Appendix H Risk Calculations Off-Site

Size: px
Start display at page:

Download "Appendix H Risk Calculations Off-Site"

Transcription

1 Appendix H Calculations Off-Site

2 Exposure to Chemicals via Incidental Ingestion of Water (Extracted Groundwater) IR (L/kg/day) W FIBEFED Daily ChemicalIntakeIW CW BWAT Parameters Relevant to Quantification of Exposure by Adult Workers - Industrial/Irrigation Water Ingestion Rate (Irw, L/day) 0.05 Incidental ingestion of 50 ml water Fraction Ingested from Source 100% Assumed to be 100% Bioavailability (B) 100% Assume 100% bioavailability via ingestion of chemicals in water. Exposure Frequency (EF, days/year) 96 Assume contact with industrial water 2 days per work week Exposure Duration (ED, years) 30 Duration of exposure as per NEPM 1999 and USEPA 1989 Body Weight (BW, kg) 78 as per enhealth (2012) Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background Intake (% TDI) TDI Allowable for Assessment (TDI- in Water (Cw) Daily Intake Non Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E % Mercury (as total, inroganic) 6.0E-04 40% 3.6E E E % TOTAL 0.12

3 Exposure to Chemicals via Incidental Ingestion of Water (Extracted Groundwater) IR (L/kg/day) W FIBEFED Daily ChemicalIntakeIW CW BWAT Parameters Relevant to Quantification of Exposure by Adults - General Public - Irrigation Ingestion Rate (Irw, L/day) Incidental ingestion of 5 ml water during irrigation of gardens Fraction Ingested from Source 100% Assumed to be 100% Bioavailability (B) 100% Assume 100% bioavailability via ingestion of chemicals in water. Exposure Frequency (EF, days/year) 90 Frequency relevant to garden irrigation Exposure Duration (ED, years) 35 Duration of exposure assumed (enhealth 2012) Body Weight (BW, kg) 78 enhealth 2012 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background Intake (% TDI) TDI Allowable for Assessment (TDI- in Water (Cw) Daily Intake Non Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E % Mercury (as total, inroganic) 6.0E-04 40% 3.6E E E % TOTAL 0.011

4 Exposure to Chemicals via Incidental Ingestion of Water (Extracted Groundwater) IR (L/kg/day) W FIBEFED Daily ChemicalIntakeIW CW BWAT Parameters Relevant to Quantification of Exposure by Older Children - General Public - Irrigation Ingestion Rate (Irw, L/day) Incidental ingestion of 5 ml water during irrigation of gardens Fraction Ingested from Source 100% Assumed to be 100% Bioavailability (B) 100% Assume 100% bioavailability via ingestion of chemicals in water. Exposure Frequency (EF, days/year) 90 Frequency relevant to garden irrigation (more conservative than municipal Exposure Duration (ED, years) 10 Duration of exposure as per NEPM 1999 and USEPA 1989 Body Weight (BW, kg) 34.5 As per USEPA 1997 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) 3650 USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background Intake (% TDI) TDI Allowable for Assessment (TDI- in Water (Cw) Daily Intake Non Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E % Mercury (as total, inroganic) 6.0E-04 40% 3.6E E E % TOTAL 0.025

5 Exposure to Chemicals via Incidental Ingestion of Water (Extracted Groundwater) IR (L/kg/day) W FIBEFED Daily ChemicalIntakeIW CW BWAT Parameters Relevant to Quantification of Exposure by Young Children - General Public - Irrigation Ingestion Rate (Irw, L/day) Incidental ingestion of 5 ml water during irrigation of gardens Fraction Ingested from Source 100% Assumed to be 100% Bioavailability (B) 100% Assume 100% bioavailability via ingestion of chemicals in water. Exposure Frequency (EF, days/year) 90 Frequency relevant to garden irrigation (more conservative than municipal Exposure Duration (ED, years) 6 Duration of exposure as per NEPM 1999 and USEPA 1989 Body Weight (BW, kg) 13.2 Asper NEPM 1999 and enhealth 2002 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) 2190 USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background Intake (% TDI) TDI Allowable for Assessment (TDI- in Water (Cw) Daily Intake Non Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E % Mercury (as total, inroganic) 6.0E-04 40% 3.6E E E % TOTAL 0.066

6 Dermal Exposure to Chemicals via Contact with Water (Extracted Groundwater) DailyChemical Intake C DW W SAw ETDPCFEFED BW AT (L/kg/day) Parameters Relevant to Quantification of Exposure by Adult Workers - Industrial/Irrigation Water Surface Area (Saw, cm 2 ) 1120 Workers get hands wet (90% for adult males, USEPA 1997) during operation of the bore and watering activities Exposure Time (ET, hr/day) 8 Assume hands remain wet all day when used Conversion Factor (CF, L/cm 3 ) 1.E-03 Conversion of units Dermal Permeability (cm/hr) Chemical-specific (as below) Exposure Frequency (EF, days/yr) 96 Assume contact with industrial water 2 days per work week Exposure Duration (ED, years) 30 Duration of exposure as per NEPM 1999 and USEPA 1989 Body Weight (BW, kg) 78 as per enhealth (2012) Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background TDI Allowable for Intake (% TDI) Assessment (TDI- Dermal Permeability (DP) in Water (Cw) Daily Intake Non- Non- Calculated % Tota l Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (cm/hr) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E E % Mercury (as total, inroganic) 4.2E-05 40% 2.5E E E E % 0.30

7 Dermal Exposure to Chemicals via Contact with Water (Extracted Groundwater) DailyChemical Intake C DW W SAw ETDPCFEFED BW AT (L/kg/day) Parameters Relevant to Quantification of Exposure by Adults - General Public - Irrigation Surface Area (Saw, cm 2 ) 6300 Exposed skin surface area for adults as per enhealth 2012 Exposure Time (ET, hr/day) 1 Assume adults remain wet for 1 hour each time Conversion Factor (CF, L/cm 3 ) 1.E-03 Conversion of units Dermal Permeability (cm/hr) Chemical-specific (as below) Exposure Frequency (EF, days/yr) 90 Frequency relevant to garden irrigation (more conservative than municipal Exposure Duration (ED, years) 35 Duration of exposure assumed (enhealth 2012) Body Weight (BW, kg) 78 enhealth 2012 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background TDI Allowable for Intake (% TDI) Assessment (TDI- Dermal Permeability (DP) in Water (Cw) Daily Intake Non- Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (cm/hr) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E E % Mercury (as total, inroganic) 4.2E-05 40% 2.5E E E E % 0.20

8 Dermal Exposure to Chemicals via Contact with Water (Extracted Groundwater) DailyChemical Intake C DW W SAw ETDPCFEFED BW AT (L/kg/day) Parameters Relevant to Quantification of Exposure by Older Children - General Public - Irrigation Surface Area (Saw, cm 2 ) 4865 Surface area of hands, lower legs, forearms and feet (USEPA 2011) Exposure Time (ET, hr/day) 1 Assume adults remain wet for 1 hour each time Conversion Factor (CF, L/cm 3 ) 1.E-03 Conversion of units Dermal Permeability (cm/hr) Chemical-specific (as below) Exposure Frequency (EF, days/yr) 90 Frequency relevant to garden irrigation (more conservative than municipal Exposure Duration (ED, years) 10 Duration of exposure as per NEPM 1999 and USEPA 1989 Body Weight (BW, kg) 34.5 As per USEPA 1997 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) 3650 USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background TDI Allowable for Intake (% TDI) Assessment (TDI- Dermal Permeability (DP) in Water (Cw) Daily Intake Non- Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (cm/hr) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E E % Mercury (as total, inroganic) 4.2E-05 40% 2.5E E E E % 0.35

9

10 Dermal Exposure to Chemicals via Contact with Water (Extracted Groundwater) DailyChemical Intake C DW W SAw ETDPCFEFED BW AT (L/kg/day) Parameters Relevant to Quantification of Exposure by Young Children - General Public - Irrigation Surface Area (Saw, cm 2 ) 2300 Exposed skin, hands, forearms, lower legs and feet as per enhealth 2012 Exposure Time (ET, hr/day) 1 Assume adults remain wet for 1 hour each time Conversion Factor (CF, L/cm 3 ) 1.E-03 Conversion of units Dermal Permeability (cm/hr) Chemical-specific (as below) Exposure Frequency (EF, days/yr) 90 Frequency relevant to garden irrigation (more conservative than municipal Exposure Duration (ED, years) 6 Duration of exposure as per NEPM 1999 and USEPA 1989 Body Weight (BW, kg) 13.2 As per NEPM 1999 and enhealth 2002 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) 2190 USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background TDI Allowable for Intake (% TDI) Assessment (TDI- Dermal Permeability (DP) in Water (Cw) Daily Intake Non- Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (cm/hr) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E E % Mercury (as total, inroganic) 4.2E-05 40% 2.5E E E E % 0.43

11 General Parameters Air s During Irrigation - Main Plumes (Reference: Guidelines for the Assessment and Management of Petroleum contaminated Sites in New Zealand) All Calculations NOTES: Vs = Volume of Air within Irrigation zone (m3) Chemical Parameters (H and MW) for taken from RAIS in August 2010 Q = Volumetric Flow rate of Water (L/min) 30 H (atm.m3/mol) = H' (dimensionless) / 41 Time = Duration of Irrigation (min) 60 d = Droplet diameter (cm) 0.2 t = Droplet drop time (s) 10 R = Gas Constant (atm.m3/mol/k) 8.20E-05 T = Absolute Temperature (K) 293 Ts = Sprinkler Water Temperature (K) 288 m1 = Water viscosity at 20oC (g/m.s) m2 = Water viscosity at Sprinkler Water Temperature (g/m.s) Chemical Parameters Calculations Liquid Mass Transfer Coefficient (cm/hr) Gas Phase Mass Transfer Coefficient (cm/hr) Overall Mass Transfer Coefficient (cm/hr) Adjusted Overall Mass Transfer Coefficient (cm/hr) Fraction Volatilised (mg/mg) Mass Volatilised (mg) in Soil Water (mg/l) COPC in Water (mg/l) Henry's Law (atm.m 3 /mol) Molecular Weight in Air (mg/m 3 ) Cw HL MW Kl Kg KL KL' fv Ms Cair Cwater Mercury (as methyl mercury) E-05 Mercury (as total, inroganic) E-01 Mercury (as elemental) E E E E E E E E-05

12 Inhalation of Volatiles (derived from Irrigation of Groundwater) Inhalation Exposure Conc V C a ET FI EF ED AT (mg/m 3 ) Parameters Relevant to Quantification of Exposure by Adult Workers - Industrial/Irrigation Water Exposure Time (ET, hr/day) 8 Assume use of water for 8 hours each time Fraction Inhaled from Contaminated Source (FI, unitless) 1 All derived from impacted groundwater Exposure Frequency (EF, days/yr) 96 Assume contact with industrial water 2 days per work week Exposure Duration (ED, years) 30 Duration of exposure as per NEPM 1999 and USEPA 1989 Averaging Time - Non (Atc, hours) USEPA 2009 Averaging Time - (Atn, hours) USEPA 2009 Inhalation Unit Chronic TC Background air Intake (% Chronic TC) Chronic TC Allowable for Assessment (TC- Daily Exposure Calculated in Air (Ca) Inhalation Exposure Inhalation Exposure Non- Chronic Hazard - - Quotient Non (mg/m 3 ) -1 (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (unitless) (unitless) Mercury (as methyl mercury) 8.1E-04 20% 6.4E Mercury (as total, inroganic) 2.1E-03 10% 1.9E Mercury (as elemental) 2.0E-04 10% 1.8E E E E % TOTAL

13 Inhalation of Volatiles (derived from Irrigation of Groundwater) Inhalation Exposure Conc V C a ET FI EF ED AT (mg/m 3 ) Parameters Relevant to Quantification of Exposure by Adults - General Public - Irrigation Exposure Time (ET, hr/day) 1 Assume the general public near irrigation for 1 hour each time Fraction Inhaled from Contaminated Source (FI, unitless) 1 All derived from impacted groundwater Exposure Frequency (EF, days/yr) 90 Frequency relevant to garden irrigation (more conservative than municipal irrigation) Exposure Duration (ED, years) 54 Duration of exposure as per NEPM 1999 and USEPA 1989 Averaging Time - Non (Atc, hours) USEPA 2009 Averaging Time - (Atn, hours) USEPA 2009 Inhalation Unit Chronic TC Background air Intake (% Chronic TC) Chronic TC Allowable for Assessment (TC- Daily Exposure Calculated in Air (Ca) Inhalation Exposure Inhalation Exposure Non- Chronic Hazard - - Quotient Non (mg/m 3 ) -1 (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (unitless) (unitless) Mercury (as methyl mercury) 8.1E-04 20% 6.4E Mercury (as total, inroganic) 2.1E-03 10% 1.9E Mercury (as elemental) 2.0E-04 10% 1.8E E E E % TOTAL

14 VAPOUR PARTITIONING, EMISSION AND AIR DISPERSION MODEL FOR CONTAMINATED SOIL & GROUNDWATER SOURCES Using Johnson & Ettinger Model (USEPA 2003) for VI and ASTM (2002) for Outdoors and Excavations Calculated Air s - Slab on Grade Commercial Building Above Impacted Groundwater Off-Site Site Specific Physical Input Parameters Units Abbrev. Value Comments Top Layer (unsaturated zone) Sand/Fill Depth to Groundwater [m] vd1 2 Assumed Moisture Content [ml/g] mocon 0.08 Default for sand Friebel & Nadebaum (2011) Soil Bulk Density [g/ml] rhob Default for sand, Friebel & Nadebaum (2011) Density of Solids [g/ml] sd 2.65 default Total Soil Porosity [ml/ml] theta 0.39 Calculated (1 - (rhob/sd)) Volumetric Water Content [ml/ml] wacon Calculated (mocon*rhob) Volumetric Air Content [ml/ml] acon Calculated (theta-wacon) Capillary Fringe Thickness of Capillary Fringe [m] cd 0.1 Estimated for on-site areas Volumetric Water Content [ml/ml] cfwacon 0.35 Value representative of capillary fringe, ASTM (2002) Volumetric Air Content [ml/ml] cfacon 0.04 Calculated (theta2-cfwacon) Receptor Specific Input Parameters Units Abbrev. Value Comments Building Characteristics Depth of Basement [m] basement 0 Slab on grade Width of Building [m] bwidth 10 Assumed size of workspace above impacts Length of Building [m] blength 10 Assumed size of workspace above impacts Area of Emission - Building Area [m 2 ] emarea Calculated based on building dimensions Proportion of site above contaminated groundwater Conservative estimate from review of data Foundation/wall thickness [m] fthick 0.10 Minimum relevant for commercial/industrial buildings Height of Room [m] boxh 2.4 Assumed for off-site offices Hourly Volume Exchange of Fresh Air [exch/hr] exchanges 2 Minimum exchange rate as per BCA Fraction of Cracks in Walls and foundation - cracks Default Value for type of building, USEPA 2004 Qbuilding [cm 3 /s] Qb Calculated, USEPA 2004 Is advective vapour flow significant? - Adv yes Based on building type/assumptions adopted Qsoil [cm 3 /s] Qs 13.3 Based on Qb/Qs ratio of Acrack [cm 2 ] Ac 3800 Calculated from building area and crack ratio, USEPA 2004 Volumetric Water Content in foundation/wall cracks [ml/ml] fwacon 0.12 Default Value Volumetric Air Content in foundation/wall cracks [ml/ml] facon Default Value Outdoor Air Characteristics Length of Contaminated Area [m] length 15 Assumed area outdoors contributing to outdoor concentration Width of Contaminated Area [m] width 15 Assumed area outdoors contributing to outdoor concentration Wind Speed Outdoors [m/s] wspd 4.9 Average 9am and 3pm winds from Sydney Airport Height of Outdoor Mixing Zone [m] outboxh 1.5 Default Value relevant for outdoors and excavations

15 Chemical Specific Parameters Water Solubility (mg/l) Koc (cm 3 /g) MW (g/mol) Air Diffusion Coefficient (cm 2 /s) Water Diffusion Coefficient (cm 2 /s) Vapour Pressure (mmhg) Henry's Law Constant (unitless) Mercury (as elemental) E Note: Physical/chemical properties obtained from RAIS website (January 2010) Vapour Transport Calculations Deff Layer 1 (cm 2 /s) Effective Diffusion Soil to Surface (cm 2 /s) Deff Layer 3 (cm 2 /s) Deff Foundations and Cracks (cm 2 /s) Deff Capillary Fringe (cm 2 /s) Total Effective Diffusion (GW to surface) (cm 2 /s) Total Effective Diffusion (GW to excavation) (cm 2 /s) Mercury (as elemental) 2.21E E E E E E E-4 Modelled Air s from Groundwater Source Phase Partitioning Results Dissolved Phase GW (mg/l) Modelled Vapour Phase (g/cm 3 ) Saturated Vapour (g/cm 3 ) Free Phase Mole Fraction (mol/mol) above Free Phase (g/cm 3 ) Vapour Phase Adopted (g/cm 3 ) Mercury (as elemental) E E E E-11 Calculated Air s Vapour Phase at Source 3 Vapour Phase at Source (mg/m 3 ) JE Attenuation Coefficient (unitless) Indoor Air (mg/m 3 ) Outdoor Air (mg/m 3 ) Excavation Air (mg/m 3 ) Mercury (as elemental) 5.6E E E E E-08

16 Inhalation of Volatiles (derived from Groundwater Source) Inhalation Exposure Conc V C a ET FI EF AT ED (mg/m 3 ) Parameters Relevant to Quantification of Exposure by Adult Workers Exposure Time Indoors (ET, hr/day) 10 Assumed long workday Fraction Inhaled from Contaminated Source (FI, unitless) 1 Assume all areas affected by impacted groundwater Exposure Frequency (EF, days/yr) 240 Working days per year Exposure Duration (ED, years) 30 Working lifetime as per enhealth 2012 Averaging Time - Non (Atc, hours) USEPA 2009 Averaging Time - (Atn, hours) USEPA 2009 Inhalation Unit Chronic TC Background air Intake (% Chronic TC) Chronic TC Allowable for Assessment (TC- Daily Exposure Calculated in Air (Ca) Inhalation Exposure Inhalation Exposure Non- Chronic Hazard - - Quotient Non (mg/m 3 ) -1 (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (unitless) (unitless) Mercury (as methyl mercury) 8.1E-04 20% 6.4E Mercury (as total, inroganic) 2.1E-03 10% 1.9E Mercury (as elemental) 2.0E-04 10% 1.8E E E E TOTAL

17 Inhalation of Volatiles (derived from Groundwater Source) Inhalation Exposure Conc V C a ET FI EF AT ED (mg/m 3 ) Parameters Relevant to Quantification of Exposure by General Public Visiting Area Exposure Time Indoors (ET, hr/day) 1 Assumed time spent indoors visiting businesses Fraction Inhaled from Contaminated Source (FI, unitless) 1 Assume all areas affected by impacted groundwater Exposure Frequency (EF, days/yr) 20 Assume visits to the premises in the area over 20 days each year Exposure Duration (ED, years) 10 Assume visits occur over 10 separate years Averaging Time - Non (Atc, hours) USEPA 2009 Averaging Time - (Atn, hours) USEPA 2009 Inhalation Unit Chronic TC Background air Intake (% Chronic TC) Chronic TC Allowable for Assessment (TC- Daily Exposure Calculated in Air (Ca) Inhalation Exposure Inhalation Exposure Non- Chronic Hazard - - Quotient Non (mg/m 3 ) -1 (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (unitless) (unitless) Mercury (as methyl mercury) 8.1E-04 20% 6.4E Mercury (as total, inroganic) 2.1E-03 10% 1.9E Mercury (as elemental) 2.0E-04 10% 1.8E E E E TOTAL

18 Exposure to Chemicals via Incidental Ingestion of Water (shallow groundwater) IR (L/kg/day) W FIBEFED Daily ChemicalIntakeIW CW BWAT Parameters Relevant to Quantification of Exposure by Workers involved in Excavations Ingestion Rate (Irw, L/day) Incidental ingestion of 5 ml water Fraction Ingested from Source 100% Assumed to be 100% Bioavailability (B) 100% Assume 100% bioavailability via ingestion of chemicals in water. Exposure Frequency (EF, days/year) 10 Assume intrusive works on services occur over 10 days each year Exposure Duration (ED, years) 5 Assume works occur on the same site over 5 years Body Weight (BW, kg) 78 enhealth 2012 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) 1825 USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background Intake (% TDI) TDI Allowable for Assessment (TDI- in Water (Cw) Daily Intake Non Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E % Mercury (as total, inroganic) 6.0E-04 40% 3.6E E E % TOTAL

19 Exposure to Chemicals via Incidental Ingestion of Water (shallow groundwater) DailyChemical Intake C DW W SAw ETDPCFEFED BW AT (L/kg/day) Parameters Relevant to Quantification of Exposure by Workers involved in Excavations Surface Area (Saw, cm 2 ) 3300 Exposed surface area for construction workers as per USEPA 2001 Exposure Time (ET, hr/day) 3.3 Assume workers in excavation and wet for 33% of time on site (total 10 hrs/day) Conversion Factor (CF, L/cm 3 ) 1.E-03 Conversion of units Dermal Permeability (cm/hr) Chemical-specific (as below) Exposure Frequency (EF, days/yr) 10 Assume intrusive works on services occur over 10 days each year Exposure Duration (ED, years) 5 Assume works occur on the same site over 5 years Body Weight (BW, kg) 78 enhealth 2012 Averaging Time - Non (Atc, days) USEPA 1989 and CSMS 1996 Averaging Time - (Atn, days) 1825 USEPA 1989 and CSMS 1996 Non- Slope Factor TDI Background Intake (% TDI) TDI Allowable for Assessment (TDI- Dermal Permeability (DP) in Water (Cw) Daily Intake Non- Non- Calculated Chronic Hazard Quotient (mg/kg-day) -1 (mg/kg/day) (mg/kg/day) (cm/hr) (mg/l) (mg/kg/day) (mg/kg/day) (unitless) (unitless) Mercury (as methyl mercury) 2.3E-04 20% 1.8E E E E % Mercury (as total, inroganic) 4.2E-05 40% 2.5E E E E % 0.039

20 Inhalation of Volatiles (derived from Irrigation of Groundwater) Inhalation Exposure Conc V C a ET FI EF ED AT (mg/m 3 ) Parameters Relevant to Quantification of Exposure by Adult Workers - Industrial Water Exposure Time (ET, hr/day) 10 Assume working day is 10 hours Fraction Inhaled from Contaminated Source (FI, unitless) 1 All derived from impacted groundwater Exposure Frequency (EF, days/yr) 10 Assume intrusive works on services occur over 10 days each year Exposure Duration (ED, years) 5 Assume works occur on the same site over 5 years Averaging Time - Non (Atc, hours) USEPA 2009 Averaging Time - (Atn, hours) USEPA 2009 Inhalation Unit Chronic TC Background air Intake (% Chronic TC) Chronic TC Allowable for Assessment (TC- Daily Exposure Calculated in Air (Ca) Inhalation Exposure Inhalation Exposure Non- Chronic Hazard - - Quotient Non (mg/m 3 ) -1 (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (mg/m 3 ) (unitless) (unitless) Mercury (as methyl mercury) 8.1E-04 20% 6.4E Mercury (as total, inroganic) 2.1E-03 40% 1.3E Mercury (as elemental) 2.0E-04 10% 1.8E E E E TOTAL

Appendix C Risk Calculations: Western Margin of Northern Plumes

Appendix C Risk Calculations: Western Margin of Northern Plumes Appendix C Calculations: Western Margin of Northern Plumes Consolidated Human Health Assessment - 2017 Table of Contents C1.0 Introduction... C-1 C2.0 Calculation of Exposure and : Young Children... C-2

More information

Appendix C Risk Calculations Western Margin of Northern Plumes

Appendix C Risk Calculations Western Margin of Northern Plumes Appendix C Calculations Western Margin of Northern Plumes Consolidated Human Health Assessment - 2010 General Parameters Air s During Irrigation (Reference: Guidelines for the Assessment and Management

More information

Risk Assessment Report for AGSS-ICS

Risk Assessment Report for AGSS-ICS 1. INTRODUCTION This Risk Assessment evaluated the human health risks from exposure during and after application of AGSS-ICS. This information will determine whether AGSS-ICS used to treat soil will present

More information

B Supporting Information for Human Health Risk Assessment

B Supporting Information for Human Health Risk Assessment B Supporting Information for Human Health Risk Assessment 001688.OY06.06_PT083 Appendix B Table of Contents 1. Calculation of Infant Body Weight 2. Calculation of Consumption Rate of Meat for Native American

More information

ANNEX A. Subchapter A. GENERAL PROVISIONS * * * * *

ANNEX A. Subchapter A. GENERAL PROVISIONS * * * * * ANNEX A TITLE 25. ENVIRONMENTAL PROTECTION PART I. DEPARTMENT OF ENVIRONMENTAL PROTECTION SUBPART D. ENVIRONMENTAL HEALTH AND SAFETY ARTICLE VI. GENERAL HEALTH AND SAFETY CHAPTER 250. ADMINISTRATION OF

More information

Evaluation of Mixture Exposures in Human Health Risk Assessments. Ruth Custance, MPH

Evaluation of Mixture Exposures in Human Health Risk Assessments. Ruth Custance, MPH Evaluation of Mixture Exposures in Human Health Risk Assessments Ruth Custance, MPH March 2016 Objectives Objectives Describe each of the major steps of a HHRA Data Evaluation What chemicals and at what

More information

Development of Interim CCME PCB Soil Quality Guidelines for Missing Pathways of Exposure for the Protection of Human Health and Ecological Receptors

Development of Interim CCME PCB Soil Quality Guidelines for Missing Pathways of Exposure for the Protection of Human Health and Ecological Receptors Development of Interim CCME PCB Soil Quality Guidelines for Missing Pathways of Exposure for the Protection of Human Health and Ecological Receptors By: Karl Bresee, B.Sc., PBD, P.Biol. Intrinsik Environmental

More information

Table H3-1 Values Used for Daily Intake/Absorbed Dose Inhalation of Particulates

Table H3-1 Values Used for Daily Intake/Absorbed Dose Inhalation of Particulates Table H3-1 Values Used for Daily Intake/Absorbed Dose of Particulates Exposure Point Receptor Age: Particulates See Below Adult Exposure Parameter Parameter Definition Units RME RME Equation/ Route Code

More information

Screening Level Health Risk Assessment of PCCD/PCDF Contamination Da Nang Airbase Case Study

Screening Level Health Risk Assessment of PCCD/PCDF Contamination Da Nang Airbase Case Study Regional Capacity Building Program for Health Risk Management of Persistent Organic Pollutants (POPs) in South East Asia Program 7/15/2009 SLIDE 1 Screening Level Health Risk Assessment of PCCD/PCDF Contamination

More information

APPENDIX G: TECHNICAL BASIS FOR PRELIMINARY REMEDIATION GOALS FOR FISH TISSUE IN ONONDAGA LAKE HONEYWELL

APPENDIX G: TECHNICAL BASIS FOR PRELIMINARY REMEDIATION GOALS FOR FISH TISSUE IN ONONDAGA LAKE HONEYWELL : TECHNICAL BASIS FOR PRELIMINARY REMEDIATION GOALS FOR FISH TISSUE IN ONONDAGA LAKE Prepared For: HONEYWELL 101 Columbia Road P.O. Box 2105 Morristown, NJ 07962 Prepared By: Exponent 4 Computer Drive

More information

Development of NJ Human Health-based Criteria and Standards

Development of NJ Human Health-based Criteria and Standards Development of NJ Human Health-based Criteria and Standards Gloria Post NJDEP Office of Science Presented to: Public Health Standing Committee October 18, 2010 Human Health-based Criteria and Standards

More information

APPENDIX IV.I.1. Delivery Truck HRA

APPENDIX IV.I.1. Delivery Truck HRA APPENDIX IV.I.1 Delivery Truck HRA Diesel Particulate Matter (DPM) Health Risk Assessment (HRA) of Delivery Trucks from the Project at Pico and Sepulveda, Los Angeles, California Introduction This health

More information

Poly-fluoroalkyl substances (PFASs), also called perfluoroalkyl substances (PFASs)

Poly-fluoroalkyl substances (PFASs), also called perfluoroalkyl substances (PFASs) Poly-fluoroalkyl substances (PFASs), also called perfluoroalkyl substances (PFASs) Perfluorooctane sulphonic acid (PFOS), and perfluorooctanoic acid (PFOA) belong to a group of man-made compounds called

More information

Evaluation of Swimming Pool Treatment Chemicals Health Effects under NSF/ANSI Standard 50

Evaluation of Swimming Pool Treatment Chemicals Health Effects under NSF/ANSI Standard 50 Evaluation of Swimming Pool Treatment Chemicals Health Effects under NSF/ANSI Standard 50 Presentation Outline About NSF International NSF/ANSI 50 Overview Development Process of Annex R Annex R Requirements

More information

AECOM Environment Figures January 2010

AECOM Environment Figures January 2010 AECOM Environment Figures January 2010 Figure 1 General Monitoring Approach Readville 5-Yard Site Dedham and Readville, MA Real-ime Monitoring Constituent-Specific Monitoring Conduct Field Screening for

More information

EVALUATION OF POLYCYCLIC AROMATIC HYDROCARBONS IN CLAY TARGET FRAGMENTS AND SURFACE SOIL AT SHOT GUN RANGE SITES Presenter: Glenn Hoeger and Brian

EVALUATION OF POLYCYCLIC AROMATIC HYDROCARBONS IN CLAY TARGET FRAGMENTS AND SURFACE SOIL AT SHOT GUN RANGE SITES Presenter: Glenn Hoeger and Brian EVALUATION OF POLYCYCLIC AROMATIC HYDROCARBONS IN CLAY TARGET FRAGMENTS AND SURFACE SOIL AT SHOT GUN RANGE SITES Presenter: Glenn Hoeger and Brian Magee ARCADIS/Malcolm Pirnie May 11, 2011 Objectives 1.

More information

Benzo[a]Pyrene Update - A Game Changer for Environmental Remediation and Property Revitalization? April 28, Presented by Kristen Rivera

Benzo[a]Pyrene Update - A Game Changer for Environmental Remediation and Property Revitalization? April 28, Presented by Kristen Rivera Benzo[a]Pyrene Update - A Game Changer for Environmental Remediation and Property Revitalization? April 28, 2017 Presented by Kristen Rivera What is Benzo[a]Pyrene (BaP)? Polycyclic aromatic hydrocarbon

More information

ENV 455 Hazardous Waste Management

ENV 455 Hazardous Waste Management Risk Assessment Basic Information ENV 455 Hazardous Waste Management Environmental Risk Assessment Özgür ZEYDAN (Phd.) http://cevre.beun.edu.tr/zeydan/ Hazard: a potential source of harm to a worker. Risk:

More information

Prelude to Risk Characterization Exposure Calculations from Risk and Decision Making

Prelude to Risk Characterization Exposure Calculations from Risk and Decision Making ENV U6220 THURSDAY, 8/04/05 RISK CHARACTERIZATION / MANAGEMENT PAGE 1 Prelude to Risk Characterization Exposure Calculations from Risk and Decision Making ENV U6220 THURSDAY, 8/04/05 RISK CHARACTERIZATION

More information

5.0 HAZARD ASSESSMENT AND RISK CHARACTERIZATION

5.0 HAZARD ASSESSMENT AND RISK CHARACTERIZATION 5.0 HAZARD ASSESSMENT AND RISK CHARACTERIZATION 5.1 SELECTING A TOXICITY REFERENCE VALUE (TRV) Appropriate Toxicity Reference Values (TRVs) are required to characterize the potency of the contaminants

More information

Assessing Risks for Inhalation and Ingestion of Pollutants

Assessing Risks for Inhalation and Ingestion of Pollutants Assessing Risks for and Ingestion of Pollutants This investigation focuses on the basics of human and ecological risk assessment. The activity uses hypothetical scenarios to investigate inhalation of an

More information

Updates to HSRA Risk Reduction Standards

Updates to HSRA Risk Reduction Standards Updates to HSRA Risk Reduction Standards Georgia AWMA Regulatory Update Conference May 11, 2017 Chris Saranko, Ph.D, DABT Atlanta, GA Presentation Outline 2017 Hazardous Site Response Rulemaking Phased

More information

Human Health Risk Assessment Guidance

Human Health Risk Assessment Guidance Human Health Risk Assessment Guidance Oregon Department of Environmental Quality Environmental Cleanup Program 811 SW Sixth Avenue Portland, OR 97204 DRAFT May 12, 2010 I. ACKNOWLEDGEMENTS The primary

More information

Hazard, exposure, and risk Thinking about risk Risk assessment processes Risk management A.001 Environmental Engineering 2

Hazard, exposure, and risk Thinking about risk Risk assessment processes Risk management A.001 Environmental Engineering 2 1 Hazard, exposure, and risk Thinking about risk Risk assessment processes Risk management 457.210A.001 Environmental Engineering 2 2015 2 Hazard: the inherent properties of a substance, object, or activity

More information

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES WASHINGTON, D.C

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES WASHINGTON, D.C UNITED STATES ENVIRONMENTAL PROTECTION AGENCY OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES WASHINGTON, D.C. 20460 September 7, 2005 MEMORANDUM Subject: From: Through: Occupational and Residential

More information

Methodology for Developing Chemical Exposure Guidelines for Deployed Military Personnel

Methodology for Developing Chemical Exposure Guidelines for Deployed Military Personnel 2013 REVISION Methodology for Developing Chemical Exposure Guidelines for Deployed Military Personnel Reference Document 230 2013 Addendum This is the support document for Technical Guide 230 U.S. Army

More information

Screening-Level Risk Assessment for Styrene- Acrylonitrile (San) Trimer Detected in Soil and Groundwater

Screening-Level Risk Assessment for Styrene- Acrylonitrile (San) Trimer Detected in Soil and Groundwater University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln U.S. Environmental Protection Agency Papers U.S. Environmental Protection Agency 2012 Screening-Level Risk Assessment for

More information

Human Health Risk Assessment. Marian Olsen U.S. EPA ERRD October 13, 2011

Human Health Risk Assessment. Marian Olsen U.S. EPA ERRD October 13, 2011 Human Health Risk Assessment Marian Olsen U.S. EPA ERRD October 13, 2011 Presentation Overview Conceptual Site Model Defining Risk Assessment Conceptual Site Model Superfund Risk Assessment Process Data

More information

KOP-COAT NEW ZEALAND LIMITED

KOP-COAT NEW ZEALAND LIMITED STATEMENT OF HAZARDOUS NATURE: Inhalation of wood dust may cause irritation Certain wood species may cause skin, and respiratory tract sensitization COMPANY DETAILS COMPANY: Kop-Coat, Inc Kop-Coat New

More information

HEALTH CONSIDERATIONS RELATED TO ARSENIC IN SOIL UNDER PLAYGROUND EQUIPMENT CONSTRUCTED OF CCA-TREATED WOOD

HEALTH CONSIDERATIONS RELATED TO ARSENIC IN SOIL UNDER PLAYGROUND EQUIPMENT CONSTRUCTED OF CCA-TREATED WOOD HEALTH CONSIDERATIONS RELATED TO ARSENIC IN SOIL UNDER PLAYGROUND EQUIPMENT CONSTRUCTED OF CCA-TREATED WOOD Prepared for: Hopping Green Sams & Smith Tallahassee, FL and American Wood Preservers Institute

More information

HEEG opinion on. Assessment of Inhalation Exposure of Volatilised Biocide Active Substance

HEEG opinion on. Assessment of Inhalation Exposure of Volatilised Biocide Active Substance EUROPEAN COMMISSION JOINT RESEARCH CENTRE Institute for Health and Consumer Protection Chemical assessment and testing HEEG Opinion 1 Endorsed at TM IV 2011 and amended after TM III 201 to take into account

More information

1, 2, 3-Trichloropropane (TCP): Assessment of Risks from Drinking Water

1, 2, 3-Trichloropropane (TCP): Assessment of Risks from Drinking Water 1, 2, 3-Trichloropropane (TCP): Assessment of Risks from Drinking Water 1, 2, 3-Trichloropropane (TCP): Assessment of Risks from Drinking Water Prepared for Alaimo Group (Engineers and Architects) 200

More information

Appendix B Toxicity of Mercury

Appendix B Toxicity of Mercury Appendix B Toxicity of Mercury - 2013 B1 General Mercury is a heavy metal which exists in three oxidation states: 0 (elemental), +1 (mercurous) and +2 (mercuric). As well as the common mercurous and mercuric

More information

Outline: risk assessment. What kind of environmental risks do we commonly consider? 11/19/2013. Why do we need chemical risk assessment?

Outline: risk assessment. What kind of environmental risks do we commonly consider? 11/19/2013. Why do we need chemical risk assessment? Outline: Human health h and ecological l risk assessment Purpose of risk assessment Methodology for quantifying risk Case study: Children s exposure to As from CCA wood staircases Issues practical and

More information

Product: H12MDI (4,4 -Methylene dicyclohexyl diisocyanate; CAS No )

Product: H12MDI (4,4 -Methylene dicyclohexyl diisocyanate; CAS No ) February 013 Properties, Hazards and Safety Information for H1MDI* Product: H1MDI (4,4 -Methylene dicyclohexyl diisocyanate; CAS No. 514-30-1) Physical and chemical data Physical state liquid Colour colourless

More information

1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION. Material for temporary filling and rebuilding root canals

1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION. Material for temporary filling and rebuilding root canals Page 1 of 7 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION Product name: BIO MTA + Application: Manufacturer s name: Material for temporary filling and rebuilding root canals Wojciech Pawłowski 37-450

More information

Chapter 6 Quantifying Exposure

Chapter 6 Quantifying Exposure What s Covered in Chapter 6: Chapter 6 Quantifying Exposure 6.1 Inhalation Exposure Pathways 6.2 Ingestion Exposure Pathways 6.3 Dermal Exposure Pathways 6.4 Exposure Frequency 6.5 Exposure Duration 6.6

More information

Risk Characterization

Risk Characterization Risk Characterization 1 Learning Objectives By the end of this module, participants should have an understanding of: The purpose of risk characterization Integrating the results of hazard identification,

More information

Appendix I DOCUMENTS RECEIVED OR USED IN PREPARATION OF THE HUMAN HEALTH RISK ASSESSMENT FOR THE STRECKER FOREST DEVELOPMENT SITE, WILDWOOD MO

Appendix I DOCUMENTS RECEIVED OR USED IN PREPARATION OF THE HUMAN HEALTH RISK ASSESSMENT FOR THE STRECKER FOREST DEVELOPMENT SITE, WILDWOOD MO Appendix I DOCUMENTS RECEIVED OR USED IN PREPARATION OF THE HUMAN HEALTH RISK ASSESSMENT FOR THE STRECKER FOREST DEVELOPMENT SITE, WILDWOOD MO ATSDR. 1998. TOXICOLOGICAL PROFILE FOR CHLORINATED DIBENZO-p-

More information

Sacramento Rendering Company Health Risk Assessment

Sacramento Rendering Company Health Risk Assessment Sacramento Rendering Company Health Risk Assessment The SMAQMD regulates emissions of toxic substances under Rule 402 and SMAQMD s guidance document, Health Risk Management Programs for Existing, Modified

More information

TRIS (NONYLPHENYL) PHOSPHITE SUMMARY RISK ASSESSMENT REPORT

TRIS (NONYLPHENYL) PHOSPHITE SUMMARY RISK ASSESSMENT REPORT TRIS (NONYLPHENYL) PHOSPHITE CAS-No.: 26523-78-4 EINECS-No.: 247-759-6 SUMMARY RISK ASSESSMENT REPORT Final report, 2007 France Rapporteur for the risk assessment of tris(nonylphenyl) phosphite is the

More information

Arkansas Department of Health

Arkansas Department of Health Mr. Jim Wise Ecologist Coordinator, Office of Water Arkansas Department of Environmental Quality 5301 Northshore Drive North Little Rock, AR 72118-5317 Dear Mr. Wise: Arkansas Department of Health 4815

More information

Risk Assessment Pt2. K.E. Kelly University of Utah

Risk Assessment Pt2. K.E. Kelly University of Utah Risk Assessment Pt2 K.E. Kelly University of Utah Reminders/Updates I will post the solu.on to HW#1 on Tuesday evening. - Presenta.on topics and schedules are up. Please review the schedule. I have done

More information

Part 2. Chemical and physical aspects

Part 2. Chemical and physical aspects Part 2. Chemical and physical aspects 12. Chemical and physical aspects: introduction 12.1 Background information used The assessment of the toxicity of drinking-water contaminants has been made on the

More information

Material Safety Data Sheet of dangerous substance METHYLENE CHLORIDE (DICHLOROMETHANE) 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION

Material Safety Data Sheet of dangerous substance METHYLENE CHLORIDE (DICHLOROMETHANE) 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION Page 1 of 7 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION Product name: Application: Distributor: METHYLENE CHLORIDE Solvent Wojciech Pawłowski 37-450 Stalowa Wola ul. Kwiatkowskiego 1 Tel. 015 / 842

More information

RISK ASSESSMENT GUIDANCE FOR SUPPLEMENTAL GUIDANCE FOR INHALATION RISK ASSESSMENT SUPERFUND, PART F: Midwestern States Risk Assessment

RISK ASSESSMENT GUIDANCE FOR SUPPLEMENTAL GUIDANCE FOR INHALATION RISK ASSESSMENT SUPERFUND, PART F: Midwestern States Risk Assessment RISK ASSESSMENT GUIDANCE FOR SUPERFUND, PART F: SUPPLEMENTAL GUIDANCE FOR INHALATION RISK ASSESSMENT Michael Sivak EPA Region 2 Superfund Program Midwestern States Risk Assessment Symposium - November

More information

Product: IPDI (Isophorone diisocyanate; CAS No )

Product: IPDI (Isophorone diisocyanate; CAS No ) November 2015 Properties, Hazards and Safety Information for IPDI* Product: IPDI (Isophorone diisocyanate; CAS No. 4098-71-9) Physical and chemical data Physical state liquid Colour colourless to yellowish

More information

HUMAN HEALTH RISK ASSESSMENT THROUG TitleCHAIN IN SOME AREAS WITH HIGH ARSEN CONCENTRATION Author(s) Nguyen, Thi phuong Thao Annual Report of FY 2004, The Core Citation between Japan Society for the Promo

More information

SAFETY DATA SHEET. Natural Guard Neem RTU. Effective Date: 23-Mar PRODUCT AND COMPANY IDENTIFICATION

SAFETY DATA SHEET. Natural Guard Neem RTU. Effective Date: 23-Mar PRODUCT AND COMPANY IDENTIFICATION 1. PRODUCT AND COMPANY IDENTIFICATION PRODUCT NAME: Neem RTU EPA Reg. No.: 70051-13-7401 COMPANY IDENTIFICATION: Bonham, TX. 75418 2. HAZARDS IDENTIFICATION 2.1. Classification of the substance or mixture

More information

Pizza Pan Case Study

Pizza Pan Case Study Session 4 Case Study of Risk Assessment and Management Pizza Pan Case Study Fernanda Takata The Dow Chemical Company, Product Stewardship and Regulatory Specialist 16 March, May, 2013 2011 Taipei Chile

More information

1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION

1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION Page 1 of 6 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION Product name: Application: Manufacturer: ENDO-SOLution Liquid for root canal preparation Wojciech Pawłowski 37-450 Stalowa Wola ul. Kwiatkowskiego

More information

RISK ASSESSMENT OF EXPOSURE TO BENZENE, TOLUENE AND FORMALDEHYDE IN RESIDENTIAL ENVIRONMENT IN CHINA

RISK ASSESSMENT OF EXPOSURE TO BENZENE, TOLUENE AND FORMALDEHYDE IN RESIDENTIAL ENVIRONMENT IN CHINA RISK ASSESSMENT OF EXPOSURE TO BENZENE, TOLUENE AND FORMALDEHYDE IN RESIDENTIAL ENVIRONMENT IN CHINA C Zheng 1, GQ Zhang 1,*, J.H Hao 2, J.P Lin 2, YH Liu 2 1 College of Civil Engineering, Hunan University,

More information

CURRENT ISSUES: Risk-Based Corrective Action 14 TH ANNUAL FLORIDA BROWNFIELDS CONFERENCE & EXHIBITION

CURRENT ISSUES: Risk-Based Corrective Action 14 TH ANNUAL FLORIDA BROWNFIELDS CONFERENCE & EXHIBITION 14 TH ANNUAL FLORIDA BROWNFIELDS CONFERENCE & EXHIBITION November 14, 2011 Orlando, Florida CURRENT ISSUES: Risk-Based Corrective Action Paula Cobb, Esq Hopping Green & Sams Tallahassee, FL Koren Taylor,

More information

1,4-Dioxane: Overview & NJDEP Ground Water Quality Criterion

1,4-Dioxane: Overview & NJDEP Ground Water Quality Criterion 1,4-Dioxane: Overview & NJDEP Ground Water Quality Criterion Gloria B. Post, Ph.D., DABT New Jersey Drinking Water Quality Institute December 18, 2018 USGS Water Science Center Lawrenceville, NJ Information

More information

APPENDIX A STANDARD FORMULAS, EXPOSURE DATA, AND RISK CALCULATIONS FOR OCCUPATIONAL AND RESIDENTIAL EXPOSURES TO MEFLUIDIDE

APPENDIX A STANDARD FORMULAS, EXPOSURE DATA, AND RISK CALCULATIONS FOR OCCUPATIONAL AND RESIDENTIAL EXPOSURES TO MEFLUIDIDE APPENDIX A STANDARD FORMULAS, EXPOSURE DATA, AND RISK CALCULATIONS FOR OCCUPATIONAL AND RESIDENTIAL EXPOSURES TO MEFLUIDIDE 1 APPENDIX A -1 STANDARD FORMULAS USED FOR CALCULATING OCCUPATIONAL AND RESIDENTIAL

More information

UNITED STATES AIR FORCE IERA

UNITED STATES AIR FORCE IERA IERA-RS-BR-TR-2000-0005 UNITED STATES AIR FORCE IERA Human Health Risk Assessment, Pope Air Force Base, North Carolina (AMC) Victor Caravello, Captain, USAF, BSC G. Cornell Long July 2000 Air Force Institute

More information

Risk assessment for redevelopment of contaminated land at an old industrial site

Risk assessment for redevelopment of contaminated land at an old industrial site 5th WSEAS nt. Conf. on ENVRONMENT, ECOSYSTEMS and DEVELOPMENT, Tenerife, Spain, December 14-16, 2007 358 Risk assessment for redevelopment of contaminated land at an old industrial site D.F. VENDAS (a,1),

More information

Safety Data Sheet according to COMMISSION REGULATION (EU) 2015/830 (REACH)

Safety Data Sheet according to COMMISSION REGULATION (EU) 2015/830 (REACH) Safety Data Sheet according to COMMISSION REGULATION (EU) 2015/830 (REACH) Validity Print date Last revision Version 01 IDENTIFICATION OF THE SUBSTANCE/MIXTURE AND OF THE COMPANY/UNDERTAKING EU, CH 02.01.2013

More information

Contains: Hydrocarbons, C9-C12, n-alkanes, isoalkanes, cyclics, aromatics (2-25%), 60-80% EC No.:

Contains: Hydrocarbons, C9-C12, n-alkanes, isoalkanes, cyclics, aromatics (2-25%), 60-80% EC No.: 1. Identification of the substance/mixture and of the company/undertaking 1.1. Product identifier Material/trade name: Product number(s): 91003 / 91125 1.2. Relevant identified uses of the substances or

More information

SAFETY DATA SHEET (SDS)

SAFETY DATA SHEET (SDS) 1. PRODUCT AND COMPANY IDENTIFICATION SAFETY DATA SHEET (SDS) Product Name: Product Number: Formula: Product Use: Restrictions on Use: NaturaLyte (45X) (0000 through 4000 Series) None Solution: Acetic

More information

Human health effects of antimony an update

Human health effects of antimony an update Human health effects of antimony an update Dr. R.V. Battersby EBRC Consulting GmbH Karine Van de Velde i2a Secretary General Raffaelstr. 4 30177 Hannover Germany Public perception of HH effects of antimony

More information

Section 1 - Product Information. Section 2 - Composition/Information on Ingredient. Section 3 - Hazards Identification. Product Name GOSSYPOL

Section 1 - Product Information. Section 2 - Composition/Information on Ingredient. Section 3 - Hazards Identification. Product Name GOSSYPOL Section 1 - Product Information Product Name GOSSYPOL Product Number ST065835 Supplier: TimTec LLC www.timtec.net info@timtec.net Section 2 - Composition/Information on Ingredient Substance Name CAS #

More information

SAFETY DATA SHEET. Issue Date: 05/25/2015 Version No: 1 1. Identification

SAFETY DATA SHEET. Issue Date: 05/25/2015 Version No: 1 1. Identification Page 1 of 7 1. Identification Product identifier Application of the substance or the preparation Addition curing vinyl polysiloxane dental impression materials (consisting of Base & Catalyst) Manufacturer/Supplier

More information

Dental City - VPS Putty SAFETY DATA SHEET

Dental City - VPS Putty SAFETY DATA SHEET Issue Date: 2/5/207. Identification Page of 9 Product identifier Trade name: Dental City - VPS Putty 49-8008 Fast Set / 49-8006 Regular Set Application of the substance or the preparation Addition curing

More information

GPS Safety Summary - TOLUENE

GPS Safety Summary - TOLUENE GPS Safety Summary - TOLUENE SUBSTANCE NAME TOLUENE CHEMICAL IDENTITY Name: TOLUENE Chemical name (IUPAC): TOLUENE CAS number: 108-88-3 EC number: 203-625-9 Molecular formula: C 7 H 8 Structure: USES AND

More information

ATTACHMENT E. Selection of Soil Ingestion Rates

ATTACHMENT E. Selection of Soil Ingestion Rates ATTACHMENT E Selection of Soil Ingestion Rates In assessing exposures and risks from the ingestion of floodplain soil, the HHRA evaluates eleven exposure scenarios (including residential, recreational,

More information

Risk Assessment Report on Tris (nonylphenyl)phosphite (TNPP)

Risk Assessment Report on Tris (nonylphenyl)phosphite (TNPP) EUROPEAN COMMISSION HEALTH & CONSUMER PROTECTION DIRECTORATE-GENERAL Directorate C - Public Health and Risk Assessment C7 - Risk assessment SCIENTIFIC COMMITTEE ON HEALTH AND ENVIRONMENTAL RISKS SCHER

More information

Appendix B Toxicity Summaries

Appendix B Toxicity Summaries Appendix B Toxicity Summaries Table of Contents B1 Introduction... B-1 B2 Carbon Tetrachloride... B-2 B3 Chloroform... B-8 B4 Dichloromethane... B-14 B5 1,1,2,2-Tetrachloroethane... B-20 B6 1,1,2-Trichloroethane...

More information

GPS Safety Summary. 2-Phenoxyethyl acrylate

GPS Safety Summary. 2-Phenoxyethyl acrylate GPS Safety Summary Substance Name: 2-Phenoxyethyl Acrylate 1. General Statement 2-Phenoxyethyl acrylate is a monofunctional acrylic monomer which can be polymerised by free radicals. In particular, 2-Phenoxyethyl

More information

GPS Safety Summary. N-(2-Methacryloxyethyl) ethylene urea (25 % solution in methyl methacrylate)

GPS Safety Summary. N-(2-Methacryloxyethyl) ethylene urea (25 % solution in methyl methacrylate) GPS Safety Summary (25 % solution in methyl methacrylate) The Product Safety Summary is intended to provide a general overview of the chemical substance in the context of ICCA Global Product Strategy.

More information

Toxicology. Toxicity. Human Health Concerns. Health Effects of Hazardous Materials

Toxicology. Toxicity. Human Health Concerns. Health Effects of Hazardous Materials Human Health Concerns Health Effects of Hazardous Materials Toxicology Study of the nature, effects, and detection of poisons in organisms Humans are obvious focal point Other species and ecosystem function

More information

Updated Health Risk Assessment Guidelines

Updated Health Risk Assessment Guidelines Updated Health Risk Assessment Guidelines California OEHHA s Air Toxics Hot Spots Program March 31 st, 2015 Insert then choose Picture select your picture. Right click your picture and Send to back. Copyright

More information

American Chemistry Council n-alkane VCCEP Consortium

American Chemistry Council n-alkane VCCEP Consortium American Chemistry Council n-alkane VCCEP Consortium Errata and Clarifications to n-alkane Category: Decane, Undecane, Dodecane (CAS Nos. 124-18-5, 1120-21-4, 112-40-3) Voluntary Children s Chemical Evaluation

More information

SAFETY DATA SHEET according to Regulation (EU) 2015/830

SAFETY DATA SHEET according to Regulation (EU) 2015/830 SAFETY DATA SHEET according to Regulation (EU) 205/830 Page /6 SECTION : Identification of the substance/mixture and of the company/undertaking.. Product identifier Product name Product code BDCCBS4.2.

More information

Cancer Risk Assessment from Trihalomethanes in Community Water Supply at Northeastern Thailand

Cancer Risk Assessment from Trihalomethanes in Community Water Supply at Northeastern Thailand Cancer Risk Assessment from Trihalomethanes in Community Water Supply at Northeastern Thailand Prapat Pentamwa, Benchamaporn Sukton, Tanisa Wongklom, and Sathaporn Pentamwa Abstract This study aims to

More information

SAFETY DATA SHEET according to 1907/2006/EC, Article 31

SAFETY DATA SHEET according to 1907/2006/EC, Article 31 SAFETY DATA SHEET according to 1907/006/EC, Article 31 SECTION 1: Identification of the substance/mixture and of the company/undertaking 1.1. Product identifier Product name CAS No. 1309-48-4 EC No. 15-171-9

More information

Date Printed: 1/24/2015 Product: M Wood Filler Natural Paste Qt. Surface Preparation or Protection

Date Printed: 1/24/2015 Product: M Wood Filler Natural Paste Qt. Surface Preparation or Protection Safety Data Sheet 1. Identification Product Information: Product Name: Recommended Use: Supplied by: M608-4206 Wood Filler Natural Paste Qt Surface Preparation or Protection CCI Finishworks Division of

More information

DARENT WAX COMPANY LIMITED SAFETY DATA SHEET

DARENT WAX COMPANY LIMITED SAFETY DATA SHEET 1. Identification of the substance/mixture and of the company/undertaking 1.1. Product identifier Material/trade name: Product number(s): 14504 14219-15508 1.2. Relevant identified uses of the substances

More information

Safety Data Sheet. KHA300 INTERTUF 262 OFF WHITE PART A Version Number 2 Revision Date 05/14/18

Safety Data Sheet. KHA300 INTERTUF 262 OFF WHITE PART A Version Number 2 Revision Date 05/14/18 International Paint Singapore Pte Ltd Safety Data Sheet KHA300 INTERTUF 262 OFF WHITE PART A Version Number 2 Revision Date 05/14/18 1. Product and company identification 1.1. Product identifier INTERTUF

More information

: SikaTop Armatec -110 EpoCem Part B

: SikaTop Armatec -110 EpoCem Part B SECTION 1: Identification of the hazardous chemical and of the supplier Product name : Product code : 000000022218 Type of product : liquid Recommended use of the chemical and restrictions on use Product

More information

Unit 5, Passfield Mill Business Park, Liphook, Hampshire, GU30 7RR +44 (0) (0)

Unit 5, Passfield Mill Business Park, Liphook, Hampshire, GU30 7RR +44 (0) (0) SAFETY DATA SHEET According to Regulation (EC) No. 1272/2008 on, Labelling and Packaging of Substances and Mixtures. SECTION 1: Identification of the substance/mixture and of the company/undertaking 1.1.

More information

Material Safety data sheet

Material Safety data sheet 1. IDENTIFICATION OF THE SUBSTANCE / PREPARATION AND THE COMPANY / UNDERTAKING Product Name: UTURN - PLANT GROWTH REGULATOR CAS No. 76738-62-0 SUPPLIER: SEVROC PTY.LTD ABN: 09947875 STREET ADDRESS: 51

More information

Bystander & Resident Exposure to Plant Protection Products

Bystander & Resident Exposure to Plant Protection Products Health and Safety Executive Bystander & Resident Exposure to Plant Protection Products Available Data and the EFSA Guidance Paul Y Hamey Overview Regulatory objective Bystanders (B) and residents (R)?

More information

Contains: Hydrocarbons, C9-C11, n-alkanes, isoalkanes, cyclics, < 2% aromatics, 40-60% EC No.:

Contains: Hydrocarbons, C9-C11, n-alkanes, isoalkanes, cyclics, < 2% aromatics, 40-60% EC No.: 1. Identification of the substance/mixture and of the company/undertaking 1.1. Product identifier Material/trade name: Product number(s): 92072 1.2. Relevant identified uses of the substances or mixture

More information

Version 0.1 Revision Date 06/02/2015 Print Date 06/02/2015

Version 0.1 Revision Date 06/02/2015 Print Date 06/02/2015 SECTION 1. PRODUCT AND COMPANY IDENTIFICATION Product name : Substance number : REL_11387 Chemical usage : Cleaning Compound Manufacturer or supplier's details Company : Chemetall US, Inc. Address : 675

More information

: SikaForce B Part B

: SikaForce B Part B SECTION 1: Identification of the hazardous chemical and of the supplier Product name : Product code : 000000611895 Type of product : liquid Manufacturer or supplier's details Company : Sika Kimia Sdn.

More information

Safety Summary. Ammophos Grade (MAP)

Safety Summary. Ammophos Grade (MAP) EuroChem-BMU Chemical Site Belorechensk Krasnodar Territory, 352636, Russia Safety Summary Global Product Strategy (GPS) according to the recommendations of International Council of Chemical Associations

More information

SAFETY DATA SHEET. Section 1: Identification of the substance/mixture and of the company/undertaking. Section 2: Hazards identification

SAFETY DATA SHEET. Section 1: Identification of the substance/mixture and of the company/undertaking. Section 2: Hazards identification Page: 1 Compilation date: 27-08-2015 Revision No: 1 Section 1: Identification of the substance/mixture and of the company/undertaking 1.1. Product identifier Product name: Product code: 3201-3211 1.2.

More information

Arsenic in the Environment

Arsenic in the Environment Arsenic in the Environment Teresa S. Bowers Gradient Corporation Presented at Middleport, New York October 28, 2008 2 Arsenic Occurs Naturally All arsenic in the environment is of natural origin (natural

More information

SAFETY DATA SHEET. Section 1: Identification of the substance/mixture and of the company/undertaking

SAFETY DATA SHEET. Section 1: Identification of the substance/mixture and of the company/undertaking SAFETY DATA SHEET Section 1: Identification of the substance/mixture and of the company/undertaking Product identifier Trade name or designation of the mixture Registration number FLUOROCARBON GEL 813-1

More information

SAFETY DATA SHEET Janitol Lo-Foam According to Regulation (EC) No 1907/2006, Annex II, as amended by Regulation (EU) No 453/2010

SAFETY DATA SHEET Janitol Lo-Foam According to Regulation (EC) No 1907/2006, Annex II, as amended by Regulation (EU) No 453/2010 SAFETY DATA SHEET According to Regulation (EC) No 1907/2006, Annex II, as amended by Regulation (EU) No 453/2010 SECTION 1: Identification of the substance/mixture and of the company/undertaking 1.1. Product

More information

SAFETY DATA SHEET BICOWHITE COMPLEX. SECTION 1: IDENTIFICATION OF THE SUBSTANCE/MIXTURE AND OF THE COMPANY/UNDERTAKING 1.1 Product Identifier BW_S3

SAFETY DATA SHEET BICOWHITE COMPLEX. SECTION 1: IDENTIFICATION OF THE SUBSTANCE/MIXTURE AND OF THE COMPANY/UNDERTAKING 1.1 Product Identifier BW_S3 Pag. 1/9 SAFETY DATA SHEET SECTION 1: IDENTIFICATION OF THE SUBSTANCE/MIXTURE AND OF THE COMPANY/UNDERTAKING 1.1 Product Identifier Code 1.2 Relevant identified uses of the substances or mixture and uses

More information

ABLEBOND 8361J Adhesive Page 1 of 6 December 19, 05 *** MATERIAL SAFETY DATA SHEET *** 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION

ABLEBOND 8361J Adhesive Page 1 of 6 December 19, 05 *** MATERIAL SAFETY DATA SHEET *** 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION ABLEBOND 8361J Adhesive Page 1 of 6 1. CHEMICAL PRODUCT AND COMPANY IDENTIFICATION PRODUCT NAME... ABLEBOND 8361J Adhesive SYNONYM NAME(S)... Modified Epoxy Resin Ablestik Laboratories Subsidiary of National

More information

and Benchmark Toxicology Services HEALTH RISK ASSESSMENT OF ATMOSPHERIC EMISSIONS EXPANSION OF WAGERUP REFINERY TO 4.7 MTPA

and Benchmark Toxicology Services HEALTH RISK ASSESSMENT OF ATMOSPHERIC EMISSIONS EXPANSION OF WAGERUP REFINERY TO 4.7 MTPA and Benchmark Toxicology Services HEALTH RISK ASSESSMENT OF ATMOSPHERIC EMISSIONS EXPANSION OF WAGERUP REFINERY TO 4.7 MTPA for Alcoa World Alumina Australia ENVIRON Australia Pty Ltd Level 2, Adelaide

More information

Effects of moisture condition and internal water movement on penetration property of chloride ion in concrete

Effects of moisture condition and internal water movement on penetration property of chloride ion in concrete Effects of moisture condition and internal water movement on penetration property of chloride ion in concrete Kentaro KOIKE 1, Toshinobu YAMAGUCHI 1, Koji TAKEWAKA 1 1 Kagoshima University, Japan * k279773@kadai.jp,

More information

Not NGWA Board-approved DRAFT COPY. Not for circulation. Overview NGWA. Groundwater and PFAS: State of Knowledge and Practice. Section 1.

Not NGWA Board-approved DRAFT COPY. Not for circulation. Overview NGWA. Groundwater and PFAS: State of Knowledge and Practice. Section 1. Overview Section 1 Groundwater and PFAS: State of Knowledge and Practice One of eight sections prepared by National Ground Water Association volunteers. Each section was prepared to stand independently,

More information

: Sikalastic -821 LV Part B

: Sikalastic -821 LV Part B SECTION 1: Identification of the hazardous chemical and of the supplier Product name : Product code : 000000206440 Type of product : liquid Recommended use of the chemical and restrictions on use Product

More information

Date Printed: 03/03/2004 Date Updated: 09/04/2002 Version 1.2. Product Name HEXADECANE, ANHYDROUS, 99+% Product Number

Date Printed: 03/03/2004 Date Updated: 09/04/2002 Version 1.2. Product Name HEXADECANE, ANHYDROUS, 99+% Product Number SIGMA-ALDRICH MATERIAL SAFETY DATA SHEET Date Printed: 03/03/2004 Date Updated: 09/04/2002 Version 1.2 Section 1 - Product and Company Information Product Name HEXADECANE, ANHYDROUS, 99+% Product Number

More information

Development and Use of Wildlife Inhalation Toxicity Reference Values for Ecological Risk Assessment

Development and Use of Wildlife Inhalation Toxicity Reference Values for Ecological Risk Assessment Development and Use of Wildlife Inhalation Toxicity Reference Values for Ecological Risk Assessment Michael Anderson, California Environmental Protection Agency Ned Black, U.S. Environmental Protection

More information

SCIENTIFIC COMMITTEE ON TOXICITY, ECOTOXICITY AND THE ENVIRONMENT (CSTEE) Opinion on the results of the Risk Assessment of:

SCIENTIFIC COMMITTEE ON TOXICITY, ECOTOXICITY AND THE ENVIRONMENT (CSTEE) Opinion on the results of the Risk Assessment of: EUROPEAN COMMISSION DIRECTORATE-GENERAL HEALTH AND CONSUMER PROTECTION Directorate C - Scientific Opinions Unit C2 Management of Scientific Committees; scientific co-operation and networks Scientific Committee

More information