Gross nitrogen surplus in agriculture decreased.
Agricultural Institute of Slovenia, 2014
1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | ||
---|---|---|---|---|---|---|---|---|---|---|---|
Livestock manure | t N | 40195 | 37637 | 37502 | 38405 | 37646 | 37286 | 37900 | 38655 | 41091 | 40318 |
mineral fertilisers | t N | 38938 | 33376 | 33944 | 32235 | 31296 | 33999 | 34801 | 34380 | 34159 | 34765 |
deposition | t N | 8338 | 8291 | 8064 | 7874 | 7702 | 7414 | 7364 | 7479 | 7634 | 7644 |
biological fixation | t N | 2087 | 2060 | 1890 | 2187 | 1929 | 1914 | 1807 | 1730 | 1471 | 1723 |
seeds and seedlings | t N | 325 | 326 | 308 | 312 | 297 | 282 | 286 | 279 | 298 | 301 |
Total input N | t N | 89961 | 81768 | 81786 | 81091 | 78940 | 80957 | 82213 | 82556 | 84665 | 84771 |
Livestock manure | % | 44.7 | 46 | 45.9 | 47.4 | 47.7 | 46.1 | 46.1 | 46.8 | 48.5 | 47.6 |
mineral fertilisers | % | 43.3 | 40.8 | 41.5 | 39.8 | 39.6 | 42 | 42.3 | 41.6 | 40.3 | 41 |
biological fixation | % | 9.3 | 10.1 | 9.9 | 9.7 | 9.8 | 9.2 | 9 | 9.1 | 9 | 9 |
deposition | % | 2.3 | 2.5 | 2.3 | 2.7 | 2.4 | 2.4 | 2.2 | 2.1 | 1.7 | 2 |
seeds and seedlings | % | 0.4 | 0.4 | 0.4 | 0.4 | 0.4 | 0.3 | 0.3 | 0.3 | 0.4 | 0.4 |
Total input N | % | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 |
2002 | 2003 | 2004 | 2005 | 2006 | 2007 | 2008 | 2009 | 2010 | 2011 | ||
Livestock manure | t N | 42505 | 39672 | 37857 | 38556 | 38814 | 40323 | 38673 | 38667 | 37919 | 36559 |
mineral fertilisers | t N | 33412 | 34501 | 30264 | 29169 | 30383 | 29613 | 25039 | 28202 | 27486 | 27134 |
deposition | t N | 7582 | 7646 | 7358 | 7631 | 7355 | 7477 | 7386 | 7027 | 7242 | 6873 |
biological fixation | t N | 1778 | 1833 | 2096 | 2341 | 2550 | 2523 | 2863 | 3164 | 3050 | 3013 |
seeds and seedlings | t N | 283 | 285 | 282 | 277 | 295 | 293 | 295 | 290 | 274 | 258 |
Total input N | t N | 85603 | 83955 | 77862 | 77977 | 79398 | 80230 | 74256 | 77350 | 75989 | 73837 |
Livestock manure | % | 49.7 | 47.3 | 48.6 | 49.4 | 48.9 | 50.3 | 52.1 | 50 | 49.9 | 49.5 |
mineral fertilisers | % | 39 | 41.1 | 38.9 | 37.4 | 38.3 | 36.9 | 33.7 | 36.5 | 36.2 | 36.7 |
biological fixation | % | 8.9 | 9.1 | 9.5 | 9.8 | 9.3 | 9.3 | 9.9 | 9.1 | 9.5 | 9.3 |
deposition | % | 2.1 | 2.2 | 2.7 | 3 | 3.2 | 3.1 | 3.9 | 4.1 | 4 | 4.1 |
seeds and seedlings | % | 0.3 | 0.3 | 0.4 | 0.4 | 0.4 | 0.4 | 0.4 | 0.4 | 0.4 | 0.3 |
Total input N | % | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 |
2012 | |||||||||||
Livestock manure | t N | 36036 | |||||||||
mineral fertilisers | t N | 26300 | |||||||||
deposition | t N | 7195 | |||||||||
biological fixation | t N | 2904 | |||||||||
seeds and seedlings | t N | 275 | |||||||||
Total input N | t N | 72710 | |||||||||
Livestock manure | % | 49.6 | |||||||||
mineral fertilisers | % | 36.2 | |||||||||
biological fixation | % | 9.9 | |||||||||
deposition | % | 4 | |||||||||
seeds and seedlings | % | 0.4 | |||||||||
Total input N | % | 100 |
Agricultural Institute of Slovenia, 2014
1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | ||
---|---|---|---|---|---|---|---|---|---|---|---|
cereals | t N | 6028 | 6762 | 8417 | 8170 | 7762 | 8579 | 8919 | 7557 | 7968 | 8103 |
vegetables, fruit, ornamental crops | t N | 778 | 829 | 875 | 821 | 916 | 850 | 902 | 831 | 973 | 731 |
dried pulses, root and industrial crops, other harvested crops and others | t N | 1596 | 1752 | 2414 | 2322 | 2376 | 2152 | 2396 | 2480 | 2035 | 1497 |
fodder from arable land | t N | 2760 | 3566 | 5815 | 6051 | 6223 | 6673 | 6709 | 5960 | 4674 | 3929 |
grassland consumption | t N | 17811 | 16712 | 32460 | 29761 | 28330 | 31402 | 30783 | 30940 | 25412 | 26073 |
Nitrogen output - Total | t N | 28973 | 29621 | 49981 | 47125 | 45607 | 49656 | 49709 | 47768 | 41062 | 40333 |
cereals | % | 20.8 | 22.8 | 16.8 | 17.3 | 17 | 17.3 | 17.9 | 15.8 | 19.4 | 20.1 |
vegetables, fruit, ornamental crops | % | 2.7 | 2.8 | 1.8 | 1.7 | 2 | 1.7 | 1.8 | 1.7 | 2.4 | 1.8 |
dried pulses, root and industrial crops, other harvested crops and others | % | 5.5 | 5.9 | 4.8 | 4.9 | 5.2 | 4.3 | 4.8 | 5.2 | 5 | 3.7 |
fodder from arable land | % | 9.5 | 12 | 11.6 | 12.8 | 13.6 | 13.4 | 13.5 | 12.5 | 11.4 | 9.7 |
grassland consumption | % | 61.5 | 56.4 | 64.9 | 63.2 | 62.1 | 63.2 | 61.9 | 64.8 | 61.9 | 64.6 |
Total | % | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 |
2002 | 2003 | 2004 | 2005 | 2006 | 2007 | 2008 | 2009 | 2010 | 2011 | ||
cereals | t N | 9754 | 6432 | 9267 | 9154 | 7934 | 8502 | 9336 | 8542 | 9161 | 9727 |
vegetables, fruit, ornamental crops | t N | 949 | 767 | 1043 | 931 | 886 | 875 | 840 | 874 | 825 | 883 |
dried pulses, root and industrial crops, other harvested crops and others | t N | 1911 | 1523 | 1858 | 1942 | 1741 | 1403 | 1155 | 1206 | 1340 | 1339 |
fodder from arable land | t N | 5019 | 4190 | 5723 | 7039 | 5005 | 5440 | 5703 | 6007 | 5930 | 6096 |
grassland consumption | t N | 32958 | 20670 | 33252 | 35890 | 28877 | 32889 | 34195 | 33822 | 35652 | 31719 |
Nitrogen output - Total | t N | 50591 | 33582 | 51143 | 54956 | 44443 | 49109 | 51229 | 50451 | 52908 | 49764 |
cereals | % | 19.3 | 19.2 | 18.1 | 16.7 | 17.9 | 17.3 | 18.2 | 16.9 | 17.3 | 19.5 |
vegetables, fruit, ornamental crops | % | 1.9 | 2.3 | 2 | 1.7 | 2 | 1.8 | 1.6 | 1.7 | 1.6 | 1.8 |
dried pulses, root and industrial crops, other harvested crops and others | % | 3.8 | 4.5 | 3.6 | 3.5 | 3.9 | 2.9 | 2.3 | 2.4 | 2.5 | 2.7 |
fodder from arable land | % | 9.9 | 12.5 | 11.2 | 12.8 | 11.3 | 11.1 | 11.1 | 11.9 | 11.2 | 12.2 |
grassland consumption | % | 65.1 | 61.6 | 65 | 65.3 | 65 | 67 | 66.7 | 67 | 67.4 | 63.7 |
Total | % | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 | 100 |
2012 | |||||||||||
cereals | t N | 9441 | |||||||||
vegetables, fruit, ornamental crops | t N | 673 | |||||||||
dried pulses, root and industrial crops, other harvested crops and others | t N | 1247 | |||||||||
fodder from arable land | t N | 5379 | |||||||||
grassland consumption | t N | 27622 | |||||||||
Nitrogen output - Total | t N | 44362 | |||||||||
cereals | % | 21.3 | |||||||||
vegetables, fruit, ornamental crops | % | 1.5 | |||||||||
dried pulses, root and industrial crops, other harvested crops and others | % | 2.8 | |||||||||
fodder from arable land | % | 12.1 | |||||||||
grassland consumption | % | 62.3 | |||||||||
Total | % | 100 |
Agricultural Institute of Slovenia, 2011.
1992 | 1993 | 1994 | 1995 | 1996 | 1997 | 1998 | 1999 | 2000 | 2001 | ||
---|---|---|---|---|---|---|---|---|---|---|---|
Input N | kg N/ha | 162 | 148 | 152 | 154 | 154 | 164 | 167 | 166 | 166 | 166 |
Output N | kg N/ha | 52 | 53 | 93 | 89 | 88 | 100 | 101 | 95 | 80 | 79 |
Gross Nitrogen balance [kg N/ha] | kg N/ha | 110 | 95 | 60 | 65 | 65 | 64 | 67 | 70 | 86 | 88 |
2002 | 2003 | 2004 | 2005 | 2006 | 2007 | 2008 | 2009 | 2010 | 2011 | ||
Input N | kg N/ha | 169 | 165 | 159 | 153 | 162 | 161 | 151 | 165 | 157 | 161 |
Output N | kg N/ha | 100 | 66 | 104 | 108 | 91 | 99 | 104 | 107 | 109 | 108 |
Gross Nitrogen balance [kg N/ha] | kg N/ha | 70 | 99 | 55 | 45 | 71 | 62 | 47 | 58 | 48 | 53 |
2012 | |||||||||||
Input N | kg N/ha | 152 | |||||||||
Output N | kg N/ha | 92 | |||||||||
Gross Nitrogen balance [kg N/ha] | kg N/ha | 59 |
Agricultural Institute of Slovenia, 2010; OECD, 2010.
France | Italy | Sweden | Spain | Portugal | Austria | Ireland | United Kingdom | Finland | EU-15 | ||
---|---|---|---|---|---|---|---|---|---|---|---|
2000 | kg N/ha | 25 | 37 | 38 | 39 | 42 | 43 | 44 | 45 | 51 | 55 |
Greece | Denmark | Slovenia | Germany | Luxembourg | Belgium | Netherlands | |||||
2000 | kg N/ha | 69 | 77 | 90.1 | 105 | 117 | 174.3 | 226 |
Kmetijski inštitut Slovenije, 2011
4017 Vzhodne Slovenske gorice | 3012 Dravska kotlina | 1001 Savska kotlina in Ljubljansko Barje | 1002 Savinjska kotlina | 4016 Murska kotlina | 3015 Zahodne Slovenske gorice | 4018 Goričko | 3014 Haloze in Dravinjske gorice | 1009 Spodnji del Savinje do Sotle | 3013 Vzhodne Alpe | ||
---|---|---|---|---|---|---|---|---|---|---|---|
Input N | t N | 3352 | 5220 | 7997 | 1376 | 6382 | 6372 | 3179 | 3407 | 6865 | 4443 |
Input N | kg N/ha | 242 | 247 | 248 | 225 | 188 | 186 | 167 | 180 | 181 | 177 |
Output N | t N | 1272 | 2051 | 3966 | 661 | 2827 | 3400 | 1712 | 2100 | 4383 | 2900 |
Output N | kg N/ha | 92 | 97 | 123 | 108 | 83 | 99 | 90 | 111 | 116 | 115 |
N balance | t N | 2080 | 3168 | 4031 | 715 | 3555 | 2972 | 1467 | 1306 | 2482 | 1543 |
N balance | kg N/ha | 150 | 150 | 125 | 117 | 105 | 87 | 77 | 69 | 66 | 61 |
1003 Krška kotlina | 1008 Posavsko hribovje do osrednje Sotle | 1006 Kamniško-Savinjske Alpe | 1011 Dolenjski kras | 1007 Cerkljansko, Škofjeloško in Polhograjsko hribovje | 6021 Goriška | 1004 Julijske Alpe v porečju Save | 6020 Julijske Alpe v porečju Soče | 5019 Obala in Kras z Brkini | 1010 Kraška Ljubljanica | ||
Input N | t N | 769 | 7138 | 2481 | 9327 | 2693 | 2404 | 639 | 728 | 1963 | 2184 |
Input N | kg N/ha | 150 | 156 | 154 | 151 | 150 | 107 | 114 | 111 | 97 | 103 |
Output N | t N | 485 | 5118 | 1849 | 7064 | 2098 | 2167 | 645 | 751 | 2061 | 2472 |
Output N | kg N/ha | 95 | 112 | 115 | 114 | 117 | 97 | 115 | 115 | 102 | 116 |
N balance | t N | 284 | 2020 | 633 | 2263 | 595 | 237 | -6 | -22 | -99 | -287 |
N balance | kg N/ha | 55 | 44 | 39 | 37 | 33 | 11 | -1 | -3 | -5 | -13 |
1005 Karavanke | |||||||||||
Input N | t N | 292 | |||||||||
Input N | kg N/ha | 87 | |||||||||
Output N | t N | 384 | |||||||||
Output N | kg N/ha | 115 | |||||||||
N balance | t N | -92 | |||||||||
N balance | kg N/ha | -27 |
- balanced consumption of nitrogen from mineral fertilizers and livestock manures, gradual increase in the scope of ecological production, and prevention of soil loading from point sources and non-point sources.
- fertilise plants in a way to make the best use of nutrients without being wasted into the groundwater and the atmosphere
- reduction and prevention of further pollution of waters by nitrates from agricultural production.
In Slovenia, the balance surplus (gross stock) of nitrogen in agriculture has shown a downward trend in the last twenty years. In 2012, the amount of
nitrogen per hectare of utilised agricultural area stood at 59 kg N/ha.
The balance of nitrogen in agriculture is the difference between the input and output of nitrogen from agricultural land. The sources of nitrogen input to
utilised agricultural area are mineral fertilisers, livestock manure, and other kinds of organic manures, biological nitrogen fixation, atmospheric
deposition and nitrogen from the seeds and planting material. The agricultural crops harvested from agricultural areas are nitrogen output. The surplus of
nitrogen input over output presents an environmental threat, because it accumulates on the ground, leaches into waters, or ends up in the air in a gaseous
state.
The overall input of nitrogen on utilised agricultural area declined by almost a fifth, from 89,961 tons in 1992 to 72,710 tons in 2012, which is the
lowest amount in the observed period. Furthermore, the average input of nitrogen per hectare of utilised agricultural area reduced, from 162 kg N/ha to 152
kg N/ha. The main source of nitrogen is livestock manures (50% in 2012) and mineral fertilisers (36% in 2012). The reduction of nitrogen input from mineral
fertilisers significantly contributed to the reduced input of nitrogen in Slovenia.
The output of nitrogen with crops varied, since it amounted to between 28,973 and 54,956 tons of N, or 52 and 109 kg of N/ha per year on average. Such
great differences depend on varying weather conditions, since in periods of drought; the output of nitrogen also decreases, mainly due to lower crop
yields. The main source of nitrogen output is grassland (62% in 2012); arable crops and green fodder contribute around 33%, while the contribution of
permanent plantations and vegetable crops is relatively small.
Spatial diversity in Slovenia is also shown in the balance of nitrogen. The analysis of areas with groundwater bodies which, due to the risks of pollution
from nitrates in agriculture, are most sensitive to excessive concentrations, showed amounts of more than 100 kg N/ha in the south-eastern part of
Slovenia, and below 50 kg N/ha in the central part of Slovenia, while the west and north-western parts show a barely positive balance of nitrogen, and in
some groundwater bodies, even a negative nitrogen balance.