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Accepted Papers - 3.pdf - UNESCO

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them to a great extent. Metals concentrated within<br />

macrophytes are available for grazing by fish. These<br />

may also be available for epiphytic phytoplankton,<br />

herbivorous and detrivorous invertebrates. This may<br />

be a major route for incorporating metals in the<br />

aquatic food chain. It is therefore of interest to assess<br />

the levels of heavy metals in macrophytes due to<br />

their importance in ecological processes. The<br />

immobile nature of macrophytes makes them a<br />

particularly effective bio-indicator of metal<br />

pollution, as they represent real levels present at<br />

that site. Data on phytotoxicity studies are<br />

considered in the development of water quality<br />

criteria to protect aquatic life, the toxicity evaluation<br />

of municipal and industrial effluents (APHA.<br />

American Public Health Association. (1998). In<br />

addition aquatic plants have been used to assess the<br />

toxicity of contaminated sediment elutriates and<br />

hazardous waste leachates.<br />

In the past research with macrophytes has<br />

centered mainly on determinig effective eradication<br />

techniques for nuisance growth of several species<br />

such as Elodea Canadensis, Eichhornia crassipes,<br />

Ceratophyllum demersum etc… Scientific literature<br />

exists for the use of wide diversity of macrophytes<br />

in toxicity tests designed to evaluate the hazard of<br />

potential pollutants, but the test species used is quite<br />

scattered. Similarly literature concerning the<br />

phytotoxicity tests to be used, test methods and the<br />

value of the result data is scattered. Estuarine and<br />

marine plant species are being used considerably<br />

less than freshwater species in toxicity tests<br />

conducted for regulatory reasons. The suitability of<br />

a test species is usually based on the specimen<br />

bioavailability, sensitivity to toxicant, reported data<br />

and the like. Table 1. uptades the variety of test<br />

species used for phytotoxicity studies. The<br />

sensitivity of various plants to metals was found to<br />

be species and chemical specific, differing in the<br />

uptake as well as toxicity of metals. Many<br />

submersed plants have been used as test species,<br />

but there is no widely used single species. In a<br />

literature survey only 7% of 528 reported<br />

phytotoxicity tests used macrophytic species. Their<br />

use in microcosm and mesocosm studies is even<br />

rarer and has been highly recommended. Several<br />

plant species like Lemna, Myriophyllum,<br />

Potamogeton have been exhaustively used in<br />

phytotoxicity assessment, but several others have<br />

356<br />

been given less importance as a bioassay tool.<br />

Duckweeds have recieved the greatest attention for<br />

toxicity tests as they are relevant ot many aquatic<br />

environments, including lakes, streams, effluents.<br />

Duckweeds comprise Spirodela, Wolfiella, Lemna<br />

and Wolffia, of which Lemna has been almost<br />

exhaustively studied.<br />

CONSTRUCTED WETLANDS :<br />

The most important role of plants in wetlands<br />

is that they increase the residence time of water,<br />

which means that they reduce the velocity and<br />

thereby increase the sedimentation of particles and<br />

associated pollutants. Thus they are indirect<br />

involved in water cleaning. Plants also add oxygen<br />

providing a physical site of microbial attachment<br />

to the roots generating positive conditions for<br />

microbes and bioremediation. For efficient removal<br />

of pollutants a high biomass per volume of water of<br />

the submerged plants is necessary. Uptake of metals<br />

in emergent plants only accounts for 5% or less of<br />

the total removal capacity in wetlands. Not many<br />

studies have been performed on submerged plants,<br />

however, higher concentration of metals in<br />

submerged than emerged plants has been found and<br />

in microcosm wetland the removal by Elodea<br />

canadensis and Potamogeton natans showed up to<br />

69 % removal of Zn. (Kadlec 1995; Kadlec and<br />

Knight 1996).<br />

Constructed and engineered wetlands for water<br />

treatment (Figures 1-5; Okurut et al 1999).<br />

Natural wetlands<br />

used for wastewater treatment for centuries<br />

uncontrolled discharge irreversible degradation.<br />

Constructed wetlands<br />

effective in treating organic matter, nitrogen,<br />

phosphorus, decrease the concentrations of heavy<br />

metals, organic chemicals, and pathogens.<br />

POTENTIAL ROLE OF AQUATIC PLANTS IN<br />

PHYTOTECHNOLOGY FOR WASTE WATER<br />

TREATMENT :<br />

Phytoremediation is defined as the use of<br />

plants for environmental cleanup. Aquatic<br />

macrophytes have paramount significance in the<br />

monitoring of metals in aquatic ecosystems<br />

(eg: Lemna minor, Eichhornia crassipes, Azolla

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