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Identification of Stability, Kinetics, and Thermodynamic Parameters in Biosorption of NickelII Ions

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Experimental and theoretical isotherms for biosorption of nickel(II) ions to ... Isotherm Model. 8/5/09. 8. 4. Findings and Discussion. Figure 4.6. ... – PowerPoint PPT presentation

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Title: Identification of Stability, Kinetics, and Thermodynamic Parameters in Biosorption of NickelII Ions


1
Identification of Stability, Kinetics, and
Thermodynamic Parameters in Biosorption of
Nickel(II) Ions to Enteromorpha prolifera
  • M. Görkem GÜRBÜZ
  • REPUBLIC OF TURKEY MINISTRY OF INDUSTRY AND TRADE
  • SMALL AND MEDIUM INDUSTRY DEVELOPMENT
    ORGANISATION (KOSGEB) / TURKEY

2
1. Purpose of the study
  • Based on the literature research on
    biosorption, as an alternative to the biosorbents
    in those studies conducted, this study aims the
    release of the nickel(II), which is found in
    industrial wastes in quite considerable amounts,
    into Enteromorpha prolifera on the Mediterranean
    coast.
  • Identification of the most appropriate ambient
    conditions
  • Identification of the most appropriate stability
    model
  • Identification of the most appropriate kinetics
    model
  • Identification of thermodynamic parameters
  • 2. Biosorption
  • Biosorption is the process of adsorption, in
    which thermally or chemically inactivated
    biomasses are used.
  • Fast and efficient removal of metal,
    Recyclable waste
  • Simple operating conditions,
    High capacity of operation
  • Removal in a short period of time,
    Mathematically identifiable system
  • Desorbable and recyclable metal,
    Economic

3
3. MATERIAL AND METHOD
  • A) Material
  • Micro organism
  • Enteromorpha prolifera of green algae,
    which was used in the studies, was collected on
    the Mediterranean coast in Davultepe Municipality
    in Mersin.
  • Chemical substances
  • The chemical substances used in the studies
    were the products of the companies Merck and
    Sigma. Chemicals used were
  • - HCl - Sodium diethyl
    ditiocarbomate - NiCl2
  • - NH3 - NaOH
  • B) Method
  • Preparation of micro organisms for
    biosorption studies
  • Algae collected from the wild were cleaned by
    supply water, and then by pure water one or more
    times, and dried at 100 C for 8 hours.
  • Preparation of heavy metal (Nickel(II)) stock
    solutions
  • Ni2 stock solution of 1 g/L used in the
    study was prepared by NiCl2 and pure water.
  • Nickel solutions were used in the studies after
    having had the required dilutions from stock

4
3. Material and Method (Continued)
C) Test System
5
4. Findings and Discussion
4.1 Identification of the most appropriate
ambient conditions for nickel(II) ion
pH 5
  • Figure 4.1. For biosorption of nickel(II) ions to
    Enteromorpha prolifera, the impact of initial pH
    on the nickel(II) ion amount biosorbed per
    stabilised unit biosorbent of nickel (II) ions
    (Conditions Co 100 mg/L pH 2,3,4,5 Xo 1
    g/L T30 oC KH100 rpm)
  • Figure 4.2. For biosorption of nickel(II) ions to
    Enteromorpha prolifera, the impact on the
    nickel(II) ion amount biosorbed per unit
    biosorbent at different initial temperatures
    (Conditions Co 100 mg/L pH 4 Xo 1 g/L
    KH100 rpm)

pH qd
T 30 oC qdmax Tgt 30 oC qd
6
4. Findings and Discussion
4.2 Identification of the most appropriate
ambient conditions for nickel(II) ion (continued)
  • Figure 4.4. For biosorption of nickel(II) ions to
    Enteromorpha prolifera, nickel(II) ion amount
    biosorbed at different mixing speeds (Conditions
    Co 100 mg/L pH 5 T30 C Xo 1 g/L)
  • Figure 4.3. For biosorption of nickel(II) ions to
    Enteromorpha prolifera, exchange of nickel(II)
    ion amount biosorbed per unit biosorbent with
    biosorbent concentration at different initial
    biosorbent concentrations (Conditions Co 100
    mg/L pH 5 T30 C KH100 rpm)

7
4. Findings and Discussion
4.3 Stabilisation modelling for nickel(II) ion
Freundlich Isotherm Model
  • Figure 4.5. Experimental and theoretical
    isotherms for biosorption of nickel(II) ions to
    Enteromorpha prolifera (Conditions pH 5 T30
    oC KH100 rpm)

8
4. Findings and Discussion
4.4 Kinetics studies of nickel(II) ion
dq ?
k2.ad (qden q)2
dt
  • Figure 4.6. For biosorption of nickel(II) ions to
    Enteromorpha prolifera, pseudo second degree
    kinetics model graphic obtained at different
    nickel(II) ion concentrations (Conditions pH 5
    Xo1 g/L T 30 C KH100 rpm)

9
7. Findings and Discussion
4.5. Calculation of activation energy for
nickel(II) ion
EA 5,83 kJ/mol
Inclination EA Breakpoint ko
  • Figure 7.7. For biosorption of nickel(II) ions to
    Enteromorpha prolifera, the activation energy
    graphic for the temperature range of 20 C - 30 C
    (Conditions pH 5 Co100 mg/L, Xo 1 g/L
    KH100 rpm)

10
7. Findings and Discussion
4.6. Calculation of thermodynamic parameters for
nickel(II) ion
?So ? ?Ho 1 (ln Kc)
????? ?? R
T
Inclination ?Ho Breakpoint ?So
?Go ?Ho (T?So)
  • Figure 4.8. For biosorption of nickel(II) ions to
    Enteromorpha prolifera, Vant Hoff graphic for
    the temperature range of 20 C - 30 C

11
5. CONCLUSIONS
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