Hydrogen sulfide adsorption from natural gas and its treatment

The research conducted in the field of adsorption-catalytic extraction of H2S from low sulfurous natural gases and conversion into elemental sulfur using the synthetic CaA zeolite and natural modified adsorber mordenite as well as the palladium catalyst.

Рубрика Химия
Вид статья
Язык английский
Дата добавления 11.07.2018
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HYDROGEN SULFIDE ADSORPTION FROM NATURAL GAS AND ITS TREATMENT

Ibrahimov Ch.Sh.,

Yusubov F.V.

Critical to a certain extent situation which develops around natural gas processing is primarily defined by sulfur compounds content in it that leads to catalyst poisoning and environment contamination with sulfur industrial wastes [1-3].

With continuous improvement of gas desulfurization processes there are still many issues that are to be resolved. The problem of creation and development of methods of practically absolute natural gas cleaning against any undesirable ingredients combined with high efficiency and cost effectiveness of the technological process providing an acceptable ecological setting dominates among such issues.

This paper describes the following problem-solving results.

For the first time, a mathematical model of hydrogen sulfide adsorption from low sulfurous natural gases and the process of conversion of H2S into elementalsulfur by catalytic oxidation in a plant of similar combination continuously and consistently was developed. Researches were conducted in the field of selection of effective adsorbents and catalysts for the considered process, and the results of the experiments analysis have shown that hydrogen sulfide adsorption from low sulfurous natural gases was more effective in CaA zeolite (activity 120 mg/g). At the same time it was determined that use of modified natural mordenite was more reasonable in terms of cost effectiveness (15 mg/g). Conversion of H2S into elementalsulfur by catalytic oxidation was performed using palladium catalysts.

A mathematical model of the processes of hydrogen sulfide adsorption from low sulfurous natural gases and catalytic oxidation was developed to provide an optimal design of these processes, the method of analytic solution was found to facilitate its practical application, and the method to confirm parameter identification was developed.

So, the method to confirm designing and management of the plant and continuous coordinated operation of the processes of hydrogen sulfide adsorption from low sulfurous natural gases and conversion of H2S into elementalsulfur by catalytic oxidation which provides the practical significance of this paper has been developed.

Experimental: The adsorption method of hydrogen sulfide removal is effective when natural gas contains less than 5% H2S. Synthetic zeolites of NaA, NaX, CaA, NaY, NaA, etc. are used for this purpose.However use of the adsorption method entails the problem of utilization of extracted H2S. It is known that application of the Claus' method to low sulfurous natural gases is not always effective. Grigoryeva N.A., Jagfarov F.G. Design of the sulfur recovery unit using the Claus' method. Moscow, 2006.

Taking into account the abovementioned, this paper proposes a technological scheme (Figure 1) of H2S extraction and utilization. Low sulfurous natural gas is fed to the adsorber A-1 or A-2 under 6 MPa where hydrogen sulfide is adsorbed on zeolite CaA after H2S saturation of which the adsorber is switched over the desorption mode. A part of raw gas preheated in the furnace P-1 up totemperature 250-300oC is used as the desorbing agent. Desorbed hydrogen sulfide together with desorbing gas is fed to the converter (reactor 1) through line V where the reaction of oxidation of H2S takes place and elemental sulfur is produced on the palladium catalyst synthesized for this purpose at temperature 270-290oC.

Since the temperature of the regeneration gas at outlet from the desorber is about temperature 300oC and the oxidation reaction is exothermic, no change in its temperature in the reactor is needed. This is one of the causes of cost effectiveness of use of this technological system.

The experimental design method was used for experimentation. As a result, a regression equation linking the degree of conversion of hydrogen sulfide (S) into elemental sulfur with the parameters of adsorption and reactor sections of the plant was obtained as follows:

S=5, 67 - 0, 32*t + 0, 415*T-4, 47*Cd + 0, 81*10-2*V + 0, 39*10-2*t*T - 0, 056*Cd - 0, 16*10-3*t*V - 0, 014*T* Cd - 0, 59*10-4*T*V + 0, 25*10-2*Cd*V

Here, S, % is the degree of conversion of hydrogen sulfide into elemental sulfur; t, hour is H2S desorption time; T, 0C is the temperature of reaction; Cd, % is the concentration of H2S in the strippant; V, hour-1 is the volume rate of the desorbing gas in the reactor. Some experimental materials are given in Figures 2-3 and Table 1. Isothermic diagrams and kinetic data of adsorption of H2S from the hydrocarbon blend on CaA zeolite are given in Figures 2 and 3.

Fig. 1. Technological scheme of hydrogen sulfide adsorption from low sulfurous natural gases and its conversion into elemental sulfur: A-1, A-2 - adsorbers; C-1 - separator; P-1 - furnace; 1 - converter with catalyst; 2 - coagulator; 3 - sulfur trap; 4 - cooler. Flows: I - raw gas; II - pure gas; III - fuel gas; IV - regenerating gas; V - desorption products; a) adsorption unit; b) reactor section

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Partial pressure H2S, mm Hg

Fig. 2. Isotherms of H2S adsorption on zeoilites of various grades: 1 - CaX; 2 - NaA; 3 - CaA; 4 - NaX

Fig. 3. Elution (a) and kinetic (b) curves of H2S adsorption from the hydrocarbon blend of the gas by synthetic CaA zeolite (initial concentration of H2S in gas C0=6.1*10-3 kg/m3)

Discussion of results: As is seen from Figure 2, the most active zeolite for H2S is NaX. However the use of thise zeolite would be inexpedient in terms of sieve effect as its pore size is about 10A0. In this case other components of the gas get into active centers of zeolite when passing the pores and reduce its activity against H2S. It is advisable, therefore, to use CaA zeolite with pore size not exceeding 5A0, I.e. corresponding to H2S molecule size.

As is seen from Figures 3, activity of the synthetic CaA zeolite against H2S is by a factor of ten higher that activity of modified natural mordenite. Mordenite is more attractive because it is lower in cost and there are rich resources of natural zeolites in the Azerbaijan Republic [4-7].

adsorber mordenite palladium catalyst

Table 1. Comparison of experimental and design data on the degree of conversion of hydrogen sulfide into the elemental sulfur

t, hour

T, oC

Cd, %

V, hour-1

S, % (ex)

S, %

Error

1

0.33

250

3.0

2000

88.38

(86.891design)

+1.68

2

1.00

250

6.3

2000

75.14

76.588

-1.93

3

1.667

250

4.35

2000

82.96

82.795

+0.20

4

0, 667

250

5.1

3000

85.54

86.140

-0, 70

5

1, 33

250

6, 15

3000

84.72

85.305

-0, 691

6

1, 33

250

6, 15

4000

93.69

93.555

+0, 14

7

0, 33

300

3, 75

2000

96.64

96.832

-0, 20

8

2, 00

300

3, 9

2000

95.98

96.765

-0, 82

9

1, 00

300

8, 4

4000

100

100.859

-0, 86

10

0, 33

350

6, 0

2000

97.17

98.921

-1, 97

11

2, 00

350

6, 75

3000

100

99.815

+0.19

12

1, 33

350

11.25

4000

100

104.986

-4.99

Table 1 provides the data as an examplewhich reflect the influence of H2S desorption time in the adsorption unit, temperature of reaction, H2S concentration in the strippant and volume velocity of the desorbing gas in the reactor on the degree of conversion of hydrogen sulfide into the elemental sulfur. The average error of experimental and design data on the degree of conversion of hydrogen sulfide into the elemental sulfur is +/1.18%.

The problem of optimization of the process of H2S adsorption from gas was solved using the data of conducted researches.

We obtain the following values of input parameters: quantity of crude gas - 26 t/hour; pressure in the adsorber - 40 atm; adsorbent - CaA zeolite the dynamic activity of which against H2S is 120 mg/g. Based on the practical researches, the following limits were accepted:

20oC ? T ? 80oC oC

0.1m / c ? v ? 0.7 m/c

0.001kg/m3 ? C0 ? 0.1 kg/m3

where Ta - temperature of adsorption; Tре - temperature of reaction; v - linear velocity of gas feeding to

adsorber; C0- initial concentration of H2S in the original (feed) gas.

Costs given for one cycle of periodical adsorption were selected as an optimality criterion. In the result the following optimal values of parameters were obtained: the period of adsorption is 24 h; the gas flow velocity is 0.36 m/sec; the temperature of adsorption is 22oC; the temperature of regeneration is 265oC; the adsorber diameter is 1.95 m; the quantity of adsorbent in one adsorber is 13202 kg; the adsorbent layer height is 6.3 m.

Conclusion

1. The technological scheme of H2S adsorption from low sulfurous natural gases and its conversion into elementalsulfur was developed.

2. The experimental design method was used to create a regression equation linking the degree of conversion of hydrogen sulfide into elemental sulfur with the parameters of adsorption and reactor sections of the plant.

3. Zeolites which provide the most effective results for the process considered in this paper were selected.

4. The following was obtained: a) experimental balanced, kinetic and output data of H2S adsorption; b) dependence of the degree of conversion of H2S into elemental sulfur on the time of its desorption in the adsorption unit, temperature of reaction, concentration of H2S in the strippant and volume velocity of the desorbing gas in the reactor.

References

1. Conference of United Nations Organization by climate problems, Paris (12.12.2015).

2. Ahnazarova S.L., Gafarov V.V.: Optimization experiment in Chemistry and Chemical Engineering, Graduate School, Moscow, 1978. С. 126-132.

3. Ibragimov Ch.Sh. To design and management methods of the adsorption process. Elm. Baku, 1999. С. 145147.

4. Keltsev N.V. Base of adsorbtivetechnige, Chemistry. Moscow, 1984. С. 138-141.

5. General course of processes and chemical engineering apparatuses: Textbook: in 2 volumes / V.G. Einstein, M.K. Zakharov, G.A. Nosov, etc. M: Logos; Higher school, Moscow, 2002. С. 1157-1175.

6. Qorbatenko Y.A. Adsorption of admixtures of toxical gas from polluted air. Yekaterinburg, 2014. 47 c.

7. Renato R., Phillip W. Эntensification of pressure swing adsorption processes. // Aiche Journal, 1990.36. № 9. Р. 1299-1312.

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