Eswatini vs Luxembourg: Leaching — Cropland nitrogen

Eswatini
1,092 t
in 2023
Luxembourg
913.8 t
in 2023
Eswatini rank
158th
Luxembourg rank
160th

Leaching — Cropland nitrogen over time

  • Eswatini
  • Luxembourg
4006008001.0k1.2k196119922023

How they compare

Eswatini currently reports 1,092 t against 913.8 t in Luxembourg, a difference of 178.2 t.

That makes Eswatini's figure about 1.2 times Luxembourg's.

The two have swapped places 1 time across 24 shared years of data; in 2000 it was Luxembourg ahead.

Eswatini ranks 158th and Luxembourg ranks 160th of 201 countries.

Across the 3 decades both report, Eswatini averaged higher in 1 and Luxembourg in 2.

Head to head by decade

Decade Eswatini Luxembourg Difference Ahead
2000s 784.43 t 1,007 t 222.19 t Luxembourg
2010s 931.31 t 1,116 t 184.78 t Luxembourg
2020s 1,133 t 982.87 t 150.19 t Eswatini

Averages of every year both report within each decade.

Frequently asked questions

Which has higher leaching — cropland nitrogen, Eswatini or Luxembourg?
Eswatini, at 1,092 t against 913.8 t in Luxembourg as of 2023.
What is the difference in leaching — cropland nitrogen between Eswatini and Luxembourg?
178.2 t, with Eswatini ahead.
How many years of comparable data are there for Eswatini and Luxembourg?
24 years are reported by both, from 2000 to 2023.
How do Eswatini and Luxembourg rank globally for leaching — cropland nitrogen?
Eswatini ranks 158th and Luxembourg ranks 160th of 201 countries.
Where does this data come from?
Food and Agriculture Organization of the United Nations, published as Leaching — Cropland nitrogen. Statizoid refreshes it automatically from the source and publishes the full history for both places.

Individual pages

About this data

Indicator
Leaching — 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 (%).