Title: Frans Aarts
1Frans Aarts
Plantekongres 2005, Denmark
Nutrient balances experiences from The
Netherlands
- Wageningen University and Research Centre (W-UR)
- Plant Research International
2Agricultural facts
- Denmark
- agricultural land 2.7 million ha
- animal production 5 billion euro
- Netherlands
- agricultural land 1.9 million ha
- animal production 8 billion euro
- 24,000 dairy farms (grass, maize)
- 6,000 pigs/chicken farms (no land)
3Agricultural facts
- Denmark
- agricultural land 2.7 million ha
- animal production 5 billion euro
- Netherlands
- agricultural land 1.9 million ha
- animal production 8 billion euro
- 24,000 dairy farms (grass, maize)
- 6,000 pigs/chicken farms (no land)
high
very high
Livestock density
4Manure-N (1997)
- Netherlands
- 258 kg N/ha on average
- 288 kg N/ha on dairy farms
- Denmark
- - 90 kg N/ha on average
5Effect of livestock density on N balance (Denmark)
6Effect of livestock density on N balance (EU, le
Gall)
7500 kg milk 170 kg N-manure
7Effect of livestock density on N balance (le Gall)
Dutch average
8Effect of livestock density on N balance
N surplus/ha ( input output)
manure-N/ha
9Nitrates directive
N surplus
190 kg
manure-N/ha
170 kg EU nitrates directive
10Nitrates directive
N surplus
355 kg
190 kg
manure-N/ha
170 kg EU nitrates directive
288 kg
Dutch dairy farms
11Effect of livestock density on N surplus
Individual farms
N surplus
manure-N/ha
12Effect of livestock density on N surplus
Individual farms
N surplus
On farm level livestock density is a weak
indicator for N surplus
manure-N/ha
13N-surplus as indicator for environmental effects
Quality water
excellent
bad
N surplus/ha
14N-surplus as indicator for environmental effects
Quality water
excellent
peat, grassland
average
dry sand, arable
bad
N surplus/ha
15N-surplus as indicator for environmental effects
Quality water
desired
peat, grassland
average
light sand, arable
N surplus/ha
acceptable
16N-surplus as indicator for environmental effects
Quality water
At farm level N-surplus can be a good indicator
for environmental performance
desired
peat, grassland
average
light sand, arable
N surplus/ha
acceptable
17Surplus N related to nitrate leaching (light
sandy soils)
18Surplus N (1998, kg/ha)
Acceptable
250 ? peat
130 light sand
19Surplus N (1998, kg/ha)
Acceptable
250 ? peat
130 light sand
Strong reduction of surpluses is needed
20How to reduce surpluses?
- limit to livestock density animal accounting
- or
- Limit to surpluses mineral accounting
21Limit to livestock density
N surplus
Reducing livestock density
190 kg
288 kg
manure-N/ha
170 kg
22Limit to livestock density
N surplus
190 kg
manure-N/ha
170 kg
23Limit to livestock density
N surplus
190 kg
Not all farms below acceptable level
manure-N/ha
170 kg
24Limit to the surplus of N
N surplus
Improving management
190 kg
288 kg
manure-N/ha
170 kg
25Limit to the surplus of N
N surplus
190 kg
288 kg
manure-N/ha
170 kg
26Limit to the surplus of N
N surplus
190 kg
All farms below acceptable level
288 kg
manure-N/ha
170 kg
27Mineral accounting, with limited surpluses
- Advantages
- environmental quality is better guaranteed
- more attractive if land is expensive and animal
density is high - Disadvantages
- High cost to control
- Acceptance of EU?
28How to reduce surpluses?
- Improve N-turnover in farm components
- less inputs needed
feed
18
Milk/meat
herd
71
crop
manure
80
53
soil
fertilizer
291987
200?
De MarkeAn experimental farm on light sandy
soil, with an average intensity of milk
production and very tight environmental standards
30How to reduce surpluses?
- Improved N-turnover De Marke
feed
18
23
Milk/meat
herd
71
93
crop
manure
80
92
70
soil
fertilizer
53
31Results 1993-1998
-
- Mineral fertiliser-N 70 kg/ha
- reduction of 70
-
- Purchased feed 2,000 kg dm/ha
- Reduction of 60
- Surplus N 150 kg/ha
32Results 2004
-
- Mineral fertiliser-N 0 kg/ha
- reduction of 100
-
- Purchased feed 2,000 kg dm/ha
- Reduction of 60
- Surplus N 100 kg/ha
33How to convince farmers?
- Father G. van den Elsen (founder of Rabo-bank,
Campina etc.) It is
impossible to convince farmers only with books
and journals. The truth should be pumped into
their heads by clear, visible examples.
(Sociologie der Boeren,
1918)
341999
2005
Cows Opportunitiescommercial intensive dairy
farms, demonstrating possibilities to realise low
surpluses
35Characteristics of pilot farms
36Environmental performance pilot farms
37Economics
Income
N surplus
Measures to reduce surplus
38Economics
Income
N surplus
Pilot farms
measures
39Economics
Income
N surplus
2,500 euro
Pilot farms
measures
40Dutch Mineral Accounting System (1998 2006)
Farm gate balance
Input
Output
concentrates
livestock
milk, livestock
roughage
roughage
manure
manure
artificial fertilizer
Farm gate surplus
41Dutch Mineral Accounting System (1998 2006)
Farm gate balance
Input
Output
concentrates
livestock
milk, livestock
roughage
roughage
manure
manure
artificial fertilizer
About 70 kg N below real surplus (including
deposition, clover etc.)
Farm gate surplus
42Permitted farm gate surpluses (kg N/ha)
On light sandy soils 40 kg less
43Real N-surplus of very specialized dairy farms
(kg/ha)
(-150)
Average annual decrease 38 kg 11
44Farmgate N-surplus of all dairy farms
Save area
MINAS
45 P2O5 -surplus of very specialized dairy farms
(kg/ha)
(-31)
Average annual decrease 8 kg 13
46The future
- ? We love mineral accounting, but European Court
of Justice does not ?
47The future
- ? We love mineral accounting, but European Court
of Justice does not ? - We will introduce application standards for
fertilizers in 2006 ?
48The future
- ? We love mineral accounting, but European Court
of Justice does not ? - We will introduce application standards for
fertilizers in 2006 ? - We expect that costs will increase for farmers ?,
but costs for government will be lower ?
49The future
- ? We love mineral accounting, but European Court
of Justice does not ? - We will introduce application standards for
fertilizers in 2006 ? - We expect that costs will increase for farmers ?,
but costs for government will be lower ? - We hope that in the future a mineral accounting
system can be reintroduced, because nutrient
surplus is the better indicator for environmental
quality ?
50