China, mainland vs Lithuania: Seed — Cropland nitrogen per unit area
Seed — Cropland nitrogen per unit area over time
- China, mainland
- Lithuania
How they compare
Lithuania currently reports 3.38 kg/ha against 3.12 kg/ha in China, mainland, a difference of 0.26 kg/ha.
That makes Lithuania's figure about 1.1 times China, mainland's.
The two have swapped places 13 times across 32 shared years of data; in 1992 it was China, mainland ahead.
China, mainland ranks 12th and Lithuania ranks 9th of 201 countries.
Across the 4 decades both report, China, mainland averaged higher in 1 and Lithuania in 3.
Head to head by decade
| Decade | China, mainland | Lithuania | Difference | Ahead |
|---|---|---|---|---|
| 1990s | 3.08 kg/ha | 2.83 kg/ha | 0.2481 kg/ha | China, mainland |
| 2000s | 2.97 kg/ha | 3.32 kg/ha | 0.3456 kg/ha | Lithuania |
| 2010s | 2.89 kg/ha | 3.22 kg/ha | 0.332 kg/ha | Lithuania |
| 2020s | 3.1 kg/ha | 3.15 kg/ha | 0.0498 kg/ha | Lithuania |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher seed — cropland nitrogen per unit area, China, mainland or Lithuania?
- Lithuania, at 3.38 kg/ha against 3.12 kg/ha in China, mainland as of 2023.
- What is the difference in seed — cropland nitrogen per unit area between China, mainland and Lithuania?
- 0.26 kg/ha, with Lithuania ahead.
- How many years of comparable data are there for China, mainland and Lithuania?
- 32 years are reported by both, from 1992 to 2023.
- How do China, mainland and Lithuania rank globally for seed — cropland nitrogen per unit area?
- China, mainland ranks 12th and Lithuania ranks 9th of 201 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Seed — Cropland nitrogen per unit area. 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 (%).