The non-carcinogenic health risks represented as hazard quotients (HQs) are equal to the chronic daily intake (
CDI) divided by the chronic reference dose (
RfD). Therefore, the risk assessment models vary depending on exposure routes such as oral ingestion, dermal contact and inhalation.
For ingestion of soil particles, sediment particles, surface water and ground water, the health risk models can be written as
Eq. (1)7 22 :
where
i represents a target media or land use.
IRi represents the ingestion rate, including soil ingestion rate
IRs (mg/d), sediment ingestion rate
IRsd (mg/d), daily water ingestion rate
IRw (mL/d); and
EFi represents the exposure frequency (d/yr) for indoor activities
EFia, outdoor activities
EFoa and swimming
EFsd, respectively.
ED indicates the exposure duration (yr),
BW indicates the average body weight (kg), and
AT indicates the average total time (d).
RfDingestion denotes the chronic oral reference dose (mg/kg/d).
UF represents a unit transfer factor, which is ×10
−6 for soil and sediment and ×10
−3 for water.
Ci indicates the metal concentrations in the target media or land use (mg/kg for soil and sediment and μg/L for water).
The metal concentrations in groundwater
Cgw (μg/L) were calculated using a leaching equation and a dilution factor (
DF) (
Eq. 2)7 :
where
Cts (mg/kg) indicates the metal concentrations in the total soil profile (0–100 cm),
Kd represents the soil-water partition coefficient (L/kg),
θw represents the water-filled soil porosity (L
water/L
soil) and
ρb is the dry soil bulk density (g/cm
3).
The risks arising from intake of heavy metals from vegetables planted in soil can be written as
Eq. (3)14 (
link):
where
Cas (mg/kg) indicates the metal concentrations in the agricultural soils (0–20 cm),
PUF (unit-less) represents the plant uptake factor,
IRv indicates the vegetable ingestion rate (kg/d), and
θv (unit-less) is the vegetable water content.
For dermal contact with soil, sediment and water, the health risk model is written as
Eqs (4) and (
5)7 22 :
For soil and sediment
For water
where
ABS (unit-less) represents the dermal absorption factor for soil and sediment.
Kp (cm/h) represents the dermal permeability constant for heavy metals in water.
SAi (m
2) represents the skin surface area available for exposure in outdoor activities or in swimming.
AFi (mg/cm
2) represents the soil-to-skin adherence factor for farmers and adults.
RfDdermal (mg/kg/d) is the chronic reference dose through dermal contact and
UF represents a unit transfer factor (×10
−6).
For inhalation routes, the health risk model for risks posed by inhalation of soil particles and vapors is
Eq. (6)7 22 .
where,
IRa (m
3/d) is the air inhalation rate,
RfDinhalation (mg/kg/d) is the chronic inhalation reference dose,
PEF (m
3/kg) indicates the particulate emission factor and
VF is the volatilization factor, which in this study was relevant only for elemental Hg (32,376.4 m
3/kg)10 (
link).
The total hazard quotient (
THQ) is the sum of individual
HQs for each media or land use,
i, and is given by
Eq. (7):
in which is calculated only for heavy metals in surface soils. Values of HQ and THQ greater than 1 indicate potential health risks while those less than 1 suggest acceptable risks.
Peng C., Cai Y., Wang T., Xiao R, & Chen W. (2016). Regional probabilistic risk assessment of heavy metals in different environmental media and land uses: An urbanization-affected drinking water supply area. Scientific Reports, 6, 37084.