Table 2.
Summary of input parameters in the ILCR model
| Parameters | Input estimates | Distribution type | Data source | |
|---|---|---|---|---|
| Abbreviations: ILCR, Incremental Lifetime Cancer Risk | ||||
| Breathing rate | m3/h | 1.37 ± 0.042 | Normal | US EPA, 200935) |
| Average work hours | h/day | 8.87 | Point estimate | DBAS, 201632) |
| Exposure frequency | d/yr | 246 ± 1.5 | Normal | MOL, 201633) |
| Exposure duration | year | 45 | Point estimate | MOL, 201634) |
| Body weight | kg | 69.81 ± 1.39 | Normal | MHW, 201652) |
| Time to cancer | year | 77.01 ± 2.01 | Normal | MOI, 201653) |
| Cancer slope factor | (mg/kg/day) –1 | |||
| - Cr | 47.6 | Point estimate | Health Canada, 200726) | |
| - Cr (VI) | 41 | Point estimate | US EPA, 200727) | |
| - Oxidic nickel | 4.4 | Point estimate | NTP, 19969) | |
| - Soluble nickel | 3.0 | Point estimate | Health Canada, 200726) | |
| Concentration | ||||
| - Cr | 10–3 mg/m3 | |||
| Pipeline construction | 1361.6 ± 639.8 | Log-normal | Field sampling | |
| Pressure container manufacturing | 33.8 ± 59.8 | Log-normal | Field sampling | |
| Shipyard building | 1.1 ± 0.9 | Log-normal | Field sampling | |
| - Cr (VI) | 10–3 mg/m3 | |||
| Pipeline construction | 503.8 ± 294.7 | Log-normal | Field sampling | |
| Pressure container manufacturing | 4.4 ± 8.0 | Log-normal | Field sampling | |
| Shipyard building | 0.4 ± 0.3 | Log-normal | Field sampling | |
| - Oxidic Ni | 10–3 mg/m3 | |||
| Pipeline construction | 145.2 ± 119.4 | Log-normal | Field sampling | |
| Pressure container manufacturing | 13.0 ± 11.5 | Log-normal | Field sampling | |
| Shipyard building | 0.1 ± 0.1 | Log-normal | Field sampling | |
| - Soluble Ni | 10–3 mg/m3 | |||
| Pipeline construction | 101.8 ± 85.8 | Log-normal | Field sampling | |
| Pressure container manufacturing | 1.0 ± 0.9 | Log-normal | Field sampling | |
| Shipyard building | 0.1 ± 0.1 | Log-normal | Field sampling | |