THOMAS C. DEANE, PG/CHG (CA), RG (AZ) - (775) 895-1994, PO Box 131, Silver Springs NV 89429
Orange Crest/Mission Grove Area (OCMGA), Riverside CA (2008-2012)
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OCMGA Part 1: Visual Quantification of Surface Water Outflow Resulting From
Over-Irrigation of OCMGA Residential/Business Landscaping (as Deane Consulting, Inc., "DCI")
Previous Personal Study on Observed Field Conditions

During and following groundwater investigations conducted in support of construction of the KIA Distribution Center ("LNR-Meridian", 2007) and the Metropolian Water District's North Reach Perris Valley Pipeline ("NRPVP", 2008-2009) adjacent to the Orange Crest - Mission Grove area (OCMGA) of Riverside CA (see Figure 1 link below), the surface water discharge rates of forty (40) radially-oriented drainages originating from the OCMGA (Figure 2) were visually estimated on an annual schedule from 2008 to 2012.  The drainages apparently receive runoff residential/business landscape irrigation water originating from the OCMGA via yard drains, curbs/gutters, and receptor storm drains that discharge to the drainages (Figure 3).  Estimates were conducted during July of each year to reduce the influence of each preceding rainy season and during the afternoon hours to reduce the influence of assumed morning mass landscape irrigation, resulting in the collection of daily drainage surface water "base flow" data.  The noted projects and the OCMGA are underlain by in situ-derived alluvial sediments that overlie a jointed shallow crystalline bedrock complex (Figure 4; Morton & Cox, 2001), into which paleochannels had been eroded prior to current accumulation of alluvium.  In addition, to save costs developers will typically install storm drain alignments/outlets within existing drainages that, in this case, appear to overlie the noted paleochannels.  The OCMGA is a unique study area for landscape irrigation water overuse in that the shallow bedrock complex prevents the downward percolation of water (visual loss) into deep aquifers that typically underlie large developed areas, and instead, directs the water laterally outward via the noted paleochannels where it can be observed and quantified.  Furthermore, pre-construction geotechnical investigations of several areas within the OCMGA conducted during 1988 to 1990 did not indicate any appreciable volumes of groundwater in the vicinity of the drainages nor future storm drains, even during relatively wet precipitation conditions that occurred between 1987 and 1990.

2008/2009 flow rates ranged between approximately 0.25 and 15 GPM (2008 total 74 GPM/2009 total 80 GPM), under drought conditions.  Increased precipitation during 2010/2011 increased flow rates to a range between approximately 0.25 and 30 GPM (2010 total 109 GPM/2011 total 124 GPM), whereas decreased precipitation during 2012 decreased flow rates to a range between approximately 0.25 and 20 GPM (2012 total 81 GPM).  These data indicate that 2008/2009 data corresponded to the latter portion of a multi-year region-wide drought, 2010/2011 data corresponded to a region-wide increase in precipitation, and 2012 data corresponded to a region-wide decrease in precipitation (Figure 5).  Thus, 2008/2009/2012 flow data may represent annual "base flow" landscape irrigation runoff conditions for the OCMGA.  Although Figure 5 indicates a much lower 2007 total flow rate, this total represents only the initial four drainages (D01 through D04, Figure 2) that were estimated during the LNR-Meridian project, prior to the incorporation of the remaining 36 drainages (D05 through D40, Figure 2) during the NRPVP project.

A conceptual model describing at least three (3) possible routes of landscape irrigation water to the drainages has been developed (Figure 6).  The routes are: (1) surface overflow into curb/gutter systems to drainages via storm drains; (2) vertical downward percolation of water to buried interface between alluvium/bedrock complex, gravity flow along interface toward/along paleochannel axes, perhaps entering slip-joints of buried storm drains; and (3) lateral fracture flow of unknown portion of percolated water within uppermost portion of bedrock complex toward drainages, perhaps entering slip-joints of buried storm drains.

Assuming that mass landscape irrigation occurs 365 days per year, the visually-estimated total annual flow volumes originating from the OCMGA for 2008/2009/2010/2011/2012 were approximately 119/128/176/200/130 AFY, respectively, originating from a potable water supply.  In addition, historical aerial photographs dating back to 1938 indicate that the "base flow" water originating from the OCMGA is anthropogenic, as shown by the establishment of "swamp" willows within many of the noted drainages only after OCMGA development (landscape irrigation) within associated up-drainage areas.

California Department of Finance census data indicate that the 2010 total southern California population within Imperial, Los Angeles, Orange, Riverside, San Bernardino, and San Diego Counties was approximately 20,323,529 people.  Using average per-county household sizes ranging from 2.75 (San Diego) to 3.34 (Imperial) people per household, southern California had approximately 6,801,059 occupied households in 2010 within the noted counties.  Assuming only 50% of these household irrigated landscaping with potable water, this results in approximately 3,400,530 occupied households with such landscape irrigation.  Using an OCMGA single-family/multi-family/commercial connection-weighted "base flow" average of approximately 1.992E-02 AFY per connection, approximately 67,739 AFY (approximately 22,072,956,370 GPY) of potable water may be lost to landscape over-irrigation within the noted southern California counties.  This represents approximately 4.5% of the 2011/2012 MWD imported potable water total volume (1.5 million AF or 488,776,500,000 gallons), at a loss of approximately $50,397,816.                          







RESULT: Although no direct clients were involved in this personal study per se, if the potential state-wide volume of potable water lost to over-irrigation of landscaping was reduced or eliminated such that this volume could remain within infrastructure storage facilities for a longer period of time until actually needed, then perhaps these structures would not require replacement/enlargement until a later date, thus extending their use over time "as-is" and delaying the potential implementation of increased customer fees/bonds/taxes/etc. that are typically used for upgrading infrastructure

Associated documents produced by DCI on this project:

No documents were produced on this project as this was a personal "labor of love" interest regarding the effects of overwatering practices on the local hydrogeology.


I appreciate the opportunity to have worked with Mr. Jay Martin, EG/PG of CHJ, Inc., Colton CA, on the associated LNR-Meridian project.