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Black Veatch MESPON 2014 - UniverSUL Consulting · • 150 mg SO 2 /Nm3 (dry basis with 3% excess...

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20 October 2014 SULPHUR TECHNOLOGY MANAGER BLACK & VEATCH ENERGY BILL BRECKENRIDGE MIDDLE EAST SULPHUR PLANT OPERATIONS FORUM AGENDA Interactive Discussion Trends in Overall Plant Emissions Regional / Global Market Perspectives Technical Topics CBA Performance: Improvements & Feedback Organic Sulfur in Acid Gas Contaminated Acid Gas Design Basis
Transcript

20Octob

er2014

SULPHUR TECHNOLOGY MANAGERBLACK & VEATCH ENERGYBILL BRECKENRIDGE

MIDDLE EAST SULPHUR PLANTOPERATIONS FORUM

AGENDAInteractive Discussion

Trends in Overall Plant EmissionsRegional / Global Market Perspectives

Technical TopicsCBA Performance: Improvements & FeedbackOrganic Sulfur in Acid GasContaminated Acid GasDesign Basis

TRENDS IN OVERALLPLANT EMISSIONS

20October 2014

WHAT ARE THE REGIONALTRENDS/OBSERVATIONS?

• 150 mg SO2/Nm3 (dry basis with 3% excessoxygen)• 2007 Environmental Health Standard (EHS)Guidelines for Sulfur Recovery Units inRefineries issued by the InternationalFinance Corporation (“World BankStandard”)

• Commonly used in:• Early project development• Developing countries with no localguidelines

• 750 mg SO2/Nm3 (dry, air free basis)• Roughly 250 ppmv on a dry, air free basis(United States Environmental ProtectionAgency in Part 60, Subpart J. for PetroleumRefineries)

SO2 EMISSION STANDARDS FOR SULFURRECOVERY UNITS

20 October 2014

TYPICAL RECOVERY LEVELS FOR SO2EMISSIONS FROM SULFUR RECOVERY UNITS

20 October 2014

*815C Incinerator Temperature

DRY + 3% OXYGEN DRY + AIR FREE

% Recovery SO2mg/Nm3*

SO2 Stackppmv*

SO2mg/Nm3*

SO2 Stackppmv*

99.97% 150 ~50 180 ~60

99.9% 500 ~165 600 ~200

99.85% 750 ~250 900 ~300

Conventional SRU / TGTU (Amine Based) Design Performance

The trend is lowerand lower emissionrequirements, <150mg/Nm3

CONCLUSIONS:1. Conventional units cannot consistently achieve 50ppmv total sulfur

2. COS remains principal constituent to address

HISTORICAL TGTU PERFORMANCE(CONVENTIONAL REDUCTION / ABSORPTION)

20 October 2014

Absorber Overhead

H2S(ppmv)

COS (ppmv)

CS2(ppmv)

Other (ppmv)

Total(ppmv as S1)

HighPerformance Units

30(<10 to 90)

17(2 to 80)

2(1 to 12)

2(0 to 13)

~50(<10 to 90)

Generic MDEA Units

150(100 to 300)

~175 (100 to 300)

LowPerformance Units

1500(up to 2000)

1500 (up to 2000)

REGIONAL / GLOBALMARKET PERSPECTIVES

20October 2014

REGIONAL GAS SUPPLY/DEMAND &FORECAST FOR NEW SOUR GASDEVELOPMENTS

REGIONAL SULFUR MARKET

GLOBAL GAS MARKETSUPPLY/DEMAND & VIABILITY OFSOUR GAS DEVELOPMENT PROJECTSVS. IMPORTING GAS

TECHNICAL TOPICS

CBA PERFORMANCE:IMPROVEMENTS &FEEDBACK

20October 2014

WHAT ARE THE REGIONALOBSERVATIONS REGARDINGSUBDEWPOINT PERFORMANCE &RELIABILITY?

• CBA process developed by Amoco in 1970s• Achieves higher sulfur recovery than conventionalClaus process (>98.7% vs. 92 96%)

• CBA reactor is a conventional Claus reactoroperated at lower temperature

• CBA reactor operates in “subdewpoint” mode• CBA reactor uses conventional Claus catalyst

SULFUR RECOVERY USING COLD BEDADSORPTION (CBA) PROCESS

20 October 2014

• Cyclical process, CBA reactor alternates adsorptionstep with regeneration step

• There are other similar subdewpoint Clausprocesses; these differ from CBA in method ofregeneration:

• About 35 CBA units have been installed, many innatural gas purification service. Capacities rangefrom 10 TPD – 700 TPD.

SULFUR RECOVERY USING COLD BEDADSORPTION (CBA) PROCESS

20 October 2014

CBA REACTOR SUBDEWPOINTOPERATION

20October 2014

TypicalClaus Reactor

TypicalSubdewpoint Reactor

415° F

450° F

260° F

300° F

Gas inside reactor stays abovesulfur dewpoint as Clausreaction progresses

Gas inside reactor reachessulfur dewpoint as Clausreaction progresses

2 BED CBA—HAS ACHIEVED >99.0%RECOVERY

20 October 2014

SULFUR

CBACONDENSER

CLAUSCONDENSER

CLAUSREACTOR

CBAREACTOR

NO. 1

CBAREACTOR

NO. 2

FROM1ST

CONDENSER

TAIL GASTOINCINERATOR

STEAM STEAM

1st 2nd

3 BED CBA—HAS ACHIEVED >99.2%RECOVERY

20 October 2014

SULFUR

CBACOND. NO. 1

CLAUSCONDENSER

CBACOND. NO. 2

CBACOND. NO. 3

CLAUSREACTOR

CBAREACTOR

NO. 1

CBAREACTOR

NO. 2

CBAREACTOR

NO. 3

FROM1ST

CONDENSER

TAIL GASTO

INCINERATOR

STEAM STEAM STEAM STEAM

1st 2nd 3rd

ONE COMPLETE 2 REACTOR CBA CYCLE

20 October 2014

200

250

300

350

400

450

500

550

600

650

700

4:00

5:00

6:00

7:00

8:00

9:00

10:00

11:00

12:00

13:00

14:00

15:00

16:00

17:00

18:00

19:00

20:00

21:00

22:00

23:00

0:00

1:00

Tempe

rature,°

F

JUST INLET TEMPERATURESAND INCINERATOR SO2 CONCENTRATION

20October 2014

0

1000

2000

3000

4000

5000

200

300

400

500

600

700

12:00

0:00

12:00

0:00

12:00

0:00

Incine

ratorS

O2,pp

mv

Tempe

rature,°

F

• Apply 3 improvements:1. Use a better CBA reactor rotation sequence to avoid

SO2 emissions spikes, improving sulfur recoveryefficiency

2. Use an improved condenser arrangement, requiringonly 3 condensers instead of 4

3. With improved condenser arrangement, operate lastbed at cooler temperature, get better sulfur recoveryefficiency

CAN IMPROVE 3 BED CBA SULFURRECOVERY EFFICIENCY

20 October 2014

• Past 3 bed designs considered catalyst sulfurloadings, sequenced reactors from most loaded toleast loaded

• Better to consider temperature instead of loading,sequencing reactors from highest temperature tolowest temperature

• Catalyst temperature has greater effect on sulfurrecovery efficiency than does catalyst sulfur loading

BETTER 3 BED CBA REACTOR ROTATIONSEQUENCE

20 October 2014

REVISED 3 BED CBA SEQUENCE

20 October 2014

1st 2nd 3rd

1st 2nd 3rd

Old Sequence:(Stages Loadings)

New Sequence:(Stages Temps.)

• Adopt a reactor condenser arrangement wherereactor and upstream condenser switch in sequenceas a unit

• Only 3 condensers required instead of 4• 2 more switching valves required• Facilitates operation of last condenser at coolertemperature

NEXT, IMPROVE 3 BED CBA CONDENSERARRANGEMENT

20 October 2014

3 BED CBA—REACTOR SWITCHES AS UNITWITH UPSTREAM CONDENSER

20 October 2014

1st 2nd 3rd

CBACOND. NO. 1

CLAUSREACTOR

CBAREACTOR

NO. 1

FROM1ST

CONDENSER

STEAM

CBACOND. NO. 2

STEAM

CBAREACTOR

NO. 2

CBACOND. NO. 3

STEAM

CBAREACTOR

NO. 3

SULFUR

TAIL GASTOINCINERATOR

150

200

250

300

350

400

450

500

12:00

0:00

12:00

0:00

12:00

Tempe

rature,°

F

Time, Hours

EXPECTED LAST REACTOR OUTLETTEMPERATURE PROFILES

20 October 2014

2 Bed

3 Bed

3 Bed, Better Rotation3 Bed, Better Rotation, Cooler Temperature

CALCULATED SULFUR RECOVERY EFFICIENCYCOMPARISON FOR NEW 3 BED CBA SCHEME—41% H2S IN ACID GAS FEED

Step Duration(hr)

Sulfur RecoveryEfficiencyPrior 3 Bed

Sulfur RecoveryEfficiencyImproved 3 Bed

Precool 3.0 99.36% 99.52%

Final Cool 3.0 99.43% 99.55%

Heat Up 4.1 99.43% 99.55%

Plateau 1.4 99.35% 99.60%

Heat Soak 1.9 99.45% 99.64%

Overall Averagefor Cycle

13.4 99.41% 99.56%

20 October 2014

• Improved 3 Bed CBA performance (B&V Patent)• Better CBA reactor rotation sequence• Better sulfur condenser arrangement• Cooler last CBA reactor

• No performance data yet• Can test performance improvements in existing 3Bed CBA units, without plant modifications

• Expect 0.15% improvement in sulfur recoveryefficiency—a 25% reduction in SO2 emissions

• Reliable CBA operation at >99.5% cycle averagesulfur recovery efficiency appears within reach, witha cost effective flowsheet

CBA IMPROVEMENT SUMMARY

20 October 2014

SULFUR RECOVERY FOR CLAUS AND CBA DESIGNS

20 October 2014

H2S Concentration in Acid Gas, Mole Percent

Sulfu

r Rec

over

y Ef

ficie

ncy,

Per

cent

0

96

98

100

40 8094

99

97

95

3 Reactor Claus

4 Reactor Claus

CBA 3 ReactorCBA 4 Reactor

20 60 100

Higher SRU recovery by CBAconfiguration may eliminate redundantTGTU sparing requirements

UNIT CONFIGURATION OPTIONS EXAMPLE

20 October 2014

Each SRU has its own dedicated TGTU.Spare SRU and TGTU capacity.e.g. – 3 x 50%

UNIT CONFIGURATION OPTIONS EXAMPLE

20 October 2014

Make each TGTU slightly larger, and eliminateone unit. Spare SRU and TGTU capacity. Somepiping / control complications.e.g. – 3 x 50% SRUs, 2 x 100% TGTUs

UNIT CONFIGURATION OPTIONS EXAMPLE

20 October 2014

Convert each SRU to subdewpoint. Based on~99% recovery, eliminate the requirement forspare TGTU capacity.e.g. – 3 x 50% SRU, 1 x 100% TGTU

Each project will have uniquecircumstances governing /limiting the unit size, recoveryand sparing approach.

ORGANIC SULFUR IN FEEDGAS

20October 2014

HOW OFTEN IS COS/RSH PRESENT INYOUR ACID GAS?

HOW DOES THIS IMPACT EMISSIONS,PARTICULARLY WITH ACID GASENRICHMENT?

DESI

GN

CHALL

ENGES

• For AGE facilities, COS and mercaptans (RSH) contributedirectly to emissions because they tend to slip throughAGE Absorber• COS comes from upstream AGRU that is normally designedto remove all COS (also coabsorbs abundant CO2)

• Mercaptans depend on upstream, AGRU solvent selectionand sophistication of model

• Predicting performance of organic sulfur absorption iscomplex and challenging, particularly at low pressuresand in the presence of H2S• Heavily dependent on accuracy of solvent vendorperformance data to meet emissions

ORGANIC SULFUR IN FEED GAS20 October 2014

Cannot decouple AGRU and SRU Performance!!

1. Diversion of inlet feed gas to TGTU, which contains areducing section that will hydrolyze mercaptans andCOS (no AGE Absorber)

OPTIONS TO MITIGATE ORGANIC SULFUR INFEED GAS – SULFUR BLOCK MODIFICATION

20October 2014

DESI

GN

CHALL

ENGES

2. Diversion of AGE Absorber overhead to TGTU usingsemi rich solvent in AGE Absorber (B&V Patent)

OPTIONS TO MITIGATE ORGANIC SULFUR INFEED GAS – SULFUR BLOCK MODIFICATION

20October 2014

DESI

GN

CHALL

ENGES

3. Interstage cooling and hydrolysis in the AGRU tomaximize CO2 slip and hydrolyze COS (B&V designfrom Sinopec Puguang Natural Gas Treating Project)

OPTIONS TO MITIGATE ORGANIC SULFUR INFEED GAS – UPSTREAMMODIFICATION

20October 2014

DESI

GN

CHALL

ENGES

4. Tail Gas Scrubbing (Caustic Scrubber)• Last resort if integration with AGRU or project optimizationcannot be achieved

• Challenges with tail gas scrubbing• Wastewater disposal or treatment• High alloy metallurgy• Cost (Opex) and delivery logistics of caustic

• Tail gas scrubbing represents a trade of air emissions forliquid emissions or costly wastewater treatment

OPTIONS TO MITIGATE ORGANIC SULFUR INFEED GAS – DOWNSTREAMMODIFICATION

20October 2014

DESI

GN

CHALL

ENGES

CONTAMINATED ACIDGAS

20October 2014

HOW OFTEN IS BTX A COMPONENT INACID GAS?

HAS IT BEEN A PROBLEM?

WHAT ARE YOUR MITIGATIONMEASURES?

• Uncertainty in BTX contained in Produced Gas• Uncertainty in BTX pickup by AGRU solvent• BTX has to be removed or destroyed prior to cominginto contact with any catalyst bed

• Lean acid gases often do not burn hot enough forsufficient BTX destruction in the SRU ThermalReactor

BTX IN FEED GAS

20 October 2014

DESI

GN

CHALL

ENGES

DESI

GN

CHALL

ENGES

• Lean Acid Gas (<45% H2S) + COS/RSH + BTX + Ultra LowEmissions (<150 mg SO2/Nm3) = Difficult Challenge toProcess

• In addition to ultra low emissions, some projects arerequiring a minimal level of SRU recovery• Requirements >95% will require 3rd catalytic stage or moreelaborate design

CONTAMINATED LEAN ACID GAS

20 October 2014

DESI

GN

CHALL

ENGES

• Often significant technical challenges and uncertaintywith lean acid gas feeds and ultra low emissions

• Sizeable commercial and operational impacts forachieving ultra low emissions

• Design optimization requires joint effort andcooperation between designers, end users andregulatory agencies

CONTAMINATED LEAN ACID GAS

20 October 2014

• Alternative options to destroy BTX• Thermal Reactor temperature enhancements:

• Oxygen enrichment – unattractive if oxygen notreadily available. Higher Opex.

• Co firing natural gas – not recommend, trades onecatalyst contaminant (BTX) for another (soot)

• Acid Gas Enrichment to improve acid gas quality• Upstream BTX removal – Sorbead™ Quick Cycleprocess (silica gel based absorbent that removes BTXwith heavier hydrocarbons, also removes mercaptans)

• Carbon beds upstream of SRU (developed by SaudiAramco)

BTX IN FEED GAS

20 October 2014

DESI

GN

CHALL

ENGES

DESIGN BASIS20October 2014

WHAT IS YOUR APPROACH TO SETTINGDESIGN PARAMETERS GAS TREATINGDURING EARLY PROJECTDEVELOPMENT?ARE YOU THINKING ABOUTCOS/RSH/BTX?WHAT ARE LONG TERMPERFORMANCE REQUIREMENTS?

DESI

GN

CHALL

ENGES

• Important components that need to be adequatelydefined:• Organic Sulfur Species – complicate achieving ultra lowemissions• Carbonyl Sulfide (COS) and/or mercaptans (RSH)

• Contaminants – potential catalyst deactivation• Benzene, Toluene, Xylene (BTX)

DESIGN BASIS – FEED COMPOSITION

20 October 2014

DESI

GN

CHALL

ENGES

• Upstream modifications can reduce organic sulfur andBTX content in acid gas feed to SRU

• Being able to integrate and optimize upstreammodifications with SRU design is often complicated• It is difficult for SRU designed to influence overall design ofupstream units that may or may not be in SRU designersscope

• If design can be integrated and optimized across all unitinterfaces, it will result in an overall project WIN in termsof OPEX/CAPEX

DESIGN BASIS – UPSTREAMMODIFICATIONS

20 October 2014

DESI

GN

CHALL

ENGES

• Typically contractors focus on start of run (SOR)guarantees

• Projects with lean acid gases and ultra low emissionsmay have some exposure to performances shortcomingsat end of run (EOR)

• Technology provider and Owner should focus onmaximizing performance at EOR and not just meetingguarantees

DESIGN BASIS – SOR VS. EOR

20 October 2014

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