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THE FLORIDA STATE UNIVERSITY ARTS AND SCIENCES ...

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1.1. Overview<br />

CHAPTER ONE<br />

1. INTRODUCTION<br />

Widespread pollution of ground and surface waters from Nitrate ( NO ) is of global<br />

concern to human health and the environment. The presence of<br />

1<br />

−<br />

3<br />

−<br />

NO in drinking water is<br />

3<br />

hazardous to health. The Environmental Protection Agency (EPA) has advised that<br />

excessive levels of nitrate in drinking water have been known to cause serious illness and<br />

sometimes death.<br />

Serious illnesses such as methemoglobinemia which can interfere with the oxygen-<br />

carrying capacity of a child's blood are known to be related to increased nitrate levels. In<br />

addition exposure to high levels of nitrate can cause diuresis, increased starchy deposits<br />

and hemorrhaging of the spleen (Department of Ecology). To ensure the safety of the<br />

public the EPA (2009) has established the following standards for Nitrate: Maximum<br />

Contaminant Level Goal (MCLG): 10 mg/l<br />

(MCL): 10 mg/l<br />

−<br />

NO3 -N.<br />

−<br />

NO3 -N; Maximum Contaminant Levels<br />

In addition to the adverse impact on the health of humans using the contaminated water,<br />

excess nitrate has unfavorable effects on the ecosystem as well. Excess<br />

−<br />

NO causes<br />

3<br />

eutrophication in many aquatic systems (Turner & Rabalais, 1994; Fenn et al., 2003).<br />

While it is apparent that contamination of groundwater supplies by<br />

−<br />

NO 3 is a major issue<br />

and is responsible for blue baby syndrome and cancer, what is currently debatable is the<br />

mechanism of nitrate attenuation.<br />

It is widely accepted that once nitrate is leached into the soils there are 4 accepted<br />

pathways for its removal or reduction (DeBernardi et al., 2008; Rivet et al., 2008).

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