Belgium vs China: Seed — Cropland potassium per unit area

Belgium
0.8965 kg/ha
in 2023
China
0.8933 kg/ha
in 2023
Belgium rank
25th
China rank
26th

Seed — Cropland potassium per unit area over time

  • Belgium
  • China
00.250.50.751196119922023

How they compare

Belgium currently reports 0.8965 kg/ha against 0.8933 kg/ha in China, a difference of 0.0032 kg/ha.

The two have swapped places 11 times across 24 shared years of data; in 2000 it was China ahead.

Belgium ranks 25th and China ranks 26th of 201 countries.

Across the 3 decades both report, Belgium averaged higher in 2 and China in 1.

Head to head by decade

Decade Belgium China Difference Ahead
2000s 0.8985 kg/ha 0.8692 kg/ha 0.0293 kg/ha Belgium
2010s 0.8697 kg/ha 0.8333 kg/ha 0.0364 kg/ha Belgium
2020s 0.8648 kg/ha 0.8962 kg/ha 0.0314 kg/ha China

Averages of every year both report within each decade.

Frequently asked questions

Which has higher seed — cropland potassium per unit area, Belgium or China?
Belgium, at 0.8965 kg/ha against 0.8933 kg/ha in China as of 2023.
What is the difference in seed — cropland potassium per unit area between Belgium and China?
0.0032 kg/ha, with Belgium ahead.
How many years of comparable data are there for Belgium and China?
24 years are reported by both, from 2000 to 2023.
How do Belgium and China rank globally for seed — cropland potassium per unit area?
Belgium ranks 25th and China ranks 26th of 201 countries.
Where does this data come from?
Food and Agriculture Organization of the United Nations, published as Seed — Cropland potassium per unit area. Statizoid refreshes it automatically from the source and publishes the full history for both places.

Individual pages

About this data

Indicator
Seed — Cropland potassium per unit area
Unit
kg/ha
Source
Food and Agriculture Organization of the United Nations
Licence
CC BY-NC-SA 3.0 IGO (FAO)
Coverage
233 places, 13,483 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 (%).