A liquid solid semi-moving bed with non-mechanical particle transport system is proposed and used for fractionation of cesium ion in wastewater. The particle transport system, which consists of a suction chamber, a mixing chamber, a nozzle and a riser tube, is designed to be controlled completely by hydraulic force. Experiments show that continuous feeding and discharging of resin can be realized by the transport system. The removal of cesium ion from wastewater is realized. The concentration of cesium ion in effluent liquid remains below 0.1g · L−1 (the initial concentration is 5.3g · L−1) during the 73 hours' experiment. The average exchange capacity of resin discharged from the bed is 0.57 mmol · (g dry resin)−1, which is close to the saturated capacity of 0.65 mmol · g−1. And it is also proved that the non-homogeneity of particle vertical velocity along the radial direction can seriously influence the ion-exchange process.
Pollution by heavy metal ions happen frequently
to wastewater discharged from nonferrous smelting,
printing and dyeing, electroplating, chemical industry
etc. The heavy metal ions can make the water body
smelly and even poisonous when the concentration
reaches certain degree. For example, cadmium may
replace calcium in skeleton resulting in chronic intoxication
or even death. So, there has been increased
awareness of the importance of wastewater disposal of
heavy metal ions.
The technologies of wastewater disposal used
nowadays can be grouped into chemical treatment,
physicochemical treatment and biological treatment.
The method of chemical treatment includes the coagulation
method using femc salt, aluminous salt or chitosan
as coagulant[ 11, oxidation-reduction method[2], gas
foam separation method[3-51, neutralization precipitation
method[6] and chemical precipitation method[7,8].
The method of physicochemical treatment includes
adsorption[9,10], ion-exchange[ 11-13], solvent extraction[
141 and membrane separation[ 151. The
method of biological treatment uses algae or microorganism
to purify the water body[16,17], which is still
at experimental stage and not adopted in commercial
application at present. Among these technologies, the
ion-exchange method, in which metal ions are exchanged
to resins, has received most of attention and
widely utilized in wastewater disposal due to high selectivity,
high enrichment factor and convenient operation.
The liquid-solid treatment equipment is a key factor
influencing treatment effects of the ion-exchange
method. Up to now, fixed-bed is adopted in most cases
because of its simple structure and mild resin wearing.
But for fixed bed, continuous production can not be
realized, and complex pipelines and numerous valves
may result in huge equipment investment and operation
cost. To avoid these disadvantages, continuous
equipment becomes a subject of much concern.
In an earlier article, a rotary ion-exchange system,
a continuous equipment similar to simulated moving
bed, was reported[ 181. Although the equipment can
overcome some disadvantages of fixed-bed, the manufacture
is very difficult because it requires high working
accuracy and tightness. Moving bed is another
applicable continuous equipment for ion-exchange
method. In early research, an annular moving bed was
proposed by Higgins[l9]. Carlson[20] studied on a
continuous moving bed system composed of water
disposal column, regenerating column and some circulation
columns. It is very important that the particles
can move steadily downward for continuous equipment.
In these studies, moving rate and moving direction
of solid particles (resin) are controlled by some
valves, which may result in particle crushing. Also,
the maintenance of these valves is difficult, especially
in corrosive, poisonous or radioactive systems. To
obtain enough contact time of resin with liquid, a long
exchange section is often required, which makes the
particle crushing more serious. Until now, relatively
few papers are devoted to the studies of particle
transport in liquid-solid moving bed and heavy metal
ion separation using moving bed by ion-exchange
method.
Much interest has been recently focused on Cs'
purification in wastewater disposal, for cesium ion can
result in biological cell damages. Especially in the
wastewater discharged from nuclear reactor, I3'Csf
ions with high radioactivity may cause radiation sickness.
Heretofore, some works devoted to Cs' purification
in wastewater have been reported[21-241. Experiments
show that high selectivity of Cs' for wastewater
disposal can be obtained when insoluble ferrocyanide
is used as ion-exchanger[21-231. Mass-transfer
performance of Cs' with potassium titanium hexacyanoferrate
was examined by shallow-bed techniques[24].In this article, a liquid-solid semi-moving bed with
non-mechanical particle transport system and potassium
titanium hexacyanoferrate as ion-exchanger is
proposed and tested for purification of cesium ion.
In this work, a liquid-solid semi-moving bed with
non-mechanical particle transport system is proposed
and used for ion-exchange of cesium ion in wastewater.
The transport system is operated completely by
hydraulic force. Conclusions may be drawn as follows:
(1) Continuous operation for feeding and discharging
of resins can be realized steadily by the
non-mechanical particle transport system, which is
especially suitable for corrosive, poisonous or radioactive
system.
(2) The cesium ion in wastewater can be well
separated in the liquid solid semi-moving bed using
ion-exchangers prepared by the method in this article.
The concentration of Cs' within effluent liquid keeqs
lower than 2% of the initial concentration (5.3g.L- )
throughout 73h treatment process in most cases. The
average exchange capacity of resins discharged from
the bed is 0.57mmol.(g dry resin)-', which is close to
the saturated capacity of 0.65mmol.g-'.(3) The distribution of exchange capacity of resins
along axial direction is non-monotonic, which is
caused by the vertical speed difference at radial positions
for particles. Large area ratio of the exchange
section to the conduit and the conical distributor are
the key factors.
The work in this article is a preliminary investigation
for semi-moving bed, and problems such as
adjustment of flow pattern of particles are required to
be examined further.