Nitrogen
balance from pig 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 loses in different types of Danish
pig 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 on full
time mixed pig farms in Denmark year 1999
Table
2. Farm gate N-turnover and -loss at mixed pig farms in Denmark
year
1999
Table
3. Field level N-turnover at mixed pig farms in Denmark
year 1999
Table
1. Characteristics
of area, land use and production levels on full time mixed pig farms
in Denmark year 1999 (average by farm type)
Soil
type1)
|
Sandy
loam
|
Sand
|
Farm
type (LSU2) ha-1) |
<1.4 |
1.4-1.7 |
>1.7 |
<1.4 |
1.4-1.7 |
>1.7 |
Representatively
|
|
|
|
|
|
|
Number
of farms in data set |
50 |
27 |
98 |
99 |
38 |
164 |
Area
represented by farm type [1000 ha] |
77 |
33 |
97 |
177 |
48 |
156 |
%
of Danish pig production |
4 |
4 |
21 |
13 |
5 |
31 |
Herd
data |
|
|
|
|
|
|
LSU
per farm [LSU farm-1] |
40 |
111 |
169 |
58 |
110 |
167 |
Stocking
rate [LSU ha-1] |
0.7 |
1.4 |
2.5 |
0.8 |
1.4 |
2.5 |
Feed
uptake, 100 SFU LSU-1 y-1 |
46 |
44 |
47 |
47 |
47 |
46 |
N
uptake, kg N LSU-1 y-1 |
151 |
146 |
150 |
153 |
148 |
152 |
N-efficiency,
herd3) |
34.4% |
37.4% |
35.6% |
36.3% |
34.1% |
35.8% |
Area
|
|
|
|
|
|
|
Total
farm area [ha farm-1] |
58 |
77 |
68 |
76 |
79 |
67 |
Crop
rotation [% of farm area] |
|
|
|
|
|
|
Permanent
grass |
1 |
1 |
2 |
2 |
2 |
2 |
Set-aside
|
6 |
7 |
5 |
9 |
9 |
8 |
Cereal
for harvest |
75 |
77 |
73 |
68 |
73 |
71 |
Grass/clover
in rotation |
1 |
1 |
0 |
1 |
1 |
1 |
Production |
|
|
|
|
|
|
Grover
pigs, no |
125 |
368 |
511 |
-289 |
1501 |
981 |
Pork
meat, 100 kg, live weight |
701 |
2031 |
3151 |
1186 |
1570 |
2841 |
Cereal
yield [100 kg ha-1] |
63 |
66 |
70 |
56 |
55 |
54 |
1)
Sandy loam > 5% clay, Sand > 5% clay
2)
Livestock units (LSU), DK definition: 1 LSU = 100 kg total N in
manure ex-storage, 1 LSU = 35 pigs produced (30 - 100 kg), 1 LSU
= 4.3 sow and 175 piglets in one year
3)
N-efficiency = output of animals products/input of feed
|
Table
2. Farm gate N-turnover and -loss at mixed pig 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 |
>1.7 |
<1.4 |
1.4-1.7 |
>1.7 |
Imputs |
|
|
|
|
|
|
Mineral
fertiliser |
119 |
99 |
86 |
96 |
76 |
63 |
Organic
fert. & live stock1) |
16 |
10 |
-50 |
16 |
10 |
-53 |
Supplement
feed |
57 |
160 |
327 |
72 |
164 |
333 |
Biological
N-fixation |
3 |
2 |
1 |
4 |
4 |
4 |
Deposition
and precipitation |
16 |
16 |
16 |
16 |
16 |
16 |
Total
input |
211 |
287 |
380 |
203 |
270 |
364 |
|
|
|
|
|
|
|
Outputs |
|
|
|
|
|
|
Meat |
-46 |
-89 |
-152 |
-51 |
-80 |
-154 |
Cash
crops |
-45 |
-46 |
-55 |
-34 |
-34 |
-32 |
Straw1) |
-5 |
-5 |
-5 |
-6 |
-5 |
-4 |
Total
output |
-96 |
-140 |
-212 |
-90 |
-119 |
-191 |
|
|
|
|
|
|
|
Farm
gate N-balance |
115 |
146 |
168 |
113 |
151 |
173 |
N
loss, stable and storage2) |
-14 |
-28 |
-51 |
-16 |
-29 |
-53 |
|
|
|
|
|
|
|
Field
N balance |
100 |
118 |
116 |
97 |
121 |
119 |
Field
N-efficiency3) |
50% |
47% |
49% |
46% |
41% |
42% |
|
|
|
|
|
|
|
N
loss, field |
|
|
|
|
|
|
Fertilisation,
manure spreading2) |
-8 |
-11 |
-13 |
-8 |
-11 |
-12 |
Crops2) |
-5 |
-5 |
-5 |
-5 |
-5 |
-5 |
Denitrification2) |
-14 |
-23 |
-24 |
-7 |
-9 |
-9 |
Soil-N
changes |
-3 |
5 |
7 |
-1 |
3 |
4 |
Leaching4) |
-78 |
-73 |
-67 |
-79 |
-95 |
-90 |
1)
Net
import = import-export of manure, straw and living animals
2)
Calculated standard
ammonia emission and denitrifiction
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 pig farms in Denmark year
1999 (kg
N ha-1 year-1)
Soil
type
|
Sandy
loam
|
Sand
|
Farm
type (LSU ha-1)
|
<1.4 |
1.4-1.7 |
>1.7 |
<1.4 |
1.4-1.7 |
>1.7 |
Inputs |
|
|
|
|
|
|
Mineral
fertiliser |
119 |
99 |
86 |
96 |
76 |
63 |
Imported
organic fertiliser |
6 |
0 |
0 |
6 |
0 |
0 |
Manure
from own herd1) |
55 |
104 |
124 |
59 |
108 |
123 |
Biological
N-fixation |
3 |
2 |
1 |
4 |
4 |
4 |
Deposition
and precipitation |
16 |
16 |
16 |
16 |
16 |
16 |
Total
input |
200 |
222 |
227 |
181 |
205 |
206 |
|
|
|
|
|
|
|
Outputs |
|
|
|
|
|
|
Cash
crops |
-13 |
-11 |
-18 |
-13 |
-9 |
-11 |
Grain |
-32 |
-35 |
-37 |
-21 |
-25 |
-21 |
Grain
for feed2) |
-45 |
-49 |
-46 |
-42 |
-41 |
-43 |
Straw
harvested |
-7 |
-7 |
-9 |
-7 |
-8 |
-8 |
Straw
mulched3) (Not in output) |
-9 |
-9 |
-13 |
-3 |
0 |
0 |
Roughage
for feed2) |
-3 |
-1 |
-1 |
-2 |
-1 |
-3 |
Roughage
not utilized by own herd4) (Not in output) |
0 |
-2 |
0 |
-1 |
-3 |
0 |
Total
output |
-99 |
-104 |
-111 |
-84 |
-84 |
-86 |
|
|
|
|
|
|
|
Field
N balance |
100 |
118 |
116 |
97 |
121 |
119 |
Field
N-efficiency5) |
50% |
47% |
49% |
46% |
41% |
42% |
1)
After
deduction of amonia loss in stables, storage and sold manure,
see farm gate balance
2)
Feed
used in own hemrd
3)
Straw
left on field, not included in balance but used in soil-N modeling
4)
Factor
= 0 = not include in balances
5)
N-efficiency = 100*output/input
|
Administrative
information
Data
URL: http://www.lcafood.dk/processes/agriculture/N_balance_pigfarms.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.
|