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Rothamsted Research
where knowledge grows
Rothamsted Research
where knowledge grows
On-farm measures for
sediment control:
options, impacts and
challenges
Adie Collins
SILTFLUX workshop, UCD, Dublin, February 2016
Water policy and on-farm interventions
Parallel work streams
Fundamental
empirical evidence
Evidence synthesis
for national policy
support
On-farm
measures for
sediment
control
The scale challenge for sediment mitigation
Measure scale
Farm scale
Landscape scale
control
realism
Demonstration test catchments (DTCs)
Example policy questions to the DTCs
• How can you extrapolate mitigation efficacy from
a single measure to a series of interconnected
measures?
• How much of an improvement in terms of
receptors can we attain by implementing
mitigation?
• To what extent does targeting only part of the
anthropogenic pressures on water bodies allow us
to achieve significant improvement in status?
• How long will it take for mitigation interventions
to: (i) meet a set pollutant threshold (WFD related
targets) at a given point in a catchment and (ii)
achieve an ecological response?
Targets for guiding sediment management
Targets for guiding sediment management
Overarching questions
• how do you best characterise
‘the problem’?
• what are the technical remedies?
• how do you best get farmers more
engaged?
• what are the challenges for
delivering positive outcomes from
targeted on-farm interventions?
Defining sediment as a stressor
Typical problems in livestock areas
1. 4. 6.
2. 5. 7.
3. 1.Poached surface soils
2.Over-full FYM store
3.Dirty yard by parlour
4.Drain connecting 3. to stream
5.Runoff from 2. to stream
6.Timing of slurry applications
7.Farm track channelisation
Typical problems in arable areas
1. 2.
3. 4.
5.
1. Exposed arable soils in the
winter months
2. Field drain and ditch
discharge to rivers
3. Grazing of fodder crops
4. Rill and gully formation on
steep, cultivated slopes
5. Cultivation practices:
ploughing downslope
Conceptualising the sediment cascade
Receptor Delivery Mobilisation Source
Potential source mitigation options
Method Efficacy Farm scale
costs
Mean Range Mean Range
Reduce field stocking rates when soils are
wet
25 10–50 5413 3419-
7814
Move feeder rings at regular intervals 10 2-25 1190 928-
1461
Construct troughs with a concrete base 10 2-25 394 333-
451
Do not apply manure to high risk areas 25 10-50
Do not spread slurry or poultry manure at
high risk times
50 10-95
Potential mobilisation mitigation options
Method Efficacy Farm scale
costs
Mean Range Mean Range
Loosen compacted soil layers in grass fields 25 10–50 1425 1104-
1745
Establish cover crops in the autumn 80 50-95 3843 3612-
4058
Cultivate compacted tillage layers 25 10-50 3276 2532-
4004
Incorporate manure into the soil 50 25-80 8417 7670-
9177
Use slurry injection application techniques 50 25-80 1151 447-
1844
Potential delivery mitigation options
Method Efficacy Farm scale
costs
Mean Range Mean Range
Re-site gateways away from high risk areas 10 2-25 1314 1196-
1438
Farm track management 50 10-95 190 158-
223
Cultivated and drill across the slope 25 10-50 812 628-
995
Establish new hedges 10 2-25 2025 1757-
2297
Potential receptor mitigation options
Method Efficacy Costs
Mean Range Mean Range
Fence off rivers and streams from livestock 50 10-95 926 801-
1050
Construct bridges for livestock crossing 80 50-95 944 732-
1154
Locate out-wintered stock away from
watercourses
2 0-10 165 150-
179
Riparian buffer strips 50 25-80 505 405-
606
Listening to farmer preferences for options
Mitigation measure
Establish cover crops in the autumn
Adopt reduced cultivation systems
Cultivate compacted tillage soils
Manage over-winter tramlines
Loosen compacted soil layers in grassland fields
Ditch management on arable land
Ditch management on grassland
Move feeders at regular intervals
Increase the capacity of farm slurry stores to improve timing of slurry applications
Install covers to slurry stores
Minimise the volume of dirty water produced (sent to dirty water store)
Minimise the volume of dirty water produced (sent to slurry store)
Store solid manure heaps on an impermeable base and collect effluent
Use slurry injection application techniques
Incorporate manure into the soil
Fence off rivers and streams from livestock
Construct bridges for livestock crossing rivers/streams
Re-site gateways away from high-risk areas
Farm track management
Establish new hedges
Listening to farmer preferences for options
Challenges for on-farm sediment mitigation
Farm incomes – note not profit and commodity prices
Challenges for on-farm sediment mitigation
General poor management – e.g. maintaining cover
Challenges for on-farm sediment mitigation
General poor management – e.g. compaction and runoff
problems
Challenges for on-farm sediment mitigation
General poor management – e.g. maintenance of buffer leading
edges
Riparian
buffer
efficacy
statistics
(0-2 m
leading
edge)
Avon Wensum Eden All DTCs
Mean 71 93 97 86
SE Mean 13 4 3 6
Median 78 92 100 92
Range 55 13 8 63
Minimum 37 87 92 37
Maximum 92 100 100 100
Challenges for on-farm sediment mitigation
Grass re-seeds and specific crops are high risk for soil loss during cultivation,
establishment and post harvest phases
Challenges for on-farm sediment mitigation
Targeted advice – e.g. remembering treatment-trains
Challenges for on-farm sediment mitigation
Due consideration of common configurations of risk
Challenges for on-farm sediment mitigation
Due consideration of the drain flow pathway
0
10
20
30
40
50
60
70
Pre-1939 1940s 1950s 1960s 1970s 1980s 1990s Unknown
Relativefrequency(%)
Drain age
Drain age distribution
Hampshire Avon
Wensum
Eden
Challenges for on-farm sediment mitigation
Current low impacts at landscape scale
Challenges for on-farm sediment mitigation
Cross sector sediment source apportionment
72
22
5
1
Agriculture
Urban
Channel banks
STWs
Challenges for on-farm sediment mitigation
Source-specific sediment impacts on aquatic ecology
Challenges for on-farm sediment mitigation
Interactions with hydromorphology
Challenges for on-farm sediment mitigation
Overriding effect of hydro-climatic patterns
The sustainable intensification agenda
SI
Environmental
SocialEconomic
Concluding remarks
• mitigation of agricultural
sediment losses must be part of
whole-farm, multi-pollutant
intervention planning and must
cover inorganic and organic
components of sediment
pressure
• on-farm sediment management
is only part of the solution to
cross sector catchment
sediment problems
• the current SI agenda should be
seen as an opportunity, not a
barrier, for sediment
management

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On-farm measures for sediment control: options, impacts and challenges

  • 1. Rothamsted Research where knowledge grows Rothamsted Research where knowledge grows On-farm measures for sediment control: options, impacts and challenges Adie Collins SILTFLUX workshop, UCD, Dublin, February 2016
  • 2. Water policy and on-farm interventions
  • 3. Parallel work streams Fundamental empirical evidence Evidence synthesis for national policy support On-farm measures for sediment control
  • 4. The scale challenge for sediment mitigation Measure scale Farm scale Landscape scale control realism
  • 6. Example policy questions to the DTCs • How can you extrapolate mitigation efficacy from a single measure to a series of interconnected measures? • How much of an improvement in terms of receptors can we attain by implementing mitigation? • To what extent does targeting only part of the anthropogenic pressures on water bodies allow us to achieve significant improvement in status? • How long will it take for mitigation interventions to: (i) meet a set pollutant threshold (WFD related targets) at a given point in a catchment and (ii) achieve an ecological response?
  • 7. Targets for guiding sediment management
  • 8. Targets for guiding sediment management
  • 9. Overarching questions • how do you best characterise ‘the problem’? • what are the technical remedies? • how do you best get farmers more engaged? • what are the challenges for delivering positive outcomes from targeted on-farm interventions?
  • 10. Defining sediment as a stressor
  • 11. Typical problems in livestock areas 1. 4. 6. 2. 5. 7. 3. 1.Poached surface soils 2.Over-full FYM store 3.Dirty yard by parlour 4.Drain connecting 3. to stream 5.Runoff from 2. to stream 6.Timing of slurry applications 7.Farm track channelisation
  • 12. Typical problems in arable areas 1. 2. 3. 4. 5. 1. Exposed arable soils in the winter months 2. Field drain and ditch discharge to rivers 3. Grazing of fodder crops 4. Rill and gully formation on steep, cultivated slopes 5. Cultivation practices: ploughing downslope
  • 13. Conceptualising the sediment cascade Receptor Delivery Mobilisation Source
  • 14. Potential source mitigation options Method Efficacy Farm scale costs Mean Range Mean Range Reduce field stocking rates when soils are wet 25 10–50 5413 3419- 7814 Move feeder rings at regular intervals 10 2-25 1190 928- 1461 Construct troughs with a concrete base 10 2-25 394 333- 451 Do not apply manure to high risk areas 25 10-50 Do not spread slurry or poultry manure at high risk times 50 10-95
  • 15. Potential mobilisation mitigation options Method Efficacy Farm scale costs Mean Range Mean Range Loosen compacted soil layers in grass fields 25 10–50 1425 1104- 1745 Establish cover crops in the autumn 80 50-95 3843 3612- 4058 Cultivate compacted tillage layers 25 10-50 3276 2532- 4004 Incorporate manure into the soil 50 25-80 8417 7670- 9177 Use slurry injection application techniques 50 25-80 1151 447- 1844
  • 16. Potential delivery mitigation options Method Efficacy Farm scale costs Mean Range Mean Range Re-site gateways away from high risk areas 10 2-25 1314 1196- 1438 Farm track management 50 10-95 190 158- 223 Cultivated and drill across the slope 25 10-50 812 628- 995 Establish new hedges 10 2-25 2025 1757- 2297
  • 17. Potential receptor mitigation options Method Efficacy Costs Mean Range Mean Range Fence off rivers and streams from livestock 50 10-95 926 801- 1050 Construct bridges for livestock crossing 80 50-95 944 732- 1154 Locate out-wintered stock away from watercourses 2 0-10 165 150- 179 Riparian buffer strips 50 25-80 505 405- 606
  • 18. Listening to farmer preferences for options Mitigation measure Establish cover crops in the autumn Adopt reduced cultivation systems Cultivate compacted tillage soils Manage over-winter tramlines Loosen compacted soil layers in grassland fields Ditch management on arable land Ditch management on grassland Move feeders at regular intervals Increase the capacity of farm slurry stores to improve timing of slurry applications Install covers to slurry stores Minimise the volume of dirty water produced (sent to dirty water store) Minimise the volume of dirty water produced (sent to slurry store) Store solid manure heaps on an impermeable base and collect effluent Use slurry injection application techniques Incorporate manure into the soil Fence off rivers and streams from livestock Construct bridges for livestock crossing rivers/streams Re-site gateways away from high-risk areas Farm track management Establish new hedges
  • 19. Listening to farmer preferences for options
  • 20. Challenges for on-farm sediment mitigation Farm incomes – note not profit and commodity prices
  • 21. Challenges for on-farm sediment mitigation General poor management – e.g. maintaining cover
  • 22. Challenges for on-farm sediment mitigation General poor management – e.g. compaction and runoff problems
  • 23. Challenges for on-farm sediment mitigation General poor management – e.g. maintenance of buffer leading edges Riparian buffer efficacy statistics (0-2 m leading edge) Avon Wensum Eden All DTCs Mean 71 93 97 86 SE Mean 13 4 3 6 Median 78 92 100 92 Range 55 13 8 63 Minimum 37 87 92 37 Maximum 92 100 100 100
  • 24. Challenges for on-farm sediment mitigation Grass re-seeds and specific crops are high risk for soil loss during cultivation, establishment and post harvest phases
  • 25. Challenges for on-farm sediment mitigation Targeted advice – e.g. remembering treatment-trains
  • 26. Challenges for on-farm sediment mitigation Due consideration of common configurations of risk
  • 27. Challenges for on-farm sediment mitigation Due consideration of the drain flow pathway 0 10 20 30 40 50 60 70 Pre-1939 1940s 1950s 1960s 1970s 1980s 1990s Unknown Relativefrequency(%) Drain age Drain age distribution Hampshire Avon Wensum Eden
  • 28. Challenges for on-farm sediment mitigation Current low impacts at landscape scale
  • 29. Challenges for on-farm sediment mitigation Cross sector sediment source apportionment 72 22 5 1 Agriculture Urban Channel banks STWs
  • 30. Challenges for on-farm sediment mitigation Source-specific sediment impacts on aquatic ecology
  • 31. Challenges for on-farm sediment mitigation Interactions with hydromorphology
  • 32. Challenges for on-farm sediment mitigation Overriding effect of hydro-climatic patterns
  • 33. The sustainable intensification agenda SI Environmental SocialEconomic
  • 34. Concluding remarks • mitigation of agricultural sediment losses must be part of whole-farm, multi-pollutant intervention planning and must cover inorganic and organic components of sediment pressure • on-farm sediment management is only part of the solution to cross sector catchment sediment problems • the current SI agenda should be seen as an opportunity, not a barrier, for sediment management