Document evEMG3G3w4BJNBQJZqLxN4j69
PLAINTIFFS EXHIBIT
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TASK FORGE REPORT PROJECT 7185
#2 OPEN HEARTH FUME ABATEMENT MIDDLETOWN WORKS
May 15, 1968
Task Force Members J. Rosenberger, Chairman J. E. Barker G. R. Curtis J. J. Delaney M. Sample C. F. Staley T. L. Taubken C, R. Taylor, Consultant
Prepared by: T. L. Taubken
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TABLE OF CONTENTS
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SECTION I - INTRODUCTION . . . .
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SECTION II - GENERAL DESCRIPTION .
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SECTION III - MAJOR EQUIPMENT LIST
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SECTION IV
- SPECIFICATIONS AND CAPACITIES .............................. 10 1. Waste Gas 2. Clean Gas
3. Services
SECTION V
- APPROXIMATE COSTS ....................................................... 13 1. Capital Expenditure 2. Operating Costs
SECTION ViC - ALTERNATIVES INVESTIGATED .................
SECTION VII - COST COMPARISONS .................................. ................. 1%
SECTION VIII - DRAWINGS ...................................................
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SECTION I
INTRODUCTION
The Task Force herein submits its report, summarizing its recommen dations for gas cleaning facilities for the three natural draft furnaces at the Middletown Works No, 2 Open Hearth Shop, A more complete descrip tion of the scope of the work and equipment details will be recorded with a complete cost estimate in the forthcoming Engineering Report,
These recommendations have been agreed upon by the Task Force members after review of visits to all types of treatment facilities, test data and a previous Kaiser Engineers study, consultation with appropriate Armco personnel and discussions with equipment suppliers. The criteria have been established with considerations for compliance with state and local air pollution control requirements, economy of treatment, and compati bility with furnace operation.
The basis for the design of a gas cleaning system was established in 1965 through an extensive testing program by Armco and Kaiser Engineers personnel. Measurements were made of dust concentrations, temperatures, volumes, and composition of gases. The investigations were published in Report No, 65-21-RE titled "Study of Proposed Gas Cleaning Systems No. 2 Open Hearth Shop" dated June 1965.
The objective of this Task Force was to examine all possibilities in order to develop a gas cleaning scheme that would meet cleaning require ments at the lowest possible investment without adversely affecting the open hearth operations. Of the many possible gas cleaning schemes, investigated, the following three were selected for detailed study:
1. Individual high energy scrubber systems.
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2 Centralized precipitator system preceeded by a centralized air-to-air heat exchanger system.
3. Centralized precipitator system preceeded by individual air-to-air heat exchangers at each furnace.
After reviewing all available information, the Task Force recommends the individual high energy scrubber systems because they require the lowest capital expenditure and offer the greatest reliability. A com parison of the approximate capital cost for the three alternate schemes is summarized in Section VII. The target date for completion of this project is late 1969 or early 1970.
To meet our commitments to the citizens of Middletown will require early approval of this report and the subsequent program and appropria tion request.
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SECTION II
GENERAL DESCRIPTION
The gas cleaning system for 'each furnace consists of a high energy wet scrubber, mist eliminator, slurry system, fan, cold stack, connecting duct work, instrumentation and services. The object of the gas cleaning system is to provide the proper draft at the base of the hot stack and discharge clean gas to the atmosphere without decreasing the production of the furnace.
The system is tapped into the existing natural draft stacks at a point approximately 75 feet above grade. Two water cooled butterfly dampers will be provided to by-pass the dirty gas to the atmosphere in case of equipment fail-are. The hot ductwork connecting the natural draft stack and the Venturi scrubber will be designed so that expansion forces will not be transmitted to the stack.
The dirty gas flows from the hot ductwork down through the vertical scrubber. A high energy wet scrubber operates on the principle of impac tion, the collision of small dirt and water particles at high velocities causes an agglomeration of particles which can be -removed from the gas stream in a separator. The efficiency of the gas cleaning system is primarily a function of the pressure drop across the scrubber.
The vertical separator section, downstream of the scrubber, removes the agglomerated dirt and water particles from the gas stream. The clean gas is exhausted from the top of the separator and the slurry is drained from the bottom.
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The induced draft fan, which maintains a maximum pressure-differential
across the system of 56" W.G., exhausts the clean gas through the 150 foot
cold stack* The fan noise level will be dampened by enclosing the fans
and equipping the system with sound attenuators. The fan and motor, if
practical, will be designed so that it may be used in the B.O.F. gas
cleaning system in an emergency.
A graphic control panel, located in the central control room, will be
provided for constant monitoring and complete control of all the gas
cleaning equipment. The control system maintains a preset draft at the
base of the stack automatically. The system will be protected by a series
of interlocks which will reverse the dampers and by-pass the dirty gas
out the existing stack in the case of major equipment failures. Minor
equipment failures will be annunciated on the main control panel. Instru
mentation will be- transmitted and controlled electronically wherever
practical.
The slurzy will flow by gravity from the separator to a classifier
to remove large particles. From the classifier, an 1800 gpm pump will
recirculate 600 gpm to wet the scrubber approach and pump the remaining
1200 gpm into a gravity header to the water treatment plant (Project
7183). The supply and return headers will be sized to accommodate three
future scrubbers. The large particles will be discharged into dumpster
boxes and trucked to the dump.
A continuous 100 gpm supply of cooling water will be pumped from the
return header of the existing cooling water circuit to the water cooled
dampers and fan bearings and returned to the same return header.
The source of the electric power will be from the existing Substa
tion No. 17. The distribution voltage from this substation will, be
13,200 volts.
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This substation consists of two 20,000 KVA transformer banks, No. 7
and No. 8, with a primary voltage of 132,000 volts and the secondary voltage
is 13,200 volts. One bank of transformers. No. 7, (3 single phase trans
former in a closed delta) is now feeding an existing load. The second
bank. No. 8 is energized but has no appreciable load connected. No. 8
bank of transformers will require a zigzag transformer on the secondary
to match the existing No. 7 bank.
This project will add one cubicle complete with all relaying and
metering to this existing 15 KV switchgear. These two transformer banks
may now be paralleled through an existing 15 KV walk-in type switch-
gear.
A wood pole line with three wires will feed 13,200 volts to a new
substation. No. 605, at the northeast corner of the No. 2 Open Hearth
shop. The wood pole transmission line will follow Lefferson Road, north
to the McGraw Construction Co. field office area, from whence the line will
follow the newly paved patrol road and then south to the new Substation
No. 605.
The purpose of this station is to receive and distribute the 13,200
volts to transformers to obtain 2400 volts for the three 2000 HP motors
and 460 volts for the auxiliary equipment required.
The station will consist of a steelox building 40* x 60* and will
house all indoor type equipment instead of using outdoor weather proof
type equipment. The transformers used indoors will contain a non-flammable
type coolant.
The 2400 volt leads to the three 2000 HP motors and the 460 volt
feeders to the three motor control centers will be installed (in gal
vanized steel conduits) on steel supports on the roof of the No. 2 Open
Hearth lean-to.
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Galvanized steel conduit runs will be made from the leanutp roof to the individual 2000 HP motors and to the individual motor control centers.
Galvanized steel conduits will leave from the motor control centers to each individual auxiliary motor and for motor controls.
Galvanized steel conduits will be used for all control and instrumen tation runs from the respective equipment to the control and instrumen tation room.
The equipment steel platforms will be used as much as possible to support these many runs of steel conduits.
Since it is anticipated that Ho. 2 Open Hearth furnaces No. 9-10-11 will be equipped for fume abatement in the future, the following provisions will be built-in at this time:
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a. The incoming 13 KV power feeder is designed to carry the fume abate ment capacity of all six furnaces operating at the same time.
b. The conduit roof bracket supports on the roof of the lean-to are designed to carry the future two 13 KV feeders for fume abatement of furnaces No. 9-10-11.
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SECTION III MAJOR EQUIPMENT LIST
Three (3) High energy wet scrubber systems of suitable corrosion and
errosion resistant materials.
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Three (3) Water cooled (butterfly
the existing 7'-6" I.D.
lav" Three (3) Water cooled (butterfly m H:;. the new hot duct to the fe jwy Three (3) Hot duct sections from t
scrubber. The ducts, which include expansion joints and/or
a water seal, will be constructed of mild carbon steel lined
with a suitable refractory.
Three (3) Cold duct sections from the separator to the induced draft fan. The ducts will be constructed of mild carbon steel with a suitable corrosive and abrasive resistant lining.
Six (6) Vibration isolators at the inlet and outlet of each fan.
Three (3) Induced draft fans designed for approximately 150,000 ACFM saturated of clean gas at a temperature of 165 F. and a pres
sure differential of 56" W.G. The fan will be constructed of
suitable corrosive and abrasive resistant material. The fan will be equipped with water sprays to keep the fan wheel clean.
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Three (3) Fan drivers will be approximately 2000 HP, 2400 volts, 1200 rpm, NEMA class B design, 1*15 service factor, with Class B insula tion, NEMA type II outdoor enclosures and same rotation as B.O.F, fan motors. Split sleeve oil ring bearings, corrosion resistant finish and hardware. Motors will be equipped with 460 volt space heaters, winding temperature detectors, bearing resistance thermometers, oversized terminal boxes, and lightning and surge arrestors mounted in boxes.
Three (3) Cold stacks, complete with ladder cage and platforms approxi mately 150* high, constructed of mild carbon steel with a suitable liner.
Three (3) Classifiers to be installed directly below the separators. The classifier tank will be constructed of carbon steel with a suitable lining and the mechanism will be of either 316 stain less steel or carbon steel with an abrasion and corrosion resistant coating.
Six (6)
Sludge pumps rated at 1800 gpm and constructed of an abrasive and corrosive resistant alloy.
One (1) Graphic control panel to be located in the central control room.
Two (2) Cooling water supply pumps and pump tank rated @ 300 gpm.
One (1) 2400 volt unit substation - 5000/6250 KVA.
One (1) 460 volt unit substation - 1000/FUT 1250 KVA.
One (1) 138 KV switchgear.
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One (l) 125 volt D.C. battery and battery charger.
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Three (3) Motor control centers - 600 volt, 600 amps.
Additions to Substation No. 17. a. 3 - I67 KVA transformers b. 1 - 15 KV walk-in type cubicle, with breaker, relaying, and metering.
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SECTION IV SPECIFICATION AND CAPACITIES
1. Waste Gas
The gas cleaning system design is based on the furnace using
a maximum oxygen lancing rate of 100,000 CFH, or a maximum firing
rate of 13? million BTU/Hr with combustion air plus 3? million
BTU/Hr with oxygen.
The following characteristics of the waste gas at the base of
the existing stack are considered normal expected maximums:
Gas Volume
- 62,000 standard cubic feet per minute wet (ll$ moisture)
Gas Temperature
- 13?0 F. (Average) 1900 F. (three minute peak)
Static Pressure - (-) 3.0" W.G. (Constant)
Dust Concentration - 6 grains per standard cubic foot dry (during oxygen lancing)
2. Clean Gas
In order to achieve the required cleaning efficiency at the
normal maximum waste gas discharge conditions outlined below, a total pressure differential of ?6" W.G. across the system will be provided.
Gas Volume Gas Temperature
- 9it, 000 standard cubic feet per minute saturated
- 180 F.
Static Pressure - (+) 2.0" W.G.
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Dust Concentration - .0$ grains per standard cubic footdry (instantaneous loading)
- .03 grains per standard cubic foot dry (average over oxygen lancing period)
3. Services The various services required to operate the gas cleaning
facilities are as follows: Damper Cooling Water - A continuous 300 gpm supply of cooling water from the return header in the open hearth cooling tower circuit.
Scrubber Water - A continuous 3^00 gpm supply of clarified water with a maximum of 1000 ppm suspended solids (to be provided under Project 7183).
Air - Less than $0 cfm dry where pneumatic controls are required.
Electrical - Power requirements include the following: A new 13,200 volt electric power feeder will originate from
the existing No. 17 Substation. This project will provide trans former bank No, 8 with a new zigzag transformer to match the existing No. 7 transformer bank. This project will also provide a new 1$ KV cubicle and breaker to add to the existing outdoor switchgear.
A new 13,200 volt wood pole line will furnish power to the new No. 60f> Substation at the northeast corner of No. 2 Open Hearth shop.
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Substation No. 60$ will feed 2iiOO volts to the three 2000 HP motors and also feed three phase k60 volt, 60 cycle to the motor control centers for all auxiliary motors, for each of the three open hearth furnaces.
The total power requirements for each open hearth furnace is approximately 2000 KVA.
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SECTION V
APPROXIMATE COSTS
The following budget estimates, based on available information, are as follows* A more complete cost estimate will be reported in the forthcoming Engineering Report. These costs do not include the water treatment which will be covered under Project 7183.
1. Capital Cost The following' total includes all direct, indirect, eecalftti'CB', contingency and start up costs: Total Expenditure - $L,500,000
2. Operating Cost The following total includes yearly costs for labor, maintenance and power: Total Operating Cost - $380,000
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SECTION VI
ALTERNATIVES INVESTIGATED
The following alternatives were investigated by the Task Force, but were not recommended for the #2 open hearth gas cleaning system.
Precipitators proceeded by waste heat boilers, which require the largest capital expenditure of any scheme investigated, cannot be economically Justified by the value of the steam produced.
Precipitators proceeded by air-to-air heat exchangers, which have questionable reliability, require a larger capital expenditure than a scrubber system.
A scrubber system with gas cooling has several distinct advantages such as a smaller steam plume, lower power requirements and improved fan performance; but these advantages cannot justify the larger capital expenditure required.
Cap dampers should not be installed on the top of the 20 ft. high natural draft stacks because the caps are difficult to maintain and add additional stresses to the stack.
The dual radial concept for electrical power distribution cannot be justified for the gas cleaning system because emergency electrical repairs can be made without a shut down of the open hearth furnaces. Only the gas cleaning system will be shut down for emergency electrical repairs.
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SECTION VII
COST COMPARISONS
m The following costs represent the approximate capital expendi
tures required for the alternate schemes that were investigated. The
Task Force feels that these estimates are sufficiently accurate for
comparisons:
1. Individual high energy scrubber systems without gas cooling. j-.
V.- Approximate Capital Expenditure - $lj, 500,000
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2. Individual high energy scrubber systems with gas cooling.
b;:Si Approximate Capital Expenditure - $5,500,000
3. Precipitators proceeded by individual air-to-air heat
exchangers.
Approximate Capital Expenditure - $5,900,000
lj. Precipitators proceeded by centralized air-to-air heat
exchangers.
Approximate Capital Expenditure - $7,000,000
In order to compare the various alternatives, it should be
noted that the scrubber systems will require approximately a
$1,200,000 expenditure for water treatment facilities. (Project
7183) The cost to expand the water treatment facilities for three
future scrubbers would be approximately $350,000.
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SECTION VIII DRAWINGS
PR-3297-198? - Proposed Gas Cleaning System - Plan PR-3297-1988 - Proposed Gas Cleaning System - Section PR-3297-1990 - Flow Diagram of Fume Control System PR-3297-1998 - 13.8 KV Switchgear & Electrical Control House - Layout PR-3297-2000 - Power Line Location to Electric Control Room
A complete set of scoping drawings, including the alternates, is available upon request.
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>, Rosenberger - TaskCPorce Chairman
'.! E. Barker
G. R. Curtis
vV JJ elaney
M. Sample
C. F. Staley
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C. R,, Taylor - Consultarn.
Distribution of Task Force Report:
Task Force Members
C. L. LUoyd
F. "W, Barnes
H. B. Nicholson
H. Berry
D. C. Osborne
r T. R. Foley H. Holiday
R. J. Thompson J. G. Townsley
iv.
C. G. Kramer
Central File
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N. T. Kurfiss
File ?18?
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