A field study on the impact of the nitrification inhibitor DMPP on nitrous oxide emissions from pasture - Helen Suter
1. A field study on the impact
of the nitrification inhibitor
DMPP on N2O emissions
from a pasture in south
western Victoria
Helen Suter, Humaira Sultana
and Deli Chen
(The University of Melbourne)
Rohan Davies and Matthew Mahoney
(Incitec Pivot)
4. Experimental methodology
• Location : Murroon, south west Victoria
• Average annual rainfall : 660 mm
• Pasture : 2 year old ryegrass seed pasture
• Soil : duplex, silty loam topsoil, pHW 5.5
• Grazing : sheep grazing (prior to trial)
• Plot size : 2 m x 1 m
• Application rate: 40 kg N/ha Source: Google maps
• Start date: 12 April 2010
• End date: 23 December 2010
• Fertilisation events: 7
• Gas collection: manual chambers (23 x 20 cm)
5. Experimental methodology : Data Collection
o Gas – N2O, CO2, CH4
• 3 samples (0, 30, 60 mins)/chamber
• weekly and event driven
• analysed in lab
o Soil
• fortnightly
• NH4+ and NO3-
o Biomass production and N content
• monthly
o Additional data
• climate data
• soil moisture and temperature
6. Results: Daily N2O emissions (April-Oct)
45
control fertiliser application at 40 kg N/ha
40 urea
DMPP
35
Calculated daily N2O (g/ha)
30
25
20 site waterlogged, no sampling
15
10
5
0
7. 35
control fertiliser application at 40 kg N/ha
30
urea
DMPP
25
Calculated daily N 2O (g/ha)
20
site waterlogged, no sampling
Results: 15
Daily N2O
10
emissions and
rainfall (April-Oct) 5
0
40
35
30
Rainfall (mm)
25
20
15
10
5
0
(Total rainfall 522 mm)
8. 35
control fertiliser application at 40 kg N/ha
30
urea
DMPP
25
Calculated daily N 2O (g/ha)
20
site waterlogged, no sampling
Results: 15
Daily N2O
10
emissions and
daily mean 5
maximum
0
temperature
(April-Oct)
30
25
Temperature (oC)
20
15
10
5
0
11. 18
16
14
12 Control
Nitrate -N (kg/ha)
DMPP
10
Urea
8
Results : soil 6
nitrate levels and
4
potential for
2
leaching loss
0
40
35
30
Rainfall (mm)
25
20
15
10
5
0
12. 18
16
14
12 Control
Nitrate -N (kg/ha)
DMPP
10
Urea
8
Results : soil 6
nitrate levels and
4
potential for
2
leaching loss
0
40
Potential for leaching 35
losses reduced with DMPP 30
Rainfall (mm)
25
20
15
10
5
0
13. Results : Dry Matter (DM) production (kg/ha)
Cumulative
Treatment 10-May 7-Jun* 19-Jul 3-Sep 27-Sep 21-Oct (240 kg N
applied)
Control 428 ± 68 106 ± 24 232 ± 45 259 ± 35 256 ± 29 454 ± 46 1736
Urea 699 ± 70 159 ± 9 569 ± 11 876 ± 82 818 ± 33 1027 ± 41 4149
Urea + DMPP 748 ± 97 207 ± 36 618 ± 71 949 ± 74 754 ± 60 1030 ± 78 4307
% increase in
net DM with 18 89 14 12 -11 1 6
DMPP
(Value is average of 5 reps ± standard error)
* 7 June sampling comes 2 months after fertilisation on 12 April
14. Results : Dry Matter (DM) production (kg/ha)
Cumulative
Treatment 10-May 7-Jun* 19-Jul 3-Sep 27-Sep 21-Oct (240 kg N
applied)
Control 428 ± 68 106 ± 24 232 ± 45 259 ± 35 256 ± 29 454 ± 46 1736
Urea 699 ± 70 159 ± 9 569 ± 11 876 ± 82 818 ± 33 1027 ± 41 4149
Urea + DMPP 748 ± 97 207 ± 36 618 ± 71 949 ± 74 754 ± 60 1030 ± 78 4307
% increase in
net DM with 18 89 14 12 -11 1 6
DMPP
* 7 June sampling comes 2 months after fertilisation on 12 April
15. Conclusions : DMPP impact on N2O emissions from a
pasture
Compared to urea, DMPP :
• delayed formation of NO3--N at some times of the year with greatest impact
during high rainfall periods
– April, June, August
• reduced Net-N2O emissions:
– over a 6 month period by 73%
– at particular times of the year (high temp/rainfall) but not always
• increased the longevity of supply of N for plant growth for 60 days leading to
an 87% increase in DM production (June sampling) compared to urea