North Macedonia vs Papua New Guinea: Biological fixation — Cropland nitrogen
Biological fixation — Cropland nitrogen over time
- North Macedonia
- Papua New Guinea
How they compare
Papua New Guinea currently reports 835.64 t against 798.24 t in North Macedonia, a difference of 37.4 t.
The two have swapped places 1 time across 32 shared years of data; in 1992 it was North Macedonia ahead.
North Macedonia ranks 136th and Papua New Guinea ranks 133rd of 176 countries.
Across the 4 decades both report, North Macedonia averaged higher in 3 and Papua New Guinea in 1.
Head to head by decade
| Decade | North Macedonia | Papua New Guinea | Difference | Ahead |
|---|---|---|---|---|
| 1990s | 1,363 t | 489.18 t | 873.69 t | North Macedonia |
| 2000s | 1,060 t | 566.72 t | 493.76 t | North Macedonia |
| 2010s | 873.24 t | 751.42 t | 121.81 t | North Macedonia |
| 2020s | 797.38 t | 835.81 t | 38.43 t | Papua New Guinea |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher biological fixation — cropland nitrogen, North Macedonia or Papua New Guinea?
- Papua New Guinea, at 835.64 t against 798.24 t in North Macedonia as of 2023.
- What is the difference in biological fixation — cropland nitrogen between North Macedonia and Papua New Guinea?
- 37.4 t, with Papua New Guinea ahead.
- How many years of comparable data are there for North Macedonia and Papua New Guinea?
- 32 years are reported by both, from 1992 to 2023.
- How do North Macedonia and Papua New Guinea rank globally for biological fixation — cropland nitrogen?
- North Macedonia ranks 136th and Papua New Guinea ranks 133rd of 176 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 (%).