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Greywater Management in Low and Middle-Income Countries - SSWM

Greywater Management in Low and Middle-Income Countries - SSWM

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Moderately tolerant<br />

Bean Cowpea Vigna unguiculata<br />

Okra Abelmoschus esculentus Wheat <br />

Onion Allium cepa Fig Ficus carica<br />

Avocado Persea americana Olive Olea europaea<br />

Lemon Citrus limon Papaya Carica papaya<br />

Mango P<strong>in</strong>eapple Ananas comosus<br />

Moderately sensitive<br />

<br />

Maize Zea mays Barley <br />

Rice, paddy Sugarbeet <br />

Cabbage Brassica oleracea capitata Asparagus <br />

Eggplant Date palm <br />

Sp<strong>in</strong>ach<br />

Tomato<br />

Sp<strong>in</strong>acia oleracea<br />

Lycopersicon lycopersicum<br />

can lead to the degradation of well-structured soils (dispersion of clay particles),<br />

reduc<strong>in</strong>g soil porosity <strong>and</strong> aeration, <strong>and</strong> <strong>in</strong>creas<strong>in</strong>g the risk of poor water movement<br />

through the soil. Depend<strong>in</strong>g on soil characteristics, greywater with a SAR as low as<br />

3-4 can already lead to degradation of soil structure (Patterson, 1997, Gross et al.,<br />

2005).<br />

Sodium salts are soluble <strong>and</strong> cannot be removed under typical wastewater<br />

treatment conditions. The best <strong>and</strong> by far cheapest strategy to avoid excessive<br />

sodium loads on soils is the selection of low sodium laundry detergents (see Chapter<br />

Source control).<br />

Figure 4-10 can be used to evaluate irrigation water quality <strong>in</strong> relation to its<br />

potential impact on soil structure as a function of EC <strong>and</strong> SAR values. In the event<br />

of uncerta<strong>in</strong>ty regard<strong>in</strong>g the potential effects of greywater irrigation on soil structure<br />

stability, soil samples can be submitted for analysis to an accredited laboratory.<br />

Other problems related to greywater irrigation may be caused by chloride <strong>and</strong><br />

boron toxicity. Although essential to plants <strong>in</strong> very low concentrations, boron <strong>and</strong><br />

chloride can cause toxicity to sensitive crops at high concentrations. Leaf burn at<br />

the leaf tip is a typical toxicity symptom for high chloride concentrations. Similar<br />

to sodium, high chloride concentrations cause more problems when applied with<br />

spr<strong>in</strong>klers. Plant <strong>in</strong>juries must be expected with chloride concentrations as low as<br />

140 mg/l (Bauder et al., 2004). Boron toxicity is likely to occur on sensitive crops at<br />

concentrations lower than 1 mg/l. Gross et al. (2005) observed boron accumulation <strong>in</strong><br />

greywater-irrigated soils <strong>in</strong> Israel. After three years of irrigation, boron concentrations<br />

<strong>in</strong> the soil reached 2.5 mg/kg. The risk of chloride <strong>and</strong> boron toxicity can best be<br />

m<strong>in</strong>imised by utilis<strong>in</strong>g clean<strong>in</strong>g agents poor <strong>in</strong> boron <strong>and</strong> chloride.<br />

<strong>Low</strong>-cost <strong>Management</strong> <strong>and</strong> Treatment Options<br />

48

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