China vs Eastern Asia: Leaching — Cropland nitrogen
Leaching — Cropland nitrogen over time
- China
- Eastern Asia
How they compare
Eastern Asia currently reports 3.66 million t against 3.52 million t in China, a difference of 148,560 t.
Across all 63 years both countries report, Eastern Asia has been ahead every year.
China ranks 1st and Eastern Asia ranks 3rd of 201 countries.
Eastern Asia has averaged higher in every one of the 7 decades both report.
Head to head by decade
| Decade | China | Eastern Asia | Difference | Ahead |
|---|---|---|---|---|
| 1960s | 500,348 t | 630,290 t | 129,942 t | Eastern Asia |
| 1970s | 1.01 million t | 1.20 million t | 181,990 t | Eastern Asia |
| 1980s | 2.03 million t | 2.25 million t | 220,128 t | Eastern Asia |
| 1990s | 2.97 million t | 3.16 million t | 196,803 t | Eastern Asia |
| 2000s | 3.57 million t | 3.72 million t | 151,217 t | Eastern Asia |
| 2010s | 3.96 million t | 4.10 million t | 148,000 t | Eastern Asia |
| 2020s | 3.53 million t | 3.68 million t | 150,035 t | Eastern Asia |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher leaching — cropland nitrogen, China or Eastern Asia?
- Eastern Asia, at 3.66 million t against 3.52 million t in China as of 2023.
- What is the difference in leaching — cropland nitrogen between China and Eastern Asia?
- 148,560 t, with Eastern Asia ahead.
- How many years of comparable data are there for China and Eastern Asia?
- 63 years are reported by both, from 1961 to 2023.
- How do China and Eastern Asia rank globally for leaching — cropland nitrogen?
- China ranks 1st and Eastern Asia ranks 3rd of 201 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Leaching — 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 (%).