A “Best Management Practice” is a term used in the United States and Canada to describe an action of water pollution control. These practices range from ensuring a riparian corridor or a “filter strip” to capture nutrient run-off, to fencing off riparian corridors to protect stream banks, to active stream bank restoration. Below briefly describes a variety of these practices. This information is taken directly from Appendix C of the Lake Helena Watershed Restoration Plan.
Bioengineered treatments used to stabilize and protect banks of streams or constructed channels, and shorelines of lakes or reservoirs. Biological, mechanical, and ecological concepts are synthesized to control erosion and stabilize soil through the use of vegetation. Tree and root wad revetments are used in place of or in combination with rock. This practice may require deflection of water away from the target reach. Bioengineering treatments are developed systematically, taking
into consideration the causes of erosion and the upstream and downstream effects of the treatment and changes that may occur in the watershed hydrology and sedimentation over the design life of the treatments. Vegetation used in bioengineered treatments must be native or compatible with native habitat. Treatments that include woody debris, woody riparian vegetation, or other treatments that provide shade and cover can improve fish and wildlife habitat in addition to water quality benefits.
Bioengineering treatments are usually, but not always, much less expensive than traditional methods of streambank erosion control. Allen and Leech (1997) note that costs can vary tremendously due to differences in the availability of materials, hauling distances, labor rates, project objectives, and other factors. Maintenance costs over the life-cycle of the treatment must be considered. Allen and Leech (1997) present comparisons of actual costs of bioengineering treatments with estimated costs of traditional rip-rapped revetments under similar conditions in the same area.
A strip of permanent perennial vegetation placed on the down-gradient edge of a field, pasture, barnyard, animal confinement area or some types of impervious urban/transportation areas. The strip can slow surface runoff, filter particulate matter, or absorb and use nutrients. If the purpose of the strip is to take up nutrients, the vegetation must be periodically harvested in order to prevent nutrient buildup. Grazing would not constitute harvesting because nutrients are
deposited as well as removed.
An off-stream watering facility is a permanent or portable device to provide an adequate amount and quality of drinking water for livestock and wildlife. The device and its location should encourage or enable livestock to obtain water from a
source other than a surface water body.
Off-stream watering facilities can help livestock meet daily water requirements and improve animal distribution. This practice is typically used in conjunction with riparian fencing.
Fencing used to permanently or temporarily control livestock access to riparian areas. Fencing may be used to prevent streambank trampling, reduce nutrient and pathogen pollution, or promote vegetative growth and plant species diversity. This practice is typically used in conjunction with off-stream watering.
Storm water runoff occurs when precipitation from rain or snowmelt flows over the ground. Impervious surfaces like driveways, parking lots, streets, and sidewalks prevent storm water from naturally soaking into the ground. Storm water carries debris, chemicals, dirt and other pollutants into the surface waters of the Lake Helena watershed. Storm water runoff can also pollute the Helena Valley aquifer. Residents and businesses can help to reduce pollution by not dumping
pollutants into storm drains and by doing the following: