Most
electrostatic precipitators are operated dry and use rappers to remove the collected
particulate matter. The term dry is used because particles are charged
and collected in a dry state and are removed by rapping as opposed to water
washing which is used with wet ESPs. The major portion of this course covers
dry ESPs that are used for collecting dust from many industries including steel
furnaces, cement kilns and fossil-fuel-fired boilers
Bag Filter
Bag Filter- It is used only low teperature application. The cleaned gas will goes through chimney to out and the dust will collect at the hopper
Cyclone
Cyclone- It is used for another types of dust cleaning from gas.
ESP
ESP- Electrostatic Precipitator
ESP
ESP-Electrostatic precipitator. it is most commonly used Dust cleaning machine from Gas. It is Used High temperature application .
Wet Scrubber
Wet Scrubbber- It is used in chemical factories to remove hazardes chemicals from the gas.
Showing posts with label ESP-Types. Show all posts
Showing posts with label ESP-Types. Show all posts
Thursday, June 26, 2014
Wet ESPs
Any of the
previously described ESPs can be operated with a wet spray to remove collected particles.
Wet ESPs are used for industrial applications where the potential for explosion
is high (such as collecting dust from a closed-hood Basic Oxygen Furnace in the
steel industry), or when dust is very sticky, corrosive, or has very high
resistivity.
The water flow
may be applied continuously or intermittently to wash the collected particles
from the collection electrodes into a sump (a basin used to collect liquid). The
advantage of using a wet ESP is that it does not have problems with rapping reentrainment
or with back corona. Figures 1 and 2 show two different wet ESPs. The casing of
wet ESPs is made of steel or fiberglass and the discharge electrodes are made
of carbon steel or special alloys, depending on the corrosiveness of the flue
gas stream. In a circular-plate wet ESP, shown in Figure 1-15, the circular
collection plates are sprayed with liquid continuously. The liquid provides the
electrical ground for attracting the particles and for removing them from the
plates. These units can handle gas flow rates of 30,000 to 100,000 cfm.
Preconditioning sprays located at the inlet remove some particulate matter
prior to the charging stage. The operating pressure drop across these units is
typically 1 to 3 inches of water.
Rectangular
flat-plate wet ESPs, shown in Figure 2, operate similarly to circular plate wet
ESPs. Water sprays precondition the gas stream and provide some particle removal.
Because the water sprays are located over the top of the electrical fields, the
collection plates are continuously irrigated. The collected particulate matter
flows downward into a trough that is sloped to a drain
figure 1
Figure 2
Hot Side
Hot-side ESPs
(Figure 1-14) are placed in locations where the flue gas temperature is relatively
high. Their collection electrodes can be either tubular or plate. Hot-side ESPs
are used in high-temperature applications, such as in the collection of cement kiln
dust or utility and industrial boiler fly ash. A hot-side precipitator is
located before the combustion air preheater in a boiler. The flue gas
temperature for hot-side precipitators is in the range of 320 to 420°C (608 to
790°F).
The use of
hot-side precipitators helps reduce corrosion and hopper plugging. However, these
units (mainly used on coal-fired boilers) have some disadvantages.
Because the
temperature of the flue gas is higher, the gas volume treated in the ESP is larger.
Consequently, the overall size of the precipitator is larger making it more costly.
Other major disadvantages include structural and mechanical problems that occur
in the precipitator shell and support structure as a result of differences in
thermal expansion.
For years,
cold-side ESPs were used successfully on boilers burning high-sulfur coal. However,
during the 1970s when utilities switched to burning low-sulfur coal, cold side ESPs
was no longer effective at collecting the fly ash. Fly ash produced from low
sulfur coal-fired boilers has high resistivity (discussed in more detail later
in the course), making it difficult to collect. As you will learn later, high
temperatures can lower resistivity. Consequently, hot-side ESPs became very
popular during the 1970s for removing ash from coal-fired boilers burning low
sulfur coal. However, many of these units did not operate reliably, and
therefore, since the 1980s; operators have generally decided to use cold-side
ESPs along with conditioning agents when burning low sulfur coal.
Hot-side ESPs
are also used in industrial applications such as cement kilns and steel refining
furnaces. In these cases, combustion air pre-heaters are generally not used and
hot side just refers to the high flue gas temperature prior to entering the
ESP.
Cold Side
Cold-side ESPs
(Figure 1-13) have been used for over 50 years with industrial and utility
boilers, where the flue gas temperature is relatively low (less than 204°C or 400°F).
Cold-side ESPs generally use plates to collect charged particles. Because these
ESPs are operated at lower temperatures than hot-side ESPs, the volume of flue gas
that is handled is less. Therefore, the overall size of the unit is smaller,
making it less costly. Cold-side ESPs can be used to remove fly ash from
boilers that burn high sulfur coal. As explained in later lessons, cold-side
ESPs can effectively remove fly ash from boilers burning low-sulfur coal with
the addition of conditioning agents.
Cold-side and Hot-side ESPs
Electrostatic
precipitators are also grouped according to the temperature of the flue gas that
enters the ESP: cold-side ESPs
are used for flue gas having temperatures of approximately 204°C (400°F) or
less; hot-side ESPs are used for
flue gas having temperatures greater than 300°C (572°F). In describing ESPs
installed on industrial and utility boilers, or municipal waste combustors using
heat recovery equipment, cold side and
hot side also refer to the
placement of the ESP in relation to the combustion air preheater. A cold-side
ESP is located behind the air preheater,
whereas a hot-side ESP is located in
front of the air preheater. The air preheater is a tube section that
preheats the combustion air used for burning fuel in a boiler. When hot flue
gas from an industrial process passes through an air preheater, a heat exchange
process occurs whereby heat from the flue gas is transferred to the combustion air
stream. The flue gas is therefore "cooled" as it passes through the
combustion air preheater. The warmed combustion air is sent to burners, where
it is used to burn gas, oil, coal, or other fuel including garbage. APTI Course
SI:428A Introduction to Boiler
Operation describes boilers and heat recovery equipment in greater
detail.
Two Stage
The two-stage
precipitator differs from the single-stage precipitator in both design and amount
of voltage applied. The two-stage ESP has separate particle charging and
collection stages (Figure). The ionizing stage consists of a series of small, positively charged wires equally
spaced 2.5 to 5.1 cm (1 to 2 in.) from parallel grounded tubes or rods. A
corona discharge between each wire and a corresponding tube charges the
particles suspended in the air flow as they pass through the ionizer. The
direct-current potential applied to the wires is approximately 12 to 13 kV.
The second stage
consists of parallel metal plates less than 2.5 cm (1 in.) apart. The particles
receive a positive charge in the ionizer stage and are collected at the
negative plates in the second stage. Collected smoke or liquids drain by
gravity to a pan located below the plates, or are sprayed with water mists or
solvents that remove the particles and cause them to fall into the bottom pan. Two-stage
precipitators were originally designed for air purification in conjunction with
air conditioning systems. (They are also referred to as electronic air
filters). Two stage
ESPs are used
primarily for the control of finely divided liquid particles. Controlling solid
or sticky materials is usually difficult, and the collector becomes ineffective
for dust loadings greater than 7.35 x 10-3g/m3 (0.4 gr/dscf). Therefore,
two-stage precipitators have limited use for particulate-emission control. They
are used almost exclusively to collect liquid aerosols discharged from sources
such as meat smokehouses, pipe-coating machines, asphalt paper saturators, high
speed grinding machines, welding machines, and metal-coating operations.
Representation of gas flow in a two-stage precipitator
Single Stage
A single-stage precipitator uses high voltage
to charge the particles, which are then collected within the same chamber on
collection surfaces of opposite charge. Most ESPs that reduce particulate
emissions from boilers and other industrial processes are single-stage ESPs
(these units will be emphasized in this course). Single stage
ESPs use very high voltage (50 to 70 kV) to
charge particles. After being charged, particles move in a direction
perpendicular to the gas flow through the ESP, and migrate to an oppositely
charged collection surface, usually a plate or tube. Particle charging and
collection occurs in the same stage, or field; thus, the precipitators are
called single-stage ESPs. The term field
is used interchangeably with the term stage and is described in more detail later in this course.
Figure 1 shows a single stage tubular precipitator. A single-stage plate precipitator
is shown in Figure 2Figure 1
Figure 2
Plate
Plate electrostatic
precipitators primarily collect dry particles and are used more often than
tubular precipitators. Plate ESPs can have wire, rigid-frame, or occasionally, plate
discharge electrodes. Figure 1 shows a plate ESP with wire discharge
electrodes. Dirty gas flows into a chamber consisting of a series of discharge
electrodes that are equally spaced along the center line between adjacent
collection plates. Charged particles are collected on the plates as dust, which
is periodically removed by rapping or water sprays. Discharge wire electrodes
are approximately 0.13 to 0.38 cm (0.05 to 0.15 in.) in diameter. Collection
plates are usually between 6 and 12 m (20 and 40 ft) high. For ESPs with wire
discharge electrodes, the plates are usually spaced from 15 to 30 cm (6 to 12
in.) apart. For ESPs with rigid-frame or plate discharge electrodes, plates are
typically spaced 30 to 38 cm(12 to 15 in.) apart and 8 to 12 m (30 to 40 ft) in
height. Plate ESPs are typically used for collecting fly ash from industrial
and utility boilers as well as in many other industries including cement kilns,
glass plants and pulp and paper mills
Gas flow through a plate precipitator
Tubular
Tubular precipitators
consist of cylindrical collection electrodes (tubes) with discharge electrodes
(wires) located in the center of the cylinder (Figure 1). Dirty gas flows
into the tubes, where the particles are charged. The charged particles are then
collected on the inside walls of the tubes. Collected dust and/or liquid are
removed by washing the tubes with water sprays located directly above the
tubes. The tubes may be formed as a circular, square, or hexagonal honeycomb
with gas flowing upward or downward. A tubular ESP is tightly sealed to
minimize leaks of collected material. Tube diameters typically vary from 0.15
to 0.31 m (0.5 to 1 ft), with lengths usually varying from 1.85 to 4.0m (6 to
15 ft).
Tubular
precipitators are generally used for collecting mists or fogs, and are most commonly
used when collecting particles that are wet or sticky. Tubular ESPs have been
used to control particulate emissions from sulfuric acid plants, coke oven
byproduct gas cleaning (tar removal), and iron and steel sinter plants.
Gas flow through a tubular precipitator
Types of Electrostatic Precipitators
ESPs can be
grouped, or classified, according to a number of distinguishing features in
their design. These features include the following:
• The structural
design and operation of the discharge electrodes (rigid-frame, wires or plate)
and collection electrodes (tubular or plate)
• The method of
charging (single-stage or two-stage)
• The
temperature of operation (cold-side or hot-side)
• The method of
particle removal from collection surfaces (wet or dry)
These categories
are not mutually exclusive. For example, an ESP can be a rigid-frame, single- stage,
cold-side, plate-type ESP as described below.


















