Key Messages
- Local information required
- Knowledge gap- how big are the losses in our region
- Production loss vs greenhouse gas impact
- Losses via volatalisation are far less from surface applied area than previously thought
- Losses from denitrification are not only in the form of N, O
- Nitrogen use efficiency is ordinary
- Increase soil C can increase N2O (much worse)
- That N2O equals roughly 300 times C02
- Crops in 50% efficiency. Livestock – 30% off
- N in OM has to be processed through the microbial population before it is available and many factors drive that especially C:N balance
- If lots of extra carbon can lock up N
- Different forms of carbon – POC, HOC, ROC will influence possible losses
- Volatilizations NOT a big even in low pH, temp, NH4 plus cone plus water (if one ore more is missing)
- Denitrification pathway- if severe water logging goes straight to N2, not only as N2 loss however as more O2 appears, get increase N20 less N2
- Lots of opportunity to be more efficient
- Inhibitors may have a plan in high water logged soils as they dry out
- If can improve pore space then the possible time in the damaged zone (>60% water in pore space) is reduced
- N2O 300x more impact than CO2
- Greater risk in high RF and water logged conditions
- Split N and Inhibitors can reduce N2O
- 10% volatalisation- ROT NH2+ NOT N2O
- Worst case in low- M Rainfall current practice systems
- N2) @ 65-85% water filled pore space N2 > 85%
- Its all too hard
- The N2O losses in lower rainfall are insignificant
- Unless there is an N2O emission cost the simple remedy is to increase N rate
- N rate is a key driver of N2O emissions
- Variability is high
- It’s a fine line between N20 and N2 losses
- Claimed efficiency of inhibitors doesn’t match reality
- Match supply with demand
- Volatalisation losses of applied area are low
Potential Applications
- Matching N timing and rate with plant demonstration and water logging events
- Ammonium uptake referencing plants have a role
- Not much in inhibitors- time spent better elsewhere
- Getting N Rates right is important
- Spreading SOA on high CaCO3 soils can result in volatile losses
- Application timing based on weather events (e.g. what to spread before 10mm not 50mm)
- Inhibitors (cost vs benefit)
- In crop application
- Local information required
- Fill research gaps in cotton system/ soil types- NUE
- Can demonstrate we can make improvements in N2O emissions between drained (e.g. raised bed) and un-drained land
- Working out how to introduce carbon into the system to promote improved pore space- but not allow it to drive the increase in N2O by use of inhibitors, stop water logging, make ‘bucket’ bigger
- Improve water use by improved pasture management- perennials – take some highly water logged areas out of crop into pasture
- Timing of N application can be tailored to conditions e.g. water in soil, avoid before rain soil type
- Catch crops
- Soil structure activities are good- e.g. gypsum, raised beds, drainage, deepripping, spading
- Improving inhibitor efficiency? Recognising when they will work
- Decision tools, enhance effectiveness and cost benefit of costly inhibitors
- Regional alerts on N2O emissions
- Ag Machinery efficiency (diesel) exhaust emissions
Knowledge Gaps
- How to measure water logging squeeginess test)
- Measuring N2 release
- Gaps in the whole N audit
- C/N ratios of residues
- Bullshit peddlers in the NUE space
- If decrease waterlogging by amelioration- how important is it?
- Microbial activity through the soil profile
- Drainage
- Pulse crops/ pasture legumes are included in emissions??
- Timing N
- Liquids – uptake/ losses
- Local data on inhibitors
- Understanding in detail loss pathways and mechanism for loss
- Role of inhibitors- when, where, type, rate, economics
- Application of research on when to apply N to create new messages e.g.- dairy model? Model (create RoT)
- How different sources (e.g. compost, stubble) contribute to the ‘pools’ over time
- How to control the losses of N2O from urine- e.g. diets
- How might we ‘catch crops?’
- What are realistic efficiency targets what should be aiming for?
- Applications for high rainfall pasture areas
- Water filled pore space- is this water logging?
- Confirm losses
- Confirm breakdown periods and pathways- give e.g. 20mm on dry or wet soils as case studies
- Performance of inhibitors,
- Cost/ benefit calculator
- Greenhouse gas emissions impact
- Modeling tool to learn?
- What’s happening to N- local (N cycle)- seek clarity Baldock (extra N) S. N budget (re costings)