Powerline Plan and Environ. Assessment Jan. 2013 - Flood Control ...
Powerline Plan and Environ. Assessment Jan. 2013 - Flood Control ...
Powerline Plan and Environ. Assessment Jan. 2013 - Flood Control ...
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<strong>Powerline</strong> <strong>Flood</strong> Retarding Structure<br />
Pinal County, AZ<br />
Draft Supplemental Watershed <strong>Plan</strong><br />
<strong>and</strong> <strong>Environ</strong>mental <strong>Assessment</strong><br />
Subsidence<br />
Lowering the groundwater elevation in a column of alluvial basin material increases the effective<br />
stress <strong>and</strong> loading on the material column. If the column consists of granular materials, typically<br />
s<strong>and</strong>s <strong>and</strong> gravels, compression of the material below the initial water level takes place rapidly.<br />
Until granular particle contact points are changed by compression, at least some of the<br />
compression can be recovered elastically if water levels rise <strong>and</strong> the effective stress is decreased.<br />
Compression that results from particles slipping or crushing tends to have much less elastic<br />
rebound. If the material column contains a significant fraction of fine-grained materials, such as<br />
clay, consolidation of the material below the initial water level takes place more slowly. The<br />
time frame of consolidation is a function of the permeability of the material, where lower<br />
permeability increases consolidation time. Consolidation is also a function of the distance to <strong>and</strong><br />
the interconnectivity of higher permeability zones which can relieve the excess pore pressure by<br />
draining water from clay-rich materials. Greater distances to permeable drainage zones increase<br />
the consolidation time. Although consolidation increases can be modeled as an elastic<br />
phenomenon, consolidation does not typically recover with a decrease in loading.<br />
Earth Fissure Development<br />
Where differential rates <strong>and</strong> magnitudes of subsidence occur over relatively short distances,<br />
horizontal strains can become sufficient to cause earth fissuring. Jachens <strong>and</strong> Holzer (1979,<br />
1982) evaluated the threshold tensile strains for fissuring based on studies in the Eloy-Casa<br />
Gr<strong>and</strong>e area of central Arizona. Jachens <strong>and</strong> Holzer (1982) concluded that most fissuring occurs<br />
at horizontal tensile strains in the range of 0.02 to 0.06 percent. This compares with threshold<br />
strains for cracking of compacted clays zones in dam embankments (or compacted clay liners) of<br />
about 0.1 to 0.3 percent (Leonards <strong>and</strong> Narain 1963; Covarrubais 1969).<br />
Earth fissures in alluvial aquifers that have experienced large groundwater declines are likely<br />
associated with a process termed generalized differential compaction (Carpenter 1994). Three<br />
mechanisms are likely at play in the formation of fissures. These mechanisms include: 1)<br />
bending of a plate above a horizontal discontinuity in compressibility (Lee <strong>and</strong> Shen 1969), 2)<br />
dislocation theory representing a tensile crack (Carpenter 1994), <strong>and</strong> 3) vertical propagation of<br />
tensile strain caused by draping of the alluvium over a horizontal discontinuity in compressibility<br />
(Haneberg 1992). Due to these probable mechanisms, fissures commonly develop along the<br />
perimeter of subsiding basins, often in apparent association with exposed bedrock or shallow<br />
buried bedrock, suspected mountain-front faults, or distinct facies changes in alluvial materials.<br />
Role of Groundwater Level Changes<br />
One of the most important parameters for delineating earth fissure risk is groundwater declines,<br />
specifically, future groundwater declines. If groundwater declines do not occur, then significant<br />
subsidence will not occur. However, predicting future groundwater declines is particularly<br />
challenging due to the social-political factors that drive groundwater use. As a result, accurate<br />
prediction of future groundwater withdrawal is not possible. Related to this challenge is the<br />
influence of groundwater recharge facilities. To date it is unclear how recharge facilities impact<br />
subsidence. It’s well understood that in the immediate vicinity of a recharge facility groundwater<br />
levels increase; however, how that increase influences more regional-scale groundwater<br />
elevations is less certain. Also uncertain are the overall operation of recharge facilities <strong>and</strong> the<br />
long-term availability of excess water for recharge. Other uncertainties are the socio-political<br />
impacts of recharge facilities.<br />
USDA- NRCS <strong>Jan</strong>uary <strong>2013</strong><br />
Kimley-Horn <strong>and</strong> Associates, Inc. Page 39