Concawe_fuel use map_v1.0<p>The Concawe use map for fuel use has been developed based on the European Solvents Industry Group (ESIG) Generic Exposure Scenarios (GES). Each use is described with two (2) levels of Risk Management Measures (RMM)/ Operating Conditions (OCs) to allow the selection of appropriate level of RMMs/OCs based on the volatility (vapour pressure) and hazard profile of the assessed substance, as follows:</p><ul><li>Level I - basic level of RMMs/OCs: makes use of the ESIG GES for Low Volatility/Low DNEL , and </li><li>Level II - advanced level of RMMs/OCs: makes use of the ESIG GES for Medium Volatility/Low DNEL, <br/></li></ul><p>where: </p><p><em>Low Vapour Pressure: < 0.5 kPa at STP <br/>Medium Vapour Pressure: 0.5 – 10 kPa at STP <br/>Low DNEL: < 10 ppm for inhalation exposure; < 5 mg/kg/day for dermal exposure</em><br/></p><p>The assessor needs to delete the Exposure Scenarios of the non-applicable level for the given substance, preferably after carrying out the assessment with the uses Level I and II by default. RMMs and OCs can be modified by the assessor.</p><p>Details on the ESIG GES are available on the ESIG website: <a href="http://www.esig.org/regulatory/reach-ges">http://www.esig.org/regulatory/reach-ges</a><br/></p><p>Consumer uses are based on Concawe SCEDs. Details are available on the Concawe website: <a href="https://www.concawe.eu/reach/specific-consumer-exposure-determinants-sceds-documents/">https://www.concawe.eu/reach/specific-consumer-exposure-determinants-sceds-documents/</a></p><p><br/></p>Last revision July 2020ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:47:452017-12-13T15:51:24ACTIVE2.1Fuels, Liquefied gas, Automotive refuellingFilling motor vehicle outdoors with a full tank of fuel every weekDeterminant values refer to Liquefied Petroleum Gas (LPG) as the fuel; an assessment for liquids should be carried out.PC_13Concawe_SCED_13_2_ahttp://www.concawe.orgConcawe_SCED_13_1_a; Concawe_SCED_13_3_aLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTESubstance is a gas. If dermal contact occurs then it will result in cold burns.falseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_NO_CONTACTTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased LPG vehicle tank filled with 80 L LPG and LPG density of 533 g/Lfalse43000.0TRA_CONSUMER_EXPOSURE_TIMEConsistent with reported refuelling time ranging from 0.3-3.5 min, with an average of 1 min.false0.05TRA_CONSUMER_INHALATION_FACTORLPG refuelling is via a contained self-sealing nozzle due to flammability considerations. Hence, leakage on nozzle insertion and withdrawal is very low (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false5.0E-4TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_OUTDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR52 times/year - once/week; consistent with the 90th percentile of 5 times per month (0.17) and average of 3.1 times per month (0.1);
corresponds to "frequent" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:48:282017-12-13T15:51:44ACTIVE2.1Fuels, Liquids, Garden equipment refuellingFilling lawn mower outdoors with a full tank of fuel once per week during spring and summer (6 months)SCED data refers to gasolinePC_13Concawe_SCED_13_4_ahttp://www.concawe.orgLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_YESTRA_CONSUMER_DERMAL_TRANSFER_FACTOREstimated value for gasoline. This value is greater (more conservative) than the <0.001% of material handled that has been measured as being transferred onto the skin when refuelling cars (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org). Rationale for skin contact area: only one hand holds the fuel nozzle when re-fuelling. Total area exposed less than for one hand.false0.001TRA_CONSUMER_BODY_PARTY_DERMALfalseINSIDE_HANDS_IDTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased on tank size of 1 L and substance density of 750 g/Lfalse750.0TRA_CONSUMER_EXPOSURE_TIMEEstimated 2 min: time taken to refuel a smaller size tank should be significantly less than for the auto-refuelling exposure time of 3 min.false0.033TRA_CONSUMER_INHALATION_FACTOREstimated loss of <0.03 product used via spillage or evaporation (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.03TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_INDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR26 times/year - Once/two weeks: refuelling of garden machinery activity occurs mostly during spring and summer; reported frequency for (vehicle) refuelling activity throughout the year was once/week, that corresponds to once/two weeks per year for garden equipment; corresponds to "occasional" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:46:082017-12-13T15:51:53ACTIVE2.1Fuels, Liquid, Home space heaterFilling space heater indoors with fuel every day during heating seasonDeterminant values refer to kerosene as the fuelPC_13Concawe_SCED_13_5_ahttp://www.concawe.orgLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_YESTRA_CONSUMER_DERMAL_TRANSFER_FACTOREstimated value. This value is greater (more conservative) than the <0.001% of material handled that has been measured as being transferred onto the skin when refuelling cars (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org). Rationale for skin contact area: palm of only one hand expected to hold the fuel container when refueling.false0.001TRA_CONSUMER_BODY_PARTY_DERMALfalsePALM_OF_ONE_HAND_IDTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased on 4L and a density of 830 g/L (tank size of a home space heater is about 5L and the heater with a full tank of the fuel can last for 12-15hr.false3320.0TRA_CONSUMER_EXPOSURE_TIMEEstimated 2 min as it should take significantly less time to refuel a smaller size tank than auto-refuelling (3 min).false0.033TRA_CONSUMER_INHALATION_FACTORIt is reasonable to anticipate that only a low amount (c. 5 mL) is likely to be routinely spilled during pouring in a residence and this equates to a comparative evaporative loss of <0.02 based on equivalent gasoline values for scooters (for scooter refuelling, the emission loss is calculated to be ~0.001 for refuelling spillage and 0.002 for vapour displacement emission based on the scooter tank volume of 5 L) (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.02TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_INDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR180 times/year - Daily use during heating season (6 months); corresponds to "frequent" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:49:142017-12-13T15:52:24ACTIVE2.1Fuels, Liquids, Recreational vehicles (quad bikes or similar)Filling tank of recreational vehicle with fuel every week outdoorsDeterminant values refer to gasoline as the fuelPC_13Concawe_SCED_13_7_ahttp://www.concawe.orgLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_YESTRA_CONSUMER_DERMAL_TRANSFER_FACTOREstimated value. This value is much greater (more conservative) than the <0.001% of material handled that has been measured as being transferred onto the skin when refuelling a car with diesel fuel (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org). Rationale for skin contact area: only one hand holds the fuel nozzle when refuelling.false0.01TRA_CONSUMER_BODY_PARTY_DERMALfalsePALM_OF_ONE_HAND_IDTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased on a typical 10 L fill volumefalse7500.0TRA_CONSUMER_EXPOSURE_TIMEEstimated 1 min due to small volume being transferred. Changed from ECETOC TRA default value (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.017TRA_CONSUMER_INHALATION_FACTORAssumed to be equivalent to the value applied for general gasoline transfers (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.01TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_OUTDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR52 times/year - once/week; corresponds to "frequent" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:48:522017-12-13T15:52:16ACTIVE2.1Fuels, Liquefied gas, Home space heaterChanging compressed gas cylinder to indoor space heater every weekDeterminant values refer to Liquefied Petroleum Gas (LPG) as the fuel; an assessment for liquids should be carried out.PC_13Concawe_SCED_13_6_ahttp://www.concawe.orgLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTESubstance is a gas. If dermal contact occurs then it will result in cold burns.falseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_NO_CONTACTTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased on a typical 15 kg domestic gas cylinderfalse15000.0TRA_CONSUMER_EXPOSURE_TIMEEstimated 1 min due to small volume being transferred. Changed from ECETOC TRA default value (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.017TRA_CONSUMER_INHALATION_FACTOROnly low evaporative losses likely but percentage increased as compared to lubricant refueling (further justification in SCED Supporting Explanation document at www.concawe.org).false5.0E-4TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_INDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR52 times/year - once/week; corresponds to "frequent" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:47:282017-12-13T15:51:19ACTIVE2.1Fuels, Liquid, Automotive refuelling (gasoline)Filling motor vehicle outdoors with a full tank of fuel every weekDeterminant values refer to gasoline as the fuelPC_13Concawe_SCED_13_1_ahttp://www.concawe.orgConcawe_SCED_13_2_a; Concawe_SCED_13_3_aLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_YESTRA_CONSUMER_DERMAL_TRANSFER_FACTOREstimated conservative value for gasoline. This value is greater (more conservative) than the 75th percentile of 0.00005 for hand contamination during pouring from a pesticide container (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org). Rationale for skin contact area: only one hand holds the fuel nozzle when refueling.false0.002TRA_CONSUMER_BODY_PARTY_DERMALfalsePALM_OF_ONE_HAND_IDTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased on 50 L fuel dispensed and density of 750 g/L. Value is consistent with reported refuelling amounts: 90th percentile of 53 L and average of 30 Lfalse37500.0TRA_CONSUMER_EXPOSURE_TIMEConsistent with reported refuelling time ranging from 0.3-3.5 min, with an average of 1 minfalse0.05TRA_CONSUMER_INHALATION_FACTORMeasured evaporative losses of 4 – 10.4 g VOC emitted per gallon of gasoline during vehicle refuelling converts to an inhalation transfer factor of 0.001 – 0.004 for automobiles without vapour capture systems. EU laws mandate vapour capture and applying the recovery system default value of 98% efficiency to this data gives an estimated emission of 0.0001-0.0003 weight fraction (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.002TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_OUTDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR52 times/year - once/week; consistent with the 90th percentile of 5 times per month (0.17) and average of 3.1 times per month (0.1);
corresponds to "frequent" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:48:032017-12-13T15:51:35ACTIVE2.1Fuels, Liquid, Automotive refuelling (diesel)Filling motor vehicle outdoors with a full tank of fuel every weekDeterminant values refer to gasoil (diesel) as the fuelPC_13Concawe_SCED_13_3_ahttp://www.concawe.orgConcawe_SCED_13_1_a; Concawe_SCED_13_2_aLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_YESTRA_CONSUMER_DERMAL_TRANSFER_FACTORThis value is greater (more conservative) than the <0.001% of material handled that has been measured as being transferred onto the skin when refuelling cars with diesel (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org). Rationale for skin contact area: only one hand holds the fuel nozzle when refuelling.false0.005TRA_CONSUMER_BODY_PARTY_DERMALfalsePALM_OF_ONE_HAND_IDTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased on 50 L fuel dispensed and density of 880 g/L. Value is consistent with reported refuelling amounts: 90th percentile of 53 L and average of 30 L.false44000.0TRA_CONSUMER_EXPOSURE_TIMEConsistent with reported refuelling time ranging from 0.3-3.5 min, with an average of 1 min.false0.05TRA_CONSUMER_INHALATION_FACTORRefuelling via contained nozzle. Leakage on nozzle insertion and withdrawal is expected to be very low. As diesel fuel has a higher boiling point and let much lower vapour pressure than gasoline, emissions are expected to be much less significant than those for gasoline (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.002TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_OUTDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR52 times/year - once/week; consistent with the 90th percentile of 5 times per month (0.17) and average of 3.1 times per month (0.1);
corresponds to "frequent" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T15:49:472017-12-13T15:52:32ACTIVE2.1Fuels, Liquid, Lamp oilFilling oil lamp indoors with fuel every weekDeterminant values refer to foots oil as the fuelPC_13Concawe_SCED_13_8_ahttp://www.concawe.orgLIQUIDSTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_DERMAL_ROUTE_YESTRA_CONSUMER_DERMAL_TRANSFER_FACTOREstimated conservative value based on a comparison with values available for handling lubricants where <0.001% of product is transferred to the skin (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org). Rationale for skin contact area: only inside of one hand expected to hold fuel container when refuelling.false0.005TRA_CONSUMER_BODY_PARTY_DERMALfalsePALM_OF_ONE_HAND_IDTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTEfalseTRA_CONSUMER_EXPOSURE_VIA_INHALATION_ROUTE_YESTRA_CONSUMER_AMOUNT_OF_PRODUCT_USED_PER_APPLICATIONBased on an upper end lamp reservoir volume of 0.3 L and density of 850 g/L.false255.0TRA_CONSUMER_EXPOSURE_TIMEEstimated 1 min due to small volume being transferred. Changed from ECETOC TRA default value (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.017TRA_CONSUMER_INHALATION_FACTOROnly low evaporative losses likely but percentage increased as compared to lubricant refueling (further justification in Concawe Handbook “SCEDs and Supporting Explanation” at www.concawe.org).false0.05TRA_CONSUMER_SPRAYfalseSPRAY-NOTRA_CONSUMER_PLACE_OF_USEfalseTRA_CONSUMER_PLACE_OF_USE_INDOORTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTEThe SCED already addresses inhalation and dermal exposure routes assuming 100% systemic absorption. Oral exposure (e.g. from hand-to-mouth behaviour) is only likely to arise from incidental consumer actions. The potential contribution of oral exposure to systemic dose is therefore expected to be minimal when seen in the context of the other exposure routes.falseTRA_CONSUMER_EXPOSURE_VIA_ORAL_ROUTE_NOTRA_CONSUMER_ADULT_CHILD_ASSUMEDfalseTRA_CONSUMER_ADULT_ASSUMEDC_PERCENTAGE_OF_SUBSTANCE_IN_MIXTUREfalse100.0TRA_CONSUMER_FREQUENCY_YEAR52 times/year - once/week; corresponds to "frequent" Use Freq band in ECETOC TRA v3.1falseTRA_CONSUMER_FREQUENCY_YEAR_FREQUENTTRA_CONSUMER_FREQUENCY_OF_USEUnchanged from ECETOC TRA default valuefalse1.0December 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T16:21:102017-12-13T16:24:15ACTIVE1ESVOC 7.12aUse as a Fuel (industrial): solvent-borne Covers the use as a fuel (or fuel additive) and includes activities associated with its transfer, use, equipment maintenance and handling of waste.
Substance Domain: Applicable to petroleum substances (e.g., aliphatic and aromatic hydrocarbons) and petrochemicals (e.g., ketones, alcohols, acetates, glycols, glycol ethers, and glycol ether acetates).
Size of installation: substance use rate assumed to be 5000000 kg/d
Processing conditions: dry processing
Industrial use of solvent-borne fuels encompasses a wide range of activities such as material transfer, use, equipment maintenance, etc. Substance losses are reduced through use of general and site-specific risk management measures to maintain workplace concentrations of airborne VOCs and particulates below respective OELs; and through use of closed or covered equipment/processes to minimize evaporative losses of VOCs. Substance properties and uses result in limited to no discharge to wastewater or to soil from the industrial site.http://www.esig.orgfalseINDUSTRIAL_USEINDUSTRIALPC_13VP < 1000;Vapor pressure < 1000ESVOC 7.12a.b.v1ERC_71000.00.001Estimates based on losses to water for kerosene and diesel at large sites that ranged from <0.001% to 0.056% (CONCAWE 2010 personal communication).0.55 % represents the ERC7 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 Environmental Release Categories). For moderate to low volatility substances a 10-fold decrease in release is assumed. This order of magnitude decrease provides a conservative estimate based on calculated air emission factors for mid-distillate fuels that range from 0.05 % to 0.2 % (CONCAWE 2010 personal communication).0.0Release prohibited.0.0This will be addressed at a later stageVP > 1000;Vapor pressure > 1000ESVOC 7.12a.a.v1ERC_71000.00.001Estimates based on losses to water for kerosene and diesel at large sites that ranged from <0.001% to 0.05% (CONCAWE 2010 personal communication).5.05 % represents the ERC7 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 Environmental Release Categories). For moderate to low volatility substances a 10-fold decrease in release is assumed. This order of magnitude decrease provides a conservative estimate based on calculated air emission factors for mid-distillate fuels that range from 0.05 % to 0.2 % (CONCAWE 2010 personal communication).0.0Release prohibited.0.0This will be addressed at a later stagec6651a1e-c3cf-4b07-9a9c-e7fcf96b5ae8falsetrue89b15027-cf4b-45c8-82a1-67a53ed08632RELEASE_MODULE_DAILY_USE_AT_SITEThe substance maximum use rate (MSPERC) is assumed to be 5000 tonnes/d. This is the maximum site tonnage, based on sector knowledge (Amount of substance that is delivered for fuel use at a large airport (CONCAWE personal communication)).
300 days/year are assumed (default value for an ‘Industrial end use’ with tonnage > 5000 tonnes/year (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Section R.16.3.2.1).falsetrue5000.0EUSES_DISCHARGE_RATE_OF_STPfalsetrue2000.0fb016d84-9a6d-4b66-90a4-8e9a549aa669falsetrue4da935f2-c081-41c9-a3d2-f3a432693232EUSES_BIOLOGICAL_STPfalsetrueEUSES_BIOLOGICAL_STP-STANDARDWATERAPPLICATION_OF_THE_STPfalsefalseAPPLICATION_OF_THE_STP-YESWASTE_TREATMENT_CONSIDERATIONfalsefalse45299f90-0723-4cff-898f-805172d92e06falsetrued9b3d82b-57e3-48a9-93da-7b318d5e03ffDecember 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T16:18:452017-12-13T16:24:52ACTIVE1ESVOC 9.12bUse as a Fuel (wide dispersive use): solvent-borne Covers the use as a fuel (or fuel additive) and includes activities associated with its transfer, use, equipment maintenance and handling of waste and consumer uses in liquid fuels.
Substance Domain: Applicable to petroleum substances (e.g., aliphatic and aromatic hydrocarbons) and petrochemicals (e.g., ketones, alcohols, acetates, glycols, glycol ethers, and glycol ether acetates).
Size of installation: Applicable to professional and consumer use with an assumed use rate of 0.05% of regional tonnage
Processing conditions: Some disposal via wastewater assumedUse as a Fuel (wide dispersive use): solvent-borne http://www.esig.org/falsePROFESSIONAL_WORKER_USEINDUSTRIALPC_135.5E-6VP 500 - 5000 Pa;Vapor pressure 500 - 5000 PaESVOC 9.12b.b.v1ERC_9b500.05000.00.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.1Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.0This will be addressed at a later stageVP < 500 Pa;Vapor pressure < 500 PaESVOC 9.12b.c.v1ERC_9b500.00.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.01Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.0This will be addressed at a later stageVP > 5000 Pa;Vapor pressure > 5000 PaESVOC 9.12b.a.v1ERC_9b5000.00.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).1.0Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.0 This will be addressed at a later stageENVIRONMENT_PLACE_OF_USEfalsefalseWATER_CONTACT_DURING_USEfalsefalseEUSES_BIOLOGICAL_STPfalsetrueEUSES_BIOLOGICAL_STP-STANDARDWATERWASTE_TREATMENT_CONSIDERATIONfalsefalseDecember 2017ESIGIUC5-ead92b6f-f38f-4025-8388-c8dab8f685422012-10-10T10:23:252013-02-05T17:44:47ACTIVEESVOC 2.2.v1Formulation & (re)packing of substances and mixtures (industrial): solvent-borne Formulation, packing and re-packing of the substance and its mixtures in batch or continuous operations, including storage, materials transfers, mixing, tabletting, compression, pelletisation, extrusion, large and small scale packing, sampling, maintenance and associated laboratory activities.
Substance Domain: Applicable to petroleum substances (e.g., aliphatic and aromatic hydrocarbons) and petrochemicals (e.g., ketones, alcohols, acetates, glycols, glycol ethers, and glycol ether acetates).
Size of installation: Use rate assumed to be 100 t/d
Processing conditions: Dry process
Formulation of solvent-borne substances encompasses a wide range of activities such as transfers, mixing, tabletting, compression, pelletilisation and sampling. Substance losses are reduced through use of general and site-specific risk management measures to maintain workplace concentrations of airborne VOCs and particulates below respective OELs; and through use of closed or covered equipment/processes to minimize evaporative losses of VOCs.
Substance losses to waste water are generally restricted to equipment cleaning as processes operate without contact with water Such uses and substance properties result in limited to no discharge to wastewater or to soil from the industrial site.falseFORMULATIONINDUSTRIALVP 10 - 100 Pa and WS 1 - 10 mg/L;Vapour pressure 10 - 100 Pa and water solubility 1 - 10 mg/LESVOC 2.2.l.v1ERC_210.0100.01.010.00.002Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage4dea5442-88ad-4fb9-b1f6-05806b5b1ff0VP 10 - 100 Pa and WS 10 - 100 mg/L;Vapour pressure 10 - 100 Pa and water solubility 10 - 100 mg/LESVOC 2.2.m.v1ERC_210.0100.010.0100.00.02Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagee257bc21-d333-4e4b-872b-867a4908043aVP 10 - 100 Pa and WS 100 - 1000 mg/L;Vapour pressure 10 - 100 Pa and water solubility 100 - 1000 mg/LESVOC 2.2.n.v1ERC_210.0100.0100.01000.00.2Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagede7a56d2-408e-4896-9867-bd33f27b0de8VP 10 - 100 Pa and WS < 1 mg/L;Vapour pressure 10 - 100 Pa and water solubility < 1 mg/LESVOC 2.2.k.v1ERC_210.0100.01.05.0E-4Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage62e1536a-5c2c-41e8-90ed-c2d0c3331215VP 10 - 100 Pa and WS > 1000 mg/L;Vapour pressure 10 - 100 Pa and water solubility > 1000 mg/LESVOC 2.2.o.v1ERC_210.0100.01000.00.5Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage6dca065c-cd96-4834-b758-5f1bbc9079d0VP 100 - 1000 Pa and WS 1 - 10 mg/L;Vapour pressure 100 - 1000 Pa and water solubility 1 - 10 mg/LESVOC 2.2.g.v1ERC_2100.01000.01.010.00.002Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.1.0Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stageeac8048f-a5ab-45aa-bc10-0876c6562352VP 100 - 1000 Pa and WS 10 - 100 mg/L;Vapour pressure 100 - 1000 Pa and water solubility 10 - 100 mg/LESVOC 2.2.h.v1ERC_2100.01000.010.0100.00.02Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.1.0Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage40f770a1-cf7d-4d53-947d-806b25911647VP 100 - 1000 Pa and WS 100 - 1000 mg/L;Vapour pressure 100 - 1000 Pa and water solubility 100 - 1000 mg/LESVOC 2.2.i.v1ERC_2100.01000.0100.01000.00.2Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.1.0Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagef3189641-5bc0-4fbb-8ab7-37becbf76bccVP 100 - 1000 Pa and WS < 1 mg/L;Vapour pressure 100 - 1000 Pa and water solubility < 1 mg/LESVOC 2.2.f.v1ERC_2100.01000.01.05.0E-4Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.1.0Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stageec56fef9-60f4-4469-8525-5a00a6515ed0VP 100 - 1000 Pa and WS > 1000 mg/L;Vapour pressure 100 - 1000 Pa and water solubility > 1000 mg/LESVOC 2.2.j.v1ERC_2100.01000.01000.00.5Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.1.0Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage8a4297c9-21fb-48cc-907c-28b977b59956VP < 10 Pa and WS 1 - 10 mg/L;Vapour pressure < 10 Pa and water solubility 1 - 10 mg/LESVOC 2.2.q.v1ERC_210.01.010.00.002Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.25Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage2d3429f3-f61e-4032-ad5e-1b087c5b6e32VP < 10 Pa and WS 10 - 100 mg/L;Vapour pressure < 10 Pa and water solubility 10 - 100 mg/LESVOC 2.2.r.v1ERC_210.010.0100.00.02Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.25Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagec4612ae5-d7d7-4970-9451-27a8b88fab04VP < 10 Pa and WS 100 - 1000 mg/L;Vapour pressure < 10 Pa and water solubility 100 - 1000 mg/LESVOC 2.2.s.v1ERC_210.0100.01000.00.2Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.25Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagec1c7e156-4e23-4b54-9481-0bcbe9f7a982VP < 10 Pa and WS < 1 mg/L;Vapour pressure < 10 Pa and water solubility < 1 mg/LESVOC 2.2.p.v1ERC_210.01.05.0E-4Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.25Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagee18aa61c-5965-4d9e-9f89-a3d66fe5ec38VP < 10 Pa and WS > 1000 mg/L;Vapour pressure < 10 Pa and water solubility > 1000 mg/LESVOC 2.2.t.v1ERC_210.01000.00.5Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.0.25Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage64108fae-942a-4ed5-8fff-8e9de7bab2b2VP > 1000 Pa and WS 1 - 10 mg/L;Vapour pressure > 1000 Pa and water solubility 1 - 10 mg/LESVOC 2.2.b.v1ERC_21000.01.010.00.002Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.2.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagefddc13e7-c156-448b-9622-46fdae4a2b18VP > 1000 Pa and WS 10 - 100 mg/L;Vapour pressure > 1000 Pa and water solubility 10 - 100 mg/LESVOC 2.2.c.v1ERC_21000.010.0100.00.02Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.2.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage809e2e98-2640-49f3-a6ea-20d8a6632471VP > 1000 Pa and WS 100 - 1000 mg/L;Vapour pressure > 1000 Pa and water solubility 100 - 1000 mg/LESVOC 2.2.d.v1ERC_21000.0100.01000.00.2Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.2.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagebf6d84e7-5ef9-4a4f-8b26-dfb58f00481dVP > 1000 Pa and WS < 1 mg/L;Vapour pressure > 1000 Pa and water solubility < 1 mg/LESVOC 2.2.a.v1ERC_21000.01.05.0E-4Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.2.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stagea8a63e88-4ca8-4261-8121-874578b27a95VP > 1000 Pa and WS > 1000 mg/L;Vapour pressure > 1000 Pa and water solubility > 1000 mg/LESVOC 2.2.e.v1ERC_21000.01000.00.5Emission factors to wastewater are conservatively calculated based on wastewater volume generated from cleaning operations and substance aqueous solubility Assumption of 5 m3 of wastewater generated per 1 tonne of substance used is relatively conservative (Data from OECD Lubricants & Lubricant Additives ESD (2004) suggest a reasonable worst case estimate of wastewater discharge for a blending plant (formulation) is 0.1 m3/tonne lubricant (-> OECD Series on Emission Scenario Documents, Number 10. November 2004. Emission Scenario Document on Lubricants and Lubricant Additives); thus, assumed value of 5 m3/tonne represents a conservative estimate.).
Example: 1 mg/L x 5 m3/tonne use x 1000 L/m3 x 1tonne/109mg = 0.000005 tonnes/tonne used. For WS range (e.g., 1-10 mg/L), the geometric mean (i.e., 3.2 mg/L) is used to calculate the fraction released.
OECD Coatings ESD4 reports no releases of volatile substances to water. The values used here are consistent with those reported for dust.2.5Estimates on the basis of substance vapor pressure taken from EUTGD (2003) Appendix 1 (European Commission Technical Guidance Document on Risk Assessment (EUTGD) Part 2 – 2nd Edition (2003). Appendix 1 Polymers Industry, Table 2.1 (MC = 3)).
These values are consistent with the range of emissions reported in OECD Coatings ESD (OECD Series on Emission Scenario Documents, Number 22. July 2009. Emission Scenario Documents on Coating Industry (Paint, Laquers and Varishes)) and consistent with EU Solvent Emissions Directive after typical RMMs as further documented in Coatings SPERC Factsheet.0.01ERC 2 default (ECHA Guidance on information requirements and chemical safety assessment, Chapter R.16: Environmental Exposure Estimation, Appendix R.16-1 – Environmental Release Categories)0.0This will be addressed at a later stage2a827ceb-1395-435b-a1ef-f91387549960c6651a1e-c3cf-4b07-9a9c-e7fcf96b5ae8false89b15027-cf4b-45c8-82a1-67a53ed08632RELEASE_MODULE_DAILY_USE_AT_SITEThe substance use rate is the maximum site tonnage for a typical operation (Msperc). It is based on sector knowledge (a use rate of 100 tonnes/day over 300 emission days is equivalent to 30000 tonnes annually; which is consistent with the maximum capacity for a major lubricant producing plant (OECD lubricants and lubricant additives, ESD 2004).
As a default for the formulation stage, 300 emission days were taken into account (tonnage > 2000 tonnes/year)false100.0EUSES_DISCHARGE_RATE_OF_STPfalse2000.01a7e2af0-114b-4f9f-9f57-c24be15a2176false36fbeed0-2d8a-4b5e-8f70-c92b2eeaf4e3fb016d84-9a6d-4b66-90a4-8e9a549aa669false0461cc3e-ee26-4357-9d01-8182600d2061EUSES_BIOLOGICAL_STPfalseEUSES_BIOLOGICAL_STP-STANDARDWATERAPPLICATION_OF_THE_STPfalseAPPLICATION_OF_THE_STP-YESWASTE_TREATMENT_CONSIDERATIONfalse45299f90-0723-4cff-898f-805172d92e06falsed9b3d82b-57e3-48a9-93da-7b318d5e03ffcce79222-a756-4dc2-96ec-662dcc4912b6ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-13T16:20:332017-12-13T16:24:27ACTIVE1ESVOC 9.12cUse as a Fuel (wide dispersive use): solvent-borne Covers the use as a fuel (or fuel additive) and includes activities associated with its transfer, use, equipment maintenance and handling of waste and consumer uses in liquid fuels.
Substance Domain: Applicable to petroleum substances (e.g., aliphatic and aromatic hydrocarbons) and petrochemicals (e.g., ketones, alcohols, acetates, glycols, glycol ethers, and glycol ether acetates).
Size of installation: Applicable to professional and consumer use with an assumed use rate of 0.05% of regional tonnage
Processing conditions: Some disposal via wastewater assumedUse as a Fuel (wide dispersive use): solvent-borne http://www.esig.org/falseCONSUMER_USEINDUSTRIALPC_135.5E-6VP 500 - 5000 Pa;Vapor pressure 500 - 5000 PaESVOC 9.12c.b.v1ERC_9b500.05000.00.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.1Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.0This will be addressed at a later stageVP < 500 Pa;Vapor pressure < 500 PaESVOC 9.12c.c.v1ERC_9b500.00.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.01Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.0This will be addressed at a later stageVP > 5000 Pa;Vapor pressure > 5000 PaESVOC 9.12c.a.v1ERC_9b5000.00.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).1.0Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.001Emission factors based on calculated losses for petrol, kerosene and diesel fuels during professional and consumer use (CONCAWE personal communication).0.0 This will be addressed at a later stagec6651a1e-c3cf-4b07-9a9c-e7fcf96b5ae8falsetruefedf46dc-d0e8-4e82-8d8b-0364da8ac5e4EUSES_BIOLOGICAL_STPfalsetrueEUSES_BIOLOGICAL_STP-STANDARDWATERWASTE_TREATMENT_CONSIDERATIONfalsefalseDecember 2017ConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32018-10-17T15:11:132018-10-17T15:11:13OBSOLETEc04346be-7cea-4611-ab31-3f8cff573b6cWORKERSfalseDERMALINHALATIONW_3...trueHandle in a fume cupboard or under extract ventilation. E83.ESCom-11133171436trueESIGIUC5-ead92b6f-f38f-4025-8388-c8dab8f685422013-01-21T12:12:142015-02-05T10:34:06ACTIVEENVIRONMENTfalseAIRE_W_3Typical measures to maintain workplace concentrations or airborne VOCs and particulates below respective OELStruee.g. thermal wet scrubber - gas removal and/or air filtration - particle removal and/or thermal oxidation and/or vapour recovery - adsorptionTypical measures to maintain workplace concentrations or airborne VOCs and particulates below respective OELStrueConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-11T12:53:212017-12-11T12:53:21ACTIVEWORKERSWear suitable coveralls to prevent exposure to skin [PPE27]falseDERMALW_4ESCom-11133171468...trueWear suitable coveralls to prevent exposure to skin [PPE27]ESCom-11133171468trueEuropean Solvent Industry Group - ESIGd80050a1-d06d-4e39-bdfd-ca1b9a7c30922017-04-06T10:26:512017-04-06T10:28:14ACTIVEWORKERSAssumes a good basic standard of occupational hygiene is implemented [G1].falseDERMALINHALATIONW_5ESCom-11133171303...trueAssumes a good basic standard of occupational hygiene is implemented.ESCom-11133171303trueESIGIUC5-ead92b6f-f38f-4025-8388-c8dab8f685422012-09-05T08:43:132015-02-05T11:11:06ACTIVEENVIRONMENTProcess efficiencyfalseWATERE_W_3E_C_4Process optimized for highly efficient use of raw materials (very minimal environmental release)trueProcess optimized for highly efficient use of raw materials (very minimal environmental release).trueProcess optimized for efficient use of raw materialsfalseProcess optimized for efficient use of raw materials.trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTEUSES DeterminanttrueWATERE_W_4EUSES 2.1.2YestruefalseNofalseESCom-11133170644trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSTRA Consumer condition of usetrueDERMALINHALATIONORALC_1ConsExpo100.00.0100.0<=ESCom-9269144102ESCom-11133171519trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERStrueDERMALINHALATIONC_1GasfalsefalseLiquidfalsefalseLiquid for spraying (spraying can)falsefalseSolid (unspecified form)falsefalseSolid (very dusty form)falsefalseSolid (medium dusty form)falsefalseSolid (non or low dusty form)falsefalseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueDERMALINHALATIONW_2TRA Worker 3.08.00.024.0<=ESCom-15193135624ESCom-11133171521trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTtrueAIRSOILWATERE_W_6E_C_4IndoorfalseESCom-9313213237trueOutdoorfalseESCom-9313213238trueIndoor/OutdoorfalseESCom-10133220202trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTEUSES DeterminanttrueWATERE_W_4E_C_4EUSES 2.1.2StandardtrueESCom-11133170613trueWATER0.0100.0Site specificfalseESCom-11133171638trueWATER0.0100.0NonefalsefalseWATER0.00.00.0ChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTEUSES DeterminanttrueWATERE_W_4EUSES 2.1.22000.00.0>=ESCom-11133170818ESCom-10133222104trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueDERMALINHALATIONW_5TRA Worker 3.040.00.0<=ESCom-9269144108ESCom-12355002161trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTReleaseModule's DeterminanttrueAIRSOILWATERE_W_2EUSES 2.1.20.0<=ESCom-11133170824ESCom-10076084404trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTReleaseModule's DeterminanttrueAIRSOILWATERE_W_2EUSES 2.1.20.0<=ESCom-15193135620ESCom-10076084403trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTReleaseModule's DeterminanttrueAIRSOILWATERE_W_2E_C_2EUSES 2.1.20.0<=ESCom-15193135620falseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueDERMALW_4TRA Worker 3.0NotruefalseDERMAL0.00.00.0Yes (Chemically resistant gloves conforming to EN374) and (other) appropriate dermal protectionfalseESCom-10133224896ESCom-17297180800ESCom-12355002165trueDERMAL80.080.080.0Yes (Chemically resistant gloves conforming to EN374 with basic employee training) and (other) appropriate dermal protectionfalseESCom-11133171457ESCom-17297180800ESCom-12355002165trueDERMAL90.090.090.0Yes (Chemically resistant gloves conforming to EN374 with specific activity training) and (other) appropriate dermal protectionfalseESCom-11133171458ESCom-17297180800ESCom-12355002165trueDERMAL95.095.095.0ChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueINHALATIONW_3TRA Worker 3.0Basic general ventilation (1-3 air changes per hour)trueESCom-12355002163trueINHALATION0.00.00.0Good general ventilation (3-5 air changes per hour) falseESCom-11133171363trueINHALATION30.030.030.0Enhanced general ventilation (5-10 air changes per hour)falseESCom-12355002164trueINHALATION70.070.070.0ChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueDERMALINHALATIONW_3TRA Worker 3.0NotruefalseINHALATION0.00.00.0DERMAL0.00.00.0YesfalseESCom-14141091100ESCom-15193135690trueINHALATIONDERMALYes (TRA effectiveness)falseESCom-14141091100ESCom-15193135690trueINHALATIONDERMALChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueDERMALINHALATIONW_3TRA Worker 3.0AdvancedfalseESCom-17297180701trueBasicfalsefalseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueINHALATIONW_5TRA Worker 3.0IndoortrueESCom-9313213237trueOutdoorfalseESCom-9313213238trueIndoor and outdoorfalsefalseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueINHALATIONW_4TRA Worker 3.0NotruefalseINHALATION0.00.00.0Yes (Respirator with APF of 10)falseESCom-16012153001ESCom-15193135690ESCom-12355002165trueINHALATION90.090.090.0Yes (Respirator with APF of 20)falseESCom-16012153001ESCom-15193135690ESCom-12355002165trueINHALATION95.095.095.0ChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERStrueDERMALORALC_3TRA Consumer 3.1;ConsExpoAdultfalsefalseChildfalsefalseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSTRA Consumer condition of usetrueINHALATIONC_2TRA Consumer 3.0;TRA Consumer 3.1;ConsExpo0.0<=ESCom-11133170819ESCom-11133171520trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSsurface of the skin exposed to the contact with the substance and identified uniquely by a selected body part.trueDERMALC_4TRA Consumer 3.0;TRA Consumer 3.1FingertipsfalseESCom-12355002180trueTwo fingertipsfalseAssumes that potential dermal contact is limited to two fingertipstruePalm of one handfalseAssumes that potential dermal contact is limited to palm of one handtrueInside hands / one hand / palm of handsfalseESCom-12355002181trueHandsfalseESCom-12355002182trueHands and forearmsfalseESCom-12355002183trueUpper part of the bodyfalseESCom-12355002184trueLower part of the bodyfalseESCom-12355002185trueWhole body except feet, hands and headfalseESCom-12355002186trueWhole bodyfalsefalseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSFraction of substance transferred (>0 to 1) from the product/article contact layer (layer assumed to be in interaction with the skin) to the skintrueDERMALC_4TRA Consumer 3.0;TRA Consumer 3.11.00.01.0=falseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSAssumed duration of exposure per use event.trueINHALATIONC_2TRA Consumer 3.0;TRA Consumer 3.10.024.0=ESCom-15193135758ESCom-11133170461trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERStrueDERMALC_1TRA Consumer 3.1YestruefalseNo dermal contactfalseAssumes no dermal contacttrueDermal exposure assumed to be negligiblefalseDermal exposure assumed to be negligibletrueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERStrueINHALATIONC_1TRA Consumer 3.1YestruefalseInhalation exposure is considered to be not relevant falseESCom-12355002171trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERStrueORALC_1TRA Consumer 3.1YestruefalseOral exposure is considered to be not relevant falseESCom-12355002172trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSNumber of use events per day.trueDERMALINHALATIONORALC_2TRA Consumer 3.0;TRA Consumer 3.1;ConsExpo1.01.0=ESCom-12355002188ESCom-11133171521trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERStrueDERMALINHALATIONORALC_2TRA Consumer 3.1;ConsExpoFrequenttruefalseInfrequentfalseCovers infrequent uses, up to 2 weeks per yeartrueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSRepresents the fraction of product that is released to air during a consumer use: a factor of 0.05 would be the ITF in a case where 5% of a substance is released to air during a consumer use.trueINHALATIONC_4TRA Consumer 3.11.00.01.0=falseChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERStrueINHALATIONC_3TRA Consumer 3.1IndoortruefalseOutdoorfalseESCom-9313213238trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVECONSUMERSConditions of use that implies the substance to be entirely released to air during the application.trueINHALATIONC_1TRA Consumer 3.0;TRA Consumer 3.1YesfalsefalseNotrueESCom-10133224609trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEENVIRONMENTSpecific conditions during the waste life stage of the substance potentially going beyond the local or national legal requirements for waste treatment (disposal or recovery) operations. The determinant values either provide i) a generic justification why no particular considerations regarding environmental risks from the waste life stage are needed or ii) indicate particular conditions to be met during waste treatment. For both assessment cases the single registrant can edit justification/conditions if the generic determinant values do not cover his case.trueWATERE_W_5E_C_3EUSES 2.1.2No (no waste)falseNo waste generated.ESCom-11133170674trueNo (low risk)falseERC based assessment demonstrating control of risk with default conditions. Low risk assumed for waste life stage. Waste disposal according to national/local legislation is sufficient.ESCom-11133171479trueNo (low amount)falseParticular risks from waste treatment unlikely due to small fraction of used substance entering into the waste stage. Waste disposal according to national/local legislation is sufficient.ESCom-11133171479trueNo (low concentration)falseParticular risks from waste treatment unlikely due low concentration of substance in waste stream. Waste disposal according to national/local legislation is sufficient.ESCom-11133171479trueNo (other reason)falseWaste disposal according to national/local legislation is sufficient. "Explanation for the CSR" to be reported by each registrant:ESCom-11133171479trueDedicated recollection infrastructure requiredfalseESCom-12355002107trueBiological treatment not appropriatefalseESCom-12355002101trueIncineration not appropriatefalseESCom-12355002100truePrevent formation of hazardous break down products during thermal waste treatment destruction.falsePrevent formation of hazardous break down products during thermal waste treatment.trueClosed system required to minimise release to the environment.falseClosed system required to minimise release to the environment during waste treatment.trueOtherfalse"Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment:trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5ACTIVEENVIRONMENTtrueWATERE_W_6E_C_4YesfalsefalseNofalseESCom-16354140700trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueDERMALINHALATIONW_1100.00.0100.0<=ESCom-9269144102ESCom-11133171519trueChesarIUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b52015-03-16T16:40:11ACTIVEWORKERSTRA Worker condition of usetrueDERMALINHALATIONW_1GasfalsefalseLiquefied gasfalsefalseLiquidfalsefalseSolid (unspecified form)falsefalseSolid (very dusty form)falsefalseSolid (medium dusty form)falseESCom-11133171332trueSolid (non or low dusty form)falseESCom-11133171331trueConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32018-10-17T14:31:142018-10-17T14:31:14ACTIVEWORKERSfalseDERMALINHALATIONW_3...trueProvide extract ventilation to points where emissions occur. E54.ESCom-11133171412trueESIGIUC5-ead92b6f-f38f-4025-8388-c8dab8f685422012-09-05T08:33:332013-04-08T14:08:17OBSOLETEENVIRONMENTIndoor or outdoor use of the productfalseAIRSOILWATERE_W_3E_C_4Indoor usetruetrueCovers indoor and outdoor usefalsetrueConcaweIUC5-4c260f86-4ac7-4ebf-b012-44b4743017f32017-12-11T12:56:512017-12-11T13:03:41ACTIVEWORKERSUse drum pumps [E53]falseDERMALINHALATIONW_3ESCom-10133223503ESCom-15193135762ESCom-16014091800RMMtrueUse drum pumps [E53]ESCom-11133171411trueINHALATION90.090.095.0Based on results from Fraunhofer experimental study report Verifying the Effectiveness of Solvent RMMs 15/6/2016. This supports ESIG standard phrase E53.DERMAL0.00.090.0Expect dermal exposure is substantially reduced when drum pumps are used. Specific exposure reduction is per assessor professional judgment.European Solvent Industry Group - ESIGd80050a1-d06d-4e39-bdfd-ca1b9a7c30922017-04-06T13:31:252017-04-06T13:33:30ACTIVEWORKERSNo other specific measures identified [E120]falseDERMALINHALATIONW_5...trueNo other specific measures identified [E120]ESCom-11133171454trueEuropean Solvent Industry Group - ESIGd80050a1-d06d-4e39-bdfd-ca1b9a7c30922017-01-19T13:10:202017-01-19T13:10:47OBSOLETEd7837b51-0ff3-4468-a1f1-f26dd735d9f4WORKERSDrain down and flush system prior to equipment break-in or maintenance.falseDERMALINHALATIONW_3ESCom-10133223503RMMtrueDrain down and flush system prior to equipment break-in or maintenance.ESCom-11133171413trueINHALATION90.080.095.0Based on results from Fraunhofer experimental study report Verifying the Effectiveness of Solvent RMMs 15/6/2016. This supports ESIG standard phrase E55.DERMAL0.00.095.0Expect dermal exposure is substantially reduced when lines and equipment are properly drained and flushed according to Standard Operating Procedures (SOP). Specific exposure reduction is per assessor professional judgment.European Solvent Industry Group - ESIGd80050a1-d06d-4e39-bdfd-ca1b9a7c30922017-03-02T12:22:472017-03-02T12:22:47ACTIVEWORKERSStore substance within a closed system [E84].falseDERMALEYEINHALATIONW_3ESCom-10133223503ESCom-16014091800ESCom-151931357620.00.090.0ESCom-11133171437Store substance within a closed system [E84].ESCom-11133171437trueEuropean Solvent Industry Group - ESIGd80050a1-d06d-4e39-bdfd-ca1b9a7c30922017-02-06T12:24:592017-02-06T12:25:36ACTIVEWORKERSEnsure material transfers are under containment or extract ventilation [E66]falseDERMALINHALATIONW_3ESCom-10133223503ESCom-16014091800ESCom-15193135762RMMtrueEnsure material transfers are under containment or extract ventilation.ESCom-11133171422trueINHALATION90.080.095.0Based on results from Fraunhofer experimental study report Verifying the Effectiveness of Solvent RMMs 15/6/2016. This supports ESIG standard phrase Ensure material transfers are under containment or extract ventilation. E66DERMAL0.00.095.0ESIGIUC5-ead92b6f-f38f-4025-8388-c8dab8f685422013-01-21T12:04:402015-02-05T10:30:31ACTIVEENVIRONMENTfalseWATERE_W_3E_C_4No release to wastewater from process as such, wastewater emissions limited to release generated from final equipment cleaning step using watertrueNo release to wastewater from process as such, wastewater emissions limited to release generated from final equipment cleaning step using watertrueNo release to wastewater form process as suchfalseNo release to wastewater from process as suchtrueMixing or blending in batch processesfalsefalsefalseDaily amount per sitetruetruetrueAnnual amount per sitetruetruetrueStoragefalsefalsefalseIndoor or outdoor usefalsefalsefalseAssumed domestic sewage treatment plant flowtruetruetrueECETOC TRA worker v3falsefalsefalsePhysical form of productfalsefalsefalseCovers the use as a fuel (or fuel additive) and includes activities associated with its transfer, use, equipment maintenance and handling of waste.falsefalsefalseDrum and small package fillingfalsefalsefalseBulk transfersfalsefalsefalseEquipment cleaning and maintenancefalsefalsefalseNo sprayingfalsefalsefalseDedicated facilityfalsefalsefalseNon-dedicated facilityfalsefalsefalseClosed systemsfalsefalsefalseProduct samplingfalsefalsefalseWear suitable gloves tested to EN374.falsefalsefalseCovers use at ambient temperatures.falsefalsefalseLiquid: lamp oilfalsefalsefalseRefuellingfalsefalsefalseFuelsfalsefalsefalseUse of fuelsfalsefalsefalseExposure durationtruetruetrueCovers use in a one car garage (>34 m3) under typical ventilation.falsefalsefalseMunicipal sewage treatment plant is assumed.falsefalsefalseNo application of sewage sludge to soilfalsefalsefalseNo waste from processfalsefalsefalseDermal exposure is considered to be not relevant.falsefalsefalsem3/dayfalsefalsefalseg/eventfalsefalsefalsetonnes/yearfalsefalsefalseUse in fuelfalsefalsefalseGeneral exposuresfalsefalsefalseDrum/batch transfersfalsefalsefalseTransfer from/pouring from containersfalsefalsefalseLaboratory activitiesfalsefalsefalseAssumes a good basic standard of occupational hygiene is implementedfalsefalsefalseSolid, low dustinessfalsefalsefalseSolid, medium dustinessfalsefalsefalseProvide a good standard of general ventilation (not less than 3 to 5 air changes per hour).falsefalsefalseUse drum pumps.falsefalsefalseProvide extract ventilation to points where emissions occur.falsefalsefalseDrain down and flush system prior to equipment break-in or maintenance.falsefalsefalseEnsure material transfers are under containment or extract ventilation.falsefalsefalseEnsure operation is undertaken outdoors.falsefalsefalseHandle in a fume cupboard or under extract ventilation.falsefalsefalseStore substance within a closed system.falsefalsefalseNo other specific measures identified.falsefalsefalseWear chemically resistant gloves (tested to EN374) in combination with ‘basic’ employee training.falsefalsefalseWear chemically resistant gloves (tested to EN374) in combination with specific activity training.falsefalsefalseWear suitable coveralls to prevent exposure to the skin.falsefalsefalseDispose of waste product or used containers according to local regulations.falsefalsefalseCovers concentrations up tofalsetruetrueFor each use event, covers use amounts up tofalsetruetrueCovers use up tofalsetruetrueProvide onsite wastewater treatment.falsefalsefalseLiquefied gasfalsefalsefalseIncineration is not appropriate for waste.falsefalsefalseBiological treatment is not appropriate for waste.falsefalsefalseDedicated recollection infrastructure required for wastefalsefalsefalseAssumes process temperature up tofalsetruetrueProvide a basic standard of general ventilation (1 to 3 air changes per hour).falsefalsefalseProvide a good standard of controlled ventilation (5 to 10 air changes per hour).falsefalsefalseFor further specification, refer to section 8 of the SDS.falsefalsefalseInhalation exposure is considered to be not relevant.falsefalsefalseOral exposure is considered to be not relevant.falsefalsefalseAssumes that potential dermal contact is limited to fingertips.falsefalsefalseAssumes that potential dermal contact is limited to inside hands / one hand / palm of hands.falsefalsefalseAssumes that potential dermal contact is limited to hands.falsefalsefalseAssumes that potential dermal contact is limited to hands and forearms.falsefalsefalseAssumes that potential dermal contact is limited to upper part of the body.falsefalsefalseAssumes that potential dermal contact is limited to lower part of the body.falsefalsefalseAssumes that potential dermal contact excludes feet, hands and head.falsefalsefalseevents per dayfalsefalsefalseLocal exhaust ventilationfalsefalsefalsetonnes/dayfalsefalsefalseh/dayfalsefalsefalseInhalation - minimum efficiency oftruetruetrueh/eventfalsefalsefalseStoffenmanager v5.6.10falsefalsefalseWear suitable respiratory protection.falsefalsefalseART v1.5falsefalsefalseNo water contact during use.falsefalsefalseAssumes that activities are undertaken with appropriate and well maintained equipment by trained personnel operating under supervision.falsefalsefalseIf skin contamination is expected to extend to other parts of the body, then these body parts should also be protected with impervious garments in a manner equivalent to those described for the hands.falsefalsefalseGasolinefalsefalsefalseAutomotive refuellingfalsefalsefalseDieselfalsefalsefalseGarden equipmentfalsefalsefalseHome space heaterfalsefalsefalseRecreational vehiclesfalsefalsefalseQuad bikes or similarfalsefalsefalse(falsefalsefalse)falsefalsefalseConsumerfalsefalsefalseLiquidfalsefalsefalse%falsefalsefalse°CfalsefalsefalseIndoor usefalsefalsefalseOutdoor usefalsefalsefalse