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Q1 2024
REFINING
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DIGITAL TWINS
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CHALLENGES
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& TOWERS CONTROLLING
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© 2023 Honeywell Inc. All rights reserved
uop.indd 1
13/12/2023 17:46:07
ptq
PETROLEUM TECHNOLOGY QUARTERLY
Q1 (Jan, Feb, Mar) 2024
www.digitalrefining.com
3 Challenges to chemical recycling of plastic waste
Rene Gonzalez
5 ptq&a
15 Adding CHP to refinery power infrastructures
Rene Gonzalez
PTQ
19 Filtration and separation for industrial carbon capture, transport, and storage
Lara Heberle and Julien Plumail
Pall Corporation
25 Overcoming wastewater challenges of opportunity crude processing
Shane Lund
Veolia Water Technologies & Solutions
31 Biofilm: A hidden threat
Brian Martin Marathon Petroleum Corporation
Tim Duncan and Gordon Johnson Solenis LLC
39 Simulating FCC upset operations
Tek Sutikno
Fluor Enterprises
45 Refractory detection system and floating roof protection
Bob Poteet and Andrea Biava WIKA
Haytham Al-Barrak and Mahendran Sella Saudi Aramco
51 Crude to chemicals: Part 2
Kandasamy M Sundaram, Ujjal K Mukherjee, Pedro M Santos and Ronald M Venner
Lummus Technology
59 Revolutionising refining with digital twins
Michelle Wicmandy, Jagadesh Donepudi and Rodolfo Tellez-Schmill
KBC (A Yokogawa Company)
65 Optimising nitrogen utilisation in refinery operations
Rajib Talukder and Prabhas K Mandal
Aramco
75 Simulating VGO, WLO, and WCO co-hydroprocessing: Part 2
Mohamed S El-Sawy, Fatma H Ashour and Ahmed Refaat Cairo University
Tarek M Aboul-Fotouh Al-Azhar University
S A Hanafi Egyptian Petroleum Research Institute
81 Considerations for crude unit preflash drums and preflash towers
Henry Z Kister and Walter J Stupin (dec.) Fluor
Maureen Price Maureen Price Consulting LLC
93 Technology in Action
Cover
Large volumes of utility steam and cooling water are key to sustainable refinery and petrochemical operations, such
as the unit shown on the front cover.
Photo courtesy of Kurita Water Industries Ltd
©2024. The entire content of this publication is protected by copyright. All rights reserved. No part of this publication may be reproduced,
stored in a retrieval system or transmitted in any form or by any means – electronic, mechanical, photocopying, recording or otherwise
– without the prior permission of the copyright owner.
The opinions and views expressed by the authors in this publication are not necessarily those of the editor or publisher and while every
care has been taken in the preparation of all material included in Petroleum Technology Quarterly and its supplements the publisher
cannot be held responsible for any statements, opinions or views or for any inaccuracies.
www.digitalrefining.com
www.decarbonisationtechnology.com
q1 ed com.indd 1
12/12/2023 12:34:25
Revamp to thrive in
the new reality
Ever-changing market conditions, global economic challenges, and the shared journey
of the energy transition all mean it is crucial to evaluate easy-to-implement and costeffective improvement opportunities. At Shell Catalysts & Technologies, our solutions
open new possibilities for smarter investments while preserving cash through revamping,
reconfiguring, or optimising your existing assets. Our experts co-create tailored solutions
while keeping your margins in mind – ensuring the investments you make right now can
help you maintain your competitive advantage into the future.
Learn more at catalysts.shell.com/revamps.
shell.indd
1
shell_revamp_PDQ.indd
1
08/12/2023
11/14/2312:55:23
2:59 PM
ptq
Challenges to
chemical recycling
of plastic waste
PETROLEUM TECHNOLOGY QUARTERLY
Vol 29 No 1
Q1 (Jan, Feb, Mar) 2024
Editor
Rene Gonzalez
[email protected]
tel: +1 713 449 5817
Managing Editor
Rachel Storry
[email protected]
Editorial Assistant
Lisa Harrison
[email protected]
Graphics
Peter Harper
Business Development Director
Paul Mason
[email protected]
tel: +44 7841 699431
Managing Director
Richard Watts
[email protected]
Circulation
Fran Havard
circulation@petroleumtechnology.
com
EMAP, 10th Floor, Southern House,
Wellesley Grove, Croydon CR0 1XG
tel +44 208 253 8695
Register to receive your regular copy
of PTQ at https://bit.ly/370Tg1e
PTQ (Petroleum Technology Quarterly)
(ISSN No: 1632-363X, USPS No: 014-781)
is published quarterly plus annual Catalysis
edition by EMAP and is distributed in the US
by SP/Asendia, 17B South Middlesex Avenue,
Monroe NJ 08831. Periodicals postage paid at
New Brunswick, NJ. Postmaster: send address
changes to PTQ (Petroleum Technology
Quarterly), 17B South Middlesex Avenue,
Monroe NJ 08831. Back numbers available
from the Publisherat $30 per copy inc postage.
T
he end products obtained through the chemical recycling of plastic wastes
can be used as fuels, lubricants, or feedstocks for chemicals production, contributing to a more sustainable and circular economy. However, the efficiency
and economic viability of chemical recycling processes can vary depending on the
specific feedstock and the desired end products.
The chemical recycling of pyrolysis oil (from plastic waste) typically involves refining or upgrading the oil to improve its properties or convert it into specific chemicals.
This can be done through processes such as hydrotreating, hydrocracking, and other
chemical reactions. The goal is to produce higher-quality products that can be used
as fuels, chemicals, or feedstocks for various industrial applications.
However, some sceptics in Europe, the US, and elsewhere say the technical challenges run much deeper than previously expected, including contaminants poisoning of hydroprocessing catalysts, energy consumption, and emissions. The landscape
of waste management and recycling initiatives can change rapidly, though, and new
developments in one small pilot plant or research project could resolve these hurdles.
Steady progress is expected in 2024 to fund scale-up to commercial production
of chemical recycling of plastic waste-derived pyrolysis oil to its basic monomer.
Although there are already proven technologies for producing propylene, polypropylene, and other plastics precursors, these are single-use, non-circular routes.
Public campaigns to arrive at an international treaty limiting single-use plastics production coincide with calls for the implementation of Extended Producer
Responsibility policies. This would make plastics manufacturers responsible for the
entire life cycle of plastic products, and may incentivise resolutions of the many challenges associated with expanding chemical recycling of plastic wastes.
Despite the 2022 Inflation Reduction Act that could provide up to $1 trillion for
‘green’ investments (possibly including biomass or plastics chemical recycling to
valuable products like PVC), billions of dollars continue to pour into the conventional
fossil fuel industry, including refinery and petrochemical projects in the Middle East,
Saudi Arabia, and China.
Regardless of the increased use of EVs, solar, and other ‘green’ energy alternatives,
global oil demand in 2024 is set to grow year on year by an impressive 2.2 million
bpd, supported by steadily rising road mobility in major consuming countries, such
as China, India, and the US.
The IEA estimated growth in demand for petrochemical products means that
petrochemicals are set to account for nearly half of growth in oil demand to 2050,
ahead of diesel, SAF, and maritime fuel. It is no secret that refiners can sell fuels for
$550/ton or else convert fossil-based feedstocks to petrochemicals and earn around
$1,400/ton, such as with the integrated refinery and petrochemical facilities in India.
Against this backdrop, it is projected that global production of thermoplastics will
amount to 445.25 million metric tons per year (mmtpy) in 2025. Annual production
volumes are expected to continue rising in the following decades to approximately
590 mmtpy by 2050. While the percentage from chemical recycling of plastic waste
contributing to that 590 mmtpy seems insignificant, the fossil fuel industry seems
confident that steady technical improvements will allow the upgrading of higher volumes of plastics waste-derived pyrolysis oil through refinery hydroprocessing units.
The profitable link between plastics and fossil fuels may have provided a lifeline for
Big Oil, including the refining industry. This begs the question: why invest in chemical recycling of plastic waste? With the prospect of a global treaty that limits noncircular, single-use plastics production, it could be a big winner.
Rene Gonzalez, Editor, PTQ
PTQ Q1 2024
q1 ed com.indd 3
3
11/12/2023 11:38:41
es
ot
N
Process
Vacuum tower cutpoint delivers profits
Cutpoint Concerns
Crude unit vacuum tower performance is often critical
to a refiner’s bottom line. The vacuum tower bottoms
stream is valued far below the gas oil cuts, so most
refineries look to minimize it. Many vacuum columns
are also designed or revamped to produce a diesel cut,
recovering diesel slipped from the atmospheric column
that would otherwise be downgraded to VGO product.
Good vacuum column performance can maximize the
profitability of downstream units by removing distillate
hydrotreater feed (diesel) from FCCU or hydrocracker
feed (VGO) and removing VGO from coker feed (resid).
One important measure of vacuum column
performance is VGO/resid cutpoint. The cutpoint is the
temperature on the crude TBP curve that corresponds
to the vacuum tower resid yield.
Vacuum column cutpoint depends on three variables:
1. Flash zone temperature
2. Flash zone pressure
3. Stripping section performance (if present)
Flash zone temperature is driven by vacuum heater coil
outlet temperature (COT). Increasing COT increases
cutpoint. Vacuum heater outlet temperature is typically
maximized against firing or coking limits. When
processing relatively stable crudes, vacuum heaters
with better designs and optimized coil steam can avoid
coking even at very high COT (800°F+, 425°C), but
poorly designed heaters may experience coking with
COT below 700°F (370°C).
Flash zone pressure is set by vacuum system
performance and column pressure drop. Lower flash
zone pressure increases cutpoint until the tower shell
C-factor limit is reached, at which point the packed
beds begin to flood. Vacuum producing systems are
mysterious to many in the industry, so a large number
of refiners unnecessarily accept poor vacuum system
performance. With technical understanding and a good
field survey, the root causes of high tower operating
pressure can be identified and remedied.
In columns with stripping trays, stripping steam rate
and tray performance are important. Stripping steam
rate is limited by vacuum column diameter (C-factor)
and vacuum system capacity. Any steam injected into
the bottom of the tower will act as load to the vacuum
system, so vacuum system size, tower operating
pressure, and stripping steam rate must be optimized
together. Depending on the design, a stripping section
with 6 stripping trays can provide between zero and
two theoretical stages of fractionation, which can drive
a big improvement in VGO yield.
Although the variables for maximizing vacuum tower
cutpoint are simple, manipulating them to maximize
cutpoint without sacrificing unit reliability is not.
Contact Process Consulting Services, Inc. to learn how
to maximize the performance of your vacuum unit.
3400 Bissonnet St.
Suite 130
Houston, TX 77005, USA
pcs cutpoint.indd 1
+1 (713) 665-7046
[email protected]
www.revamps.com
16/09/2020 12:05
ptq&a
Q
With the chemical value of hydrogen (H₂) increasing,
what are the best options for extracting H₂ from fuel gas?
A Neeraj Tiwari, Principal Process Engineer, Honeywell
UOP, [email protected]
High-yield byproducts generated by the refinery process
for motor fuel, diesel or aromatics production can be highvalue secondary revenue. The typical composition of fuel
gas contains H2 as ~30-50 mol%, and other major components are LPG range material. To monetise the benefit of
these high-value byproducts and increase the overall profitability, a novel concept involving a dual sponge absorber
can be applied to the off-gas stream (routed to fuel gas
header) to recover the majority of LPG range material along
with light naphtha, if any.
The application of a novel dual sponge absorber will
improve the hydrogen composition in off-gases to a high
level (such as 70-85 mol%). This high-purity gas can then
be routed to PSA to recover hydrogen efficiently having
a purity of 99.9 mol%. In catalytic reforming, secondary
byproducts generated include H₂, LPG, and fuel gas. Of
these byproducts, the lowest value byproduct is generally
fuel gas.
UOP’s proprietary RecoveryMax system allows 95%
recovery of hydrogen, >85% LPG recovery, and nearly
100% reformate recovery by purifying more of these
byproducts and not diverting them to fuel gas. Alternative
options are being explored based on where hydrogen is
being used as one of the raw materials.
One option is to contact the feed stream or any hydrocarbon stream with hydrogen-rich fuel gas that will absorb the
hydrogen; then, the absorbed hydrogen can be used during
the reaction process.
Concern with this option is that it can also absorb impurities from fuel gas (such as C1, C2), which may not be desirable in the process.
A
Cristian Spica, Application Engineer, OLI Systems
Hydrogen is an integral part of the modern energy industry
and plays a crucial role in the path to net zero.
Despite the strong momentum behind ‘green’ hydrogen, to stay on track for achieving net zero emissions by
2050, we will need more than a doubling of the announced
investments by 2030. These investments must mature and
be put into action.
Therefore, considering their significant economic advantages and as part of the short- to mid-term strategy to
support the development of a clean hydrogen economy, we
should make use of ‘grey’, ‘turquoise’, and especially ‘blue’
hydrogen production methods. Industrial technologies currently employed for grey hydrogen production include:
• Catalytic steam methane reforming (SMR)
• Dry reforming (DR)
• Catalytic partial oxidation (CPO)
www.digitalrefining.com
Q1 q&a.indd 5
More answers to these questions can be
found at www.digitalrefining.com/qanda
• Autothermal reforming (ATR)
• Tri-reforming (TR)
• Coal/petroleum coke gasification/pyrolysis.
Blue hydrogen also relies on hydrocarbons but is combined with carbon capture, utilisation, and storage (CCUS)
technology, which helps mitigate its environmental impact
but may require additional investments.
Turquoise hydrogen is produced through methane thermal pyrolysis. Each of these technologies has its own set of
advantages and disadvantages based on the unique characteristics of the process.
While SMR is one of the most established and widely
used technologies for grey hydrogen production, it is also
one of the most energy and capital-intensive processes.
This is because the endothermic reaction in SMR requires
heat, and the catalyst can suffer from deactivation if the fuel
gas is not properly desulphurised.
Additionally, in an SMR plant, there are two sources of
CO₂ emissions: one from the oxidation of carbon atoms in
the feedstock during reforming and shift reactions and the
other from combustion in the reformer furnace. To capture
all the CO₂, a post-combustion plant is required, as precombustion capture can only capture the CO₂ in the syngas.
Despite these challenges, SMR is still considered one of
the most efficient methods for producing grey hydrogen,
especially when heat integration is part of the process
design. The same efficiency advantage applies to DR, but it
also faces the drawback of coke deposition on the catalyst
surface. In the case of CPO, the partial oxidation of CH₄
and other hydrocarbons in the fuel gas is a slightly exothermic reaction, making it less capital-intensive than SMR.
However, it initially produces less hydrogen and CO₂ per
unit of input fuel compared to SMR. To produce high-purity
H2, pure oxygen or an air separation unit (ASU) is needed.
ATR generates syngas by partially oxidising a hydrocarbon feedstock with oxygen and steam, along with subsequent catalytic reforming. Unlike SMR, the heat for the
reaction is provided within the reaction vessel, eliminating
the need for an external furnace. This method allows up to
99% of carbon removal directly from the syngas, resulting
in lower carbon capture costs. ATR, when combined with
CO-shift and carbon capture technology, is one of the most
cost-effective solutions for large-scale low-carbon hydrogen production.
TRM is a combination of SMR, CO₂ reforming, and PCO in
a single reactor for efficient syngas production. The inclusion of oxygen in the reaction generates in-situ heat, which
can enhance energy efficiency. However, it may present
challenges in terms of heat transfer and temperature uniformity in the catalyst bed.
The choice of the best production process depends on
several factors affecting both capital and operational expenditures, including hydrogen yield, purity, energy efficiency,
flexibility, plant complexity, and raw material availability.
PTQ Q1 2024
5
08/12/2023 13:54:17
ATR combines the advantages of both SMR and partial oxidation, offering a high hydrogen yield, rapid reaction kinetics, and reduced reactor number and size.
OLI Systems provides unique tools for designing and
safely operating grey and blue hydrogen facilities. These
tools encompass a wide range of capabilities, including
modelling for various production processes (SMR, ATR,
TRM, CPO) for hydrogen storage, transportation, and
CCUS. These tools offer rigorous mass balance, corrosion,
and scaling risk assessment, considering the reactivity and
phase equilibria of impurities and their potential negative
impacts on plant safety and reliability. Hydrogen as well as
CO₂ dense phase, especially when containing impurities,
can promote corrosion in materials such as steel, pipelines,
and storage tanks. Impurities like water vapour, oxygen,
sulphur compounds, nitrogen compounds, and carbon
monoxide can react with hydrogen to form corrosive substances, making the selection of corrosion-resistant materials essential for hydrogen transportation infrastructure.
Q
What contaminants removal capabilities are available
to expand the SAF feedstock base?
A Yvon Bernard, Business Development Manager,
Renewable Product Line, Yvon.BERNARD@axens.
net, Yoeugourthen Hamlaoui, Global Market Manager,
[email protected], Alexandre Javidi,
Alcohol to Jet Business & Technology Manager, Alexandre.
[email protected], Axens
u For SAF production from low-carbon ethanol through
Axens’ proprietary Jetanol solution, one of the key Axens
features (Atol) is an innovative and profitable technology
due to its flexibility in handling a wide range of feedstocks.
During the technology development, Axens, along with its
partners IFPEN and TotalEnergies, developed customised
analytical methods for mastering the ethanol impurities
that are critical for this application.
Extensive testing in pilot plants was also performed to
confirm the technical ability to process virtually all kinds
of ethanol: bioethanol (1G) or advanced ethanol (2G)
and waste-based ethanol (from blast furnace flue gas
and municipal solid waste) at various levels of dilution.
Furthermore, Atol relies on its superior catalyst, which has
proven to have a high tolerance to feedstock impurities and
is fully regenerable. Atol catalyst provides even more flexibility by allowing the handling of feedstock quality fluctuations. In terms of ethanol, impurities are well-known and
can be handled with pretreatment solutions.
v For SAF production from lignocellulosic biomass via gasification route (BioTfueL), impurities are dealt with in three
steps. The first is the pretreatment step, which ensures the
removal of foreign contaminants such as glass, rocks, plastics, and moisture. Additionally, the pretreatment homogenises the biomass through drying and torrefaction: this step
is key to enabling the utilisation of a wide array of lignocellulosic biomass, from agricultural residues to energy crops
and forestry residues. In the second step, biomass gasification technology removes the inorganic (mineral, metals)
and chlorine from the biomass.
6
Q1 q&a.indd 6
PTQ Q1 2024
The remaining S- or N-based impurities are removed in the
syngas phase through well-known separation technologies.
Its smart and flexible contaminant removal scheme allows
BioTfueL to operate with any kind of biomass. This feature
means more resilience for the project and gives significant
flexibility in operation to the customers. Some additional feedstock, like municipal solid wastes, brings other opportunities
but requires additional pretreatment and purification steps to
deal with the heterogeneity of the feedstock and impurities.
w For SAF production from CO₂ and H₂, purity requirements are often regulated by the downstream unit, mainly
the Fischer-Tropsch reaction section for the e-fuel production. Axens dispatches its wide portfolio to cope with
the common impurities found in CO₂ feedstock, including
adsorbents for impurities trapping as well as washing sections, to bring the feed to the desired specifications. The
final scheme of purification will depend on CO₂ project quality and is typically adapted on a case-by-case approach.
Typical contaminants for FT catalyst are (sulphur, organic
nitrogen, metal, NOx). Axens’ integrated scheme takes
advantage of its expertise and know-how to optimise the
sizing and positioning of such purification requirements.
x For SAF production from vegetable oils with Vegan
technology, pretreatment is also needed. Phospholipids
and metals (Fe, Mg, K, Ca, Na) were the main contaminants present in the first-generation vegetable oil (soybean
oil, palm oil, rapeseed oil) and could be abated with wellestablished edible oil refining technologies. The processing
of second-generation waste oil (used cooking oil, animal
fats) brings a wide variety of contaminants, including the
same contaminants as vegetable oil, but at higher content.
Pretreatment technologies are adapting to remove contaminants to acceptable levels. Higher nitrogen, sulphur
and chlorine are also observed in these new feeds: nitrogen/sulphur are partially removed by pretreatment and then
converted by the hydrotreatment, inorganic chloride is completely removed by pretreatment, whereas organic chloride
slips to the hydroprocessing unit, which has an impact
on the unit design and metallurgy selection. Polyethylene
found mostly in animal fats should be removed in a dedicated section of the lipid feed pretreatment.
A
Andres Coy, Business Development Manager SAF,
Syngas and Fuels, [email protected], Rainer Albert
Rakoczy, Technology Advisor Fuel and Hydrocarbons,
Syngas and Fuels, [email protected], Clariant
Catalysts
The potential feedstocks and process routes toward SAF
are constantly increasing. Any SAF as a final Jet fuel blending component must meet very stringent specifications, as
aviation fuels are the most delicate fuel products in terms
of quality and stability. In addition, most of these processes
need optimum reactant properties to achieve the most efficient SAF yields. Clariant offers a broad variety of catalysts
and adsorbents technology to clean most feed and intermediate species in gas or liquid phase for these SAF processing technologies. This technology is primarily based on
long-time experience in handling non-benign and demanding feed streams even in industries beyond refinery.
www.digitalrefining.com
08/12/2023 13:54:18
Turn iron into gold?
Alchemy? No.
It’s chemistry.
Grace, the global leader in FCC catalysts and additives, introduces
MIDAS® Pro catalyst
MIDAS® Pro catalyst, for resid cracking in high iron applications.
offers the solution for
This innovation, built on our workhorse MIDAS catalyst platform, proved
resid cracking in high iron
its capacity to handle even the worst Fe excursions. In commercial trials
environments. Gain feed
with multiple in-unit applications, MIDAS Pro catalyst demonstrated
flexibility with better
sustained bottoms cracking in the face of iron spikes that measured
bottoms upgrading.
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among the highest in the industry. Diffusivity levels were consistently
high, indicating no transport restrictions with concentration of Fe.
This improved iron tolerance allows refiners to operate at higher iron
levels which increases feed processing flexibility and profitability.
Talk with your Grace partner about the
advantages of MIDAS® Pro catalyst today.
Learn more at grace.com
grace.indd 1
08/12/2023 12:52:29
A Kandasamy Sundaram, Distinguished Technologist &
Lummus Fellow, [email protected]
SAF is addressed from different angles. Plastics pyrolysis,
tyre pyrolysis, and vegetable oils are a few examples. They
all have different types of contaminants compared with fossil
fuels. Some adsorbents are used to remove some contaminants. However, they are not able to reduce the concentration
significantly. Hydrotreating is required. Isoterra for vegetable
oil uses hydrotreating. Plastic pyoil requires hydrotreating
to reduce chlorides and nitrogen. For chemicals production,
adsorbents meet the specification in some cases.
produce soft sensors generated through surrogate models
that will provide insights for adjustments of parameters
such as temperature, pressure, and flow rates to maximise
efficiency and product quality.
w Predictive maintenance: AI can monitor equipment and
machinery in real-time, analysing data from sensors to predict when maintenance is needed. This can help prevent
unplanned downtime and reduce maintenance costs.
x Production scheduling: AI can create optimised production schedules that balance production efficiency with
demand fluctuations and resource constraints.
A Ezequiel Vicent, Senior Application Engineer and A Ezequiel Vicent, Senior Application Engineer and
Consulting Lead, OLI Systems
The advent of renewable fuels has brought the necessity to
change catalyst to treat the carboxylic groups in the fatty
acids that make up vegetable oils (increased CO, CO₂ and
H₂O production) as well as an increase in chlorides. In addition to catalyst selection, unit engineers need to focus on
the production of the byproducts from these reactions.
We have seen an increase in NH₄Cl salt formation out of
these feeds that can foul the feed-effluent exchangers at
higher temperatures. The increase in water formation (up
to five times larger than usual hydrocarbon feed) means
the possibility of the salts that deposit in the feed-effluent
exchangers getting wet increases dramatically. Engineers
need to monitor the exchangers for the NH₄Cl formation
temperature as well as the relative humidity increase due
to increased water content.
The engineer should note that at relative humidity greater
than 10%, ammonium chloride salts will start to absorb
water from the vapour stream. This can cause underdeposit corrosion and pitting in equipment and piping. The
equipment most at risk for this type of corrosion is the feedeffluent heat exchangers and the piping up to the reactor
effluent air coolers inlet wash water injection.
In this case, operations will need to invest in monitoring
tools (both software and hardware) that can help them calculate salt formation temperatures, water relative humidity,
and sour water concentrations (especially bisulphide concentration) to maintain static asset reliability.
Q What role are AI systems expected to play when optimising plant-wide operations?
A Isabelle Conso, Digital Innovation Director, Isabelle.
[email protected], and Philippe Mege, Digital Services
Factory Manager, [email protected], Axens
AI is expected to play a significant role in optimising plantwide operations. Here are some key roles and benefits that
AI systems can provide in this context:
u Safety and compliance: AI can monitor safety conditions
in the plant and detect anomalies or potential hazards. It
can also assist in compliance with regulatory requirements
by ensuring that processes and products meet the necessary standards.
v Process optimisation: AI can continuously analyse vast
amounts of data from various sensors to uncover patterns
in view of production process optimisation. It can also
8
Q1 q&a.indd 8
PTQ Q1 2024
Consulting Lead, OLI Systems
AI will play a major role in the optimisation of plant-wide
operations both during steady-state times and during shutdowns and start-ups. There are many examples of how AI
is being used today to optimise a plant, but the decision to
go from an open system to a closed system is still a few
years away< and the technology has not yet caught up.
A prime example of AI being used in plant optimisation
is in the area of energy and emissions management. There
are energy optimisers that use first principles to look at the
current energy status of the unit and are able to optimise
fuel consumption and steam production while accounting for combustion emissions to minimise the amount of
energy needed for the steam demand.
They will account for steam Cogen units and heat integration. However, to predict future demand, AI models
‘learn’ where the peaks and valleys come in and are able to
predict the input changes before they happen. This helps
the energy optimiser capture changes more quickly and
have additional energy savings.
Another area where AI, or in this case a Machine Learning
(ML) model, can make a big impact is in dynamic processes,
like the start-up or shutdown of a unit. Consider a unit where
a process upset occurs upstream, and a column needs to be
quickly shut down with a precise sequence of events. The
outcome largely relies on the operators’ experience. In such
a case, a ML model can be ‘taught’ that exact sequence
under varying process and environmental conditions.
Various dynamic simulations can be created to show the
different types of upsets that can trigger a shutdown, and
the shutdown sequence can be included. The ML model,
once tested against multiple simulations, can now be
added as a closed-loop system and allowed to ‘operate’ the
shutdown or start-up of the column to avoid damage to the
unit or unwanted chemical releases.
However, for more complex systems, AI still needs to
evolve as a technology. Several refiners we have worked
with have started on the path of AI implementation but have
stopped short of full ‘autonomous plant’ systems. We have
heard that the complexity of the processes at the refinery
and the constant variation of feedstock and pricing have
made it difficult to gain value from full AI implementation.
A
Lisa Krumpholz, CSO, Navigance GmbH, Lisa.
[email protected]
The major challenges of optimising plant-wide operations
www.digitalrefining.com
08/12/2023 13:54:19
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08/12/2023 13:01:07
are the vast amount of data available and the high complexity of interconnected unit operations. Traditional
first-principles models and tools for optimisation have disadvantages in coping with these challenges as they usually
require high effort and thus cost to develop, maintain, and
adapt to changes in the operation.
In contrast, AI systems with machine learning-based
models at their core can be designed with reasonable effort
for complex systems. They offer the opportunity to learn
automatically from continuous data streams in the plant
and adapt quickly to changing conditions.
Thus, AI systems will see rapid adoption in the coming
years to replace, complement or enhance existing optimisation approaches. Like the developments in autonomous
driving, AI systems are expected first to be adopted as
assisting systems to support and enable better human
decision-making for plant-wide optimisation.
Q
Gasoline, diesel, and aviation fuel are still expected
to dominate refinery markets to 2030; what reactor and
catalyst systems will be the most effective in maximising
fuel production?
A Pierre-Yves le-Goff, Global Market Manager Reforming
and Isomerisation, [email protected],
Laurent Watripont, Clean Fuels Technologies Director
Expert, [email protected], Christophe
Pierre, Reforming Product Line Manager, Gasoline
Product Line Technology and Technical Support Business
Division,
[email protected],
Matthew
Hutchinson, Senior Technology Manager, Gasoline and
Petrochemical Technologies, Technology Dept., Matthew.
[email protected], Axens
For gasoline production, among the building blocks of
the gasoline pool, we can mention isomerate and reformate. For reforming, maximisation of gasoline production
is linked to a reduction of cracking while ensuring a stable
operation. The addition of modifiers is one of the possibilities to reduce cracking; however, rigorous selection process
is needed to ensure that stability and regenerability are not
impacted. Axens, formerly Procatalyse, has been involved
in such a field of expertise since the mid-1990s.
From a process standpoint, reduction of the pressure will
improve the fuel production. However, such a reduction
needs to be compatible with unit constraints (for example,
pressure drop). To mitigate these pressure drops, a possibility is to move from a standard axial flow reactor to a
radial flow reactor. Axens has already performed such
modifications and has proprietary internals to improve gas
distribution.
On the isomerisation side, depending on the octane target and feed composition, different schemes can be proposed. For example, if the feed is rich in C6 paraffin, the
deisohexaniser (DIH) column can be implemented to maximise octane without selectivity debit. In addition, to reduce
cracking, the use of high-activity catalyst is of paramount
importance. Therefore, Axens process expertise with
ATIS-2L catalyst provides the best combination for isomerisation unit optimisation.
10
Q1 q&a.indd 10
PTQ Q1 2024
A Johanna Fernengel, Product Manager, Syngas and
Fuels, [email protected], and Rainer Albert
Rakoczy, Technology Advisor Fuel and Hydrocarbons,
Syngas and Fuels, [email protected], Clariant
Catalysts
Besides topping upgrading, the key to maximising fuel production is the right balance of hydrocracking (HC), delayed
coking (DC), and catalytic cracking (FCC), as this gives
the highest flexibility in utilising nearly any crude source,
including renewable sources. In particular, utilisation of the
light olefins from the FCC off-gas with alkylation and oligomerisation with alternative concepts can give a higher flexibility, moving from sole gasoline focus towards distillates
as potential diesel and jet blending components.
A Ioan-Teodor Trotus, Team Leader Refining, Ioan-
[email protected], hte GmbH
Which reactor system will be the most effective depends
on multiple factors, such as the feed or feed mix to be converted, the actual fuel to be produced – diesel, gasoline, or
aviation fuel – and, of course, on which reactors are already
operating in the refinery.
For a refinery that aims to convert mainly crude oil with
existing plants – be it hydrotreaters, hydrocrackers or FCC
units – pilot plant tests will yield the most reliable results for
choosing the right catalyst system.
The right catalyst system must show a reasonable level of
activity and stability to maximise the duration of an operating
cycle. This can be determined in pilot plant testing either as
the start-of-run activity or by performing accelerated deactivation studies to estimate the mid-run or end-of-run activity.
At the same time, pilot plant testing will give information
about the yields and properties of each fuel fraction, allowing one to feed a techno-economic model with actual plant
data and make a like-for-like comparison of all the catalyst
systems to be compared.
For a refinery aiming to co-process or process renewable
feedstocks in existing equipment, a pilot plant test is even
more important because it also allows the operator to see a
new application in action before testing in a production unit.
The number of industrial references for the conversion of
renewable fuels is still relatively low compared to the number of references for the conversion of crude-derived feeds.
Simply relying on models and paper studies is particularly
risky in these cases, as such models still have relatively little
data on which to build their estimates.
In short, the most effective catalyst – be it for hydroprocessing or FCC applications aimed at the production of
fuels and the conversion of renewables – will most likely be
the one that was determined by a pilot plant test.
A Kurt du Mong, CEO, Zeopore Technologies
A key value creator in the refinery, specifically to yield fuels,
remains the hydrocracker. These units feature multicomponent catalysts involving NiW or NiMo hydrogenation
components supported on acidic zeolite/alumina carriers.
These types of catalysts have gone through generations of
remarkable developments, particularly with respect to the
optimisation of the zeolite component.
www.digitalrefining.com
08/12/2023 13:54:20
Over the last decade, it has become clear that optimising the zeolite’s mesoporosity and macroporosity enables
the control of the degree of cracking, thereby maximising
the yield of fuels, which was demonstrated in a selection
of refineries. However, thus far, mesoporous zeolite-based
hydrocracking catalysts have been associated with inhibitive cost increases and lower conversion levels, limiting
their widespread application.
Zeopore helps to overcome such limitations via a platform
of affordable USY zeolites, yielding selectivity and activity benefits of a wide range of catalyst types and zeolite
contents.
Zeopore’s mesoporised hydrocracking zeolites have
recently been tested in a high throughput facility of a
major refiner, generating up to 4 wt% more middle distillates at retained activity levels, generating $15 million
more profit per average hydrocracker (see Zeopore press
release: www.zeopore.com/post/zeopore-enables-breakthrough-in-hydrocracking-by-leveraging-zeolite-mesopore-quality)
Q
How is the dual focus on increasing butylene and propylene production being met?
A
Alvin Chen, Global Technology Application Manager,
Hernando Salgado, Technical Service Manager, BASF
While butylene pricing is often quite stable (typically either
very high or very low), propylene pricing has seen significant volatility over the past few years. One approach that
many refiners have adopted, to address the dual focus on
butylene and propylene production, is to formulate a base
FCC catalyst with moderate overall LPG= selectivity and an
emphasis on strong C₄= selectivity. Such a catalyst coupled
with judicious usage of ZSM-5 offers excellent C₄= selectivity during times when C₃= value is low. However, it still
allows the refiner to capture short-term C₃= opportunities
while maintaining a strong C4= yield.
One strategy for the optimum base catalyst is to optimise
the acid site distribution on the catalyst by increasing total
surface area while reducing acid site density, allowing similar catalytic activity with reduced hydrogen transfer. Since it
is known that butylenes are more sensitive than propylene
to hydrogen transfer effects, a catalyst with this approach
will target both products depending on process conditions
and externally added ZSM-5. BASF applies this catalyst
design approach in the Multiple Frameworks Topologies
(MFT) technology, where secondary zeolite frameworks are
also used to further improve butylenes to propylene flexibility. Catalysts like Fourte and Fourtune for VGO applications and Fortitude for resid applications are examples of
the MFT catalyst technology for FCC units.
It should not be forgotten that operating conditions, such
as catalyst-to-oil ratio and reactor outlet temperature, also
have an impact on butylenes to propylene distribution, with
butylenes favoured at mild severity conditions, while propylene is favoured at high severity conditions.
A Stefan Jäger, Applied Catalyst Technology Engineer,
[email protected],
www.digitalrefining.com
Q1 q&a.indd 11
Rainer
Albert
Rakoczy,
Technology Advisor Fuel and Hydrocarbons, Syngas and
Fuels, [email protected], Clariant Catalysts
In traditional refining, the catalytic cracker (FCC) is the
source for light olefins such as propylene and butylenes. In
many countries, demand for gasoline is shrinking as individual transportation is the most influenced section during
the energy transition, moving to lean consumption engines,
plug-in hybrids or fully electric-driven solutions. Thus, the
product slate behind FCC calls for more distillates and light
olefins and less gasoline. Cracking technology providers can
offer revamp solutions to follow these requirements (second
riser and modified catalyst solution). Clariant can offer adsorbents and catalysts to clean these streams, delivering highpurity light olefins over the fence or utilising these olefins in
the refinery grid toward fuels or even chemicals.
A
Cai Zeng, Head of PDH Strategic Marketing and
Product Management, Propylene Catalysts, Cai.Zeng@
clariant.com, Clariant Catalysts
Petrochemicals customers are now looking for unique and
extremely reliable technology for co-processing butane
and propane to meet both increasing butylene production
and propylene demand. Catalysts such as Clariant’s highly
selective Catofin catalyst and the company’s patented
metal-oxide HGM allow for thermodynamically advantaged
reactor pressure and temperature to achieve a high conversion rate and maximised yield. One example is the Hengli
Group’s world’s largest mixed-feed dehydrogenation plant
in China using the Catofin technology. The plant is designed
to process 500 KTA of propane and 800 KTA of iso-butane
feeds to produce propylene and iso-butylene.
A Kandasamy Sundaram, Distinguished Technologist &
Lummus Fellow, [email protected]
On-purpose propylene routes are satisfying the demand to
some extent. FCC and olefin conversion technology satisfy
some additional capacity in addition to thermal cracking.
Butene-1, Butene-2, and isobutene have different markets.
Due to the decline in the MTBE market, isobutene is not
requested by our clients. The dimerisation of ethylene is
meeting some demand.
A Victor Batarseh and Bani Cipriano, W. R. Grace & Co.
The FCC unit is a key source of both propylene and butylene. While the primary drivers for propylene and butylene
demand are different, there is some overlap in the factors that influence their production in the FCC. Propylene
demand stems mostly from the demand for polypropylene
and other chemicals such as acrylonitrile and cumene.
Meanwhile, butylene demand primarily stems from the production of high-octane alkylate used as a blending stock
for gasoline. The FCC can produce high amounts of propylene and butylene, and to increase their production, refiners
have process knobs available such as feedstock selection,
implementation of FCC product recycles, adjustment of
cat-to-oil ratio, and hydrocarbon partial pressure (among
others).
At times, the knobs previously listed are not sufficient to
bring refiners to a truly optimised yield slate with respect to
PTQ Q1 2024
11
08/12/2023 13:54:20
C3= Yield vs. Conversion
8.0
8.0
7.5
7.5
Total C3= Yield (vol%)
Total C4= Yield (vol%)
C4= Yield vs. Conversion
7.0
6.5
6.0
5.5
Base
Base w/GBA
5.0
60
62
64
66
68
70
72
7.0
6.5
6.0
5.5
Base
Base w/GBA
5.0
74
Conversion
60
62
64
66
68
70
72
74
Conversion
Figure 1 Yield shifts from an FCC implementing GBA, where the FCC observed increased butylene and propylene yields of
approximately 1 vol% at equivalent conversion levels
propylene and butylene production. In this case, collaboration with the FCC catalyst partner is required to evaluate
catalytic solutions that bring another degree of freedom
to solving this challenge. To target increased LPG olefin
production, it is important to ensure the FCC base catalyst
drives appropriate levels of gasoline yield and olefinicity.
The resulting gasoline olefins are then cracked into
smaller LPG olefins via the incorporation of a pentasil zeolite technology. While this overall approach holds for both
propylene and butylene, the choice of catalyst and pentasil
technology can influence whether butylene or propylene
selectivity is maximised, as will be explained in more detail.
Butylene
Grace’s approach to increasing butylene yields is twofold. Starting with a base catalyst that supplies sufficient
conversion and gasoline olefinicity is key. Building on that
foundation, Grace supports customers with both additivebased and catalyst-oriented solutions. For refiners who
2.0
require flexibility to quickly manipulate butylene yields with
the backdrop of shifting constraints or feedstock availability, an additive solution is recommended. GBA can be
implemented to quickly increase butylene without as much
propylene increase as a traditional ZSM-5 additive.
Figure 1 shows yield shifts from an FCC implementing GBA,
where the FCC observed increased butylene and propylene
yields of approximately 1 vol% at equivalent conversion levels.
When refiners consistently require higher butylene yields,
Grace considers adjustments to base catalyst formulation to
incorporate both Y and pentasil zeolites with its proprietary
Achieve 400 platform of catalyst, which delivers impressive
butylene yields and selectivity.
Incorporating the pentasil zeolite functionality directly
into the base catalyst with optimised active-matrix surface
area, zeolite-to-matrix surface area ratio, pore distribution,
and Y-zeolite stabilisation maximise butylene yield and
selectivity while also improving gasoline octane and LPG
olefinicity. Achieve 400 Prime is the latest development on
the butylene selective catalyst platform and delivers the
highest butylene yields, selectivity, and LPG olefinicity.
Figure 2 demonstrates the step-out butylene yield and
selectivity performance of Achieve 400 Prime relative to
competitor butylene selective catalyst.
Total C4= /wt. %
1.5
1.0
0.5
0.0
-0.5
Competitor
Grace
-1.0
-5
-4
-3
-2
-1
0
1
Conversion / wt. %
Figure 2 Butylene yield and selectivity performance
of Achieve 400 Prime relative to competitor butylene
selective catalyst
12
Q1 q&a.indd 12
PTQ Q1 2024
Propylene
As in the case of butylene maximisation catalyst systems,
when selecting a catalyst for maximising propylene, the
need for conversion is balanced against minimising hydrogen transfer reactions to preserve gasoline-range olefins.
Traditionally, to minimise hydrogen transfer, max propylene
catalysts are designed with low unit cell size and a cokeselective matrix. Max propylene catalyst systems include a
ZSM-5 technology that cracks gasoline olefins into LPG olefins while shifting the selectivity towards propylene. FCCs
with a high propylene yield of 11 wt% or higher are not
uncommon. In these cases, a high addition rate of ZSM-5
is used.
Relative to a lower activity ZSM-5 additive, using the
www.digitalrefining.com
12/12/2023 15:45:36
highest activity ZSM-5 results in reduced additive consumption for a similar or higher propylene yield. Since
ZSM-5 can only crack gasoline-range molecules, using
a large amount of ZSM-5 additive results in a dilution of
the base catalyst activity and lower conversion of feedstock into gasoline olefin precursors. The main benefit
then of using a high-activity additive is to minimise the
dilution of the base catalyst activity vs the use of a loweractivity ZSM-5 additive. To maximise propylene, Grace
recommends using high-activity ZSM-5 additives from its
OlefinsUltra family of additives or its newest innovation in
ZSM-5 technology, Zavanti additives.
In summary, refiners are adopting a variety of strategies to increase butylene and propylene from the FCC,
depending on their specific hardware constraints, downstream handling limits, and regional economics. FCC catalysts and additives are key elements of the strategy as
well, given the flexibility they offer and the dynamic nature
of the FCC unit operation.
A
Ezequiel Vicent, Senior Application Engineer and
Consulting Lead, OLI Systems
The dual focus on increasing butylene production and propylene production is being met with ZSM-5 technology
and a propane/propylene (PP) splitter (50-300 MMUSD).
Refiners on the US West Coast and the Gulf of Mexico
are best positioned to take advantage of an increase in the
production of butylene and propylene. However, market
www.digitalrefining.com
Q1 q&a.indd 13
drivers and asset characteristics will dictate the extent of
the benefit realised.
Increasing the production of propane, propylene, and
butylene can be achieved by introducing additives to the
FCC catalyst, the zeolite ZSM-5. This ZSM-5 will help in
the cracking and production of butylene and propylene.
The butylene will be used at the alkylation (sulphuric or HF
acid) unit to produce alkylate, a gasoline-range material
almost void of contaminants and aromatic components
and makes an excellent blending component in the gasoline pool.
Whenever there is insufficient butylene or a market need
for increased alkylate, propylene can also be added to the
alkylation unit.
However, the propylene can be cleaned at a PP splitter and further refined to either chemical-grade propylene
(92-95 mass% propylene) or polymer-grade propylene
(99.5 mass% and greater).
If a refinery does not have a PP splitter as an asset, the
butylene/propylene or propane/propylene mix can be sent to
the gas plant and recovered as ‘refinery gas’, which can be
later used as fuel to the various furnaces in the refinery.
The investment to design and install a PP splitter at a refinery is not small. Pre-COVID estimates put the total cost of
the project at around 300 million US dollars (2019) on the
West Coast (California) and around 50 to 100 million US dollars (2019) in the Gulf. The three-to-one ratio difference is
due to labour and materials costs on the West Coast.
PTQ Q1 2024
13
08/12/2023 13:54:24
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08/12/2023 12:49:36
Adding CHP to refinery power
infrastructures
CI scores and delivered economic impact at downstream facilities improve when
adding CHP units to increase electrical and thermal efficiency
Rene Gonzalez
Editor, PTQ
I
mplementing combined heat and power (CHP) plants
fuelled by natural gas (NG), renewable natural gas (RNG),
or hydrogen can reduce refinery operating costs during
normal run lengths or extended downtime for a unit revamp.
The end game is a huge reduction in the process gas emissions footprint. Financially, this means that with proper
equipment selection and layout design, the return on investment (ROI) of the CHP cogeneration power plant in the refining and petrochemical industry could be less than a year.
Cogeneration facilities have been a mainstay in commercial
and industrial facilities worldwide, with capacities approaching 100 MW in various applications. In addition, CHP cogeneration units under 20 MW are used throughout the oil and
gas industry, including the refining and petrochemical sectors, particularly during a major revamp or turnaround, as
well as during normal operations.
Although the demand for CHP units has remained relatively flat until recently, that market is projected to expand
as these portable systems are part of the broader effort
towards transitioning to more sustainable energy sources,
reducing GHG emissions, and promoting circular economy
practices by reusing waste materials, such as in the production of RNG. For example, combining CHP units powered
by fuels such as RNG or hydrogen benefits project carbon
intensity (CI) scores in the long term.
Energy efficiency
Downstream processing facilities have significant energy
requirements, both for electricity (compressors, pumps)
and thermal energy (heat and steam), making CHP systems
an efficient and cost-effective solution for the following
applications:
Steam and power generation: Refineries use steam for
various processes, including distillation, desalting, and
heating. CHP systems can simultaneously generate electricity and steam, optimising energy use and reducing overall energy costs.
Waste heat recovery: Refineries produce a substantial
amount of waste heat as a byproduct of their operations.
CHP systems can capture and use this waste heat to generate electricity or provide supplementary process heating,
improving energy efficiency.
Process heating: High-temperature heat is often required
www.digitalrefining.com
RENE.indd 15
for specific processes. CHP systems can provide this heat,
reducing the need for separate heating systems and improving overall energy efficiency.
Energy cost reduction: By generating electricity on-site,
refineries can reduce their reliance on external power sources,
potentially leading to cost savings, particularly when energy
prices are high.
Environmental benefits: CHP systems can help reduce
greenhouse gas emissions (GHG) and other pollutants, as
they are more energy efficient compared to traditional power
generation methods.
Energy security and reliability: CHP systems enhance the
reliability of power supply in refineries, offering a back-up
power source during grid outages or other disruptions.
Specific configurations of CHP systems in a refinery or
petrochemical unit will depend on the plant’s energy needs,
available energy sources, and operational processes. The
choice of technology, such as gas turbines, steam turbines,
reciprocating engines, will also be based on the refinery’s
specific requirements, such as the volatile process of upgrading refinery-grade propylene to higher margins polypropylene via thermocompression benefits from an integrated CHP
and chiller design to balance cooling water requirements.
In some cases, refineries and chemical plants with CHP
systems can contribute excess electricity back to the grid,
potentially earning revenue through power sales. CHP technology can be deployed quickly, cost-effectively, and with
few geographic limitations.
Natural gas-powered CHP has quietly provided highly
efficient electricity and process heat to some facilities.
Improve CI scores
To date, NG-powered CHP operations provide the leverage
to decouple from grid electricity affected by high GHG emissions and unreliable grid connectivity. In the future, combining RNG and NG, or pure RNG, improves a facility’s CI scores,
but other factors also influence whether a refinery or chemical plant benefits from CHP. For example:
• Would there be substantial business, safety, or health
impacts if the electricity supply were interrupted, such as
during a major turnaround or weather-related outage?
• Is there interest in reducing a facility’s impact on the
environment?
PTQ Q1 2024
15
08/12/2023 14:59:50
Conventional generation
Power station fuel
(US average fossil fuel)
155 units fuel
Combined heat and power (CHP)
Power plant
Electricity
52% efficient
Electricity
Annual
consumption
Boiler
Heat
Boiler fuel
(Gas)
36 units
Electricity
44 units
Heat
Combined heat
and power (CHP)
1 MW Natural gas
reciprocating engine
CHP fuel
(Gas)
100 units fuel
Heat
TOTAL FUEL EFFICIENCY
80% efficient
Figure 1 EPA-sourced diagram comparing conventional generation vs CHP
• Are there concerns about the impact of current or future
energy costs on the business?
• Does the facility operate at high utilisation rates?
• Are there plans to replace, upgrade, or retrofit central plant
equipment (such as generators, boilers, and chillers) within
the next three to five years?
Overall, integrating CHP into a facility demonstrates a
commitment to sustainable practices and environmental
stewardship, enhancing the facility’s reputation and appeal
to environmentally conscious consumers and stakeholders.
CHP systems are one of the most direct pathways towards
reducing carbon intensity and increasing RNG’s value.
Opportunities
For these bespoke circumstances, CHP has proven its ability
to offer a variety of benefits, including avoided capital costs,
revenue stream protection while reducing exposure to electricity rate increases from the grid. Against this backdrop, NG
or RNG-powered CHP will positively impact carbon scores
vs the grid’s supply mix.
By using waste heat recovery technology to capture
wasted heat associated with electricity production, CHP
systems can typically achieve total system efficiencies of
60-80%, compared to 50% for conventional technologies
(such as purchased utility electricity and an on-site boiler).
In fact, the Waste Heat & Carbon Emissions Reduction Act
encourages the development of small CHP projects of less
than 20 MW. This includes CHP/NG/RNG/microgrid applications at facilities without temporary or permanent grid access.
Basically, they need less fuel, including tail gas, for a given
unit of energy output. Operating costs are further reduced
because the CHP output reduces electricity purchases.
Through on-site generation and improved reliability, CHP
can allow facilities to continue operating in the event of a
disaster or grid interruption, thus protecting revenue streams
from the increasing drop in grid reliability, such as the hurricane-prone US Gulf Coast refining region. Unfortunately,
the drop in grid reliability is co-occurring with electricity rate
increases. Because less electricity is purchased from the grid
using CHP, facilities have less exposure to rate increases.
CHP units can be configured to operate on a variety of fuel
types, such as NG, RNG, biogas, hydrogen, or a combination
thereof. Therefore, a facility could build in fuel-switching capabilities to hedge against high fuel prices. With the passage of
the US Inflation Reduction Act (IRA) and its full implementation
16
RENE.indd 16
PTQ Q1 2024
in 2024, flat demand for CHP seen over the past decade will
increase linearly for RNG-powered CHP units.
Paybacks
To further generate credits, The IRA reduced ‘direct pay’
timelines, increasing paybacks from CHP projects with
built-in efficiencies, resiliency, and sustainability. All signs
suggest that RNG projects fuelling CHP units will grow significantly in 2024. RNG economics increase with CHP utilisation, exhibiting a linear relationship between improved CI
score and improved RNG market value.
The Wall Street Journal recently predicted that RNG may
make up nearly 30% of the total natural gas supply by 2040
compared to less than 1% today. Against this backdrop, tax
and regulatory-driven incentives (renewable identification
numbers [RINs], Low Carbon Fuel Standard [LCFS]) can
facilitate the pace and permitting pathways to RNG and
CHP integration, such as identifying the necessary permits
and approvals required for RNG and CHP components of
the project.
Notwithstanding, every effort should be made to maximise LCFS and Investment Tax Credits (ITC) in addition to RINs
under the Renewable Fuel Standard (RFS) programme. This
is the reason why CHP projects are seen in other industries.
CHP market growth in the refining and petrochemical industry may soon follow. However, according to some experts,
CHP downstream applications in Europe, The Middle East,
and other major refining regions outside North America seem
minimal to nothing, perhaps because IRA, US Environmental
Protection Agency (EPA), and other similar types of government incentives are not available in other regions.
For more near-term prospects, biogas (biomethane) and
RNG-powered CHP projects can be implemented now. RNG,
meanwhile, can be generated from the direct gasification or
pyrolysis of biomass. “The high methane content of RNG
allows for full compatibility within pipeline systems. CHP
fleets that run on natural gas require minimal upgrades to
be fuelled by RNG and would produce immediate emission
reductions by transitioning,” the CHP Alliance noted.
EPA support
On the market front, evolving opportunities include the
outgrowth of Power Purchase Agreement (PPA)-style contracts, which can be designed for heat and power purchases.
The EPA’s CHP Partnership programme aims to promote
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the adoption of CHP systems across different industries and
sectors. The programme provides technical assistance, tools,
and resources to help organisations and businesses assess
the feasibility of CHP projects and facilitate their implementation and certification. This programme includes all types of
CHP applications.
While not directly administered by the EPA, various federal
and state-level renewable energy incentives may apply to certain facilities that utilise CHP. These incentives could include
tax credits, grants, or other financial benefits aimed at promoting clean and renewable energy sources. The EPA occasionally offers grant programmes supporting clean energy projects
and initiatives, including those involving CHP and RNG.
EPA grant opportunities are typically designed to reduce
GHG emissions and promote sustainable energy practices.
The EPA’s Combined programme aims to highlight the benefits of CHP in improving energy efficiency, resiliency, and reliability for critical infrastructure and facilities, which could be
relevant for chemical processing facilities looking to enhance
their energy systems with CHP (see Figure 1).
IRA and RIN credits
Along with these bespoke opportunities, state-driven efforts
to boost distributed generation are opening new pathways
for non-traditional CHP entrants. The IRA will allow production tax credit (PTC) and investment tax credit (ITC) recipients to monetise credits through the previously mentioned
‘direct pay’ option or by selling all or a portion of the credits.
With these incentives covering as much as 30% of project
cost, the payback timeline decreases.
CHP projects are more attractive with their built-in efficiency, resiliency, and sustainability. Going forward, the
onus on achieving circa 20% LCFS reduction by 2030,
and even more so by 2040, predicates the development of
RNG-powered CHP units demonstrating highly negative CI
scores. RNG-based CI score ranges benefit from combined
value delivered LCFS and D3 RINs, as well as D5 RINs (RINs
is the RFS programme’s ‘currency’).
When considering value ranges to produce RNG, such
as the -100 to -400 CI scale, adding value from LCFS compounds the attractiveness of RNG-powered CHP projects.
Using a more specific demonstration, the value of dairy RNG
= (D3 + LCFS) or RNG = ($37 [for D3 RIN @ $3.15/RIN]) +
(LCFS = $65 [with a CI of -225]) is what is driving RNG/CHP.
If a refinery, such as one in California, uses a certain amount
of RNG for cogeneration originating from agricultural or
dairy waste, it can demonstrate sustainable performance in
a circular economy. Note that the $37 is from the Federal
RFS RINs programme, the $65 is from the California LCFS
programme, and the commodity value of the gas is just $2.
Although CI scores are typically discussed without units, it is
actually measured in grams of CO2 equivalent per megajoule.
Because of the combined value delivered by RFS RINs and
California LCFS, interesting programmes are also developing
for RNG/CHP projects in other industries, such as the plastics
industry. Under the RFS programme, every feedstock and
fuel type has a specific ‘D’ code of RINs. With RNG, there are
pathways for qualification as a D3 RIN or D5 RIN.
For example, D3 ($3.15/RIN) is generated from a
www.digitalrefining.com
RENE.indd 17
cellulosic-based feedstock (landfill gas, wastewater treatment plant, or any other feedstock with a 75% or greater
adjusted cellulosic content). If a D3 RIN cannot be generated, then a D5 ($1.87/RIN) can be generated as long as it is
renewable biomass. However, that gap (or spread) has been
wider in the past at about 4x or 5x difference. So, many planners, including a few refiners, are targeting those cellulosic
feedstocks to capitalise on the higher value D3 RIN.
Existing pathways
In this early stage of incentives implementation, it is likely to
be seven to 10 months from commercial operation before
LCFS credits are awarded. This expected revenue needs to
be planned for, understanding that incentive payments may
not be realised for at least seven months before obtaining a
registered certification pathway under an LCFS. The credit
must then be generated and sold.
A common business practice among corporate planners
involves banking and planning for about 10 months of limited LCFS cash flow. The RIN usually falls within that period
because the RNG is being stored during that time. The
important aspect to understand is that earned value is not
lost during those 10 months. Certain accounting exercises
allow for the virtual storing of the RNG. The bottom line is
that patience is necessary to fully monetise value from the
RIN and LCFS pathway during that 10-month delay.
The LCFS also has a process where a temporary pathway
can be used to generate credits upon submitting an application. That temporary pathway can be as much as -150 CI
for cellulosic feeds, so a lot of revenue could be left on the
table using that temporary pathway because the project is
expected to provide CIs in the -200 to -400 range. It boils
down to an economic exercise as to what works for a given
project. Otherwise, carefully budgeting and planning for
those seven to 10 months is good practice. So, it is more of a
timing delay until you receive that LCFS credit.
Alignment
We are seeing the coalescing of regulations, business practices, and technical advancements favouring RNG-powered
CHP systems. They are well suited for applications with very
negative CI scores associated with lucrative LCFS values. In
the US, the Fuel LCA model is used to measure the same
(low CI ~ high $ value).
Organisations like the Combined Heat & Power Alliance
provide monetisation support to the CHP industry, particularly through CHP Technical Assistant Programs (TAPs).
Such alliances help deploy CHP more effectively, which is
why the CHP market is projected to be worth $35.2 billion by
2026. Adding CHP to a facility not only increases CI scores
but also has a positive economic impact on the project.
The IRA extends the ITC of 30% and PTC of $0.0275/
kWh (2023 value) until at least 2025. However, projects over
1 MW AC must meet prevailing wage and apprenticeship
requirements. Overall, CHP is a valuable technology that can
offer many benefits to facilities. By integrating CHP, processing facilities can demonstrate their efforts at reducing their
environmental impact, saving money on energy costs, and
improving their operational resilience.
PTQ Q1 2024
17
08/12/2023 14:59:52
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Our proprietary chemistries dissolve and stabilize any asphaltenic/paraffinic/polymeric deposits, by transforming the same into a fully
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When applied to tank cleaning, our technologies effectively, safely and quickly recover oil from sludge, thereby eliminating waste generation
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Pro-active application of our cleaning technologies reduces CO2 , VOCs and greenhouse gas emissions, while reducing energy consumption
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ITW proprietary technologies promote safe working, as they eliminate/reduce mechanical cleaning operations as well as working in confined
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itw.indd 1
09/09/2022 11:49:53
Filtration and separation for industrial
carbon capture, transport, and storage
Novel filtration and separation products and a deep understanding of material science
and fluid contamination characteristics are needed to reduce the Opex of carbon capture
Lara Heberle and Julien Plumail
Pall Corporation
I
n addition to electrification, hydrogen, and other clean
energy technologies, large-scale carbon capture, utilisation, and storage (CCUS) is critical to achieving netzero 2050 goals. These goals were set forward by the
International Energy Agency (IEA) in 2021 as a challenging path to restrict global temperature rise to 1.5°C. One
of the key aspects of the plan is to limit emissions from
point-source industrial emitters that produce elevated levels of CO₂, which are often hard to abate. These industries
include cement, lime, steel, and aluminum production, bioenergy, refineries, chemicals, natural gas and coal power
plants, pulp and paper, and waste-to-energy.1
Looking at the carbon capture value chain, there are a
range of technologies at widely varying technical readiness
levels (TRL). The most mature carbon capture technology,
which is currently used in most industrial carbon capture
installations, is chemical absorption, where a solvent selectively binds with the CO₂ in one column called the absorber
and regenerates in a secondary regenerator column where
the CO₂ is released. Solvent-based absorption technology
is well known and has been used extensively in natural gas
treating plants such as in amine sweetening processes.
Other carbon capture technologies at lower TRLs include
physical absorption, adsorbents, oxyfuel combustion, cryogenics, calcium or chemical looping, and membranes.
Once CO₂ is captured, it is typically dehydrated, compressed into a dense or supercritical phase for easier transport, then transported via pipeline or ship. It can be utilised
in material production, enhanced oil recovery, or other processes or stored in depleted reservoirs or saline formations.
Treated gas
CO2 to
compression
Condenser
3
Water wash
loop
Carbon
bed
Reflux drum
Cooler
5
Feed gas
1
4
Stripper
4
2
Heat
exchanger
Cooler
Absorber
Reboiler
Rich solvent
Lean solvent
Figure 1 Pretreatment and solvent-based capture filtration and separation needs
Filtration and separation recommendations for select process locations in Figure 1
#
Need
Driver
1
Particulate removal from dry gas feeds
Protect equipment, prevent solvent loss
2
Remove contaminants on inlet gas
Protect equipment, prevent solvent loss
3
Prevent amine carry-over on absorber outlet
Meet environmental specs, prevent solvent loss
4
Remove solid contaminants from solvent loop
Prevent fouling of critical equipment
5
Prevent activated carbon fine carry-over in solvent loop
Prevent fouling of critical equipment
Separation solution
Low ΔP flue gas filter
Low ΔP aerosol removal
Low ΔP aerosol removal
Absolute-rated particulate
filter
Absolute-rated particulate
filter
Table 1
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PALL.indd 19
PTQ Q1 2024
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08/12/2023 15:02:19
Compressor
stages (high-P)
5
Dehydration
stages
Compressor
stages (low-P)
CO2 gas
Cooler
Regenerator
2
8–9
3
4
1
2
3
Glycol
contactor
Heat
exchanger
Rich glycol
Reboiler
Lean glycol
Displaced H2O
Reservoir
7
6
Reservoir
Dense phase
(supercritical)
CO2
CO2
transport,
pipeline
Dense phase
(supercritical) CO2
CO2 storage
Figure 2 Downstream compression, dehydration, and storage filtration and separation needs
Which capture technologies are favourable highly
depends on process economics, often cited in units of $/ton
CO₂. Because CO₂ does not have an intrinsic value, installations are driven by credits and regulations. This drives the
industry to seek the lowest expense-proven solution and
actively pursue technologies that offer cost reduction and
increased equipment lifetime.
Solving the contaminant challenge
In the critical-to-decarbonise industrial sectors, CO₂ is
typically captured after a combustion process. Therefore,
flue gas feed streams entering CO₂ capture processes can
contain an elevated level of combustion byproduct contaminants. These feed contaminants can increase process
operating expenses by (1) increasing the need for water
replacement in wash systems and direct contact coolers, (2)
increasing the frequency of solvent, membrane, or adsorbent replacement, (3) for solvent-based processes, causing
amine emissions in the flue gas outlet from the absorber,
and (4) fouling critical process equipment such as heat
exchangers, reboilers, compressors, and absorber internals, thereby reducing process efficiency, increasing energy
requirements, and requiring more frequent maintenance.
Additionally, contaminants can be generated during the
carbon capture process. For instance, corrosion byproducts, solvent degradation compounds, and heat-stable
salts can build up over time in solvent loops. Similarly,
in downstream process steps, lube oil and solid contaminants can be introduced into the concentrated CO₂
stream. These contaminants also increase operating
expenses by contaminating successive stages of equipment, leading to off-specification pipeline contents, and
can plug reservoirs.
For each of these problems related to contaminants,
reliable filtration and separation steps are critical to maintaining low operating expenses. Filtration and separation
products for solvent clean-up are well known due to decades of experience with gas treatment. However, other
applications, such as feed treatment before CO₂ capture
processes, solvent emission prevention, and downstream,
including dense-phase CO₂ purification are less known,
emerging applications in this sector. Pall applications in
solvent clean-up, feed treatment, and solvent emission
prevention are shown in Figure 1, with detail in Table 1.
Applications downstream and in dense-phase CO₂ purification are shown in Figure 2, with details in Table 2.
Filtration and separation recommendations for select process locations in Figure 2
#
1
2
Need
Driver
Remove solids and liquids on inlet
Compressor protection
Remove solid contaminants from lube oil
Keep lube oil clean, reduce compressor
component wear
3
Compressor vent
Prevent compressor cavitation
(depends on compressor)
4
Prevent lube oil carry-over to TEG
Keep TEG/dehydration loop process
dehydration loop
efficiency high
5
Remove solvent carry-over
Protect downstream compressor
6
Remove contaminants from supercritical CO₂
Prevent reservoir fouling
7
Remove contaminants from displaced water
Prevent reservoir fouling
8-9 See applications 4-5 in solvent carbon capture, Figure 1.
Separation solution
Liquid-gas coalescer
Particulate filter or vacuum purifier Vent filter, also called a ‘breather’
Liquid-gas coalescer
Liquid-gas coalescer
Absolute-rated particulate filter
Absolute-rated particulate filter
Table 2
20
PALL.indd 20
PTQ Q1 2024
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08/12/2023 15:02:20
Solvent purification
With a solvent-based CO₂ capture process, the process
efficiency and operating expenses of the entire unit hinge
on the cleanliness of the solvent and equipment.
On a positive note, recommended filtration and separation steps are well-studied due to the longevity of these
processes in gas processing plants.
Solid feed contaminants such as fine fly ash particulates
(as small as <1 µm diameter) that can bypass feed pretreatment steps due to their small size can build up and foul the
lean/rich heat exchanger, the reboiler, the absorber internals
and require more frequent solvent change-out over time.
Contaminants can also alter the surface tension of the solvent, causing an increased tendency to foam and increased
foam stability, requiring the use of anti-foam. Finally, fine
particulates can form aerosol nuclei, which contribute to
solvent emissions, resulting in solvent losses out of the
absorber vent, as found from tests at the post-combustion
carbon capture plant at Niederaussem.² Corrosion products
from stainless steel and similar equipment can also precipitate in the rich side of the solvent loop into solid particulates such as iron compounds, causing similar issues.
To remove these solids, particulate filtration of the solvent is recommended at a minimum of 10% slipstream. The
target level for solids after filtration is 1-5 ppmw. Five or
10 µm-rated absolute particle filters are recommended,
based on the diameter of the solid particulates.
It is important to understand the differences between
how particulate filters are rated. Nominal ratings are arbitrarily assigned by the filter manufacturer, and there is no
regulation for the value of the nominal ratings to indicate
the performance of removing certain particle sizes. In contrast, absolute particle filter ratings must meet rigorous
‘ISO or ASTM’ standards. The absolute rating of a particle
filter directly corresponds to the largest diameter of particle
that the filter will allow through – all larger particulates will
be captured. An example of the difference between solvent
cleanliness after using no filter, a nominally rated filter, and
an absolute-rated filter is shown in Figure 3.
Rich side filtration is commonly recommended to remove
precipitated corrosion like iron sulphide and to protect the
lean/rich heat exchanger. Significant improvements in the
removal of solvent contaminants have been demonstrated
using Pall absolute-rated filters, with extensive data proving the removal of precipitated corrosion products and process equipment protection from the gas treating industry.³
Lean filters can also be added to the process scheme to
prevent fine particulates from entering the absorber. Lean
filtration is particularly recommended for polishing and
removing adsorbent fines if there is a carbon bed on the
lean solvent side.
Carbon beds are often installed to remove solvent degradation products and have been found to remove some
metal ions. Degradation products such as organic acids,
formed by the solvent degrading through oxidative and
thermal mechanisms, can be corrosive, cause foaming,
solvent losses, and reduced absorber capacity. Metals are
common from internal metallurgy and can catalyse amine
degradation. Not all activated carbon targets the same
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PALL.indd 21
contaminants, so the product must be selected carefully to
ensure that it does not prematurely plug.
Other concerns in the solvent loop include heat-stable
salts, which are produced when amines react with acidic
components such as O₂, CO, and SO₂. Concerns with heatstable salts are that they render the amine inactive and can
make the solution corrosive if allowed to reach a level above
3%. Ion exchange techniques are commonly recommended
for treating heat-stable salts.
Finally, there is increasing concern about nitramines and
nitrosamines in the carbon capture industry due to their
nature as a potential carcinogen. These compounds are
produced from NOx in the flue gas reacting with amines.
Water wash prevents nitramines and nitrosamines from
venting out of the absorber, but they must still be removed
from the water wash before disposal to avoid environmental contamination. Processes to remove nitrosamines and
nitramines, such as selective catalytic reduction (SCR) for
NOx removal and use of activated carbon, are ongoing
areas of study to ensure that these compounds remain
below desired levels.⁴
Flue gas pretreatment
The top three contaminants commonly present in post-combustion flue gas are NOx, SOx, and particulates such as fly
ash. All three of these contaminants should be removed
prior to CO₂ capture, regardless of the capture technology used. NOx levels are reduced in the pretreatment step
before the absorber with a selective catalytic reduction
process (SCR); SOx levels are also reduced during pretreatment with a wet or dry scrubbing process.
Particle filtration is commonly employed in pretreatment
steps with cyclones, electrostatic precipitators, and bag
filters. Cyclones use rotation to separate solids but have
difficulty removing small particulates. Electrostatic precipitators (ESPs) remove fine particulates by applying an
electric charge but can be expensive and associated with
an increased safety risk. Furthermore, wet ESPs have been
found to break up large contaminants, increasing the total
number of contaminants in some cases. Finally, bag filters
can be temperature-limited due to the use of polymeric
material. They can have a shorter lifetime and lower particulate removal efficiency when compared to absolute-rated
filters with inorganic (metallic or ceramic) filter media.
One key requirement of filtration pretreatment is that it
operates at a low pressure drop due both to the excessive
Figure 3 Amine cleanliness after no filtration, nominal
filtration, and absolute filtration
PTQ Q1 2024
21
08/12/2023 15:02:21
Clean gas pipe
Blowback valves
Module
Clean gas chamber
Filter module
Dust hopper
Figure 4 Fine fly ash
present in flue gas feed to Figure 5 Low pressure drop filtration testing. Left: test stand setup. Right: filter inlet
a carbon capture process following tests. Fine particulate contaminants are visible on the face plate
costs of compressing large gas flows and near-atmospheric process conditions of flue gas feed to CO₂ capture
processes. Low pressure drop filtration systems are often
large, making their integration into existing plants a potential challenge in terms of space constraints. They also do
not always capture fine (<1 µm) particulates present in
industrial flue gases, such as those shown in Figure 4.
Pall has recently developed a new low pressure drop particulate filter to address this application. The system and
overall operation are based on decades of experience with
Blowback filter technology, where particle contaminants
build up on the feed side of a filter. After a period, caked
contaminants are ejected off the filter for collection or disposal at automated intervals via a short gas pulse in the
reverse direction. Filters regenerate at separate times, such
that most of the filters in the system provide continuous
operation and filtration. Through regeneration, filters maintain a long on-stream service life, and the pressure drop
after solids are blown off reaches an equilibrium point.
Blowback filter cartridges were conventionally cylindrically shaped and made from inorganic materials such
as metals or ceramics to withstand harsh process conditions and offer fine filtration ratings with good reliability.
However, to achieve an extremely low pressure drop with
an order of magnitude in the 10s of millibar, as requested
by the CCUS industry, conventional blowback technology
would need to be oversized and thus would not have been
an economical solution and would have been challenging to
fit into brownfield industrial plants.
This new product development leverages recent
advances in additive manufacturing (AM) to produce a
remarkably high surface area filter element with minimal
manual manufacturing, enabling bulk production of filters
at a given time. The high surface area ensures a small filter
system footprint to handle a given flow rate and pressure
drop (down to <20% the size compared to the conventional
product and similar alternatives), which directly translates
to reduced infrastructure needs and production costs.
The new filter design was optimised through iterations of
advanced computational fluid dynamics (CFD) modelling,
coupled with rapid 3D printing prototypes that were tested
at a lab scale with representative test dust and varied blowback cycle time to regenerate the filter. Larger bench-scale
tests depicted in Figure 5 with multiple elements were
performed internally at Pall and offer impressive results.
The pressure drop across the filters for the duration of
22
PALL.indd 22
PTQ Q1 2024
the tests is kept between 20-30 mbar, with an estimated
pressure drop below 60 mbar for full-scale installations,
which include piping and valves. Solid loading in the gas
feed varied above 1 g/Nm³, with exceptionally low downstream solid loading after filtration – well below 1 mg/Nm³.
Removal efficiency is above 99%, even for sub-micron particulates down to a 0.5 µm diameter and below. The next
steps are to continue to prove performance at increasing
scales.
Emission prevention
Aerosol emission management has been another major
focus of carbon capture technology providers. In solvent-based carbon capture technology, SOx and fine
(<1 µm) flue gas feed particulates are responsible for most
of the solvent losses out of the vent, which have been found
to reach more than 1,000 mg/Nm³. In contrast, desired
levels are typically as low as possible to minimise solvent
losses and environmental impacts, well below 10 mg/Nm³.
A water wash mounted on the top of the absorber unit
limits gas-phase solvent emissions, but particulates and
SOx, which form H₂SO₄ aerosols, serve as sub-micron
diameter droplet nuclei. Droplet nuclei can then grow to
larger micron-sized droplets as they travel through the
water wash section.
In this application, like flue gas pretreatment requirements, there is an extremely low pressure drop (<20 mbar,
as an example) available due to pressure conditions near
atmospheric. Again, Pall is developing a product to uniquely
meet the low-pressure requirements, while removing fine
aerosols with an exceedingly high-efficiency (>99% aerosol
removal) separator, producing well below 1 ppmw downstream and also providing a minimal footprint. The unique
ability of this separator to meet high-efficiency removal
requirements and a low desired pressure drop is a result
of the material science used in its fabrication and in-house
technical expertise. The product design allows liquid to
drain off quickly and easily, similar to the industry-proven
high-efficiency liquid-gas coalescers shown in Figure 6.
Downstream purification and dense phase CO₂
After CO₂ has been captured, it is dehydrated and compressed to a high pressure for transport and storage. After
dehydration and compression, CO₂ reaches a high-pressure ‘supercritical’ or ‘dense phase’ state, with a high density nearing that of a liquid and a viscosity nearing that of
www.digitalrefining.com
08/12/2023 15:02:22
a gas. Converting CO₂ to a dense phase enables the use of
smaller pipelines and increases the amount of CO₂ that can
be stored in reservoirs.
In downstream applications, lube oil can become contaminated through compressor wear, requiring filtration. It can
also be carried over after the compressors, which can cause
the CO₂ to become off-specification. Similarly, dehydration
processes such as adsorbent-based dryers or glycol loops
can require filtration and liquid/gas coalescence to prevent
fouling of dryers and absorption loops, and to prevent
carry- over of fines or glycol contaminants.
After compression and dehydration stages, undesired
contaminants such as water, lube oil, oxygen, and H₂S can
be present in the CO₂, which pose a threat to the integrity
of the pipelines. Hydrogen sulphide and oxygen are corrosive, damaging the pipelines and, in the worst case, causing
cracks. Trace water can react with CO₂, forming corrosive
byproducts, and can also form hydrates, which produce
pipeline blockages.
As pipelines deteriorate, solid corrosion products and pipe
scale formed through these reactions can be carried downstream, plugging critical equipment needed for carbon capture storage, such as control valves, metering stations, and
high-pressure injection pumps. This increases maintenance
costs and can require equipment replacement or unscheduled downtime. Solid contaminants can also plug permeable storage reservoir pore structures, requiring increased
energy for CO₂ injection and even limiting the amount of
available and accessible reservoir storage capacity.
In selecting filters and separators for dense phase CO₂
applications, substantial care must be taken on which materials are used, how filter sizing is performed, and what the
filtration rating is. To fully protect reservoirs, the filter rating
must be selected based on the reservoir permeability and
approximate pore diameter. Regarding material choice, safe
operation favours corrosion-resistant metallic materials or
CO₂-stable plastics. Plastics must be carefully selected, as
some materials may swell under contact with supercritical
CO₂. Additionally, some polymers can mechanically fail by
explosive decompression if there is a rapid pressure drop
during upset conditions or routine maintenance after CO₂
has adsorbed and diffused into the polymer due to highpressure operation.
Conclusions
Filtration and separation applications in solvent-based
absorptive carbon capture are well-known from decades of
gas processing technology with amine solvents. However,
there are emerging requirements specific to carbon capture,
such as low available pressure drops in pretreatment and
high pressures in downstream CO₂ transport and storage.
These requirements mean that new filters and separators
tailored to the applications outlined in this article, as well
as expert knowledge in material and product selection, are
needed. By choosing the right purification product with the
right material compatible with the application, both capital
and operating expenses can be minimised by protecting
critical equipment, meeting environmental specifications
on contaminant levels, and keeping process efficiency high.
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PALL.indd 23
Gas out
Gas in
Water in
Figure 6 Pall high-efficiency liquid-gas coalescer
Acknowledgements
Special thanks to Olivier Trifilieff, Ali Arshad, Joe Youberg, and Keith
Webb for their contributions and review of this article.
References
1 IEA, Transforming Industry through CCUS, 2019, www.iea.org/
reports/transforming-industry-through-ccus.
2 Moser et al, Solid particles as nuclei for aerosol formation and cause
of emissions – Results from the post-combustion capture pilot plant
at Niederaussem, 13th International Conference on Greenhouse Gas
Control Technologies, Lausanne, Switzerland, 2016.
3 Raymond A, Levesque F, Lakhani H, Separations technologies
to improve amine system reliability: A case study. Pall Corporation
Scientific & Technical Report FCASRCSENa, 2008.
4 Mazari et al, Formation and Elimination of nitrosamines and nitramines
in freshwaters involved in post-combustion carbon capture process.
Journal of Environmental Chemical Engineering, Vol 7, Issue 3, 2019.
Lara Heberle is the Global Technology Development Manager for
Carbon Capture, Utilization, and Storage at Pall Corporation. She
holds a BSc in engineering physics and mechanical engineering from
the University of British Columbia, and a Doctorate in mechanical
engineering, with a focus on fluid dynamics and a minor in thermal
sciences from Cornell University. Email: [email protected]
Julien Plumail is the Global Vertical Marketing Manager for Carbon
Capture, Utilization, and Storage at Pall Corporation. He holds an MSc
in engineering from the French Petroleum Institute, and an MBA from
IESEG. Email: julien_plumail@ pall.com
PTQ Q1 2024
23
08/12/2023 15:02:24
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12/12/2022 14:23:23
Overcoming wastewater challenges
of opportunity crude processing
Refinery wastewater facilities need new practices and solutions for efficient and
sustainable operation with heavy opportunity crudes
Shane Lund
Veolia Water Technologies & Solutions
T
he challenges associated with processing opportunity crudes have been well-documented over recent
years. Their high content of small, suspended solids,
tramp amines, asphaltenes, naphthenic acids, and many
other problematic substances combined with high variability can make these crudes difficult to treat from beginning
to end in a refinery. Increased difficulty desalting these
crudes can lead to brine effluent heavily contaminated with
hydrocarbons sent to the wastewater treatment plant. Even
when the desalting operation is working well, the increased
loading can overwhelm some wastewater plants, forcing
production to be curtailed.
When faced with this higher loading, many wastewater
assets can become overburdened and more likely to push
past the breaking point into upset conditions. Symptoms
of these upset conditions can include foaming, poor sludge
settling and compaction, internal or external toxicity,
reduced nitrification rates, and reduced chemical oxygen
demand (COD) removal.
Identification and treatment of the symptoms and root
causes are important to maintain compliance with increasingly tight water discharge limits. This article discusses common wastewater management problems associated with
processing opportunity crudes, holistic monitoring strategies
to identify potential upsets early, and operation strategies
and treatment techniques used to maintain effluent discharge
compliance while processing opportunity crudes reliably.
Opportunity crude contaminants
The blending of tight oils and heavy ‘opportunity’ crude oils
is now a common practice for many industry players. This
practice certainly benefits operators by sourcing crudes
based on availability and price. However, it does present
a risk to the performance and reliability of the various process units within the refinery. The resulting blend sent to
the crude unit can exhibit less-than-ideal properties that
vary daily, even hourly, making it very hard to maintain the
unit’s production quality.
Increased use of ‘opportunity’ crudes has been shown to
create challenging conditions in wastewater treatment as
the crude unit struggles to separate water and oil efficiently.
Working upstream by optimising crude blending strategies
and desalter operations should certainly be part of a holistic
www.digitalrefining.com
VEOLIA.indd 25
plan to manage heavy crudes. However, conditions should
also be in place downstream to address potential desalter
upsets. If a comprehensive plan to prevent and address
wastewater systems’ contaminations and upsets is not put
into place, there is a real risk that production may need to
be curtailed as contaminants in the effluent discharge get
too close to allowable limits.
Much has been written about the connection between
opportunity crudes and wastewater difficulties, such as
foaming, poor sludge settling and compaction, internal or
external toxicity, reduced nitrification rates, and reduced
COD removal. Problematic features associated with the
opportunity crudes that have been blamed for the wastewater difficulties include increased quantity of solids that
are smaller in size, increased amine loading, more naphthenic acids, and high variability in the crudes.
The use of opportunity crudes in a refinery’s crude
diet is expected to lead to a higher potential for desalter
upsets due to variability, emulsions, pH, viscosity, stability,
and asphaltene precipitation. These contaminations and
fluctuations would provoke more frequent primary wastewater treatment problems as the desalter effluent brine
undercarries process compounds such as asphaltenes,
small, suspended solids and oil, all in variable quantities.
In the secondary wastewater system, we expect to see
potential problems due to elevated biochemical oxygen
demand (BOD) and COD, elevated levels of both long- and
short-chain organic acids, more tramp amines, higher surfactant loads, and inhibitory substances.
While it is true that any one of these properties can detrimentally impact wastewater treatment, a single bad actor
is not usually identified, as multiple parameters typically act
together during an upset event. These combined properties
push refinery wastewater treatment assets ever closer to
the edge, and contingency plans cannot contain these conditions indefinitely.
Each refinery wastewater treatment plant has its own
unique set of potential constraints based on its system’s
design and level of contingencies. However, the lack of a plan
to predict and address upsets takes the system ever closer
to the breaking point. Once the breaking point is hit, several
things can occur, including foaming of aeration basins and
clarifiers, floating solids on clarifiers, poor sludge settling and
PTQ Q1 2024
25
08/12/2023 15:15:35
compaction, internal and external toxicity, reduced nitrification rates, and reduced COD removal rates.
Holistic monitoring
Predicting and addressing stressed conditions on a complex and dynamic system such as a refinery’s wastewater
plant requires the implementation of a holistic monitoring
strategy. The strategy should prioritise areas found to be
most vulnerable for a given system, which should not be
assumed to be the same as another wastewater system.
For example, a wastewater system with limited secondary
system capacity may need to focus on ensuring fast COD
oxidation and rapid settling sludge, which may need to be
enhanced with bioaugmentation and chemical aids. Closely
monitoring the bioaugmentation and chemical systems will
be important in this case. A system with adequate secondary
system capacity but limited primary system capacity may be
better served by honing in on monitoring for source control,
primary chemical treatment programmes, and optimisation
of the primary system. Once vulnerabilities are understood,
set up a programme to monitor each wastewater asset.
Some typical monitored parameters are found in Table 1.
Monitoring of primary treatment operations should
include, at minimum, oil and grease (O&G), total suspended
solids (TSS), COD, and turbidity. In addition to the influent
and effluent of the primary treatment assets, other streams
that should be monitored are specific influent streams
(desalter brine), equalisation systems, API systems, floatation, and clarifier systems.
Secondary biological treatment is the heart of most
complex wastewater treatment plants, so a holistic monitoring programme becomes ever more important as to the
sensitivity and criticality of the process. Standard chemical tests combined with dissolved oxygen uptake (DOUR),
microscopy, and advanced tools such as Veolia’s BioHealth
Adenosine Triphosphate (ATP) can provide unique insights
to better understand the condition of the secondary system’s biology ahead of performance showing decline.
BioHealth DNA genomics testing can also help detect shifts
in the microbiome due to changes in food source or other
stressors, enabling better long-term process decisions.
Because BioHealth ATP testing considers multiple intrant
factors to simulate the impact on the secondary treatment
biomass, it can provide earlier detection of potential upset
conditions than other monitoring tools. Key output information includes Biological Stress Index (BSI), Active Biomass
Ratio (ABR), Active Volatile Suspended Solids (AVSS), and
True Food to Mass ratio (True F:M).
BSI provides the ratio of ATP released from deteriorating
cell membranes compared to the total quantity of ATP in a
sample, which is a good indicator that inhibitory conditions
are present. This allows operators to make smart decisions
when considering discretionary loads and can help direct
efforts in searching upstream for problematic flows and
detrimental environmental conditions such as elevated
temperature.
ABR informs us how much of the system mass is actively
doing the job of reducing contaminants. This information
can help optimise plant operation and reduce excess energy
consumption as it can be used to reduce the quantity of
inert solids safely.
AVSS gives the concentration of living biomass in the
system. Each system has a specific range of AVSS that
provides optimal performance, so once this optimal range
is understood, deviation from the optimum should drive
process control adjustments. AVSS can also be used to
calculate food to mass (F:M) ratio. Traditional F:M includes
comparing the mass of BOD to the mass of Mixed Liquor
Suspended Solids (MLVSS), but replacing the MLVSS with
AVSS provides more accurate information based on the
amount of biomass that consumes nutrients.
Monitoring the final stage of solids separation following
the primary and secondary treatments is also needed to
ensure a consistent operation that does not suffer poor effluent quality. Clarifiers, which are most commonly used for
removing remaining suspended solids, require a minimum
daily record of settling rates, bed depths, solids concentrations, and overflow quality in order to adjust and optimise
effluent quality.
Operation strategy
Data collected from the monitoring programme at the various stages of the wastewater treatment process is key
to making process control decisions. However, the basics
should not be neglected, which apply no matter what the
crude diet. The basics include:
 Understanding your plant’s specific vulnerabilities
 Understanding problematic substances from each process
stream and avoid shock loads to these streams
Communicating frequently with process units

Some typical monitored parameters when setting up a
 Maintaining all equipment (maintenance freprogramme to monitor each wastewater asset
quency needs to increase with extra loading)
Primary effluent
Bio-reactor
Clarifier
 Optimising all primary treatment assets to
Flow
MLSS, MLVSS, AVSS
Bed depth
remove as much insoluble matter as possible to
pH
BioHealth ABR & BSI
SSV₅, SSV₃₀, SVI
protect downstream biomass
TOC, COD, BOD
DO
RAS flow
 Optimising secondary treatment by giving the
TN, NH₃
DOUR, SOUR
RAS TSS
biomass a healthy living environment free from
TSS
F:M ratio
WAS flow
fast changes
Oil & grease
pH
WAS TSS
 Optimising clarification/solids separation.
Metals
Temperature
Visual – scum, overflow
Primary treatment systems’ data should lead
Known toxins
Microscopy
Turbidity
to operational decisions to prevent the process
Alkalinity
Biohealth DNA
Regulated parameters
from becoming overloaded with excess solids and
Table 1
hydrocarbons associated with varying crudes’
26
VEOLIA.indd 26
PTQ Q1 2024
www.digitalrefining.com
08/12/2023 15:15:35
diets. These may include adjust- and primary treatment optimisation are
DIBconveyor
performance
ments to skimming rates,
keycomparison
to reducing shock loads.
speeds, solids loading rates, and gasWhen controlling the secondary
Operating ratios.
parameter
Pre-optimisation
to-solids
With higher loads
system, choose aPost-optimisation
method, such as conFeed point
#21 tray
#9 tray
that may include more emulsion, and stant sludge age, constant
MLSS, or
Feed rate, b/d
Base
+ ∆ 15%
more
smaller
solids
(more
net
surface
constant
F:M
and
stick
with
it.
However,
Feed temperature, ºF
Base
Base
area
and
more
net
negative
charge),
new
conditions
may
warrant
a new
Reflux temperature, ºF
Base
- ∆ 1.3ºF
chemical
treatment
programmes may Base
approach. For example,
Reflux ratio,
volume basis
- ∆ 5%if a 25-day
require
adjustment.
sludge historically provided optimum
Side reboiler
unit steam
consumption,
lb steam/bbl
+ ∆ 9%and associNot only the
dosage feed
but also the Base
results, new crude slates
choice
coagulants
and flocculants ated contaminant loading may warrant
Bottomof
reboiler
unit steam
consumption,
steam/bbl so
feedthe chem- Base
∆ 7% even notice
may
require lb
changes,
a 30-day sludge age.-Some
ical
systems
a ‘seasonal’ sludge- ∆age
approach is
RVPinjection
of the bottom
product,and
psia controls Base
1.2 psi
should allow for easy adjustments and needed based on ‘crude seasons’.
replacement.
In some cases, online
The goal of secondary treatment is
Table
2
monitoring of parameters such as to remove all contaminants via bacturbidity,traffic
TSS, would
or totalbeorganic
teria that
them,
form
floc
column
fulfilledcarto duties
are metabolise
also stabilised
at the
target
bon (TOC)
the DIB
clearfeed
advantage
of performances.
and then settle out in clarifiers or are
achieve
thehas
target
rate and
allowing
for real-time automation of removed through filtration methods.
RVP
value.
the chemical programme at the pri- Summary
This should leave clear, contamimary
treatment.
This
can
significantly
nant-freeimpacts
water distillation
dischargedunit
in perthe
Case study 2: Post-optimisation
Fouling
reduce
the
variability
of
this
stage’s
overflow.
Increased
organic
loading
performance
formance/run length adversely. It is
effluent andtohelp
stabiliseresults,
secondary
associateddifficult
with opportunity
According
evaluation
the extremely
to resolve thecrudes
foultreatment
operation.
could
push
clarifier
solids
loading
outDIB feed point was relocated from tray ing problem without
unit
outages.
Astoopportunity
side of theiridentifying
operating limits.
#21
tray #9. The crudes’
number challenging
of stripping However,
non-optimum
naturewas
oftenincreased
leads to by
more
par- parameters
If clarifiers and
become
a pinch
point,
trays
11.fine
Bottom
building
pertinent
ticles
and
higher
levels
of
emulsions
the
chemical
programme
should
be
reboiler duty was maintained at the optimisation strategies can enhance
in
the
process
wastewater
streams,
optimised
to
encourage
faster
setmaximum duty available, and the side distillation unit performances and
source control
andincreased
source treatment
tling. Routine
bioaugmentation, which
reboiler
duty was
to meet avoid
unit outages.
of
these
various
streams
can
facilconsists
of
the
addition of specialty
the required total reboiler duty and taritate
overall
wastewater
operation
bacteria
populations
to the secondary
get DIB bottom temperature. A major Acknowledgements
and
prevent
more
general
upsets.
For
treatment’s
biomass,
helpofimprove
version
a presbenefit of the optimisation is that these The article is an updatedcan
example, were
desalter
brine accomplished
streams may entation
organicsgiven
removal
and optimise
solids
at AIChE
Spring Meeting,
changes
simply
be treated
separately
they are Kister
settling
characteristics.
Coagulants
Distillation
Symposium, March
13-16,
while
the unit
remainedwhen
in service.
affected
contaminants
and flocculants
may also be required,
in Houston TX.
Anotherbytest
run after theassociated
optimisa- 2023,
with
heavy
crudes,
and
further
treateven
if
not
necessary
when operating
tion was arranged to verify the perment
of
specific
components
of
the
on
a
more
traditional
and
stable crude
formance enhancement. The pre- and References
brine
stream
may
make
sense
in
some
diet,
to
consistently
meet
desired
T, California
post-optimisation test run data are 1 Kister H, Hanson D, Morrisonthe
circumstances.
effluent
quality.
summarised and compared in Table 2. Refiner Identify Crude Tower Instability Using
To target
improve
effluent
quality,
The
DIB
feed treatment
rate and RVP
of Root Cause Analysis, AIChE Spring Meeting,
In case
of2001.
upset, listen to the data
ensure
all assets
arewere
properly
cleaned April
22-26,
the
bottom
product
met. Column
keeping
critical
wasteand maintained,
as more
means 2Even
Kisterwhile
H, Distillation
Design,
McGraw-Hill
fractionation
was
evensolids
enhanced
Company,
1992.
water
assets
in
top
condition,
commore
chance
of
settling
and
fouling,
despite a lower reflux ratio. These
3
Lee S H, Balanced
distillation
equipment
municating
frequently
with
process
resulting
in
reduced
volumes
and
performance enhancements were
Q1 2017.from head to tail,
units, PTQ,
monitoring
reduced efficiency.
Byoutages.
reducing avail- design,
acquired
without unit
4
Hanson
D, Leeoperating
S H, Reducing
FCC main
and
adjusting
strategies
to
able
tank
volume,
solids
accumulation
As the optimisation moves were
fractionator
operating wastewater
risks, PTQ, Q1 2021.
the
‘new
normal’,
upsets
reduces
equalisation
capacity,
and
implemented with fouled column con5
D, Piping
Result cirin
doHanson
still happen
due Circuits
to extreme
reaction further
time for fouling
the treatment
ditions,
could chemerode
Distillation
Column
Underperformance,
cumstances. Even the best-run plants
istry, so
a regular cleaning
programme
these
performance
enhancements.
To
Fractionation
Research
Institute
have experienced
upsets
due to Annual
unexcan present
a significant
benefit.
ensure
performance
improvements
on
Meeting Experts Panel, May 4, 2022.
pected
crude
incompatibility,
extreme
Secondary
treatment
systems
do
a long-term basis, post-optimisation
not suffer as much
presence weather, power outages, or other
performances
havefrom
beenthemonitored
Soun Ho Lee is the Subject Matter Expert
of
contaminants
as
the
speed
at which uncontrollable circumstances.
for more than two years. Operating
for fractionation and separation with Valero
The stress of upset conditions can
these new
andan
adverse
conditions
trends
show
enhanced
DIB presfeed Energy
Corporation in San Antonio, Texas.
lead
decision-making by
ent
themselves.
The
biological
wasterate and the RVP of the bottom prod- He istoinemotional
the Strategic Technology and
operation,
and
the
loudest voice in the
water
system
is
amazingly
resilient
if
uct are well maintained. There has Development group, overseeing
large proroom often gets the most attention; be
shocksno
aresign
avoided
and the microbes
been
of downgraded
per- jects
and advanced optimisation and troublesure theinloudest
voice is your monitorhave adequate
timethan
to two
acclimate.
formance
for more
years shooting
fractionation.
ing
data.
Source
control,
adequate
equalisation,
of operation. Rebalanced reboiler Email: [email protected]
www.digitalrefining.com
www.digitalrefining.com
VEOLIA.indd 27
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PTQ Q4
Q1 2023
2024
PTQ
27
95
08/12/2023 15:15:35
13/09/2023 10:00:14
7.0
6.0
25
Decreasing ABR
5.0
20
4.0
15
3.0
Increasing stress
2.0
10
5
1.0
0.0
BSI & ABR (%)
Ammonia (mg/L)
30
Bioaugmentation programme started
0
Ammonia
10
20
Biomass Stress Index (BSI)
30
Active Biomass Ratio (ABR)
50
40
60
70
80
0
Days
Figure 1 Refinery secondary wastewater treatment monitoring during upset
Step back. Review the data. Understand your specific
constraints and targets. Accept that more than one parameter may be responsible for the upset. Identify and correct
the root cause, along with secondary causes. Adjust based
on these insights and operating guidelines, and then be
patient while the system recovers.
Considering that biological systems recover slowly, often
taking two to three sludge ages for full recovery, implementing contingency measures to maintain acceptable discharge water quality may be required. These measures may
include supplemental coagulants, flocculants, antifoams,
bioaugmentation, flow reductions, and other measures.
Overcommunicate with production units during upset
conditions; failure in communication can lead to extended
recovery times if difficult wastewater loads are released from
production units when the wastewater plant is vulnerable.
Finally, never waste an upset: document more than you
think necessary to ensure all lessons are learned, leading to
new operating practices and optimised contingency plans.
Case study: Downtime averted for refinery wastewater treatment under severe stress
In this case example, a refinery wastewater influent was
characterised by high levels of organics and ammonia, with
frequent variations. While nitrifying bacteria are essential in
the secondary treatment to remove ammonia, high-stress
events saw their population being depleted. This caused
ammonia levels in the effluent to shoot up, and the refinery
had to curtail production to prevent potential environmental impacts and discharge permit exceedances.
The on-site Veolia team had been using the BioHealth
monitoring technology to assess the health of the biological
wastewater operation. When combined with the other data
collected by the site’s operators, this enabled the plant to
make optimal decisions regarding wastewater treatment
and process unit adjustments.
As shown in Figure 1, the BioHealth tests indicated the
BSI gradually increasing, with the ABR decreasing as the
challenging conditions worsened. The nitrification process
became unstable and completely inhibited as the bacteria
population degraded. The production rate was reduced to
ensure the plant’s effluent did not exceed regulations, so
the wastewater system needed to return to normal rapidly.
28
VEOLIA.indd 28
PTQ Q1 2024
With frequent communications of results between Veolia
and the operations team and continued monitoring, it was
decided to initiate a bioaugmentation programme. The
BioHealth technology was used to identify the proper contingency treatment and dosage for fast and efficient recuperation of the system.
While the typical response to a nitrification upset could
have taken one month or longer to recover, the data provided by BioHealth to detect the problem and help identify
the bioaugmentation solution allowed the plant to return
to normal operation within just six days. Throughout the
event, the operation team enacted the detailed monitoring
programme well, so the discharge quality always remained
in compliance.
Conclusion
Increased processing of opportunity crudes will likely continue as there are clear financial incentives for refiners to
include them in their crude diet. Even when trying to optimise crude blends and desalter operation, it is not always
practical or economical to prevent all contaminations in the
desalter brine effluent, and the wastewater treatment plant
should be equipped to handle these while respecting discharge quality limits.
For the refinery’s wastewater facility to operate efficiently
and sustainably when faced with the challenges attached
to these heavy crudes, new practices and solutions must
be implemented. Enhanced monitoring, data-driven decisions, and a good understanding of the treatment basics
combined with openness to apply these basic rules to new
conditions will reduce the frequency of wastewater upsets
and increase speed of recovery when they do occur. This
will enable the plant to maintain operation while consistently respecting discharge limits and regulations.
Shane Lund is a Senior Application Engineer at Veolia Water
Technologies & Solutions based in Minnesota. With more than 24 years
of water treatment experience, he provides technical and sales support. He has also co-authored several papers on biological wastewater
treatment systems in refineries and regularly makes presentations and
provides training on the topic. He has a BSc in biology from St. Cloud
State University and an Associate of Science in water technologies from
St. Cloud College.
www.digitalrefining.com
08/12/2023 15:15:37
valmet.indd 1
13/12/2022 14:34:33
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PTQ Q4 vega.indd 1
11/09/2023 14:20:05
Biofilm: A hidden threat
A new approach to the costly problem of biofilm formation in refinery and
petrochemical operations
Brian Martin Marathon Petroleum Corporation
Tim Duncan and Gordon Johnson Solenis LLC
R
efineries and petrochemical operations rely on
water-cooled heat exchangers in many areas of their
facilities. These heat exchangers provide the heat
removal from refining processes required for the production of various products and intermediates. The efficient
transfer of heat in these exchangers often determines
production rates. Fouling of the heat exchanger surfaces
or flow restriction resulting from biofilm, scale, or debris
may limit production and result in downtime for cleaning.
Additionally, corrosion of the heat exchangers because of
microbiological deposits may result in failures that require
downtime, maintenance, and capital expenses.
Expenses can run into millions of dollars, particularly if
they include unscheduled downtime and heat exchanger
replacement. Proper management of heat exchanger performance includes analysis of heat transfer data and understanding failure mechanisms. Data management tools can
assist in the development of preventative maintenance
guidelines and in the optimisation of chemical treatment
programmes that minimise these expenses. Many refineries and petrochemical plants struggle with heat exchanger
bundle failures and efficiency losses between turnarounds.
Inspections of failed bundles often reveal under deposit
corrosion (UDC) with biofilm as the culprit.
Traditional monitoring and control techniques
Warm cooling tower water containing microorganisms and
nutrients fosters ideal conditions for microbial growth and
biofilm formation. Microorganisms and nutrients enter the
cooling system through multiple paths. They enter the system in the make-up water – even though it may have been
treated for microorganisms, the treatment only renders
the water sanitary, not sterile. As the water flows over the
tower during the evaporation process, microorganisms and
nutrients enter the system through the scrubbing process.
Nutrients enter the cooling system from hydrocarbon leaks
on the process side of heat exchangers, and they enter
in the form of phosphate corrosion inhibitors applied to
protect the carbon steel piping and heat exchangers from
corrosion.
Figure 1 depicts various stages of biofilm formation on a
surface as microorganisms and nutrients continually inoculate the cooling water system. In the first stage, the cooling water transports these microorganisms to the surface.
In the second stage, the microorganisms begin to attach
themselves to the surface and within 20-30 minutes of
system inoculation begin colonisation. In the third stage,
because microorganisms reproduce through cell division at
a geometric rate, within one to two days significant growth
can occur.
Part of this growth involves the production of extracellular polymeric substances (EPS). The composition of
the EPS includes polysaccharides, proteins, extracellular
DNA (eDNA), and lipids. The EPS from various microorganisms interact with each other and form a slime matrix
that encompasses and protects the microorganisms. In the
fourth stage, within three days to three weeks, the thickness of the biofilm matures. In the fifth and final stage, at
maturation, detachment occurs because of turbulence or
ecological conditions. This detached biofilm can then populate other regions of the cooling water system.
Most microbiological control programmes using strong
oxidising biocides, such as bleach or chlorine gas, even
when used in combination with non-oxidising biocides,
can only control biofilm up to a point. The matrix formed
by the EPS encapsulates the microorganisms and provides
a level of protection from these biocides. The EPS creates
a demand for strong oxidisers, which generally cannot be
Stage 1
Stage 2
Stage 3
Stage 4
Stage 5
Conditioning layer
Bacterial attachment
Biofilm formation/
EPS production
Biofilm maturation
Detachment
Figure 1 Five stages of biofilm formation
www.digitalrefining.com
MARATHON SOLENIS.indd 31
PTQ Q1 2024
31
08/12/2023 15:56:44
90%
Biofilm
Heat transfer resistance
80%
CaSO4
70%
60%
50%
CaCO3
40%
30%
Al2O3
20%
10%
0%
20
2000
200
Fouling thickness (µm)
Figure 2 Thermal effect of biofilm and typical mineral scales
exceeded at typical dosages. Dosages that can exceed the
demand have a negative impact on the corrosion rates of
metal surfaces themselves and degrade dispersants that
are used to provide protection from inorganic deposition.
Non-oxidising biocides similarly have difficulty penetrating
the EPS’s protective slime matrix without reacting with the
EPS. Economics do not favour traditional approaches to
biofilm control.
Underappreciated and underestimated aspects of industrial cooling water treatment include the effect of biofilm
on heat transfer and the resultant heat exchanger failure
from microbiologically induced corrosion (MIC). As shown
in Figure 2, thinner biofilms, as compared with mineral
scale, exhibit a more severe resistance to heat transfer.
Microbiological fouling inhibits heat transfer up to four
times that of calcium carbonate fouling. Additionally, once
the biofilm exceeds 50 microns, approximately the thickness of adhesive tape, the resulting anaerobic conditions
support the growth of acid-producing bacteria. The acidic
waste products from anaerobic bacteria often aggressively
pit heat exchanger tubes and eventually cause leaks, requiring repair or replacement.
Traditional techniques for monitoring microbial growth and
biofilm formation cannot measure biofilm. Biofilm forms when
planktonic (free-floating) microorganisms begin to adhere on
surfaces, such as pipe walls, heat exchangers, and cooling
tower fill. Traditional approaches to monitoring microbial
activity include measuring halogen residuals, heterotrophic
plate counts, and adenosine triphosphate (ATP) levels in
the bulk water. Unfortunately, no correlation exists between
any of the results of these monitoring techniques and the
attached, sessile microorganism levels that cause biofilm.
Since traditional approaches to monitoring neither predict nor indicate biofilm, mechanical approaches have been
employed to monitor the efficiency of heat exchangers to
determine if biofilm fouling is present. However, detecting
biofilm by measuring heat exchanger approach temperatures, unfortunately, only indicates the presence of biofilm
after the fact. Similarly, flow studies only show restrictions
and loss of velocity after biofilm has formed.
New approach
Solenis’ proprietary ClearPoint biofilm detection and control
programme provides a new approach to the costly problem of biofilm fouling. This programme comprises three
components: a novel biofilm analyser, proprietary chlorine
stabiliser chemistry, and expert service. Employing the biofilm analyser, the programme provides early detection and
accurate measurement of biofilm growth in real-time. The
chlorine stabiliser chemistry is used to produce a patented,
in situ stabilised active chlorine solution. The solution significantly reduces microbiological activity without the adverse
side effects associated with strong oxidising biocides. Field
service personnel provide the expertise required to maintain clean and efficient heat exchangers.
The proprietary OnGuard 3B analyser uses a patented
ultrasonic sensor, shown in Figure 3, to accurately measure
the thickness of biofilm that accumulates on a heated target
assembly, shown in Figure 4. The sensor detects biofilm
with a measurement accuracy of approximately 10 μm and
at a resolution of ±5 μm. The analyser mimics critical heat
exchanger conditions in real-time by duplicating the shear
stress on a surface while also simulating the local surface
temperature to provide continuous fouling factor measurements that inform the adjustment of chemical feed when
Ultrasonic
pulse (p)
Ultrasonic
sensor
Heated
target
assembly
Reflection (r)
Time (p + r)
Biofilm growth
Figure 3 Working principle of the ultrasonic sensor
32
PTQ Q1 2024
MARATHON SOLENIS.indd 32
Figure 4 Heated target assembly showing presence of biofilm
www.digitalrefining.com
08/12/2023 15:56:46
required. The analyser can also differentiate between soft
deposits (organic and microbiological fouling) and hard
deposits (scaling). The early detection capability of the
analyser allows corrective actions to be taken before biofilm
can cause heat transfer loss or equipment damage.
The advanced chlorine stabiliser chemistry employed as
part of the biofilm detection and control programme is used
in combination with sodium hypochlorite to produce a patented, in situ stabilised active chlorine solution. The resulting
solution is not consumed when reacting with the EPS’s protective slime matrix, thereby allowing the solution to penetrate the biofilm, where it reacts only with the hydro-sulphur
and sulphur-sulphur bonds of the biological proteins on the
cell membrane and within the microorganisms. The in situ
stabilised active chlorine solution not only controls both
planktonic and sessile microorganisms but also removes
existing biofilm and inhibits biofilm regrowth. The solution
also effectively controls biofilms that harbour legionella.
The in situ stabilised active chlorine solution does not
increase the corrosion of metal substrate because of its
lower oxidation reduction potential (ORP). For the same
reasons, the solution does not degrade cooling water inorganic deposit inhibitors or react with other organics potentially present in the water. Thus, adsorbable organic halogen
(AOX) and trihalomethane (THM) production does not occur.
The lack of these reactions provides desirable environmental
and health advantages over strong oxidising biocides.
Unlike strong oxidising biocides, ammonia and amine
contamination in cooling water does not increase the
demand for the in situ stabilised active chlorine solution.
Additionally, the patented solution results in lower chloride
levels and reduced overall corrosivity of the cooling water.
Stainless steel, in particular, has a reduced risk of chlorideinduced stress cracking.
As a complement to the biofilm detection and control
programme, the Solenis HexEval performance monitoring
programme is available. Using advanced monitoring and
predictive modelling capabilities, this programme enables
decision-makers to identify which heat exchangers pose
the greatest threat to reliable operation because of biofouling, scale or both. As a result, plant personnel can develop
appropriate action plans.
Solenis experts work directly with plant engineers to
assign a critical rating score to each exchanger based on its
impact on production if taken offline for cleaning or repair.
The algorithm, developed from more than five million hours
of study time on thousands of heat exchangers, then analyses the flow study data of each exchanger, within the
context of its design, to calculate a hydrothermal stress
coefficient (HSC) – a discrete value used to assess the reliability of the heat exchanger and identify factors threatening
its performance.
processing units using 10 cooling towers and more than
400 individual heat exchangers. Heat exchanger reliability
and efficiency have a dramatic impact on the profitability of
the operation. The facility and its water treatment supplier,
Solenis, monitor the conditions of the water chemistry and
the individual heat exchangers to ensure smooth operation.
Case history: Marathon refinery
Marathon and Solenis set about defining the problem
and developing a plan to address the root cause. Before
changes to the existing treatment programme could be recommended, the hypothesis that biofilm was the root cause
of the exchanger problems required additional validation.
To do this, Solenis, working with the local Marathon team,
Marathon Petroleum Corporation operates the Garyville
oil refinery on the banks of the Mississippi River in southeastern Louisiana between Baton Rouge and New Orleans.
The facility has a crude oil refining capacity of 596,000
barrels per calendar day. Crude refining takes place in 19
www.digitalrefining.com
MARATHON SOLENIS.indd 33
Hidden biofilm cost
Despite maintaining corrosion coupon rates of less than
two mils per year (mpy) and controlling water treatment
parameters within key operating indicators (KOIs) for mineral saturation and corrosion inhibitor residuals, the refinery
struggled with heat exchanger bundle failures and efficiency losses between turnarounds.
Even with corrosion coupon results well within industry standards, heat exchanger bundle lifespans averaged
seven years, lower than predicted. Corrosion coupon data
suggested that the exchanger longevity should have been
50-80% longer. Agar dip slides, used to measure aerobic
planktonic bacteria growth, routinely yielded results well
within the Cooling Technology Institute (CTI) guidelines of
101–102 cfu/ml. Halogen residuals, used to control planktonic microorganisms, conformed to recommended values.
The programme used a non-oxidising biocide, selected by
laboratory kill studies, fed to the system two to three times
per week. Still, summer conditions resulted in constrained
refinery capacity, with exchangers being taken offline
for cleaning because of water side fouling and requiring
Underappreciated and
underestimated aspects of
industrial cooling water treatment
include the effect of biofilm on
heat transfer
unscheduled shutdowns for cleaning, repair, and replacement. The negative impact on plant production and profitability ran into the millions of dollars annually.
Because the heat exchangers were typically removed
from service for decontamination, deposit analysis did not
show the true cause of the corrosion, which was ultimately
determined to be biofilm. The steaming required to decontaminate the process side dehydrated the biofilm. Despite
deposit analysis that predicted a different corrosion mechanism, closer inspections of failed bundles revealed UDC and
pitting resulting from biofilm. In addition, corrosion coupon
visual examination and laboratory testing confirmed that
biofilm was the root cause of the problem.
A million-dollar problem
PTQ Q1 2024
33
08/12/2023 15:56:47
Tube side velocity (ft/s)
6
5
Turnarounds
4
Biofilm detection &
control programme
3
2
Measured velocity (ft/s)
Design velocity (ft/s)
1
5/
7/
2
5/ 003
7/
2
5/ 004
7/
2
5/ 005
7/
2
5/ 006
7/
2
5/ 007
7/
2
5/ 008
7/
2
5/ 009
7/
2
5/ 010
7/
2
5/ 011
7/
2
5/ 012
7/
2
5/ 013
7/
2
5/ 014
7/
2
5/ 015
7/
2
5/ 016
7/
2
5/ 017
7/
2
5/ 018
7/
20
19
0
Figure 5 Heat exchanger water velocity before and after
implementation of the biofilm detection and control
programme
used the modelling capabilities of the HexEval performance
monitoring programme to categorise the heat exchangers
at risk of developing biofouling, scale or both.
Prior to the implementation of the performance monitoring
programme, American Petroleum Institute (API) guidelines
were in use. The guidelines identified at-risk exchangers as
having a water velocity less than 0.91 m/sec (3 ft/sec), a cooling water outlet temperature greater than 48.9°C (120°F),
and a process inlet temperature greater than 60.0°C (140°F).
According to these guidelines, 233 of the 400 exchangers in
the refinery were at risk of developing deposition.
Managing the risk to 233 heat exchangers would have
been a daunting task. However, the Marathon engineers
used the heat exchanger performance monitoring programme to calculate each exchanger’s HSC value. The HSC
assesses the reliability of each heat exchanger and identifies factors threatening their performance. The higher the
HSC value, the greater the risk of deposition. An HSC value
less than 2.0 identifies a low risk, and a value greater than
2.0 identifies an increasing risk of biofouling or scale. The
calculated HSC values reduced the number of at-risk bundles from 233 to 94.
After identifying the 94 at-risk exchangers in the plant,
the engineers concentrated on improving the mechanical
aspects of the cooling system to reduce the overall risk
of biofouling and scale formation. Better transient debris
mitigation using improved tower screens combined with
other mechanical modifications helped to reduce the risk of
fouling in the at-risk exchangers and improved the overall
performance of the cooling system. These modifications
included flow balancing across the exchanger network,
using a hot process bypass instead of throttling the cooling water flow, adding supply side jumpers for back wash
assistance, introducing metallurgical changes, and making
exchanger design changes. The number of at-risk exchangers was reduced to 37.
Reducing the number of ‘bad actors’ from 233 exchangers to 37 exchangers brought focus to the problem.
Recalculating the HSC values revealed biofouling risk factors for 32 of the 37 problem exchangers. Clearly, these
34
PTQ Q1 2024
MARATHON SOLENIS.indd 34
results warranted a change in the microbiological control
programme.
To address the biofouling issue, Solenis recommended
implementation of its biofilm detection and control programme on one of the refinery’s cooling towers on a trial
basis. The recommended chemistry for the trial was the
patented, in situ stabilised active chlorine solution. After the
six-month trial, the general corrosion rate was cut by a factor
of three and the pitting rates were cut by a factor of two. The
refinery’s leadership decided to adopt the biofilm detection
and control programme for all of its cooling towers.
General corrosion rate and corrosion pitting, measured
by metal coupon testing, and average weighted wall loss,
measured during heat exchanger inspections by non-destructive testing, all showed dramatic improvement. After
converting to the in situ stabilised active chlorine solution,
corrosion rates of 0.2-0.3 mpy were achieved without pitting. Eddy current testing data collected before and after
the implementation of the in situ stabilised active chlorine
solution showed a decrease in heat exchanger wall loss
of 45%. This loss corresponded to a 50-80% increase in
bundle life. Solenis continued to monitor heat exchanger
flows and cooling tower efficiency. Monitoring of the heat
exchangers revealed that exchangers that historically had
lost flow rapidly shortly after a turnaround now maintained
their start-up flows. This improvement was validated during annual flow studies, as shown in Figure 5.
Furthermore, the biofilm detection and control programme effectively eliminated algae on the cooling water
return hot decks. Prior to implementing the programme,
even with aggressive doses of conventional biocide, algae
covered the hot decks, short-circuited the cooling tower fill,
and drove up supply water temperatures, resulting in production rate reductions, until the hot decks were cleaned.
After the algae build-up was removed by the new in situ
stabilised active chlorine solution, the hot decks remained
clean and the supply side approach to wet bulb temperatures immediately improved by -17.2°C to -16.7°C (1-2°F).
Towers with high-performance fill experienced the greatest gains. The approach to wet bulb readings were monitored closely for three years. In the first year, the approach
to wet bulb temperatures decreased by -16.1°C (3°F)
and in the third year by almost -13.9°C (7°F). The colder
water flow to the process improved vacuum on overhead
exchangers, resulting in production gains with only a negligible increase in operational expense. Additional data
analysis would corroborate the evidence of improved performance and profitability.
Next, Solenis analysed the data and determined how
many heat exchangers required cleaning outside of turnarounds and how many experienced failures before and after
the implementation of the biofilm detection and control
programme. If biofilm caused the fouling, then the implementation of the programme should result in fewer heat
exchanger cleanings during production runs. As shown in
Figure 6, the number of heat exchanger cleanings outside
of turnaround decreased by 89% with the programme.
If biofilm causes corrosion, fewer heat exchanger failures should result from improved biofilm control. The data
www.digitalrefining.com
08/12/2023 15:56:48
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12/09/2023 10:21:47
35
29
25
20
18
Biofilm detection & control programme
17
15
15
10
15
11
10
9
9
5
5
3
3
3
2
2
2
2
0
0
20
20
20
20
0
20
0
20
0
20
0
20
0
20
20
20
20
20
20
20
20
20
20
20
20
20
19
19
19
19
19
0
20
0
19
23
22
21
20
19
18
17
16
15
14
13
12
11
10
09
08
07
06
05
04
03
02
01
00
99
98
97
96
95
94
-5
3
20
0
3
2
1
20
Heat exchanger cleanings (#/yr)
30
Figure 6 Heat exchanger cleanings before and after implementation of the biofilm detection and control programme
presented in Figure 7 shows fewer heat exchanger failures
with the implementation of the biofilm detection and control programme. The number of heat exchanger failures
decreased by 85%, and no new failures have been recorded
since February of 2016.
Implementation of the performance monitoring and biofilm detection and control programmes provided a documented annual net return on investment (ROI) of seven
figures. This ROI was based on increased crude charges,
increased production through the FCC, overall increased
production, reduced propane in the fuel gas, reduced frequency of exchanger cleanings, reduced frequency of cooling tower deck cleanings, and increased heat exchanger
life. Overall, the programmes significantly improved the
refinery’s profitability.
MIC on a large cooling water system, so much so that
the expense for sodium hypochlorite and non-oxidising
biocide had soared to almost $85,000 per month with its
existing treatment programme. The refinery leadership
implemented the heat exchanger performance monitoring
programme and new biofilm detection and control programme. After the implementation of the programmes,
the monthly chemical expenditure decreased to roughly
$10,000 per month.
The system that once had experienced leaks at least
annually, now saw only one leak in the three years after
the implementation of the new programmes. Shortly after
implementation, that ‘annual’ leak, unrelated to water
chemistry, occurred again. Under normal circumstances,
that amine-related leak would have resulted in an immediate need to shut down to repair the heat exchanger. Instead,
the biofilm detection and control programme maintained
microbiological control and corrosion rates in the system for
Continued success
A sister refinery experienced issues with biofilm and
12
11
11
Heat exchanger failures (#/yr)
10
9
9
8
Biofilm detection & control programme
7
5
6
6
6
5
5
5
5
5
5
4
4
3
3
3
2
2
2
2
3
2
1
1
20
20
20
20
20
23
20
22
0
21
0
20
0
19
0
18
0
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0
16
0
20
15
20
14
13
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20
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10
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20
08
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0
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0
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00
20
99
20
98
19
97
19
96
19
95
19
94
19
19
-1
0
20
0
0
Figure 7 Heat exchanger failures before and after implementation of the biofilm detection and control programme
36
PTQ Q1 2024
MARATHON SOLENIS.indd 36
www.digitalrefining.com
08/12/2023 15:56:49
six months, enabling the exchanger to be repaired during a
scheduled unit turnaround.
This system has operated without a leak for more than
two years and without the need for an unscheduled cleaning. The refinery intends to implement the biofilm detection
and control programme in the coming year on an additional
cooling tower and the influent water system. Another
Marathon refinery has plans to install the biofilm detection
and control programme on its two cooling towers.
Marathon’s success has motivated other refineries and
petrochemical operations. A petrochemical plant using
impound water ran a successful trial using the performance monitoring and biofilm detection and control
programmes on part of its pond system, resulting in the
expansion of the programmes to two large circulating
cooling water systems.
Another refinery that implemented the programmes
increased the flow through its cooling system by 25%
within a month of implementation because of the removal
of biofilm. Refinery leadership plans to expand the programmes to several cooling towers. Successful implementation at an ammonia plant allowed continued operation of
the plant at a reduced cost, compared with the previous
programme, despite a 50 ppm ammonia leak into the cooling water system. Thus far, a shutdown for repair has been
avoided for nine months. Actual turnarounds at this facility
may be yet another year away.
The number of success stories continues to grow at
an accelerating rate. These examples show that careful
analysis of heat exchanger data to determine the causation
of failure and loss of efficiency due to biofouling resulted
in the implementation of a biofilm detection and control
programme that delivered a large ROI for a wide variety
of industrial operations. Thanks to these innovative programmes, biofilm – the hidden threat – can no longer hide.
ClearPoint, OnGuard, and HexEval are marks of Solenis LLC.
Brian Martin is based out of Canton, Ohio, and is responsible for
Marathon’s utility water systems at its 17 plants in the US. He holds
bachelor’s degrees in chemistry and biology and has 33 years of water
treatment experience, seven of which have been with Marathon.
Tim Duncan is based in St. Louis, Missouri, and is responsible for
Solenis’ cooling water applications in North America. He holds a
bachelor’s degree in chemical engineering and a master’s degree in
business administration. During his 35-year career, he has held various
water and wastewater management positions in the specialty chemicals industry. For the past seven years he has focused on providing
technical expertise in cooling water chemistry and controls.
Email: [email protected]
Gordon Johnson is based in Baton Rouge, Louisiana, and is responsible for providing technical guidance for Solenis’ petrochemical business in North America. He holds a bachelor’s degree in chemistry and
has 27 years of water treatment experience in oil refining and paper
manufacturing. For the past 18 years he has managed the water treatment solutions provided by Solenis for the third largest oil refinery in
North America.
Email: [email protected]
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MARATHON SOLENIS.indd 37
PTQ Q1 2024
37
12/12/2023 15:41:32
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A4 halliburton.indd 1
20/06/2023 11:01:17
Simulating FCC upset operations
Examples are provided of FCC upset event consequences predicted by using FCC
performance simulation models
Tek Sutikno
Fluor Enterprises
M
ore than half of the world’s petroleum refineries
include a fluidised (or fluid) catalytic cracking (FCC)
operation generating 30-50% of the gasoline
product pool of a refinery. The FCC is typically one of the
most productive and profitable processing units among the
refining processes. Primarily by utilising the proper catalyst
type, product yield distribution can be modified for selectively maximising the yield of the gasoline blending components, light ends high in olefins, high-grade petrochemical
feedstocks, or LCO (feedstock for diesel). Light ends from
an FCC unit include propylene and olefins that are alkylated
to produce high-octane gasoline.
Likely due to its role in refinery profitability, an FCC unit
often operates at much higher throughput capacities relative to the original design capacity and yields a product
distribution significantly different from that of the original
yield target. Field implementation of the associated revamp
projects is typically completed during the scheduled turnaround period. A hazard and operability (HAZOP) review
is normally necessary in each of these revamp projects to
examine the design and engineering of the revamp modifications and to assess upset/deviation cases that could
cause harm to people, environment or assets.
Representatives from operators, unit engineers, engineering contractors, and subject matter experts (SME)
are generally required to participate in the HAZOP review
meetings and are expected to describe the potential consequences of an upset event where a process parameter
deviates from the normal or regulated level.
Due to the complexity of the FCC reactor and regenerator
involving several essential operating parameters, consequences or operating impacts from a particular upset event
may not be obviously known to the operators, the unit engineer, or the SME, especially if they have not observed, experienced, or analysed the same or similar event in the FCC unit.
The unit engineer or the SME may likely need time to evaluate the upset consequences using an FCC performance or
simulation model. However, the performance or simulation
model for the FCC reactor and regenerator in a revamp or
new project is commonly developed by the licensor or/and
the catalyst vendor and not accessible to the engineering
contractor. In these cases, the unit engineer or SME will
need to work with the licensor to assess the upset consequences. Based on the severity levels of the consequences,
the required protective measures are discussed and specified in the layers of protection analysis (LOPA).
www.digitalrefining.com
FLUOR.indd 39
Various FCC performance models are reported in the literature. However, these models involving numerous parameters are mathematically complex and likely time-consuming
to utilise for a particular FCC system, in addition to the likely
absence of a specific deviating parameter in the accessible
models. However, recent versions of commercial simulators, such as Hysys Version 12, include FCC performance
models with reasonable details of operating parameters.
Performance model
The Hysys Version 12 FCC performance model discussed
herein is a steady-state model with several options applicable to common FCC designs. The default parameter input
values in the Hysys model template are used and defined as
the base case. By changing one of the input variables in the
model, the operating consequences can be checked from the
calculation results. The results are the steady-state operation
and do not predict any actual or probable time-dependent
deviation or response before reaching the steady state.
Transient responses from a deviating parameter in an
upset event will depend on the control schemes, which
To flue gas
pressure
control valve
Reactor effluent
to main fractionator
PDC
TC
To flue gas system
Reactor
LC
Regenerator
Stripping
steam
FC
Regen. Cat.
slide valve
Main air blower/
compressor
Feed steam
Spent Cat.
slide valve
Lift steam/gas
Figure 1 FCC control scheme
PTQ Q1 2024
39
08/12/2023 16:07:41
Summary of example upset case consequences
Base case
Flow rate, BPD
lb/hr
Temperature to riser, ºF
Steam to riser, lb/hr
Stripping steam, lb/hr
37,739
508,373
347
10,124
13,879
Case 1
Lower cat.
circulation
rate
37,739
508,373
347
10,125
13,879
Case 2
Lower
combustion
air flow
37,739
508,373
347
10,124
13,879
Case 3
Higher
stripping
steam flow
37,739
508,373
347
10,124
16,656
Case 4
Higher
feed
steam flow
37,739
508,373
347
20,255
13,879
Case 5
Lower
feed
temp.
37,739
508,373
327
10,124
13,879
Reactor
Plenum temp, °F
1,013
1,003
1,013
1,013
989
1,013
Top pressure, psig
49.3
49.3
49.3
49.3
49.3
49.3
Catalyst circulation rate, lb/hr
4,596,476
4,472,270
4,616,501
4,953,155
4,591,363
4,643,976
Catalyst-to-oil ratio
9.076
8.829
9.113
9.779
9.062
9.169
Coke yield, wt%
6.569
6.499
6.563
6.582
6.381
6.644
Delta coke, wt%
0.716
0.728
0.712
0.666
0.697
0.717
Regenerator
Dense bed temp. ºF
1,373.8
1,369.0
1,372.0
1,348.3
1,341.1
1,374.9
Outlet temp. °F
1,381.1
1,376.8
1,374.3
1,356.2
1,349.7
1,381.7
Outlet pressure, psig
53.7
53.7
53.7
53.7
53.7
53.7
Combustion air, lb/hr
461,890
461,890
438,796
461,890
461,890
461,890
Flue gas, O₂, vol%
1.00
1.23
0.11
1.07
1.58
0.77
CO, vol% (dry)
0.08
0.05
0.48
0.11
0.06
0.12
CO₂, vol% (dry)
16.77
16.62
17.24
16.79
16.30
16.93
SOx, vol% (dry)
0.04
0.04
0.05
0.05
0.04
0.04
CO₂, lb/hr
111,484
110,563
108,845
111,797
108,460
112,447
SOx, lb/hr
428.6
413.8
426.4
437.2
385.0
434.6
Yields/conversions
Conversion, vol%
76.83
75.26
76.62
77.77
72.18
76.96
Conversion, wt%
75.71
74.15
75.49
76.65
71.08
75.84
Propylene, lb/hr
30,881
29,067
30,725
31,108
26,619
30,874
Cat. naphtha (gasoline), lb/hr
199,372
201,571
199,097
203,101
199,362
199,703
LCO, lb/hr
68,174
71,939
68,600
66,100
77,864
67,874
Table 1
may differ from one FCC unit to another. Applications of
the model for predicting the consequences of an upset
case need to be consistent with the control schemes of
the system being analysed. Figure 1 is an example of an
FCC control scheme where the combustion air flows to the
regenerator that is on flow control, and the combustion air
flow rate to the regenerator will need to be kept constant
in the performance model when using the model to assess
the impact of different deviating process parameters.
The Hysys Version 12 FCC performance model includes
physical dimensions of the reactor and regenerator, feed
composition and characteristics, operating parameters
including common reaction kinetic parameters, catalyst
selection, and details of the reaction. Property data of
hydrocarbon feeds, typically ranging from the gasoil fraction of the crude oil to heavier feedstocks, including atmospheric resid, vacuum gasoils, and/or vacuum resids, can be
input into the model. The calculated results from the Hysys
model include fairly comprehensive parameters similar to
those normally provided by the licensor.
With the proper input data, the results from the model can
be useful for analysing the upset conditions or off-design
operating performances. For further elaboration, examples
are provided of upset events from five different deviating
parameters: catalyst circulation rate, combustion air flow
rate, stripping steam flow rate, steam feed rate, and feed
40
FLUOR.indd 40
PTQ Q1 2024
temperature to the riser. These five were chosen as illustrative examples, but other upset events can also be modelled.
The simulated consequences from the upset events
discussed herein are intended to show the resulting operational changes at the steady-state condition and have
not been checked against the actual field operating data.
Moreover, for extreme or severe upset cases such as loss
of flow, the model will not be applicable directly to these
cases, which typically result in activating the shutdown
system. However, the model can be used to generate reference data likely useful for developing a dynamic model,
which is typically needed to determine the process safety
time available for system shutdown.
Catalyst circulation rate
Catalyst circulation rate is an essential parameter or variable determined by the heat balance between the reactor
and the regenerator. An FCC reactor involves both exothermic and endothermic reactions, resulting in a net total
endothermic reaction.
The heat required for increasing the sensible heat of the
feed, vaporisation, and the net endothermic reaction is supplied by the temperature drop of the circulating catalysts as
they pass through the reactor. The resulting catalyst-to-oil
ratio (C/O) affects the cracking reaction yield conversions
and reactor temperatures. With increasing C/O, active sites
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increase to cause more cracking and higher conversion
of gasoil, and the yield of fuel gases and coke increases.
Common parameters such as coke yield and delta coke (wt%
difference between the spent catalyst and the regenerated
catalyst) can be related to C/O. For a given FCC reactor and
regenerator system with the same feed rate and characteristics, the catalyst (regenerator) circulation rate increases with
changes in process conditions such as higher reactor riser
temperature, lower feed preheat, or others demanding additional heat input to the reactor.
While the Hysys model includes fairly complete input and
output parameters commonly used in FCC performance
modelling, only some are displayed in this discussion. As an
example of upset cases in the normal catalyst circulation rates
in Case 1, Table 1 shows the changes or consequences relative to the base case when the catalyst circulation rate in Case
1 reduces by 2.7% (arbitrary, about 120,000 lb/hr reduction).
This reduction decreases the C/O, the reactor temperature
(1,013-1,003ºF), and, expectedly, the total conversion.
Due to the decreased catalyst circulation, the resulting
delta coke in Case 1 increases slightly to satisfy the system
heat balance even at the reduced reaction temperature of
1,003ºF, and the resulting coke yield (equal to delta coke x
C/O) decreases slightly. For FCC units with control schemes
similar to Figure 1, the air flow rate from the main air blower
will remain essentially unchanged when a lower set point for
reactor temperature reduces the catalyst circulation rate.
Compared to the base case, Case 1 in Table 1 shows a
reduced yield conversion, mainly with lower propylene and
slightly higher yields for cat naphtha and LCO. This yield
distribution varies depending on the selectivity and activity
of the catalysts selected. The Hysys model contains several
options for catalyst types to select.
Modern catalysts can accumulate some quantities of coke
and still maintain significant activity. Recent revamp options
include recycling fractions of the spent catalysts (or carbonised catalyst) from the stripper back to the reactor riser.
The Hysys model also includes this recycling option, which
offers the flexibility of increasing the C/O in the reactor riser
to increase conversion and selectivity without significantly
impacting the system heat balance.
Combustion air flow
Case 2 in Table 1 shows the calculated results for operation
when the combustion air flow rate from the main air blower
to the regenerator is reduced by 5%, relative to that for the
base case. As shown, flue gas oxygen content drops from
1 vol% in the base case to 0.11 vol% in Case 2, and CO content in flue gas increases from 0.08 vol% in the base case
to 0.48 vol% in Case 2, which is six times higher due to less
excess oxygen. The regenerator will operate in partial burn if
combustion air further reduces to below 0% excess oxygen
in the flue gas. With reduced inlet air flow in Case 2, CO₂
vol% increases in Case 2 compared to that in the base case.
Reduction of O₂ vol% in flue gas to 0.11 vol% in Case 2
decreases flue gas temperature rise in the regenerator dilute
phase due to afterburning of CO, as depicted by a lower
regenerator flue gas temperature of 1,374ºF in Case 2 vs
1,381ºF in the base case. Additionally, combustion air to the
42
FLUOR.indd 42
PTQ Q1 2024
regenerator in each case of Table 1 does not include any
oxygen enrichment, but this option is available in the Hysys
FCC model.
Reactor feed streams (hydrocarbon and steam) and outlet temperature do not change from the base case to Case
2, and heat transferred from the regenerator to the reactor
through the circulating catalyst remains about the same for
both the base case and Case 2. The combusted amount of
coke on spent catalysts mainly converted to CO₂ (in full burn
operation) to supply required heat remains essentially the
same for the base case and Case 2, as shown in the essentially unchanged coke yield data (coke combusted in regenerator relative to the feed rate).
Stripping steam
Case 3 in Table 1 shows the calculated results from the Hysys
model for operating with a stripping steam rate 20% higher
than the base case. This high stripping steam rate could occur
because of operator action or the control valve sticking open.
The increased stripping steam rate reduces the amount of
heavy hydrocarbons or coke on the spent catalyst, leaving
the stripper and recycling back to the regenerator. As the
reactor feed rate and outlet temperature in Case 3 remain
the same as those in the base case, the reduced combustibles on the spent catalyst to the regenerator increase the
required catalyst circulation rate by about 7.7% to generate
the unchanging heat demand of the reactor and decrease
delta coke by about 7%.
As shown in Table 1, the Hysys model results in increasing
the conversion from 76.83 vol% in the base case to 77.77
vol% in Case 3, mainly due to the increase in catalyst circulation rate or C/O. Relative to the base case, mass flow yields
for propylene and naphtha are respectively 0.7% and 1.9%
higher, with a reduced yield of -3.0% for LCO.
Steam feed rate
The FCC reactor typically includes several steam feed
streams, including those for catalyst transfer line aeration,
feed atomisation, riser lift and emergency purge, stripping,
and others such as instrument purging. When the control
valve for one of these steam feed streams malfunctions and
becomes wide open, the total steam rate feeding the reactor
will increase. Case 4 in Table 1 shows the results when the
steam feed rate to the riser increases by 100%. The steam
feed rate could potentially increase by higher than 100%
of the normal rate if the emergency steam control valve
becomes wide open.
Steam feeding the reactor is superheated, but the temperature is much lower than the riser operating temperature.
The sensible heat required to raise the steam temperature
in the riser comes from the regenerated catalysts entering
the riser. When the steam flow rate to the riser increases,
the riser and reactor temperatures could drop before the
regenerated catalyst flow rate increases to a level adequate
for reaching and maintaining the reactor normal set temperature. Case 4, with the same catalyst circulation rate as
that in the base case, shows the reactor (plenum) temperature drops from 1,013ºF in the base case to 989ºF when
the steam feed to the riser increases by 100%. The Hysys
www.digitalrefining.com
08/12/2023 16:07:43
model shows the conversion yield reduces from 76.83 vol%
in the base case to 72.18 vol% in Case 4.
The reduced conversion yield in Case 4 has a 14% reduction in the propylene yield and virtually none in the naphtha yield, based on the selected catalyst type in the model.
Moreover, a higher total steam feed rate to the reactor will
increase the hydraulic load to the downstream system and
could result in a pressure surge in the reactor and the associated systems.
Feed temperature to riser
Hydrocarbon feed to the FCC reactor typically passes
through a preheat system, receiving heat rejected from
exchangers in the downstream system. Excessive exchanger
fouling or malfunctioning of the exchanger bypass control
system could reduce the temperature of the reactor feed.
Case 5 in Table 1 shows the Hysys model results for operation with 20ºF less feed temperature to the reactor riser.
With the reactor temperature kept the same in the models for both Case 5 and the base case, more heat is needed
in Case 5 to compensate for the 20ºF drop in the feed inlet
temperature, and the catalyst circulation increases by about
1% in Case 5 relative to that in the base case.
The resulting higher C/O from the increase in the catalyst
circulation rate in Case 5 also leads to a slightly higher yield
conversion. With the combustion air flow rate set the same
in the models for Case 5 and the base case, the higher catalysts circulation rate in Case 5 reduces the excess oxygen
content of the flue gas from the regenerator, and the vol% of
CO and CO2 in the flue gas also increases. Compared to the
base case, the Case 5 model calculates a slightly higher delta
coke and about 0.8% higher CO2 emission.
Conclusion
Based on the upset events due to process parameter
changes previously discussed, the FCC model in Hysys
seems useful for predicting reasonable details of performance consequences resulting from the selected upset
events. The model apparently includes reaction kinetics
parameters to calculate yield distributions, flue gas compositions, and heat balances at varying operating conditions.
Several catalyst type options with varying selectivity
performances for specific yield distribution targets are also
available in the model, along with the design and operating options, such as combustion air oxygen enrichment
and recycling a fraction of spent catalyst to the reactor
riser. Utilising the model to simulate these options has not
been included in this discussion but may be considered.
Moreover, fine-tuning the model input parameters and verifying the calculation results against actual operating data
could likely make the model useful for quantitative assessment of consequences from upset events or for process
design analysis and optimisation.
Tek Sutikno is a Process Engineering Manager with Fluor and a
Professional Engineer registered in 11 US states with more than 35
years of experience in the process industries. He holds BSc, MSc, and
DEngr degrees in chemical engineering and a MBA degree, all from the
University of Kansas. Email: [email protected]
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www.digitalrefining.com
FLUOR.indd 43
PTQ Q1 2024
43
08/12/2023 16:07:43
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merichem.indd 1
12/12/2022 14:28:51
Refractory detection system and
floating roof protection
New refractory detection system monitors skin temperatures in Claus or thermal
oxidisers as well as SMRs, gasifiers, and emissions from floating roof tanks
Bob Poteet and Andrea Biava WIKA
Haytham Al-Barrak and Mahendran Sella Saudi Aramco
T
here are many applications in the process industries
where detecting a hotspot on the outside of an operating unit can bring safety and protection of valuable assets, such as the refractory detection system (RDS)
under discussion. This technology can be used in a variety
of applications, such as in the Claus section of a sulphur
recovery unit (SRU).
An installation was recently completed at the Aramco
gas plant. The results Aramco saw in its investigation after
six months of run-time (now 12 months running) will be
discussed, in addition to some other applications. The
device’s potential applications are only limited by the processor’s imagination (see Figure 1). So, what exactly is this
technology?
The heart of the system is a special sheath (typically
4.5mm or 3/16in) made of 316SS that only reads out the
highest temperature anywhere along the sheath. To install
the system on a Claus unit, first divide the unit into zones,
which are areas designated for sensing. As illustrated,
there can be anywhere from one to six zones in most Claus
units, depending on the licensor or operator’s preference.
The readout from each zone will resemble a type K thermocouple, but it indicates the hottest area in a zone. You
will not know where the hotspot is in the zone, but you will
be aware that one exists so that appropriate action can be
taken (see Figure 2). This technology has been successfully
running on a Claus unit for more than 12 years at a major
refinery in Italy.
reading. Older transmitters can be used that read below
0°C, but careful consideration would need to be made in
the evaluation process
• Above 400°C, the readings will lose their reliability again,
but they have done their job. No damage will occur to the
system until it reaches 900°C.
Uncertainties
The industry standard has been to attach thermocouples, but nobody knows how many to install. As a result,
many installations do not have any thermocouples at all.
Thermocouples can indicate the temperature of a specific
point, but temperature excursions in other areas will go
undetected. If a reactor with thermocouples could be covered, costs increase substantially.
The American Petroleum Institute (API) states that an
operator should have a system so that an ‘accurate shell
temperature measurement system under the shroud should
be included in the ETPS design.’ They also request routine
thermal imaging of the external shell to spot-check the
thermocouples. This can be a maintenance headache if followed as it is intended.
Refractory problems in Claus or thermal oxidisers
For many operators of SRU plants, detecting refractory
problems in the Claus unit can keep them up at night. If
the refractory starts to fail, a situation may occur where the
hot gasses hit the carbon steel shell and damage or lead to
failure of the wall of the reactor. Many ways to detect this
have been tried, but they all have limitations. Some have
tried thermal imaging, but the problem with rain shields,
cowlings, and insulation can be a real barrier.
A couple of points should be noted:
• This is not a thermocouple. Modern transmitters have
self-diagnostics built in, and readings below 120°C are
not reliable. While we can prove the system is working at
installation, you will have to start the unit without a stable
www.digitalrefining.com
WIKA.indd 45
Figure 1 Refractory failures at high temperatures are
difficult to pinpoint.
PTQ Q1 2024
45
08/12/2023 16:11:42
Temperature values sensed by CTLS (WIKA) just two months after installation
Time stamp
∆P - kPa
TC/PYRO
1 Feb-11, 5:30pm
7.1 kPa
IR Survey ºC
1. 203
2. 206
3. 208
4. 203
5. 201
6. 208
CTLSºC
Observation
1. Faulty*
CTLS is working
2. 213
3. 235
4. 233
5. 248
6. 242
2 Feb 15, 6:30pm
7.6
1074
1. 213
2. 213
3. 218
4. 211
5. 213
6. 217
1. Faulty*
2. 232
3. 244
4. 233
5. 239
6. 221
CTLS is working
3 Feb 16, 6:30pm
7.5
1090
1. 194
2. 196
3. 204
4. 196
5. 204
6. 211
1. Faulty*
2. 213
3. 228
4. 221
5. 235
6. 213
CTLS is working
4 Feb 17, 7:30pm
7.5
1084
1. 178
2. 183
3. 188
4. 183
5. 195
6. 201
1. Faulty*
2. 210
3. 222
4. 217
5. 234
6. 211
CTLS is working
5 Feb 18, 9:30pm
7.5
1083
1. 200
2. 204
3. 212
4. 202
5. 205
6. 211
1. Faulty*
CTLS is working
2. 228
3. 240
4. 232
5. 240
6. 221
Table 1 Temperature values sensed by CTLS (WIKA) just two months after installation closely represent the true values
as cross-verified by an IR camera survey
Throughput vs burner ∆P vs reaction temperature vs
outer shell temperature
% Acid gas
throughput
25
35
45
55
65
75
85
95
100
Burner ∆p,
kPa
0.8
1.07
2.13
3.2
4.3
5.3
6.4
7.5
8.8
Hot face (firebrick) Shell outer skin
temperature, ºC temperature, ºC
~ 1000
~ 1033
~ 1067
~ 1100
~ 1133
~ 1167
~ 1200
~ 1233
~ 1250
210 ± 15
212 ± 15
216 ± 15
218 ± 15
221 ± 15
225 ± 15
229 ± 15
234 ± 15
238 ± 15
Table 2
Aramco findings
In an effort to resolve technical challenges, Saudi Aramco
(SA) piloted a newly developed RDS to monitor the skin
46
WIKA.indd 46
PTQ Q1 2024
surface temperature of SRU thermal reactors (reaction
furnace).
Since 90% of SA SRU units are shrouded (weathershielded), measuring the surface temperature online
becomes challenging. Without the correct monitoring
device in place, catastrophic failures could occur, affecting
plant throughput. Deployment of this technology aims to
detect repetitive refractory failures early by sensing hot
spots on the reactor surface, even with the presence of a
shroud. Maintenance and shutdown will be planned and
timed accordingly.
Collaboration between the technology provider, WIKA,
and SA began in March 2022 with the installation of the
thermocouple on one of Saudi Aramco’s gas plant SRUs.
In October 2022, the CTLS installation was completed
and successfully tested.
The plant continued monitoring the unit, keeping a
close eye on the measured skin temperature to confirm
continuous and reliable outputs (see Table 1). Upon
testing performance, the new linear thermocouple technology proved to be working well. The CTLS coils’ peak
www.digitalrefining.com
08/12/2023 16:11:42
10
100% throughput - 8.8 kPa
95% throughput - 7.5 kPa
67104
85% throughput - 6.4 kPa
75% throughput - 5.3 kPa
Delta pressure (kPa)
65% throughput - 4.3 kPa
55% throughput - 3.2 kPa
45% throughput - 2.13 kPa
1
35% throughput - 1.07 kPa
16776
25% throughput - 0.8 kPa
Acid gas /
MW=37.88
0.1
10000
16776
23486
30197
36907
43617
50328
57038
63749
67104
100000
Capacity (kg/h)
Figure 2 Burner capacity curve showing the capacity vs ΔP
Figure 3 RDS unit installed outside reactor by a trained crew
Figure 4 Close-up view of Nelson studs applied to reactor
temperature readings were recorded at 10 different time
stamps over the course of eight months of operation since
the coils were first put into operation.
This is a great tool, but based on our first use, we believe
the way forward is if we had the ability and freedom to
move the thermocouple CTLS while the unit is running
without the need to weld on the reactor casing. We are
jointly evaluating the use of magnets to facilitate this
feature.
Industry feedback
Installation
The RDS is installed by a trained field crew. Nelson studs
are applied to the reactor, and the system is held down by
galvanised steel channels attached to the Nelson studs.
This system ensures good contact between the RDS and
the reactor shell. On a larger Claus, it took a three-man
crew five to six days to completely install a six-zone unit
(see Figures 3 to 5).
www.digitalrefining.com
WIKA.indd 47
An Italian refiner who had this bespoke system installed
12 years ago agreed to provide feedback, reporting that
he knew of no other system that could provide the required
coverage, particularly the need for system reliability. While
two of the four zones were lost after contractors cut components, a high level of reliability was still maintained. We
enquired if the system had ever alarmed during the 12-year
period and he reported that it had only done so twice. In
neither case did the hotspot reach the point where he had
to shut down. However, during the next routine maintenance, they could see that in the zones where the alarm
occurred there were indeed some refractory problems.
Other applications
Other applications include:
• Gasifier applications: Gasifier applications are very
similar to the Claus but in a much larger way with more
PTQ Q1 2024
47
08/12/2023 16:11:44
Figure 6 Installed scraping and sealing solution for a
floating roof tank
Figure 5 Multi-zoned RDS unit installation
zones. The sensors are run vertically over the full unit and
at the top.
• Steam methane reformers (SMRs): The outlet header in
an SMR is a refractory line piping that requires constant
monitoring of the outside temperature by operators. Some
use thermocouples, while others just do scanning. A common question related to thermocouples is how many are
needed to give complete coverage while the scanning is a
real Opex cost. For this solution, we can simply wrap the
pipe with the RDS and monitor for any refractory failures.
This can be easily installed with a clamping system or
even magnets.
• Floating roof oil storage: There have always been concerns about the possibility of generating a fire in a floating
roof tank (see Figure 6). For their conformation, these tanks
have a mobile roof that slides along the vertical axis of a
metallic structure fixed cylindrically. To avoid product leaks
during the sliding of the roof, a scraping and sealing system
(seal) is installed. The seal, made of rubber, undergoes continuous mechanical vertical movement and is exposed to
corrosive agents contained in the product, usually hydrocarbons. Over time, it deteriorates and emits vapours released
by the stocked product, which is normally maintained in the
tank at a variable temperature between 70°C and 90°C.
Under certain climatic conditions, this escape of vapours
can trigger fires that cause significant damage to plants,
the environment, and staff. Protecting these tanks with fire
detection systems is therefore essential. However, deterioration of the coating material of the linear heat detection
48
WIKA.indd 48
PTQ Q1 2024
cable (thermowire) can often generate false alarms. This
uncertainty is a sign of low sensor reliability and creates a
challenge for operators, who must decide when and how
to intervene.
It is important to decide whether the system should be
turned off immediately or, if a false alarm is suspected, the
field cause of the alarm should be verified. In the former
case, restoration of the area under consideration would
result in high costs.
Over time, multiple false alarms can cause staff to consider a system unreliable and, therefore, of little use. The
third option would mean, in case of ignition, a delay in activating the fire extinguishing system with its related consequences. To avoid these problems, it is therefore necessary
to maintain detection systems with technical features that
are immune to false alarms and can respond immediately.
Moreover, by continuously monitoring the temperature
near the seal, valuable information about the wear of the
seal can be provided to the operator, allowing for intervention prior to a critical situation arising. Advantages include:
• Increased level of security
• Increased functional efficiency and durability
• Programming of maintenance interventions
• Self-recovery sensor after the intervention of the alarm
• Reduced cost of insurance premiums, as the provision of
prevention systems reduces the level of risk, thus increasing the level of security.
Bob Poteet is Director of Business Development for the Global Project
Business group at WIKA, Houston, Texas. He graduated from Texas
A&M University. He has four patents in temperature sensing areas
used in the process industries.
Andrea Biava is Business Development Manager for Electrical
Temperature and Services at WIKA Italia.
Haytham Al-Barrak is a Fired Equipment Engineering Consultant
at Saudi Aramco. He holds an MS in mechanical engineering from
University of Southern California. He has two patents in fired equipment monitoring.
Mahendran Sella is a Heat Transfer and Combustion Engineer at
Saudi Aramco. He holds a BS degree in mechanical engineering from
Institute of Engineers, India.
www.digitalrefining.com
08/12/2023 16:11:45
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nalco.indd 1
11/12/2023 10:36:34
Crude to chemicals: Part 2
Part 1 covered the basics of crude-to-chemicals. Part 2 explains how hydroprocessing
technology can be used to convert any crude to chemicals to maximise yields
Kandasamy M Sundaram, Ujjal K Mukherjee, Pedro M Santos and Ronald M Venner
Lummus Technology
S
audi Aramco Technologies Company, Lummus
Technology, and Chevron Lummus Global (CLG)
conducted several years of research to develop an
improved thermal crude-to-chemicals technology known as
Thermal Crude to Chemicals (TC2C). This proprietary technology can produce high chemicals yields while extending
the feedstock range beyond just very light crudes or condensates typically considered. The research and subsequent
commercialisation of the technology involved the following
vital steps:
• Very detailed componential analysis of crudes and heavy
oils
• Development of specialised separation devices to separate
the crude into fractions for optimised processing without
having to utilise energy and Capex-intensive crude atmospheric and vacuum distillation
• Utilisation of commercially proven integration of fixed bed,
ebullated bed, and slurry reactor systems in crude conditioning so that the products from the crude conditioning section
could be routed directly to the steam cracker
• Development of unique catalyst systems for the fixed bed
and ebullated reactors that would provide the right amount
of hydrogenation without overcracking to naphtha, LPG, and
light ends
• Rigorous testing of the impact of varying amounts of
pyrolysis fuel oil recycled from the recovery section. TC2C
successfully upgrades the pyrolysis fuel oil to steam cracker
reactor feed.
Throughout the development, particular attention was
paid to minimising equipment count (Capex), energy input,
carbon footprint, emissions, catalyst deactivation rate, and
the reactor fouling rates for various feeds. Overall, hydrogenation improved the steam cracking reactor feed quality.
The integrated crude conditioning/steam cracking reactors/
recovery systems formulate the integrated TC2C technology.
evaluated compounds with a hydrogen deficiency or ‘Z’
value. He showed that complete hydrogenation and ring
opening with no change in carbon number could consume
vastly different amounts of hydrogen depending on the ‘Z’
value. The general formula is:
CnH2n+Z
where
Z = 2-2*(R+DB)
n = number of carbon atoms
R = number of rings,
DB = number of double bonds,
Z = hydrogen deficiency.
In all crudes, the hydrogen deficiency increases with boiling point with a higher concentration of condensed rings, as
previously shown in Part 1 (PTQ, Q4 2023). Typically, the
highest boiling fractions in crude (containing what is broadly
termed asphaltenes) are the most difficult to convert to
transportation fuels or petrochemical feedstocks. Indeed, the
analysis of asphaltenes using advanced techniques formed
part of the research.
In TC2C, a naturally abundant n-paraffin-rich light stream
is separated with a novel separation device such that it eliminates heavier molecules from the product that is routed to
the steam cracker, as previously shown in Part 1. This step
uses dilution steam to vapourise the light cut. Bottoms from
the separation device are routed through another separation
Truncated VGO
(470-495˚C BP)
www.digitalrefining.com
LUMMUS.indd 51
15
15
17
17
24
26
Full range VGO
(500-525˚C BP)
Crude analysis and conditioning
There have been many attempts to characterise crude
through detailed compositional analysis.1,3 In the lower
carbon numbers, the total number of n-paraffins, i-paraffins, naphthenes, and aromatics is reasonable and easily
identified. With increasing carbon numbers, the number of
possible compounds increases exponentially. Boduszynski3
started evaluating crude using detailed compositional analysis. It is well known that diverse compounds with similar
molecular weight cover a broad boiling range. Boduszynski
15
VR (580-605˚C BP)
19
22
Figure 1 DBE values of some species (DBE=C+1-H/2X/2+N/2; X is halogen, C, H, N are carbon, hydrogen, and
H atoms respectively)
PTQ Q1 2024
51
08/12/2023 16:32:29
Vacuum residue
Pyrolysis oil
50
39
High
31
40
35
27
% Total
DBE
DBE
30
23
19
20
15
11
10
7
0
10
20
30
40
50
60
70
80
90
0
10
Low
20
30
Carbon number
40
50
60
70
80
90
Carbon number
Figure 2 Double bond equivalent vs carbon number for residue and fuel oil
Typical pyrolysis oil properties
API
Sulphur, wt%
Nitrogen, wppm
Hydrogen, wt%
MCRT, wt%
Simdist,ºC
0.5 wt%
Table 1
52
LUMMUS.indd 52
PTQ Q1 2024
10.3
1.01
592
8.65
4.47
164
5 wt%
50 wt%
95 wt%
99 wt%
Recovery, wt%
Metals by ICP, wppm
200
267
606
735
98
44
The measured DBE of a typical ethylene plant pyrolysis
fuel oil and a residue are shown in Figure 2. Typical pyrolysis fuel oil characteristics are shown in Table 1. Within the
integrated hydrocracking system, the catalysts system and
operating conditions are carefully controlled such that DBE is
restricted to 15 or lower in the effluent. Slurry hydrocracking
utilising a very special catalyst can increase the conversion of
residue to more than 97%. The addition of pyrolysis fuel oil
to the residue feed increased the residue conversion significantly. The remaining unconverted oil is filtered and sent over
a fixed bed reactor system to meet IMO-compliant very low
sulphur fuel oil (VLSFO) specifications (<0.5 wt% sulphur).
Thus, TC2C ensures that no part of the converted crude is
wasted while maximising the yield of chemicals. Changes in
DBE before and after an LC technology are shown in Figure
3. High DBE value species are almost reduced to zero.
When a crude is primarily used to produce chemicals only,
it is important to know whether it is worthwhile to upgrade
it or not. Upgrading typically requires either carbon rejection
or hydrogen addition.
Upgrading naphtha may not improve the olefin yields significantly, and it produces only a small quantity of fuel oil.
10
D2007 corrected abundance
device that separates a heart cut with carbon number varying between 20 and 35, depending on the TC2C variant. The
heart cut is sent for fixed bed hydroprocessing to remove
nitrogen and sulphur, hydrogenation of aromatics, ring opening and hydrocracking. The catalyst systems are carefully
selected to optimise the molecular profile for subsequent
processing.
The heaviest fraction of the crude with a carbon number
exceeding 35 is routed to a liquid circulation (LC) reactor with
either extrudate or slurry catalyst. These reactors have small
online catalyst addition and withdrawal capabilities and can
run continuously for more than five years. LC reactor information can be found elsewhere.2 The liquid circulation reactors convert the asphaltene and recycle pyrolysis oil from the
ethylene plant to lighter components that are hydrotreated/
hydrocracked to suitable steam cracker feed.
This system ensures no heavy polynuclear aromatics
(HPNA) reach the steam cracker. Some known structures
that impede the full conversion of residue hydrocracked
VGO are shown in Figure 1. Through extensive analysis of
commercial data from residue hydrocracking and tailored
pilot plant tests, residue hydrocracking has an increased
concentration of double bond equivalent (DBE) value of 15+
compounds. For pure hydrocarbons, DBE=C+1-H/2, where
C is the number of carbon atoms, and H is the number of
hydrogen atoms. It represents the level of unsaturation or
hydrogen deficiency.
9
8
7
6
5
Before
After
4
3
2
1
0
4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24
DBE
Figure 3 Changes in DBE before (blue) and after (red)
hydrocracking
www.digitalrefining.com
08/12/2023 16:32:32
Hydrogen manufacturing
Natural gas
Hydrogen
Light oil
Heat
Cooling
Crude oil
Desalter
Middle oil
Tailored
separation
HOPS
Tricle flow
reactors
C9+
Low-value
streams
Liquid circulation
reactors
Crude conditioning section
Stripped sour
water
Tricle flow
reactors
Sour
water
Stripped sour
water unit
Lean
amine
Steam
cracker
complex
Chemicals
Pyrolysis oil
VLSFO
Rich
amine
Amine
regeneration unit
Sulphur recovery unit
Sulphur
Figure 4 TC2C flow scheme with liquid circulation reactor configuration. The total yield of chemicals ranges from 70 to
more than 85 wt%, depending on the nature of the crude
The qualities of gasoil and vacuum gasoil are reasonable,
but when cracked they produce a significant amount of fuel
oil. The intent of a crude-to-chemicals project is to maximise
chemicals production and, hence, the target was to minimise fuel oil. Hydroprocessing will upgrade the quality of
the feeds. In the previous section, various cuts are obtained
by vapourising the crude at a lower temperature by adding
steam in the heavy oil processing system (HOPS) tower.
Dilution steam is also required for thermal cracking to
reduce hydrocarbon partial pressure to increase olefin yields
and suppress coking. However, though a small quantity of
saturated water in oil is not harmful to hydroprocessing catalysts, the levels required for thermal cracking are detrimental to the catalyst. TC2C utilises a novel separation device
and targeted hydroprocessing of fractions to provide the
right amount of hydrogenation of feeds to the steam cracker
reactor for maximum crude conversion. The simplified flow
scheme is shown in Figure 4.
The importance of the desalter must be stressed at this
time. Crude can come from different sources and different
transport methods. This will contain some debris and salts.
Ppm chloride levels cause havoc on material selection,
requiring equipment to be alloyed up for resistance against
chloride corrosion. Ppm sodium levels are sufficient to cause
significant damage to catalysts, especially when the target
run lengths exceed five years. Hence, the investment in
desalters and feed filter systems is worthwhile and justified.
The desalted crude goes to the first-stage HOPS, where
naphtha mixed with steam is separated for the steam
cracker. The material heavier than naphtha in the crude
enters the tailored separation section. The fixed bed hydrocracking reactor and liquid circulation reactor technologies
previously explained are used to condition the feed. Typically,
www.digitalrefining.com
LUMMUS.indd 53
an ethylene plant turnaround exceeds five years and, hence,
all sections are also designed to last that period.
An important TC2C feature is the ability to utilise the pyrolysis oil generated by the steam cracker in the liquid circulation
reaction section. The addition of pyrolysis oil with the feed
to the liquid circulation reaction section where asphaltene
conversion occurs permits higher conversion of asphaltenes
while maintaining product stability. During research and
development, several types of pyrolysis oils were tested,
including very high proportions of pyrolysis oil in the feed
mix, to ensure the concept was robust.
Extensive pilot plant results show that at low catalyst consumption, heavy boiling material can be converted easily to
high-quality feeds for olefins production. This is one of the
major benefits of the integrated steam cracker/LC reactor
system. Low-value fuel oil is upgraded to high-value chemicals. More than 90% of feed conversions can be achieved at
very low catalyst consumption in the liquid circulation reactor platform.
Very low sediments were also observed, improving the
operation of downstream units. Many CLG-designed integrated LC-Fining/hydrocracker plants have been in operation over the last 25 years for producing jet and diesel quality
fuels and some as feed to ethylene plants. When certain catalysts and operating conditions are used in the hydrocracker,
certain types of species are produced in the hydrocracker
which are not present in the feed.
A lot of research was conducted to limit the high DBE
HPNA from reaching the cracker so there would be no highly
condensed molecules such as coronenes (six ring) and ovalenes (10 ring) in the steam cracker feed. These molecules
deposit as solids, fouling the transfer line exchanger.4 The
resulting run length could be a few hours instead of a few
PTQ Q1 2024
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08/12/2023 16:32:38
in SRT ethylene furnaces are given in Table 2. The balances
are based on Arab Light crude, and for Case 1, a typical
Middle Eastern full-range naphtha is used for comparison.
Case
1
2
Acetylene and MAPD are hydrogenated with appropriate
Feed
Naphtha
Crude
selectivities to their respective olefins. Ethane and propane
Feed, KTA are recycled to extinction. For this case study, all C5 species
Full-range naphtha
4,132
are fully hydrogenated and recycled to extinction. Benzene,
Naphtha from crude + TC2C
toluene, and xylenes (BTX) are extracted and considered
crude conditioning
1,524
Gasoil from TC2C crude conditioning
3,045
valuable products. C6-C8 raffinate is recycled to extinction.
LPG from crude + TC2C
C9-204°C is a heavy gasoline containing a high concentracrude conditioning
233
tion of C9-C10 aromatics. It is processed in the feed prepaSteam reacted
4
5
ration section and recycled to heaters for crude cracking.
Total
4,136
4,807
Pyrolysis gasoil (PGO) (204°C-288°C) and pyrolysis fuel oil
Products, KTA
(PFO) (288°C+) are generally sold as products. The salient
H2 product
46
43
feature of TC2C technology is the ability to upgrade these
Methane-rich off-gas
722
671
materials to high-value products, as shown in Figure 4. A
PG ethylene
1,500
1,500
PG propylene
649
750
small amount of residue is always purged to minimise the
Butadiene
195
245
coke precursors circulating in the system. This is taken out
Other C4s
167
230
as VLSFO for Case 2, as shown in Figure 4. Case definitions
BTX
569
603
shown in Table 2 are further discussed:
Heavy gasoline
90
126
• Case 1 is a standard naphtha cracker. Only C2/C3 recycle,
PGO
66
195
PFO
126
441
fully hydrogenated C5s, and hydrogenated C6-C8 raffinate
Acid gases
4
3
are recycled to extinction.
Total
4,136
4,807
• Case 2 – TC2C for the configuration shown in Figure 4. All
recycles of Case 1 and recycles with C9-204°C and pyrolysis
High-value chemicals
3,119
3,351
fuel oil after treatment.
Amount of crude, KTA
4,444
Valuable chemicals include hydrogen, ethylene, propylene,
Crude, BBL/day
93,344
butadiene,
butene, and BTX. VLSFO is also valuable but not
% HV chemicals to crude
75.4
included in this study since it is considered a fuel product.
Table 2
Upgrading the feed (Case 2) by hydroprocessing produces
the highest amount of valuable chemicals per unit of crude.
months. Therefore, CLG and Lummus have strict monitoring The naphtha cracker is the simplest liquid cracker. When
procedures for the HPNA of the cracker feeds.
only thermal cracking (no hydroprocessing) is considered, a
Optimum hydrocracker reactor operation and conversion significant amount of residue must be rejected.
are essential for high ethylene yield and long run length.
In addition, vacuum gasoil range molecules must be
This is achieved by passing the products of the LC reactor cracked with a higher steam-to-oil ratio. They consume
through the fixed bed reactor, which further improves the more crude and more energy. With hydrocracking options,
quality of cracker feed and reduces polynuclear aromatics residue is also used to some extent. Almost all PGO and
(PNAs). Not only materials (chemicals and refrigerants) are PFO produced in the cracker are recycled after upgrading.
exchanged between the ethylene plant and hydroprocess- Therefore, crude consumption is significantly reduced. The
ing (feed preparation) section, as heat integration (steam amount of high-value chemicals is also increased signifiand fuel system) is also essential for energy conservation cantly. A cost is associated with this configuration as it
and CO₂ minimisation.
requires the incorporation of select components for hydroTC2C maximises olefins from any crude. FCC is an effec- cracking, residue hydrocracking, and a hydrogen manufactive way to produce propylene, and Lummus has introduced turing plant.
both Indmax and single regenerator dual catalyst (SRDC)
Considering the reduction in crude and the increase in
technology to maximise FCC propylene. Experimental data high-value chemicals, the increase in Capex is justified and is
and model calculations clearly show the maximum amount substantially less than a classical refinery configuration. The
of total valuable chemicals is achieved through the hydropro- payout is less than two years for most locations. With light
cessing/steam cracker route, which also produces the high- crudes, such as Permian, as high as 70% high-value chemiest amount of ethylene with the lowest crude consumption.
cals instead of 50% for Arab Light crude can be obtained in
thermal mode,5,6 and with TC2C more than 80% high-value
Ethylene plant
chemicals production is possible.
The previous sections discuss how the feeds to the ethylIn addition to the cracking heater, the recovery section
ene pyrolysis reactors are prepared from crude. Since the plays a vital role in the ethylene plant. Fortunately, after the
molecular structure is altered through different processing hot section, the recovery section configuration is nearly indemethods, ethylene and the byproduct distributions will vary pendent of the feed. Since a naphtha plant is chosen as a
for different cases. Therefore, illustrative overall material reference, relative factors can be used to prorate the capacity
balances for producing 1,500 KTA ethylene at high severity of the plant. Figure 5 shows specific energy relative to the
Cracker overall material balance summary
54
LUMMUS.indd 54
PTQ Q1 2024
www.digitalrefining.com
08/12/2023 16:32:39
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1.4
1.3
1.2
1.1
1
C2H4
plant
only
1.2
1.1
0.9
1
0.8
0.9
C2H4 plant
+ feed
preparation
0.7
0.6
0.5
0.8
0.7
0.6
Naphtha
HCRK
1.3
C2H4 plant
+ feed
preparation
HCRK(TC2C)
Heater
effluent
Gasoline
fractionator
Quench
tower
Charge gas Refrigeration
compressor
Figure 5 Comparison of specific energy to a naphtha
cracker (HCRK = TC2C with hydrocracker)
Figure 6 Relative capacity factors for major ethylene plant
recovery section
reference naphtha cracker. In addition, major capacity factors
are shown in Figure 6 relative to the naphtha cracker.
Capacity factor represents the quantity of feed with that
quality relative to reference feed cracking. These are based
on simplified mass transfer models and sometimes based
on two-component distillation models. Most of the unit
capacity can be accurately predicted within +/-2%; hence,
it is a standard design tool for preliminary design. Most sections have less than 5% over the reference plant except the
charge gas compression and quench section. Naphtha feeds
have higher ultimate ethylene yields than crude. Generally,
crude and in this case, Arab Light crude, has high residue,
reducing the ultimate yield. However, as shown in Table
2, crude conditioning (hydroprocessing) has significantly
improved the yields.
The specific energy is one of the key performance parameters of the ethylene plant. It is defined as the energy required
to produce per unit weight of ethylene after accounting for
energy generated in the plant. Industry-standard energy
equivalents are used for the import/export of steam, fuel,
and electricity. Cooling water is another parameter. After
accounting for all credits and debits, the energy to produce
per unit of ethylene is calculated as specific energy. The
lowest one is desirable.
In the industry, pure ethane cracking has the lowest specific energy value (~3,000 kcal/kg C₂H₄). In this exercise, no
additional schemes are considered; hence, direct comparison
with the reference plant gives a good indication of energy
consumption for crude to chemicals. In the traditional way, a
refinery is used to produce feeds (naphtha and gasoil) for the
olefin plant. The refinery contributes additional Capex and
energy. Therefore, for a proper comparison, the additional
Capex and energy must be included for the naphtha plant
in principle to account for the upfront naphtha production.
That is based on some in-house data in Figure 6. Although
the ethylene plant shows higher specific energy than the
naphtha plant, including the refinery to produce that naphtha, it clearly shows that TC2C is superior. When the specific
energy is reduced, that also reduces the CO₂ emission.
This clearly shows that a crude-to-chemicals configuration bypassing the refinery not only reduces Capex but
also energy consumption. More than 10 patents have been
granted and/or pending for different feed treatment/ethylene plant configurations and technologies covering crude to
chemicals. Although only complete crude to chemicals is discussed here, partial transportation fuel production depending upon the local market can also be considered.
Extensive bench-scale, pilot-scale, and demo-scale feed
preparation units (1 bbl/day) were operated over three years,
and all relevant data were collected and modelled. A digital
twin of the flow scheme was also constructed. One plant
is currently under construction, which is expected to start
up in 2026. There are other projects under various stages
of design. TC2C not only reduces Capex but also reduces
energy consumption and CO₂ emissions. The material balance shown is only an example and will vary case-by-case
basis to project specific objectives.
56
LUMMUS.indd 56
PTQ Q1 2024
Conclusion
Ethylene is produced by thermally cracking hydrocarbons
mixed with dilution steam in tubular reactors at high temperatures in a short residence time. During this process, coke (a
solid) deposits in the reactor and, hence, the cracking coils
must be cleaned periodically using steam/air. The coking tendency of heavy molecules such as gasoil and vacuum gasoils
is high, and the relative ethylene yield from these feeds is
typically low compared with gaseous and naphtha feeds.
Traditional feeds such as naphtha and gasoil to the cracker
are obtained from crude through distillation in a refinery.
These are made to specifications to meet the fuel standards. In this transcript, crude is cracked to produce ethylene
bypassing the refinery. In TC2C technology, all crude molecules ranging from naphtha to residue are processed to produce light olefins. Detailed analysis and understanding of the
crude characterisation have resulted in better catalyst and
reactor systems to upgrade the crude for olefin production.
Coke precursors that shorten the heater run length are
reduced significantly with better characterisation and experimental techniques of crude characterisation. In the scheme
proposed, in addition to the standard C2 to C6-C8NA recycles, pyrolysis gasoil and fuel oil produced in the ethylene
plant are sent to the TC2C crude conditioning section, where
they are upgraded to meet ethylene plant feed requirements.
By doing this, the amount of crude required to meet the
design ethylene production is significantly reduced. Only a
small purge is taken out as valuable IMO-compliant VLSFO.
For Arab Light crude with hydroprocessing, total high-value
chemicals are increased to >75%, much higher than that
www.digitalrefining.com
08/12/2023 16:32:40
without hydroprocessing. Capex for the integrated ethylene
plant and crude conditioning section is reduced along with
the specific energy reduction. Relative to a 100% naphtha
cracker, the specific energy of a crude cracking ethylene
plant increases only slightly.
When the energy required to produce the naphtha cut
from crude in the refinery is included, the TC2C technology
route demonstrates lower specific energy and, hence, will
emit lower CO₂ for the complex. With hydroprocessing, the
complete refinery is bypassed. Therefore, Capex and energy
savings are higher than an integrated ethylene plant/refinery. Extensive bench-scale and pilot plant studies for various sections of TC2C technology were run to collect data
for design. A plant using this scheme is under construction
and is expected to start up in 2026. Although the scheme
is shown with Arab Light crude, the technology is applicable to all types of crudes. Lighter crudes such as Permian or
Agbami will reduce the Capex and improve crude utilisation.
TC2C is a mark of Lummus Technology.
Acknowledgement
The authors thank the Lummus, Chevron, and Saudi Aramco colleagues
who worked with us in this project.
References
1 Altgelt K H, Boduszynski M M, Composition and Analysis of heavy
Petroleum Fractions, Marcel Deckker, NY 1994.
2 Sundaram K M, Mukherjee U, Baldassari M, Thermodynamic Model
of sediment deposition in the LC-FINING Process, Energy & Fuels, 22,
2008. p.3226-3236.
3 Boduszynski M M, Composition based crude oil evaluation, Haverly
Systems Asian Technical Conference, Jun 2001.
73
EST. 1951
4 Fernandez-Baujin J M, Maddock M J, Sundaram K M, A case study
based on commercial experience: Vacuum gasoils to Petrochemicals,
presented at AIChE Spring meeting, Orlando, Fl, March 18-20, 1990.
5 Sundaram K M, Mukherjee U K, Venner R M, Santos P M, Thermal
crude to chemicals, presented at AIChE spring meeting, Houston, March
13-16, 2023.
6 Biswas G, Maesen T, Sundaram K M, Unlocking Permian value,
Hydrocarbon Eng., Apr 2022, p.29.
Kandasamy M Sundaram is a Technologist responsible for pyrolysis
reactors and other process reactor designs. He holds a Bachelor’s in
chemical engineering from Madras University, a Master’s in chemical
engineering from the Indian Institute of Science, and a PhD from the
University of Ghent, Belgium.
Email: [email protected]
Ujjal Mukherjee is Chief Technology Officer responsible for Lummus’
existing portfolio and developing technologies at the forefront of the
energy transition and digitalisation. He holds a Bachelor’s in chemical
engineering from National Institute of Technology, India, a Master’s
in chemical and petroleum engineering from ENSPM, France, and a
Master’s in business administration from Rutgers University, US.
Email: [email protected]
Pedro Santos is Technology Director leading the commercial deployment
and further technology development of TC2C. He holds a Bachelor’s in
chemical engineering from the New Jersey Institute of technology, and
he has been granted five patents related to crude to chemicals.
Email: [email protected]
Ronald Venner is Chief Business Officer, Clean Fuels, leading the
strategic direction and performance of Lummus’ clean fuels and
crude-to-chemicals businesses, as well as the company’s joint venture
Chevron Lummus Global. He holds a Bachelor’s in chemistry and a
Master’s in chemical engineering from Manhattan College.
Email: [email protected]
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74TH ANNUAL
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Register online at pacs.ou.edu/lrgcc
For questions, contact Lily Martinez at [email protected].
The University of Oklahoma is an equal opportunity institution. www.ou.edu/eoo. Printed at no cost to Oklahoma taxpayers.
www.digitalrefining.com
LUMMUS.indd 57
PTQ Q1 2024
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08/12/2023 16:32:41
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Revolutionising refining with
digital twins
Exploring applications and outputs across the refinery landscape
Michelle Wicmandy, Jagadesh Donepudi and Rodolfo Tellez-Schmill
KBC (A Yokogawa Company)
R
efiners are at the crossroads of innovation and challenge. They are facing disruptions ranging from oil
price volatility to the complexities of the global energy
transition. Adding to this complexity, Offshore Technology
claims India is expanding its pipeline network to more than
29,600 km by 2025. This significant expansion is roughly
three-quarters of the Earth’s circumference. As the industry
confronts these uncertainties, securing the integrity of this
expanding pipeline infrastructure becomes crucial for meeting the nation’s growing energy demands while reducing risks
and accidents that can harm people, profits, and property.1
Navigating new refining challenges
To navigate these new challenges, the refining industry is
revamping how it produces, uses, and manages energy.²
Although existing assets have data acquisition capabilities,
the hurdle lies in reviewing, cleaning, and assessing this
data. This process is necessary to determine both current
and future operating conditions, as well as meet safety and
environmental regulations.
In this journey, Indian refiners are in the process of implementing digital twins across various refinery process units
for long-term sustainability.3 This initiative centres around
creating digital twins for diverse applications, which provides real-time visualisation of key performance indicators
(KPIs) and benchmark parameters. By using digital twins,
refiners can improve the plant’s efficiency and productivity
while reducing miscommunication, data waste, and labour
costs. Essentially, digital twin technology is revolutionising
the way refiners operate and paving the way to long-term
profitability.4
Furthermore, it is evident that all aspects of an entire refining supply chain are highly interrelated and complex. Thus,
integrating digital twins into the supply chain delivers added
value, too, by optimising processes, energy consumption,
and control applications such as real-time optimisation (RTO)
and advanced process control (APC) systems. In the supply chain, these applications help bridge the gap between
forecasting and actual operations.4 Validating these gaps, or
delta vectors, uncovers the disparities between the planned
and actual operations in terms of demand, inventory, and
production. By validating these delta vectors, supply chain
managers can quickly assess and address gaps in their models and processes to accommodate changes in inputs and
outputs.1
www.digitalrefining.com
KBC.indd 59
In regard to process optimisation, which is integrated with
supply-side optimisation for power, steam, and utility balances, energy demand takes centre stage. The comparison
between linear programming (LP), actual data, and simulation enables automated vector updates and model recalibrations via artificial intelligence (AI) and machine learning (ML)
methods.
The following discussions explore various applications,
including KPI visualisation, production accounting, LP model
updates, process optimisation, real-time optimisation, and
corrosion monitoring. The digital twin architecture includes
connecting process models through open platform communications unified architecture (OPC UA) with historians to
ensure proper calibration.
Digital twin technology
Digital twins offer a solution to transform the oil and gas
industry by improving efficiency and reducing risk. According
to researchers,5 these virtual models of physical assets
seamlessly connect with real-time data across assets, columns, reactors, pipinmg, and equipment. Despite changes in
crude quality, catalyst composition, and process conditions,
digital twins continuously analyse industrial data to predict
and optimise processes.4 Their perpetual operation brings
multiple benefits, such as asset monitoring in planning and
scheduling studies, refinery-wide flow sheeting, real-time
optimisation, and more.
Furthermore, digital twins set benchmarks for both the
quantity and quality of units. These benchmarks are then
transmitted to the RTO/APC layer for optimisation on a
global scale.6 This iterative process involves ongoing validation and adjustments to maximise benefits derived through
the APC in a closed loop. The APC, armed with its dynamic
process model, aims to stabilise operations and reduce fluctuations. It effectively implements the desired setpoint from
the RTO to achieve closed-loop optimisation.5 The optimiser
identifies the optimal operational state and communicates it
to the APC.
Implementing a digital twin starts with identifying possibilities and choosing a pilot configuration with the highest
ROI. After implementation, the digital twin becomes an integral part of the enterprise’s digital backbone.4 The final step
involves monitoring the value created and modifying the digital twin to maximise economic benefits.
Refiners apply digital twins in various applications to
PTQ Q1 2024
59
12/12/2023 10:29:35
P tro-SIM
KBC Explorer
Process Digital Twin
KPIs, DQPs, MPIs
Raw data
Dashboard
Data Archive
Historian and
LIMS
Advanced
Analytics
$
P tro-SIM™
Monitoring service
Process model
LP Submodel
KPI estimation
ERP
Figure 1 Digital twin architecture
improve plant performance. These applications include visualising KPIs for performance tracking, reconciling data in
production accounting, updating LP models in the supply
chain, optimising processes to improve yield and energy,
conducting real-time optimisation through quick gain calculations, and managing corrosion to monitor equipment and
system degradation. These applications underscore the value
of digitalisation in the refining process and are addressed in
the remainder of this study.
Digital twin architecture
The digital twins are process models connected through
OPCs with historians such as IP.21, Exa Quantum, OSI PI,
or any other real-time data gateways, as shown in Figure 1.
The models are calibrated using test data to ensure energy
and mass balance accuracy. After calibrating the model, it
is scheduled to run, and the results appear on dashboards.
Other applications use these to generate advanced analytics.4
The success achieved from this system depends on
whether the model is accurate and current. An outdated
model limits the operation’s potential, resulting in value leakage, lost opportunities, and substantial financial costs.
Visualisation: Enhancing KPI management
Fuel gas
LPG
Naphtha
Distillate 1
Distillate 2
Bottoms
Production accounting: Single version of the truth
The typical production accounting digital twin serves as
the facility’s single version of the truth, laying the foundation for the hydrocarbon balance and loss control initiatives
as shown in Figure 4. The system not only generates the
hydrocarbon balance accurately, but it also detects losses.
Product yield, WT%
In the refinery, KPIs act as a compass, guiding performance
tracking of key metrics such as temperature, pressure,
equipment status, and more. Digital twins, adept at tracking
and measuring KPIs, calculate intrinsic parameters such as
yields, energy consumption, and column performance such
as flooding, heat exchanger fouling, furnace efficiencies,
coking tendencies, and emissions along with the benchmark
parameters. Closing these gaps between the actual measurements and the benchmarks adds value.7
KPI management uses a strategic approach that aligns
with the company’s goals to optimise plant and equipment
performance. This approach ensures measurable progress.
Derived from plant measurements, KPIs offer real-time
insights into critical parameters such as unit throughput,
feed, and product quality.
Furthermore, calculations address yields and fractionation
efficiency to identify process improvement opportunities. The
intrinsic layer, estimated via a process digital twin, dives into
issues such as column flooding, exchanger UA and fouling
factors, and coking inside heater tubes. Using these intrinsic
KPIs, operators can maximise asset utilisation and proactively
improve the plant’s efficiency. Essentially, this system not only
evaluates performance holistically but also provides insight to
continuously improve individual assets or the entire complex.7
Figures 2 and 3 illustrate trends in product yields and
intrinsic parameters, respectively. Figure 2 indicates the
product yields vs timeline such as day/month. Figure 3 shows
the intrinsic parameter limits and trends for jet flooding and
downcomer backup, which are regularly calculated.
Day /Month
Figure 2 KPI product yield (wt%) trends
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It provides a systematic approach to reconciling data input
errors. Reconciliation entails distributing mass imbalance
errors across streams, adjusting specific streams to achieve a
close mass balance, and using site-wide tools to seamlessly
close the balance across assets.5
Additionally, the process digital twin enhances operational
efficiency through various capabilities. First, it ensures a precise elemental balance apart from mass considerations, providing a comprehensive understanding of the hydrocarbon
processes. Moreover, it contains details about plant and tank
farm operations, offering insights into movements critical
for effective management. As a result, the digital twin helps
uncover gross errors early in the business process, ranging
from data entry errors and instrument failures to missing
movements. With automatic logic, it uses coke production
and adapts to flow variance, ensuring uninterrupted production even during outages.
Supply chain – LP model updates for robust planning
In refinery and petrochemical complexes, LP models play a
vital role in assessing crude selection, yields, and gross margin via optimisation functions. Despite their utility, these linear models often face challenges due to infrequent updates
in sensitivities related to feed, severity, and product qualities.
This discrepancy between model predictions and actual performance, particularly at the end of back casting, can negatively impact operational efficiency.4
Traditional LP models used for planning, scheduling, and
optimising assets lack continuous validation. This deficiency,
often performed by individuals, creates inaccuracies that
contribute to suboptimal operations. To overcome these
challenges, the digital twin continuously tracks asset performance. Thus, all stakeholders get a comprehensive view
of asset performance, including optimum operating targets,
enhanced scheduling, and inventory cost savings.
Additionally, digital twins not only automate complex work
processes such as kinetic model calibration and validation
but also leverage AI and ML methods to automate workflows, check the application’s health, validate AI recalibration
recommendations, and validate the accuracy of the vectors.
As shown in Figure 5, the automated model maintenance
tool determines when the model needs to be recalibrated
and establishes protocols for validating the model. The result
Max. Jet flooding
50
74.4%
50
40
90
100
30
Figure 3 Intrinsic parameters monitoring
is ongoing health score tracking, data quality analysis, and
actionable email alerts.
Process optimisation: Bridging gaps and identifying
opportunities
Process optimisation can be achieved using a digital twin to
identify gaps between actual and benchmark performance
during plant operation or the design stage. The gaps are
analysed for corrective actions such as changing operating
parameters or modifying equipment, piping, or instrumentation. Digital twin applications for process optimisation include:
• What-if analysis, debottlenecking, and optimisation
• Constraint management
• Molecular management
• Unit/equipment optimisation
• Product blending and stream routings
• Identify margin improvement opportunities
• Screen opportunities
• Continuously track benefits for each implemented
opportunity.
Based on the authors’ experiences, the digital twin of an
integrated refinery and petrochemical complex with a multifeed steam cracker complex helped identify operational
improvement opportunities exceeding 100 million USD and
Capex savings tipping 100 million USD during the design
review of its configuration.
Real-time optimisation: Dynamic control for
operational excellence
In traditional distributed control systems (DCS), the process
parameter from specified boundaries is common. In APC,
Mass Balance
Raw mass imbalance using outage
1.25
0
1.3
-2
1.35
1.3
1.4
1.45
1.05
1
80
46.8%
90
100
40
CCR-Coke Ratio
1.15
1.1
70
60
80
60
Key Ratio
1.2
Max. Downcomer backup
70
1.5
Max. Reconciled in mass flow
2
4
4
-4
-2.4 WT%
-6
-8
-10
10
6
7
3
6
8
5
5.2 WT%
2
1
8
9
0
10
Figure 4 Key performance indicators
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 Optimise NH3 injection flow rates
 Optimise wash water rates
 Generate integrity operating envelopes
 Estimate corrosion rates.
Real time optimisation
Planning & scheduling
Enhanced unit monitoring
Decarbonisation studies
New Data
Set Alert
AMM
Simulation / LP health scores
Actionable alerts
Best calibration case
Calibration & tuning factors
Corrosion monitoring: Guarding infrastructure
integrity
Digital
Twin
AMM Proposed
Calibrated &
Tuned model
Figure 5 Automated model maintenance
the process is maintained at desired operating conditions by
reviewing process constraints, reducing process variability.
During actual plant operations, equipment availability, economic conditions, and process disturbances result in changes
in optimum conditions, as shown in Figure 6. Hence, the
optimum operating conditions need to be re-calculated in
real time. The RTO of set points requires two models: the
economic model and the operating model. The economic
model functions to minimise costs while maximising product
values, and the operating model is a steady-state process
model to identify the operating limits for the process variable.
Case study: Showcasing digital twin applications
This case study minimises corrosion for a refinery overhead
system. As part of their digitalisation journey to improve
asset reliability, this client sought a centralised corrosion
monitoring system. To address corrosion issues in the crude
distillation units’ (CDU) overhead system, KBC (A Yokogawa
Company) deployed a corrosion digital twin.
The following objectives were set to guide the deployment
of a digital twin to monitor corrosion in the refinery’s CDU
overhead section and optimise operations:
 Online prediction and monitoring of corrosion indicator
parameters.
a. Ionic dew point temperature and pH
b. Salting point temperature
c. Aqueous phase condensation temperature and pH
Traditional: DCS only
Control with fluctuation
Corrosion in CDU overheads caused unplanned and costly
unit outages.8 Eliminating or minimising corrosion in the
overhead system of CDUs was challenging, as it could lead
to pipe leaks. This corrosion stemmed from aqueous corrosion attributed to hydrogen chloride forming from hydrolysis of inorganic chlorides in crude preheat and furnace
processes. Factors such as ammonium and/or hydrochloride salts that absorb moisture often cause corrosion above
the dew point. Mitigation strategies involved optimising
the injection of chemical agents or dew point control in
the overhead system. This complexity made the overhead
system one of the most vulnerable parts of each distillation unit. As shown in Figure 7, the corrosion digital twin
provided a comprehensive solution that consolidated processes as well as chemical and corrosion data to streamline
monitoring from a single location. The corrosion control
delivered the following benefits:
 Minimised corrosive conditions
 Prevented excessive corrosion, thereby extending the
service life of the pipe and process equipment
 Reduced and prevented unpredictable shutdowns or
accidents
 Cut maintenance costs.
The corrosion digital twin achieved these outcomes by
tracking the following parameters:
• Ionic dew point temperature
• Salting point temperature
• Aqueous phase condensation temperature and pH
• Neutralising ammonia injection rate
• Boot water pH
• Wash water injection rate.
An electrolyte-based fluid package with the proprietary
OLI and Petro-SIM digital twin of the CDU overhead was
developed to demonstrate the capabilities of a corrosionmonitoring digital solution. It provided key information to
confirm corrosion mechanisms, rates, and comprehensive
operational guidelines.
Modern: APC + DCS
Minimise fluctuation
New standard: RTO + APC+ DCS
Minimise fluctuation +
maximise profit
Optimal setpoint
Manual setpoint
Process data (ex. Product properties)
Figure 6 Control systems
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To use the model for
troubleshooting
Modelling,
troubleshooting,
case studies
Data historian, lab analysis,
corrosion data
Petro-SIM + OLI
engine
Stream
properties
KPI
(in Petro-SIM)
Corrosion rate,
metallurgy
OLI application
Corrosion analysis
pH, Cl conc, solid,
generalised corrosion
rate*, velocity etc.
To identify deviation
based on low and
high value
*Only when operating
below ionic dew point
Figure 7 Corrosion digital twin
Conclusion
Standing at the crossroads of innovation and challenge,
refiners face the complexities of the refinery and petrochemical industry. At this moment, KPIs emerge as valuable
tools that monitor critical metrics such as temperature, pressure, and equipment status. These metrics not only provide
insights but also serve as catalysts for innovation, helping
refiners navigate the intricacies of yields, energy variances,
column performances, and more.
Refineries and petrochemical plants are increasingly
adopting digital technologies. One such tool, the digital twin,
has proven to be a multi-faceted solution for both operational and design stages based on our experience. In this
article, we present a case study of a refinery that benefited
from digital twin applications, including:
• KPI visualisation incorporates intrinsic parameters like
flooding and heat exchanger fouling characteristics
• Production accounting systems leverage mass balances
and elemental balances to identify and address real losses
within the production process
• Supply chain planning systems update LP vectors to represent non-linear sensitivities for more robust supply chain
planning
• Production optimisation closes gaps based on benchmarking parameters to improve gross margins
• Real-time optimisation continuously calculates gains by
optimising set points in real time
• Corrosion monitoring minimises corrosion rates and implements corrective actions to prevent pipe corrosion, ensuring
the longevity and reliability of the infrastructure.
These applications emphasise the wide-ranging benefits that a process digital twin simulation software offers
refiners, demonstrating its potential to revolutionise various
aspects of plant operations and design.
This point of convergence should not be seen as a
period of uncertainty. Rather, it represents a strategic
juncture where the industry holistically assesses its overall performance and implements strategies for continuous
improvement. It serves as a roadmap that motivates the
industry to drive toward a sustained state of excellence.
References
1 Priyanka E B, Thangavel S, Gao X-S, Sivakumar N S, Digital twin
for oil pipeline risk estimation using prognostic and machine learning
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KBC.indd 63
techniques, Journal of Industrial Information Integration, 26, 2022,
pp.100,272. https://doi.org/10.1016/j.jii.2021.100272.
2 Yadav V G, Yadav G D, Patankar S C, The production of fuels and
chemicals in the new world: critical analysis of the choice between crude
oil and biomass vis-à-vis sustainability and the environment, Clean
Technologies and Environmental Policy, 22(9), (2020), pp.1757-1774.
https://doi.org/10.1007/s10098-020-01945-5.
3 Alsayoof L, Shams M, The role of crude oil selection in enhancing
the profitability of a local refinery with lube hydro-processing capacity,
Chemical Engineering Research and Design, 185, 2022, pp.146-162.
https://doi.org/10.1016/j.cherd.2022.07.002.
4 Wanasinghe T R, Wroblewski L, Petersen B K, Gosine R G, James L
A, De Silva O, Mann G K I, Warrian P J, Digital Twin for the Oil and Gas
Industry: Overview, Research Trends, Opportunities, and Challenges,
IEEE Access, 8, 2020, pp.104,175–104,197. https://doi.org/10.1109/
access.2020.2998723.
5 Min Q, Lu Y, Liu S, Su C, Wang B, Machine learning based digital
twin framework for production optimisation in petrochemical Industry,
International Journal of Information Management, 49, 2019, 502–519.
https://doi.org/10.1016/j.ijinfomgt.2019.05.020.
6 Singh A, Be in Control of Your Operation – Integrating Real-Time
Optimisation with Advanced Process Control for Optimum Energy
Management and Optimisation. OnePetro, 2022.
7 Sarantinoudis N, Tsinarakis G, Dedousis P, Arampatsis G, ModelBased Simulation Framework for Digital Twins in the Process Industry.
IEEE Access, 11, 2023, pp.111,701-111,714. https://doi.org/10.1109/
access.2023.3322926.
8 Schempp P, Kohler S, Mensebach M, Preuss K, Troger M, Proceedings
of the European Corrosion Congress, Prague, Czech Republic, Paper No.
88826 (EFC Working Party 15: Corrosion in the Refinery Industry), 2017.
Michelle Wicmandy is the Marketing Campaigns Manager at KBC (A
Yokogawa Company) in Houston, Texas, with more than 20 years of
experience in marketing and communications. She serves on the Forbes
Communication Council and has contributed to both academic and
trade publications. She holds a DBA in business administration.
Jagadesh Donepudi is the Director for Business Development South
Asia at KBC (A Yokogawa Company) in India. He has more than 30
years of experience adding value to refineries and upstream oil and gas
companies via digitalisation, digital twins, and energy transitions. He
holds a PhD in chemical engineering from the University of Mumbai.
Rodolfo Tellez-Schmill is the Product Champion for Process Simulation
at KBC (A Yokogawa Company) in Canada. He has more than 20 years of
experience in chemical engineering, including process engineering, quality control, project management, R&D, technical support, and training He
holds a PhD in chemical engineering from the University of Calgary.
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Find out more at
arielcorp.com/applications
PTQ Q4 Ariel.indd 1
08/09/2023 10:46:38
Optimising nitrogen utilisation in
refinery operations
Technical aspects and insights on managing nitrogen by considering actual
operational scenarios
Rajib Talukder and Prabhas K Mandal
Aramco
N
itrogen gas, known for being chemically inert,
non-flammable, colourless, odourless, and slightly
lighter than air at atmospheric temperatures, has
been extensively used in the chemical and process industry for many years. The oxygen content in empty vessels,
equipment, and pipeline spaces is reduced by it to facilitate
start-ups, or hydrocarbons are driven out by it on shutdowns. Due to its non-reactive nature and low solubility in
liquids, it is commonly chosen as a blanketing gas, thereby
virtually eliminating any risk of product contamination.
In refineries, most of the nitrogen is consumed in gaseous
form. Liquid nitrogen is stored and then vapourised into gaseous nitrogen as needed. The base nitrogen demand load
for a refinery during normal operation is met by gaseous
nitrogen, a demand that is an order of magnitude smaller
than the peak load observed during plant shutdowns. The
peak load demand is met by liquid nitrogen.
This article does not address the methods by which the
overall base or peak nitrogen demands of a refinery are
determined. Instead, attention is given to several major
contributors to the base or peak load where significant optimisation opportunities are believed to exist due to a high
degree of conservatism associated with these contributors.
In the following sections, major contributors, such as the
nitrogen required for tank blanketing, surge drum blanketing, and starting up hydroprocessing units, are addressed.
Nitrogen blanketing is utilised in vessels/tanks containing
liquids, such as a surge drum or tanks, for the following reasons:
• Safety: The use of nitrogen lessens the chance of oxygen
penetration, thereby disrupting the formation of the fire
triangle (fuel, heat, oxygen). This is especially relevant for
vessels containing flammable liquid hydrocarbons.
• Protection against oxidation: Preventing oxygen from
entering hinders the oxidation process, which could otherwise
harm the quality of the liquid inside the vessel. This is particularly important for lean amine and wash water surge drums.
• Prevention of vapour loss: A nitrogen barrier restricts the
amount of hydrocarbon vapour that can leave the vessel.
Estimation of nitrogen blanketing for surge drums
By maintaining an inert atmosphere over the stored liquid,
nitrogen blanketing ensures quality, regulates pressure,
and prevents incidents.
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ARAMCO.indd 65
To correctly estimate the flow rate of the blanket gas, it
is important to keep the pressure inside the vessel within
safe and operational limits. Here is a basic guide on how to
measure the blanket gas flow rate:
• Assess volume changes due to liquid outflow: The initial
step involves identifying the maximum liquid volume that
will exit the vessel over a certain period. This shift in volume
results in a change in pressure inside the vessel, necessitating compensation via the blanket gas to maintain positive
pressure. The Ideal Gas Law is used to convert the change
in liquid volume into the needed gas volume.
• Consider pressure changes due to liquid contraction: The impact of major pressure changes in the vessel
resulting from variations in incoming feed temperature is
also accounted for, such as the volume contraction caused
by the entry of cold feed when the supply of hot feed is
interrupted.
When calculating the total need for blanketing gas for
any surge drum, thermal inbreathing is generally not considered along with normal inbreathing resulting from liquid
movement from the vessels, unlike in the case of tanks. This
is primarily because the empty vapour space in a surge
drum is much smaller than in tanks, and the likelihood of
a coinciding loss of liquid inflow and contraction of the
vessel’s vapour due to sudden ambient cooling from rain is
extremely low.
However, it is essential to note that nitrogen blanketing
of vessels is not designed to address certain circumstances:
• Using blanket gas as a safeguard for the vessel design
for full vacuum: A total feed failure to the surge drum during
the vessel’s emptying process is considered a severe situation. In such cases, according to API 521 standards, blanket
gas cannot be used as a safety measure since control action
credits (for instance, the blanket gas control valve) are not
acknowledged as safety precautions. The vessel should be
either constructed for full vacuum to ensure its safety or
equipped with a safety instrumentation system to avert a
vacuum under these emergency circumstances.
• Supporting NPSHa for the pump connected to the surge
drum: While estimating NPSHa, the blanket gas’s solubility
in the liquids being pumped is considered, and the vapour
pressure is presumed to be higher than the actual vapour
pressure, equal to the surge drum’s normal operating
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requirements for the process units, subsequently driving up the total nitrogen
demand for the facility. Moreover, it could
Project
Project A
Project B
result in an overly conservative sizing of
Equipment name
Lean amine surge drum
Lean amine drum
the nitrogen blanketing valve, which might
Vessel pressure (bara)
3
2
introduce control challenges when the
Vessel temperature (°C)
70
60
Vessel head type
2:1 Semi-ellipsoidal
2:1 Semi-ellipsoidal
valve output is minimal, possibly triggering
Vessel ID (mm)
3,000
2,500
unnecessary nitrogen wastage. Refiners
Vessel T-T (mm)
10,000
9,000
are adding gap control for the blanketing
Out flow (m³/h)
180
85
control valves, as described later in detail,
Normal liquid level- NLL (mm)
7,000
6,000
and this practice results in near zero openLo Lo liquid level- LALL (mm)
750
500
ing of the nitrogen blanket control valve
Nitrogen blanket gas flow (Nm³/h)
during normal plant operation.
1. Method 1
358
139
2. Method 2
63
51
Observations from actual plant data
3. Design value
360
50
reveal a consistent level during normal
operations. During emergency situations
Table 1
when the inflow to the surge drum is diminished or completely lost, operator actions
pressure. This is done to account for slight degassing in the ensure the feed surge drum level is maintained, preventing
liquid and to prevent pump cavitation.
the connected pump from being tripped due to the activation of the low liquid level trip. The surge drum’s hold-up
Calculation of volume changes due to liquid outflow time is generally set between 10-15 minutes, providing
The volume changes due to liquid outflow can be estimated ample time for operator intervention.
using two different methods:
Considering the ample time available for operator inter• Method 1: The flow of nitrogen blanketing is calculated vention and the lack of benefits from designing the nitrogen
to maintain the normal operating pressure in the surge blanket flow with high conservativism using Method 1, it is
drum when the outflow from the drum is continuous, but more pragmatic to adopt Method 2 for estimating the nitrothe inflow to the drum ceases. This estimation uses the API gen blanket gas flow.
2000 liquid outflow method. Licensor does not normally
Pressure changes due to liquid contraction
include thermal inbreathing.
• Method 2: The nitrogen blanketing flow is calculated Volumetric contraction in the surge drum can happen due
to maintain the vessel at a slightly positive pressure (1.1 to the replacement of hot feed with cold feed, especially for
bara) when the outflow from the drum is continuous, but hot hydrocarbon feed.
Reduction of pressure can be estimated as follows:
the inflow to the drum fails. This is calculated based on the
vapour volume change due to the decrease from the normal
liquid level to the very low liquid level at which the con- Liquid volume change (dV) = VNLL x (1- ϱhot/ϱcold)
nected pump is stopped.
Vapour volume above NLL (Vvapour) = VTotal - VNLL
The operation of the surge drum is different from that of
tanks. While tanks are either in receiving or dispatch mode, Pfinal = Pnormal x [Vvapour/( Vvapour + dV)]
surge drums are always in both receiving and dispatch mode.
They are frequently positioned between process units to help Where:
= Normal liquid level volume (m³)
mitigate the impact of flow rate variations between intercon- VNLL
= Vessel total volume (m³)
nected process units. Unlike the typical control objective of VTotal
= Hot liquid density (kg/m³)
maintaining a measurement at a set point, the goal of surge ϱhot
= Cold liquid density (kg/m³)
drum level control is to buffer the changes in controlled flow ϱcold
= Final vessel pressure (bara)
while keeping the liquid level in the vessel within limits. For Pfinal
surge drums, it is usually more important to allow levels to Pnormal = Vessel normal pressure (bara)
= Density (Rho)
‘float’ to minimise flow rate variations. Therefore, the level r
controller must permit this movement and try not to hold the
level close to its set point. Instead, the controller should keep Example calculation:
the surge vessel’s level between its upper and lower limits This example calculation is performed for a diesel hydrotreater feed surge drum (FSD) when hot feed is replaced
with the least possible change to its flow output.
The estimation of nitrogen blanketing for the lean amine with cold feed during hot feed failure. Assuming the FSD
surge drum of two different licensors' diesel hydrotreater will continue to maintain a normal liquid level after replaceunits using both methods is presented in the Table 1. The ment, cold feed with a higher density will have a lower liquid head. The reduction of the liquid head will result in a
calculation details can be found in Appendix 1.
Employing Method 1 to determine the nitrogen blanket reduction in liquid volume at a normal liquid level, and this
for the surge drum may lead to a high degree of conserv- volume reduction is estimated considering liquid volumetric
ativism. This strategy could increase the normal nitrogen contraction.
Required blanketing nitrogen gas
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The hot feed, initially at 125°C, is preheated to 218°C
before entering the FSD. In situations where there is a failure in the hot feed supply, a cold feed is used as a replacement. This cold feed, starting at 40°C, is then preheated to
155°C before being introduced to the FSD.
It is assumed that the FSD has a similar dimension to the
lean amine surge drum of Project A above and the FSD is
operating at the same pressure of 2.5 bara. From this, the
following is calculated:
VTotal
VNLL
ϱ
hot
ϱ
cold
Pnormal
Pfinal
= 78 m³
= 53 m³.
= 700 kg/m³
= 751 kg/m³
= 2.5 bara
= To estimate (bara)
In the case of determining the nitrogen blanketing flow
rate for tanks, the API 2000 method serves as a standardised procedure.
Estimation of inbreathing due to liquid transfer effect
According to Section 3.3.2.2.2 ‘Inbreathing’ of API 2000,
the estimation of inbreathing, resulting from the maximum
outflow of liquid from a tank, necessitates consideration of
the rate of volume change of tank vapour space due to liquid movement.
The requirement for inbreathing, denoted by VinL and
measured in normal cubic meters per hour of air, should
equal the maximum liquid discharging capacity for the tank,
denoted by Vliq and measured in cubic meters per hour. This
correlation is presented in Equation 1. Here, Vliq signifies
the rated capacity of the pump connected to the tank:
Liquid volume change (dV) = 53 X (1- 700/751) = 3.6 m³
VinL = Vliq Vapour volume above NLL (Vvapour) = 78 – 53 = 25 m³
Estimation of inbreathing due to thermal effect
Pfinal = 2.5 X (25/(25+3.6) = 2.2 bara
From the above calculation, it is evident that the pressure
reduction due to liquid volumetric contraction when replacing hot feed with cold feed is relatively minor.
Determination of nitrogen requirement for tank
blanketing
Inert gas systems, like those using nitrogen, help prevent
air from entering a tank when there is a chance of vacuum
generation inside it. These systems make tanks safer by
reducing the chance of creating explosive atmospheres and
minimising the risk of dangerous flashbacks.
However, it is important to note that this nitrogen blanketing system should not replace vacuum relief devices.
Despite having an inert gas system in place, the vacuum
relief devices need to be large enough to handle situations
where the inert gas might not be available.
Vacuum conditions in a tank can occur due to two main
causes:
 Liquid transfer effect: This phenomenon occurs when
there is an outflow of liquid from the tank without a corresponding inflow, creating a vacuum.
 Thermal effect: Changes in atmospheric conditions,
such as a drop in temperature or shifts in weather patterns
(like wind changes or precipitation), can lead to the contraction or condensation of vapours, consequently resulting
in a vacuum.
Eq. 1
The API-2000 standard, specifically Section 3.3.2.3.3
‘Thermal Inbreathing,’ provides guidelines for calculating
inbreathing attributed to thermal effects. As per this
section, the thermal inbreathing of the tank, measured in
normal cubic meters per hour of air, is calculated in line
with Equation 2:
VinT = C X Vtk0.7 X Ri
Eq. 2
Where:
VinT is inbreathing flow rate (Nm³/h)
C is a factor that depends on vapour pressure, average
storage temperature, and latitude (ref API 2000 Table 2)
Vtk, which represents the tank’s vapour volume, is expressed
in cubic meters. For vertical cylindrical tanks, it is acceptable to calculate this volume based on the tank shell height,
not including the tank roof.
The term Ri refers to the reduction factor for insulation.
In situations where no insulation is used, such as this, Ri is
assigned a value of 1.
When establishing inbreathing requirements, the design
basis must account for the most significant single contingency or any plausible combination of contingencies. To
ensure comprehensive coverage, the total normal inbreathing of the tank should, at a minimum, consider the combined
effects of liquid transfer and thermal conditions during
normal operations. As a result, the normal inbreathing
C factors
Latitude
C factor for various conditions
Vapour pressure similar to hexane Vapour pressure higher than hexane, or unknown
Average storage temperature, ºC
<25
≥ 25 <25
≥ 25
Below 42° 4
6.5 6.5
6.5
Between 42° and 58° 3
5 5
5
Above 58° 2.5
4 4
4
Table 2
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requirement for the tank is derived by summing the values
from Equations 1 and 2, capturing both the liquid transfer
and thermal influences on the inbreathing system.
pragmatic approach, a more realistic estimation of nitrogen
demand for tank inbreathing can be achieved, potentially
reducing the overall nitrogen consumption significantly.
Frequently, when estimating the total nitrogen inbreathAlternate method for estimating nitrogen
ing requirement for a tank farm, a common practice is to
inbreathing quantity
add the inbreathing due to liquid movement to the thermal
According to API 2000 section 3.5.3, when an inert gas inbreathing for all tanks. However, it is important to note
system is employed to prevent the entry of air into the that, for a specific service, typically only one tank operates
tank during vacuum conditions, thereby reducing the risk in despatch mode, driven by the connected pump. This genof a potentially explosive atmosphere inside the tank, the eral addition of inbreathing due to liquid movement leads
Annex F method can be utilised to estimate inert gas blan- to a significant increase in the normal nitrogen inbreathing
keting for tanks.
requirement for the entire tank farm. As a result, a more
In the context of refineries, tank vents are typically with- accurate and pragmatic approach is needed to optimise
out any flame arrester, and thus, the sizing of venting nitrogen usage and better reflect the actual operational
devices is determined using Annex F Level 3 equation, as conditions of the tanks.
shown below:
Various interpretations and methodologies have been
observed when estimating nitrogen inbreathing for a tank
0.7
VI = 0.5C • RiVtk + Vpe
farm. To facilitate a comparative analysis of inbreathing
flow rates using different methods, nitrogen blanketing for
VI = 0.12 • Vtk
a selection of representative tanks with representative outflow has been estimated using the following approaches:
Where:
• Method 1: Liquid transfer effect according to API 2000
C is a factor that depends on vapour pressure, average section 3.3.2.2.2 + thermal inbreathing as per section
storage temperature, and latitude (see Table 2)
3.3.2.3.3. In this approach, all tanks are assumed to be
Ri is the reduction factor for insulation
empty, and the outflow of liquid occurs from all tanks when
Ri is 1 if no insulation is used
there is no inflow to any of the tanks.
Vtk is the tank volume
• Method 2: Liquid transfer effect based on API 2000 secVpe is the maximum rate of liquid discharge
tion 3.3.2.2.2 + thermal Inbreathing per section 3.3.2.3.3.
Here, all tanks are assumed to be 50% empty, and the
In both the methods above, the calculation of tank outflow of liquid occurs only from one tank for a specific
thermal inbreathing requirement adopts a conservative service, with no inflow to that tank.
approach, assuming that tanks are empty and filled with air • Method 3: Inbreathing as per Annex F of API 2000. In this
before cooldown. However, it is believed that a more prag- method, all tanks are assumed to be 50% empty, and the
matic approach can be adopted, leading to a reduction in outflow of liquid occurs only from one tank for a particular
the normal nitrogen demand of the tank farm, which often type of liquid, with no inflow to that tank.
accounts for more than 20% of the overall refinery’s normal
For detailed calculations, refer to Appendix 2, and a sumnitrogen demand.
marised result of various methods is shown in Table 3.
In practice, storage tanks are typically not operated comTable 3 shows that the nitrogen inbreathing requirement
pletely empty. They usually maintain some minimum inven- estimated using Method 1 is 1.7 times more than that estitory levels. For product tanks in a specific service, one tank mated using Method 2 and 3.3 times more than that estimay be in receiving mode, another under certification, and mated using Method 3. Additionally, Method 2 provides an
another in despatch mode. Intermediate tanks are com- estimated nitrogen requirement 1.9 times higher than that
monly kept at around 50% level, while feed tanks are tar- estimated using Method 3. These comparisons highlight
geted to be kept full of inventory.
the significant differences in nitrogen inbreathing estimaIt is pragmatic to consider a 50% level of inventory in the tions based on the different methods used.
tanks while estimating the nitrogen requirement for tank
The thermal inbreathing requirements given by API 2000
inbreathing. This approach finds support in Annex F of API are approximately equivalent to a rate of change in ambient
2000, which states that: “If several tanks with a common temperature of 38°C per hour. While this may seem excesinert gas supply are divided so that no single tank has a sive, it reflects a change of about 10°C in 15 minutes, which
capacity exceeding 20% of the total capacity of all tanks, the is not uncommon as storm fronts move through. It also concalculated values may be reduced by 50%.” By applying this siders the impact of sudden cold rainfall on the shell of the
tanks.
Normal nitrogen inbreathing rate
It is essential to consider that
the change in volume is comMethod
Liquid transfer (Nm³/h)
Thermal inbreathing (Nm³/h)
Total (Nm³/h)
monly converted into equivalent
Method 1
31,082
283,551
314,633
volumetric rates based on air
Method 2
9,296
174,546
183,842
at standard or normal condiMethod 3
9,296
87,273
96,569
tions. Consequently, the voluTable 3
metric rates may not appear as
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Technical nuances and best practices in refinery units
 Gaseous nitrogen for purging
One of the most frequent uses of nitrogen is to purge equipment of explosive or hazardous vapours before lining up the
vessel after maintenance or handing it over for maintenance.
This is usually done using a pressure/de-pressure cycle.
The cycles needed to ensure the oxygen concentration is
below the Lower Explosive Limit (LEL) can be determined
through the equation:
n = log[(Ci-Cn)/(Cf-Cn)]/log (Pf/Pi)
Eq. 3
Where:
Cn = mol% oxygen in nitrogen
Ci = mol% oxygen initially in space to be purged
Cf = mol% oxygen finally in space to be purged
Pi = Initial pressure in bara
Pf = Final pressure in bara
n = Number of pressure/de-pressure cycles
For oxygen removal from equipment, a method involving multiple pressurisation and depressurisation cycles is
employed by refiners. The equipment is first pressurised to
the maximum nitrogen header pressure. It is then depressurised from several points until a slight positive pressure
of approximately 0.5 barg is reached. This process of pressurising and depressurising is repeated until an oxygen
concentration below 4 mol% is achieved. For some cases,
like reformer or hydrotreater, target oxygen is less than 0.5
vol%. Once this level has been reached, the equipment is
pressurised to its normal operating pressure using nitrogen, ensuring it is prepared for hydrocarbon introduction.
The method of pressurising equipment to the maximum
nitrogen header pressure is associated with the following
drawbacks:
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100
% of nitrogen flow
equivalent displacement, especially when the assumed
operating or ambient temperatures do not align with standard or normal conditions. The calculated inbreathing considers the assumption of ambient airflow through the tank
vent, where it is customary to consider the ambient air to be
at normal or standard conditions.
In cases where a medium other than air is utilised for
vacuum relief, it might be necessary to convert the rate to
an air-equivalent flow. Adjustments may be required for
inbreathing if the inbreathing medium significantly differs
from air. However, no adjustments are necessary for nitrogen, as the molecular weight of nitrogen (28.02) and air
(28.96) exhibits only a marginal difference (3.3% variation
in molecular weight).
In conclusion, facilities should assess the nitrogen
inbreathing requirement for tanks using the appropriate method as described earlier. By doing so, they can
potentially achieve significant reductions in overall nitrogen requirement, leading to substantial savings in Capex
and Opex while ensuring safety and tank integrity are not
compromised. This prudent approach allows for efficient
resource allocation while maintaining the highest standards
of operational safety.
100%
98%
94%
87%
80
78%
66%
60
47%
33%
40
20
0
2
3
4
5
7
6
8
9
Vessel pressure (bara)
Figure 1 Reduction of nitrogen flow rate vs vessel pressure
a) Flow reduction: As equipment is pressurised, a notable
decrease in the nitrogen flow rate is observed, particularly
when vessel pressure exceeds half of the header pressures.
This phenomenon can be seen in Figure 1, which highlights
the decline in flow rate under various pressures where the
nitrogen header pressure is at 9 bara.
b) Excessive consumption: To estimate the nitrogen volume needed to achieve an oxygen content below 4 mol%,
a comparative estimation is carried out for three different
scenarios. In each scenario, the first cycle of nitrogen pressurisation of the vessel, which is full of air, is considered.
The vessel is pressurised from atmospheric pressure to
different pressurisation scenarios. Here are three scenarios
illustrating the differences:
Scenario 1: Pressurised to 9 bara
Scenario 2: Pressurised to 5 bara
Scenario 3: Pressurised to 3 bara
Upon reaching the targeted pressure, if the oxygen content is below 4 mol%, the vessel is depressurised to its
normal operating pressure of 3 bara, making it ready for
hydrocarbon introduction. Otherwise, it is brought down
to 1.5 bara and then pressurised to start the next cycle
of pressurisation/depressurisation. This cycle continues
until the oxygen content meets the desired threshold, after
which the vessel is pressurised to 3 bara using nitrogen.
The results are shown in Table 4.
In Table 4, it can be observed that for Scenario 1, the
required nitrogen volume is the highest, being 1.5 times
that of Scenario 2 and two times that of Scenario 3, even
though only one cycle of pressurisation with nitrogen is
required in Scenario 1.
Key takeaway: Limiting pressurisation to half of the nitrogen header pressure is both cost-effective and efficient, as
supported by the provided scenarios.
 Start-up nitrogen for hydroprocessing units’
high-pressure (HP) section
The start-up of hydroprocessing units demands a substantial amount of nitrogen, primarily for leak tests and
inertisation. For a typical 1,000 m3 volume hydroprocessing high-pressure loop, three cycles of pressurisations
and depressurisations between 1.5 barg and 5 barg are
essential. The goal is to reach O2<0.5 mol%, necessitating
approximately 14,000 Nm3 of nitrogen.
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Comparison table – pressurising to different levels
Cn = mol% oxygen in nitrogen
Ci = mol% oxygen initially in space to be purged
Cf = mol% oxygen finally in space to be purged
Pi = Initial pressure in bara
Pf = Final pressure in bara
n = Number of pressure/de-pressure cycles
Required nitrogen volume(Nm3) [vessel volume -V ]
Total nitrogen volume for scenario (Nm³)
Scenario 1 Scenario 2 Scenario 3
1st Cycle
1st Cycle 2nd Cycle
1st Cycle 2nd Cycle
0.10
0.10
0.10
0.10
0.10
21.00
21.00
4.28
21.00
7.07
2.42
4.28 2.19
7.07 3.58
1.00
1.00
1.50
1.00
1.50
9.00
5.00 3.001
3.00 3.0
1
1 1
1
1
8V
4 V
2V
2 V
2V
8 V
6V
4V
Note 1: Pressurisation is limited to 3 bara as oxygen content was below the target value of 4 vol%.
Table 4
Typically, hydroprocessing units undergo leak testing
at varying pressure levels using nitrogen. For the context
of this article, 20 barg is assumed as the maximum leak
test nitrogen pressure. Upon successful completion of this
test, a nitrogen circulation at 20 barg is established. The
process involves an initial cycle for detecting and rectifying leakages. Then, a second cycle is used to stabilise the
nitrogen circulation. Under conditions where the HP loop
is successfully tested at 5 barg and pressurised in the first
cycle from 5 barg to 20 barg, the total nitrogen requirement
amounts to 35,000 Nm3, which includes leak test, inertising
and pressurisation.
Frequently, hydroprocessing licensors specify a nitrogen
amount with a peak flow rate of 3,000 Nm3/h. The standard configuration for the nitrogen line to the HP loop is
3in, equipped with a full-bore globe valve. As per industry
standards, the allowed depressurisation rate stands at 20
bar/hour, prompting operators to fully open the 3in globe
valve. With a 3in API 600 type globe valve with a Cv of
106 for a 1,500 lb rating, the flow results in 12,000 Nm3/h.
In contrast, when considering compressible flow through
a 3in 80 sch. pipe, the nitrogen flow rate is 8,000 Nm³/h
where upstream nitrogen pressure is at 8 barg and downstream at atmospheric pressure.
Key takeaway: The start-up nitrogen line for reactor loop
pressurisation should be sized to match licensor-prescribed
nitrogen demand in the utility summary.
A noteworthy observation is that the peak nitrogen
demand of a hydroprocessing unit significantly influences
the overall peak demand of the refinery, especially when the
refinery has multiple hydroprocessing units. At the design
stage, it is proposed by some refiners that the peak nitrogen
demand for hydroprocessing units be met using a tanker
connected directly at the unit level. By this method, the
hydroprocessing units’ peak nitrogen demand is removed
from the overall refinery nitrogen balance. Consequently,
potential savings are realised, as the requirement for a
nitrogen liquid tank and vapouriser is eliminated. However,
practical implementation can pose challenges due to limited access during unit shutdowns, especially during catalyst loading/unloading. A prudent approach is to inertise
one hydroprocessing unit at a time.
To minimise risk, at present, hydroprocessing units are
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ARAMCO.indd 72
PTQ Q1 2024
not practising vacuum pulling while inertising the HP loop.
This precaution helps to prevent potential hazards, such as
oxygen entering the system due to leaks. If oxygen does
enter, it could react with hydrocarbons and catalysts in the
system, as well as compromise the iron sulphide passivation layer.
Key takeaway: For optimal refinery operations, inertise
one hydroprocessing unit at a time, considering a minimum
peak demand rate of more than 3,000 Nm3/h for a 3in nitrogen line.
 Start-up nitrogen for hydroprocessing units
low-pressure (LP) section
As discussed in the previous section, hydroprocessing units
are identified as one of the major units demanding peak
nitrogen during start-up. Because of this, the hydroprocessing unit’s LP section is commonly inertised with steam.
Once sufficient steam out is completed, fuel gas is introduced after steam venting to the atmosphere is boxed up.
The LP section is pressurised to the maximum fuel gas pressure, which is typically around 4 barg. However, it should
be noted that if the normal pressure of the stripper exceeds,
say, 10 barg, the provision for nitrogen pressurisation to the
LP section is considered prudent since the nitrogen header
pressure is approximately 8 barg. Such nitrogen pressurisation is found essential during the start-up phase, especially
when the stripper requires pressurisation beyond 4 barg.
Key takeaway: It is recommended to provide a nitrogen connection in addition to a fuel gas connection for the LP section.
 Gap control for blanketing gas for vessel
Normally, the surge drum level is permitted to fluctuate
within a small band, typically within 5%, instead of maintaining strict control. Due to this small fluctuation in level, a
swing in the drum pressure is caused. This pressure swing
causes the blanketing valve to open when the level drops
and the vent to flare to open when the level rises. The continuous activation of these valves leads to a loss of nitrogen
from the surge drum. Typically, a dead band is incorporated
into the surge drum pressure controller output, allowing
the pressure to fluctuate without opening the valves in the
nitrogen and flare lines for minor demands.
Key takeaway: By implementing this gap control for all
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blanketing pressure controllers, the consumption of nitrogen can be minimised.
 Flow through utility station of nitrogen
Different approaches for determining the normal and peak
demand for refiners exist, and the determination of overall
normal and peak demand is considered beyond the scope
of this article. Nonetheless, it is observed across refiners
that for both normal and peak nitrogen demand, the nitrogen flow through at least one utility station is considered.
The nitrogen flow through a utility station is typically seen
to range from 200 Nm3/h to 400 Nm3/h. It was observed
that when considering compressible flow through a 0.75in
pipe, the nitrogen flow rate is 350 Nm³/h where upstream
nitrogen pressure is at 8 barg and downstream at atmospheric pressure. Utility station sizes very often are 1in.
Key takeaway: The designer should consider the maximum
possible nitrogen flow through a utility station while estimating normal and peak nitrogen demand.
Conclusion
This article emphasises key considerations for nitrogen
management in refinery operations at the design stage,
focusing on nitrogen blanketing in surge drums and tankage. The findings reveal that conventional guidelines,
notably those based on API 2000 standards, may lead to
overestimation of nitrogen requirements. Such overestimation not only elevates nitrogen demand but also contributes
to operational inefficiency and waste.
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ARAMCO.indd 73
Beyond the scope of tank and surge drum blanketing, the
articles outlines crucial best practices for handling nitrogen
throughout various units in a refinery. This encompasses
optimal purging protocols, sizing of nitrogen lines for HP
hydroprocessing units, actual peak nitrogen flow through
the utility station, necessity of nitrogen connection for the
LP section of hydroprocessing units, and effective control
mechanisms for gas blanketing.
In summary, this article endorses a customised approach
to managing nitrogen, considering actual operational
scenarios. It suggests a balanced use of both standard
and alternative methods without compromising safety.
Implementing these recommendations has the potential to
result in significant cost reductions, more efficient resource
allocation, and the upholding of stringent safety norms.
Appendices 1 and 2 can be viewed in the digital issue.
Rajib Talukder is a Process Specialist in the Global Manufacturing
Excellence department at Aramco, Saudi Arabia. He has more than
30 years of experience in process engineering and holds a B.Tech in
chemical engineering from NIT Tiruchirappalli, India.
Email: [email protected]
Prabhas K Mandal is an Operations Engineer Specialist at Aramco.
He has more than 30 years of experience in petroleum refining, and
supports front end design development for capital projects. He holds a
B.Tech in chemical engineering and a M.Tech in petroleum engineering.
Email: [email protected]
23.10.2023 07:52:37
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Simulating VGO, WLO, and WCO
co-hydroprocessing: Part 2
Economic analysis performed when co-hydroprocessing VGO, WLO, and WCO shows
that WLO studied percentages increase hydrocracking unit net profits
Mohamed S El-Sawy, Fatma H Ashour and Ahmed Refaat Cairo University
Tarek M Aboul-Fotouh Al-Azhar University
S A Hanafi Egyptian Petroleum Research Institute
P
art 1 of this study (PTQ, Q4 2023) presents simulation
and analytical studies made on vacuum gasoil (VGO),
waste lubricating oil (WLO), and waste cooking oil
(WCO) co-hydroprocessing over commercial hydrocracking catalyst. This study follows our previous work which
studied the co-hydroprocessing of VGO, WLO, and WCO
experimentally on a lab-scale reactor, utilising the commercial hydrocracking catalyst. Most fuel producers prefer to
utilise existing units to co-hydroprocess WLO, WCO, and
VGO rather than install new separate hydroprocessing units
because there is a high degree of similarity between units
used to hydroprocess petroleum cuts and units to hydroprocess waste oils mixture with VGO.
In this discussion, market analysis and economic studies
were conducted to illustrate the flexibility and prevalence of
using these unconventional feed mixtures (blends of VGO
with WLO and WCO) as industrial feedstock during the
COVID-19 pandemic, which caused transportation limitations and market upsets. The analysis focused on the fluctuations in crude oil, petroleum fuels, and bio-diesel prices last
year. By mixing WLO and WCO with VGO as hydrocracking
feed, good opportunities for expense optimisation and net
profit maximisation can be found, especially when crude oil
prices increase.
Resource optimisation
Many countries were highly affected by the COVID-19 pandemic and its consequences on global markets and economics. Hard times usually lead to a concentrated effort to
use all available resources. One of these resources is waste
oils and their application to convert to fuels with traditional
esterification for WCO, distillation followed by extraction
for WLO or hydroprocessing of both. Waste recycling has
several benefits, including using waste as an energy source,
which will suppress toxic and hazardous emissions into the
environment and reduce greenhouse gas (GHG) emissions.
In addition, waste recycling is stimulating development in
the region as well as aiding social structure, especially in
developing countries. Furthermore, the refining industry
faces numerous challenges in producing high-quality fuels
at reasonable costs. Cold flow properties are often a concern
when dealing with products derived from hydroprocessing
waste oils or VGOs.1,²
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CAIRO UNI.indd 75
Generally, the hydroprocessing unit consists of a reaction
section and a fractionation section to separate the reaction
products into desired product streams. Hydroprocessing
units’ reactors commonly use a trickle bed reactor (TBR) configuration due to its simplicity, reliability, and good operability. A TBR is a fixed bed reactor with a trickle flow regime of
hydrocarbon and hydrogen mixture moving from the top to
the bottom of the reactor, passing through catalyst bed(s).
Usually, heavy hydrocarbons and middle distillates hydroprocessing reactors consist of more than one catalyst bed with
intermediate hydrogen quenching streams to control reaction
temperature, as all hydroprocessing reactions are exothermic.
Co-hydroprocessing of VGO, WCO, and WLO is a mixedphase reaction where liquid moves downwards and forms
a laminar stream around the catalyst pellets and hydrogen
is distributed through available voids in the catalyst bed.
Reactions start by diffusing a dissolved hydrocarbon feed
mixture and hydrogen in the catalyst pores, reaching the
active sites. On the active sites, cracking and hydrogenation
reactions occur. These are enhanced by increasing the reaction temperature and hydrogen partial pressure.³
Modelling and simulation are important tools for optimising plant profit and operating conditions. Modelling and simulation of an existing industrial hydroprocessing unit need
operating conditions and product yield identification. The
simulation model case of the hydroprocessing unit consists
mainly of a reaction section and a fractionation section. The
most complicated aspect of building the simulation model is
the calibration of the kinetic model, which forms the core of
the simulation.
The reaction kinetics depend on many factors, such as
reaction temperature, hydrogen partial pressure, liquid
hourly space velocity (LHSV), feed composition, and catalyst
configuration. From these data, in addition to product yields
and specifications, simulation software can predict calibration factors that will be the core of the simulation model.
To overcome the complexity of building hydroprocessing
reactions kinetic models, many studies and technical papers
recommend using commercial software to execute the modelling and simulation of hydroprocessing units.⁴
An extensive literature review has been conducted to
study the technologies and equipment used industrially in
the hydroprocessing of WCO and WLO individually, and
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101
Conversion wt%
100
99
Mix 1 Pred. (VGO 80% + WCO 20%)
Conv. (%)
98
Mix 3 Pred. (VGO 80% + WLO 10% + WCO 10%)
97
Mix 1 act. (VGO 80% + WCO 20%)
96
Mix 3 act. (VGO 80% + WLO 10% + WCO 10%)
95
Mix 2 Pred. (VGO 80% + WLO 20%)
94
93
Mix 4 Pred. (VGO 70% + WLO 20% + WCO 10%)
92
Mix 2 act. (VGO 80% + WLO 20%)
91
370
380
390
400
410
420
430
440
450
Mix 4 act. (VGO 70% + WLO 20% + WCO 10%)
Temp. (˚C)
Figure 1 Predicted and actual reaction conversion
the co-hydroprocessing mixture blended with petroleum
feedstock. Axens has recently introduced a new proprietary
technology called Revivoil, developed jointly with Itelyum
(formerly Viscolube Italiana SpA). This technology is a significant step forward in waste lube oil re-refining and has the
potential to accelerate its success.
UOP has also developed with ENI a proprietary technology called Ecofining for hydroprocessing plant-derived oil.
Feedstocks include plant-derived oils like soybean, rapeseed and palm. The co-processing of waste oils is not only
of interest to process technology developers, but also to
refineries. For example, Petrobras has developed the H-BIO
hydrogenation process to produce renewable diesel using a
mixture of waste vegetable oil and mineral oil in existing oil
refineries through hydrotreating units.
The co-processing of waste frying oils in a gasoil
hydrodesulphurisation unit (HDS-I) at CEPSA’s refinery in
Tenerife has been successful. CanmetENERGY’s research
centre supports and funds such research activities. It has
been observed that most refiners choose to inject WCO (on
a large scale) or WLO (on a small scale) with VGO for co-hydroprocessing units, rather than installing a separate unit to
hydroprocess pure WCO or WLO, taking into consideration
the high degree of similarity between technologies and catalysts used in these units. The novelty of this work is to study
the co-hydroprocessing of VGO, WCO, and WLO blend over
commercial industrial hydrocracking catalyst. This will be followed by an economic study of the produced model in the
recent market changes caused by COVID-19.5,6,7
The aim of this study is to simulate a conceptual design of
an industrial hydrocracking unit that utilises the same catalyst as our previous experimental work.1 This conceptual
design has been performed using Aspen Hysys V.11, which
comes with a built-in hydrocracker model (HCR). This model
simulates the hydroprocessing of light and heavy petroleum
fractions based on a built-in reaction network and kinetic
lumps. This simulation can be used to evaluate technically
and economically co-hydroprocessing normal unit feedstock
of VGO vs blends of unconventional feedstocks of WCO and
WLO with VGO.
Process simulation case
The industrial hydrocracking unit licensed by UOP
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PTQ Q1 2024
(commercially called Unicracking unit) was simulated using
Aspen Hysys V.11. This unit was selected because it utilises
the experimentally used catalyst (TK-711 and DHC-8) and a
similar reactor bed configuration. The reaction section of the
unit consists of two reactors. The first reactor has three beds,
with one for hydrotreating and the other two for hydrocracking. The second reactor has two beds, both for hydrocracking. All five beds are roughly equal in weight. The unit is
designed to process 33,500 barrels per stream day (BPSD)
of combined feed consisting mainly of vacuum gasoil (VGO)
from the vacuum distillation unit and heavy cocker gasoil
(HCGO) from the delayed cocker unit. The unit is targeted to
produce light fuel products from heavy petroleum distillates
while removing the majority of impurities such as sulphur,
nitrogen, and oxygen.
Performance evaluation of simulation model
The hydrocracking unit represented in the simulation case
includes two main sections: the reaction section and fractionation section. The performance of the reaction section
can be evaluated by comparing the predicted feed with the
actual feed conversion. Figure 1 shows both the actual and
predicted feed conversion wt%, represented by solid and
dash lines respectively.
A clear positive gap can be observed between the actual
and predicted values of conversion. This gap widens as the
WCO content in the feed mixture increases and reaches its
minimum value or disappears completely when WCO is not
present in the mixture. This observation aligns with the results
of our previous work, which clearly states that increasing the
WCO content in the feed mixture increases catalyst acidity
and activity, leading to a higher reaction conversion at the
same reaction temperature. The model provides accurate predictions of the relationship between reaction temperature and
conversion profile in the hydrocracking reactor. This is important for estimating product yields and hydrogen consumption
(see Figure 2). This prediction tool helps in anticipating the
operating cost of each case and determining its feasibility.
There are seven different products in the simulated hydrocracking unit, namely: purge gas, fuel gas, LPG, hydrocracked
naphtha (represented as gasoline in this study), kerosene
(generally known as jet fuel or dual-purpose kerosene
[DPK]), diesel (ultra-low sulphur diesel according to Euro
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n
1
AADs = –n ∑(|Ypred.- Yact.|)
i=1
for the 16 runs expressed in the following graphs for product property value.⁸ These AAD values help in evaluating
the degree of variation between actual and simulation cases.
This represents the prediction of the model on each product
yield rather than the overall yield, which is the revenue key of
the refinery. In contrast, absolute deviation shows how the
model affects the estimation of the refinery profit by considering deviations in the same scale towards overall production.
Figure 4 compares the predicted gasoline yield (dash lines)
and actual gasoline yield (solid lines) from studied test runs.
It is evident that the predicted values are very close to the
actual values in the range of 380-400°C. This is the recommended operating window of the commercial catalyst used
in this study, as stated by the catalyst manufacturer and process unit licensor. Table 1 shows the calculated overall AADs
for each studied product yield and stream property value.
Market and economic analysis
Crude oil prices are the most determining factor for fuel costs.
Available crude oil price trends show gradual ascending logic
behaviour, with two sharp declines at the end of 2018 and
the beginning of 2020. The first decline was caused by political negotiations about production quantities ruled by the
Organization of the Petroleum Exporting Countries (OPEC),
especially the Kingdom of Saudi Arabia and its share in the
oil market competing with Russia and Iran.
The second decline was caused by the COVID-19 pandemic. Due to the pandemic, there were restrictions on movements, especially across countries, leading to a decrease in
fuel demand and hence a reduction in crude oil prices. In
response, the oil sector adjusted by reducing fuel production to achieve price balance. There was also a decrease in
movement restrictions, the production of new vaccines, and
an increase in the number of vaccinated people to achieve
herd immunity or community immunity. These rapid changes
in crude oil prices were interesting to study. In this section, a
brief economic analysis studies how the business model of
the hydrocracking unit changed over the previous year.⁷
H2 make up Nm3/Sm3 of fresh HC feed
490
480
H2 M/U Nm3/Sm3 fresh feed
5 specifications), and unconverted cooking oil (UCO). The
four products that are the main focus of this study are LPG,
gasoline, kerosene, and diesel, as they make up more than
95% of the total production. Figure 1 and other figures presented in this study show a comparison between the model
predictions and actual values of resulting product yields. The
average absolute deviations (AADs) are calculated using the
following equation:
470
460
450
440
430
420
410
400
370
380
390
400
410
420
430
440
450
Temp. (˚C)
Mix 1 Pred.
(VGO 80% + WCO 20%)
Mix 2 Pred.
(VGO 80% + WLO 20%)
Mix 3 Pred. (VGO 80% +
WLO 10% + WCO 10%)
Mix 4 Pred. (VGO 70% +
WLO 20% + WCO 10%)
Figure 2 Predicted make-up of hydrogen from
hydrocracking simulation model at different reaction
temperatures and feed mixtures
In contrast, looking at the long-term behaviour of the oil
market, supply is ensured since new deposits are continuously discovered. However, despite the steady supply, the
demand for oil is not expected to increase as environmental
restrictions become more stringent in developed countries.
For example, the International Maritime Organization (IMO)
lowered the limit for sulphur content in marine fuel from
3.5% to 0.5% in 2020.
When reviewing the prices for VGO, WCO, and WLO, it
has been noticed that there is a narrow margin between the
selling price of ultra-low-sulphur diesel, jet fuel, and gasoline
and feedstock price. This indicates that the fuel market for
fossil fresh feed and waste recycle feed is highly competitive. As a result, selecting the capacity of the processing
plant needs to be done with great care to ensure profitability.
This study has already selected the process capacity, as the
research work depends on the commercial catalyst used in
the existing plant, while the operating conditions of this plant
are used in building the simulation model.
It is worth mentioning that research work has confirmed
the availability of WCO and WLO quantities in the local market. This ensures a stable supply chain and stable production
of the hydrocracking unit under the studied feed mixtures
and pre-selected unit processing capacity.
Based on this data, the capacity of the hydrocracking unit
AAD values at different temperatures for each studied product yield and product property value
Gasoline yield
Kerosene yield
Diesel yield
(Kerosene + diesel) yield
AAD @380 °C
0.43
0.99
0.79
0.06
AAD @400 °C
0.18
0.98
0.41
0.03
AAD @420 °C
0.28
0.98
0.68
0.06
AAD @440°C
0.38
0.98
0.94
0.12
AAD
0.32
0.98
0.71
0.07
Table 1
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Operating cost items
UOM basis
Hour
Nm3
Nm3
Nm3
kWh
Ton
m³
10000
Cost, $
250
0.21
0.18
0.08
0.07
14.7
0.24
Net profit (US $/hr)
Item
Indirect operating cost
Fuel gas cost
Natural gas cost
Hydrogen make-up cost
Electricity cost
Steam cost
Cooling water cost
15000
2
3
T = 380˚C
T = 400˚C
4
-10000
-15000
-20000
Feed mixture
T = 440˚C
price continues to rise. Figure 6 shows that the profit margin increases as the price of crude oil compared to waste oil
increases. Finally, economic models indicate that WLO offers
significant cost savings and can increase unit net profit,
regardless of fluctuations in crude oil prices.
Conclusion
Commercially available software was used to build a simulation case of an industrial hydrocracking unit using the same
catalyst and reactor configuration as our previous experimental runs.¹ This case is a reliable prediction tool, with only
a minor deviation from actual mass, heat balance, and product specifications. The total reaction conversion values predicted by the simulation model of 16 run cases show a good
match between the simulation model and actual values, with
a positive gap between the actual values in most cases.
This gap widens as the WCO content in feed mixtures
increases. This happens because the acidic nature of WCO
increases catalyst cracking activity, leading to enhanced
reaction conversion under the same operating conditions
of reaction temperature, hydrogen partial pressure, and
LHSV. The Aspen Hysys built-in fluid package (HCRSRK)
needs to be modified to accurately predict hydrocracking
catalyst activity in the presence of WCO, accounting for the
45000
40000
Net profit (US $/hr)
25000
20000
15000
10000
5000
0
T = 420˚C
Figure 3 Net profit values of the studied cases at Dated
Brent = 18.8 $/bbl
30000
Net profit (US $/hr)
1
-5000
-30000
has been set to 297 tons of hydrocarbon feed per hour. This
implies total processing of around 98,000 tons of hydrocarbon oil feed mixture per year, with more than 90% of the
feed mixture being converted into lighter valuable hydrocarbon product. As previously stated, three economic business
models are examined in this study.
The first model was made just before the start of the
COVID-19 pandemic. It was selected at a Brent crude oil
price of 18 $/bbl on 16 April 2020, affected by a worldwide
lockdown. The second model was created after the crude
oil price stabilised and air flights were partially opened. The
Brent crude oil price was 42 $/bbl on 29 June 2020. The
third model was created at the beginning of 2021 on the 12
February at a Brent crude price of 62 $/bbl when normal life
conditions had resumed after more than a third of the world’s
population had been vaccinated with the COVID-19 vaccine.
The economic evaluation of the research work at three
selected times showed different net profit rates depending
on feedstocks and product prices. Economic analysis for
each model are based on operating expense details mentioned in Table 2.
The economic data of the three studied scenarios are represented in Figures 3, 4 and 5. Crude oil price increases benefit the net profit of the 16 studied cases. It is also observed
that the highest net profit is achieved for the feed mixture
evaluated at reaction temperature of 400°C, regardless of
the crude oil price.
So, there is a great opportunity for applying the studied
feed mixtures to increase profit, especially if the crude barrel
1
2
3
4
Feed mixture
T = 380˚C
T = 400˚C
T = 420˚C
T = 440˚C
Figure 4 Net profit values of the studied cases at Dated
Brent = 41.8 $/bbl
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35000
30000
25000
20000
15000
10000
5000
0
-5000
CAIRO UNI.indd 78
0
-25000
Table 2
78
5000
1
2
T = 380˚C
T = 400˚C
Feed mixture
3
T = 420˚C
4
T = 440˚C
Figure 5 Net profit values of the studied cases at Dated
Brent = 62 $/bbl
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08/12/2023 17:11:43
actual resulting activity increase caused by the acid nature
of WCO.
Predicted values of gasoline and middle distillates (kerosene and diesel yields) product yields from the simulation
case closely match the actual values from the experimental
test run. However, the predicted individual values for kerosene and diesel do not match the experimental test run
values due to different cut points between the experimental
test runs and the fractionator built in the simulation case.
Hydrogen consumption in the test runs is calculated
through the simulation case, showing that accepted hydrogen consumption rises with an increase in conversion,
reaction temperature or WCO content. Finally, an economic
analysis of the proposed alternative feed mixtures shows
high flexibility during energy market upsets caused by the
COVID-19 pandemic. This analysis shows that using WLO
with studied percentages increases the hydrocracking unit’s
net profit (see Figure 7).
On behalf of all authors, the corresponding author states there is no
conflict of interest.
References
1 El-Sawy M S, Hanafi S A, Ashour F, Aboul-Fotouh T M,
Co-hydroprocessing and hydrocracking of alternative feed mixture
(vacuum gas oil/waste lubricating oil/waste cooking oil) with the aim of
producing high quality fuels, Fuel, Vol 269, pp.117,437, 2020.
2 Inform from website: www.eia.gov/outlooks/steo/archives/apr16.pdf.
3 Elshout R V, Bains C S, Moving up a Tier – Part 2: Upgrading the bottom of the barrel, Hydrocarbon Processing, Vol 97 pp.312, 2018.
4 Bezergianni S, Athanasios D, Temperature effect on co-hydroprocessing of heavy gas oil-waste cooking oil mixtures for hybrid diesel production, Fuel, Vol 103, pp.579-584, 2013.
5 Sbaaei E S, Ahmed T S, Predictive modeling and optimization for an
industrial Coker Complex Hydrotreating unit – development and a case
study, Fuel, Vol 212, pp.61-76, 2018.
6 Naderi H, Shokri S, Ahmadpanah S J, Optimization of kinetic lumping
model parameters to improve products quality in the hydrocracking process, Brazilian Journal of Chem Eng, Vol 35, pp.757-768, 2018.
7 Dagde K K, Puyate Y T, Modelling and simulation of industrial FCC
unit: Analysis based on five-lump kinetic scheme for gas-oil cracking,
International Journal of Engineering Research and Applications, Vol 2,
Issue 5, pp.698-714, 2012.
8 Bhutani N, Ray A K, Rangaiah G P, Modelling, simulation and multi
42500
26001
11775
0
10
0.4
20
30
0.7
40
50
60
70
Dated Brent price (USD)
WLO price/Brent price
WCO price/Brent price
Net profit Case: T400-WLO20-WCO00-VGO80
Figure 6 Effect of change in (crude oil price/waste oils
price) ratio on net profit for the case at 400ºC reactor
temperature and 20% WLO, 0% WCO, and 80%VGO
objective optimization of an industrial hydrocracking unit, Industrial &
Engineering Chemistry Research, Vol 45, Issue 4, pp.1354-1372, 2006.
Mohamed S El-Sawy is a Hydroprocessing Lead Process engineer at
‘Worley’ with a history of working in the oil and energy industry. He
holds a PhD in chemical engineering from the Faculty of Engineering,
Cairo University. Email: [email protected]
Fatma H Ashour is the former Director of the Center of Hazard
Mitigation, Environmental Studies, and Research at Cairo University
and former chairperson of the Chemical Engineering Dept. at Cairo
University. She holds a BSc, MSc and PhD in chemical engineering from
Cairo University.
Ahmed Refaat is an Assistant Professor at Cairo University/King Salman
International University. He has published 12 international publications
and 16 conference papers as well as an invited book chapter in Elsevier.
Tarek M Aboul-Fotouh is an Associate Professor of Petroleum Refining
Engineering in the Mining and Petroleum Engineering Dept. at Al-Azhar
University. He holds a PhD in chemical engineering from Azerbaijan
State Oil and Industry University.
Samia A Hanafi is the Professor of Petroleum Refining at Egyptian
Petroleum Research Institute. She holds a BSc, MSc, and PhD in chemical engineering from Cairo University. She has more than 30 international publications and supervised more than 20 MSc and 10 PhDs.
LPG
WCO
Naphtha
H2
WLO
1.6
1.1
0.5
0.2
Cat.
Co-hydroprocessing
Kerosene
VGO
Diesel
Save money and
environment
Experimental work
Simulation on existing unit
Data validation
Economic
analysis
Figure 7 Represental graphic
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We make
chemistry happen
Sulzer Chemtech is global market leader in reaction, separation,
purification, static mixing as well as polymer processing technologies.
With a comprehensive offering that includes process components all the
way to complete process plants and technology licensing, we can serve
a broad range of industries with key solutions to intensify processes,
increase efficiency and improve product quality.
With an ever-expanding portfolio of cutting-edge products that supports
circularity while reducing material and energy use as well as emissions,
we are the ideal partner to support the net zero transition of businesses
across the chemical and polymer value chains. We also offer our
technology innovations to support the sustainable manufacturing of bioplastics, renewable fuels, chemical recycling for unrecyclable materials as
well as carbon capture technologies.
sulzer.indd 1
08/12/2023 12:56:18
Considerations for crude unit
preflash drums and preflash towers
A guide to debottlenecking, revamping, designing, and operating crude unit preflash
facilities based on literature and the authors’ experience
Henry Z Kister and Walter J Stupin (dec.) Fluor
Maureen Price Maureen Price Consulting LLC
P
reflash drums or towers are extensively used in
crude feed trains between the desalter and the
atmospheric tower heater. Preflash drums or towers
have been discussed by many literature references, each
focusing on one or a few important aspects and providing valuable guidelines. None of these attempted to bring
together all these lessons in a manner that can guide engineers involved in the debottleneck, revamp, design, and
operation of crude units.
Purpose and location in the crude train
In crude oil refining, a preflash drum or tower is a vessel
that flashes a portion of the light components of the crude
as well as some water upstream of the atmospheric tower
charge furnace. The use of preflash drums or preflash
towers between the desalter and the crude atmospheric
tower is typically done to manage crude hydraulics, as part
of grassroots unit design, to increase crude capacity, or to
allow processing of lighter crudes as part of a revamp.
As the preflashing term suggests, the primary function of
these devices is to flash the lighter (volatile) portion of the
crude oil before it enters the furnace inlet control valves.
These control valves distribute the feed to the various
heater passes. Flashing upstream of these valves makes it
impossible to distribute the feed to the heater passes adequately. Pass flow imbalances cause heater bottlenecks,
Top-PA
Naphtha
Water
Mid-PA
Steam
Kerosene
Bottom-PA
Steam
Diesel
Desalter
Crude
atmospheric
column
Preflash
drum
Steam
Gasoil
Water
Crude
preheat
Crude oil
Steam
Crude
heater
Atmospheric residue
Figure 1 Preflash drum scheme with the drum overhead routed to the flash zone of the atmospheric tower
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Top-PA
Naphtha
Water
Mid-PA
Steam
Kerosene
Bottom-PA
Steam
Diesel
Desalter
Crude
atmospheric
column
Preflash
drum
Steam
Gasoil
Water
Crude
preheat
Crude oil
Steam
Crude
heater
Atmospheric residue
Figure 2 Preflash drum scheme with the drum overhead routed to a higher point in the atmospheric tower
rapid coking, and even tube overheating and rupture. The
alternative is to use high-pressure booster pumps with
expensive high-pressure piping and exchangers to prevent
flashing upstream of the valves. In addition, vapourisation
in the crude train dramatically increases the pressure drop,
which may restrict the crude feed rate. Depending on the
configuration, preflashing may also be valuable in debottlenecking the furnace and/or the atmospheric tower, especially when processing lighter crudes (>30° API).
Preflash devices can be located anywhere in the preheat
train, with temperatures typically varying from 300°F to
500°F.1,2 Higher temperatures give higher preflashing rates.
Preflash device pressure often ‘rides’ on the atmospheric
tower pressure, but in some cases preflashing is performed
at higher pressure by adding a control valve in the drum
overhead vapour line. Preflash towers with condensers
have their own pressure control systems.
A key consideration is where the preflash drum overhead
vapour is routed. In most crude trains, it is routed to the
flash zone of the atmospheric tower (see Figure 1). In this
configuration, it debottlenecks neither the furnace nor the
tower. Its only merit, then, is to permit lower pressures to be
used upstream of the furnace control valves. Any unloading it does on the furnace is countered by the need to add
heat in the furnace to make up for the cooler drum overhead vapour bypassing the furnace into the flash zone of
the atmospheric tower. The bypassing of lights raises the
coil outlet temperature, raising the potential for coking or
encountering metallurgical limitation.
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Golden3 presents a case of a unit processing 26.3° API
crude, with the heater coil outlet temperature maintained
at 700°F. Raising the preflash temperature from 275ºF to
400°F reduced the heater duty by 12% but increased the
resid yield on the crude from 48.2% to 51.1%. The significant loss of distillates to resid was because no heat was
added in the furnace to make up for the cooler drum overhead vapours entering the atmospheric tower flash zone.
If one wanted to keep the resid yield unchanged for the
same increase in preflash temperature, the heater coil outlet temperature would have needed an increase of 22°F (to
722°F).
An alternative configuration to debottleneck the furnace
and atmospheric tower is to have the preflash drum overhead routed to a point further up in the atmospheric tower,
as shown in Figure 2. In this configuration, the preflash
drum unloads the furnace and the section of the atmospheric tower below the point of entry of the preflash drum
vapour into the atmospheric tower, which in Figure 2 is
above the diesel draw. The maximum unloading is achieved
with a preflash tower (or pre-fractionator), as shown in
Figure 3. This arrangement gives a large unloading both
on the furnace and the entire atmospheric tower. With
light crudes ( >30º API), debottlenecking of 10-20% can be
achieved using a preflash tower. In some cases, some kerosene can also be drawn from a preflash tower a few trays
above the feed. It has been estimated that approximately
20% of the crude distillation units in North America include
an independent crude preflash tower.2
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Light
naphtha
Top-PA
Naphtha
Water
Preflash
tower
Mid-PA
Steam
Kerosene
Bottom-PA
Steam
Diesel
Desalter
Crude
atmospheric
column
Steam
Gasoil
Water
Crude
preheat
Crude oil
Steam
Atmospheric residue
Crude
heater
Figure 3 Preflash tower scheme
Effect on atmospheric tower stripping:
“The carrier effect”
The unloading achieved by the Figure 2 and, more so, Figure
3 alternatives is not free. The preflashed naphtha bypasses
the flash zone of the atmospheric tower. Naphtha is a light,
and as a light, it helps the stripping in the bottom of the
atmospheric tower. Having it bypass the flash zone means
less stripping of lights from the resid. Stichlmair and Fair4
present charts showing that liquid yield from a flash declines
when light components are added to the mixture. Adding
a light component generates a significant partial pressure
in the vapour phase, reducing the partial pressures of the
heavier components and promoting their stripping.
This effect was studied and discussed at length by Ji and
Bagajewicz5 for the flash zone of the atmospheric crude
tower. They show that when the K-value of a component is
greater than 30, the light component (hexane and lighter)
will have the same stripping effect on a molal basis as
steam. Other naphtha components will have a smaller, yet
significant, stripping effect. When some of these components are removed in a preflash drum or preflash tower and
do not reach the flash zone of the atmospheric tower, there
will be a greater need for stripping steam. Alternatively,
especially if there is a constraint on the stripping steam, it
means a greater loss of gasoil or diesel yield. In one case5
of light crude with no steam increase, the loss was shown
to be as high as 2%. Typically, the steam can be increased
to some extent, and the loss of gasoil to resid with light
crudes is around 0.3-0.5% of the crude. With heavy
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KISTER FLUOR.indd 83
crudes, the loss with no steam increase is much smaller,
often around 0.3%.
Effect on water dew point
When using a preflash tower with an independent condenser/reflux drum system (Figure 3), some of the naphtha is completely bypassed around the atmospheric tower,
which raises the dew point and salt point at the tower
overhead. This is tempered (usually to a small extent) by
the removal of the entrained water in the crude, as well
as some of the water dissolved in the crude, in the preflash tower. As this water ends up in the preflash tower
overhead, it bypasses the atmospheric tower. With most
atmospheric towers attempting to keep a margin (typically
25°F) above the water dew point, the naphtha bypassing
means either cutting the stripping steam (usually practised)
at the expense of larger loss of diesel or gasoil yield to the
resid or raising the atmospheric tower overhead temperature, which loses kerosene to the naphtha.
There are other means of countering the naphtha bypassing. One scheme is to send preflash naphtha or naphtha
recycle to near the top of the atmospheric tower, but this
comes at the price of loading up the upper section of the
tower and reducing its thermal efficiency. Another scheme
is Soun Ho Lee’s idea6 of refluxing the preflash tower with
naphtha from the atmospheric tower and returning the preflash tower vapour to the atmospheric tower (see Figure 4).
Finally, the metallurgy near the top of the atmospheric tower
can be upgraded at a significant cost of course.
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Top-PA
Naphtha
Water
Mid-PA
Semi-preflash
tower
Steam
Kerosene
Bottom-PA
Steam
Diesel
Desalter
Crude
atmospheric
column
Steam
Water
Gasoil
Crude
preheat
Crude oil
Steam
Atmospheric residue
Crude
heater
Figure 4 Preflash tower scheme with reflux from and vapour going to the atmospheric tower⁶
Foaming
Foaming is a prime consideration for preflashing devices in
crude oil distillation. In the words of one expert,7 ‘it is not a
matter of if foaming is occurring, but rather to what degree
it is occurring’. The foaming severity tends to vary with the
crude, with some crudes generating much more severe
foaming problems than others.⁸ Simple ‘bottle shake’ tests
can often provide information on the degree of foaminess.
The foaming could be due to traces of components with
surface active properties combined with the effects of fine
solid particles. Some of these components may originate
in the desalter chemicals or those used for crude recovery
at the well. Many of these chemicals decompose in the furnace, which is why preflash devices foam while stripping
sections in atmospheric towers usually do not. In some
cases, desalter upsets cause episodes of carryover from the
preflash drum.
When foam is carried over with the vapour to the upper
sections of the atmospheric crude column, it adversely
affects the quality of the products. Typical concerns are poor
kerosene and diesel quality and high carbon residue and
metals in atmospheric gasoil (AGO). Flashed crude is dark
and has a high endpoint. When it enters the atmospheric
tower above the flash zone, all product streams below the
entry point will contain flashed crude. Even small amounts
of foam carryover will cause colour and endpoint problems
with kerosene and diesel.
Once the crude gets into the upper sections of the atmospheric tower due to a foamover, it gets into the pumparounds and stays in the system for lengthy periods of time,
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KISTER FLUOR.indd 84
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causing the product quality issue to linger. The crude also
gets into the diesel and kero hydrotreaters and rapidly deactivates their catalysts. Combined diesel and AGO product
yield losses as high as 6 vol % on crude have been reported
due to flashed crude entrained with the preflashed vapour.1,9
The foam also brings naphthenic acids and sulphur into
places not designed to handle them.
Additional adverse effects of foamovers are cavitation of
the preflash drum or tower bottom pump, which can interrupt the feed to the furnace and atmospheric tower and initiate a shutdown. If the drum overhead vapour passes through
furnace convection coils, crude carryover can severely coke
the convection coils. If the drum overhead goes to the atmospheric tower flash zone, the carryover will generate a cold
spot upon tower entry that will suck vapour downward.
Foaming can be controlled, to some degree, by antifoam
injection, typically silicones, upstream of the preflash drum.
This is not favoured by most refiners due to contamination
of products, adverse effects of antifoams or their degradation products on hydroprocessing catalysts downstream,
and high antifoam costs.
For fear of foamovers and their consequences, most refiners route the overhead of their preflash drums to the flash
zone of the atmospheric tower rather than to the upper
sections of the tower (see Figure 1), at the price of forfeiting many of the unloading benefits that preflash drums
can offer. Even when the drums are well-sized and contain
de-foaming devices, many refiners still prefer to route the
drum overhead into the flash zone for fear of the severe
implications of even a few foamover events.
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Figure 5b VTC device
Courtesy of EGS Systems, Inc.
Figure 5a VTC Systems principle of operation
Courtesy of EGS Systems Inc.
This is where the preflash tower is at a major advantage.
Should a foamover occur, it only affects its overhead product and does not contaminate the atmospheric tower or its Figure 6a GIRZ cyclonic gas inlet device
pumparounds and hydrotreaters. In addition, with a pre- Courtesy of Sulzer Chemtech
flash tower, operators get ample warning of a foamover. A
foamover floods the preflash tower trays, which can easily the top, and the liquid drains from the bottom. Figure 6b
be observed by a differential pressure rise (a reliable dif- demonstrates the effectiveness of the GIRZ cyclonic gas
ferential pressure transmitter must be provided!). Once the inlet device in preventing foamovers. However, even though
operators see a differential pressure rise, they have enough this technology helps reduce the chances of foaming, it was
time to divert the naphtha product out of the product tank recommended⁶ that the preflash drum should be sized large
into a slop tank, preventing any contamination.
enough to prevent foaming. Even though vortex foam sepA thorough discussion of foam-related issues and their arators are highly reliable, infrequent failures have occurred,
control when using crude unit preflash drums is presented mainly due to mechanical issues involving supports, and it
by Barletta, Hartman, and Leake.1 This article discusses in takes only one good foamover to contaminate the products
detail how the entrained foam impacts product yields and from an atmospheric tower badly.
qualities. It also discusses the use of vortex tube clusters
Although these separators may be costly, they are effec(VTC) systems in crude unit preflash drums.
tive in eliminating foamovers and protecting product quality.
When it comes to vortex or cyclone foam separators, there Fluor has good experience with both technologies, and has
are two popular technologies. One is the VTC systems from pioneered the use of VTCs together with MPC.1⁰
EGS Systems, described above1,11
and shown in Figures 5a and 5b.
The other is Sulzer’s proprietary
GIRZ cyclonic inlet device, shown in
Figures 6a and 6b.
Figure 5a illustrates the principle
of vortex foam separators operation.
The foam is separated by the centrifugal forces that send the liquid to
the walls, forming a continuous liquid phase, while the vapour forms a
continuous phase that concentrates Figure 6b Action with and without GIRZ cyclonic gas inlet device in a
Courtesy of Sulzer Chemtech
in the centre. The vapour exits from demonstration flash drum with foam
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Foam height (ft), (above HHLL)
Sizing preflash devices
6
5
4
3
2
1
0
0
5
10
15
20
25
30
35
Superficial liquid velocity (gpm/ft2)
Figure 7 Foam height vs superficial liquid velocity
Basis Figure 5, Reference 8
In preflash towers, even with vortex foam separators,
some entrainment from the flash zone remains, which
would normally be washed down by the reflux. If the reflux
on the tray above runs dry or very low, this entrainment may
lead to a dark product, as we have experienced.
Lastly, good instrumentation is invaluable in alleviating
and managing foamovers. Pressure, levels, flow rates, and,
most of all, temperatures can provide operators with an
early indication of the onset of foamovers. Instability in drum
level, pressure, and flashed crude flow rate forewarns the
approach of a foaming episode. Reliable measurement of
the drum level has been inherently problematic due to foam
formation. Seeing a ‘split level’ in the sight glass indicates
likely foam.3 A nuclear-level device has been advocated for
monitoring the preflash drum or tower level.7 Watching the
preflash drum overhead temperature and the bottom pump
for cavitation is also invaluable for detecting foamovers.
With preflash towers that have a kero side draw, it is imperative to closely monitor the colour of the draw because that
is where the foamover is first seen.⁷
Naphtha
Reflux
Crude
feed
Preflash
crude
Figure 8 Adding this horizontal drum did not alleviate
foaming
86
KISTER FLUOR.indd 86
PTQ Q1 2024
The ideal preflash drum is horizontal because the
cross-sectional area for flashed crude flow is larger.
However, the plot area available may be insufficient for a
horizontal vessel, and a vertical vessel would be preferred,
particularly in revamps. Because the cross-sectional area
for flashed crude flow in the vertical drum is smaller, it will
require more vessel height to retain the foam. A preflash
drum, as well as the bottom section of a preflash tower,
must have sufficient height to contain the foam to prevent
the rising vapour from carrying foam (flashed crude) into
the drum overhead or the upper preflash column trays.
Conventional trays will not break foams and will flood
upon foamovers. Barber and Wijn⁸ presented the results
of experiments on pilot and full-scale preflash drums processing various crudes at several operating conditions.
Based on these data, Barber and Wijn derived a model
and correlation that can be used to design crude preflashing devices.
According to their tests, the key sizing criterion for the
drum or the tower bottom section is the flashed crude
downward superficial velocity, which should be low
enough to allow the foam to be retained inside the drum
or in the bottom of the tower. As long as there is sufficient height above the maximum clear liquid level (HHLL),
foamover is unlikely. The smaller the cross-sectional area
for flashed crude, the higher the foam level inside. If the
disengaging height above the maximum clear liquid level is
small, then the superficial velocity must be low. Conversely,
if the available height to retain the foam is high, then a
higher superficial velocity can be tolerated before the foam
is no longer retained. The Figure 7 correlation8 applies to
a crude oil superficial liquid velocity in the range of 15 to
30 gpm/ft2. We have had excellent experience with this
correlation, and it seems to extrapolate well to values up to
60 gpm/ft2, but extrapolation beyond 30 gpm/ft2 cannot be
done with confidence.
It is important to check the preflash tower or drum size for
the lightest (and heaviest) crudes intended to run, including
start-up conditions with slop reprocessing.3
Some literature sources advocate a residence time criterion for preflash drum sizing (for example, three minutes).
The authors’ experience strongly favours the downward
velocity criterion above but does not support a residence
time criterion. In an attempt to alleviate severe foaming in
one preflash tower (not a Fluor design), a refinery added a
horizontal drum in parallel with the tower’s vertical sump.
The liquid and vapour spaces of the drums were connected by large lines, as shown in Figure 8. Doubling the
residence time with the addition of the horizontal drum did
very little to alleviate the foaming. The downward velocity
remained unchanged as all the crude was fed to the flash
zone of the tower.
Drum or tower inlet devices
Barber and Wijn⁸ also found that foaming in the preflash
drum or tower is strongly affected by the inlet device. The
inlet device needs to be adequately designed and carefully
checked.
www.digitalrefining.com
08/12/2023 17:25:40
In one case, a new preflash drum was sized per Figure
7, but upon start-up the drum experienced severe entrainment. Following the Fluor FEED design, the detailed design
was turned over to a local contractor who installed a baffle
in front of the crude inlet nozzle that was open at the top
and bottom and closed on the sides, causing an impingement jet onto the liquid level and shooting crude upwards.
In another case (again, not a Fluor design), a preflash
tower12 experienced frequent episodes – especially with
light crudes – in which the naphtha stream leaving the
tower turned dark, accompanied by a high tower dP. These
episodes originated from crude entrainment and restricted
the throughput of the entire crude unit. The root cause was
diagnosed to be excessive feed velocities with poor feed
entry design. The entrainment problem was eliminated, and
the naphtha make could be raised by more than 20% by a
unique feed entry design by Fluor for the very high-velocity
feed. This was achieved by removing two segments of the
top shed deck and by a specially designed impingement
baffle to break the incoming momentum.
Key takeaway: It is imperative to correctly specify the feed
inlet design and/or thoroughly check inlet designs by others.
Trays or packing in preflash towers
Most preflash towers recover naphtha as the only product. Some also draw an additional kero stream as a side
draw (usually a small flow) a few trays above the feed.
When drawing kero, a pumparound that preheats crude is
sometimes used right above the kero draw. The kero may
be sent to the stripper or the kero-naphtha section of the
atmospheric tower. Preflash towers have trays and reflux
to fractionate overhead product from the kero side draw or
bottom product streams. Random or large structured packings have also been used with success, although trays are
preferred.
It is important that the trays, at least those right above the
feed, are fouling-resistant, as crude carryover, entrainment,
and foamovers (especially during upsets and power cuts)
tend to entrain foulants into the trayed sections. Entrained
waxes and resins can bond together and crystallise out on
the lower trays. Fouling of the lower trays has been experienced even when VTC has been installed in the flash zone
(see Figure 9). Cases have been observed where moving
valve trays and fixed mini-valve trays right above the flash
zone plugged. Salting out and corrosion near the top have
also been experienced and, again, favour using fouling-resistant trays such as Sulzer’s SVG fixed valves with 0.5in
opening, LVG fixed valve trays, or Koch-Glitsch’s ProValves.
The trays near the top should also have corrosion-resistant
metallurgy.
The economics dictates using a reflux ratio just enough
to achieve the naphtha product specification (typically the
95% ASTM D86 temperature). Adding reflux beyond this
recycles some of the naphtha back into the crude, which in
turn counters the benefits of the tower. There are typically
15-20 trays used above the flash zone, giving about 8-10
theoretical stages.
Minimising the reflux often generates spray regime conditions (low liquid rates and high vapour rates), with tray
www.digitalrefining.com
KISTER FLUOR.indd 87
Figure 9 Plugged mini-fixed valves in wash section of
preflash tower
drying and/or break of downcomer seal, accompanied by
fouling, plugging, and instability. This is especially severe
when drawing kero, as the ‘wash’ section below the draw
is particularly liquid-lean with weir loads often below 1
gpm/in. Due to the temperature gradient, the driest spot
is just above the flash zone, and here the potential for
plugging and seal loss is maximised. A good spray regime
design (avoiding excessive open area, keeping downcomer clearances low (1-1¼in), and judiciously using
picket-fence weirs) is essential. Liquid reflux and the wash
below the kero draw (if it exists) need to be on flow-controlled pumpback to avoid fluctuations that can dry out
the trays and break the downcomer seals. Adding vortex
tubes at the flash zone (Figures 5 and 6), or at least ensuring a good feed distributor, will improve reliability, alleviate foamovers and entrainment, and may be relatively
inexpensive.
In many preflash towers, especially those recovering kero
as a side draw, designers add trays or packings below the
flash zone and use stripping steam to recover more naphtha or kero from the crude. We prefer not to do this due to
foaming concerns (see next paragraph), but some clients
insist. If stripping steam is used, its ideal rate is 10 lb/bbl,
but many units use less than that. There are also reboiled
preflash towers using fired heaters. A study by Sloley²
found that using a stripping section saves energy.
Regular trays (fouling-resistant) or packings in the stripping sections work fine as long as severe foaming is not
experienced, which is probably 50% of the time. However,
trays or packings below the feed can be disastrous if foaming is experienced, which is the other 50%. There was one
case in which it was necessary to remove the stripping trays
to stop foaming in the stripping section trays from severely
bottlenecking the entire crude unit. Trays or packings are,
therefore, not recommended for the stripping section. Shed
decks and grid packings have shown good performance in
the stripping section of preflash towers. With their large
open area, they can be designed to handle foam. Correct
design of the shed decks and grid packing is essential in
this service.
PTQ Q1 2024
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13/12/2023
Preflash tower condenser and drum
Many preflash towers have their own condenser and reflux
drum system, and their naphtha products are sent to the
naphtha processing facilities downstream of the atmospheric tower (Figure 3). If the condenser and drum of the
atmospheric tower have enough capacity, Capex can be
saved by sending the preflash tower overhead to the atmospheric tower condenser and drawing reflux for the preflash
tower from the atmospheric tower reflux drum. The scheme
proposed by Lee,6 Figure 4, also eliminates the preflash
tower condenser and drum and saves Capex.
Adding a preflash tower and condenser (as in Figure 3)
debottlenecks the atmospheric tower condenser. As many
atmospheric crude towers are bottlenecked by their condenser capacities, this condenser debottleneck is invaluable not only for achieving a higher throughput from the unit
but also for allowing better recovery of distillates (gasoil
and diesel) from the resid. Additional atmospheric tower
condenser capacity allows reducing pressure in the tower,
which vapourises some of the resid into gasoil and diesel
products. Also, atmospheric tower condenser limitations
often constrain the amount of stripping steam that can be
used, so debottlenecking the condenser allows more stripping steam to be used and again recovers more distillates
out of the resid. In addition, this system provides better
flexibility to keep the crude unit optimised for running variable API feeds depending on loading and turndown. On the
debit side, this scheme aggravates the dew and salt point
problems in the atmospheric tower, as discussed earlier.
One important consideration is that many preflash towers remove the bulk of the light gases from the crude. This
again helps the atmospheric tower condenser, as these
gases reduce its heat transfer coefficient. The absence of
these gases may convert the atmospheric tower condenser
from a partial condenser to a total condenser. This necessitates changes to the tower pressure control scheme, and
if these are not correctly performed, the atmospheric pressure control may become unstable.
Energy savings
For refineries where energy savings in the crude unit are a
desirable target, it is important to explore how adding crude
preflashing devices will affect energy consumption. The
crude heater is one of the highest energy consumers in a
refinery, and minimising its duty is a good target.
A study by Feintuch et al13 demonstrates the importance
of taking the preheat train constraints into account when
comparing energy usage between preflashing and no preflashing options. In their revamp case, adding a preflash
drum with its overhead going to the atmospheric tower
flash zone (similar to Figure 1) was a significant energy
saver because the lower downstream pressures permitted
the reuse of existing exchangers. In that case, replacing the
existing exchangers with new ones was too costly to be
economical.
Another comparison was conducted by Lee.6 In addition
to the three cases of no preflash, preflash drum, and preflash
tower, he added the semi-preflash tower option in Figure
4. The crude considered was a 60.7º API Eagle Ford crude.
www.digitalrefining.com
KISTER FLUOR.indd 89
The preflash drum overhead vapours were directed into the
atmospheric tower flash zone. Lee’s study was based on the
same product yields and the same overhead condenser duty
of the atmospheric tower for all cases. Product overlaps
were kept identical for all cases.
To counter the carrier effect, Lee raised the coil outlet
temperatures in the preflash cases. The preflash temperatures were set to comply with the atmospheric tower
condenser limitation, varying from 282ºF for the preflash
drum to 395ºF for the preflash tower and 353ºF for the
semi-flash tower. In addition, Lee’s study adjusted the
crude tower pumparound balance for each case to give
the same product yield pattern as in the no preflash case.
The changes in the pumparound duties were reflected as
changes in furnace preheat temperatures. Per our experience, Lee’s comparison has a realistic basis that is reflective
of many crude systems.
Lee’s study found that the preflash drum (with its overhead entering the flash zone in the atmospheric tower) had
little effect on the heater duty energy consumption and did
little unloading in the atmospheric tower. The preflash tower
reduced the heater duty by 18% compared to the no-preflash
case and achieved a very large hydraulic unloading in the
atmospheric tower, especially above the kero pumparound.
The semi-preflash option gave a 13% reduction in heater
duty and intermediate hydraulic unloading. In this semi-preflash option, the hydraulic unloading above the kero pumparound was much less than in the preflash tower option.
The energy savings from the addition of a preflash tower
depends on the location of the heat transfer surface area,
the cut points, the unit constraints, and the preflash scheme.
A consensus among several experts7 is that adding a preflash tower may or may not save energy. One thing both the
previous studies teach is that it is important to carry out the
comparisons on a basis that correctly reflects the specific
crude train under consideration and its constraints. A different basis and different ground rules can lead to different
conclusions. Each case should be considered on its own
merit. Market conditions may also dictate which configuration is better suited for a specific project at a given time.
Economics: Preflash drum, tower, or no preflash?
The no preflash scheme saves the cost of the drum and
piping but raises the cost of the preheat exchangers that
would need to be designed for the higher pressure required
to keep the feed liquid from flashing upstream of the heater
feed control valves. In the revamp of an existing preheat
train, being able to reuse existing exchangers and save the
cost of new ones may shift the economics in favour of preflashing, as demonstrated in one case.13
The preflash column and semi-preflash options are not
much more expensive than the flash drum, provided they
make use of the atmospheric tower overhead condenser
and reflux drum.⁹ The most expensive is the preflash tower
option with its own condenser, reflux drum, and pumps.
In a revamp, however, adding the preflash tower with the
reflux drum and pumps can be more cost-effective and
trouble-free than modifying the atmospheric tower and its
overhead system. Further, the bulk of this construction can
PTQ Q1 2024
89
08/12/2023 17:25:41
be performed while the crude unit is in operation, reducing
the downtime during the turnaround.
An optimisation study by Sloley2 concluded that for new
units in general, independent preflash towers should be
avoided, as building additional capacity in the crude tower
and associated equipment lowers Capex and improves
yields and heat recovery. In the cases where a preflash may
be beneficial in a new unit, the preferred option would be to
use a preflash drum.
A study by Gomez-Prado et al14 for a grassroots design
of a 120,000 BPD North American crude unit supports
including a preflash drum. The benefits were more crude
preheat, flexibility to process alternative lighter crudes,
reduced preheat pressure to allow the use of a 300# flange
rating instead of 600#, and reduced operating costs of the
hot crude charge pumps. Specifically, they noted that with
no preflashing, water entrainment had a high influence on
the preheat exchangers’ cost. For example, with a water
content of 0.8% LV, the difference due to water in the
required pressure rating (preflash vs no preflash) reached
about 200 psi vs 100 psi at the typical design point of 0.20.3% LV. As water upsets occur, the exchangers and piping
need to be designed to withstand the pressure produced
with the higher water content, The cost savings more than
paid for the preflash drum and its associated facilities.14
For revamps, the factors that would favour independent
preflash towers include:2,7
• Severe capacity constraints in the entire atmospheric
crude tower
• Strict limits on the duty available in the existing furnace
• Strict limit on furnace outlet vapourisation with very light
crudes (excessive coking at heater outlet)
• Severe limits on the existing overhead system – a preflash
tower would add a new overhead system (Figure 3)
• Removing the C5 and lighter paraffins reduces asphaltene
precipitation and fouling in downstream exchangers.
This is far from a comprehensive list, and each case
should be considered on its own merit. Sometimes, a
preflash device is economically attractive in the least
expected circumstances. Waintraub et al15 presented
a case in which a preflash drum was attractive for processing a heavy high naphthenic crude (API 16º). With a
preheat temperature of 590ºF and 0.6% LV water in the
desalted crude, the operating pressure to prevent flashing
before the furnace control valves would have been 640
psig. The exchangers would have needed to have special
metallurgy to withstand the presence of chlorides in an
aqueous phase and naphthenic acids. The cost of preflashing the water and the light ends was much lower.
The light ends content was too low to justify a preflash
tower, so the economic solution was a preflash drum with
its overhead going to the transfer line.
Often, there are unique considerations, such as when
processing synthetic crudes or bitumen, which are mixed
with naphtha diluent to cut viscosities and permit adequate
flow, as described in detail by Grande and Gutscher.16 In diluent recovery units (DRUs), preflash drums are often used
upstream of the furnace and DRU tower. The large volatility
gap between the naphtha and the gasoil seldom justifies a
90
KISTER FLUOR.indd 90
PTQ Q1 2024
preflash tower. In this case, free water is a major issue and
can largely raise the pressure requirement for the preheat
exchangers and cause damage to the furnace and tower
due to rapid vapourisation. To accommodate this, there is an
incentive to perform preflashing using two preflash drums at
different temperatures.16 The first drum removes most of the
free water, and both remove diluent from the feed.
Economics for preflash towers need to be examined carefully. It is conceivable that an entire parallel crude unit may
be a more cost-effective expansion option. Each case needs
to be considered on its own merits, with the broad picture
kept in mind. This is illustrated by one of the case studies
by Gomez-Prado et al.14 In that case, the preflash tower
already existed, and the challenge was optimising the preheat temperature, with a constraint on the preflash tower
overhead condenser. While additional preheat reduced
the crude furnace duty, it also decreased the yield of the
more valuable distillate. A model of the entire refinery was
needed to optimise the preflash temperature correctly. Plot
space considerations may also play a role in favouring one
scheme or another.
Reliability and environmental considerations
There is one more important reliability consideration
favouring preflash towers. Environmental and safety concerns have recently forced refiners to route discharges
from small relief valves, previously going into atmospheric
drums, back into the process. Desalter relief valves, as well
as relief valves from liquid crude-handling circuits, have
been routed into the atmospheric tower flash zone. Pockets
of water in the reliefs or sitting in the relief valve discharge
piping are common. In some instances, these pockets have
ended up in the hot flash zone of the atmospheric tower,
rapidly vapourising and causing a pressure surge. This
can damage several trays in the fractionator, causing yield
losses and forcing a premature crude unit shutdown.
When a preflash tower exists, these discharges are routed
to near the top of the tower, where the temperatures are
low enough to tolerate water without pressure surges.
Takeaways
Preflash drums and towers are invaluable for debottlenecking preheat exchangers, crude heaters, and atmospheric
towers, particularly when processing light crudes. Potential
penalties are some loss of gasoil or diesel to the atmospheric resid and aggravation of the water dew point and
salt point issues near the top of the atmospheric crude
tower. To be effective, these devices need to be adequately
designed, with special emphasis on containing foam and, in
towers, resisting fouling.
Regarding their economics, each case needs to be considered on its own merit, with unit constraints taken into
account.
This article was originally presented at the Distillation Experts Conclave
Meeting, Mumbai, India, October 12-13, 2023. This article is dedicated
to the legacy of Walter Stupin, an expert, mentor, and friend who contributed so much to advance chemical engineering, distillation, and to
help and encourage young engineers. May his memory be blessed.
www.digitalrefining.com
08/12/2023 17:25:42
References
1 Barletta T, Hartman E, Leake D J, Foam control in crude units, PTQ,
Autumn 2004, p.117.
2 Sloley A W, Atmospheric preflash towers, Proceedings Kister
Distillation Symposium, p.63, AIChE Spring Meeting, Austin, Texas,
April 26-30, AIChE, 2015.
3 Golden S W, Prevent preflash drum foaming, Hydroc. Proc., May
1997, p.141.
4 Stichlmair J C, Fair J R, Distillation Principles and Practice, Wiley-VCH,
NY, 1998, p.76.
5 Ji S, Bagajewicz M Designing crude fractionation units with preflashing or pre-fractionation: energy targeting, Ind. Eng. Chem. Res. 41,
2002, p.3003.
6 Lee, S H, Optimising preflash for light tight oil processing, PTQ, Q3,
2015, p.51.
7 AFPM 2015 Q&A and Technology Forum, Crude/Vacuum Distillation
& Coking, Q-61, 2015, p.65.
8 Barber A D, Wijn E F, Foaming in Crude Distillation Units, IChemE
Symposium Series, No 56, p3.1/15.
9 Golden S, Crude unit preflash drums and columns, PTQ Revamps &
Operations, 2005, p.11.
10 Turner J, Asquith R J, Atkinson R, Stop foaming on hydrotreater ‘hot’
separator, Hydroc. Proc., June 1999, p.119.
11 www.egs-systems.com
12 Blum B, Kister H, Tsang R, Good distributor design for high-velocity
feed debottlenecks a crude preflash tower, Hydroc. Proc., June 2021,
p.29.
13 Feintuch H M, Peer V, Bucukoglu M Z, A preflash drum can conserve
energy in a crude preheat train, Energy Progress, Sept 1985, p.165.
14 Gomez-Prado J, Goodrich R, Hoppens D, Simulating crude units
with preflash, PTQ, Q4 2016.
15 Waintraub S, Coutinho R C, Esposito R O, Preflash drum when
processing heavy oils: Paradox or reality? in Distillation 2007, Topical
Conference Proceedings, p.161, AIChE Spring National Meeting,
Houston, Texas, April 22-26, 2007.
16 Grande M, Gutscher M, Designing atmospheric crude distillation for
bitumen service, Hydroc. Proc., Feb 2011.
Henry Z Kister is a Fluor Senior Fellow and Director of Fractionation
Technology. He has more than 35 years of experience in design, troubleshooting, revamping, field consulting, control and start-up of fractionation processes and equipment. He is the author of three books,
the distillation equipment chapter in Perry’s Handbook, and more than
150 articles. He has taught the IChemE-sponsored Practical Distillation
Technology course more than 550 times in 26 countries. He holds BE
and ME degrees from the University of NSW in Australia.
Walter J Stupin was an in-house consultant on special technical problems in process engineering for petroleum refining and chemical plants.
His more than 50 years of process engineering experience included
positions as Executive Director of Process Engineering at Fluor and
Vice-President of Technology at C F Braun Inc.. He has published more
than 40 technical papers and held BS, MS, and PhD degrees in chemical engineering from the University of Southern California, Los Angeles.
Maureen Price has more than 38 years of experience as a chemical
engineer, including 31 years with Fluor. She provides expert technical consultation for clean fuels, crude and vacuum revamp, renewable
energy, and complex integration projects. She specialises in project
definition for new and revamp work at all levels of front-end planning
as well as detailed engineering, execution, and construction. She holds
a Bachelor of engineering (chemical engineering) degree from California
State University, Long Beach, and is a registered Canadian professional
engineer in the province of New Brunswick.
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KISTER FLUOR.indd 91
PTQ Q1 2024
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Technology in Action
Hydrogenation technology and catalysts
reduce PVC byproducts
Approximately 34 million tons of polyvinyl chloride (PVC)
are produced annually. A versatile material that is costeffective to produce, it boasts numerous applications:
building and construction, packaging, vehicle parts, electronics, medical devices, and more.
However, it is also the production where an issue is
found. Byproducts of PVC can be toxic, and removing and
disposing of them can be costly.
These undesired chlorinated byproducts are formed
during ethylene dichloride (EDC) cracking to vinyl chloride
monomer (VCM) – the raw material for PVC production –
and hydrochloric acid (HCI). Specifically, acetylene (C₂H₂)
traces are formed and, when returned to the process in
the HCI recycling stream, create said byproducts in the
oxychlorination reactor.
There is good news, however, in the fact that a more
economically and environmentally friendly approach to
PVC production is possible.
Hydrogenation technology
Hydrogenation technology presents itself as the solution
to this problem. Approximately 860 tons of toxic chlorinated byproducts in a 300 kta production of VCM can be
prevented when using this technology. Moreover, when
Without (%)
With (%)
1,2 Di-trans
Hydrogenation unit
0.010
0.002
CCl4
0.101
0.067
1,2 Di-cis
0.012
0.008
1,1,2 Trien
0.035
0.002
Total low boilers
0.158
0.079
Tetrachlorethylene
0.112
0.001
1,1,2,2 Tetrachlorethane
0.130
0.034
Total high boilers
0.242
0.035
Total byproducts
1,2 EDC
860 tons of toxic
byproducts avoided
98.669
98.921
∆ = +0.252
Illustrative calculation
for 300 kta VCM unit
Figure 1 Calculation for 300 kta VCM unit
TIA Q1.indd 93
∆ = –0.207
∆ = –0.286
Yield increased
by 0.3%
www.digitalrefining.com
∆ = –0.079
selective hydrogenation of C₂H₂ to ethylene (C₂H₄) in HCl
recycle streams is paired with fixed-bed catalysts throughout the VCM process, undesired byproducts can be avoided,
and valuable raw material can be returned to the process.
Evonik has been producing hydrogenation catalysts
for acetylene-to-ethylene within the HCl recycle stream
in VCM plants for the past 40 years. VCM hydrogenation
Implementing the hydrogenation
unit and avoiding acetylene
reaching the oxychlorination
reactor prevents chlorinated
byproduct formation
catalysts are produced by Evonik based on proprietary
knowledge. These catalysts are suitable for hydrogenation
units as part of fluid-bed and fixed-bed VCM synthesis
reactors. The hydrogenation catalysts have been successfully used with the highest performance in all existing
VCM process technologies, such as Vinnolit, Oxyvinyls,
INEOS, Mitsui, and Solvay.
Catalyst tailored to hydrogenation process
Developed by Evonik in co-operation with Vinnolit GmbH
& Co. KG, the proprietary Noblyst E39 catalysts are a frontrunner in providing catalysts tailored to the hydrogenation
process, and were tested and used in Vinnolit’s commercial
plants.
The series of palladium on silica crystal catalysts were
designed specifically for the selective hydrogenation of
acetylene-to-ethylene within the VCM production process, improving ethane dichloride selectivity and minimising byproduct formation in the oxychlorination step.
Implementing the hydrogenation unit and avoiding
acetylene reaching the oxychlorination reactor prevents
chlorinated byproduct formation. Acetylene will be chlorinated to low boiling compounds like di or tri chloroethane
and high boilers like tetrachloroethane and tetrachloroethene. In addition, the polymerisation of acetylene and ethylene or acetylene and acetylene, including chlorination,
can take place, causing chlorinated tar formation.
As seen in Figure 1, by reducing the said formation, the
quality of EDC increased substantially; the EDC yield also
increased by about 0.3%. So, we can conclude that the
increased yield can potentially save producers using a
hydrogenation reactor a significant amount in operational
and capital expenditure costs.
Evonik Catalysts
Contact: [email protected]
PTQ Q1 2024
93
12/12/2023 12:15:51
Worker safety when entering reactors with an
inert atmosphere
The products from petrochemical processing touch almost
every aspect of modern living. The importance of these
products to industry and society emphasises the critical
nature of facility maintenance and efficient turnarounds
that keep production going.
The lost revenue and costs associated with shutting
down a process for media bed changeouts, preventative
maintenance, or repairs are significant. During these outages, every element of the turnaround must be carefully
planned and executed efficiently by plant workers to meet
tight schedules and get the plant back on-line. As a result,
worker safety is always critical, especially when entering
the confined space and hazardous environment inside
petrochemical reactors. Injury or accidents of a worker can
result in significant impact to workers, families, and project
schedules.
Problem
Professional process engineers and managers in the industry are well-trained, knowledgeable, and equipped to comply with safety standards and guidelines from OSHA, API,
NFPA, and ASSP/ANSI for continuous worker safety.1-4 They
are trained to understand and mitigate the risks to workers
and ensure that the processes and protocols in place are
carefully followed to guarantee worker safety throughout
turnaround activities.
Regulatory and industry safety standards for rendering the internal atmosphere of a reactor inert and allowing workers to enter the confined workspace are detailed
and complex. After a vessel is purged and flooded with
inert gas to mitigate potential explosions, many significant
hazards to workers persist, including asphyxiation, working conditions, and changes to the internal atmosphere.
Fortunately, several regulatory and recommended safety
standards are in place to address and minimise these
hazards.
Defined as permit-required spaces, OSHA 1910.146,
NFPA 350 Standards detail the requirements of the written Permit-Required Confined Space (PRCS) Program
that includes area identification and barriers, atmospheric
testing, documentation, entry permitting and close-out,
emergency retrieval, stand-by personnel, continuous environmental monitoring inside the vessel, vessel purging/
inerting, ventilation, worker breathing equipment, personal
protection equipment (PPE), worker communications,
lighting, rescue and emergency equipment, and ongoing
training.
API Recommendation 2217A references the above standards while providing additional details on each aspect,
including maintaining the inert atmosphere with nitrogen
and the potential hazards of ‘catalyst crusting’, testing, and
mitigation.
Petrochemical plants are well versed in implementing
these programmes and guidelines while ensuring they are
followed for the safety of workers on the turnaround team
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TIA Q1.indd 94
PTQ Q1 2024
and specifically those who will be entering these ‘entry permit required’ spaces to perform maintenance.
Challenge
Implementation and compliance with regulatory and industry guidelines for entering PRCSs is critical, yet complex
and expensive to execute and implement. As such, companies are constantly evaluating their turnaround processes
and procedures to determine if any changes can be made to
minimise risk to workers and the necessity for implementing these protocols at various stages of the turnaround in
fixed-bed reactors.
From a regulatory standpoint, anytime workers need to
enter a vessel, the protocols for PRCS must be followed.
Changing the media when it has reached the end of its useful life, for example, requires that workers enter the vessel
to remove the hold-down screens or the manways in top
screens to allow access for the media removal equipment.
Of course, once the media is removed, the vessel can be
ventilated completely to create a safe and stable atmosphere where workers can enter the vessel and perform
service or repair to the vessel internals. However, many
hazards still exist, and once again the safety protocols and
permitting process for entering the confined space must be
followed.
With an eye on reducing costs, reducing risk to workers, and improving turnaround times, many companies
and process engineers have begun to ask how the process
for simple media bed changes can be simplified to eliminate the need for a worker to enter the vessel to remove
the media. This would help to streamline the initial stage
of the turnaround and shorten the overall process. In some
cases, companies have already begun to mandate that
employees not enter vessels when removing media during a turnaround. These corporate mandates create unique
challenges for process engineering teams at the beginning
stage of a turnaround.
Solution
Johnson Screens believes reactor internals can help processors maintain regulatory and corporate policy compliance
while enhancing worker safety and has created unique
solutions to address these challenges. These innovative
new products will be highlighted in future articles.
References
1 API (American Petroleum Institute) Recommended Practice 2217A,
5th Edition, July 2017.
2 OSHA (Occupational Safety and Health Association) Standard
1910.146 Permit-Required Confined Spaces.
3 National Fire Protection Association, NFPA 350 – Guide for Safe
Confined Space Entry and Work.
4 American Society of Safety Professionals and Approved American
National Standard (ASSP/ANSI) Z117.1, 2022, Safety Requirements
for Entering Confined Spaces.
Johnson Screens
Contact: [email protected]
www.digitalrefining.com
12/12/2023 12:15:52
THE AGENDA
IS HERE!
Take a look at the packed agenda for 2024 which will explore cuttingedge decarbonisation strategies and technologies together with the
emergence of new industrial clusters driving energy transition.
Tuesday, 16th April 2024
Wednesday 17th April 2024
09:00 Arrival, registration & breakfast networking
09:50
Chairperson’s welcome
09:50
Welcome and opening remarks
10:00
10:00
Panel: How (well) are policy and key industry
stakeholders working together for a decarbonised
future?
Panel: Catalysing the decarbonisation of the
industrial clusters and hubs
10:45
Coffee break & networking
11:15
Demand for low carbon-materials and implications
for the supply chain
11:45
Embracing circularity in the transition away from
emissions-intensive energy
10:45
Panel: Policy benchmarking: The global status of
decarbonisation policy, strategy, and industry
collaboration
11:30
Coffee break & networking
12:00
Mobilising capital and private investment to drive
funding for industrial decarbonisation
12:15
12:30
Panel: What do industries need to see in the finance,
investment, and policy landscape to move faster?
Panel: Gasification - upgrading bottom-of-thebarrel and other low-value streams into usable fuel
13:00
Networking lunch
14:00
Driving sustainability in petrochemicals: Sulzer
Chemtech’s innovations in alternative fuels and
circular economy
14:30
Realising energy transition - Unleashing the
potential of clean hydrogen to hit net zero targets
15:00
Closing keynote: Committing to green electricity
15:30
Conference wrap-up and closing remarks from
the Chair
15:45
Coffee break & networking
13:15
Networking lunch
14:15
Development of processes to utilise captured CO2
to manufacture new materials
14:45
Panel: Accelerating the standardization of CCS to
improve the technology, cost, scheduling, and safety
15:30
Coffee break & networking
16:00
Case study: Sustainable steel - Ovako’s next frontiers
16:30
Panel: Hydrogen - Potential vs progress in policy,
technology and investment
17:15
Day 1 round-up
17:30
Drinks reception & canapes
BOOK NOW!
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14:19
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15:38:30
Pump operating issue case study:
Identifying the poor performance root cause
Problem
An alkylation unit’s main fractionator reboiler pumps were
experiencing operational problems. Two 100% pumps were
available: one online and one 100% spare P-900/901.
A rotating equipment engineer described the problem:
When placed online, the P-900 control valve is 70% open
at 130,000 BPD flow. Shortly after start-up, the flow starts
decreasing, and the control valve opens. It gets to a point
where the control valve is wide open, and the flow is still
dropping off. When the pumps are switched, the same
behaviour is observed. The pump starts up per design, but
the flow quickly deteriorates.
It was concluded that the pump behaviour was indicative
of a net positive suction head (NPSH) issue. It was thought
that the net positive suction head available (NPSHa) was
lower than the net positive suction head required (NPSHr). A
new pump with a lower NPSHr was specified.
Analysis
A replacement pump was selected with input from the original equipment manufacturer (OEM) and was about to be purchased. Management asked the process engineering group
to approve the new pump before the order was placed.
In Stratus’ three decades of providing service to the hydrocarbon processing industry, the most common misdiagnosed
and undiagnosed engineering issue seen has been hydraulics. Often, this is due to a lack of effective engineering tools,
but it can also be due to improper application of available
engineering tools.
For this problem, the process engineer used Process
Engineering ToolS (PETS) software to analyse the proposed
replacement pump. Physical properties, hydraulic pressure
drop, and NPSH evaluation were performed. The analyses
Figure 1 PETS showed no NPSH issue was evident
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TIA Q1.indd 96
PTQ Q1 2024
Figure 2 The PETS Pipe System Hydraulics Tool modelled
the system and checked it at various conditions
showed that no pump suction flashing should occur at the
operating conditions. No NPSH issue was evident (see
Figure 1).
The analyses showed that the NPSHa was well above the
installed pump’s NPSHr. Additionally, the proposed replacement pump had very similar NPSH requirements to the
installed pumps.
The Fittings Equivalent Lengths Tool was used to obtain
the equivalent lengths for the pump suction and discharge
piping. The PETS Pump Curve Tool was used to enter the
pump curve data. The control valve datasheet information
was entered into the Control Valve Tool.
The Pipe System Hydraulics Tool was used to put it all
together and model the system (see Figure 2). The model
was used to check the system at various conditions. The
model showed that the system was process capable, that
the existing pump had no NPSH issues, and that there was
no flashing in the system. PETS showed the pump operational issues were not due to suction flashing, assuming
typical pipe condition.
However, the pump’s operational issues were real. What
was causing it? The pump was taken apart to investigate.
A pump suction witches hat strainer (unknown and with no
visible handle) was installed backwards in the system. Debris
was found inside the witches hat (see Figure 3).
Figure 3 Debris found inside the witches hat
www.digitalrefining.com
12/12/2023 12:15:56
Combining Prime-G+ and GT-BTX PluS to
upgrade a refinery with crucial operating
flexibility
The landscape of the petroleum refining industry has
undergone a significant transformation in the aftermath of
the global pandemic. The volatile and unpredictable nature
of market demands post-pandemic has underscored the
critical importance of adaptability for refineries. In this
rapidly evolving environment, the ability to swiftly adjust
production focus to meet changing market requirements
has become paramount. The integration of Prime-G+ and
GT-BTX PluS technologies offers refineries a unique solution to address these challenges by providing built-in operating flexibility.
Figure 4 Debris accumulated inside the backwards
witches hat impeded flow into the pump
Conclusion
Challenges of current refineries
Based on the findings, it was concluded that the pumps
were starting up fine and after operating a short time the
accumulated debris shifted in the inside cone area of the
backwards witches hat, impeding flow into the pump.
When the pump was stopped, the debris fell to the bottom
of the strainer, resulting in a lower pressure drop at start-up
but with the debris ready to shift and more fully plug the
pump’s inlet the next time the pumps were switched.
Equipment performance problems can be difficult to
diagnose. A thorough evaluation considering all possible
causes is beneficial. Using the right engineering calculation tool, such as Process Engineering ToolS software, to
examine the process is imperative to assist in analysis and
making correct decisions. In this case, the investigation
prevented the replacement of a pump that was designed
properly and process capable.
Stratus Engineering
Contact: [email protected]
Modern refineries are divided between those that emphasise fuel production, particularly gasoline, and those that
prioritise the maximisation of petrochemicals output. For
gasoline-focused refineries, the octane number is a key
determinant of profitability, with even marginal improvements translating to substantial gains. In developing
countries, refineries are compelled to elevate gasoline
specifications to meet Euro-5 standards while simultaneously reducing sulphur levels to <1 ppm. The challenge
lies in maintaining octane numbers while achieving such
stringent sulphur reduction. Meanwhile, petrochemicalcentric refineries seek efficient ways to convert gasoline
into high-value petrochemical products while minimising
investments.
Combined technology in gasoline mode for
gasoline production with max profitability
The amalgamation of Prime-G+ and GT-BTX PluS technologies introduces an innovative approach that yields impressive benefits. This combination entails the installation of a
new GT-BTX PluS unit alongside an existing Prime-G+ unit
Raffinate
Extract
P
A
Feed
P araffins
O lefins
N aphthenes
Raffinate
O
Extract
S
N
Extractive
distillation
column
(EDC)
Hydrocarbon
feed
Solvent recovery
column
(SRC)
A romatics
S
ulphurs
Rich solvent
TECHTIV® DS
Lean solvent
Figure 1 GT-BTX PluS simplified process scheme
www.digitalrefining.com
TIA Q1.indd 97
PTQ Q1 2024
97
12/12/2023 12:16:00
LCN
Olefin distribution
FCC/RFCC
Naphtha
SHU
MCN
70–150˚C
(Olefin-rich)
MCN
HCN
% fraction
LCN
Hydrogen
C6
C5
C7
C8
C9
C10
HCN
150˚C - EP
(Olefin-lean)
Figure 2 Fractionation of FCC gasoline for the combined technology
if present or grassroot of both technologies if there is no
FCC gasoline hydrotreating yet. The GT-BTX PluS unit, a
cost-effective two-column extractive distillation system,
facilitates the extraction of sulphur from the FCC gasoline,
preserving olefins in the raffinate stream with less than 10
ppm sulphur. The indicative configuration of the GT-BTX
PluS unit is illustrated in the Figure 1.
To implement the combined technology, middle cut
naphtha (MCN) that contains high-octane olefins and high
sulphurs is purposely fractionated after Prime-G+’s selective hydrotreating unit (SHU), leaving light cracked naphtha (LCN) that has high-octane olefins but low sulphurs,
and heavy cracked naphtha (HCN) that has low olefin content but high sulphurs. Such fractionation is illustrated in
Figure 2.
With such fractionation, the high-octane olefin-rich and
low-sulphur LCN will be sent to the gasoline pool. The
high-olefin and high-sulphur MCN will be processed in
the GT-BTX PluS unit, where the sulphur and olefin components will be separated to the extract and raffinate,
respectively, as illustrated in Figure 1. At the combined
technology’s gasoline mode, the preserved raffinate can be
blended into the gasoline pool, contributing to the retention of olefins and octane numbers, even in compliance
with Euro-5 ultra-low sulphur standards. Meanwhile, the
extract with concentrated sulphurs but nearly no olefins
will be combined with HCN to be hydrodesulphurised by
Prime-G+’s HDS without worrying olefin saturation. The
configuration of this combined technology is shown in
Figure 3. Notably, this configuration virtually eliminates
octane loss while significantly reducing hydrogen consumption, culminating in a refinery’s peak profitability in
Euro-5 gasoline production.
Combined technology in petrochemical
mode for gasoline-to-petrochemicals
The same combined technology of Prime-G+ and GT-BTX
PluS unveils an avenue for converting gasoline into valuable petrochemical products. In its petrochemical mode
with the same configuration, the GT-BTX PluS extract, a
nearly pure aromatic stream with sulphur being the only
impurities, undergoes intensified hydrodesulphurisation
LCN
FCC/RFCC
Naphtha
SHU
P
O
A
S
MCN
N
P
Extraction
(GT-BTX PluS)
Extract
Hydrogen
O
N
Raffinate
ULS
gasoline
<10ppm S
A
S
HCN
HDS
<10ppm S
Hydrogen
Figure 3 Configuration of the combined Prime-G+ and GT-BTX PluS technology in gasoline mode
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TIA Q1.indd 98
PTQ Q1 2024
www.digitalrefining.com
12/12/2023 12:16:02
LCN
Option of BTX and
Propylene production
P
A
FCC/RFCC
Naphtha
O
N
S
P
Extraction
(GT-BTX PluS)
MCN
SHU
Recycle to FCC for
extra Propylene
C6–C8
Extract
Hydrogen
O
N
Raffinate
ULS
gasoline
B/T/X/C9A
A
S
Higher severity
HDS
HCN
Hydrogen
Diesel
LCN
Option of only BTX
production
FCC/RFCC
Naphtha
SHU
P
O
A
S
N
MCN
C6–C8
P
Extraction
(GT-BTX PluS)
Extract
Hydrogen
O
N
Raffinate
ULS
gasoline
GT-Aromisation
B/T/X/C9A
A
S
Higher severity
HDS
HCN
Hydrogen
Diesel
Figure 4 Configuration of the combined Prime-G+ and GT-BTX PluS technology in petrochemical mode
(HDS) in the Prime-G+unit, culminating in a high-quality
petrochemical BTX product (benzene, toluene, xylenes).
Furthermore, the olefin-rich non-aromatics raffinate
stream derived from GT-BTX PluS proves invaluable for
FCC recycling, producing significantly additional propylene and enhancing the FCC propylene yield. Alternatively,
if aromatics is the focused product, this raffinate can be
routed to a fixed-bed GT-Aromatization unit, coupled
optionally with LCN, driving substantial BTX production.
Figure 4 shows the mentioned two options of combined
technology in the petrochemical mode for converting a
significant portion of FCC gasoline into petrochemical
products.
Operating flexibility of the combined
technology
The true strength of the Prime-G+ and GT-BTX PluS integration lies in its exceptional operating flexibility. Refineries
can seamlessly switch between gasoline-focused and
petrochemical-centric modes of operation. This adaptability is crucial as market demands oscillate, necessitating
rapid shifts in production focus. By adopting this combined
technology, refineries across diverse regions gain the agility to swiftly align their production strategy with prevailing
market requirements.
www.digitalrefining.com
TIA Q1.indd 99
Summary
Incorporating the combined Prime-G+ and GT-BTX PluS
technologies is a transformative investment for refineries.
This single investment affords refineries the dual capability to optimise both gasoline and petrochemical production, irrespective of ever-fluctuating market dynamics. The
intrinsic operating flexibility enables refineries to pivot
their focus instantly, whether the demand is for gasoline
or petrochemicals. In an industry where adaptability is
synonymous with success, the Prime-G+ and GT-BTX
PluS integration emerges as an indispensable asset for all
FCC-equipped refineries. By embracing this technology,
refineries can confidently navigate the intricate landscape
of post-pandemic refining, reaping significant benefits and
securing a competitive edge.
GT-Aromatization and GT-BTX PluS are trademarks of Sulzer
Chemtech. Prime-G+ is a trademark of Axens.
Sulzer Chemtech
Contact: [email protected]
Axens
Contact: [email protected]
PTQ Q1 2024
99
12/12/2023 12:16:02
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