Farming at dairy farms (produktion på mælkelandbrug)

  Denmark
year

Process description

The present data refer to production on eight typical Danish Dairy farms in year, which combines dairy and (cash) crop production in a mixed farming system. The main characteristics of the eight farms are summarized in Table 1.

Table 1: Main characteristics of the considered dairy farms.

Soil type

Loamy (clay)

Sandy

Stocking rate

<1,4

1,4-2,3

>2,3

Organic farms

<1,4

1,4-2,3

>2,3

Organic farms

Number cows

55

55

82

62

48

67

76

84

Land area (ha)

99

50

44

88

81

65

48

99

Milk yield per cow per year

7227

7288

7053

6811

7431

7429

7125

6866

part of cows' feed produced on farm

81%

58%

31%

70%

80%

61%

40%

68%

Winter wheat yield, ton per ha

6,7

6,8

7,8

5,9

6,5

5,5

7,9

5,0

Spring Barley yield, ton per ha

4,8

5,0

5,9

3,7

4,7

4,6

3,8

3,9

A large part of the feed for the cattle is produced on the farm as a combination of silage and grain in a crop rotation with grass clover swards. Moreover, some of the farms with lower stocking rate produce grains, rapeseed or grain legumes as cash crops. Most cows are Holstein-Friesian of high genetic potential using artificial insemination (AI). Average yearly milk yields are around 7000 kg per cow in the farms. Most cows graze in 180 days per year and thus needs conserved fodder for at least 185 days. Almost all the heifers are raised on the farm and grazed up to 200 days per year often on marginal land/permanent pasture. Bulls for fattening exist only on part of these farms mainly because of limitations on stocking rate. Most farms have stables with slatted floors (manure handled as slurry) and central milking parlors (rooms). All used water and effluents are collected in concrete slurry containers with a minimum capacity of 6 months (application to fields is only allowed from March to September). Cultivation of crops is often done using farmers own equipment while harvest of grains and silage is most often done by contractors. Equipment is usually modern and most processes automatic.

There is most often one owner and a full time hired helper, who both have a diploma and are trained in farm management. Most farmers use modern feed planning methods and regular feed analyses to adjust protein levels and minerals and all follow public regulation concerning manure N utilization and fertilization.

Data collection and treatment

Data collection:

All Danish farms are obliged to keep detailed records of purchases and sales for tax purposes and the yearly accounts are made with professional help. A representative set of these accounts, 2232, are reported by the advisors to the Danish Research Institute of Food Economics (DRIFE) and constitute the basic empirical input to the farm types presented here. Besides the economical data, information on the land use, livestock numbers and amounts produced are included in the data set by the advisors.

Data from other sources are used to model the technical processes: Data from the advisory services (feeding and grazing practices), the Directorate for Food, Fisheries and Agri-business, Danish Environmental Protection Agency (pesticide use in different crops) and Statistic Denmark (countrywide use of fertilizer and concentrates, partition of land use on different crops and their total yields). The Danish Institute of Agricultural Sciences (DIAS) together with DRIFE and Statistic Denmark is responsible for data collection.

Data treatment:

The data processing and details of the different farm types is the responsibility of DIAS and DRIFE. The DRIFE checks the account data and has divided the accounts according to the farm typology presented (link). These average data from each farm type has been used by DIAS to model a typical farm in terms of land use, herd size and production. All resource use, inputs, production and emissions is calculated using the farm level as the main unit and all the single enterprises have been described so that they fit coherently into the overall farm balances (e.g. crop production must fit the sum of homegrown feed used and exported). Thus, inputs of fertilizer, feeds and minerals are calculated to mach the livestock and cash crop production after correction for home grown feed (see also under validation (link)).

The nutrient turnover on the farm is calculated by multiplying the physical turnover of inputs and products with N and P contents following standard procedures described by teori papir…..link). Emissions of ammonia, methane and nitrous oxide (N20) from the livestock, stables, manure storage and handling and from crop residues and soil are calculated using standard coefficients (IPCC, ref..?) on the amounts of nutrients and feed dry matter (DM).

Direct energy use is determined by the use of a model that attaches diesel use to field operations following Dalgaard et al. 2000.

Pesticide use on crop level is estimated from national statistical data of actually used amounts of each pesticide divided by number of standard approved dosages and acreage of the different crops (Danish Environmental Protection Agency) http://www.mst.dk/udgiv/publikationer/2001/87-7944-620-5/html/bred03.htm .

Hvordan er emissioner fra pesticider beregnet?  Afventer

Technical scope 

The Inventory includes all processes on the farm necessary for the cultivation and preservation of crops and home-produced fodder (e.g. soil preparation, sowing, fertilizing/manuring, plant protection, harvesting, making silage and transport of crops).

Feeding and milking of cattle and calfs, feeding of other livestock and handling of bi-products such as manure and straw, use of electricity for milk cooling, ventilation and light is also included. To some of the processes are attached imports of e.g. feeds and fertilizers.

Resource use and emissions related to the production of fertilizer, pesticides, imported feeds, minerals and electricity are handled as external processes described separately in Simapro. Thus energy use, air emissions and other externalities are included in this inventory if they happen on the farm, while emissions from production of farm inputs are included in the process analysis in Simapro. Per skriv:  and to the use of diesel for traction

Use of medicine is not considered. Resource use and emissions related to the construction and maintenance of buildings and machinery used on the farm is not included.

Most dairy farm types produce small amounts of other items than milk and meat, e.g. bread wheat. All inputs, resource uses and emissions related to these secondary enterprises have been included in the inventory. Only technical allocations have been made between enterprises within the farm and only when resources used could be clearly divided between the enterprises. To account for the part of resource use and externalities related to e.g. meat and cash crop production on the dairy farm the method of system enlargement is recommended. This method has been used in the Simapro database developed from this inventory to define the resource use and emissions attached to milk production per se. Systems enlargement has also been used to account for the exported manure from farm types with high stocking rate. Thus, the difference in fertilizer use and emissions on the manure receiving farm type (modeled asbefore and after manure import) has been allocated to the manure selling farm type.

Representativity

The dataset of 2239 accounts used is statistically representative of the Danish farming sector (59000 farms in total) following a method developed over several decades for yearly economical analysis of Danish farms (DRIFE SJFI) and for reporting to other bodies like the EU Farm Accountancy Data Network. In order to secure representativity within the established typology only farm types that could be described by at least 14 accounts from the sample were allowed for the basic products. Moreover, a given farm could be included in only one type depending on the main enterprise. The data represent only one year (2000), but the large number of farms allows for some generalizations of the input-output relationships.

The present dairy farm types are based on 8 sub samples. Together they represent all Danish dairy farms with a maximum of 10% of Gross Margin from pig production. The total milk production on these types account for 85% of the total milk produced in Denmark. The farms have been divided into groups in order to represent dairy production on sandy and loamy soil types respectively and with different stocking rates (number of standard livestock units per hectare). Two separate types represent organic dairy farms. Farms with low or medium stocking rates usually produce 1-3 secondary products, which may differ from farm to farm. The resulting farm type thus represents an average of these secondary enterprises, but the number of small enterprises is not typical for a single farm.

Included dairy farm types:

Soil type

Loamy (clay)

Sandy

Stocking rate

<1,4

1,4-2,3

>2,3

Organic farms

<1,4

1,4-2,3

>2,3

Organic farms

Number of accounts

23

32

14

24

83

182

16

127

Pct of total Danish milk production

 

4

 

7

 

3

 

1

 

15

 

43

 

4

 

9

What do the different types represent?

There are important differences between the dairy farm types. The farms on clay soils tend to feed more imported feeds and crop residues because cash cop production is relatively more competitive than on sandy soils. The sandy soil dairy farms usually include two-year grass-clover leys in the rotation. The farms with high stocking rate sell part of their manure production. Organic farms produce most feed themselves and use no pesticides, fertilizer or imported manure. The average size of organic farms is above the average size of farms in the conventional groups.

The farm type, Sandy with 1,4-2,3 LU per ha is considered the marginal farm that is, the farm type most likely to expand production in the future, especially in a hypothetical situation of increased overall milk production as a consequence of increased demand in the food sector.

Validation

The representativity of the farm accounts has been checked using standard methodology at DRIFE. The resource use and production on the farms have been validated at two levels: Internal coherence within each farm type and overall coherence between the sum of farm types and national level input use and production.

On the farm level the quantification of each type has been validated primarily by checking the coherence between land use, crop yields and livestock production (e.g. the feed needed for the herd matches the home-produced feed plus imported feeds less sold cash crops and the sum of homegrown feeds and sold crops fits the land use).

At a higher hierarchical level the land use has been validated by comparing the sum of each crop acreage over all types with national statistics for the same year, e.g. checking that the total wheat area and total wheat yield does not differ more than a few % from the national statistics.

Likewise, the total estimated use of inputs like diesel, fertilizer and concentrated feeds across all farm types have been checked against statistical information on national level. In case of differences that could not be ascribed to an error in a specific type, a general correction factor was multiplied into all types for the relevant input item. For more details, see (link).

Inputs and outputs

Inputs and outputs associated with production processes at eight different types of diary farms. Data are provided per farm per year?.

 

Soil type

Loamy (clay)

Sandy

 

Stocking rate

<1,4

1,4-2,3

>2,3

Organic farms

<1,4

1,4-2,3

>2,3

Organic farms

Products

1000

 

 

 

 

 

 

 

 

Spring barley

kg

0

0

0

0

0

0

0

0

Winter barley

kg

0

0

0

0

0

0

0

0

Bread wheat

ton

76,3

17,2

34,0

26,7

36,7

12,1

8,4

8,3

Wheat

kg

0

0

0

0

0

0

0

0

Rye

kg

0

0

0

0

0

0

0

0

Oat

kg

690

690

690

690

690

690

690

690

Mixed crops

kg

0

0

0

0

0

0

0

0

Rape seed

ton

7,2

1,3

0,0

0,0

7,0

1,1

0,0

0,0

Grass seed

ton

0,7

0,0

0,0

0,8

0,7

0,0

0,0

0,0

Peas

ton

5,7

0,0

0,0

4,0

3,1

0,0

0,0

0,0

Potatoes

ton

11,3

0,0

6,3

2,2

11,8

0,0

0,0

0,0

Sugar beet

ton

13,6

7,0

239,0

18,0

17,1

0,0

44,9

0,0

Milk-ECM

ton

399,7

397,9

575,5

424,3

355,2

499,3

538,0

577,4

Grower pig (30 kg)

ton

0,0

0,0

0,0

0,0

0,0

0,0

0,0

0,0

Beef meat

ton

25,1

15,4

20,3

16,3

19,9

20,6

23,9

17,8

Pork meat

ton

2,4

0,0

0,0

0,0

0,0

0,0

0,0

0,0

Manure

ton

0,0

0,0

2,6

0,0

0,0

0,0

2,0

0,0

 

 

 

 

 

 

 

 

 

 

Materials/fuels

 

 

 

 

 

 

 

 

 

Winter barley

kg

0

0

0

0

0

0

0

0

Wheat

kg

0

0

0

0

0

0

0

0

Spring barley

ton

0,0

88,8

217,2

104,2

9,4

113,0

224,0

152,9

Soy meal

ton

137,0

149,9

336,2

68,2

117,5

172,4

255,8

92,5

Lubricant Oil

liter

1106

634

720

798

843

769

704

882

Manure

kg N

440

0

0

853

615

0

0

1087

Fertilizer , Calcium ammonium nitrate

kg N

10290

3468

1363

0

8074

5308

2821

0

Fertilizer P

kg P

679

68

0

0

392

190

0

0

Fertilizer K

kg K

573

0

0

0

157

0

0

0

P, Mineral Feed

kg P

458

713

1697

446

407

831

1565

647

 

 

 

 

 

 

 

 

 

 

Electricity/heat

 

 

 

 

 

 

 

 

 

Electricity Denmark

kWh

37588

24416

36016

32062

28424

34310

37078

44277

Heating

MJ

449

767

47

164

499

568

424

448

Traction

MJ

389266

223012

253439

280943

296672

270798

247760

310509

 

 

 

 

 

 

 

 

 

 

Emissions to air

 

 

 

 

 

 

 

 

 

Methane

kg CH4

11256

10634

15286

11554

10364

14076

16012

15474

Ammonia

kg NH3

2658

2485

3408

2435

2508

3203

3439

3333

N2O

Kg N2O

1069

669

657

759

968

970

834

1076

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Emissions to water

 

 

 

 

 

 

 

 

 

Nitrate

kg NO3

39419

19112

19182

13436

36777

31881

26286

25308

Phosphate

kg P

1251

745

1160

2513

1065

1131

1602

3367

 

 

 

 

 

 

 

 

 

 

Emissions to soil

 

 

 

 

 

 

 

 

 

Carbon

kg C

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Non material emissions

 

 

 

 

 

 

 

 

 

Arable land use

ha a

99

50

44

88

81

65

48

99

Administrative information

Data URL: http://www.lcafood.dk/database/processes/agriculture/diaryfarms.html
Version no.: 1.00
Authors: Niels Halberg, Danish Institute of Agricultural Science and Per H. Nielsen 2.-0 LCA Consultants.
Data responsible: Randi Dalgaard and Niels Halberg, DIAS

Contact: niels.Halberg@agrsci.dk

Data entry: data have been entered into Simapro by Randi Dalgaard, DIAS and transformed into this format by Per H. Nielsen, 2.-0 LCA Consultants
Data completed: ... 2003.

References.....

.....