Mongolia vs Saudi Arabia: Nutrient balance — Cropland nitrogen
Nutrient balance — Cropland nitrogen over time
- Mongolia
- Saudi Arabia
How they compare
Mongolia currently reports 202,579 t against 196,865 t in Saudi Arabia, a difference of 5,714 t.
The two have swapped places 4 times across 63 shared years of data; in 1961 it was Mongolia ahead.
Mongolia ranks 46th and Saudi Arabia ranks 49th of 201 countries.
Across the 7 decades both report, Mongolia averaged higher in 2 and Saudi Arabia in 5.
Head to head by decade
| Decade | Mongolia | Saudi Arabia | Difference | Ahead |
|---|---|---|---|---|
| 1960s | 64,026 t | -4,212 t | 68,238 t | Mongolia |
| 1970s | 73,201 t | 1,351 t | 71,850 t | Mongolia |
| 1980s | 81,100 t | 116,069 t | 34,968 t | Saudi Arabia |
| 1990s | 94,766 t | 164,087 t | 69,321 t | Saudi Arabia |
| 2000s | 90,916 t | 174,657 t | 83,742 t | Saudi Arabia |
| 2010s | 139,645 t | 180,576 t | 40,931 t | Saudi Arabia |
| 2020s | 202,160 t | 202,587 t | 427.75 t | Saudi Arabia |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher nutrient balance — cropland nitrogen, Mongolia or Saudi Arabia?
- Mongolia, at 202,579 t against 196,865 t in Saudi Arabia as of 2023.
- What is the difference in nutrient balance — cropland nitrogen between Mongolia and Saudi Arabia?
- 5,714 t, with Mongolia ahead.
- How many years of comparable data are there for Mongolia and Saudi Arabia?
- 63 years are reported by both, from 1961 to 2023.
- How do Mongolia and Saudi Arabia rank globally for nutrient balance — cropland nitrogen?
- Mongolia ranks 46th and Saudi Arabia ranks 49th of 201 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Nutrient balance — 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 (%).