[0001] The present invention relates to a novel composition, its use, and the method based
on the conveying of said composition through a fluid, in liquid phase or in vapor
phase, for the decontamination and cleaning of systems containing hydrocarbons in
petrochemical plants, such as refining plants or storage tanks.
STATE OF THE ART
[0002] Refining plants, petrochemical plants, storage tanks and hydrocarbon-containing systems
in general are periodically subjected to maintenance and cleaning. These operations
are required because of the depositing of organic and/or inorganic substances in the
systems, with the entailed efficiency loss and reduction in production. Apart from
increasing and/or restoring the system efficiency, cleaning is also carried out to
remove hazardous and pyrophoric substances from the apparatuses, thereby enabling
inspections by technical staff.
[0003] The cleaning process is applied for plant sections in shifts. Therefore, plant sections
face turnaround for the entire duration of the process, becoming unusable. This affects
general plant revenue. Therefore, it is important that cleaning applications be performed
effectively and over short times.
[0004] During turnaround, plants are subjected to decontamination, i.e., to a washing process
assisted by steam and specific products, called chemical steaming. The products used
in this procedure may be compositions based on mixtures of surfactants, as described
by
Patent US5462607, deriving from
International Patent Application PCT WO2016/170473 A1, or based on terpenes, as reported in USA Patent Application
US2004/0238006 A1. Specifically, this latter document describes a non-aqueous composition based on
terpenes and non-ionic surfactants that is conveyed by steam and used for cleaning
refinery and petrochemical plant apparatuses.
US 5 425 814
[0005] A discloses a method for cleaning and decontaminating hydrocarbon processing plant
equipment to remove scales and chemical deposits without a steamout step comprising
the steps of: isolating the equipment to be cleaned from other process equipment;
establishing a fluid loop of the equipment to be cleaned, including a pump for causing
fluid to circulate within the loop; filling the equipment with sufficient water to
cause any heat exchangers in the loop to be substantially full during circulation;
circulating the water through the loop; heating the water to a temperature of from
about 100°F to about the boiling point of water; adding a sufficient amount of an
extractant chemical with an affinity for contaminants present in the equipment and
a surfactant having emulsifying activity for said contaminant and extractant to said
water to form a heated emulsion to clean the surface of the equipment; contacting
surfaces of the equipment to be cleaned with the heated emulsion; circulating said
heated emulsion at the temperature through the loop for a period of time sufficient
to clean the contacted surfaces; and removing the circulating emulsion from the loop.
[0006] The compositions described in the literature have a high ecotoxicological impact
in case of dumping or intended sending to treatment (purification) systems, such as
the wastewater system and, more specifically, the activated sludge system.
[0007] Wastewater plants are developed chiefly based on the amounts of effluents (sewage)
to be treated, the typology of pollutants present and the disposal restrictions in
force.
[0008] One type of wastewater treatment is the biological process of activated sludge treatment,
which is an aerobic-type treatment conducted by a more or less prolonged aeration
of sewage inside a biological reactor in the presence of a microbial population (biomass),
aimed at reducing organic matter (in particular, Carbon and Nitrogen) concentration.
In activated sludge plants with a suspended biomass, the bacterial populations accountable
for the purification process are present in the form of floc kept in suspension through
air insufflation (if reactors are aerated) or by mixer (if reactors are anoxic or
anaerobic). The active biomass consists of numerous microorganisms (bacteria, protozoa,
metazoa, rotifera, etc.) continuously reproducing inside the reactor as a result of
biochemical reactions of organic carbon degradation and nutrient utilization, enabling
the consequent synthesis of new cell material. In short, the result obtained with
an activated sludge plant is the elimination of the biodegradable organic matter by
its transformation into inert material and in a concentrated sludge solution of organic
matter that must be subjected to further treatments prior to final disposal.
[0009] The presence, in the sewage being inlet, of chemical substances toxic to the activated
sludge is the cause of microbial population mortality and loss of wastewater plant
efficiency.
[0010] Moreover, during a cleaning application the formation of stable emulsions among condensed
steam/product/hydrocarbon can occur; said emulsions can entail a negative impact on
the wastewater plant, reducing its efficiency and polluting the activated sludges,
or reducing the system efficiency in case of refining plants, in which both the recovery
of the hydrocarbon disposed of by the system, scrubbed in order to reuse it in production,
and the concomitant clarification of water for its sending to the wastewater plant
are often required.
[0011] The chemical products usually applied in cleaning processes are compositions based
on mixtures of surfactants that, when conveyed in water, form foam. Foam has a mechanical
and chemico-physical effect fostering deposits removal from the surfaces to be cleaned.
However, when foam is persistent and present also in the sewage to be sent to the
wastewater plant, flow reduction, plant efficiency reduction and a negative impact
on activated sludges occur.
[0012] Moreover, under high-temperature conditions (50-120 °C, 122-248 °F), the chemical
compounds commonly used for cleaning might undergo thermal degradation, with the entailed
formation of products corrosive to metals that constitute the plant. Also a product
overdosage in the system might cause corrosion phenomena, in particular when the chemical
products used contain acidic substances such as dispersants. Moreover, the chemical
structure of hydrocarbons in a plant is such as to require the use of various products,
each one targeted at the removal of specific hydrocarbons. Therefore, it is important
that the products added into the system, concomitantly and, in some cases, with the
same dosage, be chemically compatible thereamong in order to prevent the formation
of undesired deposits and reaction byproducts.
SUMMARY OF THE INVENTION
[0013] The present invention relates to a novel composition developed to overcome the most
common technical problems associated with the use of the current chemical products
on the market for the decontamination and cleaning of hydrocarbon-containing systems.
In particular, the present invention provides an organic/solvent-based chemical composition
improved, compared to those currently in use, both in terms of hydrocarbon solubilization
ability and of impact on the wastewater plant, and ecotoxicological impact.
[0014] Object of the present invention are:
a composition comprising a) one or more compounds belonging to the class of N, N-Alkyl
amides and one or more compounds belonging to the class of terpenes; and b) a solvent
comprising water and at least one glycol or a derivative thereof;
the use of said composition for the decontamination and cleaning of systems containing
hydrocarbons; and
a method for decontamination and cleaning of hydrocarbon-containing systems, comprising
conveying (introducing) said composition into said systems.
GLOSSARY
[0015] In the present description, the term "hydrocarbon" (HC) has the meaning commonly
used in the literature, therefore denoting organic compounds containing only carbon
and hydrogen atoms. Three classes of hydrocarbons can be defined: aliphatic hydrocarbons,
which have a linear and/or branched open chain of carbon atoms and therefore are also
termed acyclic, and can be saturated and unsaturated;
alicyclic hydrocarbons, also termed naphthenic hydrocarbons, which are cyclic, i.e.,
closed-chain; aromatic hydrocarbons, characterized by the presence of at least one
benzene ring.
[0016] The term "solvent" in the present description has the meaning commonly used in the
chemical literature, therefore denoting a liquid substance dissolving a solid, liquid
or gaseous solute, giving rise to a solution.
[0017] The term "cosolvent" in the present description has the meaning commonly used in
the chemical literature, and therefore of one of the components of a solution, generally
the one present in greater amount along with the solvent, or the one that, in its
pure state, appears in the same aggregation state as the solution.
the term "surfactant" has the meaning commonly used in the literature, and indicates
substances having the property of lowering the surface tension of a liquid, facilitating
surface wettability or miscibility between different liquids. In general, they are
organic compounds with a polar "head" group, and a nonpolar "tail"; the compounds
with said features are more generally referred to as "amphiphilic" or "amphipathic".
[0018] The "asphaltenic crude" in the present invention is a crude containing a ≥ 5% w/w
percentage of asphaltenes. Asphaltenes are a class of high molecular weight compounds
contained in crude oil. They are solids at ambient temperature with a granular appearance
and dark brown to black color. They are substances insoluble in n-heptane and soluble
in benzene and/or toluene.
[0019] The "asphaltenic crude" considered is characterized by having 17-20% of Asphaltenes
and a Pour Point of 12°C . The Pour Point (PP) is the minimum temperature at which
the hydrocarbon is fluid (ASTM D97-17 and D5853-2017-05). The term "performance" has
to be understood as the HC solubilization ability, or the ability to have a good impact
on the wastewater plant, a good ecotoxicological impact, or both.
[0020] The term "test piece" refers to a sample of a given metal with an exposed metal surface.
The term "topping column residue" in the present invention is a hydrocarbon which
accumulates on the bottom of the topping column and proves to be of typically aromatic
composition.
[0021] By the term Benchmark BM, in the present invention, it is meant a class of commercial
products such as CHIMEC 2216 or Zymeflow 657 (products available on the market) of
reference, to which the performance and the applicative characteristics of the novel
products are compared. Said commercial products are based on active ingredients such
as alkyl amine oxide in water.
[0022] By the term Benchmark BM W, in the present invention there are meant the versions
of the same commercial products mentioned above, having a freezing temperature of
< -20°C. To attain such performances at low temperatures, BM W products compositions
commonly contain a certain amount of glycol.
[0023] The abbreviations DEK 291, DEK 293 and DEK 296 in the present invention denote different
mixtures of the same active ingredients, falling within the ranges reported below:
Glycol 30-80% w/w
Water 5 -30% w/w
N,N-alkyl amide 5-30% w/w
Terpene 0.5-5% w/w
Lauryl amine oxide 0 - 20% w/w
[0024] All mixtures are organic-based chemical compositions in solvent and water.
[0025] The term N,N-alkyl amide, for the purposes of the present description, denotes N,
N-alkyl amides wherein the alkyl group is a linear or branched chain of carbon atoms
with a number ranging from C
1 to C
18.
[0026] The term "derivative" referred to glycols, for the purposes of the present invention,
comprises glycol ethers.
DETAILED DESCRIPTION OF THE FIGURES
[0027]
Figure 1. Shows Carbon steel C1018 test pieces uniformly covered by asphaltenic crude prior
to Jar test start (see Examples Section).
Figure 2. shows said Carbon steel C1018 test pieces uniformly covered by asphaltenic crude,
immersed in the solutions tested at the end of the Jar test. In particular, the test
pieces are immersed in solutions containing 1) 1.5-2.5% BM; 2) 0.2-1% DEK 291; 3)
0.5-1.5% DEK 293; 4) 0.5-1.5% DEK 295 or 5) 1.5-2.5% BM W (see Examples Section).
Figure 3. shows a system designed and assembled to conduct the Steam-Condense Phase test, i.e.
a system able to simulate an application under chemical steaming, i.e. of reproducing
the stage of application in steam phase or in condense (condensate) phase. The system
is comprised of a glass column, a condenser, a condensate-collecting flask, a control
unit and a product nebulizing/adding system (see Examples Section).
Figure 4. shows a Carbon steel C1018 test piece, previously uniformly covered by asphaltenic
crude following a Steam-phase application of the product related to the invention,
DEK 293 (see Examples Section).
Figure 5. shows a Carbon steel C1018 test piece uniformly covered beforehand by asphaltenic
crude following a Condense-Steam-phase application of the product related to the invention,
DEK 293 (see Examples Section).
DETAILED DESCRIPTION
[0028] The present invention refers to a composition for the decontamination and cleaning
of systems containing hydrocarbons, comprising organic components able to solubilize
the hydrocarbons and a solvent conveying the components able to solubilize the hydrocarbons
into said systems through an aqueous or vapor (steam) phase.
[0029] Specifically, the composition object of the present invention comprises a) one or
more compounds belonging to the class of N,N-Alkyl amides and one or more compounds
belonging to the class of terpenes; and b) a solvent comprising water and at least
one glycol or a derivative thereof.
[0030] The novel compounds belonging to the class of N,N-alkyl amides, contained in said
composition, are new chemistry in vapor-phase applications; they were singled out
for their good solvent power for hydrocarbon substances, being conveyable by the steam
and being suitable from a toxicological standpoint to applications both in vapor phase
and of organic nature.
[0031] In fact, compounds belonging to the class of N,N-alkyl amides (NNAAs) are highly
biodegradable compounds and with a high solvent power for hydrocarbons. Such compounds
belonging to the class of N,N-alkyl amides have been classified as readily biodegradable
based on specific tests, termed OECD tests, aimed at assessing and standardizing the
biodegradability of organic compounds.
[0032] In one embodiment of the invention, said N, N-Alkyl amides can be alkyl amides wherein
the alkyl group is a linear or branched chain of carbon atoms with a number ranging
from C
1 to C
18.
[0033] In a particular embodiment, said N, N-Alkyl Amides can be selected from one or more
of N,N dimethyl 9-decenamide, N,N dimethyl decan-1-amide, N,N dimethyl octan-1-amide
and N,N dimethyl decan-1-amide, or mixtures thereof; and wherein the compound belonging
to the class of terpenes is selected from terpineol, D-limonene and Dipentene.
[0034] Terpineol and D Limonene are individual identified compounds. Dipentene is a mix
of plural terpenic structures. The terpenes in the mix can be individual ones or more
than one. Preferred NNAAs are the two N,N dimethyl 9-decenamide, N,N dimethyl decan-1-amide,
individually or a mixture of the two.
[0035] As described in the experimental section, for instance, NNAAs with a >C
18 chain of carbon atoms, obtained a 64% value in the OECD 301 B test. As a rule, the
active ingredients used in the products used in the prior art have a much lower biodegradability
percentage (> 20%); having an active ingredient highly effective and with a high biodegradability
enables the Inventors to assume a product easily disposable through the wastewater
disposal plant.
[0036] The Inventors have surprisingly discovered that the compounds belonging to the class
of N,N-alkyl amides as defined in the present description are characterized by a higher
solvent capability compared to other compounds commonly used for the cleaning of hydrocarbon-containing
systems; in fact, as reported in Table 1, N,N-alkyl amides considered in the study
(NNAAs with a <C
18 chain of carbon atoms) have a high Kauri-butanol (Kb) value.
[0037] The Kb value is an international, standardized measure of solvent power for a substance,
governed by ASTM D1133 test; therefore, the higher the Kb, the higher the activity
and the ability of the solvent being examined to dissolve hydrocarbons.

[0038] The N,N Alkyl Amides tested and considered in Table 1 prove to be non-flammable (H226),
are not carcinogenic (H350), are not suspected carcinogenic (H351), are not toxic
for the reproduction apparatus (H360D) and are not mutagenic for germ cells (H340).
These molecules, therefore, though having a Kb lower than other solvents indicated
in Table 1, do not have the H-sentences indicated, unlike:
N Methyl 2 Pyrrolidone, proves to be toxic for reproduction (H360D);
methylene chloride, proves to be H351 (suspect carcinogen);
D Limonene and xylene, prove to be flammable (H226) therefore with a handling more
difficult to manage;
benzene is H340 (germ cell mutagen) and H 350 (carcinogen).
[0039] According to the present invention, the solvent used is a solvent comprising water
and at least one glycol or a derivative thereof.
[0040] In one embodiment applicable to all of the abovedescribed embodiments, said glycol
can be an n-ethylene glycol or an ether thereof.
[0041] In a further embodiment, said glycol or derivative thereof can be selected among
monoethylene glycol, propylene glycol, triethylene glycol, polyethylene glycol, dipropylene
glycol monomethyl ether or mixtures thereof.
[0042] In one embodiment applicable to all of the above described embodiments, the composition
of the present invention could further comprise an oxidizing agent. Said oxidizing
agent could be of organic and/or inorganic nature and, preferably, able to reduce
the pyrophoric hazard from iron sulfide.
[0043] Said oxidizing agent could be, e.g., an alkyl amine oxide and/or peroxides. Non-limiting
examples of suitable alkyl amine oxides that may be comprised in the composition of
the invention can be lauryl dimethyl amine oxide, trimethyl amine oxide or N,N-dimethyl
decylamine N-oxide.
[0044] Peroxides commonly used in the field, such as, e.g., sodium percarbonate, sodium
perborate and hydrogen peroxide, could be used.
[0045] The composition of the invention consists of
Glycol 30-80% w/w
Water 5 -30% w/w
N,N-alkyl amide 5-30% w/w
Terpene 0.5-5% w/w
Oxidizing agent 0-20% w/w
to a total volume of 100%.
[0046] Non-limiting examples of embodiments of the composition as defined above, forming
part of the present invention, are provided hereinafter.
DEK 291 composition
water 10-20% w/w
glycol 60-80% w/w
N, N alkyl Amide 10-25% w/w
terpenes 0.5-3% w/w;
DEK 293 composition
Water 8-10% w/w,
glycol 60-80% w/w,
N, N alkyl Amide 5-25% w/w,
terpenes 0.5-3% w/w,
Alkyl amine oxide 0-20% w/w;
DEK 296 composition
water 10-20% w/w,
glycol 50-70% w/w,
N, N alkyl Amide 10-25% w/w;
terpenes 1-3% w/w
[0047] The composition object of the present invention, in any one of the abovedescribed
embodiments, can be used for decontamination and cleaning of systems containing hydrocarbons.
Therefore, object of the invention is the use of the composition of the invention
according to any embodiment described and/or claimed for decontamination and cleaning
of systems containing hydrocarbons.
[0048] Said use can be, e.g., applied to the decontamination and cleaning of hydrocarbon-containing
systems such as refining plants, petrochemical plants, storage tanks and Oil & Gas
systems in general.
[0049] The present invention also relates to a method of applying said composition for decontamination
and cleaning of systems containing hydrocarbons, comprising:
Adding the composition according to the invention, i.e. as defined in any embodiment
provided in the present description, in the examples and/or in the claims, into said
systems.
[0050] In one embodiment, said composition according to the invention can be added to a
fluid in an aqueous liquid phase or conveyed directly with a vapor (steam) phase,
at the typical concentrations of 0.5 - 10 %.
[0051] The composition can, e.g., be introduced into the system to be decontaminated through
lateral ports or from the highest point of the system, obtaining a "shower" effect
allowing to recover the washing fluid and the contaminants from the bottom, with a
single passage or with a recirculation. According to another embodiment, it is possible
to fill the system to be decontaminated with a volume of composition according to
the invention and water of about 1/3 of that of the unit, and by subsequently insufflating
steam from the bottom. The contaminated fluid is sent to wastewater treatment or into
a tank containing products to be disposed of.
[0052] An example of "system to be decontaminated" according to the present description
is a hydrocarbon-containing system and may be represented, without however being limited
thereto, by plants (e.g., refining ones), storage tanks or parts thereof. Therefore,
the composition can be applied with the aid of steam (Chemical Steaming) and/or of
water. As described in detail in the Examples section, the embodiments DEK291, DEK293
and DEK296, selected with the Jar test, were in fact subsequently monitored and tested
under chemical steaming. Initially, a system able to simulate an application under
chemical steaming (shown in Figure 3) was set up, thereafter the composition conveying
by the steam was assessed, whereas in the final tests the efficiency of the novel
composition was compared to CHIMEC benchmark (BM and BM W) products, both in steam
phase (as shown in Figure 4 and described in detail in the Examples section) and in
Steam-Condense phase (as shown in Figure 5 and described in detail in the Examples
section).
[0053] Therefore, it is possible to distinguish two modes for conveying said composition
for decontamination and cleaning of systems containing petroleum hydrocarbons. Specifically:
1. Application through liquid phase
[0054] The method for decontamination and cleaning of hydrocarbon-containing systems can
envisage the conveying of said composition into said systems through a liquid-phase
fluid that, therefore, can be aqueous. Moreover, said fluid that will be used for
plant decontamination and cleaning can be recirculated into the unit to be decontaminated
along with said composition, with the aid of specific pumps. Alternatively, or concomitantly,
the aqueous fluid added with the composition can be directed from the top of the system
to be treated, through the aid of a syphon, thereby obtaining a shower effect.
[0055] In each case, the wastewater is then discharged by the system from the bottom and
sent to any treatment or segregation sections.
[0056] Through this method for decontamination and cleaning of said system, both the chemical
action of the composition and the mechanical effect given by water turbulence in the
system are exploited.
2. Application through vapor phase
[0057] The method for decontamination and cleaning of hydrocarbon-containing systems envisages
the conveying of said composition into said systems through a vapor-phase (steam-phase)
fluid. The additive-charged fluid of the composition is saturated steam. For saturated
steam generation, a temperature of from 100°C to 160°C and a pressure set from 2 to
6 Bars will be used. The additive-charged saturated steam of the composition will
be used for cleaning through its introduction into the system from the bottom, so
that the nebulized/added composition be directed/conveyed by steam into the system.
[0058] Through this method for decontamination and cleaning of said system, both the chemical
action of the composition and the mechanical effect of steam are exploited.
[0059] Examples intended to illustrate, in a non-limiting manner, the invention and the
tests carried out in order to assay the efficiency thereof are provided hereinafter.
EXAMPLES
Jar Test
[0060] Test for measuring hydrocarbons (HC) solubilization ability (performance) under laboratory
conditions. The Jar test was initially carried out to test and single out the composition
and the embodiments thereof, and to further check any formation of HC/water emulsions.
[0061] A solution containing the composition to be tested was mixed with the use of an anchor,
at low speed (< 150 rpm), for 2-5 hours, at a temperature of from 90°C to 100°C. Thereafter,
Carbon steel C1018 test pieces were uniformly covered by a hydrocarbon (Figure 1).
For the Jar test, two hydrocarbon types were tested: i) an asphaltenic crude, and
ii) a topping column residue. Crude proved to be the more persistent hydrocarbon,
and more difficult to solubilize. As shown in Figure 2, the test piece was then immersed
in 200 ml of the solution to be tested. Thereafter:
- a) visual monitoring of hydrocarbons solubilization ability and emulsion formation;
- b) measuring of HC concentration in water, then measuring HC amount removed from the
test piece, and then further measuring of HC solubilization ability;
- c) measuring the Chemical Oxygen Demand (COD), which is an indirect measurement of
the amount of organic phase and of aqueous phase present in a water sample, 30 minutes
after the end of the test;
were carried out.
[0062] The performance of the composition and of the embodiments thereof was compared by
using products present on the market for the decontamination and cleaning of systems,
reported below:
Benchmark BM (CHIMEC 2216 or Zymeflow 657)
Benchmark BM W (versions of the abovementioned commercial products with a <-20°C freezing
point)
a) Visual monitoring
[0063] A visual assessment of HC amount removed from the test piece following the Jar test
allowed to visually single out some preferred embodiments, more performing compared
to Benchmark BM products. Specifically, compositions DEK 291, DEK 293, and DEK 296
were selected as more performing.
[0064] Moreover, the visual assessment of a possible formation of HC/water emulsions following
the Jar test allowed to rule out the formation of exclusions in case of use of the
composition object of the present invention.
b) HC concentration measurement
[0065] The measurement of HC concentration in water following the Jar test allowed to confirm
the higher performance of the three embodiments - 0.5% DEK 291, 1% DEK 293, and 1%
DEK 296 - compared to 2% Benchmark BM. Only data pertaining to tests carried out by
using test pieces covered by asphaltenic crude are reported, as the latter is more
persistent and more difficult to remove compared to topping column residue. In fact,
in tests with the topping column residue, all tested compositions, novel and non-novel
ones, removed HC from the test piece, not allowing to select and single out the most
performing compound/composition.
The oil amount removed from test pieces, i.e. the amount, expressed in mg/l, of HC
in water, was determined with spectrophotometric measuring (UV-Vis; at 580 nm), upon
preparation of the calibration curve. The results obtained have been reported in Table
2, and confirm that the

d) Chemical Oxygen Demand (COD) measurement
[0066] Aqueous phase COD measurement 30 minutes after the end of the Jar tests allowed to
obtain a theoretical estimate of COD contribution by the products. COD represents
one of the parameters commonly used for indirect measurement of the content of organic
substances present in a water phase. Obtained results have been reported in Table
3 and show that, considering the use percentages, the Benchmark BM is characterized
by a lower contribution of COD in the aqueous phase, whereas the three DEK embodiments
have an incidence on COD comparable thereamong.

[0067] The COD of solutions containing the composition and the Benchmark products at a 0.5%
(v/v) concentration was determined as well. The measurement was repeated 120 minutes
after the Jar Test, to check products distribution in water. The results are reported
in Table 4 and confirm that the lower COD value is attributable to the BenchMark BM,
whereas DEK embodiments have values higher and comparable thereamong.

Chemical Steaming Test
[0068] Test for assessing the steam (vapor) phase conveying of the composition object of
the present invention. HC solubilization ability by the embodiments related to the
invention were tested under chemical steaming.
As shown in Figure 3, initially a system able to simulate an application under chemical
steaming was set up. Said pilot experimental system was designed and assembled to
attempt reproducing the steam-phase application stage. The system is comprised of:
- Glass column, having a steam inlet on the bottom, a product inlet at mid-height, a hook for the
test piece at the head, a steam outlet at the head and a condense (condensation) outlet
on the bottom.
- Condenser, connected to the steam outlet at the column head. Aimed at condensing the steam.
- Flask, for collecting the condensation
- Control unit. Aimed at thermostating the column to prevent thermal shocks by steam passage, with
the entailed formation of condensate thereof.
- Product nebulizing/adding system
Steam, generated and provided by the production boiler, enters from the column bottom
at a pressure of 1-2 Bars. The composition to be tested is nebulized and injected
at mid-column and conveyed by the steam at the head, where the test piece with the
hydrocarbon is positioned.
[0069] For this test only one type of hydrocarbon was used, i.e. asphaltenic crude, which
proved to be the hydrocarbon more persistent and difficult to solubilize. These steam-phase
final tests were therefore carried out under pejorative conditions. The test piece
comes into contact with the steam/composition stream for about 3-6 hours. Steam and
composition are cooled by passing into the condenser, and the condensate is finally
collected into the flask.
[0070] Thereafter:
- a) measuring for determining steam- (vapor-) phase conveying of the composition through
a direct measurement of components present in the condensates;
- b) visual assessment of process efficiency under chemical steaming, for visual comparison
of the test piece between test start and end of test.
- c) olfactory impact under Chemical Steaming
were performed
[0071] The process efficiency, meant as the performance of the composition and of the embodiments
thereof under Chemical Steaming, was compared by using Benchmarks BM and BM W.
a) Measuring for determining Steam (vapor)-phase conveying
[0072] The conveying of the composition and of the embodiments thereof, DEK 291, DEK 293,
and DEK 296, by the steam was checked through measuring the compounds, in the collected
condensates, present in the compositions. For the detecting of Benchmark BM and BM
W concentration the Hach-Lange LCK 331 method was used, whereas for the determining
of embodiments DEK 291, DEK 293, and DEK 296 the total nitrogen measuring method,
referred to as Kjeldahl method, was used.
b) Visual assessment of Chemical Steaming process efficiency
[0073] The efficiency of the Chemical Steaming process by conveying of the composition object
of the present invention was instead assessed through a visual comparison of the test
piece covered by asphaltenic crude hydrocarbon between test start and end of test.
In particular, the efficiency was measured by visually assessing the condition of
the test pieces both at the end of the steam-phase test (Figure 4) and at the end
of the
"steam-condense" test (Figure 5). The difference between the two tests lies in the medium used to
carry the product into contact with the test piece. In fact, during the steam-phase
test, the nebulized composition is conveyed to the test piece exclusively by the steam
stream. In this condition, the novel compositions did not produce foam and removed
part of the hydrocarbon from the test piece. In the tests defined as "steam-condense
phase" the compositions are brought into contact of the test piece by the steam together
with condense (condensation).
c) Olfactory impact under Chemical Steaming
[0074] During steam phase tests, also the olfactory impact of the novel compositions was
considered. The aroma proved to be pleasant, though less intense compared to that
provided by CHIMEC benchmark BM and BM W products, under the same conditions. The
advantage of the novel compositions is that the pleasant smell is provided by a compound
that also has good solvent abilities (Terpenes) but is not toxic.
Corrosion test
[0075] In the composition object of the present invention glycol is present, which has the
dual function of making conveyable in water and steam the organic compound able to
solubilize hydrocarbons belonging to the class of N,N alkyl amide and of terpenes,
and of reaching a <-15°C freezing point.
[0076] To assess the corrosiveness of said composition, Jar tests in static mode were carried
out (reference: ASTM G31/G1) in which the composition in its embodiments, in a Chemical
Steaming process, was compared by using the Benchmarks BM and BM W .
[0077] The concentrations of the embodiments of the composition object of the invention
and of the Benchmark products in demineralized water used were equal to 20000 mg/l,
while the metal surface used (test piece) consisting of C1018 was exposed for four
days both to demineralized water without compositions and products added (blank),
and to demineralized water containing the compositions and products added. Process
temperature was of 100°C. Corrosion rate was expressed in MPY (miles per year, mm/y).
The results of the corrosion test are reported in Table 4 and have highlighted a corrosivity
of embodiments DEK 291 and 293 lower than the Benchmark products (BM and BM W), under
the conditions considered.

Respirometric tests
[0078] The method is based on the indirect measurement of the biological activity of an
activated sludge through estimate of the oxygen consumed under conditions of aerobiosis
and non-limiting substrate (Pagnotta and Tandoi, 1983). The methodology used (reference:
ISO 8192,2007-OECD 209) is based on the determination of the inhibiting effect of
the compositions being examined, tested at different concentrations, after 0.5 and
24 hours of contact time, towards the respiratory activity of an activated sludge
(OUR: oxygen uptake rate). Result expression is provided for in four inhibition classes:

[0079] The composition DEK 293, object of the invention, belongs to the fourth class related
to the power inhibiting the respiratory activity of the activated sludge, regarded
as the lower one defined by method OECD 209. It is deemed that all of the various
DEK embodiments mentioned in the present invention be equivalent to DEK 293 as to
the power inhibiting the respiratory activity of an activated sludge. The compositions
being examined are less toxic compared to the Benchmark BM reference product at 500
mg/l, as after 24 hours of exposure the activated sludge exhibits a 47.4% inhibition
thanks to the composition being examined, against the 67% obtained with exposure to
Benchmark BM. At higher concentrations the novel compositions exhibit an inhibition
that can be deemed equivalent to the best benchmark product on the ma rket.
[0080] Moreover, during the stage of aerating the activated sludge/experimental product
mixture no foam formation is observed. Test results are reported in Table 7.

[0081] The present invention therefore refers to a composition, its use, and to a method
for decontamination and cleaning of systems containing hydrocarbons based on the conveying
of said composition through a liquid-phase or a vapor-phase fluid.
[0082] Dosages being equal, the embodiments of the composition have performed a hydrocarbon
solubilization ability higher than the other known compositions considered as reference
in the study (BenchMark products BM and BM W), and moreover have exhibited a low corrosion
rate, as lower than 0.03 mm/y at 100°C in the concentration range equal to 13%. The
compositions of the products related to the invention also exhibit a low ecotoxicological
impact, as able to inhibit the respiratory activity of the activated sludges by 45%
in 24(h) at a dosage ≥ 500 mg/l. This data makes them fall under the lowest class
(IV: EC
50 >100 mg/l) of ecotoxicity for chemical compounds determined according to method OECD
209. Moreover, they have a low toxicological impact at environmental level, exhibiting
an EC
50 >100 mg/l in crustaceans, algae and fish. Moreover, when conveyed through water or
steam (vapor), they generate neither foam nor stable emulsions in the presence of
hydrocarbons. Therefore, a combining of the product with an antifoam agent and/or
with a specific product to break up the emulsion is unnecessary, as the sewage exhibits
a clear-cut phase separation between water, that will be sent to the treatment plant,
and hydrocarbon phase, that could be reused in-plant or adequately disposed of. The
composition related to the invention can however be used simultaneously with agents
generally used during liquid- and vapor-phase scrubbing. The agents considered in
the compatibility test, in a 1:1 ratio with the compositions related to the invention,
are of aqueous matrix, contain oxidizing substances suitable for the treatment of
pyrophoric iron and/or surfactant substances. Finally, the compositions object of
the invention exhibit a freezing temperature of ≤ - 15°C and, therefore, are also
applicable under extreme temperature conditions.
[0083] Applicable dosage interval: 0.5-10% on the water or steam (vapor) volume available
for the application.
1. A composition comprising one or more compounds belonging to the class of N,N-Alkyl
amides and one or more compounds belonging to the class of terpenes; and a solvent
comprising water and at least one glycol or ether thereof, wherein the composition
consists of:
a) Water 5-30%
b) N, N Alkyl amide 5-30%
c) Glycol 30-80%
d) Terpenes 0.5-5%
e) Oxidizing agent 0-20%
f) to a total of 100% w/w
expressed in percentage parts weight/weight.
2. The composition according to claim 1, wherein the alkyl group of said N, N-alkyl amide
is a linear or branched chain of carbon atoms with a number ranging from C1 to C18.
3. The composition according to claim 1 or 2, wherein the N,N-Alkyl amide is selected
from N,N dimethyl 9-decenamide, N,N dimethyl decan-1-amide, N,N dimethyl octan-1-amide
and N,N dimethyl decan-1-amide, or mixtures thereof; and wherein the terpenes are
selected from terpineol, D-limonene and Dipentene, or mixtures thereof.
4. The composition according to any one of claims 1 to 3, wherein said glycol is selected
from monoethylene glycol, propylene glycol, triethylene glycol, polyethylene glycol,
dipropylene glycol monomethyl ether, or mixtures thereof.
5. The composition according to any one of claims 1 to 4, wherein said oxidizing agent
is selected from one or more alkyl amine oxides and/or peroxides.
6. The composition according to claim 5, wherein said alkyl amine oxide is selected from
lauryl dimethyl amine oxide, trimethyl amine oxide and/or N,N-dimethyl decylamine
N-oxide, and said peroxide is sodium percarbonate, sodium perborate or hydrogen peroxide.
7. The composition according to any one of claims 1 to 6, wherein said composition consists
of
water 10-20% w/w
glycol 60-80% w/w
N, N alkyl Amide 10-25% w/w
terpenes 0.5-3% w/w;
or
Water 8-10% w/w,
glycol 60-80% w/w,
N, N alkyl Amide 5-25% w/w,
terpenes 0.5-3% w/w,
Alkyl amine oxide 0-20% w/w;
or
water 10-20% w/w,
glycol 50-70% w/w,
N, N alkyl Amide 10-25% w/w;
terpenes 1-3% w/w
8. The use of the composition according to any one of claims 1 to 7 for the decontamination
and cleaning of systems containing hydrocarbons.
9. The use according to claim 8, wherein said hydrocarbon-containing systems are refining
plants, petrochemical plants, storage tanks or oil & gas systems.
10. A method for decontamination and cleaning of hydrocarbon-containing systems, comprising:
introducing the composition according to any one of claims 1 to 7 into said systems.
11. The method according to claim 12, wherein said composition can be added to a fluid
in an aqueous liquid phase or conveyed directly with a vapor phase.
12. The method according to claim 11, wherein said composition is introduced at concentrations
of 0.5 - 10 % on the water or steam (vapor) volume.
13. The method according any one of claims 10 to 12, wherein said composition is introduced
into said system to be decontaminated through lateral ports, or from the highest point
of the system or by filling said system with a volume of said composition and water
at about 1/3 of the volume of said system by subsequently insufflating steam from
the bottom.
1. Zusammensetzung, umfassend eine oder mehrere Verbindungen, die zu der Klasse von N,N-Alkylamiden
gehören, und eine oder mehrere Verbindungen, die zu der Klasse von Terpenen gehören;
und ein Lösungsmittel, umfassend Wasser und mindestens ein Glykol oder einen Ether
davon, wobei die Zusammensetzung besteht aus:
a) Wasser 5 bis 30 %
b) N, N-Alkylamid 5 bis 30 %
c) Glykol 30 bis 80 %
d) Terpenen 0,5 bis 5 %
e) Oxidationsmittel 0 bis 20 %
f) auf insgesamt 100 Gew.-%
ausgedrückt in Prozentanteile Gewicht/Gewicht.
2. Zusammensetzung nach Anspruch 1, wobei die Alkylgruppe des N,N-Alkylamids eine lineare
oder verzweigte Kette von Kohlenstoffatomen mit einer Anzahl in dem Bereich von C1 bis C18 ist.
3. Zusammensetzung nach Anspruch 1 oder 2, wobei das N,N-Alkylamid aus N,N-Dimethyl-9-decenamid,
N,N-Dimethyldecan-1-amid, N,N-Dimethyloctan-1-amid und N,N-Dimethyldecan-1-amid oder
Mischungen davon ausgewählt ist; und wobei die Terpene aus Terpineol, D-Limonen und
Dipenten oder Mischungen davon ausgewählt sind.
4. Zusammensetzung nach einem der Ansprüche 1 bis 3, wobei das Glykol aus Monoethylenglykol,
Propylenglykol, Triethylenglykol, Polyethylenglykol, Dipropylenglykolmonomethylether
oder Mischungen davon ausgewählt ist.
5. Zusammensetzung nach einem der Ansprüche 1 bis 4, wobei das Oxidationsmittel aus einem
oder mehreren Alkylaminoxiden und/oder -peroxiden ausgewählt ist.
6. Zusammensetzung nach Anspruch 5, wobei das Alkylaminoxid aus Lauryldimethylaminoxid,
Trimethylaminoxid und/oder N,N-Dimethyldecylamin-N-oxid ausgewählt ist und das Peroxid
Natriumpercarbonat, Natriumperborat oder Wasserstoffperoxid ist.
7. Zusammensetzung nach einem der Ansprüche 1 bis 6, wobei die Zusammensetzung besteht
aus
Wasser 10 bis 20 Gew.-%
Glykol 60 bis 80 Gew.-%
N,N-Alkylamid 10 bis 25 Gew.-%
Terpenen 0,5 bis 3 Gew.-%;
oder
Wasser 8 bis 10 Gew.-%,
Glykol 60 bis 80 Gew.-%,
N,N-Alkylamid 5 bis 25 Gew.-%,
Terpenen 0,5 bis 3 Gew.-%,
Alkylaminoxid 0 bis 20 Gew.-%;
oder
Wasser 10 bis 20 Gew.-%,
Glykol 50 bis 70 Gew.-%,
N,N-Alkylamid 10 bis 25 Gew.-%;
Terpenen 1 bis 3 Gew.-%
8. Verwendung der Zusammensetzung nach einem der Ansprüche 1 bis 7 für die Dekontamination
und Reinigung von kohlenwasserstoffhaltigen Systemen.
9. Verwendung nach Anspruch 8, wobei die kohlenwasserstoffhaltigen Systeme Raffinerieanlagen,
petrochemische Anlagen, Lagertanks oder Öl- und Gassysteme sind.
10. Verfahren für die Dekontaminierung und Reinigung von kohlenwasserstoffhaltigen Systemen,
umfassend:
Einführen der Zusammensetzung nach einem der Ansprüche 1 bis 7 in die Systeme.
11. Verfahren nach Anspruch 12, wobei die Zusammensetzung einem Fluid in einer wässrigen
Flüssigphase zugesetzt oder mit einer Dampfphase direkt befördert werden kann.
12. Verfahren nach Anspruch 11, wobei die Zusammensetzung in Konzentrationen von 0,5 bis
10 % des Wasser- oder Dunst(dampf)volumens eingeführt wird.
13. Verfahren nach einem der Ansprüche 10 bis 12, wobei die Zusammensetzung in das zu
dekontaminierende System durch seitliche Öffnungen oder von dem höchsten Punkt des
Systems aus oder durch Füllen des Systems mit einer Menge der Zusammensetzung und
Wasser in Höhe von etwa 1/3 des Volumens des Systems und durch anschließendes Einblasen
von Dunst von unten eingeführt wird.
1. Composition comprenant un ou plusieurs composés appartenant à la classe des N,N-alkylamides
et un ou plusieurs composés appartenant à la classe des terpènes ; et un solvant comprenant
de l'eau et au moins un glycol ou un éther de celui-ci, dans laquelle la composition
est constituée de :
a) eau 5 à 30 %
b) N,N alkylamide 5 à 30 %
c) glycol 30 à 80 %
d) terpènes 0,5 à 5 %
e) agent oxydant 0 à 20 %
f) jusqu'à un total de 100 % p/p
exprimé en parties en pourcentage poids/poids.
2. Composition selon la revendication 1, dans laquelle le groupe alkyle dudit N,N-alkylamide
est une chaîne linéaire ou ramifiée d'atomes de carbone ayant un nombre allant de
C1 à C18.
3. Composition selon la revendication 1 ou 2, dans laquelle le N,N-alkylamide est choisi
parmi N,N diméthyl 9-décénamide, N,N diméthyl décan-1-amide, N,N diméthyl octan-1-amide
et N,N diméthyl décan-1-amide, ou des mélanges de ceux-ci ; et dans laquelle les terpènes
sont choisis parmi terpinéol, D-limonène et dipentène, ou des mélanges de ceux-ci.
4. Composition selon l'une quelconque des revendications 1 à 3, dans laquelle ledit glycol
est choisi parmi monoéthylène glycol, propylène glycol, triéthylène glycol, polyéthylène
glycol, éther monométhylique de dipropylène glycol, ou des mélanges de ceux-ci.
5. Composition selon l'une quelconque des revendications 1 à 4, dans laquelle ledit agent
oxydant est choisi parmi un ou plusieurs oxydes et/ou peroxydes d'alkylamine.
6. Composition selon la revendication 5, dans laquelle ledit oxyde d'alkylamine est choisi
parmi oxyde de lauryldiméthylamine, oxyde de triméthylamine et/ou N-oxyde de N,N-diméthyldécylamine,
et ledit peroxyde est le percarbonate de sodium, le perborate de sodium ou le peroxyde
d'hydrogène.
7. Composition selon l'une quelconque des revendications 1 à 6, dans laquelle ladite
composition est constituée de
eau 10 à 20 % p/p
glycol 60 à 80 % p/p
N,N alkylamide 10 à 25 % p/p
terpènes 0,5 à 3 % p/p ;
ou
eau 8 à 10 % p/p,
glycol 60 à 80 % p/p,
N,N alkylamide 5 à 25 % p/p,
terpènes 0,5 à 3 % p/p,
oxyde d'alkylamine 0 à 20 % p/p ;
ou
eau 10 à 20 % p/p,
glycol 50 à 70 % p/p,
N,N alkylamide 10 à 25 % p/p ;
terpènes 1 à 3 % p/p
8. Utilisation de la composition selon l'une quelconque des revendications 1 à 7 en vue
de la décontamination et du nettoyage de systèmes contenant des hydrocarbures.
9. Utilisation selon la revendication 8, dans laquelle lesdits systèmes contenant des
hydrocarbures sont des usines de raffinage, des usines pétrochimiques, des réservoirs
de stockage ou des systèmes pétroliers et gaziers.
10. Procédé de décontamination et de nettoyage de systèmes contenant des hydrocarbures,
comprenant :
l'introduction de la composition selon l'une quelconque des revendications 1 à 7 dans
lesdits systèmes.
11. Procédé selon la revendication 12, dans lequel ladite composition peut être ajoutée
à un fluide en phase liquide aqueuse ou transportée directement avec une phase vapeur.
12. Procédé selon la revendication 11, dans lequel ladite composition est introduite à
des concentrations de 0,5 à 10 % du volume d'eau ou de vapeur d'eau (vapeur).
13. Procédé selon l'une quelconque des revendications 10 à 12, dans lequel ladite composition
est introduite dans ledit système à décontaminer par des orifices latéraux, ou à partir
du point le plus élevé du système, ou en remplissant ledit système avec un volume
de ladite composition et d'eau à environ 1/3 du volume dudit système, en insufflant
ensuite de la vapeur d'eau à partir du fond.