the science of stream buffers lake george stream corridor management stakeholder meeting may 28,...
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The Science of Stream Buffers
Lake George Stream Corridor Management Stakeholder Meeting
May 28, 2008
About the Center forAbout the Center forWatershedWatershed ProtectionProtection
• Non-profit 501(c)3, non-advocacy organizationNon-profit 501(c)3, non-advocacy organization• Work with watershed groups, local, state, and Work with watershed groups, local, state, and
federal governmentsfederal governments• Provide tools communities need to protect Provide tools communities need to protect
streams, lakes, and riversstreams, lakes, and rivers• 20 staff in Ellicott City, MD and satellite Offices20 staff in Ellicott City, MD and satellite Offices
www.cwp.orgwww.cwp.orgwww.stormwatercenter.net www.stormwatercenter.net
Small Streams Small Streams Small Streams Small Streams
• 11stst and 2 and 2ndnd order 73% of order 73% of our stream miles (Leopold, our stream miles (Leopold, 1964)1964)
• Drain the majority of the Drain the majority of the landscape landscape
• Connected to a high Connected to a high percentage of our wetlandspercentage of our wetlands
• 11stst and 2 and 2ndnd order 73% of order 73% of our stream miles (Leopold, our stream miles (Leopold, 1964)1964)
• Drain the majority of the Drain the majority of the landscape landscape
• Connected to a high Connected to a high percentage of our wetlandspercentage of our wetlands
• Effective at processing Effective at processing nutrients nutrients
• Most frequently Most frequently disturbed during the disturbed during the development processdevelopment process
• Effective at processing Effective at processing nutrients nutrients
• Most frequently Most frequently disturbed during the disturbed during the development processdevelopment process
Juniper Inlet, FL: NOAA 1997
• Organic matter
• Shading
• Nutrient and sediment retention
• Bank stability
• Habitat for wildlife
Forested Stream ServicesForested Stream Services
Forested Streams
•Fallen leaves are the base of the food chain in small streams, and provide as much as 75% of the energy input to the food chain
•Woody debris enhances organic matter and nutrient retention, dissipates energy and reduces downcutting (Meyer and Wallace, 2001)
•An average nutrient molecule travels less than 20m downstream before being removed in a high quality small shallow stream (Webster et al, 2002)
Basics of Stream Buffers
• Stream buffers are more than a line on a map
• It is more than a setback• The floodplain is the core of the buffer• Management is just as important as width• Should be continuous
– Gaps can introduce additional surface flow
Water quickly runs off a shoreline cleared of natural vegetation, washing nutrients and pesticides into the water. A natural shoreline holds rainfall, which soaks into the soil; less water, soil and chemicals run into the lake or river. Shoreline and aquatic plants anchor shoreline areas, helping to protect them from erosion due to runoff and waves (Source:MN DNR)
Source: Minnesota Department of Natural Resources
Benefits of Stream Buffers
Environmental Economic / Community
How many can you name?
Environmental Benefits• Provides room for streams to safely adjust laterally over time• Provides additional streambank erosion protection• Provides distance from impervious cover• Helps prevent steep slope erosion and disturbance• Helps keep stream temperatures down• Pollutant removal
Sediment Phosphorus and nitrogen Bacteria
Source: Wenger, 1999
Temperature
• Many coldwater fish species have limited temperature range tolerance (e.g., trout)
• Stream warming from is caused by a variety of factors:– Loss of riparian cover (air temp in headwater
streams)– Impervious surfaces– Stormwater ponds
• 60% riparian forest cover retains temperature• 80% riparian forest lowers temperature
Sediment
• Sources - stream bank erosion- poor forestry, agriculture or mining practices- construction sites
• Impacts - reduced habitat for macroinvertebrates and fish- increased pollutants attached to sediment- increased cost to remove and dispose of sediment- potential for direct fish kill with high concentrations of fine, deposited sediment
Phosphorus
• Sources- generally accumulates attached to sediment particles- application of fertilizers on lawns and ag fields- animal waste and septic
• Impacts-Eutrophication of lakes-Shift in biota of stream systems
Economic/Community Benefits• Reduce public investment in stormwater management, flood control, and pollutant removal• Increase property values• Provide habitat for wildlife• Reduce watershed impervious cover• Help minimize flooding and associated property damage• Reduce time and expense of land maintenance, as compared to managed turf• Reduce small drainage problems and complaints
Stream Buffer Design
• Preferred widths– Sediment removal– Phosphorus/Nitrogen removal
• Special resource/protection areas
• Three-zone buffer design
• Allowable uses
Modified from: Emmons & Olivier Resources, 2001
Critical Buffer Widths
(EOR, 2001)
Buffer Widths and Pollutant Removal
Source: Wenger, 1999
Pollutant Removal Rate Necessary Width*
Sediment (as TSS)
66-93% 90 ft
78% 70 ft
94% 190 ft
Phosphorus (as TP)
See above
84% 164 ft
81% 92 ft
Temp N/A 30 ft of forest* Depends on slope, soils, infiltration rates, etc.
Special Resource/Protection Areas
• Base width should be expanded to include:– Ultimate 100 year floodplain– Very steep slopes greater than 25%
• Wetlands, critical habitats and forest conservation areas should have larger buffers
Three-Zone Buffer Design
• Each zone has different function, width, vegetative target, and management:
– Streamside zone: 25 feet of undisturbed forest cover
– Middle zone: 50 feet or more ofmanaged forest
– Outer zone: 25 feet of grass or forest setback from structures
Stream Buffer Crossings
• To minimize fish blockages, all crossings should follow these guidelines: – Width: minimum right of way needed for access– Angle: perpendicular to stream– Frequency: no more than one crossing/1000 feet– Depth: utilities three feet below streambed– Capacity: convey 100 year storm– Culverts: bottomless, slab, arch or box designs
preferred
Buffer Crossings
Buffer xing photo
Stream xing photo Minimize clearing required to create a buffer crossing.
Riparian Buffer Management
Riparian Buffer Management
Recommended Reading
• Emmons and Olivier Resources. Benefits of Wetland Buffers: A Study of Functions, Values and Sizes. http://www.minnehahacreek.org/documents/MCWD_Buffer_Study.pdf
• Meyer, J.L. and J.B. Wallace. 2001. Lost linkages and lotic ecology: rediscovering small streams. http://cwt33.ecology.uga.edu/publications/1444.pdf
• Sweeney, B.W., T.L. Bott, J.K. Jackson, L.A. Kaplan, J.D. Newbold, L.J. Standley, W.C. Hession, and R.J. Horwitz. 2004. Riparian Deforestation, Stream Narrowing, and Loss of Stream Ecosystem Services. Proceedings of the National Academy of Sciences 101(39):14132-14137. http://www.stroudcenter.org/about/pdfs/bs_PNAS092804.pdf
• Wenger, S. 1999. A review of the scientific literature on riparian buffer width, extent, and vegetation. Publication of the Office of Public Service and Outreach, Institute of Ecology, University of Georgia. 58pp.