Professor of Civil and Environmental Engineering
San Diego State University
San Diego, California
• INTRODUCTION Over a measurable period, say one year, the amount of precipitation over a basin is divided into evaporation, evapotranspiration, and runoff. Evaporation (E) is the fraction of precipitation returned to the atmosphere in the absence of vegetation. Evapotranspiration (ET) is the fraction of precipitation returned to the atmosphere through vegetation. In order to avoid confusion, the combined amount of evaporation and evapotranspiration is referred herein as vaporization (V). Runoff (Q) is the fraction of precipitation returned to the ocean as streamflow. On a global average basis, vaporization is about two-thirds of precipitation, with runoff constituting the remaining one-third. Therefore, the global average ratio of vaporization to runoff is: V/Q = 2. However, in humid regions, this ratio may be as low as 1, while in arid regions, it may be as high as 50.
• NATURAL SALT PRODUCTION In a pristine natural environment, the total volume of annual runoff is: Ro = Qo A in which
Ro = pristine annual runoff, in m3; Qo = pristine annual runoff, in m; and A = basin drainage area, in m2. In nature, runoff always carries a certain amount of dissolved solids, mostly salts. The salt concentration in runoff is expressed in gr/m3. Thus, the total weight of salt in annual runoff is: S = Co Ro in which S = annual weight of salt delivered to the ocean by runoff, in gr; and Co = mean salt concentration in pristine runoff, in gr/m3.
• THE EFFECT OF IRRIGATION ON RUNOFF Irrigation increases evapotranspiration. This increase can come from a reduction in evaporation or a reduction in runoff. In practice, however, for the most part, irrigation converts runoff into evapotranspiration, resulting in a net reduction in runoff. By increasing V and reducing Q, irrigation increases the ratio V/Q. Under normal contemporary settings, irrigation reduces annual runoff to Qa, in which
Qa = anthropogenic annual runoff, in m. Therefore: Ra = Qa A in which Ra = anthropogenic annual runoff, in m3.
• EXORHEIC VS ENDORHEIC DRAINAGES Hydrologic basins can be either exorheic or endorheic, depending on their drainage properties. Exorheic basins have an outlet to the sea; endorheic basins do not. Exorheic basins have finite V/Q ratios, with a global average of 2. Conversely, in an endorheic basin, runoff is zero; therefore, V/Q = ∞; i.e., all precipitation is converted to vaporization. Typically, exorheic basins feature rivers and estuaries, and drain outwards, while endorheic basins feature lakes and wetlands and drain inwards. However, some apparently closed basins (lakes) may not be fully endorheic, featuring small percentages of runoff; therefore, they are termed semi-exorheic. Similarly, some apparently open basins (rivers) may not be fully exorheic, featuring small percentages of forced loss to vaporization (through small lakes); therefore, they are termed semi-endorheic. Fully exorheic drainages do not accumulate salts and other solids. Fully endorheic and semi-endorheic drainages accumulate salts and other solids.
• THE CONCEPT OF BASIN SALT BALANCE A basin is said to be in salt balance when there is no significant salt accumulation over an extended period of time, say, one year. A basin in salt balance is an exorheic basin. An endorheic or semi-endorheic basin is not in salt balance. Semi-exorheic basins may or may not be in salt balance, depending on the local drainage conditions. For a developed exorheic basin to remain in salt balance, the mean salt concentration in anthropogenic runoff should be: Ca = S / Ra in which Ca = mean salt concentration in anthropogenic runoff, in gr/m3. It follows that Ca Ra = Co Ro Also: Ca Qa = Co Qo and Qa = Qo / (Ca /Co) This last equation is particularly significant because it states that anthropogenic runoff is inversely related to the ratio of anthropogenic to pristine mean salt concentrations. In the limit, as Qa → 0, it follows that (Ca /Co) → ∞, i.e., salt accumulates without limit in the drainage basin, defying salt balance. To achieve basin salt balance, Qa must remain finite; i.e., anthropogenic runoff must remain a finite fraction of pristine runoff. Furthermore, the minimum fraction to reserve for basin salt balance may be calculated by setting the ratio Ca /Co to a workable value determined by consensus. For instance, if Co = 300 gr/m3, and a value of Ca = 1,500 gr/m3 is assumed to be acceptable, then the anthropogenic-to-pristine mean salt concentration ratio is: Ca /Co = 5 and the anthropogenic-to-pristine runoff ratio is: Qa /Qo = 0.2
• CASE STUDY An interesting and somewhat extreme case of combined natural/anthropogenic salt sequestration is represented by the Tulare Lake basin, in the southern portion of California's Central valley. Tulare Lake functions as an endorheic basin most of the time, collecting its own local and regional runoff, plus the eventual seasonal overflow from the Kings river, located to the north. However, during extreme periods of local and regional runoff, runoff from Tulare Lake was known to reverse direction and flow northward towards the Kings and San Joaquin river valleys (Fig. 1). Thus, historically, Tulare Lake has functioned as a semi-exorheic basin.
Over the past century, irrigation development in Tulare Lake and environs has resulted in the conversion of all runoff into vaporization. While the intention (of irrigation) is to convert runoff into evapotranspiration, a significant portion of runoff is actually converted into evaporation (from water-supply ponds and evaporation basins). Every drop of water that precipitates in the basin is now captured in Tulare Lake basin; therefore, not a single iota of salt is being allowed to leave the basin. For the time being, the irrigation system works because the drainage system carries the salt brine away from the root zone, handles it and accumulates it in evaporation basins (Fig. 2). As the system continues to operate, the need for additional evaporation basins becomes apparent. However, the system is unsustainable, carrying with it the certainty of its eventual demise. • CONCLUSION The conceptual analysis formulated herein demonstrates that a minimum anthropogenic-to-pristine runoff ratio must be preserved in irrigation development if a basin is to achieve some measure of salt balance. There can be no salt balance if the anthropogenic-to-pristine runoff ratio is zero, i.e., if all the pristine runoff is converted to evapotranspiration. There is a maximum limit to the amount of runoff that can be appropiated for consumptive uses. Disregarding this limit leads to a loss of basin salt balance, a practice which is unsustainable. Thus, regulation of basin water quantity is absolutely necessary to preserve land quality. Stated in other terms, the preservation of water quality must not be achieved at the expense of the degradation of land quality. • NOTATION A = basin drainage area (m2); Ca = mean salt concentration in anthropogenic runoff (gr/m3); Co = mean salt concentration in pristine runoff (gr/m3); E = evaporation (m); ET = evapotranspiration (m); Q = runoff (m); Qa = anthropogenic annual runoff (m); Qo = pristine annual runoff (m); Ra = anthropogenic annual runoff (m3); Ro = pristine annual runoff, (m3); S = annual weight of salt delivered to the ocean by runoff (gr); and V = vaporization, defined as the sum of evaporation and evapotranspiration (m).
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