BIOLOGICAL WASTEWATER TREATMENT BY PHYTOREMEDIATION IN A CONSTRUCTED WETLAND SYSTEM

Similar documents
V E T I V E R S Y S T E M U S E D I N W A S T E W A T E R T R E A T M E N T

VETIVER PHYTOREMEDIATION TECHNOLOGY FOR TREATMENT OF SEWAGE EFFLUENT IN INDIA

VETIVER SYSTEM FOR INDUSTRIAL WASTEWATER TREATMENT AND DISPOSAL AT GELITA APA, QUEENSLAND, AUSTRALIA

WASTEWATER TREATMENT AT A SEAFOOD PROCESSING FACTORY IN THE MEKONG DELTA, VIETNAM

Cameron Smeal GELITA Australia, Beaudesert, Queensland, Australia Paul Truong Veticon Consulting, Brisbane, Queensland, Australia

EFFECTS OF SEA WATER SALINITY ON THE GROWTH OF VETIVER GRASS (CHRYSOPOGON ZIZANIOIDES L.) Doan Chi Cuong 1, Vo Van Minh 1 and Paul Truong 2

THE VETIVER SYSTEM FOR THE TREATMENT OF CONTAMINATED WATER AND EFFLUENT 12/13/17 THE VETIVER NETWORK INTERNATIONAL 1

APPLICATIONS OF VETIVER IN WESTERN AFRICA:

EFFECT OF SOIL SALINITY ON VETIVER GROWTH. Paul Truong The Vetiver Network International and Veticon Consulting Brisbane, Australia November 2012

AUTHORS MWANSA MUKUKA DR. CHISHALA BENSON H. DR. MUTITI SAMUEL DR. UCHIDA YOSHITAKA APPSA CONFERENCE 6 TH NOVEMBER, 2017

REPORT ON LAWS AND RECOMMENDATIONS ON DENTAL MERCURY MANAGEMENT IN THE EU

Role of Microorganisms in Wastewater Treatment

Phosphate removal from secondary effluent of wastewater treatment: characterization and potential re-use as fertilizer of recovered precipitates

Assessing Virus Reduction/Inactivation by UV during Municipal Wastewater Treatment

UNITED STATES DISTRICT COURT NORTHERN DISTRICT OF ALABAMA SOUTHERN DIVISION

Physico-Chemical Study of Vetiver in Wetland Soil Reclamation

Changes in C/N ratio and some chemical properties during decomposition of hazelnut husk under field conditions

Ecosystems and Microbiology Unit Study Guide

Development of Cost Functions for Sewage Treatment Plants based on Conventional Activated Sludge Process

FAQs on Proper Disposal of Drugs

LAKE NAIVASHA. A Lake in Trouble. A Possible Solution?

Conference Theme. Objectives

Influence of Polymer Selection on Nutrient Phase Separation for Waste Activated Sludge Thickening at Bench Scale

Giuseppe Mascolo. CNR Istituto di Ricerca Sulle Acque Via F. de Blasio, Bari, Italy

The Effect of the Methods of Farming on the Environment and Growth of Cultured Red Sea Bream, Pagrus major

ENVIRONMENTAL, ECONOMICS AND EQUITY ASPECTS OF VETIVER IN SOUTH INDIA

Association des Amidonneries de Céréales de l Union Européenne

Treating Wastewater with Vetiver Grass

Planning for an Inclusive Transformation in Sri Lanka

AN EVALUATION OF COMMERCIAL TEXTILE TANNINS BASED ON THEIR INERT COD CONTENT AND TOXICITY

Solubilization of organic materials in wastewater treatment

26 27 April 2012 in Isfahan, Iran. Hamid Reza Rahmani. Scientific Member of Soil and Water Institute of Iran.

VETIVER FORAGE and BIOMASS

- Overview - Mercury Releases from Dental

Product name: Yashinomi Detergent Date written : Jul. 6, 2000 Date revised : Jan. 14, Yashinomi Detergent

Vetiver in Thailand: General aspects and basic studies. Vetiver in Thailand: General aspects and basic studies. Nualchavee Roongtanakiat

Bill Boehner Pittsburgh Central Catholic PJAS 2014 Grade 11

1. understand that the internal skeleton of vertebrates is needed for support and movement

PLANT-DRIVEN IRRIGATION FROM THE GROUND UP.

VETIVER SYSTEM TECHNOLOGY: APPLICATION AND DEVELOPMENT IN CHINA FROM 1998 TO Feng Ziyuan. Director

City of Watsonville Public Works Department M E M O R A N D U M

Figure 1. Location of 43 benchmark sites across Alberta.

The Application of tannin extract from plants to reduce the concentration of arsenic

Efficiency of Arsenic Removal from Soil by Vetiveria zizanioides and Vetiveria nemoralis

Biosolids Test Description Method Number Test Code Acid Hydrolyzable Phosphate SM P E-99 AHPHOS Acidity as CaCO3 SM-2310 B (4a)-97 ACID

PLANNING FOR AN INCLUSIVE TRANSFORMATION IN SRI LANKA

Economic recovery of zinc from Mining Influenced Water (MIW)

INITIAL INVESTIGATIONS OF POOR SUGARBEET AREAS. D.W. Franzen, D.H. Hopkins, and Mohamed Khan North Dakota State University INTRODUCTION

The 1 th International and The 4 th National Congress on Recycling of Organic Waste in Agriculture April 2012 in Isfahan, Iran

Rehabilitation in Ethiopia: The Case of Wichi Wetland and Micro Watershed, Metu District

VETIVER PHYTOREMEDIATION TECHNOLOGY FOR REHABILITATING SHIRAZ MUNICIPAL LANDFILL, IRAN

Mid Term Review. 1. step 1, only 3. both step 1 and step 2 2. step 2, only 4. neither step 1 nor step 2

Wet White Energized By

4.1 Cycling of Matter Date: Cycling of Organic and Inorganic Matter. Build your Own Notes:

SECTION 1: Identification. SECTION 2: Hazard(s) identification. SECTION 3: Composition/Information on ingredients. 1.1.

Towards impact based monitoring of Estrogenic Endocrine Disrupting Chemicals (eedc).

Cell Processes Review

A COLLABORATIVE NATIONAL STRATEGY TO MANAGE FERAL SWINE IMPACTS IN THE U.S.

VETIVER SYSTEM FOR ENVIRONMENTAL PROTECTION

HIGHLANDS COMMUNITY DEVELOPMENT DISTRICT

Programme to promote Rainwater Harvesting in the Caribbean

How to Conduct On-Farm Trials. Dr. Jim Walworth Dept. of Soil, Water & Environmental Sci. University of Arizona

BRIEF SUMMARY OF THE PROJECT

Key Stage 4 Nitrogen recycling

Page 1. Name:

Essential quality and labelling requirements. Fertilisers Working Group meeting

Environmental Studies

Standard B-3: The student will demonstrate an understanding of the flow of energy within and between living systems.

THE USE OF VETIVER SYSTEM IN AFRICA VETIVERIA ZIZANIOIDES

Voting Topics. AAPFCO Summer Annual 2016

THS General Biology S1 Interim Assessment

UN Agencies strategic approach to Articles 17 and 18 of the WHO FCTC. Geneva, 17 November 2017

Production of 5-Aminolevulinic Acid from Monosodium Glutamate Effluent by Halotolerant Photosynthetic Bacterium (Rhodobacter capsulatus SS3)

Vetiver System for Industrial Wastewater Treatment in Queensland, Australia

ENVIRONMENTAL PROTECTION

Understanding your results Acidity... 3 Aluminium... 3 Base saturation... 3 Boron... 4 Bulk density... 4 Calcium... 4 Cations...

CIE4485 Wastewater Treatment

CONFERENCE SUMMARY. Criss Juliard The Vetiver Network

Yield and quality of cumin as influenced by FYM enriched micronutrients

County of San Mateo. Inter-Departmental Correspondence. Department: COUNTY MANAGER File #: TMP-0716 Board Meeting Date: 7/11/2017

Ecological Impact of Vetiver in Foreign Environments

Japan's Contribution to the Minamata Convention. To Prevent Global Mercury Pollution

Environmental Hazards in Clandestine Labs. No Disclosures. Objectives 10/17/2012

Growth variables for Vetiver zizanioides in the hyperarid region of Sistan plain

Overview of Per-and polyfluoroalkyl substances (PFAS): History, Sources, Exposure Pathways, Analytical Challenges, and Resources

Study on relationship between soil microorganisms and nutrient elements of Vetiveria zizanioides

The Use of Vetiver Grass to Rehabilitate City Garbage Leachate by Isotope Techniques

in a uniquely natural way.

Soil 4234 Guest Lecture

ANNEX GUIDANCE TO MEMBER STATES: SUGGESTED ACTIONS ON BETTER ENVIRONMENTAL IMPLEMENTATION. to the

MSU Extension Publication Archive. Scroll down to view the publication.

Understanding Phosphorus Dynamics and Controls to Better Manage the Turbid Minnesota River System

BIODIGESTION OF FOGs & TREATMENT OPTIMIZATION 2008 Bacta-Pur, BACTIVATOR & ECOPROBIOTICS are trademarks of Aquaresearch Canada Ltd used under license.

FERTIGATION 24 FERTIGATION WITH DRIPPERS

Safe Medication Disposal A white position paper Pennsylvania Pharmacists Association February 8, 2009

Soils and Soil Fertility Management

Dental amalgams & alternative materials

What is homeostasis? How is the human body organized? What are the 11 different human organ systems?

Performance Standards Workshop Midwest Case Studies

Understanding a Soil Report

Transcription:

BIOLOGICAL WASTEWATER TREATMENT BY PHYTOREMEDIATION IN A CONSTRUCTED WETLAND SYSTEM A Comparative Study using Vetiver (Chrysopogon Zizanioides) and Narkot (Phragmites karka) Nandani Pari Ghimire 5-2-408-19-2008 Batch 2012-2014 SuperVisor: Dr. Bhojraj Panta Co- Supervisor: Mr. Sunil Babu Khatry Co- Supervisor: Dr. Ramji Bogati

Outline Introduction Statement of Problem Objective Significance of Study Limitations Study Area Data Collection technique Major Findings Summary Conclusion Recommendation

Introduction Wastewater: Combination of Organic and Inorganic pollutants Wetlands: Storehouse of organic nutrients Constructed wetlands: Mimic of natural system Phytoremediation: Biologically nutrient absorption by plants and microorganisms Vetiver(Chrosopogon zizanioides) and Narkot; Common reed(phragmites karka) widely used for wastewater treatment in many countries Vetiver Narkot

Statement of Problem Human sanitary wastes, Sewerage, Industrial effluents are main cause of water pollution Bagmati river quality: COD(110-197.62), TSS (92-3000), NO3( 0.6-1.25) mg/l since 2003-2013 (ENPHO, 2003;Ghimire. N., 2013) Bagmati and its tributaries around Kathmandu being degraded Kathmandu Valley had five municipal wastewater treatment plants (WWTP) at Guheshwori, Kodku,Dhobighat,Sallaghari and Hanumanghat but the only operated was activated sludge system at Guheshwori (Aratha, 2003) Conventional methods for wastewater treatment are costly and technically advance Natural, easy and low cost method needed which is best done by phytoremediation in Constructed wetland system

Objective Broad Objective To determine the waste water treatment efficiency of Vetiver (Chrysopogon zizanioides) and Narkot (Phragmites karka) in Constructed Wetland System Specific objectives To Study the morphological changes in the Vetiver and Narkot during their growth on planting individually or mixed way To determine the Physiochemical Parameters of wastewater before and after treatment at an interval of two weeks to determine the change in chemical concentration To identify the variability of water parameters in relation to morphological change and different way of plantation of Vetiver and Narkot To compare the efficiency of Vetiver (Chrysopogon zizanioides) and Narkot (Phragmites karka) in waste water treatment

Significance of Study Phytoremediation- natural process, no additional technical assistance once planted properly with appropriate planning water quality of natural streams improved Impact on surrounding positive Beneficial for agriculture, social, environment and economic sectors Comparision bring better solution Would be helpful for further research Treatment and recycling of wastewater Meet water demand without deteriorating the natural systems

Limitation of Study conducted in very small scale (150 lt/ pond/ day) (Cull et al., 2000, 600ml/pot) The research duration only six month (March to August- favorable environmental condition) The Lab Tests were done after three months of plantation Exact variation in treatment efficiency with growth could not be studied in detail mixing of rainwater and the ground water flow during Monsoon

Study Area

Data Collection Technique S.No Objective Method Tools and methodologies 1 Studying morphological changes in the vetiver and Narkot during their growth 2 Determining Physiochemical parameters before and after treatment 3 Identify variability of water parameters in relation to morphological change Site Observation APHA, AWWA and WEF (2005) MPN method Comparing treated water parameters values at different level of growth Measuring plants height and hedge at weekly interval Determining BOD, COD, NO3,TP, CO2,Cl and coliform at two weeks interval MS-Excel 2007, SPSS 20, CONOCO 4.5 and R 1.12.1 for T-Test, Scatter Diagram and ANOVA

Major Findings Maxm Growth rate V=67cm, Narkot=48cm On the sixth month the overall concentration of BOD5, COD, NO 3 - N, TP, Free CO 2, Chloride content and EC in the effluent after treatment were reduced by % RED BOD 5 COD NO3- N TP CO2 Cl- Vetiver 92.30 80.76 90.90 78.12 87.5 81.13 Narkot 76.92 35.38 81.18 55 56.25 52.83 Mixed 84.61 53.84 84.09 60 62.5 60.37 Control 53.84 28.12 30 32.5 28.12 26.41 Treatment efficiency vetiver>mixed>narkot>control Soil Nutrients Org. matter, TN%, TP(ppm), Organic compound high from vetiver pond than Narkot, Nutrients after six month increased in all treatment ponds

Findings Contd Water Quality BOD COD reduction Soil Nutrients

Results From Paired T-Test for COD reduction Compared Between T DF P-Value 95% confidence interval Sample mean difference Vetiver Vs Phragmites 22.706 5 3.08e-06 35.35626 44.38374 39.87 Vetiver Vs Mixed 9.5919 5 0.0002087 21.04633 36.45700 28.75167 Phragmites Vs Mixed -3.663 5 0.01455-18.920748-3.315918-11.11833 One way ANOVA test of variance of COD reduction effeciency of Vetiver and Narkot with Growth Rate Vetiver(Chrosopogon Df Sum Sq Mean Sq F value Pr(>F) zizanioides) (COD Red%) 1 16.1 16.06 0.112 0.754 Residual 4 571.9 142.99 Narkot (Phragmites karka) Df Sum Sq Mean Sq F value Pr(>F) (COD Red%) 1 636.4 636.4 1.614 0.273 Residual 4 1577.0 394.2 Change in %Organic matter, % Organic carbon, Average P and Total Nitrogen concentration in soil Before Plantation After 3 months After 6 months V N M Control V N M Control V N M Control % Org. 4.64 5.23 4.86 4.64 5.82 6.04 5.67 6.67 7.55 6.26 6.81 6.30 Carbon %OM 8.00 9.02 8.38 8.00 10.03 10.41 9.78 11.49 13.02 10.80 11.75 10.86 Avg.P(ppm) 95.0 108.1 99.9 95.0 121.3 126.2 118.0 140.2 160.0 131.2 143.5 132.0 TN% 0.34 0.38 0.35 0.34 0.42 0.43 0.41 0.47 0.53 0.45 0.48 0.45

Summary Growth rate greater in the Vetiver than Narkot Narkot showed dying and new growth continuously Wastewater treatment, As new plants played role in absorbing nutrients, its efficiency was unaffected by growth rate Mixed Pond performed better than Narkot in wastewater treatment Vetiver survived 100%,Wastewater treatment efficiency remained excellent everytime along its growth, Growth rate didn t vary its efficiency Reduced range of the pollutants concentration within the standard Guideline value by Vetiver treatment

Conclusion with no arguments can be developed as an easy, natural and cost effective option for the treatment of wastewater Wastewater treated by Vetiver can be reused for irrigation, aquaculture, recreation and industrial purposes and has no harm to the aquatic lives and river ecosystem. Decentralized wastewater treatment necessary Phytoremediation in Constructed wetland- best and easy option for wastewater treatment at less invest of money, time and technology

Recommendation More practical, reliable and cheaper method of treating effluent before being passed into the river should be sought Decentralized wastewater treatment for promoting reuse and recycle of wastewater Appropriate techniques for rainwater harvesting should be developed, particularly for major urban areas Awareness activities about conserving water quality and quantity should be conducted in all parts of the country Strict laws and efflent standards should be enforced for the major contributors of wastewater like Industries, Hospitals, Hotels, Housings, Departement malls etc. Guideline should be updated and maintained

Acknowledgement to All