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accurately estimating the quantity of recharge waters is 2.6 <br /> clearly evident,particularly in cases of higher nitrogen load W=150 911/dAyid—till,it..It <br /> - <br /> ing and lower denitrification rates. _ <br /> 2'0 <br /> In Figure 2,the critical minimum gross acreage per lot, <br /> A,is plotted against the annual rate of rainfall recharge,R, g <br /> a <br /> for a selected range of values for nw and d,with nb= 1.0 a <br /> mg/l as before.In this instance the long-term waste-water a o + a <br /> flow,W,is assumed equal to 150 gal/day per DU, on the <br /> a <br /> basis of an average expected occupancy of three persons per o ,.0 <br /> residence and 50 gal/person/day.The U.S.EPA(1980)cites <br /> 45 gal/day as the typical per capita flow for residential <br /> dwellings.The influence of climate and the water balance is 0.a 'OOH <br /> seen to be significant,particularly for lower ranges of R,i.e., `o <br /> drier climates.Thus,in desert areas,very large lots may be <br /> 0 <br /> necessary. o a ,o ,a vo za ao <br /> In typical new developments of single family resi- NATURAL RAINFALL RECHARGE.R.In/yr <br /> dences,practical lot size limits exist because of minimum Fig.2.Influence of effluent quality,denitrification,and rainfall <br /> space requirements for site development, disposal fields, recharge on critical lot size. <br /> roadways,open space,etc.These limits may be on the order <br /> of 0.25 to 1.0 gross acres per dwelling unit,depending on <br /> local codes and specific development plans. As seen in <br /> Figure 2, such practical or statutory limits may often be <br /> more stringent than the critical minimum gross acreage per <br /> lot,A,determined from equation(2).This is particularly <br /> true as R values increase. <br /> Y CNICO AREA <br /> Case Study Examples <br /> To demonstrate and test their validity,the preceding <br /> methods for assessing nitrate impacts were compared <br /> against the actual ground-water quality data for three =__===__======_ <br /> - === <br /> California communities.All three of these communities rely ==BOLINA3 <br /> _MPSA==__-=___= o \ <br /> on individual on-site systems for sewage disposal. In each <br /> case ground-water contamination by nitrates has been docu- <br /> --- <br /> mented by extensive monitoring programs.The three com- <br /> munities reviewed here as case study examples are:(1)the _-=-= _=- =-====- -=== <br /> -- <br /> Bolinas Mesa area in Marin County;(2)the Chico area in <br /> Butte County;and 3 the Ba ood-Los Osos area in San _=_nos <br /> Y O Yv ---------------- <br /> Luis <br /> -____----_-- <br /> Luis Obispo County(Figure 3). <br /> Description of Study Areas <br /> The general physical characteristics of the three study o ,00 zoo aoo 400 aoo Mile. <br /> areas are summarized in Table 1.Background on the study I I I I I i <br /> sites is discussed below. Fig.3.Location of three case study communities in California. <br /> Table 1.Physical Characteristics of the Case Study Areas <br /> Characteristic Bolinas Mesa area Chico area Baywood/Los Osos <br /> Landform Marine terrace Valley floor Coastal dune <br /> Topography 0 to 5% 0 to 2% 3 to 5% <br /> Soils Sandy loam and Sandy loam Loamy sands <br /> sandy clay loam and sand <br /> Depth to ground water(ft) 2 to 6 15 to 20 15 to 30 <br /> Average rainfall(in./yr) 30.9 22.5 20.0 <br /> Estimated rainfall recharge(in./yr) 14.4 16.8 12.0 <br /> Sources:see text. <br /> 493 <br />