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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 />

Geophysical logs in a borehole about 1 mile northwest of <strong>Powerline</strong> FRS show very low<br />

resistivities indicating significant clay content. Based on the amount of subsidence that has<br />

occurred in this area, highly compressible clays are anticipated to be present in this area.<br />

The character of the geophysical logs for wells located near, or to the north <strong>and</strong> west of, the<br />

<strong>Powerline</strong> FRS indicated the presence of zones of significant thickness with resistivities less than<br />

about 10 ohm-m. Therefore, subsidence that results from consolidation of clay-rich materials<br />

occurs relatively slowly. These areas are shown by InSAR to have been actively subsiding<br />

during the 1990s in spite of relatively constant regional groundwater levels.<br />

Historical deep wells were completed near the CAP alignment at or to the south of the Vineyard<br />

Road FRS. The character of the geophysical logs for these wells is consistent with the published<br />

descriptions of the upper alluvial unit (UAU), <strong>and</strong> very different from wells completed within the<br />

middle fine-grained unit (MFGU) northwest of the <strong>Powerline</strong> FRS. Between depths of 600 <strong>and</strong><br />

1,200 feet bgs, at least 16 zones of higher resistivity (greater than 10 ohm-m), typically at least a<br />

few feet thick, could be identified. These higher-resistivity zones were interpreted to contain<br />

more granular, higher-permeability materials, rather than clayey material. This alluvial basin<br />

section was thus interpreted to include significant interbedded or interfingered units, fluctuating<br />

between s<strong>and</strong>y/gravelly horizons <strong>and</strong> clay-enriched horizons. With sufficient interconnection of<br />

the higher-resistivity, higher-permeability horizons, the basin alluvium could have been drained<br />

more rapidly as the groundwater level dropped, <strong>and</strong> subsidence would have occurred much faster<br />

than in the clay-rich alluvium to the north. Geophysical logs indicate that the basin alluvium<br />

south of the Vineyard Road FRS appears to be relatively clay poor compared to basin alluvium<br />

to the northwest of the Vineyard Road FRS. Below depths of about 1,200 feet bgs the<br />

resistivities increased <strong>and</strong> rarely fell below 10 ohm-m.<br />

Hydrogeologic Conditions<br />

A reasonable estimate of predevelopment groundwater levels can be made from well data<br />

indicating a groundwater elevation of about 1,325 feet above mean sea level (amsl),<br />

corresponding to a depth to water of approximately 275 feet, in the late 1930s to early 1940s.<br />

In 1978, groundwater levels at the northern <strong>and</strong> southern ends of the study area had dropped<br />

over 200 feet from the estimated predevelopment level, corresponding to a depth to water of<br />

about 500 feet bgs or an elevation about 1,100 feet amsl. In the middle of the study area,<br />

groundwater levels had dropped less, <strong>and</strong> were up to about 70 feet higher than in the surrounding<br />

area. Suburban growth in the area north of the <strong>Powerline</strong> FRS, <strong>and</strong> the establishment of major<br />

agriculture to the southwest <strong>and</strong> west of the Rittenhouse FRS, were probable reasons for the<br />

development of major pumping centers in 1978.<br />

By 2009, the water level trend across the PVR study area had changed significantly. Continued<br />

suburban development in the northern part of the study area had resulted in continued pumping<br />

of groundwater with a further groundwater level decline such that the depth to water was nearly<br />

600 feet bgs. Replacement of pumped groundwater by CAP water delivery for agricultural use<br />

resulted in significantly reduced pumping <strong>and</strong> recovery of groundwater levels by as much as 80<br />

feet from the 1980s to the present. Groundwater levels remained stable or declined moderately<br />

(perhaps up to about 40 feet of decline from the 1970s to the present) through the Vineyard Road<br />

FRS section of the study area.<br />

USDA- NRCS <strong>Jan</strong>uary <strong>2013</strong><br />

Kimley-Horn <strong>and</strong> Associates, Inc. Page 43

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