Latvia vs South Sudan: Leaching — Cropland nitrogen

Latvia
10,551 t
in 2023
South Sudan
11,941 t
in 2023
Latvia rank
106th
South Sudan rank
104th

Leaching — Cropland nitrogen over time

  • Latvia
  • South Sudan
05.0k10.0k15.0k199220072023

How they compare

South Sudan currently reports 11,941 t against 10,551 t in Latvia, a difference of 1,390 t.

That makes South Sudan's figure about 1.1 times Latvia's.

The two have swapped places 2 times across 12 shared years of data; in 2012 it was South Sudan ahead.

Latvia ranks 106th and South Sudan ranks 104th of 201 countries.

South Sudan has averaged higher in every one of the 2 decades both report.

Head to head by decade

Decade Latvia South Sudan Difference Ahead
2010s 10,225 t 10,486 t 261.89 t South Sudan
2020s 10,945 t 11,700 t 755.08 t South Sudan

Averages of every year both report within each decade.

Frequently asked questions

Which has higher leaching — cropland nitrogen, Latvia or South Sudan?
South Sudan, at 11,941 t against 10,551 t in Latvia as of 2023.
What is the difference in leaching — cropland nitrogen between Latvia and South Sudan?
1,390 t, with South Sudan ahead.
How many years of comparable data are there for Latvia and South Sudan?
12 years are reported by both, from 2012 to 2023.
How do Latvia and South Sudan rank globally for leaching — cropland nitrogen?
Latvia ranks 106th and South Sudan ranks 104th 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 (%).