Effect of flocculant dosage onto flock size at flocculation in agitated vessel

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See discussions, stats, and author profiles for this publication at: http://www.researchgate.net/publication/270579806 Effect of flocculant dosage onto flock size at flocculation in agitated vessel ARTICLE · JANUARY 2010 CITATION 1 READS 7 2 AUTHORS, INCLUDING: Radek Šulc Czech Technical University in Prague 22 PUBLICATIONS 13 CITATIONS SEE PROFILE Available from: Radek Šulc Retrieved on: 29 October 2015

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Flocculation is one of the most important operations in solid-liquidseparation processes in water supply and wastewater treatment. Flockproperties such as size, density and porosity affect the separation processand its effi ciency. Thus the knowledge of fl ock properties in dependenceonto operational conditions has been important for the properdesign of separation process.

Transcript of Effect of flocculant dosage onto flock size at flocculation in agitated vessel

Page 1: Effect of flocculant dosage onto flock size at flocculation in agitated vessel

Seediscussions,stats,andauthorprofilesforthispublicationat:http://www.researchgate.net/publication/270579806

Effectofflocculantdosageontoflocksizeatflocculationinagitatedvessel

ARTICLE·JANUARY2010

CITATION

1

READS

7

2AUTHORS,INCLUDING:

RadekŠulc

CzechTechnicalUniversityinPrague

22PUBLICATIONS13CITATIONS

SEEPROFILE

Availablefrom:RadekŠulc

Retrievedon:29October2015

Page 2: Effect of flocculant dosage onto flock size at flocculation in agitated vessel

Prosimy cytować jako: Inż. Ap. Chem. 2010, 49, 1, 111-112

str. 111Nr 1/2010 INŻYNIERIA I APARATURA CHEMICZNA

Radek ŠULC, Ondřej SVAČINAe-mail: [email protected] Department of Process Engineering, Faculty of Mechanical Engineering, Czech Technical University in Prague, Prague, Czech Republic

Effect of fl occulant dosage onto fl ock size at fl occulation in agitated vessel

IntroductionFlocculation is one of the most important operations in solid-liquid

separation processes in water supply and wastewater treatment. Flock properties such as size, density and porosity affect the separation pro-cess and its effi ciency. Thus the knowledge of fl ock properties in de-pendence onto operational conditions has been important for the proper design of separation process.

The aim is to propose the simple semiempirical generalized correla-tion quantifying effect of fl occulant dosage onto fl ock size, to verify experimentally the model proposed and to assess fl ock shape by fractal dimension.

Generalized correlation quantifyingeffect of fl occulant dosage

Based on our previous work [1−3] we assume that the dependence of fl ock size on the fl occulant dosage can be given by a simple formula:

1/ log / log /d A D c B D c C20 0f f F K f f K f= + +^ ^ ^h h h , (1)

where (1/df) is reciprocal fl ock size, DF/cK0 is a dimensionless fl occu-lant dosage, Af, Bf, Cf are the model parameters, DF is fl occulant dosage (fl occulant dosage per tank volume; mg/l), cK0 is a initial kaolin con-centration (g/l). Then the generalized correlation quantifying effect of fl occulant dosage onto fl ock size can be derived as follows:

1/ /d A D c* *0 log

* 2

f f F KT =^ `h j6 @ (2)

rewritten

1 /dd

A D cmax *0 log

* 2

f

ff F K= + ` j6 @ , (3)

where:

1/ 1/1/ 1/

d dd d*

max

maxf

f

f fT =-

^ h , (4)

/ log /log / log /

D c D cD c D c

0 log

*

0 max

0 0 maxF K

F K

F K F KT =

-^^

^ ^^

h h

h h h6 @ , (5)

4

AA C B

B*2

2

ff f f

f= -, (6)

where dfmax is a maximal fl ock size reached at fl occulant dosage [DF/cK0]max, [DF/cK0]max is a dimensionless fl occulant dosage in that dfmax can be reached, Af is a fl ock size shift coeffi cient and Af, Bf, Cf are parameters of Eq. (1). The generalized correlation parameters dfmax,[DF/cK0]max and Af

* depend generally on the fl occulation process condi-

tions such as mixing intensity, fl occulation time, etc.).

ExperimentalThe fl occulation experiments were conducted in a fully baffl ed cylin-

drical vessel of diameter D = 150 mm, fi lled in height H = D by a model wastewater – kaolin slurry (tap water + kaolin particles). Solid fraction of kaolin was 440 mg/l. The vessel was agitated by Rushton turbine of diameter d = 60 mm that was placed at an off-bottom clearance of H2/d = 0.85. The baffl e width B/D was 0.1.

The fl ock size was determined based on an analysis of images ob-tained by digital camera in a plane illuminated by a laser light ([3] in de-

tail). The scheme of experimental apparatus for image analysis is shown in Fig. 1. Technical parameters are presented in Tab. 1.

For the camera resolution 800#800 pixels used the scale 1 pixel ∝ 45 μm was found for our images. It corresponds to scanned area35#35 mm (approx. 6% of tank cross-section area). The model waste-water was fl occulated by the organic polymer fl occulant Sokofl ok 56A (medium anionity, 0.1% wt. aqueous solution; fl occulant weight per fl occulant solution volume mF/VF = 1 mg/ml; Sokofl ok Ltd., Czech Re-public). Experimental conditions are specifi ed in Tab. 2. During sedi-mentation the images of fl ocks passing through the plane illuminated and having 10-bit depth were captured with frame rate 10 s-1, exposure = 5 ms, and gain 35 dB. The image capturing starts 20 s after impeller

Fig. 1. Schema of experimental apparatus for image analysis

Tab. 1. Technical parameters

Item Specifi cation

Laser diode NT 57113, 30 mW, wave length 635 nm (red light), Edmund Optics, Germany

Diode optics optical projection head NT54-186, Projection Head Line, Edmund Optics, Germany

Camera color CMOS camera SILICON VIDEO®SI-SV9T001C, EPIX Inc., USA

Camera optics objective 12VM1040ASIR 10-40 mm, TAMRON Inc., Japan

Image processing card PIXCI SI PCI Image Capture Board, EPIX Inc., USA

Camera control software XCAP®, EPIX Inc., USAOperation software Linux CentOS version 5.2, Linux kernel 2.6Software for image analysis SigmaScan Pro 5.0

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Prosimy cytować jako: Inż. Ap. Chem. 2010, 49, 1, 111-112

str. 112 Nr 1/2010INŻYNIERIA I APARATURA CHEMICZNA

shutdown and takes 120 s. Finally 1200 images were obtained for given fl occulation experiment and ones were stored into a hard disk as 24-bit jpg format. The images captured were analyzed using SigmaScan soft-ware and its pre-defi ned fi lters ([4] in detail).

Experimental data evaluationFrom images captured the largest fl ock was identifi ed and its pro-

jected area was determined for given fl occulant dosage. The depen-dence of equivalent diameter df eq calculated according to fl ock area onto fl occulation time was fi tted according to the generalized correlation (2). The generalized correlation parameters are presented in the Tab. 3. The comparison of experimental data and generalized correlation is depicted in Fig. 2.

For fl ock shape characterization the fractal dimension of 2nd order Df2 was used. The relation among projected area A, characteristic length scale Lchar and fractal dimension Df2 is given by:

A CLcharD 2f= (7)

The largest fl ocks determined in obtained images were used for frac-tal dimension estimation. The maximum fl ock size was used as a cha-racteristic length scale. The fractal dimension Df2 was determined for each fl occulant dosage. For illustration the dependence of projected area on maximum fl ock size is shown in Fig. 3 for fl occulant dosage DF = 2 ml/l (i.e. dimensionless fl occulant dosage (DF/cK0) = 4.545 mgF/gK). The fractal dimension Df2 plotted in dependence on dimensionless fl occulant dosage for given fl occulation time and mixing intensity is shown in Fig. 4.

The effect of fl occulant dosage onto fractal dimension Df2 was tested by hypothesis testing. The hypothesis test result and the pa-rameter β evaluated from data is presented in the Tab. 4. The fractal

Tab. 2. Experimental conditions

Parameter Kaolin concentration cK0 = 0.44 g/lεV [W/m3] 40

n [rev/min] 180tF [min] 6.66ntF [–] 1200

DF [ml/l] 0.4, 1.2, 2, 2.4, 3.2 4.4, 5.6, 6.8, 8DF [mg/l] 0.4, 1.2, 2, 2.4, 3.2 4.4, 5.6, 6.8, 8

DF/cK0 [mgF/gK] 0.909, 2.727, 4.545, 5.455, 7.273, 10, 12.727, 15.455, 18.182No. of date 9

Tab. 3. Generalized correlation Δ(1/df eq)* = f(Δ[DF/cK0]

*log): parameters fi tted

εV[W/m3]

n[rev/min]

[DF/cK0]max[mgF/gK]

DFmax[ml/l]

df eq max[mm]

Af*

[–]Iyx

*1

[–]δr ave/δr max

*2

[%]40 180 4.693 2.07 1.3101 0.8215 0.9691 5/12.8

Fig. 2. Generalized correlation ∆(1/df eq)* = f(∆[DF/cK0]log*)

*1correlation index*2relative error of equivalent fl ock size df eq: average/maximum absolute value

Fig. 3. Fractal dimension determination – example for DF = 2 ml/l

Fig. 4. Fractal dimension vs. dimensionless fl occulant dosage – Df2 = f (DF/cK0)

Tab. 4. Fractal dimension – hypothesis testing

εV[W/m3]

m[–]

t-distributiont(m-2), α = 0.05

Relation Df2 = B.(DF/cK0)

β

βcalc

t-characteristics |t|Hypothesis

Df2 = B.(DF/cK0)0

βpred = 040 9 2.3646 0.011 0.4 (Yes)

dimension was found independent of fl occulant dosage and the value Df2 = 1.469 ± 0.086 was determined as average value.

Conclusions

The simple semiempirical generalized correlation describing effect of fl occulant dosage onto fl ock size was proposed and used for data treatment. The fl ock shape was characterized by fractal dimension Df2. Using the statistical hypothesis test the fractal dimension was found in-dependent of fl occulant dosage and the value Df2 = 1.469 ± 0.086 was determined as average value for given conditions.

LITERATURE

[1] R. Šulc: Flocculation in a turbulent stirred vessel. PhD thesis. Czech Techni-cal University, Faculty of Mechanical Engineering 2003 (in Czech).

[2] R. Šulc, P. Ditl: Czasopismo Techniczne – Seria: MECHANIKA. 105, nr 2, 341 (2008).

[3] R. Šulc, O. Svačina: submitted in Acta Polytechnica.[4] O. Svačina: Application of image analysis for fl occulation process moni-

toring. Diploma work. Czech Technical University, Faculty of Mechanical Engineering 2009 (in Czech).

This Research has been subsidized by the Research Project of MSMT of Czech Republic MSM:6840770035.

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