Erosion in recreational areas is often triggered by vegetation removal as a result of activities like walking, horse-riding, camping, motor vehicle use, mountain bike riding, and development of visitor facilities. Sandy soils in two geomorphic settings were investigated for potential differences in erosion patterns and conservation practices. On a coastal sand dune (100% coarse sand) leading to a popular beach, fencing provided regulated access via rill-eroded, 2 m-wide paths over slopes ranging from 6.5 to 10 degrees and slope lengths from 35 to 45 m. Conservation measures on back-dune paths included repeated spreading of off-site silt/clay-based fill and/or road metal, later replaced by concreting. On the seaward-facing paths where potential erosion rates were estimated to be >10 times those on adjacent vegetated areas, a below-surface board-and-chain system was replaced on some paths by low maintenance solid-surface plastic pavers. In a second area, relic cliff-top dunes were traversed by a 26- km walking track with non-vegetated and unfenced pathway segments 1-3 m wide. Soil texture of the cliff-top dune was dominated by coarse sands (coarse:fine:silt of 91:9:
Erosion in recreational areas is often triggered by vegetation removal as a result of activities like walking, horse-riding, camping, motor vehicle use, mountain bike riding, and development of visitor facilities. Sandy soils in two geomorphic settings were investigated for potential differences in erosion patterns and conservation practices. On a coastal sand dune (100% coarse sand) leading to a popular beach, fencing provided regulated access via rill-eroded, 2 m-wide paths over slopes ranging from 6.5 to 10 degrees and slope lengths from 35 to 45 m. Conservation measures on back-dune paths included repeated spreading of off-site silt/clay-based fill and/or road metal, later replaced by concreting. On the seaward-facing paths where potential erosion rates were estimated to be >10 times those on adjacent vegetated areas, a below-surface board-and-chain system was replaced on some paths by low maintenance solid-surface plastic pavers. In a second area, relic cliff-top dunes were traversed by a 26- km walking track with non-vegetated and unfenced pathway segments 1-3 m wide. Soil texture of the cliff-top dune was dominated by coarse sands (coarse:fine:silt of 91:9:
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Capararo, G., Mitchell, P., 1995. Fantastic plastic – geotextiles stabilise a walking track. Aust. J. Soil Water Conserv. 8, 21-25.
Ciccarelli, D., 2014. Mediterranean coastal sand dune vegetation: influence of natural and anthropogenic factors. Environ. Manage. 54, 194-204.
Cole, D.N., 1986. Recreational impacts on backcountry campsites in Grand-Canyon-National-Park, Arizona, USA. Environ. Manage. 10 (5), 651-659.
Cole, D.N., Spildie, D.R., 1998. Hiker, horse, and llama trampling effects on native vegetation in Montana, USA. J. Environ. Manage. 53, 61-71.
De Luca, E., Novelli, C., Barbato, F., Menegoni, P., Iannetta, M., Nascetti, G., 2011. Coastal dune systems and disturbance factors: monitoring and analysis in central Italy. Environ. Monit. Assess. 183, 437-450.
Department of Agriculture and Department of the Environment, 2012. Maroubra Beach dunes on the mend. http://www.nrm.gov.au/funding/approved/pre- 2008/nsw/sydm/2006-03.html Accessed 24 January 2014
Dragovich, D., Bajpai, S., 2012. Visitor attitudes and erosional impacts on the Coast Walk, Royal National Park. Proc. Linnean Soc. NSW 134, B113-B118.
Gager, P., Conacher, A., 2001. Erosion of access tracks in Kalamunda National Park, Western Australia: causes and management implications. Aust. Geogr. 32, 343-357.
Kutiel, P., Eden, E., Zhevelev, Y., 2000. Effect of experimental trampling and off-road motorcycle traffic on soil and vegetation of stabilized coastal dunes, Israel. Environ. Conserv. 27 (1), 14-23.
Monsef, H.A., Abahussain, A., 2013. The impact of camping activities on soil degradation in Kuwait. J. Environ. Inform. 22 (2), 102-111.
Morgan, R.P.C., Duzant, J.H., 2008. Modified MMF (Morgan-Morgan-Finney) model for evaluating effects of crops and vegetation cover on soil erosion. Earth Surf. Process. Landforms 32, 90-106.
Newsome, D., Milewski, A., Phillips, N., Annear, R., 2002. Effects of horse riding on National Parks and other natural ecosystems in Australia: implications for management. J. Ecotourism 1, 52-74.
Olive, N.D., Marion, J.L., 2009. The influence of use- related, environmental, and managerial factors on soil loss from recreational trails. J. Environ. Manag. 90, 1483-1493.
Phillips, N., Newsome, D., 2002. Understanding the impacts of recreation in Australian protected areas: Quantifying damage caused by horse riding in D’Entrecasteaux National Park, Western Australia. Pacific Conserv. Biol. 7 (4), 256-273.
Randall, M., Newsome, D., 2008. Assessment, evaluation and a comparison of planned and unplanned walk trails in coastal south-western Australia. Conserv. Sci. W. Aust. 7 (1), 19-34.
Randall, M., Newsome, D., 2009. Changes in the soil micro-topography of two coastal hiking trails in south-western Australia. Conserv. Sci. W. Aust. 7 (2), 279-299.
Randwick City Council, 1996. Maroubra Beach: Plan of Management overview. Prepared for Randwick City Council by Hassell Pty. Ltd. 37p.
Wilson, J.P., Seney, J.P., 1994. Erosional impact of hikers, horses, motorcycles, and off-road bicycles on mountain trails of Montana. Mountain Res. Develop. 14, 77-88.
Wimpey, J., Marion, J.L., 2011. A spatial exploration of informal trail networks within Great Falls Park, VA. J. Environ. Manage. 92, 1012-1022.
Zierholz, C., Hairsine, P., Booker, F.,1995. Run-off and soil erosion in bushland following the Sydney bushfires. Aust. J. Soil Water Conserv. 8, 28-37.