Nitrogen
balance from dairy farms (1999) |
Denmark
1999
|
The
Danish aquatic environment plan focuses on reducing nitrogen discharge
to the aquatic environment. Farming is one of the major contributors
to this discharge, which is why it is useful to have an overview of
the nitrogen balance and emissions in Danish farming. The data presented
here refers to the Nitrogen use and losses in different types of Danish
dairy farms in 1999. The different farm types are set according to soil
type and major enterprise and they can be seen here.
For process description, data collection and treatment etc. please look
at the processes for each farm type (Here).
For more details on the Nitrogen balance method see
here.
The Nitrogen balance
data is presented in three tables:
Table
1. Characteristics of area, land use and production levels of full
time mixed dairy farms in Denmark year 1999
Table
2. Farm gate N-turnover and -loss at mixed dairy farms in Denmark
year
1999
Table
3. Field level N-turnover at mixed dairy farms in Denmark year
1999
Table
1.
Characteristics of area, land use and production levels of full time
mixed dairy farms in Denmark year 1999 (average by farm
type)
Soil
type1)
|
Sandy
loam
|
Sand
|
Farm
type [LSU2) ha-1]
|
<1.4 |
1.4-2.3 |
>2.3 |
Org. |
<1.4 |
1.4-2.3 |
>2.3 |
Org. |
Suckler |
Representativity |
|
|
|
|
|
|
|
|
|
Number
of farms in data set |
23 |
32 |
14 |
24 |
83 |
182 |
16 |
125 |
103 |
Area
represented by farm type [1000ha] |
43 |
43 |
12 |
10 |
156 |
261 |
16 |
71 |
198 |
%
of Danish milk Production |
4 |
7 |
3 |
1 |
15 |
43 |
4 |
9 |
0 |
Herd
data |
|
|
|
|
|
|
|
|
|
Dairy
per farm [cows farm-1] |
55 |
55 |
82 |
62 |
48 |
67 |
76 |
85 |
0 |
LSU
per farm [LSU farm-1] |
87 |
84 |
121 |
100 |
81 |
109 |
126 |
133 |
20 |
Stocking
rate [LSU ha-1] |
0.9 |
1.7 |
2.8 |
1.1 |
1.0 |
1.7 |
2.6 |
1.3 |
0.6 |
Feed
uptake, 100 SFU LSU-1 y-1 |
48 |
48 |
47 |
44 |
48 |
48 |
48 |
45 |
40 |
N
uptake , kg N LSU-1 y-1 |
142 |
139 |
141 |
129 |
140 |
139 |
138 |
130 |
149 |
N-efficiency,
herd3) |
21.3% |
20.4% |
21.2% |
19.8% |
20.0% |
19.9% |
18.9% |
19.6% |
18.2% |
Area
|
|
|
|
|
|
|
|
|
|
Total
farm area [ha farm-1] |
99 |
50 |
44 |
88 |
81 |
65 |
48 |
102 |
31 |
Crop
rotation [% of farm area] |
|
|
|
|
|
|
|
|
|
Permanent
grass |
9 |
8 |
3 |
11 |
9 |
11 |
6 |
9 |
20 |
Set-aside
|
6 |
4 |
6 |
5 |
7 |
6 |
5 |
5 |
6 |
Cereal
for harvest |
46 |
32 |
42 |
23 |
40 |
19 |
16 |
14 |
46 |
Maize/whole
crop silage |
13 |
21 |
28 |
23 |
16 |
33 |
56 |
29 |
3 |
Grass/clover
in rotation |
14 |
24 |
4 |
33 |
18 |
26 |
13 |
41 |
16 |
Production |
|
|
|
|
|
|
|
|
|
Cereal
yield [100kg ha-1] |
56 |
54 |
66 |
44 |
52 |
49 |
47 |
41 |
47 |
Milk
yield [kg ECM cow-1 yr-1] |
7227 |
7288 |
7053 |
6811 |
7431 |
7429 |
7125 |
6861 |
5820 |
1)
Sandy loam > 10% clay, Sand <10% clay
2)
Livestock units (LSU), DK definition: 1 LSU = 100 kg total N in
manure ex. storage, 0.85 LSU=1 dairy cow on 8,500 l milk year-1
3)
N-efficiency = output of animals and livestock products/input of feed |
Table
2. Farm gate N-turnover and -loss at mixed dairy farms in Denmark year
1999 (kg N ha-1 year-1)
Soil
type
|
Sandy
loam
|
Sand |
Farm
type (LSU ha-1)
|
<1.4 |
1.4-2.3 |
>2.3 |
Org. |
<1.4 |
1.4-2.3 |
>2.3 |
Org. |
Suckler
|
Inputs |
|
|
|
|
|
|
|
|
|
Mineral
fertiliser |
104 |
81 |
41 |
0 |
104 |
93 |
66 |
0 |
117 |
Organic
fert. & livestock1) |
6 |
1 |
-59 |
1 |
8 |
1 |
-34 |
9 |
10 |
Supplement
feed |
42 |
108 |
307 |
41 |
46 |
104 |
232 |
48 |
28 |
Straw
for bedding1) |
0 |
6 |
10 |
6 |
0 |
6 |
14 |
7 |
0 |
Biological
N-fixation |
20 |
34 |
5 |
66 |
22 |
32 |
26 |
76 |
19 |
Deposition
and precipitation |
16 |
16 |
16 |
16 |
16 |
16 |
16 |
16 |
16 |
Total
input |
188 |
246 |
320 |
130 |
196 |
253 |
320 |
156 |
191 |
|
|
|
|
|
|
|
|
|
|
Outputs |
|
|
|
|
|
|
|
|
|
Milk |
-21 |
-41 |
-68 |
-24 |
-23 |
-40 |
-58 |
-28 |
0 |
Meat |
-8 |
-10 |
-21 |
-6 |
-8 |
-10 |
-20 |
-6 |
-19 |
Cash
crops |
-26 |
-8 |
-28 |
-7 |
-18 |
-4 |
-5 |
-2 |
-26 |
Total
output |
-55 |
-59 |
-117 |
-36 |
-49 |
-55 |
-83 |
-36 |
-45 |
|
|
|
|
|
|
|
|
|
|
Farm
gate N-balance |
133 |
187 |
204 |
94 |
147 |
198 |
236 |
120 |
146 |
N
loss, stable and storage2) |
-12 |
-23 |
-46 |
-16 |
-14 |
-23 |
-39 |
-18 |
-11 |
|
|
|
|
|
|
|
|
|
|
Field
N balance |
120 |
161 |
156 |
76 |
132 |
173 |
194 |
100 |
134 |
Field
N-efficiency3) |
49% |
46% |
44% |
60% |
47% |
44% |
41% |
56% |
43% |
|
|
|
|
|
|
|
|
|
|
N
loss, field |
|
|
|
|
|
|
|
|
|
Fertilisation,
manure spreading2) |
-10 |
-15 |
-18 |
-9 |
-11 |
-16 |
-20 |
-11 |
-9 |
Crops2) |
-4 |
-4 |
-5 |
-2 |
-4 |
-4 |
-4 |
-2 |
-3 |
Denitrification2) |
-29 |
-29 |
-32 |
-27 |
-12 |
-15 |
-17 |
-13 |
-11 |
Soil-N
change |
5 |
19 |
15 |
16 |
22 |
36 |
36 |
35 |
8 |
Leaching4) |
-73 |
-96 |
-87 |
-24 |
-85 |
-104 |
-121 |
-41 |
-104 |
|
|
|
|
|
|
|
|
|
|
1)
Net
import = import-export of manure, straw and living animals
2)
Calculated standard ammonia emission and denitrification
3)
N-efficiency = 100*output/input
4)
Leaching = field N balance - N aerial loss (fertilization+crops+denitrification)
+/- soil-N changes |
Table
3. Field level N-turnover at mixed dairy farms in Denmark year
1999 (kg
N ha-1 year-1)
Soil
type
|
Sandy
loam
|
Sand
|
Farm
type (LSU ha-1)
|
<1.4 |
1.4-2.3 |
>2.3 |
Org. |
<1.4 |
1.4-2.3 |
>2.3 |
Org. |
Suckler
|
Inputs |
|
|
|
|
|
|
|
|
|
Mineral
fertiliser |
104 |
81 |
41 |
0 |
104 |
93 |
66 |
0 |
117 |
Imported
organic fertiliser |
6 |
0 |
0 |
22 |
7 |
0 |
0 |
23 |
8 |
Manure
from own herd1) |
90 |
167 |
216 |
87 |
103 |
170 |
221 |
111 |
73 |
Biological
N-fixation |
20 |
34 |
5 |
66 |
22 |
32 |
26 |
76 |
19 |
Deposition
and precipitation |
16 |
16 |
16 |
16 |
16 |
16 |
16 |
16 |
16 |
Total
input |
235 |
298 |
277 |
191 |
251 |
311 |
328 |
226 |
234 |
|
|
|
|
|
|
|
|
|
|
Outputs |
|
|
|
|
|
|
|
|
|
Cash
crops |
-5 |
-2 |
-15 |
-1 |
-4 |
-1 |
-2 |
0 |
-3 |
Grain |
-21 |
-6 |
-13 |
-6 |
-14 |
-3 |
-3 |
-2 |
-24 |
Grain
for feed2) |
-21 |
-22 |
-31 |
-11 |
-20 |
-11 |
-9 |
-7 |
-13 |
Straw
harvested |
-9 |
-5 |
-8 |
-3 |
-7 |
-3 |
-2 |
-2 |
-8 |
Straw
mulched3) (Not in output) |
-3 |
0 |
0 |
0 |
-1 |
0 |
0 |
0 |
0 |
Roughage
for feed2) |
-61 |
-101 |
-53 |
-93 |
-73 |
-117 |
-117 |
-114 |
-53 |
Total
output |
-115 |
-138 |
-122 |
-115 |
-119 |
-138 |
-134 |
-126 |
-100 |
|
|
|
|
|
|
|
|
|
|
Field
N balance |
120 |
161 |
156 |
76 |
132 |
173 |
194 |
100 |
134 |
Field
N-efficiency4) |
49% |
46% |
44% |
60% |
47% |
44% |
41% |
56% |
43% |
1)
After
deduction of amonia loss in stables, storage and sold manure,
see farmgate balance
2)
Feed
used in own herd
3)
Straw
left on field, not included in balance but used in soil-N modelling
4)
N-efficiency = 100*output/input
|
Administrative
information
Data
URL: http://www.lcafood.dk/processes/agriculture/N_balance_dairyfarms.html
Version no.:
1.00
Author: Ib Sillebak
Kristensen, Danish
Institute of Agricultural Science.
Data responsible: Ib Sillebak Kristensen, DIAS
Contact:
Data
entry: Transformed into this format by Rikke Frederiksen, DIAS
Data completed: HTML
format: November 2004.
|