Abstract High molar mass polysaccharides (locust bean gum and karaya gum) and effluents from a mechanical pulp mill and a paper mill were nanofiltered with commercially available nanofiltration (NF) membranes. The effect of the filtration conditions on the flux (critical flux), retention, and the fouling of the membranes was studied. The experiments were conducted by increasing and decreasing the pressure and measuring the flux thus obtained. The critical flux was observed to increase with increasing flow velocity and decreasing concentration. An increase in pH increased the electrostatic repulsion between the membrane and the dissociated (charged) components in the paper mill effluents. As a result, a higher critical flux was obtained and also the retentions of the charged substances improved. Only a weak form of the critical flux was observed with the mill effluents. The permeate flux deviated from the pure water flux even at the lowest pressure, but increased linearly with pressure until the weak form of the critical flux was exceeded. The small decrease in flux immediately after filtration was started was probably caused by the plugging of the free spaces in the membranes or by the adsorption of foulants onto the membrane surface. In the filtrations with the high molar mass polysaccharides, a strong form of the critical flux as well as a weak form were observed. The significant irreversible fouling of the most hydrophobic membrane was due to adsorption of the model substances by hydrophobic interaction. A precleaning of the membranes with an alkaline cleaning agent improved the pure water fluxes by up to 30%, but it had only a small effect on the critical or the limiting flux. The pure water fluxes of precleaned membranes after filtration were still higher than the pure water fluxes of the untreated membranes before filtration.
[1]
Mika Mänttäri,et al.
Evaluation of nanofiltration membranes for filtration of paper mill total effluent
,
1997
.
[2]
A. Fane,et al.
Particle deposition during membrane filtration of colloids: transition between concentration polarization and cake formation
,
1997
.
[3]
M. Mänttäri,et al.
Fouling effects of polysaccharides and humic acid in nanofiltration
,
2000
.
[4]
El Hani Bouhabila,et al.
Microfiltration of activated sludge using submerged membrane with air bubbling (application to wastewater treatment)
,
1998
.
[5]
M. Jaffrin,et al.
Cake growth mechanism in cross-flow microfiltration of mineral suspensions
,
1995
.
[6]
M. Mänttäri,et al.
Influence of filtration conditions on the performance of NF membranes in the filtration of paper mill total effluent
,
1997
.
[7]
Anthony D. Greiner,et al.
Diagnosis of membrane fouling using a rotating annular filter. 1. Cell culture media
,
1993
.
[8]
Shoji Kimura,et al.
EVALUATION OF PORE STRUCTURE AND ELECTRICAL PROPERTIES OF NANOFILTRATION MEMBRANES
,
1995
.
[9]
H. Ruiz,et al.
A pilot study on groundwater natural organics removal by low-pressure membranes
,
1995
.
[10]
Pierre Aimar,et al.
Model for colloidal fouling of membranes
,
1995
.
[11]
R. Field,et al.
Critical flux concept for microfiltration fouling
,
1995
.