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Development and sustainability of Free
Walk housing in the Netherlands
February 23 2017, Lille France
WUR: Paul Galama, H.J. van Dooren, W. Ouweltjes, H. de Boer
NIZO: Frank Driehuis
Animal welfare and
manure quality
Labour efficiency
Why Free Walk (Bedded Pack Barns)?
Why Bedded Pack Barns?
Lying area is also manure storage
Sustainability
Animal welfare & healthEconomics
Environment
Quality
Environment Manure quality
Compost and
Wooden chips
Input NPC
Emission
land
Emission
stable
Emission of NPC
N2
N20
NH3
CH4
Freestall
Bedded
Pack
Barn
export NPC
Experiments on 3 regional farms
Drainage with sandComposting: wooden chips an sawdust
Absorbing with peat ground and reed Cows in Green house with folie
Monitoring 10 commercial farms;
5 are composting wood chips
1. Blowing air 2. Blowing air
5. No aerating3. Suckling air 4. Suckling air
four using green waste compost
one cultivates straw
10 Straw
Farms 6 to 9
use compost
Composting ...
once a day mill the bedding
12 – 15 m2 per cow
Aerating system,
Blowing air
Aerating system,
Suckling air
Bedding material used on grassland and arable land
Roof from horticulture
Farm characteristics
1 2 3 4 5 6 7 8 9 10
Number of cows 60 130 50 105 75 55 185 80 15 65
M2 per cow 16 15 13 14 10 22 27 9 20 11
Bedding material W W W W W C C C C S
Aeration B B S S N
Milking system AMS AMS AMS AMS AMS AMS
Grazing No Yes Yes No No Yes No No No Yes
Bedding material
W = wood chips
C = Compost
S = Straw
Aeration system
B = blowing air
S = sucking air
N = no aeration
Sustainability
Animal welfare & health
Animal health (Mastitis), SCC (*1000 cells/ml)
Longevity
Animal welfare and health
Welfare Bedded pack vs freestall
Time required to lie +
Hygiene 0/+
Skin injuries ++
Legs and claws +
Natural behaviour +
Health
Udder health 0
Antibiotics usage 0
Longevity +?
Temperature sensor
No heat stress from
heat production bedding
Sustainability
Economics
Economic effect of lower culling rate
Economics bedded pack barns
Bedded pack barn vs freestall
Investment manure storage -
Investment roof ++
Total investment +
Yearly costs stable and bedding +
higher production per cow +
lower replacement --
Total yearly cost -
Sustainability
Quality
Risk of sporeforming bacteria for milk quality
(X)TAS =
(Extreme) Thermofilic Aerobe Sporenformers
XTAS can lead to spoilage problems
of commercially sterile dairy products
Route of (X)TAS
Compost
Wood
chips
XTAS in bedding materials (cfu / gram on log scale)
variation between samples
Together to the next level
0
2
4
6
8
10
12
14
16
1 2 3 4 5 6 7
Numberofsamples
XTAS-Class
Sawdust / straw
0
2
4
6
8
10
12
14
16
1 2 3 4 5 6 7
Aantalmonsters
XTAS -Class
Wood chips
0
1
2
3
4
5
6
7
8
1 2 3 4 5 6 7
Aantalmonsters
XTAS-Class
GFT-compost
Source: NIZO
Directive Dairy Industry: log 5
TAS in milk (Source NIZO)
0
200
400
600
800
1000
1200
1 2 3 4
TASinmilk(cfu/liter)
sawdust freestall wood compost straw
Sustainability
Environment
Contribution of bedding material to
net N input on the barn floor
WC = wood chips, GWC = Green Waste Compost
Range in N loss (% of total N-input)
30
19%
35%
40% 40%
44%
63%
0%
10%
20%
30%
40%
50%
60%
70%
1 WC 3 WC 4 WC 5 WC 8 GWC 9 GWC
Gaseous N loss (% of N excreted on the barn floor)
Barn code
WC = wood chips
GWC = green waste compost
Low N loss with active composting
31
‐30
‐20
‐10
0
10
20
30
40
50
60
70
2‐11‐13 12‐12‐13 21‐01‐14 2‐03‐14 11‐04‐14 21‐05‐14 30‐06‐14 9‐08‐14 18‐09‐14 28‐10‐14
N loss (% of N excreted on the barn floor)
Date
Active composting Passive composting
Intensive composting: strong relationship
between development of N loss and C/N ratio (1)
32
0
10
20
30
40
50
60
70
‐25
‐20
‐15
‐10
‐5
0
5
10
13‐11‐13 13‐12‐13 13‐01‐14 13‐02‐14 13‐03‐14 13‐04‐14 13‐05‐14 13‐06‐14 13‐07‐14
C/N ratio bedding
N loss (% of N excreted on the barn floor)
Date
N loss C/N ratio bedding
Overall sustainability
Sustainability
aspect
Criteria Wood chips
5 farms
Compost
4 farms
Straw
1 farm
Economics investment
Yearly costs
longevity
Cow Production, health
Welfare
Milk quality XTAS
Environment N losses stable Prohibited
N losses land
Ammonia emission stable 2 farms and
Dairy Campus
Nitrous oxide emission
Manure Quality Soil Improver
N mineralisation
better
attention needed
worse
Change of bedding
Use of compost is prohibited, now straw
Conclusions
 Free Walk housing can be profitable if bedding material is
not too expensive and cow replacement will be reduced
 “Intensive” composting can reduce the N-loss of the
bedding by incorperation of excreted N in bacterial biomass
 Ammonia emission in stable uncertain until end of 2017,
but emission in the field is lower
 “Composted wood chips / manure” is a good soil improver,
but N will release slowly
 (X)TAS bacteria is a point of attention
Points to continue
 Bedding material and management
● Alternative for Green Waste Compost
● Control composting process of wood chips
● Emission factor (kg NH3/cow/year)
 Synthetic floors
● Hygiëne floor / cow and milk quality
● Emission factor (kg NH3/cow/year)
 Sustainability of whole farming system
 Multiple use of building
Draining floor
Draining artificial floor
Feces
Urine
Seperating feces and urine on rubber floor
Feces
Urine
...artificial floor...
“Cowgarden” and floor cleaning robot
Floor from ID Agro (Netherlands)
Robot from Betebe (Germany)
Artificial floor
to seperate feces and urine
robot picks up the feces
Dairy Campus facilities in Leeuwarden
Emission measuring unit
for case control research
6 units of 15 cows:
- 4 Cubicles
- 2 Free Walk
Meadow floor
...to reduce ammonia emission while improving cowmobility..
aerating
...to mix slurry and reduce ammonia emission...
Sustainability
Animal welfareEconomics
Environment
Quality
Free Walk
Holistic View
Animal welfareEconomics
Environment
Cow
Soil
NPC balance
Farm Manure
‘Compost’
Quality
Free Walk
Holistic View
Animal welfare
SocietySociety
Economics
Environment
Cow
Soil
NPC balance
Farm
Quality
Manure
‘Compost’
Crop
Bio-
diversity
Bio-
diversity
Soil fertility
Multiple use of building
ERANET-Susan project with
8 countries (2017-2020)
Thank you
More information: www.vrijloopstallen.nl
Paul.galama@wur.nl

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Colloque lille2017 sequence7b2-free-walk-housing-netherlands_galama_en

  • 1. Development and sustainability of Free Walk housing in the Netherlands February 23 2017, Lille France WUR: Paul Galama, H.J. van Dooren, W. Ouweltjes, H. de Boer NIZO: Frank Driehuis
  • 2. Animal welfare and manure quality Labour efficiency Why Free Walk (Bedded Pack Barns)?
  • 3. Why Bedded Pack Barns? Lying area is also manure storage
  • 4. Sustainability Animal welfare & healthEconomics Environment Quality
  • 5. Environment Manure quality Compost and Wooden chips Input NPC Emission land Emission stable Emission of NPC N2 N20 NH3 CH4 Freestall Bedded Pack Barn export NPC
  • 6. Experiments on 3 regional farms Drainage with sandComposting: wooden chips an sawdust Absorbing with peat ground and reed Cows in Green house with folie
  • 7. Monitoring 10 commercial farms; 5 are composting wood chips 1. Blowing air 2. Blowing air 5. No aerating3. Suckling air 4. Suckling air
  • 8. four using green waste compost one cultivates straw 10 Straw Farms 6 to 9 use compost
  • 9. Composting ... once a day mill the bedding 12 – 15 m2 per cow
  • 12. Bedding material used on grassland and arable land
  • 14.
  • 15.
  • 16. Farm characteristics 1 2 3 4 5 6 7 8 9 10 Number of cows 60 130 50 105 75 55 185 80 15 65 M2 per cow 16 15 13 14 10 22 27 9 20 11 Bedding material W W W W W C C C C S Aeration B B S S N Milking system AMS AMS AMS AMS AMS AMS Grazing No Yes Yes No No Yes No No No Yes Bedding material W = wood chips C = Compost S = Straw Aeration system B = blowing air S = sucking air N = no aeration
  • 18. Animal health (Mastitis), SCC (*1000 cells/ml)
  • 20. Animal welfare and health Welfare Bedded pack vs freestall Time required to lie + Hygiene 0/+ Skin injuries ++ Legs and claws + Natural behaviour + Health Udder health 0 Antibiotics usage 0 Longevity +? Temperature sensor No heat stress from heat production bedding
  • 22. Economic effect of lower culling rate
  • 23. Economics bedded pack barns Bedded pack barn vs freestall Investment manure storage - Investment roof ++ Total investment + Yearly costs stable and bedding + higher production per cow + lower replacement -- Total yearly cost -
  • 25. Risk of sporeforming bacteria for milk quality (X)TAS = (Extreme) Thermofilic Aerobe Sporenformers XTAS can lead to spoilage problems of commercially sterile dairy products Route of (X)TAS Compost Wood chips
  • 26. XTAS in bedding materials (cfu / gram on log scale) variation between samples Together to the next level 0 2 4 6 8 10 12 14 16 1 2 3 4 5 6 7 Numberofsamples XTAS-Class Sawdust / straw 0 2 4 6 8 10 12 14 16 1 2 3 4 5 6 7 Aantalmonsters XTAS -Class Wood chips 0 1 2 3 4 5 6 7 8 1 2 3 4 5 6 7 Aantalmonsters XTAS-Class GFT-compost Source: NIZO Directive Dairy Industry: log 5
  • 27. TAS in milk (Source NIZO) 0 200 400 600 800 1000 1200 1 2 3 4 TASinmilk(cfu/liter) sawdust freestall wood compost straw
  • 29. Contribution of bedding material to net N input on the barn floor WC = wood chips, GWC = Green Waste Compost
  • 30. Range in N loss (% of total N-input) 30 19% 35% 40% 40% 44% 63% 0% 10% 20% 30% 40% 50% 60% 70% 1 WC 3 WC 4 WC 5 WC 8 GWC 9 GWC Gaseous N loss (% of N excreted on the barn floor) Barn code WC = wood chips GWC = green waste compost
  • 31. Low N loss with active composting 31 ‐30 ‐20 ‐10 0 10 20 30 40 50 60 70 2‐11‐13 12‐12‐13 21‐01‐14 2‐03‐14 11‐04‐14 21‐05‐14 30‐06‐14 9‐08‐14 18‐09‐14 28‐10‐14 N loss (% of N excreted on the barn floor) Date Active composting Passive composting
  • 32. Intensive composting: strong relationship between development of N loss and C/N ratio (1) 32 0 10 20 30 40 50 60 70 ‐25 ‐20 ‐15 ‐10 ‐5 0 5 10 13‐11‐13 13‐12‐13 13‐01‐14 13‐02‐14 13‐03‐14 13‐04‐14 13‐05‐14 13‐06‐14 13‐07‐14 C/N ratio bedding N loss (% of N excreted on the barn floor) Date N loss C/N ratio bedding
  • 33. Overall sustainability Sustainability aspect Criteria Wood chips 5 farms Compost 4 farms Straw 1 farm Economics investment Yearly costs longevity Cow Production, health Welfare Milk quality XTAS Environment N losses stable Prohibited N losses land Ammonia emission stable 2 farms and Dairy Campus Nitrous oxide emission Manure Quality Soil Improver N mineralisation better attention needed worse
  • 34. Change of bedding Use of compost is prohibited, now straw
  • 35. Conclusions  Free Walk housing can be profitable if bedding material is not too expensive and cow replacement will be reduced  “Intensive” composting can reduce the N-loss of the bedding by incorperation of excreted N in bacterial biomass  Ammonia emission in stable uncertain until end of 2017, but emission in the field is lower  “Composted wood chips / manure” is a good soil improver, but N will release slowly  (X)TAS bacteria is a point of attention
  • 36. Points to continue  Bedding material and management ● Alternative for Green Waste Compost ● Control composting process of wood chips ● Emission factor (kg NH3/cow/year)  Synthetic floors ● Hygiëne floor / cow and milk quality ● Emission factor (kg NH3/cow/year)  Sustainability of whole farming system  Multiple use of building
  • 38. Seperating feces and urine on rubber floor Feces Urine
  • 40. “Cowgarden” and floor cleaning robot Floor from ID Agro (Netherlands) Robot from Betebe (Germany)
  • 41. Artificial floor to seperate feces and urine robot picks up the feces
  • 42. Dairy Campus facilities in Leeuwarden Emission measuring unit for case control research 6 units of 15 cows: - 4 Cubicles - 2 Free Walk
  • 43. Meadow floor ...to reduce ammonia emission while improving cowmobility..
  • 44. aerating ...to mix slurry and reduce ammonia emission...
  • 46. Free Walk Holistic View Animal welfareEconomics Environment Cow Soil NPC balance Farm Manure ‘Compost’ Quality Free Walk Holistic View Animal welfare SocietySociety Economics Environment Cow Soil NPC balance Farm Quality Manure ‘Compost’ Crop Bio- diversity Bio- diversity Soil fertility Multiple use of building ERANET-Susan project with 8 countries (2017-2020)
  • 47. Thank you More information: www.vrijloopstallen.nl Paul.galama@wur.nl