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comparable to those in water draining slurry treated or sheep-grazed drained plots<br />

(Vinten et al., 2004). The PO 4<br />

-P concentrations draining from all treatments were<br />

very low, comparable to those draining from arable fields, but the values were lowest<br />

from the ochre treatment. The ratio of P to NH 4<br />

-N in the drainage water w<strong>as</strong> similar<br />

to that in the input slurry.<br />

0.8<br />

EC/ECinput<br />

160<br />

DOC mg/L<br />

EC/EC in<br />

0.6<br />

0.4<br />

0.2<br />

DOC (mg/L)<br />

120<br />

80<br />

40<br />

0.0<br />

0 100 200 300<br />

mm drainage<br />

0<br />

0 100 200 300<br />

mm drainage<br />

log [E.coli]<br />

cfu/100mL<br />

5<br />

4<br />

3<br />

2<br />

1<br />

log [E.coli] cfu/100mL<br />

0 100 200 300<br />

mm drainage<br />

ammonium-N (mg/L)<br />

8<br />

6<br />

4<br />

2<br />

0<br />

NH 4-N mg/L<br />

0 100 200 300<br />

mm drainage<br />

NO 3-N mg/L<br />

PO 4-P mg/L<br />

nitrate-N (mg/L)<br />

80<br />

60<br />

40<br />

20<br />

0<br />

0 100 200 300<br />

mm drainage<br />

phosphate-P (mg/L)<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0.0<br />

subsoil<br />

Ochre<br />

0 100 200 300<br />

mm drainage<br />

Figure 2: Lysimeter leachate concentrations of EC, DOC, E. coli, NH 4<br />

-N,<br />

NO 3<br />

-N and PO 4<br />

-P for control (40 cm of subsoil) and ochre (10 cm of<br />

ochre and 30 cm of subsoil) lysimeters<br />

256

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