Sodium silicate has been used to control lead levels in drinking water, but there is little theoretical support for this practice. We find that sodium silicate is not effective in controlling lead release from lead(ii) carbonate.
Monitoring lead in
drinking water is important for public health,
but seasonality in lead concentrations can bias monitoring programs
if it is not understood and accounted for. Here, we describe an apparent
seasonal pattern in lead release into orthophosphate-treated drinking
water, identified through point-of-use sampling at sites in Halifax,
Canada, with various sources of lead. Using a generalized additive
model, we extracted the seasonally varying components of time series
representing a suite of water quality parameters and we identified
aluminum as a correlate of lead. To investigate aluminum’s
role in lead release, we modeled the effect of variscite (AlPO
4
·2H
2
O) precipitation on lead solubility, and
we evaluated the effects of aluminum, temperature, and orthophosphate
concentration on lead release from new lead coupons. At environmentally
relevant aluminum and orthophosphate concentrations, variscite precipitation
increased predicted lead solubility by decreasing available orthophosphate.
Increasing the aluminum concentration from 20 to 500 μg L
–1
increased lead release from coupons by 41% and modified
the effect of orthophosphate, rendering it less effective. We attributed
this to a decrease in the concentration of soluble (<0.45 μm)
phosphorus with increasing aluminum and an accompanying increase in
particulate lead and phosphorus (>0.45 μm).
Lead is a neurotoxin and an environmental contaminant. Many jurisdictions require that it be monitored in drinking water, especially where lead plumbing remains in use. But seasonal variation in lead concentrations can bias monitoring programs if it is not understood and accounted for. Here, we describe an unexpected pattern in lead release to drinking water, identified through point-of-use sampling. The median lead concentration representing paired first-draw water samples—collected in multiple years—was 46% lower in October compared to February. Seasonal variation in orthophosphate, pH, and alkalinity accounted for at least some of this pattern and predicted lead solubility in October was 76% of that in February. But seasonally varying aluminum may also have been a factor; as a supplement to the field study, we evaluated the effects of aluminum residual, temperature, and orthophosphate concentration on lead release from lead coupons. Increasing the orthophosphate concentration from 0–1 mg/L decreased lead release by 34%, and increasing water temperature from 4–21˚C increased lead release by 120%. Increasing the aluminum concentration from 20–500 µg/L increased lead release by 41% and modified the effect of orthophosphate, rendering it less effective in controlling lead release. We attributed this to a decrease in the concentration of soluble (<0.45 µm) phosphorus with increasing aluminum and an accompanying increase in particulate lead and phosphorus (>0.45 µm). These data suggest that residual aluminum from coagulation may interfere with orthophosphate corrosion control, especially when the treatment process does not allow the pH of minimum aluminum hydroxide solubility to be targeted.
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