Use of Filter Media Made from Vetiver Grass Root Ash for Water Treatment



Similar documents
TRADITIONAL AND HOUSEHOLD WATER PURIFICATION METHODS OF RURAL COMMUNITIES IN DEVELOPING COUNTRIES

Well Water Iron Removal Using Quantum DMI-65 Granular Filter Media

GRADATION OF AGGREGATE FOR CONCRETE BLOCK

REMOVAL OF PHOSPHATE FROM WASTEWATER USING LOW-COST ADSORBENTS

Effect of basalt aggregates and plasticizer on the compressive strength of concrete

Water Water Treatment Plant Tour

HUBER Vacuum Rotation Membrane VRM Bioreactor

WASTEWATER TREATMENT OBJECTIVES

Enhanced Organic Precursor Removals Using Aged Filter Media Page 1. Enhanced Organic Precursor Removals Using Aged Filter Media

Chemistry at Work. How Chemistry is used in the Water Service

HYDRAULIC STRUCTURES, EQUIPMENT AND WATER DATA ACQUISITION SYSTEMS Vol. IV - Testing of Materials and Soils - F. Druyts

Strength and Workability Characteristics of Concrete by Using Different Super Plasticizers

DOW Ultrafiltration. Case History. High Turbidity and Temperature Fluctuation No Obstacle for DOW Ultrafiltration

Chapter Two Types of Cement The properties of cement during hydration vary according to:

Properties of Concrete with Blast-Furnace Slag Cement Made from Clinker with Adjusted Mineral Composition

IUCLID 5 COMPOSITION AND ANALYSIS GUIDANCE DOCUMENT: IRON ORES, AGGLOMERATES [EINECS NUMBER , CAS NUMBER ] IRON ORE PELLETS

Clinker grinding test in a laboratory ball mill using clinker burning with pet-coke and coal

Physical & Chemical Properties. Properties

Membrane Filtration Technology: Meeting Today s Water Treatment Challenges

Use of Fly ash from KKAB, for sealing of landfills

APPROACHING A UNIVERSAL SAMPLE PREPARATION METHOD FOR XRF ANALYSIS OF POWDER MATERIALS

MEMBRANE TECHNOLOGY TREATING OILY WASTEWATER FOR REUSE

SYNERGISTIC APPLICATION OF ADVANCED PRIMARY AND SECONDARY WASTEWATER TREATMENT SYSTEMS

Royal Caribbean International Advanced Wastewater Purification Systems

TALLINN WATER TREATMENT AND SEWERAGE Tuuli Myllymaa

COD/BOD 5 Reduction with ROTAMAT Fine and Micro Screens

Amiad s AMF² pre-treatment technology ensures efficient and reliable nanofiltration of Scottish Highland loch water

Water Softening for Hardness Removal. Hardness in Water. Methods of Removing Hardness 5/1/15. WTRG18 Water Softening and Hardness

Sample preparation for X-ray fluorescence analysis

DOW CORNING CORPORATION Material Safety Data Sheet

Residues from aluminium dross recycling in cement

CATALOGUE OF PRODUCTS

What is Cement? History Overview of the Cement Manufacturing Process Brief Overview of Kiln Operations Why Burn Wastes?

Facility Classification Standards

TREATMENT OPTIONS FOR REMOVAL OF SPECIFIC IMPURITIES FROM WATER. S. Vigneswaran Faculty of Engineering, University of Technology, Sydney, Australia

Innovation and Progress in Water Treatment Technology

Removing Heavy Metals from Wastewater

Treatment of oily wastewater produced from refinery processes using flocculation and ceramic membrane filtration

COMPANY PROFILE & CAPABILITY STATEMENT

Wastewater Reuse. Typical treated wastewater is:

Measurement of Soil Parameters by Using Penetrometer Needle Apparatus

CGA Standard Practices Series. Article 600 Standard for Pozzolan Enhanced Grouts Used in Annular Seals & Well Destruction

Interpretation of clogging effects on the hydraulic behavior of ion treated geotextiles

Nine Industrial Scale V SEPs. Feed Tank V SEP. Feed Pumps (Three) Concentrate. Tank. V SEP Treatment System

IB Chemistry. DP Chemistry Review

Background. 179 million gallons saved for make-up water

NAN YA NYLON 66 Engineering Plastics. Flame Retardant.High Toughness.Heat Resistant. Impact Resistant.Moldability.Low Warpage

CHAPTER 7 THE DEHYDRATION AND SWEETENING OF NATURAL GAS

AP ENVIRONMENTAL SCIENCE 2007 SCORING GUIDELINES

The University of Toledo Soil Mechanics Laboratory

Honors Chemistry: Unit 6 Test Stoichiometry PRACTICE TEST ANSWER KEY Page 1. A chemical equation. (C-4.4)

Geotechnical Characteristics of Two Different Soils and their Mixture and Relationships between Parameters

Use of Nano-scale materials in Water Purification

Indiana s Newest Filtration Facility; East Chicago

Hands-On Labs SM-1 Lab Manual

Designing a Zero-Waste Concrete Mix Testing Lab

Advanced Treatment of Hazardous Wastes(1) Advanced Treatment of Hazardous Wastes(2) Advanced Environmental Chemistry. Design of Solid Waste Landfill

A Study on Recycling of CRT Glass Waste

HUBER The Partner for Paper Industry

Iranian J Env Health Sci Eng, 2004, Vol.1, No.2, pp Application of Intelligent System for Water Treatment Plant Operation.

Water and Wastewater. Sample Collection and Analysis

METHANOL REMOVAL FROM METHANOL-WATER MIXTURE USING MUNICIPAL ACTIVATED SLUDGE

Treatment of dairy wastewater by natural coagulants

Material Safety Data Sheet Fluid: 50 cp

Material Safety Data Sheet Fluid: 5 to 100,000 cp

CH3 Stoichiometry. The violent chemical reaction of bromine and phosphorus. P.76

SOLAR WATER PURIFICATION WITH THE HELP OF CSP TECHNOLOGY

A NOVEL ION-EXCHANGE/ELECTROCHEMICAL TECHNOLOGY FOR THE TREATMENT OF AMMONIA IN WASTEWATER

Coagulation and Flocculation

Ultra-High Strength Concrete Mixtures Using Local Materials

Reverse Osmosis Membranes for Wastewater Reclamation By Craig R. Bartels, PhD Hydranautics, 401 Jones Road, Oceanside California, USA 92054

LATEST TRENDS on SYSTEMS (Volume I)

14. Laundry & Dry Cleaning Industry

Total Dissolved Solids:

COMPANY PROFILE. AES Company, Head Quarter

Natural and Advanced Treatment Systems for Wastewater Management at Municipal Solid Waste Disposal Site in Developing Countries

POLYVINYL ALCOHOL. SYNONYMS Vinyl alcohol polymer, PVOH, INS No DEFINITION DESCRIPTION FUNCTIONAL USES CHARACTERISTICS

Florida Method of Test for TESTING OF GROUND TIRE RUBBER Designation: FM 5-559

ION EXCHANGE FOR DUMMIES. An introduction

Table 1.1: Typical Characteristics of Anaerobically Digested Wastewater

High Performance Dry Binding with HPC-SSL Super Fine Powder

DURABILITY OF MORTAR LININGS IN DUCTILE IRON PIPES Durability of mortar linings

Testing Water for Gardening and Lawn Irrigation

Wax-based binder for low-pressure injection molding and the robust production of ceramic parts

Chapter 3: Separating Mixtures (pg )

Inventory of Performance Monitoring Tools for Subsurface Monitoring of Radionuclide Contamination

PROPAK AquaBio Complete Water Restoration Systems

Pall in the Brewery (more value per hectolitre) DE Free Clarification FB1795

NOTE: FOR PROJECTS REQUIRING CONTRACTOR MIX DESIGN, THE DESIGN PROCEDURES ARE SPECIFIED IN THE SPECIAL PROVISIONS OF THE CONTRACT.

THERMAL CONDUCTIVITY AND THERMAL EXPANSION COEFFICIENT OF GFRP COMPOSITE LAMINATES WITH FILLERS

GRANULAR ACTIVATED CARBON FOR WATER & WASTEWATER TREATMENT

PURIFICATION TECHNIQUES

still different technique of assessment.

Homeowners and Home Buyers Guide to Wells and Private Sewage Systems

Numerical Analysis of the Resin Transfer Molding Process via PAM- RTM Software

Transcription:

2014 International Transaction Journal of Engineering, Management, & Applied Sciences & Technologies. International Transaction Journal of Engineering, Management, & Applied Sciences & Technologies http://tuengr.com Use of Filter Media Made from Vetiver Grass Root Ash for Water Treatment Krittiya Lertpocasombut a* and Maruay Onsod a, b a Department of Civil Engineering, Faculty of Engineering, Thammasat University Rangsit Campus, Pathumtani 12120, THAILAND b Quality System & Product Auditing Manager, Goodyear (Thailand) Public Co. Ltd., Pathumtani, 12120, THAILAND A R T I C L E I N F O Article history: Received 18 June 2014 Received in revised form 06 July 2014 Accepted 09 July 2014 Available online 11 July 2014 Keywords: natural material; polyvinyl alcohol; pellet; turbidity; A B S T RA C T Vetiver grass and its usages have been widely reported in many researches. This research aimed to use the vetiver grass root ash (VGRA) to filter water to improve its quality. The investigation of the physical and chemical properties of the VGRA indicated the product from natural material ash could be used as a filter medium. The distribution of particle size, the specific gravity, and the Iodine number of the VGRA were determined as well as the ratio of the VGRA to polyvinyl alcohol (PVA) as a binding polymer were analyzed. The results revealed that the best mold of the VGRA pellet as a filter media was a circular shape. The ratio of the VGRA to PVA was 7.33 to 1. This was consistent with the results of the linear shrinkage that were 13.35 ± 2.10 which was the best form of the VGRA product to be used as a filter medium for water turbidity treatment. 2014 INT TRANS J ENG MANAG SCI TECH. 1. Introduction The water used must be safe and free from dangerous bacteria. It is necessary to have the water quality meet the required standard. The use of plants to improve water quality is one method that has received considerable attention. In general, natural materials are cheap and readily available in every country. Many researchers [1][2][3] have reported both viable or nonviable properties of vetiver grass and its usages. Vetiver grass is regarded as a miracle plant that is the subject of ongoing research. This research focuses on studying the properties of vetiver grass root ash to produce the filter material suitable for improving water quality. The filter material was formed with polyvinyl alcohol at various *Corresponding author (Krittiya Lertpocasombut). Tel: +66-2-5643005 x3109. E-mail: lkrittiy@engr.tu.ac.th. 2014. International Transaction Journal of Engineering, Management, & Applied Sciences & Technologies. Volume 5 No.4 ISSN 2228-9860 eissn 1906-9642. Online Available at http://tuengr.com/v05/0247.pdf. 247

percentages for the purpose of studying the performance of the filter media produced in terms of the linear shrinkage, the porosity and the apparent density of the product. Then the product selected was used as a filter media for water turbidity treatment. 2. Materials and Methods 2.1 Materials and Chemicals The vetiver grass used was grown for at least 18 months with a length of root not less than 0.50 m. The polyvinyl alcohol (PVA) used was commercial grade with the molecular weight of 30,000 50,000. Water used for the experiment was deionized water. 2.2 Preparation of the Vetiver Grass Root Root of vetiver grass of Nakhon Sawan species was chosen due to its availability and abundance. It was washed thoroughly five times with clean water and then dried under the sun for at least 48 hours. The dried root was burned at 550 ºC for 15 to 30 minutes and ground for size reduction in a laboratory blender at a speed of 3,000 rpm for 15 minutes. At this stage, the properties of the vetiver grass root ash (VGRA) were determined for the particle size distribution following the ASTM D2862 Standard test method, the specific gravity of soil solid by water pycnometer following the standard ASTM 854, and the Iodine number following the standard ASTM D4607. 2.3 The VGRA Pellet The VGRA particles were sifted through a sieve of 50, 100 and 200 mesh sizes, divided into 3 sieve sizes and combined with PVA in ratios varying from 6 to 18 % wt. by wt. The slip behavior flow of the 3 sieve sizes of the VGRA with various percentages of PVA was determined. The linear shrinkage of the VGRA pellet formed was taken into account after drying at 125 ºC for 2 hours. 2.4 Experimental Setup for Water Turbidity Removal Figure 1 shows a schematic diagram of the experimental set up. It was comprised of 3-filter units, and a receiving vessel attached to available suction pump. Figure 1: The schematic diagram of the experimental unit. The raw water sample was taken from the natural river source at the intake of the water supply 248 Krittiya Lertpocasombut and Maruay Onsod

plant located in Pathum Thani province in Thailand. The inlet and exit water turbidity of the filtration unit was measured by UV spectrophotometer. The pressure, the flow rate and the particles capture performances were measured under the experimental conditions. 3. Results and Discussions 3.1 The Physical and Chemical Properties of the VGRA After grinding, the composition of the ash of the vetiver grass root was determined by XRF following the Standard ASTM C114 and results are shown in Table 1. Table 1 The chemical composition of the VGRA. Chemical Composition % Weight % Standard Error Carbon Dioxide (CO 2 ) 52.67 0.16 Silicon Dioxide (SiO 2 ) 44.10 0.14 Aluminum Oxide (Al 2 O 3 ) 1.03 0.17 Iron Oxide (Fe 2 O 3 ) 2.11 0.14 Other 0.10 0.21 It was found that the vetiver grass root ash (VGRA) contained 44.10 % silicon dioxide which was similar to that of the results from AIT research group [3] on the use of vetiver grass ash to replace cement in which composition of silicon dioxide in the ash of the vetiver grass up to 57.48 % was reported. The silica content in the VGRA makes it feasible to further study of the use of roots of vetiver grass as a filter material when combined with a polymer such as polyvinyl alcohol (PVA), which was selected for this study. The mean particle size is useful when determining the specific gravity of the substance. Root of the vetiver grass after burning at 550 C was crushed in a laboratory blender to a mean particle size of 0.068 ± 0.003 mm by sieve analysis. This size is similar to fine sand (0.05-0.25 mm). The specific gravity of the VGRA by the ASTM standards for classification was found to be in the range of 2.26 to 2.60. It was comparable to the compounds like carbon (2.26), gypsum (2.3), clays (2.6), sand and silica (2.6), with a similar specific gravity. Three sieve sizes (50, 100 and 200 mesh) of VGRA were evaluated for Iodine number according to the ASTM standards. This value was considered to examine the assumption that the VGRA has the ability to adsorb. The results showed that the Iodine number of the VGRA (36-46 g/kg) was comparable to the standard carbon N550 and N660. The VGRA of 200 *Corresponding author (Krittiya Lertpocasombut). Tel: +66-2-5643005 x3109. E-mail: lkrittiy@engr.tu.ac.th. 2014. International Transaction Journal of Engineering, Management, & Applied Sciences & Technologies. Volume 5 No.4 ISSN 2228-9860 eissn 1906-9642. Online Available at http://tuengr.com/v05/0247.pdf. 249

mesh sieve size, which was comprised mostly of the smallest particle size, gave the highest Iodine adsorption number. 3.2 The Ratio of the VGRA to PVA Pellets of VGRA were formed by casting. The VGRA of sieve sizes 50, 100 and 200 mesh were combined with the PVA to give concentrations of 6, 8, 12 and 18 % in order to measure the flow behavior and stability of the slip. The results are shown in Figure 2. Plastic Viscosity (mpas) y = 1.0029x + 148.25 R² = 0.9286 y = 0.2436x + 115.27 R² = 0.9681 y = 0.1189x + 52.61 R² = 0.9577 y = 0.0733x + 88.497 R² = 0.9924 PVA 18 % PVA 12 % PVA 8 % PVA 6 % Mesh Number Figure 2: Plastic viscosity values of the VGRA slip at different ratios of PVA. 50 Mesh (%shringkage) y = -66.571x + 42.503 R² = 0.7555 y = -127.62x + 25.488 R² = 0.5476 y = -73.595x + 21.445 R² = 0.8594 Concentration of PVA (%) 100 Mesh 200 Mesh Figure 3: The linear shrinkage of the VGRA of 3 sieve sizes at different ratios of PVA. R 2 values ranging from 93 to 99 % were obtained for all ratios of the VGRA to PVA. The maximum R 2 value was found with the mixture of 12 % PVA producing the optimum flow and stability of the slip. 250 Krittiya Lertpocasombut and Maruay Onsod

3.3 The Linear Shrinkage of the VGRA Pellet Hollow casting was used to test for the linear and volumetric shrinkages of the VGRA which had been combined with PVA in different ratios to form a pellet. The results are shown in Fig. 3. The VGRA of 100 mesh sieve size showed the highest coefficient of determination with 86 % corresponding to the VGRA to PVA ratio of 7.33 to 1. 3.4 The Capability of the VGRA Filter Media A water volume of 0.25 L was filtered through the VGRA pellets produced from 50, 100 and 200 mesh sieve sizes with the PVA content of 12 % and a constant pressure of 2 bars. With the filtration pressure constant, the flow rates of water filtered through the 3 sets of VGRA pellets declined as the mesh number of the VGRA pellets increased from 50, 100 and 200 mesh. The flow rates were 444, 309 and 151 L/m 2 h, respectively. On comparing these values with the flow rates of microfiltration membrane (10 20 L/m 2 h) [4], they were about 10 times higher. The flow rate decreased similarly when the water was filtered through the VGRA pellets under a constant pressure of 7 bars as well. However, all VGRA pellets produced from 50 mesh were cracked as were some of the 100 and 200 mesh pellets also. The efficiency of particles capture was 67, 73 and 73 % and their residual values were 67, 55 and 54 ppm respectively under a pressure of 2 bars. No similar research on filter media has been found to make a comparison. One explanation of the effect of removal of coliform bacteria (as suspended solid) with modified homemade filter media could be that as the treatment time progressed, the adsorbent sites of the media had a tendency towards saturation [5]. 3.5 The Effects of Turbidity on the VGRA Filter Media With the constant pressure of 2 bars and the water sample used from the natural river source, the effluent turbidity reached a steady value of 30 ± 1 NTU when flowing through the VGRA pellet of 100 mesh sieve size, whereas, the VGRA pellet of 50 mesh sieve size exhibited lower efficiency of removal turbidity (up to 50 NTU) as shown in Table 2. Table 2 Turbidity of the water before and after passed through the VGRA pellet. Turbidity Mesh Number (NTU) 50 100 200 Inlet 122 122 122 Exit 50 31 30 From these results, removal efficiency of 75 % was obtained for inlet turbidity of 122 NTU and a flow rate of 309 L/m 2 h for filtration using the 100-mesh VGRA pellet with PVA 12 % as the filter media. *Corresponding author (Krittiya Lertpocasombut). Tel: +66-2-5643005 x3109. E-mail: lkrittiy@engr.tu.ac.th. 2014. International Transaction Journal of Engineering, Management, & Applied Sciences & Technologies. Volume 5 No.4 ISSN 2228-9860 eissn 1906-9642. Online Available at http://tuengr.com/v05/0247.pdf. 251

4. Conclusions The vetiver grass root ash (VGRA) containing up to 44.10 % of silicon oxide with a mean particle size of 0.068 mm was used as a filter material. Its specific gravity was in the range of 2.26 to 2.60, similar to silt and fine sand. The VGRA with 200 mesh sieve size showed acceptable results with the maximum Iodine number of adsorption, the flow behavior of slip in forming, and a suitable PVA ratio. However, the linear shrinkage of the VGRA pellet formed with 100 mesh sieve size resulted in the best coefficient of determination compared to the VGRA pellet with 200 mesh and 50 mesh sieve sizes, respectively. The filtration experiment confirmed that the 100-mesh VGRA pellet formed with PVA content of 12 % was the optimal composition as a filter media under 2-bar pressure for water turbidity removal. 5. References [1] Thiramongkol, V., & Baebprasert, B. The vetiver grass pot: Production and use. Department of Science Service, Bangkok, Thailand, pp.350-352, www.prvn.rdpb.go.th/files/cp-4-6.pdf, [18 July 2012]. [2] Ash, R., & Truong, P. (2004). The use of vetiver grass for sewage treatment. Sewage Management QEPA Conference, Cairns, Australia, April 5-7, 2004. www.vetiver.com/aus_ekeshire01.pdf, [18 July 2012]. [3] Nimityongskul, P. & Chomchalow, N. Utilization of vetiver grass as construction materials. AIT. www.prvn.rdpb.go.th/files/7-05.pdf, [18 July 2012]. [4] Lertpocasombut, K. (2004). Hollow fiber microfiltration membrane in activated sludge and its chemical cleaning for water reuse. Proceedings of the International Symposium on the Development of Water Resource Management System in Mekong Watershed, Hanoi, Vietnam, December 3-4, 2004, 46-52. [5] Devi, R., Alemayehu, E., Singh, V., Kumar, A., & Mengistie, E. (2008). Removal of fluoride, arsenic and coliform bacteria from drinking water by modified homemade filter media. Bioresource technology, 99(7), 2269-2274. Dr.Krittiya Lertpocasombut is an Associate Professor in the Department of Civil Engineering, Faculty of Engineering, Thammasat University, Thailand. She received a B.Sc. in Chemistry from Chulalongkorn University, Thailand, an M.Sc. in Environmental Engineering, Asian Institute of Technology (A.I.T.), D.E.A. Diplome d Etudes Approfondies in Water Purification and Treatment Engineering from INSA de Toulouse, France, and a PhD in Water Purification and Treatment Engineering, Institut National des Sciences Appliquees (INSA), Toulouse, France. Dr. Lertpocasombut is interested in water and wastewater treatment; wastewater recycled by membrane technology; water supply sludge treatment and its reuse/recycle. Maruay Onsod is Quality System & Product Auditing Manager, Goodyear (Thailand) Public Co. Ltd., Thailand. She obtained a B.Sc (Chemistry) from Rajamagala University of Technology (Thanyaburi). She is a master candidate in the Department of Civil Engineering, Faculty of Engineering, Thammasat University. She is interested in water treatment technologies. Peer Review: This article has been internationally peer-reviewed and accepted for publication according to the guidelines in the journal s website. 252 Krittiya Lertpocasombut and Maruay Onsod