By: B.V.Kulkarni, Dr. S. V. Ranade and Dr. A.I. Wasif
Abstract
In a present investigation phytoremediation of textile process effluent by using water hyacinth has been carried out in the KIT's College of Engineering Campus, for studying reduction of COD and metals from textile process effluent. It has been observed that there is a reduction of 80% in COD and about
Key Words Phytoremediation, textile effluent, water hyacinth
Introduction
Phytoremediation is the use of certain plants to clean upsoil, sediment and water contaminated with metals and/or organic contaminantssuch as crude oil, solvents, and polyaromatic hydrocarbons (PAHs).Phytoremediation is the use of plants to remediate contamination by the uptakeof contaminated water by plants.
Plants can be used to contain, remove, or degradecontaminants. It is a name for the expansion of an old process that occursnaturally in ecosystems as both inorganic and organic constituents cyclethrough plants.
Plant physiology, agronomy, microbiology, hydrogeology, andengineering are combined to select the proper plant and conditions for aspecific site.
Phytoremediation is an aesthetically pleasing mechanism thatcan reduce remedial costs, restore habitat and clean up contamination in placerather than entombing it in place or transporting the problem to another site.
Phytoremediation can be used to clean up contamination inseveral ways:
Phytovolatillization:
Plants take up water and organic contaminants through theroots, transport them to the leaves, and release the contaminants as a reducedor detoxified vapor into the atmosphere.
Microorganism stimulation:
Plants excrete and provide enzymes and organic substancesfrom their roots that stimulate growth of microorganisms such as fungi andbacteria.
The microorganisms in the root zone then metabolize theorganic contaminants.
Phytostabilization
Plants prevent contaminants from migrating by reducingrunoff, surface erosion, and ground water flow rates. Hydraulic pumping canoccur when tree roots reach ground water, take up large amounts of water,control the hydraulic gradient, and prevent lateral migration of contaminantswithin a ground water zone.
Phytoaccumulation/extraction:
Plant roots can remove metals from contaminated sites andtransport them to leaves and stems for harvesting and disposal or metalrecovery smelting processes.
Phytodegradation by plants:
Organic contaminants are absorbed inside the plant and metabolized (broken down) to non-toxic molecules by natural chemical processes within the plant.
Day |
Date |
COD mg/l |
1 |
02.04.2006 |
415 |
2 |
03.04.2006 |
410 |
3 |
04.04.2006 |
400 |
4 |
05.04.2006 |
380 |
5 |
06.04.2006 |
366 |
6 |
07.04.2006 |
348 |
7 |
08.04.2006 |
344 |
8 |
09.04.2006 |
333 |
9 |
10.04.2006 |
320 |
10 |
11.04.2006 |
310 |
11 |
12.04.2006 |
280 |
12 |
13.04.2006 |
172 |
13 |
14.04.2006 |
140 |
14 |
15.04.2006 |
100 |
15 |
16.04.2006 |
92 |
16 |
17.04.2006 |
80 |
17 |
18.04.2006 |
78 |
18 |
19.04.2006 |
71 |
A Phytoremediation system capitalizes on the synergistic relationships among plants, microorganisms, water, and soil that have evolved naturally in wetlands and upland sites over millions of years. In the biological sequences that transform contaminants to neutral compounds, plants contribute inherent enzymatic and uptake processes that can recycle or sequester the organic molecules they encounter.
Plants act as hosts to aerobic and anaerobic microorganisms, supplying them with physical habitat and chemical building blocks. Plants roots and shoots increase microbial activity in their direct environment by providing additional colonizable surface area, increasing readily-degradable carbon substrates by organic exudates and leachate and by decomposition of part of their mass and spatially varying oxygen regimes.
Physically, plants slow the movement of contaminants in soil, by reducing run-off and increasing evapotranspiration and by adsorbing compounds to their roots. Once a wetland or upland Phytoremediation system in place, its biological components are naturally self-sustaining, powered by plant photosynthesis
Phytoremediation can be applied in terrestrial and aquatic environments. It can be used as "a preparative or finishing step for other clean-up technologies. Plants are aesthetically pleasing, and theses are relatively self-sustaining and cost-effective.
Water hyacinth is just beginning to be used for Phytoremediation. This use came about for a few reasons, the first being that water hyacinth is so plentiful. People have been trying to remove the plant from many waterways, spending billions of dollars in doing so. In many cases removal is high up to impossible. It has been discovered that water hyacinth's quest for nutrients can be turned in a more useful direction.
The results of several studies show plants such as the water hyacinth use appreciable amounts of the inorganic forms of nitrogen and phosphorus found in domestic sewage. Because inorganic nitrogen and phosphorus are accumulated to a large extent in the roots (roots represent 20 per cent of the wet weight of the plants), this quality signifies a second possible use for the water hyacinth as 'compost', or organic fertilizer. Water hyacinth compost (total plant), however, presents a problem because the fiber is not degraded. Water hyacinth root compost has nevertheless been used with good results as a propagation medium for house plants.
Water hyacinth is already being used to clean up waste water in small scale sewage treatment plants. This plant utilises vast amount of many nutrients, which are poisonous to humans in these amounts. The water hyacinth has been shown to remove Nitrogen and Phosphates, as well as chemical oxygen demands. In the process of studying water hyacinth's capabilities in sewage treatment it has been discovered that this plant removes trace toxic metals as well.
Sr. No. |
Metal |
Concentration in mg/ltr. 02.04.20013 |
Concentration in mg/Itr. 19.04.2006 |
1 |
Cd |
0.1 |
0.06 |
2. |
Cr |
0.41 |
0.3 |
3. |
Cu |
0.48 |
0.25 |
4. |
Fe |
1.52 |
0.9 |
5. |
Ni |
0.42 |
0.32 |
6. |
Pb |
0.32 |
0.16 |
7. |
Zn |
0.31 |
0.136 |
Water hyacinths thrive on sewage; they absorb and digest waste water pollutants, converting sewage effluents to relatively clean water. Thus, the plants have exciting promise as a natural water purification system, which can be established at a fraction of the cost of a conventional sewage treatment facility. Water hyacinths are serving that purpose in several locales and a number of other communities are considering adoption of the technique. For maximum effectiveness, Pollution gorged water hyacinths must be harvested at intervals, but this apparent drawback offers potential for additional benefit. Harvested plants can be and are being used as fertilizer. They can also be heat treated to produce consumer energy in the form of methane gas. And if an economical way of drying the plants can be developed, they may find further utility as high protein animal feed.
Materials and methods
1) Construction of trench for the study
The underground trench open to the sky, for storage of textile process effluent was constructed using one brick thick (0.09 m) thickness and lining was provided.
Trench dimensions are | = | 0.6 m x 0.6 m x 0.5 m |
Volume | = | 0.180 m3 |
Surface area | = | 0.36 sq.m. |
2) To avoid seepage plastic cover was provided.
3) Treated textile process effluent is poured into the trench.
4) Release of water hyacinth in the tank has been done.
5) Grab samples were collected from the tank and were analysed for COD and metals as per standard methods of APHA (1998)
Results & discussion
It can be seen from the results that there is a reduction of 80% COD and 25 to 45% of metals after 18 days period.
Conclusion
1) Phytoremediation of Textile process effluent by the use of water hyacinth is effective and efficient for the reduction of COD and metals present in the effluent.
2) Although the process is efficient, it consumes more time and land requirement are also more. It also produces nuisance of odor and flies.
3) Hence phytoremediation by the use of water hyacinth is recommended as polishing treatment for the textile process effluent.
Acknowledgement
The authors expressed their gratitude to the
- The Principal, KIT's College of Engg., Kolhapur
- The Principal, DKTE's Textile and Engg., Institute, Ichalkaranji
- Head CFC, Shivaji University, Kolhapur
- Head, Department of Biotechnology, KIT's College of Engg. , Kolhapur for providing facilities and encouragement throughout the studies.
References
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- Susarla, S., Medina, V.F. and S.C. McCutcheon (2002). Phytoremediation: An Ecological Solution to Organic Chemical Contamination "Ecological Engineering. 2002".
- Textile committee, Govt. of India, Ministry of Textiles, Best management Practices for Pollution Prevention in Textile Industry. 1997
About the Author:
B.V. Kulkarni is associated with Dept. of Environmental Engg., KIT's College of Engineering, Kolhapur, Maharashtra.
Dr. S. V. Ranade is Retd. Prof. and Head of with Dept. of Civil Engg. Walchand College of Engg. Sangli, Maharashtra.
Dr. A.I. Wasif is associated with DKTE's Textile & Engineering Institute, Ichalkaranji, Dist. Kolhapur, Maharashtra.
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