Kazakhstan vs Mongolia: Volatilisation — Cropland nitrogen

Kazakhstan
68,832 t
in 2023
Mongolia
68,453 t
in 2023
Kazakhstan rank
61st
Mongolia rank
62nd

Volatilisation — Cropland nitrogen over time

  • Kazakhstan
  • Mongolia
25.0k50.0k75.0k100.0k125.0k196119922023

How they compare

Kazakhstan currently reports 68,832 t against 68,453 t in Mongolia, a difference of 379 t.

The two have swapped places 2 times across 32 shared years of data; in 1992 it was Kazakhstan ahead.

Kazakhstan ranks 61st and Mongolia ranks 62nd of 201 countries.

Kazakhstan has averaged higher in every one of the 4 decades both report.

Head to head by decade

Decade Kazakhstan Mongolia Difference Ahead
1990s 75,172 t 29,098 t 46,074 t Kazakhstan
2000s 47,561 t 27,631 t 19,930 t Kazakhstan
2010s 70,854 t 44,677 t 26,177 t Kazakhstan
2020s 69,527 t 67,024 t 2,503 t Kazakhstan

Averages of every year both report within each decade.

Frequently asked questions

Which has higher volatilisation — cropland nitrogen, Kazakhstan or Mongolia?
Kazakhstan, at 68,832 t against 68,453 t in Mongolia as of 2023.
What is the difference in volatilisation — cropland nitrogen between Kazakhstan and Mongolia?
379 t, with Kazakhstan ahead.
How many years of comparable data are there for Kazakhstan and Mongolia?
32 years are reported by both, from 1992 to 2023.
How do Kazakhstan and Mongolia rank globally for volatilisation — cropland nitrogen?
Kazakhstan ranks 61st and Mongolia ranks 62nd 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

Indicator
Volatilisation — Cropland nitrogen
Unit
t
Source
Food and Agriculture Organization of the United Nations
Licence
CC BY-NC-SA 3.0 IGO (FAO)
Coverage
233 places, 13,500 data points, 1961–2023
Last refreshed

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 (%).