Combining Tools from Edge-of-Field to In-Stream to Attenuate Reactive Nitrogen along Small Agricultural Waterways
Abstract
:1. Introduction
- managing small waterways to elicit effective change in the receiving environment,
- targeting local N export dynamics and underlying hydrological variability from agricultural land to waterways, and
- overcoming factors limiting N attenuation with suites of edge-of-field to waterway-based tools at multiple scales and locations. We also emphasize the need to
- encourage codevelopment of novel, effective, multiple-tool, multiple-scale waterway N attenuation approaches by scientists, practitioners, and farming communities to overcome the technical and practical challenges to managing N in agricultural landscapes.
2. Understanding and Managing for N Export Variability along Small Waterways
3. Expanding the N Toolbox to Boost Effectiveness from the Field Edge to In-Stream
4. Moving Forward: Codeveloping and Implementing N Attenuation Toolboxes on Working Farms
5. Conclusions
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
References
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Location | N Attenuation Tool | Baseflow Versus Stormflow Attenuation | Intercepted Hydraulic Flow Pathway | Effect in the Receiving Environment | Benefits and Disbenefits | Example |
---|---|---|---|---|---|---|
Edge-of-field | Exclude livestock | baseflow, stormflow | surface drains/streams, standing water, surface runoff | decreased load | B: reduced stock losses, aesthetics D: fence maintenance, alternative drinking water sources, and potential weed management issues | [60,61,62] |
Redirect subsurface drainage (e.g., controlled drainage) | baseflow, stormflow | tile drains | decreased load, decreased concentration peaks | B: soil water storage, flood attenuation D: requires active management | [63,64,65,66] | |
Detain water (e.g., retention/detention bunds, ponds, or basins) | stormflow | standing surface water, surface runoff | decreased load, decreased concentration peaks | B: soil water storage, flood attenuation, can reduce drain clearance costs D: requires active management | [67,68,69,70] | |
Retain grass filter strips and swales | stormflow | surface runoff, surface drains | decreased load, decreased concentration peaks | D: potential weed management issues | [71,72,73] | |
Install denitrification beds or walls | baseflow | tile drains, subsurface flow | decreased load | B: little reduction of productive land D: initial flush of organic carbon, anoxic effluent, dissolved phosphorus release under anoxia, greenhouse gas production | [74,75,76,77] | |
Riparian buffer/floodplain | Construct or enhance wetlands | baseflow, stormflow | floods, surface drains, tile drains, standing surface water, subsurface flow | decreased load, decreased concentration peaks | B: able to cope with fluctuating water levels, stock water supply, waterfowl habitat, flood attenuation, recreation, biodiversity value, landscape aesthetics D: source of avian E.coli, dissolved phosphorus release under anoxia, greenhouse gas production, nutrient impacts on natural wetland ecology | [78,79,80,81] |
Disconnect tile drains to saturate riparian buffer | baseflow | tile drains | decreased load | B: soil water storage, flood attenuation D: requires active management | [40,82,83,84] | |
Plant riparian vegetation | baseflow | surface flow, subsurface flow | decreased load, decreased concentration peaks | B: channel shading, improved aquatic habitat, wood and leaf supply to stream, recreation, harvesting of biomass, biodiversity value, landscape aesthetics D: requires some active vegetation management, shading might suppress in-stream nutrient uptake | [85,86,87] | |
Within channel margins | Reshape stream banks | baseflow, stormflow | subsurface flow, surface drains/streams, floods | decreased load, decreased concentration peaks | B: able to cope with fluctuating water levels | [24,88,89] |
Create meander bends | baseflow | surface drains/streams | decreased load, decreased concentration peaks | B: able to cope with fluctuating water levels, flood attenuation, biodiversity value, landscape aesthetics | [24,90,91] | |
Create inset floodplains (e.g., two-stage channels) | baseflow, stormflow | surface drains/streams, tile drains, floods | decreased load, decreased concentration peaks | B: able to cope with fluctuating water levels, flood attenuation, biodiversity value | [92,93,94,95] | |
Widen channel | baseflow, stormflow | surface drains/streams, floods | decreased load | B: able to cope with fluctuating water levels, flood attenuation D: potential sedimentation issues, weed management | [24,96,97] | |
Vegetate channel or maintain in-ditch vegetation | baseflow | surface drains/streams | decreased load, decreased concentration peaks | B: forage crop for stock, biodiversity value D: potential heightened flood risk, sedimentation issues, requires active management | [98,99,100] | |
In-stream | Add in-stream geomorphic features (e.g., boulders, riffles) | baseflow | surface drains/streams | decreased load | B: biodiversity value, landscape aesthetics D: heightened winter flood risk | [24,101,102] |
Add debris dams/ low-grade weirs | baseflow, stormflow | surface drains/streams, floods | decreased load, decreased concentration peaks | B: able to cope with fluctuating water levels D: heightened winter flood risk | [30,103,104] | |
Add large woody debris | baseflow | surface drains/streams | decreased load | B: biodiversity value, landscape aesthetics D: heightened winter flood risk | [24,29,105] | |
Add organic matter (e.g., leaves, small wood) | baseflow | surface drains/streams | decreased load | B: biodiversity value D: heightened winter flood risk | [106,107,108,109] | |
Add in-stream bioreactors | baseflow | surface drains/streams | decreased load | D: initial flush of organic carbon, anoxic effluent, dissolved phosphorus release under anoxia, greenhouse gas production | [110,111,112,113] |
Location | N Attenuation Tool | Dominant Attenuation Mechanisms 1 | Increases Filtering, Deposition or Adsorption | Increases Water Retention Time | Enhances Surface-to-Groundwater Exchange | Increases Surface Area-to-Volume Ratio (Contact with Soil and Benthos) | Promotes Contact with Vegetation or Algae and Organic Soils or Substrates |
---|---|---|---|---|---|---|---|
Edge-of-field | Exclude livestock | P | + + + | ||||
Redirect subsurface drainage (e.g., controlled drainage) | M, B | + + + | + + | + + | |||
Detain water (e.g., retention/detention bunds, ponds, or basins) | P, M | + + + | + + + | + + | + + | + | |
Retain grass filter strips and swales | P, M, B | + + + | + | + | + + | + + | |
Install denitrification beds or walls | M, P | + | + + | + + + | |||
Riparian buffer/floodplain | Construct or enhance wetlands | M, B, P | + + | + + + | + | + + | + + + |
Disconnect tile drains to saturate riparian buffer | M, B | + + | + + + | + | + + | + + + | |
Plant riparian vegetation | M, B, P | + + | + | + + + | |||
Within channel margins | Reshape stream banks | B, M, P | + | + | + | + | |
Create meander bends | M, B | + | + | + | + + | ||
Create inset floodplains (e.g., two-stage channels) | M, B, P | + | + | + | + + | + + + | |
Widen channel | M, B | + + | + | + + | |||
Vegetate channel or maintain in-ditch vegetation | M, B | + | + | + + + | |||
In-stream | Add in-stream geomorphic features (e.g., boulders, riffles) | M, B, P | + + | + | + | + | |
Add debris dams/low-grade weirs | M, B, P | + + | + + | + | |||
Add large woody debris | M, B | + + | + + | + | + | ||
Add organic matter (e.g., leaves, small wood) | M, B | + + | + | + | |||
Add in-stream bioreactors | M, P | + + + | + + + |
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Goeller, B.C.; Febria, C.M.; McKergow, L.A.; Harding, J.S.; Matheson, F.E.; Tanner, C.C.; McIntosh, A.R. Combining Tools from Edge-of-Field to In-Stream to Attenuate Reactive Nitrogen along Small Agricultural Waterways. Water 2020, 12, 383. https://doi.org/10.3390/w12020383
Goeller BC, Febria CM, McKergow LA, Harding JS, Matheson FE, Tanner CC, McIntosh AR. Combining Tools from Edge-of-Field to In-Stream to Attenuate Reactive Nitrogen along Small Agricultural Waterways. Water. 2020; 12(2):383. https://doi.org/10.3390/w12020383
Chicago/Turabian StyleGoeller, Brandon C., Catherine M. Febria, Lucy A. McKergow, Jon S. Harding, Fleur E. Matheson, Chris C. Tanner, and Angus R. McIntosh. 2020. "Combining Tools from Edge-of-Field to In-Stream to Attenuate Reactive Nitrogen along Small Agricultural Waterways" Water 12, no. 2: 383. https://doi.org/10.3390/w12020383
APA StyleGoeller, B. C., Febria, C. M., McKergow, L. A., Harding, J. S., Matheson, F. E., Tanner, C. C., & McIntosh, A. R. (2020). Combining Tools from Edge-of-Field to In-Stream to Attenuate Reactive Nitrogen along Small Agricultural Waterways. Water, 12(2), 383. https://doi.org/10.3390/w12020383