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Improving Air Emission Profiles Using Baghouses and Other Processes EVRAZ INC NA Canada Environmental Affairs Department January 17, 2014 Prepared by: Robert Schutzman Director of Environmental Affairs & Samantha French - Environmental Data Management Specialist

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Page 1: Improving Air Emission Profiles Using Baghouses and Other … · 2014-01-21 · Improving Air Emission Profiles Using Baghouses and Other Processes EVRAZ INC NA Canada Environmental

Improving Air Emission

Profiles Using Baghouses

and Other Processes EVRAZ INC NA Canada Environmental Affairs Department

January 17, 2014

Prepared by:

Robert Schutzman – Director of Environmental Affairs &

Samantha French - Environmental Data Management Specialist

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Outline

1. EVRAZ Regina Steel Making

2. EVRAZ Emission Control Design

3. EVRAZ INC NA Canada Baghouses

4. Baghouse Basics

5. Baghouse Basics – Bag types

6. Baghouse Basics – Cleaning mechanisms

7. Baghouse Design

8. EVRAZ INC NA Canada Baghouses – Pollution Detection Equipment

9. Scheduling of Baghouse Compartment Change-outs

10.Cold Weather Operations and Issues

11.EAF Dust removal

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EVRAZ Regina Steel Making

Steel recycling using scrap steel, about 1Mt/a

Electric Arc Furnaces (EAF) with natural gas burners

Scrap steel placed into EAFs with clam-shell buckets

Lime (= “EAF Steel Slag”) added to top of molten steel to insulate and occlude air

Processing with fine carbon and oxygen

Tapping into ladles for further processing in Ladle Metallurgy Furnace (LMF), before

casting

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EVRAZ Emission Control Design

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SB

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EVRAZ Emission Control Design cont’d

Emissions from EAF melting are exhausted in a water cooled (WC) system after the ‘fourth hole’

elbow, into a drop box for post-combustion and where the larger pieces of debris are deposited.

The exhaust travels thence to a Spark Box (SB), where heavier dust and materials settle, and

then is routed to the Mikropul baghouse.

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EVRAZ Emission Control Design cont’d

When emptying the furnace, eccentric bottom tapping is used, and the liquid steel

flows to a ladle through a tap hole in the base of the furnace.

Exhaust during furnace tapping is pulled through a side draft (items L and F on

diagram) which is then routed through the water cooled exhaust piping.

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EVRAZ Emission Control Design cont’d

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Emissions from the two Electric Arc Furnaces (EAF)

into the building occur, as a charge plume to the

canopy when the furnace lid is lifted and new scrap

charges are added, or during slag pour-off.

Fume flowing into the canopy is exhausted to the

Procedair and the AAF baghouses.

Canopy hood velocity design is greater than 60

cm/s.

The LMF exhaust is drawn into a plenum (item E on

the diagram) and then into the canopy. If there are

any issues with the Mikropul baghouse, exhaust

duct flow can be rerouted and the air emissions can

be exhausted into the Procedair and the AAF

baghouses.

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EVRAZ Emission Control Design cont’d

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Meltshop Canopy Ducting

Photograph of exhaust system and spark box

Photograph of the exhaust ductwork to the baghouses

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EVRAZ Regina Baghouses

Evacuation design rate is about 1.5 acfm per Ton/year of Steel produced; (usual practice has

been 1.0).

“Net*Net” design; i.e. without two compartments per baghouse

EVRAZ has three (3) baghouses in operation, named based upon Manufacturer

Two Positive Pressure

Mikropul -- about 1 M acfm

− 12 compartments, 336 bags/compartment (4,032 bags)

− Three fans, two in operation continuously

− Maximum A/C ratio is 3:1

− most recent addition

AAF – about 0.3 M acfm

− 10 compartments, 128 bags/compartment (1,280 bags)

− Three fans, two in operation continuously

One Negative Pressure

Procedair – about 0.2 M acfm

− 10 compartments, 180 bags/compartment (1,800 bags)

− One fan in operation continuously

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Photograph of EVRAZ Baghouses: Mikropul, AAF and

Procedair (left to right)

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Baghouse Basics - Bag Types

Can be made out of woven or non-woven materials. Some of the common types and their

characteristics are listed below.

Polyester

Synthetic fibre

Acid, alkaline and abrasion resistant

Inexpensive

Fibreglass

Synthetic fibre

High temperature application use

More chemically resistant

Gore ™

Expanded polytetrafluoroethylene (PTFE) membrane

Laminated with various fibres to create

Wear resistance, longer life

Lower friction, higher flow

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EVRAZ INC NA Canada Baghouses cont’d

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Mikropul Baghouse

AAF Baghouse

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EVRAZ INC NA Canada Baghouses cont’d

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Procedair Baghouse

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Baghouse Basics

Fabric filtration is a common technique for emission control and is otherwise called a

baghouse

Filters with their supports are referred to as bags

Bags hang vertically in fabric filter shell

Dust is collected either inside or outside of the bag

During compartment cleaning and upon removal dust particles fall into the hopper and are removed

Bag material must be matched to the cleaning methodology

Baghouses are classified based upon the cleaning mechanism

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Photograph of bag tubes in the EVRAZ Mikropul Baghouse

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Baghouse Basics – Cleaning Mechanisms

Intermittent cleaning Commonly used for compartmentalized baghouses

Can also be used for single compartment baghouses

One compartment removed from service at a time and cleaned

Rotational between compartments

Continuous cleaning Fully automatic, row of bags always being cleaned in baghouse

Does not require taking the baghouse or compartment out of service for

cleaning

Compartmentalized baghouses Used for continual operating facilities with large exhaust volumes

Can have one compartment offline for cleaning and another offline for

maintenance, with the remainder in operation

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Baghouse Cleaning Mechanisms cont’d

Shaking Interior filtration (dust collection inside of the bags)

Manual or mechanical shaking of a shaft that moves a rod connected to the bags resulting in dust falling

into the hopper

− Generally horizontal shaking

Higher cleaning & filtering stress on bag

Older technology

Reverse Air Commonly used for compartmentalized baghouses

− Enables compartment to be offline

Air / gas flow stopped and compartment backwashed with low pressure air

Dust collection inside of the bags

− Sealed at top and open at bottom

− Bag has rings (~1 m apart) to prevent complete collapse during cleaning

During cleaning the bags are allowed to collapse

− dust breaks and falls into hopper

Usually used on woven fabrics

Less cleaning & filtering stress on bag

Either cycled or initiated by pressure drop switch

Use inlet and outlet dampers for filtering and bag cleaning sequences

− In operation both dampers are open

− During cleaning the outlet damper is closed blocking the flow of air / gas through compartment and reverse air damper

is opened to allow fresh air for cleaning

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Baghouse Cleaning Mechanisms cont’d

Pulse jet cleaning

High pressure jet of air into the top of the bag tube removing the dust from the exterior of the bag

Bags supported by rings or metal cages held at top with clamps and closed bottom

Used for cleaning bags with exterior filtration system

Dirty air / gas flow is not stopped

Cleaning done row by row

Can also be used in compartmentalized baghouses and compartment taken offline via poppet valve

closure

Higher cleaning & filtering stress on bag

Important to space bags to reduce bag abrasion

Less commonly used

Sonic

Sound generator produces low frequency noise causing vibration

Typically used in addition to other cleaning techniques

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Baghouse Design

Positive pressure baghouse

Fan is upstream or before the filter

Pushes air / gas through the filter

more prone to pressure leaks and fan wear

Commonly used for dusts easily ignited due to air infiltration-related fires

Negative pressure baghouse

Fan is downstream or after the filter

Air / gas is pulled through the filter

Requires more structural reinforcement due to suction on baghouse shell

Fans are integral part of baghouse thus maintenance is crucial

More wear on positive pressure baghouse fans than negative pressure baghouses

Can shutdown entire baghouse, thus best to have on-line spare

Fans are expensive

Air to Cloth (A/C) Ratio

Dependant on material, particle size distribution of collected material, particulate matter

characteristics, humidity and bag spacing

As ratio increases so does seepage through filter medium, baghouse gas inlets and bags and also

increases bag breakage

Increases as gas volumetric flow rates increase and could decrease bag life

Lower A/C based on Net*Net design is key for proper performance and operation

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Baghouse Design cont’d

Gas temperature

Important because of bag operation design range

Operation of a baghouse below dew point temperatures of the gas stream can result in moisture or acid

condensation

− Condensation is a main bag failure cause

Consider also in-leakage into gas stream

Often tied to alarm to notify of trouble

Pressure drop

Based upon gas volumetric flow rate

Fluctuates with cyclic cleaning process

Increases as dust accumulates on / in bags

Decreases after compartment cleaning

Indicates gas flow resistance and effectiveness of the cleaning system

Can indicate maintenance required

Hoppers

Store collected dust before removal and disposal

Dust removal should be frequent to reduce packing of the dust

− Double dump discharge device

− Rotary Air lock valve – shaft mounted paddle wheel driven by a motor

− Screw conveyor (auger)

− Drag conveyor

− Paddle conveyor

Access door or port to enable dust removal

Vibrators and plates

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Emission Control Design cont’d

Particulate Matter (PM), Carbon Monoxide (CO) and other emissions are collected by

building roof ducts which are connected to the baghouse(s).

Large volumes of exhaust are created in the charge plume and must be held in the canopy hood

until evacuated from the building.

Tapping emissions are collected by the push-pull side collection hood at the furnace/ladle during

tapping.

PM is removed from melt cycle using the fourth hole.

CO is either burned in furnace when sufficient oxygen is present or exhausted through the direct

evacuated system (DES) where it is post-combusted at the drop box.

Downstream ductwork can explode if excessive CO

Potential Fugitive Emissions at Baghouses

Door seals

Corroded points

Warped access hatches

Tube sheet cracking

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EVRAZ Regina Baghouses – Cleaning System

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Reverse air is used

Baghouse compartment cleaning cycles

are controlled timing cycles, and/or by

pressure drop

Manual pressure gauges and electronic

controllers are used

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EVRAZ Regina Baghouses – Performance Monitoring System

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Each baghouse has broken bag detection

sensors

Sensors installed at the clean air outlet of

each compartment

When higher than normal amounts of

particles collide with the sensor a frictional

electrification will take place

Reads in picoamps (pA)

Provides signal when higher amounts of dust

are discharged (except cleaning spikes)

High amperage is indicative of broken bag(s)

Data displayed on Programmable Logic

Controller (PLC) screens

Data saved on cards and files transferred to

software

Software called “Tribo” enables real time and

historical view of activity including particulate

spikes graphics and alarm history

summarization

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EVRAZ Regina Baghouses – Radiation Detection

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Radiation detection used in the baghouses

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Scheduling of Baghouse Compartment Change-outs

Wear and tear occurs on bags during operations

Bags Break

Individual bags in each compartment will require periodic change-out

Proper tracking of individual bag and compartment change-outs is crucial to effectively

manage bag integrity and emission control

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Photograph of broken bag

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Scheduling of Baghouse Compartment Change-outs cont’d

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Management of Change-outs

Key is to manage and monitor change-outs

− Individual bag change-outs, and

− Compartment change-outs

Multiple baghouses and compartment

change-out management

− Use tracking spreadsheets

− One compartment per worksheet

− Set up grid-like pattern to identify bag location in

compartment

− Complex calculations are used to summarize

average compartment bag age and highlight

when nearing life expectancy

Scheduling Compartment Bag Change-

outs

Enables the facility to maintain reasonable

performance over the life of the bags

− Can use various tracking spreadsheets and

updating external linkages

− Schedule based upon oldest average bags

− Improves budgeting and evens out costs of

compartment change-out over time

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Cold Weather Operations and Issues Condensation

Water is generated by combustion in the EAFs, and WC duct leaks; outer wall insulation is needed.

Ice build up can cause exterior wall and roof corrosion of the baghouse shell

− Internal hot air contacts cold sheeting

− Hot air condenses on walls and collects on compartment floor

− If water from floor contacts tube bag, then bag deterioration occurs

Can cause reaction with EAF dust in the bag causing a cement layer to form in the bag

Hopper problem reduction

Insulation, Heaters

Air tight seals

Frequent dust removal (pneumatic through augers)

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Exterior wall corrosion Roof corrosion

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EAF Dust Removal

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Dust is removed from the baghouse

hoppers, melt-shop floor and spark box

EVRAZ contracts truck operators to

remove EAF Dust, slurry with water

Dust and water slurry produces an

exothermic reaction with the lime, thus

expansion room is required in the truck

Classified as a Hazardous material

EVRAZ has an engineered, licensed

EAF Dust Storage Facility for dust

disposal

Aged and failed bags are also disposed

at the Facility

Disposal quantities are tracked on a

monthly basis

0.00 2,000.00 4,000.00 6,000.00 8,000.00

10,000.00 12,000.00 14,000.00 16,000.00 18,000.00 20,000.00

2002 2004 2006 2008 2010 2012 2014

EA

F D

ust

(to

nn

es)

Year

EAF Dust Stored - Landfilled

0

0.005

0.01

0.015

0.02

0.025

2002 2004 2006 2008 2010 2012 2014

EA

F D

ust/

Liq

uid

Ste

el

(to

nn

es)

Year

EAF Dust Produced per tonne Liquid Steel Melted

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References

Air and Waste Management Association. Air Pollution Engineering Manual. 2nd Ed. New York: John Wiley &

Sons, Inc., 2000.

Industrial Ventilation – A Manual of Recommended Practice for Design. 27th Ed. Cincinnati, Ohio: ACGIH, 2010

Jones, Jeremy A. T., Nupro Corporation. Electric Arc Furnace Steel Making. Retrieved January 7, 2014 from :

http://www.steel.org/en/Making%20Steel/How%20Its%20Made/Processes/Processes%20Info/Electric%20Arc%

20Furnace%20Steelmaking.aspx

McKenna, John D., James H. Turner. Fabric Filter – Baghouses I – Theory, Design, and Selection. Salem, VA:

Valley Printers, 1989.

United States Environmental Protection Agency (EPA) Air Pollution Training Institute (APTI). Fabric Filter

Operation Review APTI Course SI: 412A 2nd Ed.

United States Environmental Protection Agency (EPA) Air Pollution Training Institute (APTI). APTI SI:445

Introduction to Baseline Source Inspection Techniques.

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Questions

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