Belgium-Luxembourg vs Nicaragua: Atmospheric deposition — Cropland nitrogen
Atmospheric deposition — Cropland nitrogen over time
- Belgium-Luxembourg
- Nicaragua
How they compare
Nicaragua currently reports 7,995 t against 7,864 t in Belgium-Luxembourg, a difference of 131 t.
The two have swapped places 1 time across 39 shared years of data; in 1961 it was Belgium-Luxembourg ahead.
Belgium-Luxembourg ranks 100th and Nicaragua ranks 99th of 186 countries.
Belgium-Luxembourg has averaged higher in every one of the 4 decades both report.
Head to head by decade
| Decade | Belgium-Luxembourg | Nicaragua | Difference | Ahead |
|---|---|---|---|---|
| 1960s | 9,670 t | 2,208 t | 7,463 t | Belgium-Luxembourg |
| 1970s | 10,847 t | 3,083 t | 7,763 t | Belgium-Luxembourg |
| 1980s | 7,842 t | 3,745 t | 4,097 t | Belgium-Luxembourg |
| 1990s | 8,259 t | 6,228 t | 2,031 t | Belgium-Luxembourg |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher atmospheric deposition — cropland nitrogen, Belgium-Luxembourg or Nicaragua?
- Nicaragua, at 7,995 t against 7,864 t in Belgium-Luxembourg as of 2023.
- What is the difference in atmospheric deposition — cropland nitrogen between Belgium-Luxembourg and Nicaragua?
- 131 t, with Nicaragua ahead.
- How many years of comparable data are there for Belgium-Luxembourg and Nicaragua?
- 39 years are reported by both, from 1961 to 1999.
- How do Belgium-Luxembourg and Nicaragua rank globally for atmospheric deposition — cropland nitrogen?
- Belgium-Luxembourg ranks 100th and Nicaragua ranks 99th of 186 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Atmospheric deposition — Cropland nitrogen. Statizoid refreshes it automatically from the source and publishes the full history for both places.
Individual pages
About this data
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 (%).