Chad vs Mongolia: Input — Cropland nitrogen

Chad
211,950 t
in 2023
Mongolia
215,232 t
in 2023
Chad rank
86th
Mongolia rank
85th

Input — Cropland nitrogen over time

  • Chad
  • Mongolia
50.0k100.0k150.0k200.0k250.0k196119922023

How they compare

Mongolia currently reports 215,232 t against 211,950 t in Chad, a difference of 3,282 t.

The two have swapped places 4 times across 63 shared years of data; in 1961 it was Mongolia ahead.

Chad ranks 86th and Mongolia ranks 85th of 201 countries.

Across the 7 decades both report, Chad averaged higher in 2 and Mongolia in 5.

Head to head by decade

Decade Chad Mongolia Difference Ahead
1960s 48,224 t 69,698 t 21,474 t Mongolia
1970s 52,218 t 80,769 t 28,551 t Mongolia
1980s 53,484 t 95,205 t 41,721 t Mongolia
1990s 78,516 t 102,750 t 24,234 t Mongolia
2000s 107,250 t 94,984 t 12,267 t Chad
2010s 181,528 t 149,557 t 31,971 t Chad
2020s 207,016 t 214,712 t 7,696 t Mongolia

Averages of every year both report within each decade.

Frequently asked questions

Which has higher input — cropland nitrogen, Chad or Mongolia?
Mongolia, at 215,232 t against 211,950 t in Chad as of 2023.
What is the difference in input — cropland nitrogen between Chad and Mongolia?
3,282 t, with Mongolia ahead.
How many years of comparable data are there for Chad and Mongolia?
63 years are reported by both, from 1961 to 2023.
How do Chad and Mongolia rank globally for input — cropland nitrogen?
Chad ranks 86th and Mongolia ranks 85th of 201 countries.
Where does this data come from?
Food and Agriculture Organization of the United Nations, published as Input — Cropland nitrogen. Statizoid refreshes it automatically from the source and publishes the full history for both places.

Individual pages

About this data

Indicator
Input — 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 (%).