constructed wetland system for wastewater … · 2018. 9. 7. · spectrophotometer method is 2488...
TRANSCRIPT
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CONSTRUCTED WETLAND SYSTEM FOR
WASTEWATER
TREATMENT
AT KIT'S COLLEGE CAMPUS
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WHY THIS PROJECT WORK?
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Non – effective previous treatment
Strong, irritant & pungent odour to the water.
Same water was utilized for the gardening purpose.
Mosquito Breeding problem.
Disposed water of properties beyond acceptance limits.
Health & Sanitation problems to hostel residents.
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CONCEPT OF CONSTRUCTED / ENGINEERED WETLANDS
•An artificial marsh or swamp field.
Treatment of anthropogenic discharge.
Artificial wastewater treatment systems rely upon natural microbial, biological, physical and chemical processes.
•Impervious clay or synthetic liners, and engineered structures to control the flow direction, liquid detention time and water level.
•Can treat urban runoff, municipal, industrial, agricultural and acid mine drainage.
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Classification of Constructed Wetlands according to Macrophytes :-
•Free-floating macrophyte-based system •Rooted emergent macrophyte-based system •Submerged macrophyte-based system
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Classification according to Flow Type :-
•Surface flow (SF) wetlands •Subsurface flow (SSF) wetlands: Horizontal flow constructed wetlands
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General SFW Constructed Wetland Design
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Sub Surface Flow Constructed Wetland for
Domestic Waste Treatment
Source : NEERI, Mumbai
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Another typical SFW Constructed Wetland
Design
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Design of Constructed Wetland in this case :
This system is Surface Flow (Horizontal Flow) type wetland & combination of floating, emergent & submerged type of vegetation.
Preliminary Treatment :
Already available raw sewage collection tank constructed in brick – cement.
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Design of Various Zones :
Inlet Zone Design :-
This zone is meant for the application of floating vegetation.
This pond is designed for the detention time of
1 day.
The dimensions of the pond are
6.5 m x 5 m x 1.2m
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Design of Various Zones :
Ephemeral Zone Design :-
This zone is meant for the application of emergent as well as floating vegetation. .
This pond is designed for the detention time of
1 day.
The dimensions of the pond are
8.5 m x 5 m x 0.9m
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Design of Various Zones :
Wetland Zone Design :-
This zone is meant for the application of submerged as well as floating vegetation. This is the last pond from where the treated water can be pumped for any recycling purpose
This pond is designed for the detention time of
1 day.
The dimensions of the pond are
6 m x 5 m x 1.2 m
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Design of Various Zones :
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Project Execution
The project is executed considering all the factors affecting it:
Site Selection
Site clearance
Survey, Mapping for obtaining Ground Profile
Excavating according to design
Bund preparation, piping, lining.
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Project Site : Before Execution
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Layout Plan
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Excavation using JCB
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Excavated Site as per design
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Ref. from Manual
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Compaction & Bunding
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Sheets spread over the pits to check percolation of water in soil
Lining : Plastic Sheets in 1st pond
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Nominal Piping :-
Piping for conveying sewage are provided as following : Pipe conveying sewage to 1st Pond: 1 Nos – 9 inches dia. Pipe conveying sewage to 2nd Pond: 3 Nos - 4 inches dia Pipe conveying sewage to 3rd Pond: 1 Nos - 9inches dia.
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Piping at First Bund : 3 No. 4” PVC
Piping at Second Bund :
1 No. 9” PVC
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Piping Systems Provided
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Selection of Plant Species :-
Selection of plant species is done depending on the previous study.
The new concept of using combination of all three types of plants is used.
The type of plants used are :
1) Floating type
2) Emergent type
3) Submerged type
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Natural Aquatic System that can be used for treatment
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Water Hyacinth :
(Echhornia crassipes)
This is a most common aquatic plant available abundantly in polluted water.
Famous for extracting Nitrogen from water.
Reproduces vegetative
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Pistia sp.:
This is also common aquatic plant available abundantly in natural water bodies.
Famous for extracting Nitrogen & phosphorous from water.
Reproduces vegetative & faster than Water Hyacinth
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Anabena azzola:
This is most common aquatic fern available abundantly in moderately polluted water bodies.
Famous for its symbiosis with nitrogen fixing bacteria .
Reproduces vegetative
But very difficult to withstand artificially created conditions.
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Cat-Tail (Typha sp.):
This is very common emergent plant found in marsh places.
It is used here for the root zone treatment.
Reproduces sexually
Grows at relatively slow rate than floating plants.
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Green Algae :
Found in most of the water bodies having sufficient solar penetration.
It is a submerged type of algae
Grows up to depth of 0.15 to 0.90 m
It is used here for increasing in the DO biologically. Reproduces asexually Grows at very faster rate.
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Hydrilla :-
It is found in most of the water bodies having sufficient solar penetration.
It is used here for increasing in the DO biologically.
Grows at slower rate.
Requires very less toxicity to survive unlike other plants used here.
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General Processes taking place in a Wetland
System
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Phosphorus Transformation in Wetland Systems
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Various floating plants used in Inlet Zone:
Echhornia crassipes, Anabena azzola, Pistia sp.
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Various emergent plants used in Shallow Marsh Vegetation Zone:
Typha, Colocasia esculenta, Canna indica, Nymphaea pubescens
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Chemical Analysis :-
Nitrogen (Ammonia) :
Spectrophotometer Method IS 2488 Part IV : 1974 (Performed at CETP lab)
TKN Phosphorous
Phosphates Dissolved Oxygen
BOD C. O. D.
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Nitrogen (Ammonia) & Water Quality :-
1 Volume of Water will dissolve
1300 volumes of Ammonia.
Toxic Range of Nitrogen : Above 0.53 mg/L
Criteria :
The Nitrogen (Ammonia) in the water should not exceed 0.05 mg/L in order to protect aquatic organisms.
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Parameter Avg. % removal Time Period Nitrogen (NH3)
TKN
Phosphates
BOD
COD
100 35 days
85.50 50 days
46.34 50 days
34 50 days
35.14 30 days
Results in Brief
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Increase in D.O. Level :
The algal growth in abundance made it possible to dissolve higher amount of Oxygen in the water of 2nd Pond & onwards.
Period 6 days 12 days 24 days
Pond
Raw
1st
2nd
Nil Nil Nil
Nil
6.3 5.2
Nil Nil
4.3
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Increase in DO can be judged by this colour difference in precipitate during the test.
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Commissioning of the System:-
Activity Date
Site clearing 3rd December
7th January
19th January
Excavation with JCB
Dewatering from 1st pond
Tamping, consolidation & bund preparation
4th February
19th January
Collection of Emergent plants
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Commissioning of the System :-
Water entered in 1st pond
Floating plants introduced in 1st pond
Collection of few other floating plants (Azzola & Pistia)
Activity Date
Laying of plastic sheets 5th February
15th February
17th February
20th February Analysis of effluent samples started for checking results
23th February
Plantation of Emergent plants 9th February
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Economical Aspects :-
Total Cost of Project
Total Area under Project
Cost of Project per sq m area
Total Flow being treated
Total Cost per liter flow
Total cost per capita
Expected design period for pilot project
12996.00
225 sq m
57.76
40 m^3 /d
0.32
14.44
3 yrs (20-25 yrs)
1,08,000.00
2.70
:DSR 2008-09 by MJP
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Summing UP :
1. Total Odor Removal
2. Considerable removal of TKN.
3. Considerable in Oxygen Level
4. Considerable reduction in Phosphates.
5. Cost Effectiveness
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Summing UP :
4. A total solution system for college to treat wastewater.
5. A working model for the future students to pursue further study & research in this area.
6. A value addition to Institute’s policy to take initiative in any innovative ideas like ‘Energy Park’
7. The project has special contribution to the ecosystem development at the site.
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Summing UP :
Some Practical Problems & Possible Remedies :-
1. Stagnancy of Water
2. Limitations of Lining Material
3. Lack of continuous sludge removal system.
4. Waste specific behaviour of plants.
5. Limitation of time
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Waste Specific Behaviour of Echhornia crassipes
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Summing UP :
Future Scope :-
1. Maintenance of the system in future is required.
2. More study about the efficiency & process of the system is required to be done by future students.
3. Even this project can be an ideal system for the research as well as application point of view to many communities, institutes.
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THANK YOU!
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SUBMITTED & PRESENTED BY
HARSHAD VIJAY KULKARNI
VISHAL S. CHOUGALE NIKHIL N. SHETYE
SANTOSH E. SHIRKE DIPTI S. SHINDE
UNDER THE GUIDANCE OF
PROF. S. S. SHAHA
DEPARTMENT OF ENVIRONMENTAL ENGINEERING
KIT’s COLLEGE OF ENGINEERING, KOLHAPUR