May - June 2002

By Lakes' Restless Edge

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Water, wind, and waves drive dynamic processes that both erode shorelines and sustain them. Smart development recognizes these processes and gives them wiggle room.

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By Martha S. Mitchell

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Cultural Impacts in the Shore Zone

Some sediment-filled lakes will persist for a time as meadows before the fill is eroded away.
The detritus from landslides can impound streams in their own valleys.

Several anthropogenic forces that can upset this balance are the creation of continuous hard surfaces, such as retaining walls in the wave zone, and artificially raising or lowering the lake level. The decision to install retaining walls usually centers on the need to protect an important investment from the reach of wave erosion. But after the sea wall is installed, breaking waves can no longer burn up their energy in the forward-tumbling waves. Instead, they crash against the wall, and the residual energy in the backswash carries away everything it still has competence to carry: the beach sand. Within several years, the beach might be gone, the wall is undermined, and–because longshore drift has been intensified and sped up–neighboring properties downdrift might begin to experience new beach erosion.

The effects of water-level manipulation can also starve lakeside beaches. As a general rule, waves move sand onshore in summer. If we stand in the shallows of a lakeside beach in summer and study the minute movements of sand in the ripple marks at our feet (while enjoying the fragile gold nets of ripple shadows dancing over them), we can see sand trickling toward the beach over each tiny underwater dune as the wavelets nudge shoreward. In winter, storm waves will move the sand offshore, where it will remain in subsurface bars until the gentle, persistent energy of summer wave regimes can move it back onshore again. If the water level is dropped for the winter, the higher-energy winter waves can move the terrace sands to offshore depths that might be inaccessible to summer waves when the water level is raised again.

When lake levels are artificially increased, as when lake outlets are raised to increase water storage, shoreline processes must begin anew to create equilibrium at the water's new edge. The sand of drowned beaches might be too deep to be carried ashore. It can take centuries or more for shoreline processes to create sandy beaches again. But first, the constant agitation of water at the new lake edge will steadily winnow soil from rock, releasing the soil's organics, sediments, minerals, and nutrients to the lake. Unforeseen water-quality problems might ensue.

Complex conditions and needs for land and water affect decisions about lake management.

When the water level is seasonally lowered on a created lake where deep soils are present along a young shore, a series of chronic erosion processes may be set in place. During lake lowering, the pressure differential between the atmosphere and the soil interstices may generate soil loss through piping. As the lake level drops, the roots of moisture-loving vegetation at the lake edge might end up perched above the water table, and these plants lose vigor or die. The loss of root structure to hold the exposed banks leaves them vulnerable to wave erosion. The action of waves on the banks can undercut them, which results in calving or toppling of the undercut soils. Finally, depending on its composition, the exposed soil might shrink and crack as it dries, and the outer edges of the soil might drop off in plates or chunks. Finally, if the lake is shallow, waves may have the capacity to stir up bottom sediments, affecting water quality in the lake itself as well as downstream water resources. These processes will operate with every drawdown in a complex cycle of chronic shoreline erosion.

Integrated Solutions

Every lake troubleshooting team should include a person knowledgeable about the geomorphic processes that contribute to shoreline and lake conditions. To solve shoreline erosion problems on a site-by-site basis, careful analysis is required to ensure that longshore drift is not impeded, that wave energy is not amplified by the treatment, that downdrift properties are not degraded by upshore treatments, and that shore-zone processes can operate at expected magnitudes for diurnal, seasonal, annual, and periodic events. Coastal engineering has made many recent advances with respect to these considerations.

Seasonal lowering of lake levels can kill lakeside plants by lowering the water table...
...setting the stage for bank undercutting by waves and toppling of upper banks
...and causing chronic soil loss due to piping and dessication

When lake turbidity is a concern, one of the first questions to ask is: What is the origin of the materials in suspension? Before a program is put in place to address the turbidity, monitoring should provide an answer to this question that is crystal clear. Many a lake manager have been startled to learn that increased turbidity is not the result of suspended sediments, as assumed, but of algae. Similarly, a problem of suspended fine colloids should not be assumed to be the result of such disturbances as logging or mining in tributary watersheds when it might, in fact, be the result of erosion processes set into motion by manipulation of the water level.

At a lakewide scale, a community-level effort is almost always needed to arrive at lasting solutions to widespread problems associated with shoreline armoring and lake-level manipulation. Effective problem-solving will require that lake managers, shoreline residents, and governments participate in a discovery and solution-building process. A technical team composed of both physical and biological scientists should be appointed to support the effort. By working together, cross-education takes place about the processes responsible for the problems as well as the potential solutions. The most successful and cost-effective solution will be the one that addresses the entire range of forces acting upon the shoreline and that considers avoided costs in addition to the long-term costs of alternatives.

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Some of the most exciting solutions are being developed by local, regional, and state governments in the form of shore-zone codes, ordinances, and development standards. This pioneering work is being done in such places as Lake Tahoe, where there is political will and funding resources to protect a water resource recognized as a national treasure. Other states and municipalities are working on marine, stream, and shoreline protection instruments whose creation has been spurred by the National Marine Fisheries Service's listing of cold-water and anadromous fish species, or by the requirements of the Clean Water Act. These efforts are ushering in a refreshing new era of preventative, administrative best management practices (BMPs) that have been a long time coming. At their heart is the recognition that shoreline processes are dynamic and must be protected to ensure protection of the ecological functions shores provide, including water-quality protection, beach nourishment, and maintenance of aquatic and littoral habitats.

The tools of these brave new BMPs are master planning, zoning, plan review, required setbacks and vegetative buffers, limitations on hard and impervious surfaces, and requirements for restoration of the undisturbed zone at the dynamic interface between the backshore and the foreshore. They hold tremendous promise for sustainable lakeside development. When these practices guide the location and nature of built environments in shore zones, planners are finding that they are effectual and cost-effective means of preventing human works from accelerating the rate of erosion at lakes' dynamic edges.

Author's Bio: Martha S. Mitchell, CPESC, is principal of ClearWater West Inc. (www.clearwaterwest.com), consultants in erosion and natural resource planning in Portland, OR.

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