Skip links and keyboard navigation

Vegetated drains

Vegetated drains

Select from the tabs below

Other name/s

Grassed drain, vegetated drainage ditches, two-stage ditch

Description

Vegetated drains are open channels for conveying water, where vegetation covers most of the banks and bed. Drains are common throughout agriculture and aquaculture production areas. Traditionally, drains are sprayed and kept devoid of vegetation, but they can be readily modified and/or managed to promote vegetation and, in turn, improve water quality. The difference between drains and swales, is that swales are dry most of the time whereas drains often hold water for extended periods. Drains are usually located on flat and backwatered locations which results in them holding water. Some drains intercept groundwater, so they could treat both surface run-off and shallow groundwater.

Vegetated drains are often a best management practice in agricultural production systems to convey water away from production areas, whilst minimising erosion. They can have a secondary benefit as a treatment system. When used as a treatment system, vegetated drains work by slowing the water velocity (vegetation causes drag by increasing friction), causing settling of coarse to medium sediments. Nutrients and toxicants can also be removed through nitrification/denitrification, adsorption to the plant or soil material and uptake by vegetation[1][6]. Their effectiveness as a treatment system depends on site conditions and their design and management[3][2].

Figure 1 Well-vegetated drain on a cane farm in the Wet Tropics. Photo by Queensland Government

Facilitating vegetation growth within drains enhances their treatment potential, by increasing the residence time, providing a surface for the growth of biofilms and providing carbon and oxygen in the soils, which promotes nitrification/denitrification, the dominant nitrogen removal process[7][1]. Research shows that vegetated drains provide significantly higher nitrate removal than unvegetated drains[7] and that a non-vegetated drain would need to be 2-3 times longer than a vegetated drain to remove the same quantity of pesticide[5].

Vegetated drains can provide a pre-treatment function for other systems in a treatment train by preventing erosion, trapping coarse to medium sediments and removing some nutrients, prior to run-off entering other treatment systems such as treatment wetlands or bioreactors.

Effectiveness as a treatment system

A 460m long vegetated drain on a sugarcane farm in the Wet Tropics region removed over 50% of dissolved inorganic nitrogen (DIN)[3], the equivalent of 0.32kg/yr of DIN per metre of drain. This drain was effective at removing DIN as it contained patches of dense vegetation and had adequate hydrological characteristics to support denitrification, including[4]:

  • Consistent flow (i.e. not stagnant water), with a velocity over 0.04m/sec
  • Relatively high retention time.

When drains are built and managed using similar principles to a treatment wetland (i.e. mostly vegetated, adequate flow and retention time) they can remove DIN through denitrification. They generally do not remove as much DIN per hectare as a well-designed and maintained treatment wetland[3]. But drains are common in farming landscapes and could be modified and managed at minimal cost to increase their nitrogen removal capacity, making them relatively cost-effective. A drain on a sugaracne farm in the Wet Tropics region that was widened to slow water velocity, with vegetation allowed to establish, was estimated to remove DIN at a cost of $49 per kilogram[3]. This calculation included upfront design, project management and excavation costs (to widen the existing drain) and maintenance costs, including sediment removal every 10 years. Costs would be considerably less if a landowner were able to conduct the work with their own equipment.

The actual cost-effectiveness of a vegetated drain will vary for each individual site. The cost-effectiveness needs to be considered relative to other treatment systems or management intervention options. Refer to cost considerations for more information.

Services and benefits

  • Bank stabilisation and reduced drain erosion
  • Water treatment (sediment, some nutrients and toxicants)
  • Saves time on maintenance (less spraying and excavation of sediment)

Drains can have trees planted on the edge for habitat purposes and to provide other services, however the focus of this content is on water quality improvement.

Disclaimer

In addition to the standard disclaimer located at the bottom of the page, please note the content presented is based on published knowledge of treatment systems. Many of the treatment systems described have not been trialled in different regions or land uses in Queensland. The information will be updated as new trials are conducted and monitored. If you have any additional information on treatment systems or suggestions for additional technologies please contact us using the feedback link at the bottom of this page.


References

  1. ^ a b DeBose, J, Coppo, C, McIntyre, R, Nelson, P, Karim, F, Davis, A & Brodie, J (2014), Effectiveness of vegetated systems in managing contaminated runoff from sugarcane and banana farms to protect off-farm aquatic ecosystems, particularly the Great Barrier Reef, vol. 14/10, p. 115pp., TropWater - Centre for Tropical Water and Aquatic Ecosystem Research - James Cook University, Townsville, Qld..
  2. ^ Department of Employment, EDI (2011), Wetland Management Handbook: Farm Management Systems (FMS) guidelines for managing wetlands in intensive agriculture.. [online], Queensland Wetlands Program, Brisbane. Available at: https://wetlandinfo.des.qld.gov.au/resources/static/pdf/resources/reports/fms/fms_025_handbook_web.pdf.
  3. ^ a b c d Kavehei, E, Hasan, S, Wegscheidl, C, Griffiths, M, Smart, JCR, Bueno, C, Owen, L, Akrami, K, Shepherd, M, Lowe, S & Adame, MF (22 November 2021), 'Cost-Effectiveness of Treatment Wetlands for Nitrogen Removal in Tropical and Subtropical Australia', Water. [online], vol. 13, no. 22, p. 3309. Available at: https://www.mdpi.com/2073-4441/13/22/3309 [Accessed 21 December 2021].
  4. ^ Kavehei, E & Adame, F (2021), Vegetated drains for water quality improvement in the Wet Tropics, vol. ARI report No. 2021/Australian Rivers Institute, Griffith University, Brisbane.
  5. ^ Moore, MT, Denton, DL, Cooper, CM, Wrysinski, J, Miller, JL, Reece, K, Crane, D & Robins, P (March 2008), 'Mitigation Assessment of Vegetated Drainage Ditches for Collecting Irrigation Runoff in California', Journal of Environmental Quality. [online], vol. 37, no. 2, pp. 486-493. Available at: http://doi.wiley.com/10.2134/jeq2007.0172 [Accessed 26 May 2022].
  6. ^ Reichenberger, S, Bach, M, Skitschak, A & Frede, H (2007), 'Mitigation strategies to reduce pesticide inputs into ground- and surface water and their effectiveness; a review.', Science of the Total Environment, vol. 384, pp. 1-35.
  7. ^ a b Soana, E, Balestrini, R, Vincenzi, F, Bartoli, M & Castaldelli, G (June 2017), 'Mitigation of nitrogen pollution in vegetated ditches fed by nitrate-rich spring waters', Agriculture, Ecosystems & Environment. [online], vol. 243, pp. 74-82. Available at: https://linkinghub.elsevier.com/retrieve/pii/S0167880917301597 [Accessed 26 May 2022].

Last updated: 24 May 2022

This page should be cited as:

Department of Environment and Science, Queensland (2022) Vegetated drains, WetlandInfo website, accessed 5 October 2022. Available at: https://wetlandinfo.des.qld.gov.au/wetlands/management/treatment-systems/for-agriculture/treatment-sys-nav-page/vegetated-drains/

Queensland Government
WetlandInfo   —   Department of Environment and Science