Myanmar vs Russian Federation: Volatilisation — Cropland nitrogen per unit area
Volatilisation — Cropland nitrogen per unit area over time
- Myanmar
- Russian Federation
How they compare
Russian Federation currently reports 8.17 kg/ha against 8.1 kg/ha in Myanmar, a difference of 0.07 kg/ha.
The two have swapped places 2 times across 32 shared years of data; in 1992 it was Russian Federation ahead.
Myanmar ranks 142nd and Russian Federation ranks 141st of 201 countries.
Myanmar has averaged higher in every one of the 4 decades both report.
Head to head by decade
| Decade | Myanmar | Russian Federation | Difference | Ahead |
|---|---|---|---|---|
| 1990s | 8.79 kg/ha | 7.55 kg/ha | 1.24 kg/ha | Myanmar |
| 2000s | 8.79 kg/ha | 5.32 kg/ha | 3.48 kg/ha | Myanmar |
| 2010s | 13.11 kg/ha | 6.07 kg/ha | 7.04 kg/ha | Myanmar |
| 2020s | 11.45 kg/ha | 7.89 kg/ha | 3.56 kg/ha | Myanmar |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher volatilisation — cropland nitrogen per unit area, Myanmar or Russian Federation?
- Russian Federation, at 8.17 kg/ha against 8.1 kg/ha in Myanmar as of 2023.
- What is the difference in volatilisation — cropland nitrogen per unit area between Myanmar and Russian Federation?
- 0.07 kg/ha, with Russian Federation ahead.
- How many years of comparable data are there for Myanmar and Russian Federation?
- 32 years are reported by both, from 1992 to 2023.
- How do Myanmar and Russian Federation rank globally for volatilisation — cropland nitrogen per unit area?
- Myanmar ranks 142nd and Russian Federation ranks 141st of 201 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Volatilisation — Cropland nitrogen per unit area. Statizoid refreshes it automatically from the source and publishes the full history for both places.
Individual pages
About this data
The Cropland Nutrient balance domain contains information on the flows of nitrogen, phosphorus, and potassium from mineral fertilizer, manure applied, atmospheric deposition, crop removal, and biological fixation over cropland and per unit area of cropland. The flows are aggregated to total inputs and total outputs, from which the overall nutrient balance and nutrient use efficiency on cropland are calculated. Statistics are disseminated in units of tonnes and in kg/ha, as appropriate. Nutrient use efficiency is expressed as a fraction (%).