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Effect of different nitrogen rates and use of DMPP nitrification inhibitor on N2O emissions from maize in sub-tropical Ferrosols. Kingaroy, Queensland, 2011-2012 [Theme 1: Inhibitors for reducing emissions]

Data Set Citation

De Antoni Migliorati M of Institute for Future Environments, Queensland University of Technology. Effect of different nitrogen rates and use of DMPP nitrification inhibitor on N2O emissions from maize in sub-tropical Ferrosols. Kingaroy, Queensland, 2011-2012 [Theme 1: Inhibitors for reducing emissions].
datalibrarian.24.11 (http://www.n2o.net.au/knb/metacat/datalibrarian.24.11/html).

Metadata download:
Ecological Metadata Language (EML) File
Data Table
Licence
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Data Set Owner(s):
Individual:
Mr. Massimiliano De Antoni Migliorati
Organization:
Institute for Future Environments, Queensland University of Technology
Position:
PhD Student
Address:
2 George Street,
Brisbane,
QLD 4001
Australia
Phone:
07 3138 1360 (voice)
Email Address:
max.deantonimigliorati.qut.edu.au
Associated Party
Individual:
Ms. Siobhann McCafferty
Organization:
Institute for Future Environments, Queensland University of Technology
Position:
Data Librarian
Address:
2 George Street,
Brisbane,
QLD 4001
Australia
Phone:
+61 7 3138 0457 (voice)
Email Address:
siobhann.mccafferty@qut.edu.au
Role:
Custodian/Steward
Abstract

The objective of this experiment was to investigate the role of different N fertilization rates and the use of the nitrification inhibitor 3,4-dimethylpyrazole phosphate (DMPP, commercially sold as Entec) in reducing N2O emissions from subtropical maize systems over summer. At the same time, particular attention was given to the yield response shown by the different treatments, in order to evaluate the respective economical sustainability and N2O intensity. The field experiment was set up in Kingaroy ( S-E QLD), on a euchrozems Ferrosol soil, using a randomized complete three-block design (three replicates per treatment). The four treatments encompassed three different fertilization rates and two types of Urea (conventional and DMPP urea): control treatment (L1: 40 kg-N ha-1 -conv. urea), sub-optimal N rate (L2: 100 kg-N ha-1 –conv. urea) and optimal N rate (L3: 160 kg-N ha-1 –conv. urea, L4: 160 kg-N ha-1 –DMPP urea). The N2O emissions were measured from planting (December 20th 2011) to harvest (June 20th 2012) with a fully automated greenhouse gas measuring system. In order to gain optimum understanding of the dynamics influencing greenhouse gas production and release in agricultural soils, the air temperature and the soil moisture inside the measuring chambers were constantly monitored. To compare the "environmental" performances of the four treatments with agronomical sustainability grain yields were also determined.

Keywords
  • N2O
  • Maize
  • Urea
  • DMPP
  • Nitrification Inhibitor
  • Auto Chambers
  • Ferrosols
  • Kingaroy
  • QLD
anzsrc-for
  • 0502
  • 0799
License and Usage Rights

Please contact the owner for permission to use this data.

Geographic Coverage
Geographic Description:
Bjelke Petersen Research Station, Kingaroy, Queensland.
Bounding Coordinates:
West:  
151.828671  degrees
East:  
151.828671  degrees
North:  
-26.58183  degrees
South:  
-26.58183  degrees
Temporal Coverage
Begin:
2010-12-20
End:
2012-06-20
Contact(s)
Individual:
Mr. Massimiliano De Antoni Migliorati
Organization:
Institute for Future Environments, Queensland University of Technology
Position:
PhD Student
Address:
2 George Street,
Brisbane,
QLD 4001
Australia
Phone:
07 3138 1360 (voice)
Email Address:
max.deantonimigliorati.qut.edu.au
Methods Info
Step 1:
Description:
Automated closed-chamber system
The soil–atmosphere exchange of N2O was measured with a mobile fully automated measuring system.Sampling chambers (50cm x 50cm x 15cm) were fixed on stainless steel frames. The lids of the chambers were opened and closed automatically with pneumatic devices. During the closing period air samples from each chamber were taken alternately and injected towards the analytical devices. Soil-atmosphere exchange measurements were made at 3 subplots for each treatment within the split-plot design. Changes in N2O concentration after chamber closure were measured with a gas chromatograph (Texas Instruments SRI 8610C, Torrance/USA) equipped with a 63Ni electron capture detector (ECD) for N2O analysis.
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