Авторы

  • D.D. Bilalova
    Tashkent State Technical University, Tashkent
  • S.M. Turobjonov
    Tashkent State Technical University, Tashkent
  • Kh.I. Kadirov
    Tashkent Chemical-Technological Institute, Tashkent

DOI:

https://doi.org/10.71337/inlibrary.uz.arims.98156

Ключевые слова:

corrosion inhibitor oil surfactants chlorine waste anti-corrosion coatings

Аннотация

The aim of the research is to determine the inhibitory properties of the product of the interaction of chlorine-containing waste with diethanolamine. The object of the research is the water of oil production and processing enterprises, in particular, the North Urtabulak field under the jurisdiction of Mubarekneftegaz.


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CORROSION INHIBITOR BASED ON CHLORINE-CONTAINING

WASTE

1

Bilalova D.D.,

1

Turobjonov S.M.,

2

Kadirov Kh.I.

1

Tashkent State Technical University, Tashkent

2

Tashkent Chemical-Technological Institute, Tashkent

https://doi.org/10.5281/zenodo.15525994

Abstract

. The aim of the research is to determine the inhibitory properties

of the product of the interaction of chlorine-containing waste with

diethanolamine. The object of the research is the water of oil production and

processing enterprises, in particular, the North Urtabulak field under the

jurisdiction of Mubarekneftegaz.

Keywords:

corrosion inhibitor, oil, surfactants, chlorine waste, anti-

corrosion coatings

In the last decade, the use of organic and inorganic compounds as corrosion

inhibitors has become irrelevant over time, as their toxicity to the environment

has raised concerns about their use. Controlling the rate of metal corrosion by

nanomaterials is a way to highlight a new discovery in nanotechnology.

Nanomaterials have higher anti-corrosion properties, and their additives are

good corrosion inhibitors due to their larger surface-to-volume ratio compared

to conventional macroscopic materials. Many processes have been used to

prepare nanoparticles, and various researchers have successfully demonstrated

the applicability of nanomaterials as corrosion inhibitors [1,2].

BASF Company offers a coating inhibitor [3] for use in oil fields based on

polymers or oligomers of poly acid polyester, alkoxylated alcohol, or polyamine

condensate of fatty acid, which also contain surfactants; a corrosion inhibitor is

used for acidic systems, including ammonium iodide ion, a primary carbonyl

compound containing alkyl or an aromatic group containing from 1 to 6 carbon

atoms, alkyl or aromatic groups in turn may additionally contain nitrogen,

phosphorus, halogen, or a second oxygen fragment [4]; a corrosion inhibitor and

a composition based on it, including contact of a metal surface with an acidic

liquid containing a water base liquid, acid, as well as a strengthening composition

containing a compound that corresponds to the formula R

1

R

2

XCCOOH, where X

is a halogen, R

1

is C

1

-C

20

alkyl groups, C

3

-C

20

cycloalkyl groups, R

2

contains at least

one oxialkyl C

1

-C

20

and an aryl group C

6

-C

20

[5]; based on acrylonitrile, the

inhibitor Ifhangaz-1 was synthesized, developed by the Institute of Physical and
Inorganic Chemistry of the Russian Academy of Sciences jointly with the VNI Gaz

and the Volgograd branch of the VNI PAV Minneftechemprom [6]; anti-corrosion

coatings have found wide application in protecting metals from corrosion,

among which PINS [7] occupies an important place, which represents a complex

mixture of corrosion inhibitors, plasticizers, and protective components in

organic solvents; in the works [8] universal corrosion inhibitors based on amino

phenols, as well as "SNPX" heterocyclic amines (alkyl-[poly- (ethylene oxy) ]-


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phosphoryl pyridines, alkyl-[poly- (ethylene oxy) ]-phosph.

The purpose of this work is to determine the inhibitory properties of the

product of the interaction of the chlorine-containing waste with diethanolamine.

The water of oil production and processing enterprises, namely the North

Urtabulok field under the "Muborakneftegaz" Production Association, was

selected as the research object.

When extracting crude oil, to free it from mineral salts, it is washed with

water. Water after settling and separation is used in the reservoir pressure

maintenance system. For oil flushing, reservoir or furrow water heavily

contaminated with mineral salts is typically used (Table 1).

Table 1

Analysis* of the water of Northern Urtabulak under the "Muborakneftegaz" UE

Cations

Content in liters

Other definitions

mg/l

mg-eq/l

%-eq/l

Na

+

21332

927,50

65

Hardness mg-eq/l

General

505,00

K

+

30

0,77

-

Removable

NH

4+

150

2,42

-

Carbonate

4,30

Ca

2+

8000

400,00

28

Non-carbonate

500,70

Mg

2+

1276

105,00

7

рН

7,20

Fe

3+

<0,3

CO

2

free. mg/l

n/о

Fe

2+

<0,3

CO

2

agr. mg/l

n/о

Total

1435,69

100

Oxidation capacity mg O

2

/l

Anions

Content in liters

SiO

2

mg/l

n/о

mg/l

mg-eq/l

%-eq/l

Н

2

S

mg/l

7,16

Cl

49644

1400,00

98

РО

4

mg/l

SO

42-

1230

25,63

2

The

dry

residue

is

experimental.

84614

NO

2-

<0,01

Calculated.

82150

NO

3-

357

5,76

-

Physical properties:

Cont.

CO

3-

нет

Transparency

HCO

3-

262

4,30

-

Taste

brine

Total

1435,69

100

Color

Analysis of the data shows that the water of the Northern Urtabulok PPD is

distinguished by its exceptional hardness (505.0 mg-eq/l), the composition of

mineral salt precipitates (according to the ratio of the sum of cations and anions,

%-eq/l: Na

+

=32.5; Ca

2+

= 14.0; Mg

2+

= 3.5, Cl

-

= 49.0; SO4

2-

=1.0) and the content of

mechanical impurities and hydrogen sulfide.

The reaction of the chlorine-containing residue with alkanolamines and

soapstock was carried out in the following sequence: in a 250 ml round-bottom

flask with a solution and upon heating, monoethanolamine and potassium

hydroxide in a 1:1 mol ratio. The mixture was heated while stirring until

potassium hydroxide dissolved at a temperature of 75 °C. The resulting solution

was cooled to room temperature. A small portion of the chlorine-containing

residue during cooling was poured into the flask while constantly stirring, as this


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reaction is highly exothermic. As a result, diaminodiethyl ether of ethylene glycol
and potassium chloride were formed. Next, dietyl ether was added to the resulting

product (as a solvent), resulting in the precipitation of potassium chloride, which

we separated by filtration; the ether was distilled (tboil C

4

H

10

O = 34.6 °C).

Calculated amounts of soapstock - a secondary product of oil and fat plants - were

added to the resulting diamine. During the reaction, a mixture of β-

aminodiethylethyoxy-β-carboxamide of carbonic acids and glycerin is formed.

Glycerin was separated from the test substance using a separating funnel. The

mixture of β-aminodielethyoxy-β-carboxamide of carboxylic acids was

conventionally named (IngXO-DB) - a light yellow oily liquid with a pungent odor:

refractive index -1.469; boiling point - 290 °C; density - 0.9139 g/cm

3

.

A chlorine-containing waste generated in the vinyl chloride production at a

rate of 4500 t/year and not finding proper application was used as a raw material

source. Analysis of the composition of the chlorine-containing waste shows that

the product consists of a mixture of 32 products, mainly 1,1-dichloroethane, vinyl

chloride, acetaldehyde, and dichloroethylene.

Fig.1. Chromium-mass initial chlorine-containing waste

1 (0.091) benzene; 2 (0.943) Chlorethylene; 3 (1.014) chloroprene; 4 (1.137)

3-chloropropene; 5 (1.257) 1,1-dichloroethane; 6 (1.325) chloroprene; 7 (1.423)

2,2-dichloropropane; 8 (1.625) 1,2-dichloroethylene; 9 (1.760) 3-chloro-2-
methylpropene; 10 (1.948) 1,3-chlorocyclopentene; 11 (2.074) heptane; 12

(2.191) 5.5-dimethylhexane; 13 (2.345) methylcyclohexane; 14 (2.499)

ethylcyclohexane; 15 (3.036) 2-chloro-1,3-butadiene; 16 (3.179) 1,1,2-

trichloroethane; 17 (3.291) 1,3-dichlor-2-butene; 18 (4.105) 3-chloro-2-

chloropentane; 19 (4.199) 1,3-dichlorobutane; 20 (4.722) 3-chloro-2-methyl-1-

propene; 21 (4.845) 1-chloro-2-methylcyclopropane; 22 (5.105) chlorobenzene;

23 (5.262) non-identified substance; 24 (5.402) 3-methyl-1-chlorobutane; 25

(5.542) ethylbenzene; 26 (5.807) 3,5,6-trichloro-2-pyridinium acetone; 27

1.00

2.00

3.00

4.00

5.00

6.00

7.00

8.00

9.00

10.00 11.00 12.00 13.00

2e+07

4e+07

6e+07

8e+07

1e+08

1.2e+08

1.4e+08

1.6e+08

Time-->

Abundance

TIC: v-26052021-isxod1DA.D\ data.cdf

0.091

0.943

1.014

1.137

1.257

1.325

1.423

1.625

1.760

1.948

2.074

2.191

2.345

2.499

3.036

3.179

3.291 4.105

4.199

4.722

4.845

5.105

5.262

5.402

5.542

5.807 6.878 7.867

8.481

9.184

11.780

12.180


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(6.878) benzaldehydehydrazone; 28 (7.867) dihydrotoluene; 29 (8.481)
2,2,4,6,6-pentamethylheptene; 30 (9.184) 2 (1H) -pyridinone; 31 (11.780) 1,3-

bromochlorocyclobutane; 32 (12.180) 1,3-dichlor-2-butane.

Table 2-7 presents data on the corrosion rate of St.3 steel and the protective

effect of the "INHO-BD" inhibitor Z depending on the H

2

S concentration in a

solution with 50 g/l NaCl, obtained as a result of 24 and 240 hours of testing. The

protective effect Z increases with increasing H

2

S concentration in the solution and

already at an inhibitor content of 100 mg/l, a corrosion rate close to 0.04 g/

(m

2

/h) is achieved (Table 1), which corresponds to a value of about 0.05

mm/year, which is proposed as a standard for characterizing the sufficient

effectiveness of the inhibitor.

Table 2

The influence of H

2

S concentration in the solution on the corrosion rate of

steel St.3 and the protective effect of the "INHO-BD" inhibitor, according to 24-

hour tests.

C

H2S

mg/l

50 mg/l

100 mg/l

Single mg/l

К, g/m

2

h

Z, %

К, g/m

2

h

Z, %

0

0,18

-

0,40

-

10

0,07

59

0,07

83

20

0,06

67

0,06

86

30

0,04

76

0,04

90

40

0,03

85

0,02

94

The investigated inhibitor is sufficiently effective at excess CO2 pressure equal to

1 and 2 atm. (Table 2). In the presence of H2S (100 mg/l) and CO2 (1 excess
atmosphere), the inhibitor at a concentration of 200 mg/l shows somewhat higher

effectiveness compared to pure carbon dioxide media (3-table).

Table 3

The corrosion rate of steel and the protective effect of the "INHO-BD" inhibitor at

an excess CO

2

pressure equal to 1 atm (numerator) and 2 atm (denominator)

(Experiment duration 24 hours)

Сinh. mg/l

0

10

20

30

40

К, g/m

2

h

200

,

0

181

,

0

091

,

0

075

,

0

076

,

0

068

,

0

050

,

0

046

,

0

041

,

0

036

,

0

E, %

-

73

77

80

81

92

92

97

97

Table 4

Dependence of the corrosion rate of steel and the protective effect of the "INHO-

BD" inhibitor on its concentration in solution in the presence of H

2

S (100 mg/l)

and CO

2

(1 sample) simultaneously, according to 24-hour tests.

Сinh. mg/l

0

10

20

30

40

К, g/m

2

h

0,291

0,106

0,084

0,050

0,031


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E, %

0

63

71

83

89

Below are the results of 10-day corrosion tests.

Table 5

The influence of H

2

S concentration in the solution on the corrosion rate of steel

St.3 and the protective effect of the "INHO-BD" inhibitor, according to 240-hour

tests.

C

H2S

mg/l

50

100

Сinh. mg/l

К, g/m

2

h

Z, %

К, g/m

2

h

Z, %

0

0.040

-

0,100

-

25

0,028

30

0,034

66

50

0,013

68

0,017

83

100

0,012

69

0,013

87

200

0,009

77

0,001

90

Table 6

The corrosion rate of steel and the protective effect of the "INHO-BD" inhibitor

at an excess CO

2

pressure equal to 1 atm (numerator) and 2 atm (denominator)

according to 240-hour tests.

Сinh. mg/l

0

10

20

30

40

К, g/m

2

h

071

,

0

067

,

0

046

,

0

041

,

0

041

,

0

036

,

0

035

,

0

030

,

0

027

,

0

024

,

0

E, %

-

53

57

61

66

70

77

84

88

Table 7

Dependence of the corrosion rate of steel and the protective effect of the "INHO-

BD" inhibitor on its concentration in solution in the presence of H2S (100 mg/l)

and CO

2

(1 sample atm) simultaneously, according to 240-hour tests.

Сinh. mg/l

0

10

20

30

40

К, g/m

2

h

0,079

0,037

0,030

0,026

0,004

E, %

-

62

72

77

97

Comparison of the results of daily and ten-day corrosion tests shows that the

corrosion rate of steel decreases over time in both inhibited and uninhibited

solutions, and the increase in H

2

S concentration contributes to an increase in the

protective effect of the inhibitor during both test durations.

The combined presence of H

2

S and CO

2

causes an increase in inhibitor Z

compared to pure carbon dioxide environments. The values of the inhibitor's

protective effect, according to ten-day tests, were noticeably and reliably lower

compared to the daily exposure of the samples.

The corrosion rate of steel is higher in solutions containing both hydrogen

sulfide and carbon dioxide than in solutions containing hydrogen sulfide of the

same concentration. Obviously, this is due to the acidification of the medium in

the presence of CO

2

.

Thus, the inhibitor "INHO-BD" allows achieving a corrosion rate of 0.04 g/


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(m

2

h) in a highly mineralized (50 g/l NaCl) hydrogen sulfide-containing medium

during daily testing, only at a concentration of at least 20 mg/l. However, with an

increase in the duration of the tests by an order of magnitude, a similar corrosion

rate is observed already at an inhibitor concentration of 25 mg/l. This is also

characteristic of carbon dioxide and hydrogen sulfide-carbon dioxide solutions.

Thus, the "INHO-BD" inhibitor in the composition with Zn-OEDF allows

achieving a corrosion rate of about 2 g/ (m

2

h) in a highly mineralized hydrogen

sulfide-containing medium during daily tests, only at a concentration of at least 6
mg/l. However, with an increase in the duration of the tests by an order of
magnitude, a similar corrosion rate is observed already at an inhibitor
concentration of 10 mg/l. This is also characteristic of carbon dioxide and
hydrogen sulfide-carbon dioxide solutions.

Фойдаланилган адабиётлар рўйхати:

1.

Турабджанов С.М., Кадиров Б.М., Эргашева С.Х., Кадиров Х.И., Рахимова

Л.С. Изучение синергетической эффективности аминокротонола и
органофосфонатов при ингибировании коррозии. Химическая технология.
М.: 2021. №1. 2-8 б. (20)
2.

Huang Wusheng // Mizi Shori Gijutsu. 2005. V. 46. № 10. P. 473-476. C.A.

2005. V. 143. 446068.
3.

Antisedimentary and anticorrosive stabilization of water with phosphonic

and polycaproamide inhibitors / Kubicki J., Falewicz P., Kuczkowska S. // 8th
European Symposium on corrosion Inhibitors. 1995. V. 1. P. 521-532. C.A. 1996.
V. 124. 97060.
4.

Lei Ling, Yang Wen-zhong, Yu Bin // Shandong Huagong. 2007. V. 36. № 4.

P. 17-20. C.A. 2008. V. 148. 127238.
5.

Corrosion Inhibition of a Green Scale Inhibitor Polyepoxysuccinic Acid /

Rong Chun Xiong, Qing Zhou, Gang Wei // Chinese Chemical letters. 2003. Vol. 14,
No. 9, pp 955-957.
6.

Pat. CN 1781858A КНР. Low-phosphine composite inhibitor for carbon

steel material in water / Wang Fengyun, Lei Wu, Xia Mingzhu. Опубл. 07.06.2006,
C.A. 2006. V. 145. 362799.
7.

Чиркунов А. А. Ингибирование коррозии стали в нейтральных водных

средах водорастворимыми полимерами и композициями на их основе:
автореф. дис. ... кан. хим. наук. М., 2007. 27 с.
8.

Zheng Yancheng, Li Kehua et al. // Gongye Shuichuli. 2003. V. 23. № 8. P.

19-22. C.A. 2004. V. 141.427321.


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ACADEMIC RESEARCH IN MODERN SCIENCE

International scientific-online conference

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9.

Набутовский З.А., Антонов В.Г., Филиппов А.Г. Проблемы коррозии и

ингибиторной защиты на месторождениях природного газа. Практика
противокоррозионной защиты. 2000. - №3 (17). -С.53-59.

Библиографические ссылки

Турабджанов С.М., Кадиров Б.М., Эргашева С.Х., Кадиров Х.И., Рахимова Л.С. Изучение синергетической эффективности аминокротонола и органофосфонатов при ингибировании коррозии. Химическая технология. М.: 2021. №1. 2-8 б. (20)

Huang Wusheng // Mizi Shori Gijutsu. 2005. V. 46. № 10. P. 473-476. C.A. 2005. V. 143. 446068.

Antisedimentary and anticorrosive stabilization of water with phosphonic and polycaproamide inhibitors / Kubicki J., Falewicz P., Kuczkowska S. // 8th European Symposium on corrosion Inhibitors. 1995. V. 1. P. 521-532. C.A. 1996. V. 124. 97060.

Lei Ling, Yang Wen-zhong, Yu Bin // Shandong Huagong. 2007. V. 36. № 4. P. 17-20. C.A. 2008. V. 148. 127238.

Corrosion Inhibition of a Green Scale Inhibitor Polyepoxysuccinic Acid / Rong Chun Xiong, Qing Zhou, Gang Wei // Chinese Chemical letters. 2003. Vol. 14, No. 9, pp 955-957.

Pat. CN 1781858A КНР. Low-phosphine composite inhibitor for carbon steel material in water / Wang Fengyun, Lei Wu, Xia Mingzhu. Опубл. 07.06.2006, C.A. 2006. V. 145. 362799.

Чиркунов А. А. Ингибирование коррозии стали в нейтральных водных средах водорастворимыми полимерами и композициями на их основе: автореф. дис. ... кан. хим. наук. М., 2007. 27 с.

Zheng Yancheng, Li Kehua et al. // Gongye Shuichuli. 2003. V. 23. № 8. P. 19-22. C.A. 2004. V. 141.427321.

Набутовский З.А., Антонов В.Г., Филиппов А.Г. Проблемы коррозии и ингибиторной защиты на месторождениях природного газа. Практика противокоррозионной защиты. 2000. - №3 (17). -С.53-59.