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CHAPTER SIX<br />

6. USE OF ISOTOPES TO ESTIMATE LOSS OF<br />

NITRATES DUE TO DENITRIFICATION.<br />

It is well known fact that denitrification is a biological anaerobic process which involves<br />

the reduction of nitrate to nitrogen by heterotrophic bacteria such as Paracoccus<br />

denitrificans and various pseudomonads. While the process involves several stages in the<br />

conversion of nitrate to nitrogen it may be summed up and expressed as a single step<br />

reaction (Equation 6.1).<br />

-<br />

3<br />

-<br />

2 NO + 10 e + 12 H → N + 6 H<br />

+<br />

2<br />

2<br />

O<br />

154<br />

------ Equation 6.1<br />

As the reaction is biologically mediated it is an irreversible biogeochemical reaction that<br />

is accompanied by significant fractionation because of the bacterial preference for the<br />

lighter isotope. Like other irreversible biogeochemical reactions, denitrification is<br />

accompanied by significant isotope fractionation of the light isotope (i.e., 14 N or 16 O).<br />

This fractionation results in enrichment of the residual NO3 − in the heavier isotope (i.e.,<br />

15 N and 18 O) (Chen and McQuarrie, 2005).<br />

6.1. Use of dual isotopes to identify denitrification<br />

Several investigators used the dual-isotope (δ 15 N and δ 18 O) approach to investigate<br />

denitrification in groundwater (Bottcher et al. 1990; Wassenaar 1995; Aravena and<br />

Robertson 1998; Grischek et al., 1998; Cey et al. 1999; Mengis et al. 1999; Devito et al.<br />

2000, Lobnik et al., 2008). These investigators observed a relatively strong correlation<br />

between measured values of δ 15 N and δ 18 O. A potential benefit of analyzing both the<br />

δ 15 N and δ 18 O of NO3 - is that oxygen isotopic compositions vary systematically with<br />

nitrogen isotopic compositions during denitrification (Kendall 1998). Using the dual-

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