Lebanon vs Suriname: Biological fixation — Cropland nitrogen
Biological fixation — Cropland nitrogen over time
- Lebanon
- Suriname
How they compare
Suriname currently reports 1,306 t against 1,117 t in Lebanon, a difference of 189 t.
That makes Suriname's figure about 1.2 times Lebanon's.
The two have swapped places 9 times across 63 shared years of data; in 1961 it was Lebanon ahead.
Lebanon ranks 139th and Suriname ranks 136th of 191 countries.
Across the 7 decades both report, Lebanon averaged higher in 2 and Suriname in 5.
Head to head by decade
| Decade | Lebanon | Suriname | Difference | Ahead |
|---|---|---|---|---|
| 1960s | 1,142 t | 897.48 t | 244.57 t | Lebanon |
| 1970s | 1,221 t | 1,262 t | 41.26 t | Suriname |
| 1980s | 1,227 t | 1,895 t | 667.64 t | Suriname |
| 1990s | 2,472 t | 1,546 t | 926.01 t | Lebanon |
| 2000s | 1,175 t | 1,249 t | 74.11 t | Suriname |
| 2010s | 1,134 t | 1,532 t | 398.08 t | Suriname |
| 2020s | 1,206 t | 1,393 t | 186.77 t | Suriname |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher biological fixation — cropland nitrogen, Lebanon or Suriname?
- Suriname, at 1,306 t against 1,117 t in Lebanon as of 2023.
- What is the difference in biological fixation — cropland nitrogen between Lebanon and Suriname?
- 189 t, with Suriname ahead.
- How many years of comparable data are there for Lebanon and Suriname?
- 63 years are reported by both, from 1961 to 2023.
- How do Lebanon and Suriname rank globally for biological fixation — cropland nitrogen?
- Lebanon ranks 139th and Suriname ranks 136th of 191 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Biological fixation — 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 (%).