Table 3: Effect of
ozone in ascending doses on the soil pH and the release of bioavailable forms
of P, Zn, Fe and Mn.
Time of ozonation |
Dose (g.kg-1O3) |
pHa |
M-3 Pb
(ppm) |
DTPAc-Zn
(ppm) |
DTPAc-Fe
(ppm) |
DTPAc-Mn
(ppm) |
Control |
0 |
7.9 |
34 |
0.5 |
16 |
116 |
10 min |
0.5 |
7.75 |
38 |
0.9 |
24 |
24d |
13 min |
0.7e |
7.7 |
37 |
0.8 |
21 |
141 |
15 min |
0.8e |
7.8 |
33 |
0.7 |
17 |
115 |
17 min |
1.1e |
7.8 |
38 |
0.7 |
20 |
123 |
20 min |
1.2e |
7.8 |
37 |
0.7 |
22 |
24d |
25 min |
1.4e |
7.8 |
36 |
0.7 |
21 |
42d |
aThe
soil ozonation did not show a correlation between
ozone doses and variation in soil pH.
bBioavailable form of phosphorous in response to ozonation
was measured with the Mehlich-3 method, and showed no correlation between ozone
dose and M-3 P.
cBioavailable forms of zinc, iron, and manganese in response to ozonation were measured using the DTPA extraction method.
No correlation was detected between ozone dose and the variations in DTPA forms
of Zn, Fe or Mn.
dDifferences between DTPA-Mn numbers are of
an order of ppm. This is a normal and non-significant difference between soil
samples from the same soil.
eDifference in dosage increase in response to the same increase in ozonation duration (2 min) is due to the difference in
ozone absorption by the soil samples. This fluctuation depended on how tightly
submerged the ozone diffuser was in the soil sample. Doses presented are
averages of dosage measurements of 12 samples of the same ozonation
duration.