1-s2.0-S1002072110604693-main
Transcript of 1-s2.0-S1002072110604693-main
-
7/29/2019 1-s2.0-S1002072110604693-main
1/6
JOURNAL OF RARE EARTHS, Vol. 29, No. 5, May 2011, P. 407
Foundation item: Project supported by the grants from the National Key Technologies Research and Development Program of China (2008BAD94B09), and the
Key Grant of Education Department of Zhejiang Province, China (Z200907459)
Corresponding author: XIONG Chunhua (E-mail: [email protected]; Tel.: +86-571-88932083)
DOI: 10.1016/S1002-0721(10)60469-3
Adsorption behavior of ytterbium (III) on gel-type weak acid resin
ZHENG Zhanwang (), XIONG Chunhua ()
(Department of Applied Chemistry, Zhejiang Gongshang University, Hangzhou 310012, China)
Received 11 January 2011; revised 22 February 2011
Abstract: The adsorption and desorption behaviors of Yb(III) on gel-type weak acid resin (110) were investigated. The influence of opera-
tional conditions such as contact time, initial concentration of Yb(III), initial pH of solution and temperature on the adsorption of Yb(III) were
also examined. The results showed that the optimal adsorption condition of 110 resin for Yb(III) was achieved at pH=5.5 in HAc-NaAc me-
dium. The maximum uptake capacity of Yb(III) was 265.8 mg/g at 298 K. Yb(III) could be eluted by using 3.0 mol/L HCl solution and the
110 resin could be regenerated and reused. The adsorption of Yb(III) followed the Langmuir isotherm, and the correlation coefficients were
evaluated. Various thermodynamic parameters such as standard enthalpy change (H), standard entropy change (S) and standard free energy
change (G) were evaluated. The adsorption of Yb(III) on the 110 resin was found to be endothermic in nature. Thomas model was success-fully applied to experimental data to predict the breakthrough curves and to determine the characteristics parameters of the column useful for
process design. And the resin sample both before and after adsorption was described by IR spectroscopy.
Keywords: gel-type weak acid resin (110 resin); ytterbium(III); adsorption; parameter; Thomas model; rare earths
Rare earth elements (REEs) have been regarded as the vi-
tamin of metals, which means that a minute amount of REEs
may greatly enhance the properties of metals. Ytterbium(Yb)
is one of the most significant rare earth elements, which has
attracted special attention due to its unique properties and
wide range of applications. Yb can be used in optical materi-als, dentistry as well as stainless steel to help improve the
properties of those materials; the 169Yb isotope has been used
as a radiation source substitute for a portable X-ray ma-
chine[14].
However, as industry expands, ytterbium which is also
one of the harmful elements persists in the environment and
often creates long-term contamination problems. Therefore,
extraction and preconcentration of these valuable ions from
wastes are extremely important not only from the view of
their limited resource availability, but also for the reduction
of their quantum for disposal as wastes. Different methods
have been proposed for separation and preconcentration of
REEs, such as co-precipitation, solvent extraction, ion-ex-
change and solid phase extraction[59]. Solvent extraction and
ion-exchange are the two most common methodologies for
the preconcentration and separation of trace elements from
various matrices[10]. Solvent extraction is inefficient due to
the requirement of large volume of solvent, which may cre-
ate health problem. In addition, solvent extraction proce-
dures are usually time-consuming and labor-intensive [1113].
Ion exchange resins have been used in the chemical analysis
for over 50 years[11]. They are solid and suitably insolubi-
lized high molecular weight polyelectrolytes which can ex-
change their mobile ions for ions of equal charge from the
surrounding medium. The resulting ion exchange is reversi-
ble and stoichiometric with the displacement of one ionic
species by another on the exchanger. 110 resin is a poly-
meric material containing a functional group (COOH). Ithas oxygen atom that can coordinate directly with metal
ions[14,15]. 110 resin which can be used repeatedly has the
advantages of high stability and adsorption capacity. The
high adsorption rate of 110 resin due to its unique properties
opens the door to the application in industry.
In this work, the adsorption and desorption of Yb(III) ion
on 110 resin using batch and column methods were investi-
gated. Some factors affecting adsorption, such as contact
time, initial pH of solution, initial concentration of Yb(III)
ion and temperature were examined. Furthermore, kinetics
and isotherm adsorption experiments were carried out. Tho-
mas model was applied to experimental data obtained from
column experiments. With the mentioned above, 110 resin
can be widely used in the recovery of Yb(III) from aqueous
solution.
1 Materials and methods
1.1 Apparatus
The Yb(III) ion was determined with Shimadzu UV-2550
UV-VIS spectrophotometer. Mettler toledo delta 320 pH
-
7/29/2019 1-s2.0-S1002072110604693-main
2/6
408 JOURNAL OF RARE EARTHS, Vol. 29, No. 5, May 2011
meter was used for measuring pH of solutions. The sample
was shaken in a DSHZ-300A and a THZ-C-1 temperature
constant shaking machine. The water used in the present
work was purified using a Molresearch analysis-type ultra-
pure water machine.
1.2 Materials
110 resin was supplied by The Chemical Plant of Nankai
University (Tianjin, China) and the properties are shown in
Table 1. The stock solutions of Yb(III) ion were prepared
from Yb2O3 (A.R.). HAc-NaAc buffer solution with pH=
3.506.50 and C6H15O3N-HNO3 buffer solutions with pH=
7.2 were prepared from the NaAc, HAc, C6H15O3N and
HNO3 solutions. The chromophoric reagent of 0.1% ar-
senazo-I solution was obtained by dissolving 0.1000 g ar-
senazo-I powder into 100 ml deionized water. All other
chemicals were of analytical grade and purified water was
used.
Table 1 General description and properties of 110 resin
Item Property
Resin Gel-type weak acid resin
Functional group COOH
Capacity/(mmol/ml) 12
Containing moisture/% 70.080.0
Wet superficial density/(g/ml) 0.700.80
True wet density/(g/ml) 1.101.15
1.3 Adsorption experiments
Experiments were run in a certain range of pH, tempera-
ture, initial Yb(III) ion concentrations, and contact time as
well as adsorption isotherms[16]
. The operation for the ad-
sorption and desorption of Yb(III) ion is usually carried out
in batch vessels and glass columns. Batch experiments were
performed under kinetic and equilibrium conditions. A de-
sired amount of treated 110 resin was weighed and added
into a conical flask, in which a desired volume of buffer so-
lution with pH 5.5 was added. After 24 h, a required amount
of standard solution of Yb(III) ion was put in. The flask was
shaken in a shaker at constant temperature. The upper layer
of clear solution was taken for analysis until adsorption equi-librium reached. The procedure of kinetic tests was identical
to that of the equilibrium tests. The concentrations of Yb(III)
ion of aqueous samples were measured at preset time inter-
vals. Continuous flow adsorption experiments were con-
ducted in a vertical glass column of 0.45 cm inner diameter
and 23.5 cm height filled with Yb(III) ion solution. At the
bottom of the column, a stainless sieve was attached fol-
lowed by a layer of cotton wool. The particles were dropped
in from the top of the column. Time taken by the particles to
travel a distance of 7.4 cm in vertical direction was noted.
The Yb(III) ion solution was fed from the top at a fixed flowrate. The Yb(III) ion solutions at the outlet of the column
were collected periodically and analyzed for the Yb(III) ion
concentration using a UV-visible spectrophotometer at 570 nm.
The flow through the column was continued till the outlet
and inlet concentrations were equal. All the experiments
were carried out at room temperature.
1.4 Analytical method
A solution containing lower than 75 g of Yb (III) was
added into a 25 ml colorimetric tube, and then 1.0 ml of
0.1% arsenazo-I solution and 10 ml pH 7.2 C6H15O3N-HNO3
buffer solution were added. After the addition of deionized
water to the mark of colorimetric tube, the absorbency was
determined in a 1 cm colorimetric vessel at wavelength of
570 nm and compared with blank test. The adsorption
amount (Q) and distribution coefficient (D) were calculated
with the following formulas[17,18]
:
Q=(C0Ce)V/m (1)
D=Q/Ce (2)
where C0 (mg/ml) and Ce (mg/ml) are the initial and equilib-
rium Yb(III) concentrations, respectively, V(ml) is the total
volume of solution, and m (g) is the mass of 110 resin.
2 Results and discussion
2.1 Influence of pH on the distribution coefficient for
Yb(III)
The pH of aqueous solution has been identified as the
most important variable governing the adsorption capacity of
adsorbent. The influence of pH on the adsorption behavior of
110 resin for Yb (III) is illustrated in Fig. 1.
The uptake of Yb(III) as a function of hydrogen ion con-centration was in the range of pH 3.506.50 for an initial
concentration of Yb(III) ion 5.0 mg/30.0 ml at 298 K, 100
r/min. The adsorption coefficient (D) for Yb(III) ion was the
highest when pH value was 5.50 in the HAc-NaAc medium
and decreased by either raising or lowering pH under the
experimental conditions. At lower pH values, the Yb(III) ion
uptake was inhibited in the acidic medium, which can be at-
tributed to the presence of H+ ion competing with the Yb(III)
ion for the adsorption sites. In contrast, the Yb(III) ion is
prone to precipitation at higher pH values. Therefore, all the
following experiments were performed at pH 5.5 in the
HAc-NaAc system.
Fig. 1 Influence of pH on the distribution coefficient of Yb(III)
(Resin 15.0 mg, C0=5.0 mg/30.0 ml, T=298 K, 100 r/min)
-
7/29/2019 1-s2.0-S1002072110604693-main
3/6
ZHENG Zhanwang et al.,Adsorption behavior of ytterbium (III) on gel-type weak acid resin 409
2.2 Isotherm adsorption curve
The Langmuir model perhaps is the best known isotherm
to describe adsorption from a liquid solution. The Langmuir
model assumes uniform energies of adsorption on the sur-
face and no interaction between adsorbed molecules. The
model also assumes that adsorption is limited to completesurface coverage by a monomolecular layer and can be rep-
resented by the following equation[19,20]:
e e
e m m
1=
C C
Q Q bQ (3)
where Ce (mg/ml) is equilibrium concentration of Yb(III), Qe
(mg/g) the adsorbing capacity in equilibrium state, Qm (mg/g)
the saturated adsorption capacity and b the Langmuir con-
stant which reflects quantitatively the affinity between the
110 resin and Yb(III) ions. It is used to analyze batch equi-
librium data by plotting Ce/Qe versus Ce, which yields a lin-
ear plot if the data conform to the Langmuir isotherm. Ac-cording to the experiment data, plotting of Ce/Qe versus Ce
gave a straight line and the correlation coefficient R2
(R2288
K=0.9913, R2298 K=0.9869, R
2308 K=0.9958) were high as
shown in Fig. 2. This was indicative of applicability of the
proposed model for the process undertaken. In other words,
the Langmuir-type adsorption isotherm was suitable for
equilibrium studies. This indicates that the adsorption of Yb
(III) ion by 110 resin is of monolayer-type[21]
.
2.3 Determination of adsorption rate constant at dif-
ferent temperatures and apparent activation energy
The influence of contact time on the adsorption of Yb(III)
ion onto 110 resin (Fig. 3) was investigated at various tem-
peratures, i.e., 288, 298 and 308 K. The amount of adsorp-
tion increased with increasing contact time. Further, the
loading half time t1/2 was 7 h and the maximum adsorption
was observed after 36 h, beyond which there was almost no
further increase in the adsorption. Therefore, this interaction
time could be well taken as equivalent to the equilibrium
time. Meanwhile, the equilibrium adsorption capacity of
Yb(III) ion onto 110 resin was found to increase with in-
creasing temperature, indicating that the adsorption of Yb(III)
ion onto the adsorbent was favored at higher temperatures.
Fig. 2 Langmuir isotherm curves (Resin 15.0 mg, C0=5.0 mg/30.0
ml9.0 mg/30.0 ml, pH=5.5, 100 r/min)
Fig. 3 Adsorption capacity (Q)at different contact time and tem-
peratures (Resin=15.0 mg, C0=18.0 mg/60.0 ml, pH=5.5,
100 r/min)
This effect suggests that the adsorption mechanism associ-
ated with Yb(III) ion onto 110 resin involves a temperature
dependent process.
According to Brykina method, the adsorption rate constant
kcan be calculated from[22,23]:
ln(1F)=kBt (4)
whereF=Qt/Qe, Qt (mg/g) and Qe (mg/g) are the adsorption
amounts at certain time and at equilibrium, respectively. The
experimental results accord with the equation and a straight
line is obtained by plotting ln(1F) versus t(Fig. 4) and the
adsorption rate constants of 110 resin for Yb(III) can be
found from the slope of the straight line, which are shown in
Table 2. According to Boyd equation, it can be deduced
from the linear relationship of ln(1F) versus tthat the liq-
uid film spreading is the controlling step in the adsorptionprocess.
According to the formula of Arrhenius[24]:
alg lg
2.30
Ek A
RT (5)
where A is the Arrhenius factor. The relationship between
Fig. 4 Determination of adsorption rate constant (Resin=15.0 mg,
C0=18.0 mg/60.0 ml, pH=5.5, 100 r/min)
Table 2 Adsorption rate constants of 110 resin for Yb (III)
T/K Linearity relation ofln(1F) and t k/(10
5
s
1
) R
2
288 y=0.0833x0.0385 2.31 0.9924
298 y=0.0882x0.0294 2.45 0.9934
308 y=0.0912x+0.0223 2.53 0.9959
-
7/29/2019 1-s2.0-S1002072110604693-main
4/6
410 JOURNAL OF RARE EARTHS, Vol. 29, No. 5, May 2011
lgkand 1/Tis shown in Fig. 5, and the slope of the straight
line Kslope=174.97. So the apparent activation energy Ea=
3.35 kJ/mol can be calculated. It can be seen from the rate
constant that the adsorption speed accelerates when the tem-
perature increases within the scope.
2.4 Influence of adsorption temperature on distribution
ratio and determination of thermodynamic pa-
rameters
The distribution coefficient (D) of the 110 resin for Yb (III)
in the temperature range of 288308 K was measured, and
the result is shown in Fig.6. A straight line was obtained by
plotting lgD against 1/T with a correlation coefficient of
0.9908. The result obviously indicates that it is favorable for
the adsorption with the temperature increasing. It implies
that the adsorption process is endothermic. So the adsorption
reaction is a chemical adsorption.
The vant Hoff equation given below, can be used to cal-culate the enthalpy changes associated with the adsorption
process of the metal ions.
lg2.30 2.30
H SD
RT R
' ' (6)
whereR is the universal gas constant,D the distribution co-
efficient and T(K)the absolute temperature. The plot of lgD
versus 1/Tgives a straight line, from which H(the enthalpy
variation) and S(the entropy variation) were deduced from
the slope and intercept of the line, respectively. And the
Fig. 5 Relationship between lgkand 1/T(Resin=15.0 mg, C0=18.0
mg/60.0 ml, pH=5.5, 100 r/min)
Fig. 6 Influence of temperature on distribution ratio (D) (Resin=
15.0 mg, C0=5 mg/30 ml, pH=5.5, 100 r/min)
free energy variation, G was calculated from:
G=HTS (7)
The thermodynamic parameters of the sorption of Yb(III)
were calculated and given in Table 3. The positive values of
Hindicate the endothermic character of the solid phase ex-
traction and sorption process, but the negative value ofG
indicates the spontaneous nature of Yb(III) sorption. The
positive entropy change (S) value corresponds to an in-
crease in the degree of freedom of the adsorbed species.
2.5 Desorption and regeneration studies
Whether an adsorbent is an appropriate material in re-
moval of metal ions from aqueous solutions depends not
only on its adsorptive capacity, but also on its regeneration
ability. For repeated use of an adsorbent, adsorbed metal
ions should be easily desorbed under suitable conditions. In
this work, 15.0 mg 110 resin was added into a mixed solu-
tion composed of pH 5.5 buffer solution and desired amountof Yb(III) ion solution. After the equilibrium was achieved,
the concentration of Yb(III) ion in the aqueous phase was
determined, and the adsorption capacity of the 110 resin for
Yb(III) ion was obtained. Then, the 110 resin separated from
aqueous phase was washed three times with pH 5.5 buffer
solution. The 110 resin adsorbed Yb(III) ion was shaken
with 30.0 ml HCl eluant. After equilibrium was achieved,
the concentration of Yb(III) ion in aqueous phase was de-
termined and then the percentage of elution for Yb(III) ion
was obtained.
The results shown in Fig. 7 indicate that the percentage ofelution for Yb(III) ion is different when the concentration of
HCl is changed. It is evident that the 3.0 mol/L HCl solution
is suitable to be the eluant.
Table 3 Thermodynamic data calculated for adsorption of Yb(III)
on 110 resin
T/K G/(kJ/mol) H/(kJ/mol) S/(J/(molK))
288 22.80
298 24.45
308 26.10
24.59 164.56
Fig. 7 Desorption of Yb(III) from 110 resin by HCl in varying con-
centrations (Resin=15.0 mg, pH=5.5, T=298 K, 100 r/min)
-
7/29/2019 1-s2.0-S1002072110604693-main
5/6
ZHENG Zhanwang et al.,Adsorption behavior of ytterbium (III) on gel-type weak acid resin 411
2.6 Dynamic adsorption and desorption
2.6.1 Dynamic adsorption curve The performance of
packed beds is described through the concept of the break-
through curve. The breakthrough curve shows the loading
behavior of Yb(III) to be removed from solution in a fixed
bed and is usually expressed in terms of adsorbed Yb(III)concentration (Cad=inlet Yb(III) concentration (Co) outlet
Yb(III) concentration (Ce)) or normalized concentration de-
fined as the ratio of effluent Yb(III) concentration to inlet
Yb(III) concentration (Ce/Co) as a function of time or volume
of effluent for a given bed height[25]. The area under the
breakthrough curve obtained by integrating the adsorbed
concentration (Cad, mg/L) versus the throughput volume (V,
ml) plot can be used to find the total adsorbed Yb(III) quan-
tity (maximum column capacity). Total adsorbed Yb(III)
quantity (Q, mg/g) in the column for a given feed concentra-
tion and flow rate is calculated from Eq. (8):
e dV ( C )
V
0
C0
=C
Qm (8)
where m (g) is the mass of the adsorbent. The capacity value
Qc (mg/g) was obtained by graphical integration as 305 mg/g.
Successful design of a column adsorption process requires
prediction of the concentration versus time profile or break-
through curve for the effluent. The maximum sorption ca-
pacity of 110 resin is also in design.
Traditionally, the Thomas model is used to fulfill the pur-
pose. The model has the following form[26]:
0 T e
1=
1 + exp[ ( )/ ]V T 0
eC
C K Q m C
(9)
where KT (ml/(minmg)) is the Thomas rate constant,
(ml/min) the volumetric flow rate, and QT (mg/g) the theo-
retical maximum sorption capacity value. The linearized
form of the Thomas model is as follows:
T 0T T
eln ( 1) = V
0
e
K CC K Q m
C(10)
The kinetic coefficient KT and the adsorption capacity of
the bed QTcan be determined from a plot of ln [(Co/Ce)1]
versus tat a certain flow rate as shown in Fig. 8. The Tho-
mas equation coefficients for Yb(III) ion adsorption were
KT=9.7102
ml/(minmg) and Qc=311 mg/g. The theoreticalpredictions based on the model parameters were compared
Fig. 8 Thomas model for the continuous adsorption of Yb(III)
(Resin=150.0 mg, C0=0.1 mg/ml, pH=5.5, flow rate=0.28 ml/min)
with the observed data as shown in Fig. 9.
The Thomas model was found in a relatively good fitness
with breakthrough curve for sorption of Yb(III) on 110 resin
with a R2 value 0.9869. In addition, theoretical maximum
adsorption capacity value QT was very close to the experi-
mental one Qc. Therefore, it can be concluded that the ex-
perimental data fitted well to the Thomas model, which in-
dicates that this model was successfully used for the predic-
tion of the breakthrough curves and can be employed to de-
termine the characteristics parameters of the column process
design.
2.6.2 Dynamic desorption curve Efficient elution of ad-
sorbed solute from 110 resin in column was essential to en-
sure the recovery of metal ions as well as the reuse of resin
for repeated adsorption/desorption cycles. With respect to
the stripping of Yb(III) from 110 resin, 3.0 mol/L HCl eluant
was employed. Desorption curve was formed by plotting the
effluent concentration (Ce) versus elution volume (ml) fromthe column at a certain flow rate. It can be seen from Fig. 10
that the desorption flow rate was less so that the volume of
elution was less which helped in easy handling and high
concentration for economical recovery of Yb(III). It was ob-
served that the total volume of eluent was 175 ml, after
which further desorption was negligible. Therefore, the 3.0
mol/L HCl eluant could help in easy handling and recover-
ing of Yb(III).
Fig. 9 Dynamic adsorption curves of 110 resin for Yb(III)
(Resin=150.0 mg, C0=0.1 mg/ml, pH=5.5, flow rate=0.28 ml/min,
T=298 K)
Fig. 10 Dynamic desorption curve of 110 resin for Yb (III)
(Resin=150.0 mg, CHCl=3.0 mol/L, flow rate=0.25 ml/min, T=298 K)
-
7/29/2019 1-s2.0-S1002072110604693-main
6/6
412 JOURNAL OF RARE EARTHS, Vol. 29, No. 5, May 2011
Fig. 11 Infrared spectra of 110 resin
(1) Before adsorption; (2) After adsorption
2.7 IR spectra
The IR spectra of resin samples both before and after
Yb(III) was adsorbed, detected and identified by IR spec-
trometer. From the results above (Fig. 11), it can be deduced
that the sorption of Yb(III) by 110 resin can be classified as
chemical sorption by ion exchange (H>0). And the func-
tional group of 110 resin (C=O) and Yb(III) formed chemi-
cal bonds. It was found that the characteristic absorption
peak of the bond C=O (1710.77 cm1) was sharply weakened,
and the new peak (1544.62 cm1) formed. The result shows
that there are coordination bonds between oxygen atoms and
Yb(III).
3 Conclusions
Yb(III) could be optimally adsorbed on 110 resin in HAc-
NaAc medium at pH 5.50. The statically saturated adsorp-
tion capacity of Yb(III) was 265.8 mg/g 110 resin at 298 K.
The adsorption behavior of 110 resin for Yb(III) obeyed the
Langmuir isotherm. The adsorption rate constant was k298 K=
2.45105 s1 and the apparent activation energy was Ea=
3.35 kJ/mol. Thermodynamic parameters, S, Hand G,
on the adsorption for Yb(III) indicated that the adsorption
process was spontaneous and endothermic. The Yb(III) ad-
sorbed on 110 resin could be eluted by using 3.0 mol/L HCl
solution as an eluant. Infrared spectra of 110 resin adsorbed
Yb(III) showed that the functional group of resin was coor-
dinated with Yb(III) to form coordination compound.
References:
[1] Kouznetsov D, Bisson J F, Ueda K. Scaling laws of disk lasers.
Optical Materials, 2009, 31(5): 754.
[2] David R L. Handbook of Chemistry and Physics 81st Edition.
Maryland: CRC Press, 2000. 5.
[3] Halmshaw R. Industrial Radiology: Theory and Practice. Lon-
don: Springer Press, 1995. 168.
[4] Emsley J, Natures Building Blocks: An A-Z Guide to the Ele-
ments. London: Oxford University Press, 2003. 492.
[5] Sen Gupta J G. Determination of scandium, yttrium and lan-
thanides in silicate rocks and four new canadian iron-formation
reference materials by flame atomic-absorption spectrometry
with micro sample injection. Talanta, 1984, 31: 1045.
[6] Kim J S, Lee C H, Han S H, Suh M Y. Studies on complexa-
tion and solvent extraction of lanthanides in the presence of
diaza-18-crown-6-di-isopropionic acid. Talanta, 1997, 45: 437.
[7] Xiong C H, Liu X Z, Yao C P. Effect of pH on sorption for
RE(III) and sorption behaviors of Sm(III) by D152 resin.
Journal of Rare Earths, 2008, 26: 851.[8] Chen Q. Study on the adsorption of lanthanum(III) from aque-
ous solution by bamboo charcoal. Journal of Rare Earths,
2010, 28:125.
[9] Xiong C H. Sorption behaviour of D155 resin for Ce(III). In-
dian Journal of Chemistry, 2008, 47: 1377.
[10] Yao C P. Adsorption and desorption properties of D151 resin
for Ce(III).Journal of Rare Earths, 2010, 28:183.
[11] Ritcly G M, Ashbrook A W. Solvent Extraction: Principle and
Applications to Process Metallurgy, Part I. Amsterdam: El-
sevier Press, 1984. 603.
[12] Samuelson O. Ion Exchangers in Analytical Chemistry. New
York: John Wiley, 1972. 415.
[13] Xiong C H, Zheng Z W. Evaluation of D113 cation exchangeresin for the removal of Eu(III) from aqueous solution.Journal
of Rare Earths, 2010, 28: 862.
[14] Xiong C H, Yao C P, Wang Y J. Sorption behaviour and
mechanism of ytterbium(III) on imino-diacetic acid resin.Hy-
drometallurgy, 2006, 82: 190.
[15] Xiong C H, Yao C P. Study on the adsorption of cadmium(II)
from aqueous solution by D152 resin.J. Hazard. Mater., 2009,
166: 815.
[16] Yao C P. Sorption behavior and mechanism of D113 resin for
erbium.Journal of Rare Earths, 2007, 25: 169.
[17] Chiou M S, Ho P Y, Li H Y. Adsorption of anionic dyes in
acid solutions using chemically cross-linked chitosan beads.
Dyes. Pigments., 2004, 60: 69.[18] Srivastava V C, Mall I D, Mishra I M. Adsorption thermody-
namics and isosteric heat of adsorption of toxic metal ions onto
bagasse fly ash (BFA) and rice husk ash (RHA). Chem. Eng. J.,
2007, 132: 267.
[19] Basha S, Murthy Z V P. Kinetic and equilibrium models for
biosorption of Cr(VI) on chemically modified seaweed,
Cystoseira indica.Process. Biochem., 2007, 42(11): 1521.
[20] Xiong C H, Yao C P, Wang L, Ke J J. Adsorption behavior of
Cd (II) from aqueous solutions onto gel-type weak acid resin.
Hydrometallurgy, 2009, 98: 318.
[21] Gode F, Pehlivan E. Removal of chromium (III) from aqueous
solutions using Lewatit S100: the effect of pH, time, metal
concentration and temperature. J. Hazard. Mater., 2006,136(2): 330.
[22] Brykina G D, Marchak T V, Krysina L S. Sorption-photometric
determination of copper by using AV-17 anion exchanger
modified with 1-(2-thiazolyl-azo)-2-naphthol-3,6-disulphonic
acid.Zhurnal Analiticheskoi Khimii, 1980, (35): 2294.
[23] Boyd G E, Adamson A W, Myers L S. The exchange adsorp-
tion of ions from aqueous solutions by organic zeolite II kinet-
ics.J. Am. Chem. Soc., 1947, 69: 2836.
[24] Xiong C H, Yao C P. Sorption behavior of iminodiacetic acid
resin for indium.Rare Metals, 2008, 27(2): 153.
[25] Aksu Z, Gonen F. Biosorption of phenol by immobilized acti-
vated sludge in a continuous packed bed: prediction of break-
through curves.Process Biochem., 2004, 39(5): 599.[26] Mathialagan T, Viraraghavan T. Adsorption of cadmium from
aqueous solutions by perlite.J. Hazard. Mater., 2002, 94(3): 291.