China, mainland vs Russian Federation: Seed β Cropland nitrogen
Seed β Cropland nitrogen over time
- China, mainland
- Russian Federation
How they compare
China, mainland currently reports 397,591 t against 311,405 t in Russian Federation, a difference of 86,186 t.
That makes China, mainland's figure about 1.3 times Russian Federation's.
The two have swapped places 2 times across 32 shared years of data; in 1992 it was China, mainland ahead.
China, mainland ranks 3rd and Russian Federation ranks 5th of 201 countries.
China, mainland has averaged higher in every one of the 4 decades both report.
Head to head by decade
| Decade | China, mainland | Russian Federation | Difference | Ahead |
|---|---|---|---|---|
| 1990s | 401,040 t | 327,820 t | 73,219 t | China, mainland |
| 2000s | 394,153 t | 273,174 t | 120,979 t | China, mainland |
| 2010s | 378,663 t | 319,745 t | 58,918 t | China, mainland |
| 2020s | 395,572 t | 309,645 t | 85,928 t | China, mainland |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher seed β cropland nitrogen, China, mainland or Russian Federation?
- China, mainland, at 397,591 t against 311,405 t in Russian Federation as of 2023.
- What is the difference in seed β cropland nitrogen between China, mainland and Russian Federation?
- 86,186 t, with China, mainland ahead.
- How many years of comparable data are there for China, mainland and Russian Federation?
- 32 years are reported by both, from 1992 to 2023.
- How do China, mainland and Russian Federation rank globally for seed β cropland nitrogen?
- China, mainland ranks 3rd and Russian Federation ranks 5th of 201 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Seed 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 (%).