Madagascar vs Switzerland: Manure applied β Cropland nitrogen
Manure applied β Cropland nitrogen over time
- Madagascar
- Switzerland
How they compare
Switzerland currently reports 50,453 t against 49,945 t in Madagascar, a difference of 508 t.
Across all 63 years both countries report, Switzerland has been ahead every year.
Madagascar ranks 79th and Switzerland ranks 78th of 200 countries.
Switzerland has averaged higher in every one of the 7 decades both report.
Head to head by decade
| Decade | Madagascar | Switzerland | Difference | Ahead |
|---|---|---|---|---|
| 1960s | 21,408 t | 62,186 t | 40,778 t | Switzerland |
| 1970s | 24,389 t | 67,038 t | 42,649 t | Switzerland |
| 1980s | 35,947 t | 65,340 t | 29,393 t | Switzerland |
| 1990s | 38,253 t | 58,203 t | 19,949 t | Switzerland |
| 2000s | 30,474 t | 53,326 t | 22,852 t | Switzerland |
| 2010s | 41,712 t | 52,065 t | 10,354 t | Switzerland |
| 2020s | 46,847 t | 50,531 t | 3,684 t | Switzerland |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher manure applied β cropland nitrogen, Madagascar or Switzerland?
- Switzerland, at 50,453 t against 49,945 t in Madagascar as of 2023.
- What is the difference in manure applied β cropland nitrogen between Madagascar and Switzerland?
- 508 t, with Switzerland ahead.
- How many years of comparable data are there for Madagascar and Switzerland?
- 63 years are reported by both, from 1961 to 2023.
- How do Madagascar and Switzerland rank globally for manure applied β cropland nitrogen?
- Madagascar ranks 79th and Switzerland ranks 78th of 200 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Manure applied β 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 (%).