A wood-strand material for wind erosion control: effects on total sediment loss, PM10 vertical flux, and PM10 loss.

Fugitive dust from eroding land poses risks to environmental quality and human health, and thus, is regulated nationally based on ambient air quality standards for particulate matter with mean aerodynamic diameter < or = 10 microm (PM10) established in the Clean Air Act. Agricultural straw has been widely used for rainfall-induced erosion control; however, its performance for wind erosion mitigation has been less studied, in part because straw is mobile at moderate wind velocities. A wood-based long-strand material has been developed for rainfall-induced erosion control and has shown operational promise for control of wind-induced erosion and dust emissions from disturbed sites. The purpose of this study was to evaluate the efficacy of both agricultural straw and wood-strand materials in controlling wind erosion and fugitive dust emissions under laboratory conditions. Wind tunnel tests were conducted to compare wood strands of several geometries to agricultural wheat straw and bare soil in terms of total sediment loss, PM10 vertical flux, and PM10 loss. Results indicate that the types of wood strands tested are stable at wind speeds of up to 18 m s(-1), while wheat straw is only stable at speeds of up to 6.5 m s(-1). Wood strands reduced total sediment loss and PM10 emissions by 90% as compared to bare soil across the range of wind speeds tested. Wheat straw did not reduce total sediment loss for the range of speeds tested, but did reduce PM10 emissions by 75% compared to a bare soil at wind speeds of up to 11 m s(-1).

[1]  Dale A. Gillette,et al.  The influence of wind velocity on the size distributions of aerosols generated by the wind erosion of soils , 1974 .

[2]  G. Stanhill,et al.  A Simple Instrument for the Field Measurement of Turbulent Diffusion Flux , 1969 .

[3]  D. Pietersma,et al.  Design and Aerodynamics of a Portable Wind Tunnel for Soil Erosion and Fugitive Dust Research , 1996 .

[4]  D. Armbrust Effectiveness of polyacrylamide (PAM) for wind erosion control , 1999 .

[5]  William G. Nickling,et al.  A THEORETICAL AND WIND TUNNEL INVESTIGATION OF THE EFFECT OF CAPILLARY WATER ON THE ENTRAINMENT OF SEDIMENT BY WIND , 1989 .

[6]  John Leys,et al.  Efficiencies of sediment samplers for wind erosion measurement , 1993 .

[7]  J. E. Pinder,et al.  Increased wind erosion from forest wildfire: implications for contaminant-related risks. , 2006, Journal of environmental quality.

[8]  B. Sharratt,et al.  Particulate matter concentration and air quality affected by windblown dust in the Columbia plateau. , 2006, Journal of environmental quality.

[9]  M. Majewski,et al.  African and Asian Dust: From Desert Soils to Coral Reefs , 2003 .

[10]  R. Littell SAS System for Mixed Models , 1996 .

[11]  Dale A. Gillette,et al.  Fine Particulate Emissions Due to Wind Erosion , 1977 .

[12]  Brenton Sharratt,et al.  Loss of soil and PM10 from agricultural fields associated with high winds on the Columbia Plateau , 2007 .

[13]  Randy B. Foltz,et al.  Comparison of erosion reduction between wood strands and agricultural straw , 2003 .

[14]  François Dulac,et al.  Control of atmospheric export of dust from North Africa by the North Atlantic Oscillation , 1997, Nature.

[15]  W. S. Chepil,et al.  DYNAMICS OF WIND EROSION: II. INITIATION OF SOIL MOVEMENT , 1945 .

[16]  D. S. Munro,et al.  Aerodynamic boundary-layer adjustment over a crop in neutral stability , 1975 .

[17]  W. Chepil PROPERTIES OF SOIL WHICH INFLUENCE WIND EROSION: IV. STATE OF DRY AGGREGATE STRUCTURE , 1951 .

[18]  Keith E. Gorzell Finding an Economic and Environmental Balance to the Technology of Producing Building Materials from Agricultural Crop Residue , 2001 .

[19]  J. Hunt,et al.  Dust resuspension without saltation. , 2000, Journal of geophysical research.

[20]  J. Wantz,et al.  Distribution of Extreme Winds in the Bonneville Power Administration Service Area , 1981 .

[21]  D. Peden,et al.  Air pollution in asthma: effect of pollutants on airway inflammation. , 2001, Annals of allergy, asthma & immunology : official publication of the American College of Allergy, Asthma, & Immunology.

[22]  J. E. Pinder,et al.  From dust to dose: Effects of forest disturbance on increased inhalation exposure. , 2006, The Science of the total environment.

[23]  D. Chandler,et al.  Geospatial assessment of agricultural lands critical to air quality on the Columbia Plateau, Washington State , 2004 .

[24]  D. Dockery,et al.  Acute respiratory effects of particulate air pollution. , 1994, Annual review of public health.

[25]  J. Dooley,et al.  Performance assessment of wood strand erosion control materials among varying slopes, soil textures, and cover amounts , 2006 .

[26]  H. Koren Associations between criteria air pollutants and asthma. , 1995, Environmental health perspectives.

[27]  D. Finn,et al.  April 1998 Asian dust event over the Columbia Plateau , 2001 .

[28]  Chris Houser,et al.  The emission and vertical flux of particulate matter <10 μm from a disturbed clay‐crusted surface , 2001 .

[29]  Control of organic dusts from bedding choppers in dairy barns. National Institute for Occupational Safety and Health. , 1999, Applied occupational and environmental hygiene.

[30]  W. S. Chepil,et al.  DYNAMICS OF WIND EROSION: V. CUMULATIVE INTENSITY OF SOIL DRIFTING ACROSS ERODING FIELDS , 1945 .

[31]  T. Zobeck,et al.  Chemical Constituents of Fugitive Dust , 2007, Environmental monitoring and assessment.

[32]  W. S. Chepil,et al.  DYNAMICS OF WIND EROSION: III. THE TRANSPORT CAPACITY OF THE WIND , 1945 .

[33]  G. Campbell,et al.  An Introduction to Environmental Biophysics , 1977 .