Mongolia vs Sudan (former): Volatilisation — Cropland nitrogen
Volatilisation — Cropland nitrogen over time
- Mongolia
- Sudan (former)
How they compare
Mongolia currently reports 68,453 t against 63,032 t in Sudan (former), a difference of 5,421 t.
That makes Mongolia's figure about 1.1 times Sudan (former)'s.
The two have swapped places 11 times across 51 shared years of data; in 1961 it was Mongolia ahead.
Mongolia ranks 62nd and Sudan (former) ranks 65th of 201 countries.
Across the 6 decades both report, Mongolia averaged higher in 1 and Sudan (former) in 5.
Head to head by decade
| Decade | Mongolia | Sudan (former) | Difference | Ahead |
|---|---|---|---|---|
| 1960s | 20,027 t | 14,706 t | 5,321 t | Mongolia |
| 1970s | 22,846 t | 22,912 t | 65.48 t | Sudan (former) |
| 1980s | 26,402 t | 32,925 t | 6,523 t | Sudan (former) |
| 1990s | 28,987 t | 34,013 t | 5,026 t | Sudan (former) |
| 2000s | 27,631 t | 51,755 t | 24,124 t | Sudan (former) |
| 2010s | 28,513 t | 69,822 t | 41,309 t | Sudan (former) |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher volatilisation — cropland nitrogen, Mongolia or Sudan (former)?
- Mongolia, at 68,453 t against 63,032 t in Sudan (former) as of 2023.
- What is the difference in volatilisation — cropland nitrogen between Mongolia and Sudan (former)?
- 5,421 t, with Mongolia ahead.
- How many years of comparable data are there for Mongolia and Sudan (former)?
- 51 years are reported by both, from 1961 to 2011.
- How do Mongolia and Sudan (former) rank globally for volatilisation — cropland nitrogen?
- Mongolia ranks 62nd and Sudan (former) ranks 65th of 201 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Volatilisation — Cropland nitrogen. 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 (%).