Mongolia vs New Zealand: Atmospheric deposition — Cropland nitrogen
Atmospheric deposition — Cropland nitrogen over time
- Mongolia
- New Zealand
How they compare
Mongolia currently reports 2,014 t against 1,735 t in New Zealand, a difference of 279 t.
That makes Mongolia's figure about 1.2 times New Zealand's.
Across all 63 years both countries report, Mongolia has been ahead every year.
Mongolia ranks 128th and New Zealand ranks 130th of 186 countries.
Mongolia has averaged higher in every one of the 7 decades both report.
Head to head by decade
| Decade | Mongolia | New Zealand | Difference | Ahead |
|---|---|---|---|---|
| 1960s | 1,827 t | 568.87 t | 1,258 t | Mongolia |
| 1970s | 3,294 t | 728.67 t | 2,565 t | Mongolia |
| 1980s | 5,209 t | 732.79 t | 4,476 t | Mongolia |
| 1990s | 4,619 t | 913.35 t | 3,706 t | Mongolia |
| 2000s | 2,218 t | 1,202 t | 1,016 t | Mongolia |
| 2010s | 2,236 t | 1,685 t | 550.69 t | Mongolia |
| 2020s | 2,001 t | 1,766 t | 235.81 t | Mongolia |
Averages of every year both report within each decade.
Frequently asked questions
- Which has higher atmospheric deposition — cropland nitrogen, Mongolia or New Zealand?
- Mongolia, at 2,014 t against 1,735 t in New Zealand as of 2023.
- What is the difference in atmospheric deposition — cropland nitrogen between Mongolia and New Zealand?
- 279 t, with Mongolia ahead.
- How many years of comparable data are there for Mongolia and New Zealand?
- 63 years are reported by both, from 1961 to 2023.
- How do Mongolia and New Zealand rank globally for atmospheric deposition — cropland nitrogen?
- Mongolia ranks 128th and New Zealand ranks 130th of 186 countries.
- Where does this data come from?
- Food and Agriculture Organization of the United Nations, published as Atmospheric deposition — 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 (%).