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  • 7/29/2019 Reducing Carbon Emissions With Antifoulants

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    Reducing carbon emissions withantifoulants

    The UN Kyoto Protocol set the

    rst binding targets for reduc-ing greenhouse gas emissions

    in 1997. Although the US and Chinadeclined to participate, 37 industr-ialised countries and the European

    Union now regulate carbon emis-sions, and the trend seems clear.The EU Energy Pact targets a 20%reduction in CO

    2emissions by 2020,

    and a carbon pricing scheme takeseffect in Australia in 2013.

    These are challenging times forreneries. Sulphur levels must bereduced in nished fuels to meetincreasingly strict specicationsdriven by new emission controltechnologies in motor vehicles.

    Meanwhile, crude feedstocks arebecoming heavier, higher in sulphurand more difcult (and energyintensive) to process.

    Reneries are signicant sourcesof carbon emissions, much of it inthe form of CO

    2from burning fuels

    to distill, crack and hydrotreat theirfeedstocks. In spite of the caps andfees imposed on carbon, demandfor renery products continues togrow, increasing renery energyuse and emissions. Heavier, sourercrude feedstock adds to theproblem.

    The costs are substantial: energycosts for a typical renery are 50-60% of total operating costs,excluding feedstocks.1 Efciency,always a high priority in reneryoperations, has never been moreimportant or more difcult toattain.

    Since crude cost is the single mostimportant determinant of a ren-

    erys protability,2 price differentialson challenging crudes have consid-erable appeal, even though unit

    Carbon emission regulations make renery operation more costly, but appropriate

    antifoulant treatment and monitoring can reduce these costs substantially

    INDIA NAGI-HANSPAL, MAHESH SUBRAMANIYAM, PARAG SHAH and JAMES NOLAND

    Dorf Ketal Chemicals

    designs often limit feedstock exi-bility and heavy crudes can lead tofouling problems both of whichincrease carbon emissions that must

    be factored into the renery operat-ing cost model.

    Consider the current approximateprices of Murban crude (0.6 wt%asphaltenes) and Maya (10.0 wt%

    asphaltenes). Since Maya is $ 13.61/bbl cheaper than Murban, a reneryprocessing 100 000 b/d can save upto $ 1 361 000/day in feedstockcosts alone. As the small sample ofcrudes in Figure 1 shows, Maya is

    just one of many common high-asphaltene crudes.

    Processing these heavy, high-

    www.eptq.com PTQ Q1 2013 89

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    Figure 2 Greenhouse gas emissions decline with increase in API3

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    90 PTQ Q1 2013 www.eptq.com

    sulphur crudes consumes more

    energy and increases greenhouse

    gas emissions (see Figure 2).

    Calculations of actual costs can be

    quite complex, in part because

    different fuels are often used at vari-

    ous stages within the renery. Fueloil and fuel gas are common choices

    in renery furnaces, and their energycontent and emissions differ.

    Although it typically takes less ren-ery fuel oil to heat the feedstock to

    the target temperature than would

    be the case with renery fuel gas(renery fuel oil has a caloric valueof 8740 kcal/ m3 compared to 10 000

    kcal/ m3 for fuel gas), fuel oil carbon

    emissions are usually higher per

    unit of fuel consumed.

    Renery feedstock is anotherimportant consideration. Crude

    production may generate enoughCO

    2emissions to make a given feed-

    stock more costly overall. Oil shale

    production, for example, has been

    shown to contribute more heavily to

    carbon emissions than the extraction

    of other hydrocarbons.

    These issues are increasingly

    important because of the way

    carbon emissions regulations work.

    The Western Climate Initiative in

    selected Canadian provinces and

    California is running a cap-and-trade scheme. In Europe, the EU

    Energy Pact contains key targets for

    the year 2020, in particular a 20%

    reduction in CO2

    emissions (from

    1990 levels) that is designed to

    ensure that at least 20% of total

    energy consumption comes from

    renewable sources.

    Emission Trading SchemeTo meet the new targets, many

    countries will adopt Kyoto mecha-

    nisms such as the Emission TradingScheme (ETS), through which coun-

    tries can buy carbon credits known

    as emission reduction units. These

    can be bought from clean develop-

    ment mechanism projects or carbon

    emission reductions from joint

    implementation projects.

    European Union cap-and-trade

    regulations are the largest such ETS

    to date. Companies there are

    granted emissions allowances that

    they can buy, sell or trade witheach other, but at the end of the

    year each company must have

    enough emissions allowances to

    cover their total emissions.

    The EU ETS regulates 46% of the

    EUs CO2

    emissions by capping the

    amount of CO2

    that can be emitted

    from factories and plants. Once

    Phase III (2013-2020) of the scheme

    is under way, more restrictive

    controls on emissions can be

    expected, along with more efforts to

    reduce carbon credit consumption.

    Support for these schemes is not

    unanimous. Canada withdrew from

    the Kyoto Protocol in December

    2011 to avoid heavy nes for failureto meet emissions targets. China,

    one of the worlds largest emitters of

    greenhouse gases, has not signed the

    Kyoto Protocol, but even there plans

    are already under way to launch a

    few pilot cap-and-trade markets and

    to establish a fully operationalcarbon market by 2015.

    In spite of these regional differ-

    ences, it is clear to renersworldwide that carbon costs are

    becoming signicant variables in therenery cost equation, and many areactively seeking opportunities to

    reduce emissions by increasing ef-ciency. Their rst targets are thesystems that consume fuel for

    instance, furnaces and preheaters

    where efciency depends onfeedstock, fuel source and combus-tion efciency.

    Efciency gained from feedstockchanges must be weighed against

    the prot potential from lower-priced crudes. Changing fuel types

    can entail a signicant investmentand can have a substantial impact

    on operations. Combustion improv-

    ers are a lower-cost option that may

    help in some cases.

    Carbon capture and storage (CCS)

    is another alternative. As the nameimplies, CCS limits the amount of

    CO2

    released into the atmosphere

    by capturing CO2and storing it in

    geological formations underground.

    This, too, is capital intensive. CCS

    is the way of the future despite its

    economic implications.

    AntifoulantsAntifoulants offer another way to

    improve efciency, a proven

    approach that entails little or nocapital investment. Antifoulants can

    also improve gross margins by

    enhancing renery feedstock exibil-ity, and costs are usually very low

    in comparison to the alternatives.

    Uncontrolled fouling decreases

    heat transfer efciency and through-put, increasing fuel consumption

    and carbon emissions. Feedstock

    exibility is impaired and, if leftuntreated, fouling reduces through-

    put and can force units ofine forcleaning or repair.

    Fouling is of two general types:

    inorganic and organic. The former is

    usually caused by elevated levels of

    metals in renery feedstocks, typi-cally occurs between 150 and 360C,

    and tends to increase the potential

    for costly and dangerous corrosion.

    Crudes produced from deep oceanic

    locations often exhibit inorganic

    fouling due to contaminants such as

    salts, lterable solids, basic sedi-ments and corrosion products.

    Organic fouling generally occurs

    above 250C in cracked streams,

    often as a result of high asphaltene

    content or incompatible blends of

    asphaltenic and parafnic crudes.Whether the fouling is inorganic or

    organic, success with antifoulants

    depends on careful monitoring. Key

    parameters include heat transfer

    rates, heat exchanger duties,

    approach enthalpies, feedstockcomposition, CO2

    emissions and

    fuel combustion efciency.Selection of antifoulant is also

    important, especially with todays

    increasingly sour feedstocks.

    Sulphidation is common with these

    crudes, leading to iron sulphide-

    promoted fouling. In most cases,

    antifoulants must therefore be effec-

    tive on asphaltenes and iron

    sulphide.

    Antifoulants work by stabilising

    asphaltenes that would otherwisebecome destabilised when heated.

    This prevents deposition of polynu-

    clear aromatics that, upon further

    heating, can form coke. Left

    unchecked, fouling reduces heat

    transfer from the heating media to

    the cold stream and increases the

    furnace loading needed to achieve

    the required coil outlet temperature.

    Figures 3 and 4 illustrate antifou-

    lant functionality by comparing

    untreated feedstock with treatedsamples. Asphaltenes that agglom-

    erate and settle out in minutes

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    without antifoulant treatment

    remained stabilised for an hour or

    more in the test.

    Experience indicates that antifou-

    lants can increase furnace inlet

    temperature by 5 to 15C in fouled

    systems. It is possible to do even

    better with periodic cleaning. Theway the antifoulant is applied has

    considerable influence on the

    92 PTQ Q1 2013 www.eptq.com

    results, and choosing the correct

    injection point is especially impor-

    tant. A suction pump upstream of

    the main fouling exchangers is

    ideal.

    Case study

    The following case study illustratesthe potential benefits of antifoulantson fuel cost and CO

    2emissions.

    Refinery X was running at an aver-age throughput of >300 000 b/ d.

    The average coil outlet temperature

    (COT) when the feedstock wastreated with antifoulants met the

    refinery standard required toproduce target yields of down-

    stream finished products. Withoutantifoulant, the target COT was

    often impossible to achieve, and

    considerably more energy was

    required (see Figure 5).Antifoulant treatment signifi-

    cantly reduced the fuel consumption

    required to maintain target COT,

    lowering specific fuel costs bynearly 4% (see Figure 6). This savedthe refinery approximately 41 000per month on fuel alone.

    At an average carbon credit value

    of 16 per ton of CO2, refinery

    carbon cost savings would total

    59 000, raising the overall finan-cial impact of antifoulant treatment

    to approximately 100 000 permonth (see Figure 7).

    ConclusionCarbon emission regulations makerefinery operation more costly, butappropriate antifoulant treatment

    and monitoring have been shown

    to reduce these costs substantially.

    Antifoulants also allow refiners toenhance gross refining margins byexploiting lower-cost feedstocks.

    They reduce the fuel consumption

    required to maintain coil outlettemperatures for target throughput

    rates. As a whole, antifoulants

    are an environmentally friendlychoice with attractive economic

    benefits.

    Without additive With additive

    Figure 3 Asphaltene dispersion studies with and without antifoulant

    Agglomeratedasphaltenes

    Dispersedasphaltenes

    11:41 am 3:50 pm

    Figure 4 Testing under a microscope: agglomerated and dispersed asphaltenes

    1.90

    1.92

    1.88

    1.86

    1.84

    1.82

    1.80

    No antifoulant With antifoulant

    Throughput,

    /m3

    1.78

    Figure 5 Specific fuel cost with and without antifoulant

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    www.eptq.com PTQ Q1 2013 93

    References

    1Based on a natural gas price of about $6/MM

    Btu for a typical 100 KBPSD refinery that emits

    1.2-1.5 MM t/yr of CO2.

    2 Stockle M, Carter D, Jones L, OptimisingRefinery CO2

    Emissions, Foster Wheeler

    Technical Paper www.fwc.com/publications/

    tech_papers/files/ERTC%20CO2%20paper%2

    0Nov07.pdf

    3 Brandt A R, Unnasch S, Energy intensity and

    greenhouse gas emissions from California

    thermal enhanced oil recovery, Energy & Fuels

    2010: Keesom W, Unnasch S, Moretta J, Life cycle

    assessment comparison of North American

    and imported crudes. Technical report, Jacobs

    Consultancy and Life Cycle Associates for

    Alberta Energy Resources Institute, 2009.

    India Nagi-Hanspal is Lead Refinery Engineer,

    Technical Services with Dorf Ketal Chemicals,

    Mumbai, India. She holds a MEng degree in

    chemical engineering from Imperial College

    London. Email: [email protected]

    Mahesh Subramaniyam is Director of Research

    & Development with Dorf Ketal Chemicals. He

    7.96

    7.98

    7.94

    7.92

    7.90

    7.88

    7.86

    No antifoulant With antifoulant

    Specificfuelconsumption,

    kg/m3

    7.84

    Figure 6 Specific fuel consumption with and without antifoulant

    41,000 infuel savings

    59,000 incarbon credits

    Figure 7 Financial benefit of antifoulanttreatment

    holds a PhD in chemistry from Indian Institute

    of Technology, Mumbai.

    Email: [email protected]

    Parag Shahworks in Global Refinery Technical

    Services with Dorf Ketal Chemicals in software

    development for desalter adequacy testing and

    monitoring fouling in preheat exchanger trains.He holds a BEng in chemical engineering from

    Mumbai University.

    Email: [email protected]

    James Noland is Senior Director of the Process

    Chemicals Division of Dorf Ketal USA, LLC. He

    holds a BEng in chemical engineering from

    Mississippi State University, USA.

    Email: [email protected]

    http://www.eptq.com/jump.aspx?a=ABB&p=q113