EURO-ECO 2006

Hanover

1 - 2 December 2006

Environmental and Engineering Aspects for sustainable living

European Academy of Natural Sciences, Hanover

European Scientific Society, Hanover

Russian Academy of Natural Sciences, Moscow

Sverguzova
S.V. Sverguzova

T.A. Vasilenko
S.V. Sverguzova
Ch. A. Sverguzova
SORBENTS OF CARBON-CONTAINING WASTER IN SEWAGE WATER PURIFICATION FROM HEAVY METALS
Belgorod State Technological University named after V.G. Shukhov, Belgorod, Russia

Summary: the opportunity of obtaining carbon sorbents from vegetative raw materias, such as pine raspings and shells of walnuts is under investigation. It is shown that active coals obtained have high adsorptive activity and can find application in technology of waste water clearing from nickel ions.

The studies of porous timber structure and structure of walnut shells, their sorbate capacity and possibility of deriving fissile coals from vegetative raw materials are carried out. Heat treatment of the granulated raw was carried out under laboratory conditions in the hermetic container manufactured of steel at 400, 450 and 500 ºC with the purpose of clearing raw materials from volatile substances, moisture and partially gum. Besides walnut shells worked up at 600 and 700 ºC.

The time of treatment of given patterns at given temperatures amounted to 15, 25 and 35 min. The speed of raw materials heating at carbonization should be low, otherwise the exit of coal and acetic acid decreases and the exit of gum increases. The problem of obtaining lace microporous structure is solved in the process of activation. For this purpose before feeding raw materials in the container it was treated by chloride of zinc with coefficient of impregnation equal to 1:2. The chloride of zinc transfers cellulose in the solution, which emits at the temperature rise the highly dispersive amorphous carbon forming a microporous structure. The fissile coal obtained by the method of chemical activation, varies by the large uniformity of the texture as a whole from the pattern of coal of steam-gaseous activation. Besides, the identity of structure at chemical activation is saved in pellets: their peripheral and internal leases are one-type. The agent of steam-gaseous activation was steam. The criterium of carbon materials quality is the sorbate tankage (mg/g of ions Ni2+, absorbed 1 g of sorbent). Concentration of nickel was determined by the photometric method on the spectrophotometer.

Estimating quality of fissile coals it is necessary to consider complicity of their physicochemical properties. In operation some differentiating tests were applied which described the physicochemical properties of the initial raw materials and obtained carbon sorbents. At the process of activation measurings of weight of the booted and obtained products (MI and MA, g), volume of the booted and obtained products (VI and VA, cm3) were conducted. The criteria of quality estimation of fissile coals were the following parameters: methylene number, IM, %; bulk and true density (ρN and ρT, g/cm3), volume of sorbate pores (by exixated method) on benzol (WS, cm3/g), exit of fissile coal on mass RM, %; exit of fissile coal on volume RV, %; an extent of hardening of the material obtained, w, %; a ratio of the exit on weight to the exit on volume RM/Rv; a volumetric index of porosity Ws• ρN, cm3/cm3; specific surface, S, m2/g. The properties of fissile coals obtained from raspings are represented in tab. 1, in tab. 2 – from walnut shells.


Table 1. The physical properties of fissile coals from pine raspings

T of pyrolysis, ºC

Time of pyrolysis, t, min

ρN, g/cm³

ρT, g/cm³

RM, %

RV, %

RM /RV

IM, %

WS, cm³/g

w, %

Ws•ρN, cm³/cm³

S, m²/g

400

15

0,273

1,95

96,6

64

1,51

15

0,063

0,09

0,017

428

25

0,218

1,91

74,9

60

1,25

17

0,062

25,1

0,013

595

35

0,196

1,79

65,9

58

1,14

20

0,059

34,1

0,012

689

450

15

0,266

1,90

91,6

60

1,53

20

0,078

8,3

0,021

798

25

0,209

1,75

69,9

57

1,23

30

0,079

31,1

0,017

1126

35

0,202

1,56

64,8

56

1,16

22

0,063

35,2

0,013

960

500

15

0,246

1,80

79,2

56

1,41

10

0,072

21,0

0,018

780

25

0,194

1,36

59,7

54

1,11

15

0,042

40,3

0,008

852

35

0,192

1,35

57,3

52

1,10

5

0,045

42,7

0,009

838


Table 2. Physical properties of fissile coals from walnut shells

T of pyrolysis, ºC

Time of pyrolysis, t, min

ρN, g/cm³

ρT, g/cm³

RM, %

RV, %

RM /RV

IM, %

WS, cm³/g

w, %

Ws•ρN, cm³/cm³

S, m²/g

400

15

0,369

2,11

69,1

68

1,02

10

0,011

30,9

0,004

404

25

0,336

1,98

60,9

65

0,94

10

0,014

39,3

0,004

425

35

0,321

1,95

49,1

60

0,82

15

0,020

46,7

0,006

445

450

15

0,340

2,04

67,4

64

1,05

10

0,027

32,6

0,009

470

25

0,326

1,95

58,4

62

0,94

15

0,031

41,6

0,010

496

35

0,310

1,90

51,6

60

0,86

15

0,039

48,4

0,012

520

500

15

0,302

1,97

49,8

55

0,91

20

0,027

50,2

0,008

535

25

0,305

1,87

46,7

55

0,85

20

0,033

53,3

0,010

571

35

0,289

1,81

42,9

54

0,79

25

0,041

57,1

0,012

590

600

15

0,298

1,81

41,65

53,7

0,78

25

0,059

51,5

0,017

600

25

0,295

1,70

41,44

53,3

0,77

25

0,073

55

0,022

630

35

0,279

1,79

40,23

53,23

0,76

35

0,089

59,08

0,025

650

700

15

0,290

1,75

39,9

53,5

0,75

35

0,068

53

0,019

667

25

0,285

1,73

39,3

53

0,74

35

0,084

57

0,024

685

35

0,272

1,71

39,26

52,91

0,74

40

0,098

60,74

0,027

700


As it can be observed from Tab. 1 and 2 the exit of fissile coal on weight and volume decreases with the increase of time and temperature of pyrolysis, and the extent of hardening increases.

The loss of weight is bound up with the process of pore formation and the process of level-by-level combustion of the material. By the results of experiments the sorbent capacitance on an ions of nickel is established, which lays within the limits 80,1–97,7 mg/g (pine raspings) and 91,0–97,5 mg/g (walnut shells). The optimum regime of the process of pyrolysis of pine raspings is bound with the temperature 450 ºC at the time of carbonization 25 min, walnut shells – 700 ºC at the time of carbonization 30 min; at the same time the increase of specific surface, volume of sorbate pores and sorbate capacitance is marked.

Conclusions

  1. The fissile coals from vegetative raw materials, such as pine raspings and walnut shells at the temperatures of pyrolyses 400–700 ºC are obtained.
  2. Carried out analysis of physicochemical properties of sorbents after activation.
  3. The estimation of sorbate activity of several patterns of fissile coal in a ratio of sorption of ions of nickel from the model solution was carried out. The value amounts to 80,1–97,7 mg/g (pine raspings) and 91,0–99,5 mg/g (walnut shells).
  4. The optimal conditions for obtaining fissile coals from pine raspings are calculated: temperature equal to 450 ºC, the time of carbonization equal to 25 min; pine raspings – temperature 700 ºC, the time of carbonization equal to 30 min.