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SCR and SNCR optimization.pdf - Siemens

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Optimizing<br />

<strong>SCR</strong>/<strong>SNCR</strong> PROCESSES<br />

Ammonia Slip – Power Plants


The Challange – Optimizing the <strong>SCR</strong> <strong>and</strong> <strong>SNCR</strong> DeNOx Processes<br />

The <strong>SCR</strong> process<br />

The nitrogen oxides (NO x ) formed<br />

in combustion processes is effi -<br />

ciently reduced to water (H 2 O) <strong>and</strong><br />

nitrogen (N 2 ) in the <strong>SCR</strong> process<br />

(Selective Catalytic Reduction). Ammonia<br />

(NH 3 ) or urea (CO(NH 2 ) 2 ) is<br />

introduced to, <strong>and</strong> mixed with, the<br />

fl ue gases upstream of a heterogeneous<br />

catalyst over which the reduction<br />

takes place. Depending on the<br />

amount of dust, type <strong>and</strong> concentration<br />

of acidic gas components in the<br />

fl ue gas, the <strong>SCR</strong> process is normally<br />

operated in the temperature range of<br />

250 °C – 400 °C.<br />

Ammonia<br />

tank<br />

Do you use <strong>SCR</strong> – or <strong>SNCR</strong> – or both?<br />

Combustion air<br />

The <strong>SNCR</strong> process<br />

In the <strong>SNCR</strong> process (Selective Non<br />

Catalytic Reduction), usually ammonia<br />

(NH 3 ) or urea (CO(NH 2 ) 2 ) is<br />

introduced to, <strong>and</strong> mixed with, the<br />

fl ue gases in the hot combustion<br />

zone where the reduction of NO x<br />

takes place. Depending on type of<br />

the used reducing agent, different<br />

additives etc., the <strong>SNCR</strong> process is<br />

usually operated somewhere in the<br />

temperature range of 800 °C – 950<br />

°C. At this temperature range many<br />

competing reactions, consuming<br />

ammonia, takes place e.g. oxidation<br />

to nitrogen (N 2 ) <strong>and</strong> oxidation to<br />

nitrogen oxides (NO x ). At temperatures<br />

below the temperature window<br />

the reaction rate is too slow resulting<br />

in too high ammonia slip, <strong>and</strong> above<br />

the temperature window the oxidation<br />

of ammonia to NOx is too high<br />

thus the process tends to produce<br />

NOx instead of decreasing it.<br />

There are several reasons, not only<br />

to measure, but also for control<br />

of the ammonia slip after a DeNOx<br />

process.<br />

As the ammonia slip contributes to<br />

the total nitrogen emission from the<br />

plant, the emission of NH 3 is usually<br />

regulated to a maximum value<br />

by legislation. And a too high NH 3<br />

emission is of course negative also<br />

from an NH 3 consumption cost point<br />

Air preheater<br />

of view. But in order to optimize<br />

the NOx reduction reaction in the<br />

DeNOx process, the effectiveness is<br />

increased by an increased NH3 supply<br />

to the process which gives an<br />

increased NH3 slip. Optimizing the<br />

NOx reduction is of high importance<br />

in cases where there is a NOx fee or<br />

tax on NOx emission by legislation.<br />

Outside this discussion of legislation<br />

<strong>and</strong> direct costs for NOx /NH 3<br />

emissions <strong>and</strong> the NH3 consumption,<br />

there are also some process specifi c<br />

items that have to be taken into account.<br />

Ammonium BiSulphate (ABS)<br />

The NH 3 injected to the fl ue gas, or<br />

being thermally produced from<br />

Ammonia slip <strong>and</strong> water<br />

vapour measurements for<br />

catalyst <strong>optimization</strong> <strong>and</strong><br />

boiler tube surveillance<br />

Temperature catalyst: 250 – 400°C<br />

Temperature stack: 110 – 140°C<br />

Ammonia level: 0 – 10 ppm<br />

Water vapour level: 5 – 15 %<br />

n Resolution NH3 : ±0,3 ppm<br />

n Resolution H2O: ±0,1 %<br />

Dust load catalyst: ~20 g/Nm 3<br />

Dust load stack: ~5 mg/Nm 3<br />

n Response time: 1 – 30 sec.<br />

(depending on dust load)<br />

ESP FGD BH<br />

an injected ammonia derivate, can<br />

give ammonium salt formation from<br />

acidic gas components in the fl ue<br />

gas at lower temperatures. Theoretically<br />

several salts can be formed,<br />

e.g. NH 4 Cl, NH 4 NO 3 , but the main<br />

problems related to ammonium salt<br />

formation is caused by ammonium<br />

bisulphate (ABS), NH 4 HSO 4 in the<br />

power producing industry from NH 3 ,<br />

H 2 O <strong>and</strong> SO 3 in the fl ue gas. Some<br />

formation of ammonium sulphate,<br />

(NH 4 ) 2 SO 4 will also occur, especially<br />

when the ammonia is in excess of<br />

the SO 3 concentration. Ammonium<br />

bisulphate has a melting point of 147<br />

C, <strong>and</strong> will consequently be present<br />

as a liquid accumulated on surfaces<br />

or as a liquid aerosol in the fl ue gas<br />

at normal operating temperatures.<br />

Such an aerosol will contribute to<br />

the visibility of the fl ue gas plume –<br />

referred to as a “blue haze” phenomena<br />

– if the particles are able to emit<br />

through the stack. Further more, the<br />

ABS is hygroscopic at lower temperatures<br />

<strong>and</strong> will cause a corrosive solution<br />

when absorbing moisture from<br />

the gas.<br />

If the ABS is formed in the <strong>SCR</strong> catalyst<br />

in low temperature catalyst, it<br />

might plug parts of the catalyst, increasing<br />

the pressure drop over the<br />

catalyst <strong>and</strong> cause catalyst deactivation.


ABS on Air Preheater surface<br />

When the fl ue gas passes the air<br />

preheater, AP, the temperature is<br />

decreased <strong>and</strong> the ABS condensation<br />

temperature is reached somewhere<br />

inside the AP. Most of the<br />

ABS is formed <strong>and</strong> accumulated on,<br />

relative the fl ue gas, the cold heat exchange<br />

surfaces, but a part of it will<br />

be formed in the fl ue gas thus forming<br />

a liquid aerosol.<br />

The amount of the NH 3 slip will give<br />

the total amount of ABS as the SO 3<br />

usually is in excess in combustion<br />

processes. As the accumulation will<br />

partially plug the AP the pressure<br />

drop will increase <strong>and</strong> the effi ciency<br />

decrease.<br />

The AP has to be designed by using<br />

material (e.g. enamel-plates)<br />

which can withst<strong>and</strong> the corrosive<br />

ABS. Knowing the NH 3 slip <strong>and</strong> SO 3<br />

content in fl ue gas the condensation<br />

Ammonia slip control is important<br />

The process has to be controlled in<br />

order to keep the ammonia slip low<br />

<strong>and</strong> keep the total nitrogen emission<br />

low from the plant. This will avoid<br />

ammonium salt formation with potential<br />

dust plugging, corrosion <strong>and</strong><br />

catalytic deactivation. A slip control<br />

will also minimise the ammonia consumption.<br />

In order to control the <strong>SCR</strong><br />

process <strong>and</strong> the ammonia slip, a fast<br />

<strong>and</strong> accurate in-situ measurement of<br />

NH 3 has to be applied. LDS 3000 supplied<br />

by <strong>Siemens</strong> Laser Analytics will<br />

meet these requirements.<br />

temperature, <strong>and</strong> hence the height<br />

in the AP, can be predicted so that<br />

the condensation occurs in the part<br />

covered with enamel. This part will<br />

be equipped with (high pressure)<br />

water washing lances in order to<br />

wash away the ABS salt at outages.<br />

The washing will create an effl uent<br />

water which may require neutralization<br />

<strong>and</strong> possible other waste water<br />

treatment.<br />

An accurate measurement of the<br />

ammonia slip gives the possibility<br />

to predict or plan outage <strong>and</strong><br />

AP design – corrosive protection <strong>and</strong><br />

washing equipment operation.<br />

ABS on the fl y ash<br />

ABS formed on the fl y ash particles<br />

collected in an electrostatic<br />

precipitator, ESP, may cause two<br />

different problems. Ammonia accumulated<br />

to the fl y ash may be a<br />

problem if placed on a refuse tip. If<br />

LDS 3000<br />

<strong>Siemens</strong> Laser Analytics provides<br />

gas analyzers – LDS 3000 – for<br />

process control applications based<br />

on tunable diode laser. Due to the<br />

early Swedish deNOx legislation we<br />

focused on ammonia analyzers in<br />

the late eighties <strong>and</strong> grew later into<br />

combustion control applications. Filter<br />

<strong>optimization</strong> <strong>and</strong> emission monitoring<br />

are also substantial parts of<br />

our core applications.<br />

Our fi rst commercial order came<br />

1992 <strong>and</strong> today we have more<br />

than 60 installations in Europe, USA<br />

<strong>and</strong> Japan.<br />

accumulated on fl y ash, collected in<br />

an ESP which operates at a temperature<br />

above the ABS melting point, or<br />

if the heaters in the bottom hoppers<br />

locally create a temperature above<br />

this melting point the ABS can give<br />

a sticky ash from the ESP hoppers<br />

which can be problematic to h<strong>and</strong>le.<br />

If the ash collector is of a fabric fi lter<br />

type the salt can cause other operational<br />

problems, e.g. increased pressure<br />

drop.<br />

Flue Gas Desulphurization<br />

plant, (FGD)<br />

If the plant is equipped with a fl ue<br />

gas desulphurization plant, FGD,<br />

parts of the ammonia slip will also<br />

be absorbed on dust <strong>and</strong> particles<br />

<strong>and</strong> powder products from that process<br />

<strong>and</strong> parts of it will be solved into<br />

the process water in wet scrubber<br />

processes for removal of SO 2 , HCl<br />

etc. is used.<br />

The Solution – Ammonia Slip Measurement using LDS 3000 from<br />

<strong>Siemens</strong> Laser Analytics AB – Laser Based Gas Analysis.<br />

Central unit – CU 3000<br />

LDS 3000<br />

Sensor pair<br />

CD 3002<br />

The central unit CU 3000<br />

All critical components are housed<br />

in the central unit <strong>and</strong> it can be<br />

placed several hundred meters away<br />

from the measurement point. The<br />

communication with the sensor is<br />

through optical fi bers.<br />

Sensor CD 3002<br />

The sensor consists of a pair mounted<br />

opposite of each other. An optical<br />

component (lens or window) is facing<br />

the process <strong>and</strong> protected with<br />

purging air or other gas. The sensor<br />

pair contains a minimum of electrical<br />

or optical components to improve<br />

reliability <strong>and</strong> availability.<br />

Related documents<br />

Additional documents can be downloaded<br />

from our web site at:<br />

http://www.siemens.se/sla<br />

Navigate to Service & Support <strong>and</strong><br />

Documentation<br />

1 Product Information<br />

2 LDS 3000 Overview<br />

3 LDS 3000 Basic Operation<br />

4 LDS 3000 Data Sheet<br />

5 Measurement Principle<br />

6 Dust Compensation<br />

Contact<br />

<strong>Siemens</strong> Laser Analytics (headquarters<br />

in Göteborg, Sweden)<br />

Marketing Director<br />

Jan Grimbr<strong>and</strong>t<br />

jan.grimbr<strong>and</strong>t@siemens.com<br />

Marketing Assistant<br />

Michaela Hermansson<br />

michaela.hermansson@siemens.com<br />

Phone: +46 (0)31 50 68 50<br />

web: http://www.siemens.se/sla


Your local representative<br />

Better control of your process<br />

<strong>Siemens</strong> is a network encom- encom-<br />

passing more than 450,000<br />

people in 190 countries. We<br />

take pride in possessing in-<br />

depth knowledge of customers’<br />

requirements <strong>and</strong> the expertise<br />

to create innovative solutions<br />

in electrical engineering <strong>and</strong><br />

electronics.<br />

<strong>Siemens</strong> Laser Analytics AB<br />

Box 8910<br />

402 73 Göteborg<br />

Phone: +46 31 50 68 50<br />

fax: +46 31 22 21 19<br />

mail: info@lds3000.com<br />

web: http://www.siemens.se/sla

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