September-October 2001

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Some Downwind Costs of Upwind Erosion

When the wind stops blowing and the dust finally settles, the impacts of airborne sediment can be felt in a surprisingly wide range of ways–often, far from where it left the earth.

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By Greg Northcutt

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Sometimes seemingly unrelated events in widely dispersed areas of the world can share a very common cause. Take, for example, a drop in numbers of silkworm cocoons in China . . . increased road maintenance costs in Kansas . . . lowered wheat production in Alberta . . . higher crop yields in Niger . . . reduced visibility in Puerto Rico . . . red sunsets in Wisconsin . . . a phytoplankton bloom in the Pacific Ocean . . . coral reefs dying off the coast of Florida . . . North African real estate moving to Bermuda . . . a 64-car pileup on a California freeway . . . and increased health risks to infants in the Southeast United States.

Those are just some of the impacts of wind-blown dust. And that doesn’t count the 12% of New Zealand’s landscape affected by wind erosion; the approximately 148 million ac. in India, especially western Rajasthan, where nearly 60% of the land is covered by sand dunes and sand plains; or northern China, where soil from 579,000 mi.2 of land is blowing in the wind. In the US, the Natural Resource Inventory, conducted every five years by the US Department of Agriculture’s Natural Resources Conservation Service, reveals that, in 1992, an estimated 2.84 billion tons of soil from some 781 million ac. of range and cropland went airborne. That represented nearly half of all soil eroded from these lands that year.

A Big Problem

On an even larger scale, wind-blown dust is the most prominent airborne particle visible from space. By one estimate, anywhere from about 990 to 1,650 tons of soil dust enters the world’s atmosphere each year. In fact, dust in the air has been fingered as one possible suspect in atmospheric instability and climate change–no small feat for tiny pieces of soil with an aerodynamic diameter of 10 microns or less. That’s so small that several hundred 10-micron particles could fit into the period at the end of this sentence. (USEPA identifies such particulate matter as PM10.)

Wind erosion events can range in size from whirling dust devils twisting their way across a field of bare soil on the Texas plains to the eruption of massive dust storms in the Sahara Desert, where the wind can move from 66 to 221 million tons of fine sediment each year. In February 2000, a gigantic dust storm generated in northwest Africa covered hundreds of thousands of square miles above the eastern Atlantic Ocean with a thick cloud of Saharan sand. Rising 15,000 ft. or higher into the air, this dust can be carried west by the trade winds as far as the Caribbean Sea, where other winds can drive the airborne sediment north to the New England area of the Northeast US.

This past spring, the US National Oceanic and Atmospheric Administration reported that sediment originating from a dust storm in northern China reached the US, "blanketing areas from Canada to Arizona with a layer of dust" and clouding views of the Rocky Mountains from the eastern foothills.

Three years earlier, on April 19, a dust storm in Mongolia and north-central China spawned a cloud of dust that reached North America near the Canada-US border six days later. There, part of it swung south, covering the area from British Columbia to California. The rest blew into the upper Midwest US and Ontario.

Russian scientist Guennady Larionov of Moscow State University’s Research Laboratory of Soil Erosion notes that an early 1970 dust storm in the southeast part of the Russian Plain, which includes the Lower Don, Lower Volga, North Caucasus, and adjacent areas of Ukraine, lasted about 200 hours. At one spot, about 28 in. of soil blew away.

From 1950 to 1990, he says, soil losses in this region of the Russian Plain totaled about 11.7 billion tons. "Part of this soil mass accumulated in shelterbelts and behind them in gullies and river valleys. But about 60% of this soil mass was suspended in the atmosphere, producing environmental problems far away from the source of the dust."

Sometimes the sheer size of dust storms is out of this world. The Mars Global Surveyor satellite has captured photos of Martian dust storms, some of which have covered the entire Red Planet.

The Erosion Process

The energy for detaching and transporting sediment by wind is produced by air under higher pressure moving to an area of lower pressure. The greater the differences in air pressure, the stronger the wind and the more disturbed, unprotected soil and friable rock it can erode.

At least two-thirds of dust events are caused by the passage of warm and cold fronts and downmixing of upper level winds, points out Tom Gill, a professor with the Atmospheric Science Group at Texas Tech University, Lubbock, TX. "However, cyclogenesis [development or strengthening of counterclockwise circulation in the atmosphere] and thunderstorm outflows or haboobs produce the most dramatic dust clouds with the lowest visibilities."

The wind transports sediments in three ways. Soil aggregates and particles too heavy to be picked up by the wind, such as combinations of silt and clay typically about 0.8—2.0 mm (800-2,000 microns) in diameter, move by creep as the wind or impact from other particles pushes them along the soil surface.

Sediment light enough to be lifted by the wind but too heavy to travel very far moves by saltation. These particles, about 0.1—0.8 mm (100-800 microns) hop along the ground, moving just a few inches at a time and rising no higher than about 2-4 in. above the soil surface. These saltating grains cause the most damage to crops, abrading leaves and stems of young plants. They also contribute finer soil particles to the air stream.

"Saltaters leave the ground at a trajectory of about 60º to the horizon and come gliding back at about a 12º angle," states Larry Hagen, a researcher with the USDA Wind Erosion Research Unit, based at Kansas State University in Manhattan, KS. "These hard, saltating particles bombard immobile soil clods and the soil crust, cutting and breaking them down and supplying suspension materials. Typically they include the PM10 size and smaller particles that pose a health hazard.

"In drier climates, you’ll find loose PM10 and smaller particles in the soil. However, in more humid areas, saltaters contribute the bulk of these small particles in the air. The PM2.5 particles are rarely found loose by themselves and are usually created by the action of saltaters colliding with larger aggregates."

These PM10, PM2.5, and other soil particles smaller than about 20-60 microns in size travel by suspension in the wind, reducing visibility and soil quality and contributing to health problems for humans, livestock, and wildlife. These are the particles that can travel hundreds and thousands of miles, remaining airborne until washed back to earth by rain.

"The proportions of creep, saltation, and suspension in eroded soil vary with surface roughness, soil composition, and size of the eroding surface," Hagen explains. "Part of the reason is that for a given wind speed and surface condition, there is a limited transport capacity for the saltation and creep. However, the atmosphere has a much higher transport capacity for suspension-size soil than for saltation/creep particles. Moreover, abrasion of the surface by saltation often creates large amounts of suspension-size aggregates in addition to that present in the soil. Thus, on large, eroding agricultural fields or dry lakebeds, such as Owens Lake in California, the soil moved by the suspension component typically is several times the soil moved by saltation/creep."

In a paper presented in 1997 at an international symposium and workshop on wind erosion in Manhattan, KS, researcher Weinan Chen of Big Spring, TX, reported results of a study of loessial sandy loam soils in the Loess Plateau of China. About 55-70% of the wind-eroded soils moved by saltation. Creep accounted for about 5-16% of soil loss, while 8-24% of the sediment was transported in suspension.

"The erosive force of wind increases exponentially with increases in wind speed. For example, increasing wind velocity from 8 to 10 meters per second doubles the erosion capacity, while increasing wind speed from 8 to 16 meters per second generates an eightfold increase. Consequently, fast winds are capable of causing much more erosion than slow winds.

"At ground level, the roughness of the surface plays an important role in controlling the nature of wind erosion," Chen continues. "Boulders, trees, buildings, shrubs, and even small plants like grass and herbs can increase the frictional roughness of the surface and reduce wind velocity. Vegetation can also reduce the erosion effects of wind by binding soil particles to roots. Thus, as a general rule, the areas that show considerable amounts of wind erosion are open locations with little or no plant cover."

The Agricultural Toll

The impacts of wind erosion can range from the relatively minor cost and inconvenience of cleaning dust and dirt from clothes, cars, and homes to major threats to human life and the environment. In the US, awareness of the costs of wind erosion swept into the national conscience in the 1930s when clouds of airborne sediment from bare, bone-dry fields in Oklahoma and other Midwest states darkened the skies as far east as the Atlantic seaboard. Forcing many families in the wind-prone areas to abandon their farms for a new life in California, the disastrous Dust Bowl also spawned creation of the USDA’s Soil Conservation Service, now called the Natural Resources Conservation Service, to help farmers adopt soil-saving farming and ranching practices. Even today, wind accounts for more than 40% of all soil eroded each year from fields and land placed in the federal Conservation Reserve Program in the US. In 1997, the annual wind erosion rate averaged 2 tons/ac. nationwide.

Wind erosion is a major cause of soil degradation on agricultural land in arid and semiarid areas throughout the world. These areas include North America; southern South America; much of North Africa and the Near East; parts of southern, central, and eastern Asia; the Siberian Plains; and Australia. Northwest China is also prone to severe soil losses from wind. At the Manhattan conference in 1997, Xuewen Huang, a scientist with the Institute of Desert Research in Lanzhou, China, described a wind erosion study in Inner Mongolia. He found that soil losses from wind on cropland ranged as high as 44-260 tons/ha (109-642 tons/ac.) between winter and spring. On grassland plowed for crops, as much as 500-3,900 tons/ha (220-1,700 tons/ac.) of soil was lost to the wind. At this same conference, Jianyou Shen, also with the Institute of Desert Research, noted that more than 2 in. of topsoil can blow away in one year from cultivated land. In response to wind erosion, some fields may be replanted five or six times a season.

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British scientist Michael Fullen with the School of Applied Sciences at the University of Wolverhampton notes that China’s 12 deserts and desertified land occupy 1.52 million km2 (587,000 mi.2), or almost 16% of the country. This area is expanding at an annual average rate of about 2,100 km2 (800 mi.2). "Dust storms are major mechanisms of exporting sediment into desert margins and damaging desert-margin ecosystems," he says. "This dust activates a complex sequence of events that affects development of soil and plant communities."

D.J. Mitchell, along with Fullen and others with the University of Wolverhampton, has studied desertification near Yanchi on the southern edge of China’s Mu-Us Sandy Land. "As a result of sand encroachment and desertification at Yanchi, the once-stable steppe is now a mixture of fixed, semifixed, and mobile dunes," Mitchell explains. "During dry periods, dunes become unstable, leading to increased sand mobility and further burial of rangeland soils." The Institute of Desert Research of Academia Sinica has coordinated efforts to combat desertification. Communal planting of Salix psammophila prevents sands from shifting, he reports. Over a four-year period, improved management of rangeland reduced desertification by 10% and increased the amount of rangeland available for grazing by 40%.

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