adsorption of dyes from aqueous solutions by domestic wastes
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Transcript adsorption of dyes from aqueous solutions by domestic wastes
NATIONAL WORKSHOP ON “NEW TRENDS IN
BIOTECHNOLOGY: THEORY AND APPLICATIONS
ADSORPTION OF BASIC DYES ONTO LOWCOST ADSORBENTS: ANALYSIS OF THE
EQUILIBRIUM STATE
Dr. Abel E. Navarro
Science Department, Borough of Manhattan Community College, CUNY
Color:
-
Against the natural
conception of pure water. It
hides other types of
pollution.
Prevents the penetration of
sunlight into deep layers of
water – Photosynthesis.
The biological risks have
not been totally discarded
(carcinogenic and toxic
effects).
-
Use of biological techniques to
remove pollutants from air,
soil and water.
Bioaccumulation: Living
organism
Biosorption: Dead biomass
Use of non-living biomasses to
passively remove pollutants
Driven
by physico-chemical
processes
Algae,
crustacean
shells,
eggshell, nutshell, fruit peels,
fruit seeds, TEALEAVES.
Fast kinetics (saturation time).
Potential recyclability of waste
Complex structure, mainly
formed by polysaccharides
have many ways for
pollutants to be taken up:
- Metabolism dependent.
- Non-metabolism
dependent.
Competitive performance.
Pollutant selectivity.
Cost effectiveness.
Pollutant recovery.
No sludge generation.
Eco-friendly filtering
technique.
Alternative for using
man-made resins (x10
more expensive).
Potentially used for air
and water.
TARGET POLLUTANTS
Basic Blue 99: Naphthoquinoneimine,
cationic dye. Amino and hydroxyl
groups present.
O
NH
N
Cl
N
N
H3C
N
CH3
CH3
H3C
Basic Yellow (BY57)
Basic Blue 99 (BB99)
OUR ADSORBENTS
Why? High content of functional organic
groups such as alcohol (fiber and
carbohydrates), carboxylic acids and
amines (structural polysaccharides).
Widespread use of green tea as a hot/cold
drink. Massive collection from green tea
industries (i.e. Arizona and other bottled
tea-based drinks).
RESULTS
Characterization of the Adsorbents by TGA, SEM, FTIR,
SURFACE AND POROSITY
0
-2
Mass Loss (%)
-4
-6
-8
-10
-12
-14
GT
-16
-18
0
100
200
300
400
500
600
0
Temperature ( C)
FTIR ANALYSIS
cm-1
O-H STRETCH
3436
Surface Area (m2/g)
N-H BENDING
1636
Micropore Volume (cm3/g)
0.692
C=O STRETCH
1656
Total Pore Volume (cm3/g)
1.106
C-O STRETCH
1111
C=O STRETCH
1720
2,735.00
pH Effect
Higher pH promotes higher
adsorption.
100
95
90
90
80
85
70
% ADSORPTION
-
Ionization of adsorbent’s surface and
dye
% ADSORPTION
-
Mass Effect
Minimize amount of adsorbent.
Higher adsorption promotes
formation of aggregates.
60
50
40
30
80
75
70
65
20
BY57
BB99
10
BY57
BB99
60
0
55
2
3
4
5
pH
6
7
8
0
20
40
60
80
100
120
140
Adsorbent Mass (mg)
160
180
200
RESULTS
Isotherms were modeled by Langmuir and
Freundlich theories.
0.20
BY57
BB99
0.18
Adsorption Capacity (g/g)
0.16
Langmuir
qmax (g/g)
0.06
0.27
0.12
b (L/g)
63.29
25.82
0.10
R2
0.979
0.988
kF (L/g)
0.23
1.27
n
1.829
1.448
R2
0.984
0.978
0.14
0.08
0.06
Freundlich
0.04
0.02
0.00
0.02
0.04
0.06
0.08
0.10
Dye Concentration at Equilibrium (g/L)
0.12
Salinity Effect:
-
Higher the charge, the
stronger the effect.
95
NaCl
NaNO3
Ca(NO3)2
80
70
60
50
40
30
NaCl
NaNO3
Ca(NO3)2
90
% BB99 ADSORPTION
90
% BY57 ADSORPTION
Decreases adsorption due
to competition for the
adsorption sites.
85
80
75
70
65
60
55
20
50
0.0
0.1
0.2
0.3
Salt Concentration (mol/L)
BY57
0.4
0.5
0.0
0.1
0.2
0.3
Salt Concentration (mol/L)
BB99
0.4
0.5
Presence of Heavy Metals
Large and positively charge
ions.
- Present in residual waters.
-
80
Cu(II)
Pb(II)
% BB99 ADSORPTION
% BY57 ADSORPTION
100
Cu(II)
Pb(II)
60
40
20
0
0
10
20
30
40
Heavy Metal Concentration (mg/L)
BY57
50
80
60
40
20
0
0
10
20
30
40
Heavy Metal Concentration (mg/L)
BB99
50
Green Tealeaves have proven
to be promising adsorbents
for model dyes BY57 and
BB99.
TGA, FTIR, surface/porosity
and SEM studies report
advantages of GT as an
alternative adsorbent.
Langmuir and Freundlich
isotherms modeled the
adsorption indicating a qmax
of 0.06 and 0.27g/g for BY57
and BB99, respectively.
Salinity and heavy metals
have a negative effect on the
adsorption of both dyes, due
to competition for adsorption
sites.
Group Members:
Acknowledgements
Michelle Naidoo
Habib Zahir
Rada Kostadinova
Natalia Fernandez
Alvaro Sponza
San Shairzai
Funding:
Grant 001-2012-L’Oreal-CONCYTEC
2013-BMCC Faculty Development
Grant
CSTEP, PRISM and LSAMP programs