0.599 152.2 0.342 91710.3 2143 889907 744 85595 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 6 239.9 0.591 131.8 0.325 83682.5 2197 812005 710 76184 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 7 283.1 0.639 156.3 0.353 91340.7 2192 886323 744 83345 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 8 281.1 0.671 151.6 0.362 86292.9 2151 837342 744 80243 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 9 236.3 0.660 117.9 0.329 73764.6 2152 715770 720 68568 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 10 173.6 0.672 89.1 0.345 53226.6 2095 516484 476 50805 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 11 246.9 0.676 120.8 0.331 75286.6 2062 730540 720 73029 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2011 12 105.6 0.682 43.2 0.279 31889.2 2025 309437 308 31499 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 1 238.0 0.643 109.0 0.294 76321.2 2081 740583 706 73349 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 2 251.0 0.666 109.1 0.290 77644.2 2055 753410 696 75552 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 3 281.1 0.699 122.6 0.305 82868.7 2095 804115 744 79097 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 4 299.0 0.772 153.6 0.397 79792.6 2064 774264 720 77313 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 5 235.1 0.772 108.0 0.355 62763.1 2118 609019 569 59280 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 6 262.3 0.726 116.2 0.322 74458.1 2213 722501 719 67305 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 7 307.7 0.769 134.3 0.336 83179.6 2208 800049 744 75345 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 8 269.2 0.675 129.0 0.324 82900.4 2174 797362 744 76269 DB-WF LNB Baghouse KY Shawnee 9 CSSH60 2012 9 256.7 0.722 112.8 0.317 73976.7 2159 711531 720 68530 DB-WF LNB Baghouse

0.701ST Plant Unit AS YR MO SO2 (tons) SO2 Rate NOx (tons) NOx Rate CO2 (tons) CO2 Rate HI (MMBtu) OT GLoad (MWh) Unit Type SO2 Control NOx Control PM Control KY Shawnee 10 CSSH60 2006 1 169.6 0.472 0.000 73781.6 2427 719116 555 60796 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 2 188.9 0.387 0.000 100240.2 2409 977011 672 83230 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 3 124.4 0.283 0.000 90123.1 2463 878394 658 73196 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 4 89.8 0.373 85.4 0.354 49435.5 2435 481833 333 40602 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 5 117.4 0.455 87.4 0.338 52985.9 2479 516433 383 42747 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 6 239.3 0.447 185.9 0.348 109736.8 2501 1069557 720 87769 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 7 168.2 0.399 153.3 0.364 86561.1 2566 843689 600 67462 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 8 183.0 0.340 201.0 0.374 110353.6 2495 1075569 744 88464 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 9 106.6 0.212 176.6 0.351 103127.5 2546 1005139 720 81003 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 10 69.8 0.347 71.7 0.356 41344.1 2209 402974 361 37428 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 11 111.4 0.372 104.3 0.348 61457.9 1748 599008 569 70312 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2006 12 112.9 0.281 131.3 0.326 82551.2 1807 804595 744 91360 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 1 149.7 0.396 124.9 0.330 77659.7 1951 756926 714 79619 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 2 80.6 0.390 76.7 0.371 42413.7 2046 413393 361 41458 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 3 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 4 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 5 115.5 0.426 90.6 0.334 55692.1 1403 542812 700 79406 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 6 162.7 0.468 121.0 0.348 71263.9 1553 694589 720 91781 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 7 88.1 0.368 89.7 0.375 49111.8 1464 478668 531 67109 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 8 177.0 0.494 148.6 0.415 73475.7 1462 716135 744 100504 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 9 127.6 0.386 112.4 0.340 67829.4 1452 661105 720 93429 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 10 168.8 0.430 137.5 0.350 80589.8 1830 785469 694 88071 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 11 185.6 0.406 170.5 0.373 93878.9 2039 915001 689 92062 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2007 12 159.1 0.372 154.1 0.360 87835.2 1969 856098 720 89236 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 1 202.7 0.380 202.1 0.379 109324.4 2208 1065613 744 99005 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 2 134.0 0.281 181.2 0.380 97800.9 2242 953249 696 87253 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 3 200.7 0.491 160.6 0.393 83776.7 2383 816523 701 70319 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 4 103.4 0.465 92.5 0.416 45628.4 2290 444717 387 39856 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 5 255.5 0.501 193.2 0.379 104579.7 2357 1019303 744 88743 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 6 203.0 0.454 155.9 0.349 91653.6 2420 893301 720 75732 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 7 269.2 0.541 178.5 0.358 102161.1 2438 995727 744 83814 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 8 265.9 0.515 187.0 0.362 105869.5 2573 1031893 744 82296 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 9 204.9 0.509 138.2 0.343 82572.9 2595 804796 633 63638 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 10 222.5 0.472 163.4 0.347 96637.9 2290 941885 744 84397 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 11 166.8 0.403 153.0 0.369 84985.3 2089 828317 720 81355 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2008 12 52.3 0.158 111.4 0.336 68149.0 2081 664225 626 65497 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 1 132.8 0.509 64.5 0.247 53595.2 2276 522371 512 47103 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 2 128.9 0.355 129.8 0.357 74623.1 2314 727327 672 64507 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 3 33.6 0.251 38.0 0.283 27521.3 2337 268234 223 23550 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 4 132.6 0.389 81.8 0.240 70038.8 2312 682646 574 60585 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 5 168.6 0.372 107.2 0.237 93014.2 2337 906577 744 79586 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 6 115.1 0.309 100.2 0.269 76378.3 2334 744442 636 65443 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 7 39.0 0.434 18.4 0.205 18444.8 2384 179771 237 15472 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 8 86.6 0.317 72.2 0.265 55968.1 2114 545493 502 52950 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 9 82.1 0.356 40.1 0.174 47307.3 2171 461085 472 43572 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 10 0.8 0.073 2.9 0.272 2213.4 2048 21577 21 2161 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 11 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2009 12 88.1 0.387 62.4 0.274 46705.7 2027 455224 476 46087 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 1 82.1 0.218 133.7 0.355 77217.2 1957 752606 744 78908 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 2 19.1 0.118 69.8 0.430 33304.1 1982 324598 375 33598 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 3 1.8 1.783 0.3 0.323 210.1 2048 19 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 4 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 5 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 6 6.8 0.205 14.6 0.438 6859.2 3601 66857 199 3810 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 7 293.9 0.719 69.2 0.169 83916.0 2258 817894 744 74321 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 8 48.4 0.565 23.2 0.271 17578.4 2406 171329 213 14611 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 9 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 10 0.0 0.201 0.0 0.012 34.8 339 18 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 11 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2010 12 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 1 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 2 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 3 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 4 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 5 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 6 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 7 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 8 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 9 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 10 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 11 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2011 12 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 1 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 2 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 3 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 4 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 5 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 6 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 7 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 8 0 CFB Other Other Baghouse KY Shawnee 10 CSSH60 2012 9 0 CFB Other Other Baghouse

0.408