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Выпуск № 5(66), сентябрь - октябрь 2009 — "Technologies for production of chladons by a method of gas phase catalytic hydrofluorination"

Fluorine Notes, 2009, 66, 1-2

 

TECHNOLOGIES FOR PRODUCTION OF CHLADONS BY A METHOD OF GAS PHASE CATALYTIC HYDROFLUORINATION


I.G.Trukshin, V.G.Barabanov, G.G.Shelopin

Federal State Unitary Enterprise "Russian Scientific Center "Applied chemistry"
St. Peterburg, Russia

Chlorofluorocarbons and bromofluorocarbons (chladons and halons) as compounds possessing a number of unique properties such as chemical inertness, non-toxicity, explosion and fire safety, were widely used in engineering as aerosol propellants, refrigerants, foaming agents for plastics, solvents, high-performance extinguishers etc.

But the ozone depleting property of some chlorine- and bromine-containing compounds revealed in the 80-ties attracted attention to a large group of industrial chladones as potentially dangerous substances containing chlorine and bromine in their composition. The Montreal Protocol (MP) on substances that deplete the ozone layer was adopted in 1987y. As by this moment the depleting role of chlorine and bromine had been confirmed by a number of research teams, the Addendum to the MP listed ozone depleting substances (ODS) subject to regulation by all countries being the parties to the MP. This Addendum contained chlorofluorocarbons (CFC), bromofluorocarbons (halons) and some chlorohydrocarbons (CHC). The MP obliged the Parties to reduce consumption, production and import/export of ODS.

The Soviet Union was one of the first-rate manufacturers of ODS: in 1987y its share in ODS production made 15% of the world volume (approximately 200 thousand tons). At the same time the Soviet Union was one of the largest consumers and outstanding exporter of ODS that supplied not only all republics of the former USSR but also a whole number of European and Asian countries. Six large chemical plants in Russian Federation produced ODS. Almost all industry branches in RF were consumers of chladones [1,2].

FSUE RSC "Applied Chemistry" together with a number of research institutes of RF have made a great effort to convert domestic industry to a new class of chemical substances instead of the prohibited ODS.

As a result of their investigations a nomenclature of new chladones was suggested: hydrofluorocarbons 134a (CF2CFH2), 152a (CF2HCH3), 125 (CF3CF2H), 32 (CH2F2) etc. The main difference of ozone-friendly compounds from ODS is that their molecules does not contain chlorine and bromine atoms that may participate in "bromine" or "chlorine" cycle of the ozone depletion. Besides the zero value of ozone depleting potential (ODP) and the value of global warming potential (GWP), the main criteria in the choice of ODS alternatives is proximity of physical, chemical and maintenance properties to the analogues characteristics of ODS to be replaced.

The main nomenclature of ozone friendly compounds adopted for development and implementation into the industrial manufacture in Russian Federation is given in Table 1.


Table 1. Nomenclature of hydrofluorocarbons accepted for development and implementation into the industry of Russian Federation and their main properties [3]
 

Index

Unit

HFC 23

HFC 32

HFC 125

HFC 134

HFC 134a

HFC 143a

Formula

 

CHF3

CH2F2

C2F5H

CHF2CHF2

CH2FCF3

CF3CH3

Molecular weight

 

70.1

52.024

120.022

102.03

102.03

84.041

Boiling temperature
at pressure of 0,1 MPa

oC

-82.2

-51.7

-48.5

-22.5

-26.5

-47.6

Freezing temperature

oC

-155.15

-136

-103

-89.0

-101

-111.3

Critical temperature

oC

25.85

78.4

67.7

110.25

101.5

73.1

Critical pressure MPa

MPa

4.82

5.843

3.39

3.77

4.06

4.11

Concentration limits of flame propagation in air

% vol.

-

14.2-30.0

-

-

-

9.2-18.4

Self-ignition temperature

oC

765

504

--

630

--

720

Ozone depleting potential (ODP)

Relatively CFC11

0

0

0

0

0

0

Global warming potential (GWP)

Relatively CO2

14800

880

3800

1200

1600

5400

Toxicity:
Permissible limit of exposure (DuPont)
ppm
(vol./vol.)

ppm
(vol./vol.)

1000

1000

--

1000

--

--

MPCw.a.

mg/m3

3000

3000

1000

--

3000

3000

Danger class

 

4

4

4

--

4

4

 

Table 1. Continuation

Index

Unit

HFC 152a

HFC 227ea

HFC 236fa

HFC C336

HFC C438

HFC 43-10mee

Formula

 

CH3CHF2

CF3CFHCF3

CF3CH2CF3

C4F6H2-cyclo

C5F8H2-cyclo

CF3CHFCHFCF2CF3

Molecular weight

 

66.05

170.03

152.039

164

214

252.053

Boiling temperature
at pressure of 0,1 MPa

oC

-24.55

-18.3

-0.7 (-1.4)

63

79

47.0

Freezing temperature

oC

-117.0

-131.2

-93.6

--

--

-80

Critical temperature

oC

113.5

103.5

130.7

--

--

--

Critical pressure MPa

MPa

4.491

2.95

3.18

--

--

--

Concentration limits of flame propagation in air

% vol.

3.9-16.9

-

-

--

--

--

Self-ignition temperature

oC

453

>650

--

--

--

--

Ozone depleting potential (ODP)

Relatively CFC11

0

0

0

--

--

0

Global warming potential (GWP)

Relatively CO2

190

3800

9400

--

--

1700

Toxicity:
Permissible limit of exposure (DuPont)
ppm
(vol./vol.)

ppm
(vol./vol.)

1000

--

--

--

--

--

MPCw.a.

mg/m3

3000

--

--

--

--

--




In the development of technologies for ozone friendly hydrofluorocarbons at the plants in RF were used two production methods depending on their structure and taken into account existing production facilities of replaced CFC 11, 12, 113:
- liquid phase fluorination with anhydrous hydrogen fluoride of organochlorine compounds (HFCs 152a, 32, 143a etc.);
- gas phase catalytic fluorination of organochlorine compounds with anhydrous hydrogen fluoride

But the liquid phase hydrofluorination method has a number of limitations:
- replacement of the chlorine atom by fluorine in -CH2Cl and =CHCl groups proceeds with a great difficulty;
- catalyst SbClnF5-n in the hydrofluorination may act as a chlorinating agent with formation of ozone depleting chlorofluoroalkanes.

Taken that into account to obtain hydrofluorocarbons with a great fluorine content in the molecule (CF3-CFH2, CF3-CF2H) the gas phase catalytic method of hydrofluorination is used.

The peculiarities of gas phase catalytic hydrofluorination are seen on the example of 1,1,1,2-tetrafluoroethane ( HFC-134a) synthesis from trichloroethylene and hydrogen fluoride. The synthesis process runs in two stages (Scheme 1):



Scheme 1

It follows from the experimental data and thermodynamic calculation of stage (1) of the process that HFC133a content in the organic share of the synthesis products may reach 90-98%.

Stage (2) is reversible. In dependence on the conditions the contentof HFC 134a in the organic share of the synthesis products may make 10-40% by volume (from organic part of the synthesis products). For the process there is used a chromine-magenesium-fluoride catalyst [3, 16] manufactured from magnesium fluoride powder by saturation with chromium chloride solution followed by mixing, moulding, drying and treatment with hydrogen fluoride with the purpose to convert chromium chloride (CrCl3) into chromium fluoride (CrF3) [4, 5].

The study of the mechanism of the catalyst effect in the present process has shown that the catalyst acts as a carrier of fluorine and chlorine atoms [6-8]. It is suggested that the process of hydrofluorination of chlorofluoroethanes runs according to scheme (2):



Scheme 2

where chromium fluoride substitutes chlorine by fluorine in chlorofluoroethanes changing its composition to CrF2Cl,after that hydrogen fluoride replaces chlorine with fluorine in active catalyst part to form hydrogen chloride and CrF3. This mechanism seems more probable than mechanism [9, 10] that contains the stage of interaction of HF and chloroalkane molecules absorbed on neighboring active centers of the catalyst.

Besides the main hydrofluorination processes this catalyst is used for the reactions of dehydrofluorination, dehydrochlorination and disproportionation (Scheme 3)


Scheme 3

The obtaining unsaturated fluorine-containing compounds( particularly CF2=CHCl that forms azeotrope with 1,1,1,2-tetrafluoroethane) in future make more difficult the desired product separation from the reaction mixture. Obviously the mechanism of these processes is connected with formation of active transition complexes on the catalyst surface.
As a whole, taken into account the said assumptions the process of hydrofluorination of trichloroethylene may be given as the following sequence of the stages (Scheme 4):


Scheme 4

On the basis of the suggested mechanism with the use of the method of routes for complex reactions 11 a kinetic model for the process of synthesis of 1,1,1,2-tetrafluoroethane has been developed [12].


where: c1 is concentration of CF3-CClH2,
c2 - HF, c3 - CF3-CFH2, c4 - CF3-CH3,
c5 - CF3-CCl2H, c6 - CF3-CFClH, c7 - CF3-CF2H,
c8 - CF2Cl-CClH2, c9 - C2HCl3, c10 - CF2=CClH,
c11 - HCl, c12 - CFCl2-CClH2, c13 - CFCl=CClH,

In the search of the kinetic model constants for numerical integration of the system of ordinary differential equations there was used LSODA method [12]. The found values of the kinetic constants are given in Table 2.

Table 2. Parameters of Arrhenius equation for the process of production of 1,1,1,2-tetrafluoroethane from trichloroethylene

ki

lnА

Eact.,

kJ/mole

ki

lnА

Eact.,

kJ/mole

ki

lnА

Eact.,

kJ/mole

k' 1

33.8

125.2

k' 14

12.2

41.9

k' 21

17

97

k' 3

38.7

146.1

k' 16

16.5

70

k-21

26.5

103

k' -4

58.7

207.7

k-16

19.5

85

kA

43

209.3

k' 5

46.7

162.4

k' 17

11.7

76.6

kB

29.5

188.4

k' 7

16

66.5

k-17

15.6

51.1

kC

8.5

20.9

k-7

23

126.0

k' 18

26.2

148.5

kD~0

   

k' 12

17

83.7

k' 20

33

74.6

kE~0

   

k' -13

23.7

83.7

k-20

30

115

     


The kinetic model adequately describes the course of processes (1) and (2) (Scheme 1) within the following range of parameters: temperature of 175-420oC; mole ratio of the reagents: HF:C2HCl3 =(3.4-13.6) : 1; HF: C2H2ClF3=(4-20):1.

The process analysis with the use of the kinetic model has shown that the optimal conditions for stages (1) and (2) (Scheme 1) substantially differ (exothermic and endothermic processes), stage (1) is to be carried out at a lower temperature in comparison with stage (2) etc.

Therefore the synthesis of HFC 134a is reasonable to carry out according to the two-reactor scheme. For the choice of the optimal scheme of the reactor unit there was used a mathematical model of adiabatic reactor with stationary bed of chromium-magnesium-fluoride catalyst:

Ci = concentration of component i in the gas mixture, mole/m3;
X = reactor length, m; T= temperature, K;
Ri = rate of changing component i concentration as a result of chemical reactions, mole/( m3 · s);
υi = number of i-th component moles participating reaction j;
rj = rate of reaction j, mole/( m3 · s);
ρ =density of the gas mixture depending on the concentration of components and temperature (ρ(C, T)), kg/m3;

u = linear velocity of the mixture, m/s;
Cp =average heat capacity of the mixture, J/ (kg*K);
ΔHj = heat effect of reaction j, J/mole;


Four variants of the reaction unit organization given in Fig.1 have been considered:

Fig.1. Variants of two-reactor scheme of 1,1,1,2-tetrafluoroethane synthesis

The calculations according to the above stated mathematical model have shown that the maximal output of HFC-134a provides variant A [13] ( see Table 3).

Table 3. Analysis of the reaction unit for synthesis of 1,1,1,2-tetrafluoroethane (TFE)

Reaction unit scheme A B C D
TFE output, kg/s* 0.0268 0.0237 0.0218 0.0238



*The calculation were performed at the following basic data:
HF consumption: 60.86 kg/h;
C2HCl3 consumption: 97,54 kg/h;
Recycle consumption: 1121.5kg/h;
For scheme A: recycle to the first reactor: 166.44 kg/h;
Recycle to the second reactor: 955.07 kg/h;
 

According to variant A the first reactor is fed with hydrogen fluoride, trichloroethylene and part of the recycling mixture( to hold the temperature regime) in which the total content of HF and 1,1,1-trifluorochloroethane is more than 99%, the second reactor is fed with main part of the recycling mixture ("recycle") of the same composition; the flows from the reaction zones are united and directed to separation of hydrogen chloride, low-boiling products and 1,1,1,2-tetrafluoroethane while the high-boiling substances are returned as a recycle to the synthesis unit.

The standard process flowsheet for synthesis of ozone friendly HFCs has been developed by the method of gas phase catalytic hydrofluorination ( pentafluoroethane, for example) [14]. The technology of production of HFC116 [15] was developed for processes of plasmachemical etching in microelectronics and the technology for HFC 23 [17] manufacture was developed for filling low-temperature refrigerating machines.

Industrial facilities for ozone friendly HFCs in Russian Federation have been created and are creating on the basis of the investigations carried-out.


References

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Fluorine Notes, 2009, 66, 1-2

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