2.2 SHOWER WATER DERMAL CONTACT


    Use of domestic water for showering will expose individuals to pollutants from dermal contact with water. Pollutants will be taken into the body through the skin and provide a potential for health impacts. This exposure pathway is applicable to the groundwater and surface water transport pathways. As for the drinking water pathway, consideration is given to reductions of pollutant concentrations during processing in the water supply treatment plant (if present) and in transport through the water distribution system to the exposed individuals. The surface water pathway also includes estimation of losses of volatile chemicals in transport between the point of entry to the surface water and the water intake plant.
Transport Medium:
water concentration at the domestic water treatment plant, Cdwi, pCi/L or mg/L, expressed as a 70-year average value

Special Process:
removal of pollutants during water treatment loss of pollutants (environmental degradation or radioactive decay) during transport from the treatment plant to the exposure location (households) loss of pollutants during transport in the surface water body by volatilization absorption through the skin during showering event

Exposure Factors:
area of skin exposed, frequency of exposure, and exposure duration.

    Dermal exposures to chemicals are treated as ingestion intakes with correction for the fraction of the chemical absorbed in passing through the GI tract. The correction is not needed for dermal exposures to radionuclides because dose factors are available in MEPAS for radionuclide intake through the skin. The intake from dermal contact with water is evaluated using a model that first estimates the dermal intake per event (shower). This value is then used with shower frequency data and exposure parameters to determine the average daily dose.

    The intake per shower is evaluated using methods suggested by USEPA (USEPA 1992), as described in the following discussion.

    For inorganic chemicals and radionuclides, the intake per shower per unit area of skin contacted is evaluated as follows:


Ishi = 10-3 Cdwi TFi e(-lgiTHdw) Kpi TEs

(4)



where
     For organic chemicals, the USEPA model uses the permeability constant for the pollutant of interest, the skin thickness, and the duration of one shower event to estimate the total amount of pollutant transferred through the skin. These parameters are used in a six-step procedure (as defined in USEPA 1992a) to esti-mate the absorbed dose per unit area per event, as follows:

The average daily dose as computed by Equation (13) is equivalent to oral exposure because the GI absorption correction has been applied. The averaging time for noncarcinogenic chemicals is set to the exposure duration, and the averaging time for carcinogenic chemicals is fixed at 70 years. The equation is used for all pollutants except radionuclides.

    For radionuclides, the GI absorption fraction and body weight are not applied because radionuclide specific dose conversion factors for dermal intake are provided in the chemical database for the 70-kg reference man. The dermal dose factors were calculated using the CINDY software package (Strenge et al. 1992; Kennedy and Strenge 1992). The equation for radionuclides is as follows:

Dsdi = Ishi Asd FEsh Fsd DFdi EDsd 365.25

(14)



where

and other terms are as previously defined.