China, Hong Kong SAR vs Montenegro: Leaching — Cropland nitrogen per unit area
Leaching — Cropland nitrogen per unit area over time
- China, Hong Kong SAR
- Montenegro
How they compare
China, Hong Kong SAR currently reports 108.02 kg/ha against 68.61 kg/ha in Montenegro, a difference of 39.41 kg/ha.
That makes China, Hong Kong SAR's figure about 1.6 times Montenegro's.
The two have swapped places 1 time across 18 shared years of data; in 2006 it was Montenegro ahead.
China, Hong Kong SAR ranks 4th and Montenegro ranks 6th of 186 countries.
Across the 3 decades both report, China, Hong Kong SAR averaged higher in 1 and Montenegro in 2.
Head to head by decade
| Decade | China, Hong Kong SAR | Montenegro | Difference | Ahead |
|---|---|---|---|---|
| 2000s | 55.96 kg/ha | 94.92 kg/ha | 38.96 kg/ha | Montenegro |
| 2010s | 76.36 kg/ha | 79.95 kg/ha | 3.59 kg/ha | Montenegro |
| 2020s | 108.38 kg/ha | 68.76 kg/ha | 39.62 kg/ha | China, Hong Kong SAR |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher leaching — cropland nitrogen per unit area, China, Hong Kong SAR or Montenegro?
- China, Hong Kong SAR, at 108.02 kg/ha against 68.61 kg/ha in Montenegro as of 2023.
- What is the difference in leaching — cropland nitrogen per unit area between China, Hong Kong SAR and Montenegro?
- 39.41 kg/ha, with China, Hong Kong SAR ahead.
- How many years of comparable data are there for China, Hong Kong SAR and Montenegro?
- 18 years are reported by both, from 2006 to 2023.
- How do China, Hong Kong SAR and Montenegro rank globally for leaching — cropland nitrogen per unit area?
- China, Hong Kong SAR ranks 4th and Montenegro ranks 6th of 186 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Leaching — 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 (%).