Hot corrosion mechanism
Study of mechanism
involved in hot corrosion and erosion requires
a good knowledge regarding the identification of the particle formation mechanisms. In
large-scale diesel engines these mechanisms vary in magnitude and proportion
basically due to environmental variables as compared to light-duty or heavy-duty engines, due to
different fuel specifications initially to begin with.
The fuel in large-scale diesel engines usually contains a
high fraction of aromatics and ash (approx. 0.1 wt. %), which is composed of
vanadium, sodium, calcium, nickel, magnesium, aluminium, and silicon. In
addition, the sulphur content of the fuel oil is usually high, approx. 3 wt. %.
Therefore, low-melting vanadylvanadates are formed. The high calcium content of
the lubricating oil may also have a profound effect on the corrosion of some
materials/coatings.
The residence time to prevent the nucleation of hydrocarbon
(HC) species and, in the case of high S-content fuel oils, the
nucleation/condensation of sulphuric acid. Nucleation is a competing process
with adsorption and condensation on pre-existing soot particles. Thus the
dynamic behavior of this vapor-particle system in the dilution process will
determine the number size distribution after dilution and cooling. Particle and
deposit characteristics play an important role in studying corrosion and
erosion phenomena in combustion systems. Furthermore, the corrosion and erosion
of different materials nearly always involve a growing deposit layer. To
determine the effects and mechanisms of corrosion and erosion, the morphology structure,
and composition of the depositing particles and the deposit are important.
Additionally, the chemical reactions taking place in the deposit layer need to
be recognized in order to find out how the depositing particles start to
react/transform into the actual deposit. The formation of the deposit may have
crucial effects on the corrosion/erosion mechanisms; these mechanisms can be
different if the deposit is absent from the surfaces under corrosive/erosive
attack.
Attempt is made to simplify the mechanism , as well as to explain in depth , so that the process can be understood and appreciated.
The in the process of blending fuel , no method is specified other than the end result as ISO 8217/2015 - used Lubricating oil blending does take place. The effects sometimes detrimental due to burning characteristics and trace elements present.Some aid in reduction of corrosion - but the overall effect is to be studied basis condition checks and a thorough understanding of the process will aid in prevention or preventive steps , considering no punacea in the ever changing scenarios .
Effects of fuel additives in particulates and corrosive formations
Water : emulsifying, gave results that depended on the
quality of the fuel oil; the addition of small amounts of water increased the
particle mass concentrations for fuel oils with a high aromatic content (46 wt.
%) and decreased them for fuel oils with a lower aromatic content
Mg-based compounds prevent the formation of highly corrosive
vanadylvanadate compounds that contain mainly vanadium, sulphur, and sodium of
different compositions and have low melting points the particle mass concentrations decreased
clearly and SO3(g) concentrations increased. The main mechanisms for reduced
particle emissions were: easily ionisable elements that reduce soot formation;
elements that enhance OH-radical formation and increase soot oxidation, and
elements that get absorbed by soot and increase their combustion rate . Mg can
also enhance the burnout of heavy aromatics, soot, carbon, etc. in the
particles acting as a carbon oxidation accelerator
The fuel oil additives used in burning heavy
fuel oils are usually Mg-based vanadylvanadates that have melting points that
are clearly higher than those of their sodium counterparts. Thus the deposits
are no longer molten/highly The advantage of using these additives is that
magnesium reacts with vanadium toform magnesium sintered and the detrimental fluxing of the elements is hindered. Moreover, the structure of the deposit is transformed into a more porous and less adhesive form .
To attain these favourable effects, the magnesium-vanadium
weight ratio should be approx. 1.5:1 (3:1 in molar ratio ). Even higher Mg-V
weight ratios are beneficial and silicon can also be advantageous . However,
especially in oil-fired furnaces, the use of Mg-based additives causes other
problems. The deposits can build bridges between heat exchanger tubes because
of increased ash loading and thus hinder effective heat transfer . Increased
ash loadings may also cause problems.
Ferrocene (Fe(C5H5)2 can enhance soot oxidation, thus reducing
emissions.
Cerium has also been
studied as a fuel oil additive. It has been proposed that a Ce additive mainly
reduces the concentration of organic carbon (OC), but not so much the
concentration of elemental (EC) or black carbon (BC) in the exhaust particles
Mechanisms for deposition build-up
The mechanisms for deposition build-up on various components
depends upon the conditions existing at the time of combustion and post
combustion with reference to gas flow and constrictions. mechanisms for
particles present in the gas phase are direct impaction, turbulent impaction, thermophoresis,
Brownian motion, and gravitation. Vapours can deposit by direct condensation or
by chemisorption, i.e. by adsorption on to the surface followed by chemical
reaction
Basic mechanisms of deposition build-up can be considered as follows:
1.
Direct and Turbulent impaction : Main deposition
mechanism due to impaction at bends or direct incidental surfaces with a
heavier particle sizes of higher velocities with lower gas velocities The main issues to
consider in particle deposition are the turbulence of the flow and the boundary
layer of the particle concentration, consisting of the buffer layer and laminar
sublayer. The turbulence of the flow will have an impact on all of the deposition
mechanisms because it controls how great an amount of the particles will be
able to penetrate the buffer layer. In turbulent impaction the turbulent eddies
transport the particles through the buffer layer into the laminar sublayer. To
be able to deposit on to the system surfaces the particles will have to
penetrate through the laminar sublayer; this can occur if the particles have
enough momentum from the turbulent flow. The mechanism is then called turbulent
impaction. one example is soot along the pipelines , surfaces and fins on
economizers(usually accounts to 2/3 rds of deposits).
1. 2. Thermophoresis, Brawnian movement Gravitation and
Chemisorption and Maragoniconvection : Deposition mechanism due to smaller
particles , Thermophoresis is defined as the movement of particles caused by
the hot, more energetic gaseous molecules towards the gaseous molecules near
the colder surface(s). where the impact is due to absorption/ adsorption on the
surface due to surface roughness and peripheral layer being the reactive layer.This
chemical effects aided by the rate of change of surface tension with
temperature (Maragoni convection) in molten phase can also yield or emphasize
reactivities leading to oxidation/detachment.
Deposition morphology and flake-off
Corrosion build up advances from the bottom of the pit towards the surface
of the deposit, the structure analyzed was initially crystalline due to various
trace elements also sublimated under combustion and deposited forming complexes
(such as Ca), but transformed near and at the surface of the pit into one that
was more irregular and sintered/fused, increasing porosity.. This is caused by
outward Cr lattice/grain boundary diffusion. From the interface between the pit
and bottom reacted layer needles/pegs penetrating into the bottom reacted layer
were seen the “keying effect” The pegs tend to serve as “anchors” for the deposit/oxide layer
. Al was found at the vertexes of these pegs , due to reverse convections on
account of variable surface gradients of metal/oxide/ liquid sinters ,
resulting in not enough Al to form a continuous aluminum oxide layer.
A zone of “black islands”, an indicative of internal corrosion
form in the bottom layer under the pit with varied sizes.
Cr, Al, Ti, and Fe diffused from the base
material (Nimonic 80 A) towards the surface of the pit. The highest Ti and Cr
concentrations were observed at, or in the vicinity of, the bottom of the pit.
The Cr concentration decreased almost steadily until it was almost zero near
the deposit base, except for the case at 750°C, where Cr had propagated further
in the deposit than in the other cases. Similar behaviour at 750°C was also
observed for Ti. However, oxygen behaved differently in the high-temperature. At
700°C experiments the oxygen concentration increased as the concentration of Ni
and V decreased and vice versa. Vanadium, on the other hand, diffused strongly
towards the base material, as it was found throughout the corrosion pit, although
the relative concentration of V was much lower in the high-temperature 750°C
case than in the 700°C case. S was not able to penetrate deeply into the pit or
the bottom layer. On the other hand, distinct “black islands” rich in S were
detected in the bottom layer
Deposition flake-off and particle re-entrainment are the key
causes of irregular shaped particles, thus ensuring . peeling of the deposits,
mainly from the exhaust valve surfaces (also turbine blades. This could be
explained by the cleavage of the deposit material and/or re-entrained particles
from the surfaces of the combustion system.
There are several factors that may affect the
cleavage of the deposit layer or the stickiness of the deposit, viz. fuel
composition (the amount of ash), fuel additives, the composition of the
lubricating oil, the chemical environment of the elements, the materials (valve
materials, hardfacings, turbine blade materials, etc.), system temperatures,
and flow velocities. Another important factor is the carbon (C) present in
various nascent forms in the particles;
because these particles deposit on the surfaces, and nascent carbon present in
the particles is burned off, heat is released. The released localized heat can also have an effect on the deposit
stickiness because of instantaneous
local spot temperature increase, which
facilitates melting/sintering phenomena. The chemical reaction(s) taking place
in the deposit can also vary significantly, because the gas atmosphere
surrounding the deposit may first be reducing and then convert to oxidizing one
due to convective currents.
While all of these factors have an impact on the deposit stickiness,
the contributing factor to all these can be the composition of the fuel and lubricating
oil, different materials, and process and material temperatures determining the melting/sintering tendency of
the deposited particles.
The effect of fuel oil composition on the composition,
structure, and stickiness of the deposit altered significantly when the high
ash content fuel oil was doped with a Mg-Si-based fuel oil additive; the
thickness of the deposit layers was about 1/10 of that obtained with HFO only.
The structure of the deposit was also more porous and clinker-like structures
(cobble-stone) were more uncommon. The porous and brittle structure of the
deposit contributed to the small amount of the deposit and the ease of
cleavage.
.Corrosion propagation
The deposits that take place during transient conditions
cannot be termed as totally melted ones , as a molten pool will have solid
deposit due to flow of gases/ transport phenomena of other elements. One such
phenomena is Sulphur and other elements , before the detachment and further
action takes place , which can be explained as under for further propagation.
Sulphur transport mode (atomic or molecular SO2/SO3 diffusion)
into the deposit/base material . For Nimonic 80 A under these conditions the
only mode for sulphur transport was molecular SO2/SO3 diffusion. However, from
the bottom of the deposit into the base material sulphur transport occurs by
atomic sulphur diffusion via grain boundaries and/or by lattice diffusion.
As the corrosion at 700°C was strongest with both SO2(g) and
Vanadium feeds, the mutual effect of SO2/SO3 and vanadium is critical. The
Cr-based oxide layer in the pit area transformed into a more permeable form so
that the diffusion over that layer with a more rapid and sulphur can increase the activity of vanadium
compounds (mainly V2O5) and therefore enhance corrosion by solid/gas transport
promoted by a trace of V in the oxide lattice, and no liquid phase is present
at the scale/base material interface (no fluxing of the elements). This would
explain the faster corrosion found with both SO2 and Vanadium feeds, even
though no severe indications of sintering can be noticed.
The deposit and in the pit underneath the first particles
formed by nucleation and were composed of NiO followed by sodium vanadates
(Na2O·V2O5). Finally, vanadium oxide (VO2) and Na2SO4 condensedon the surfaces of the nucleated particles. However, VO2 oxidised further into V2O5. The composition of
the particles indicated that the deposit contained, at least at the beginning,
sodium sulphate.The sulphur (as SO2/SO3) diffused through the porous deposit
layer by molecular diffusion. When S, as SO2/SO3, reached the interface of the
bottom layer lower in Cr and closer to base
material, it reacted with Cr, which is the most stable oxide, and also with Ti
and Ni to form the internal sulphidation , forming precipitates seen as “black
islands” at the bottom layer initially due to low oxygen and distributed via
the grain boundaries.
Availability of oxygen in transient exhaust further results
in diffusion of molecular Oxygen through porous layers and displace sulphurin
internal sulphidation by way of catalyzed V2O5 and furthering oxidation of Sulphur
to So2/SO3 – thus making a Sulphite
layer into oxide layer and then the process continues to have a further front
of Black islands of internal sulphidation reaction – under further favourable
transient conditions of availability of Sulphur and Vanadium fronts.
Vanadium is known to (V2O5) catalyse the SO2(g)+O2(g) oxidation
reaction, the yield being heavily dependent on the gas atmosphere the
conversions can be as high as 80% in the presence of vanadium, but only a few
per cent without vanadium. Because of the high amount of V present in the
system as V2O5 (highly oxidising environment), SO2 can further react to SO3.
SO3 is even more reactive than SO2. Therefore, with both SO2(g) and synthetic
ash particles (SAP, including vanadium), more SO3 was formed and the corrosion rate can
accelerate.
The most stable oxides at the pit are Cr2O3 and
V2O5, but nickel is in the form of NiSO4 or (NiO)(Cr2O3). The most stable oxide
forms are highly dependent on partial pressures of sulphur dioxide and oxygen.,
that the formation of the nickel chromates and sulphates leading to type II hot corrosion, also called “low
temperature hot corrosion” .
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