A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-09T19:59:37 2022-03-18T11:34:20 ACTIVE Nov 2021 AISE 8a.1c.v3 Substance types / functions / properties included or excluded: Covers the use of volatile substances in cleaning and maintenance aerosol products. Volatiles which evaporate to a significant extent upon curing of the adhesives. Volatile ingredients are defined by a boiling point threshold of <250°C. cf. background document for further definition. Additional specification of product types covered: covers professional and consumer aerosol applications Spraying of volatile ingredients contained in cleaning and maintenance products https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false CONSUMER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 7.5E-4 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Wide Spread Use in Aerosol products for cleaning and maintenance products (Volatile substances incl. propellants) AISE 8a.1c.v3 ERC_8a 0.0 100.0 0.0 0.004 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT RELEASE_MODULE_REGIONAL_SCALE cf. AISE Background document false false 4.0 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 21f4b32b-ab1b-4fdc-9ae4-314b84e94e94 false false 95babb9e-8ade-44ca-947b-3349a763eee6 ec2738fd-8167-49a2-ac0f-87329ad0519e false true d8e2a5fc-30da-4bca-92ee-ce1a3400b725 14.07.2020 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:35:48 2022-03-18T11:27:47 ACTIVE March 2022 AISE 2.1b.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of granular detergents and maintenance products Additional specification of product types covered: regular powders with apparent density below ca. 0.75kg/L. Compact powders may be extruded (e.g. pearls) or tableted (tabs) detergents reaching densities of ca. 1.4kg/l. Covers the whole process of formulation as it occurs in the manufacturing of granular cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Granular detergents are obtained by drying liquid slurries. Tablets are made by compressing powder material https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 300.0 Cf. AISE background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of granular Detergents/ Maintenance Products: Regular & Compact (medium scale 1,000 - 10,000t product/a) AISE 2.1b.v3 ERC_2 0.1 0.1 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background information. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. manufacturing of different products from one premix (masterbatch), to which certain ingredients are added to yield the final products and/or Dedicated storage tanks for raw materials, premixes and final products and/or Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries false true e5bf56dd-7306-4865-8d63-f1c642de0263 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true 2093dcfc-05f9-4683-932e-460d146b1a63 8bacf2ff-f392-4079-95fc-2ccf0f496374 Dry cleaning of equipment, use of Central or Peripheral Vacuum Cleaning and/or cleaning involving so-called pigs in sub-processes involving liquid slurries and/or re-Use of process grey water for cleaning false true 02326a9e-b0b6-4cb0-a545-3f509cdd6fd9 ec2738fd-8167-49a2-ac0f-87329ad0519e false true 3dbe75c1-81f1-4d9b-8754-a2378661dc54 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:39:15 2022-03-18T11:29:07 ACTIVE March 2022 AISE 2.1h.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of liquid detergents and maintenance products Additional specification of product types covered: Low viscosity products include the following: floor cleaner, all purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim. Typically, the viscosity of these products is not specified and not adjusted. Covers the whole process of formulating water-borne mixtures for liquid cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Routine equipment cleaning and maintenance is also included and leads to the highest contribution to environmental release. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (medium scale 1,000 - 10,000t product/a) AISE 2.1h.v3 ERC_2 0.1 0.0 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background information. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process false true deeba449-3aaa-4072-a351-eca062e6b948 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true f3d0d496-f151-4c1f-a18a-e98e874c626f 8bacf2ff-f392-4079-95fc-2ccf0f496374 Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills false true 56fddd1f-bf93-41cc-bd35-3f1128b9e0cb ec2738fd-8167-49a2-ac0f-87329ad0519e false true 11d0321b-c37a-46fa-8e52-4c24b680ca45 WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T18:52:12 2020-04-21T14:09:51 OBSOLETE Oct 2012 00372dc3-4ee2-4f78-b5c5-628edbaa44a9 AISE 8a.1c.v2 Covers the use of substances in solvents in Cleaning and Maintenance Products for consumers and professional users. Substance Domain: Volatiles / Propellants The quantitative risk characterisation for this environmental exposure has been calculated using name of calculation model uses. The environmental exposure calculation per compartment is based on name of algorithms used (i.e. the algorithms of the EU TGD 2003 Risk Assessment Spreadsheet Model 1.24a) http://www.aise.eu false CONSUMER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 2.05E-6 Wide Dispersive Use of aerosol products for cleaning and maintenance products (propellants);Wide Dispersive Use of aerosol products for cleaning and maintenance products (propellants) AISE 8a.1c.v2 ERC_8a 0.0 Propellants used in air care products or cleaning and maintenance sprays evaporate completely into the air 100.0 Propellants used in air care products or cleaning and maintenance sprays evaporate completely into the air 0.0 Propellants used in air care products or cleaning and maintenance sprays evaporate completely into the air 0.0 Propellants used in air care products or cleaning and maintenance sprays evaporate completely into the air EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION false false 543cc1b6-cf09-454e-83fa-da04509b1d14 false true da0f8e39-68c8-4258-a834-40fb1f9a9055 RELEASE_MODULE_REGIONAL_SCALE false false 4.0 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR_OUTDOOR Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T15:13:41 2020-04-21T14:06:27 OBSOLETE Oct 2012 8a948b54-7d36-4c5c-bdd6-fdc2ed63d84d AISE 8a.1a.v2 Covers the use of substances in solvents in Cleaning and Maintenance Products for consumers and professional users. Substance Domain: AISE SPERC 8a.1.a.v2: down the drain cleaning and maintenance products The quantitative risk characterisation for this environmental exposure has been calculated using name of calculation model uses. The environmental exposure calculation per compartment is based on name of algorithms used (i.e. the algorithms of the EU TGD 2003 Risk Assessment Spreadsheet Model 1.24a) http://www.aise.eu false CONSUMER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 2.05E-6 Wide Dispersive Use in 'Down the Drain' cleaning and maintenance products ;Wide Dispersive Use in 'Down the Drain' cleaning and maintenance products AISE 8a.1a.v2 ERC_8a 100.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. 0.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. 0.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. 0.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. face09ad-036f-4a00-8ad1-6f5ac8c426d6 false true adf95e21-12d5-4088-8df5-a2af0f92b604 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION false false 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR_OUTDOOR RELEASE_MODULE_REGIONAL_SCALE false false 4.0 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:38:08 2022-03-18T11:28:45 ACTIVE March 2022 AISE 2.1g.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of liquid detergents and maintenance products Additional specification of product types covered: Low viscosity products include the following: floor cleaner, all-purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim. Typically, the viscosity of these products is not specified and not adjusted. Covers the whole process of formulating water-borne mixtures for liquid cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Routine equipment cleaning and maintenance is also included and leads to the highest contribution to environmental release. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (large scale >10,000t product/a) AISE 2.1g.v3 ERC_2 0.05 0.0 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process false true deeba449-3aaa-4072-a351-eca062e6b948 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true 73d80ba6-6ebf-426b-8a88-df2841a3e626 8bacf2ff-f392-4079-95fc-2ccf0f496374 Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills false true 56fddd1f-bf93-41cc-bd35-3f1128b9e0cb ec2738fd-8167-49a2-ac0f-87329ad0519e false true 11d0321b-c37a-46fa-8e52-4c24b680ca45 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T15:06:41 2020-04-21T14:05:22 OBSOLETE Oct 2012 ea406d2c-3511-4867-a43c-201fc295c098 AISE 5.1a.v2 Covers the use of metal salts in a broad range of specific applications, e.g. surface treatment, metal treatment, surface finishing, corrosion inhibition etc. This includes the core process of treating the metal substrate as well as those processes required to support the core process such as storing, mixing, equipment cleaning, maintenance and associated laboratory activities. The treatment of the metal parts can occur by bathing or by spraying. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. Substance Domain: Metal salts This SPERC describes SPERC parameters relevant to the Industrial Use of Metal Salts in a water-based process for surface treatment, surface finishing, conversion coating etc. http://www.aise.eu false INDUSTRIAL_USE INDUSTRIAL PC_14 220.0 Industrial use of Me-salts in Conversion Coating – Nickel;Industrial use of Me-salts in Conversion Coating – Nickel AISE 5.1a.v2 ERC_5 5.0 The spent process fluid consists of the rinsing, which contain the metal salts. As a first conservative approximation it assumed that the amount of metal salt is quantitatively lost from the process to the spent process water. 0.0 Metal salts in aqueous solutions are involatile and are intended to remain in the application solution. Volatilization of metal salts is therefore negligible. Spray applications are housed-in for the sake of worker protection. For the reasons above, the release factor to air is set to zero. 0.0 Releases to soil do not occur during normal operation of the process. 95.0 The treatment of the spent process fluids by pH-adjustment and subsequent filtration/sedimentation results in slurries or solid waste which is treated off-site. The content of the reservoir is disposed of once or twice per year and is treated off-site. RELEASE_MODULE_DAILY_USE_AT_SITE The daily use amount is an indicative substance use rate in a typical operation (Msperc). Msperc-represents an indicative worst case value for the substance use rate per site. The amount of metal salt used for the daily replenishment constitutes the substance use rate. The rinsing of the metal parts results in a loss of process water. The volume of process water lost by rinsing is continuously each day and the concentration of the metal salts is adjusted accordingly. 220 emission days per year are assumed. false true 0.05 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 6cc66b74-7f9f-43b5-b46c-bc66b418954d false true b6b02eaa-c95f-4dba-b8ff-6cc355b402bc EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 face09ad-036f-4a00-8ad1-6f5ac8c426d6 false true adf95e21-12d5-4088-8df5-a2af0f92b604 c989e5eb-db6f-4639-8a86-945fb0254ddc Processing fluid can be kept in reservoir or treatment baths. Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. The spent reservoir fluid is treated as chemical waste.Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. false true 190ed007-af39-4d41-93f4-10ddf2c898eb Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T13:50:13 2020-04-21T14:06:06 OBSOLETE Oct 2012 b07c00f5-5c73-43e7-93db-44a532374a9b AISE 2.1a.v2 Covers the whole process of formulation as it occurs in the manufacturing of granular cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of preparations) and equipment cleaning, maintenance and associated laboratory activities. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs large operations, which produce more than 10.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of granular cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into product. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of granular Detergents/ Maintenance Products: Regular & Compact (large scale);Formulation of granular Detergents/ Maintenance Products: Regular & Compact (large scale) AISE 2.1a.v2 ERC_2 0.01 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The numbers that are presented in this SPERC are consistent with the emissions used as default in published Life Cycle Inventories (LCI) for the manufacturing of detergents and cleaners. These data were the basis for the A/B Tables of the EU Technical Guidance Document have been adopted as defaults in this SPERC. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization of granulars are non-existent. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries. Residues which cannot be recycled are disposed off as chemical waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As default daily use amount the indicative worst case value for the substance use rate per site (Msperc) was selected. MSPERC can be used by the registrant when starting the environmental assessment. The MSPERC values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are estimated false true 16.7 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false fe89366f-9e97-429d-ab19-a5239f7d0ea0 false true 9082f8c9-0a0d-4b3c-85c8-568f8a13461d ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 Typical measures may include e.g. - Closed automated process and/or - Closed transfer system and/or - Centralized process control and/or - re-use of process grey water for cleaning - optimized and/or automated systems for the transport and handling of raw materials, that minimize overall exposure levels and incidental spills - Reduced number of transfer and cleaning operations through e.g. - Manufacturing of different products from one premix (masterbatch), to which certain ingredients are added to yield the final products. - Dedicated storage tanks for raw materials, premixes and final products Recovery of materials through e.g. - Recycling Residues of granular detergents in cleaning steps at packaging or transfer lines into the slurries. false true 2313389d-71e3-4233-9e47-6c4e3bd8a218 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 38aec4a0-96e0-4a33-94c3-97a07ae2ab81 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T14:58:36 2018-01-23T17:19:41 OBSOLETE Oct 2012 1dfad436-96b5-4d10-8483-73c8d9c3942d AISE 2.1g.v2 Covers the whole process of manufacturing water-borne mixtures for liquid cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of mixtures) and equipment cleaning, maintenance and associated laboratory activities. Low viscosity products include the following: floor cleaner, all purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim. Typically, the viscosity of these products is not specified and not adjusted. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover large operations, which produce more than 10.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of water-borne liquid cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into products. Losses of raw materials via volatilization are negligible. Significant losses to the environment can be the result of cleaning of mixing vessels, tubing, production/packaging lines. High viscosity products adhere more strongly to the walls of mixing vessels, tubing, production/packaging lines. They are less efficiently transferred into the packaging. Hence, emissions caused by equipment cleaning are higher and lower for high and low viscosity products, respectively. These losses occur irrespective of the physical-chemical properties of the detergent ingredient substances. For that reason, this SPERC pertains to all substances. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (large scale);Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (large scale) AISE 2.1g.v2 ERC_2 0.01 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The release factor originates from the Life Cycle Inventories (LCI, Franke et al., 1991). That publication formed the basis for the A/B Tables for detergent manufacturing in the EU Technical Guidance (EU TGD 2003). EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization are quantitatively very low. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As daily use amount, the indicative worst case value for the substance use rate per site (Msperc) was selected. Msperc can be used by the registrant when starting the environmental assessment. The Msperc values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are assumed. false true 16.7 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR fe89366f-9e97-429d-ab19-a5239f7d0ea0 false true 4b0fdf0e-2f19-49cd-8b9d-01191f78eb04 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 false true 2313389d-71e3-4233-9e47-6c4e3bd8a218 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:40:19 2022-03-18T11:29:23 ACTIVE March 2022 AISE 2.1i.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of liquid detergents and maintenance products Additional specification of product types covered: Low viscosity products include the following: floor cleaner, all purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim. Typically, the viscosity of these products is not specified and not adjusted. Covers the whole process of formulating water-borne mixtures for liquid cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Routine equipment cleaning and maintenance is also included and leads to the highest contribution to environmental release. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 150.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (small scale <1,000 t product/a) AISE 2.1i.v3 ERC_2 0.2 0.0 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process false true deeba449-3aaa-4072-a351-eca062e6b948 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true f3d0d496-f151-4c1f-a18a-e98e874c626f 8bacf2ff-f392-4079-95fc-2ccf0f496374 Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills false true 56fddd1f-bf93-41cc-bd35-3f1128b9e0cb ec2738fd-8167-49a2-ac0f-87329ad0519e false true 11d0321b-c37a-46fa-8e52-4c24b680ca45 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T15:15:02 2020-04-21T14:09:10 OBSOLETE Oct 2012 77eb1252-c7e8-48a4-b6a8-160274e75186 AISE 8a.1a.v2 Covers the use of substances in solvents in Cleaning and Maintenance Products for consumers and professional users. Substance Domain: AISE SPERC 8a.1.a.v2: down the drain cleaning and maintenance products The quantitative risk characterisation for this environmental exposure has been calculated using name of calculation model uses. The environmental exposure calculation per compartment is based on name of algorithms used (i.e. the algorithms of the EU TGD 2003 Risk Assessment Spreadsheet Model 1.24a) http://www.aise.eu false PROFESSIONAL_WORKER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 2.05E-6 Wide Dispersive Use in 'Down the Drain' cleaning and maintenance products ;Wide Dispersive Use in 'Down the Drain' cleaning and maintenance products AISE 8a.1a.v2 ERC_8a 100.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. 0.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. 0.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. 0.0 Laundry detergents, and cleaners are applied as additives to water. After cleaning of substrate the washing / cleaning solutions is disposed of with the waste water such that 100% of the product ingredients enter the waste water system. Product residues remaining on the substrate are likely to be washed off in the next cleaning event. face09ad-036f-4a00-8ad1-6f5ac8c426d6 false true adf95e21-12d5-4088-8df5-a2af0f92b604 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION false false 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR_OUTDOOR RELEASE_MODULE_REGIONAL_SCALE false false 4.0 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T15:00:41 2018-01-23T17:18:44 OBSOLETE Oct 2012 8b86ba5c-8d63-4b0e-8a01-57f81db068d7 AISE 2.1j.v2 Covers the whole process of manufacturing water-borne mixtures for liquid cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of mixtures) and equipment cleaning, maintenance and associated laboratory activities. High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.), and hand dishwash. Typically, the viscosity of these products is specified and may need adjustment. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover large operations, which produce more than 10.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of water-borne liquid cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into products. Losses of raw materials via volatilization are negligible. Significant losses to the environment can be the result of cleaning of mixing vessels, tubing, production/packaging lines. High viscosity products adhere more strongly to the walls of mixing vessels, tubing, production/packaging lines. They are less efficiently transferred into the packaging. Hence, emissions caused by equipment cleaning are higher and lower for high and low viscosity products, respectively. These losses occur irrespective of the physical-chemical properties of the detergent ingredient substances. For that reason, this SPERC pertains to all substances. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of liquid Detergents/ Maintenance Products: High Viscosity (large scale);Formulation of liquid Detergents/ Maintenance Products: High Viscosity (large scale) AISE 2.1j.v2 ERC_2 0.1 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The release factor for AISE 2.1.j.v2 (large scale / high viscosity products) has been extrapolated by the A.I.S.E. sector expert team from the Royal Haskoning (2009) data based on the increasing degree of control of the manufacturing process from small to large scale. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization are quantitatively very low. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As daily use amount, the indicative worst case value for the substance use rate per site (Msperc) was selected. Msperc can be used by the registrant when starting the environmental assessment. The Msperc values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are assumed. false true 16.7 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false fe89366f-9e97-429d-ab19-a5239f7d0ea0 false true 4b0fdf0e-2f19-49cd-8b9d-01191f78eb04 e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 false true 2313389d-71e3-4233-9e47-6c4e3bd8a218 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T19:20:01 2020-04-21T14:04:30 OBSOLETE Oct 2012 df16c0f9-7571-4237-b064-17c8e364238f AISE 2.1l.v2 Covers the whole process of manufacturing water-borne mixtures for liquid cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of mixtures) and equipment cleaning, maintenance and associated laboratory activities. High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.), and hand dishwash. Typically, the viscosity of these products is specified and may need adjustment. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover small operations, which produce less than 1.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of water-borne liquid cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into products. Losses of raw materials via volatilization are negligible. Significant losses to the environment can be the result of cleaning of mixing vessels, tubing, production/packaging lines. High viscosity products adhere more strongly to the walls of mixing vessels, tubing, production/packaging lines. They are less efficiently transferred into the packaging. Hence, emissions caused by equipment cleaning are higher and lower for high and low viscosity products, respectively. These losses occur irrespective of the physical-chemical properties of the detergent ingredient substances. For that reason, this SPERC pertains to all substances. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of liquid Detergents/ Maintenance Products: High Viscosity (small scale);Formulation of liquid Detergents/ Maintenance Products: High Viscosity (small scale) AISE 2.1l.v2 ERC_2 0.4 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The numbers that are presented in this SPERC originate from the study by Royal Haskoning (2009) EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization are quantitatively very low. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 RELEASE_MODULE_DAILY_USE_AT_SITE As daily use amount, the indicative worst case value for the substance use rate per site (Msperc) was selected. Msperc can be used by the registrant when starting the environmental assessment. The Msperc values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are assumed. false true 0.45 WASTE_TREATMENT_CONSIDERATION false false a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 false true ad4db595-f2b7-4649-8422-96a939d2404b ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR fe89366f-9e97-429d-ab19-a5239f7d0ea0 false true 9550d8ee-92b8-4d50-8454-fcaf7a3da0ba Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-09T19:30:02 2022-03-18T11:33:33 ACTIVE Nov 2021 AISE 8a.1a.v3 Substance types / functions / properties included or excluded: Covers the use of solid and liquid substances in laundry detergents, cleaning and maintenance products Additional specification of product types covered: covers professional and consumer applications such as: - Regular and compact powders: Regular powders with apparent density below ca. 0.75kg/L. Compact powders may be extruded (e.g. pearls) or tableted (tabs) detergents reaching densities of ca. 1.4kg/l. - Low viscosity products: floor cleaner, all purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim - High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.) and hand dishwash Substance applied in aqueous process solution with negligible volatilization https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false PROFESSIONAL_WORKER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 7.5E-4 cf. AISE Background document Wide Spread Use in 'Down the Drain' laundry detergents, cleaning and maintenance products AISE 8a.1a.v3 ERC_8a 100.0 0.0 0.0 0.004 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR RELEASE_MODULE_REGIONAL_SCALE cf. AISE Background document false false 4.0 WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 025b8ced-ea23-4300-928f-82348f092cc4 false true 8a9cc976-32a6-4332-95a6-5a9ce7abccf9 89da0a94-43b2-4b7d-a55a-1e000fcfd7a3 false true 09373d1b-22be-4885-bd15-79aaed3b8a6e ec2738fd-8167-49a2-ac0f-87329ad0519e false true d8e2a5fc-30da-4bca-92ee-ce1a3400b725 14.07.2020 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-09T19:30:38 2022-03-18T11:32:36 ACTIVE Nov 2021 AISE 8a.1a.v3 Substance types / functions / properties included or excluded: Covers the use of solid and liquid substances in laundry detergents, cleaning and maintenance products Additional specification of product types covered: covers professional and consumer applications such as: - Regular and compact powders: Regular powders with apparent density below ca. 0.75kg/L. Compact powders may be extruded (e.g. pearls) or tableted (tabs) detergents reaching densities of ca. 1.4kg/l. - Low viscosity products: floor cleaner, all purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim - High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.) and hand dishwash Substance applied in aqueous process solution with negligible volatilization https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false CONSUMER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 7.5E-4 cf. AISE Background document Wide Spread Use in 'Down the Drain' laundry detergents, cleaning and maintenance products AISE 8a.1a.v3 ERC_8a 100.0 0.0 0.0 0.004 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT RELEASE_MODULE_REGIONAL_SCALE cf. AISE Background document false false 4.0 025b8ced-ea23-4300-928f-82348f092cc4 false true 8a9cc976-32a6-4332-95a6-5a9ce7abccf9 89da0a94-43b2-4b7d-a55a-1e000fcfd7a3 false true 09373d1b-22be-4885-bd15-79aaed3b8a6e ec2738fd-8167-49a2-ac0f-87329ad0519e false true d8e2a5fc-30da-4bca-92ee-ce1a3400b725 14.07.2020 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:41:30 2022-03-18T11:29:45 ACTIVE March 2022 AISE 2.1j.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of liquid detergents and maintenance products Additional specification of product types covered High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.) and hand dishwash. Typically, the viscosity of these products is specified and may need adjustment. Covers the whole process of formulating water-borne mixtures for liquid cleaning and maintenance products. This includes typical process steps such as, storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Routine equipment cleaning and maintenance is also included and leads to the highest contribution to environmental release. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of liquid Detergents/ Maintenance Products: High Viscosity (large scale >10,000 t product/a) AISE 2.1j.v3 ERC_2 0.1 0.0 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process false true deeba449-3aaa-4072-a351-eca062e6b948 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true 8047213b-973f-4159-b2ca-ced001657eb3 8bacf2ff-f392-4079-95fc-2ccf0f496374 Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills false true 56fddd1f-bf93-41cc-bd35-3f1128b9e0cb ec2738fd-8167-49a2-ac0f-87329ad0519e false true 11d0321b-c37a-46fa-8e52-4c24b680ca45 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T15:05:54 2020-04-21T14:05:41 OBSOLETE Oct 2012 d79eb022-410e-4fea-a3c8-7bf31f9b4d49 AISE 5.1b.v2 Covers the use of metal salts in a broad range of specific applications, e.g. surface treatment, metal treatment, surface finishing, corrosion inhibition etc. This includes the core process of treating the metal substrate as well as those processes required to support the core process such as storing, mixing, equipment cleaning, maintenance and associated laboratory activities. The treatment of the metal parts can occur by bathing or by spraying. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. Substance Domain: Metal salts This SPERC describes SPERC parameters relevant to the Industrial Use of Metal Salts in a water-based process for surface treatment, surface finishing, conversion coating etc. http://www.aise.eu false INDUSTRIAL_USE INDUSTRIAL PC_14 220.0 Industrial use of Me-salts in Conversion Coating – Zinc, chromium, copper, manganese;Industrial use of Me-salts in Conversion Coating – Zinc, chromium, copper, manganese AISE 5.1b.v2 ERC_5 1.0 The spent process fluid consists of the rinsing, which contain the metal salts. As a first conservative approximation it assumed that the amount of metal salt is quantitatively lost from the process to the spent process water. 0.0 Metal salts in aqueous solutions are involatile and are intended to remain in the application solution. Volatilization of metal salts is therefore negligible. Spray applications are housed-in for the sake of worker protection. For the reasons above, the release factor to air is set to zero. 0.0 Releases to soil do not occur during normal operation of the process. 99.0 The treatment of the spent process fluids by pH-adjustment and subsequent filtration/sedimentation results in slurries or solid waste which is treated off-site. The content of the reservoir is disposed of once or twice per year and is treated off-site. RELEASE_MODULE_DAILY_USE_AT_SITE The daily use amount is an indicative substance use rate in a typical operation (Msperc). Msperc-represents an indicative worst case value for the substance use rate per site. The amount of metal salt used for the daily replenishment constitutes the substance use rate. The rinsing of the metal parts results in a loss of process water. The volume of process water lost by rinsing is continuously each day and the concentration of the metal salts is adjusted accordingly. 220 emission days per year are assumed. false true 0.05 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false 6cc66b74-7f9f-43b5-b46c-bc66b418954d false true b6b02eaa-c95f-4dba-b8ff-6cc355b402bc ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 face09ad-036f-4a00-8ad1-6f5ac8c426d6 false true adf95e21-12d5-4088-8df5-a2af0f92b604 c989e5eb-db6f-4639-8a86-945fb0254ddc Processing fluid can be kept in reservoir or treatment baths. Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. The spent reservoir fluid is treated as chemical waste.Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. false true 190ed007-af39-4d41-93f4-10ddf2c898eb Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T13:57:09 2020-04-21T14:05:01 OBSOLETE Oct 2012 c8de4e45-0ac5-43e8-9101-ab8b2d37d173 AISE 4.1.v2 Industrial uses in water borne processing aid. This definition covers substances in a broad range of specific applications, e.g. surface cleaning, surface treatment, metal treatment, surface finishing, corrosion inhibition, vehicle cleaning, industrial laundry etc. Industrial applications of water borne processing aids can typically be described as follows. The application fluid is kept in a reservoir. It is pumped to dedicated machine(s) in order to be applied to the substrate or it is kept in a bath. This type of application includes vehicle cleaning, metal working fluids, etc. With each piece of substrate a fraction of the application fluid is carried-over from the treatment bath. Via a sequence of rinsing steps this fraction of the application fluid is continuously emitted to the wastewater. The reservoir is continuously replenished. The application fluid in the reservoir can be disposed off periodically. This may or may not involve on-site pre-treatment or disposal to the wastewater. As a result, constituents of the application fluid are removed during the on-site treatment according to the efficiency of the selected emission reduction. In addition, raw materials may be recovered. The choice of suitable emission reduction (or RMM) technology depends on the process. In addition, the process can be closed with regards to emissions to the environment. Spent application fluid is not released to the environment. It is disposed of periodically as waste (with or without prior treatment). This type of application includes several surface finishing, water conditioning etc. applications. No emissions to the wastewater occur. The local waste handling regulations have to be followed. Additional instructions for handling waste may be included in the safety data sheet. http://www.aise.eu false INDUSTRIAL_USE INDUSTRIAL PC_35 220.0 Industrial use of Water Borne processing Aids – no RMM;Industrial use of Water Borne processing Aids – no RMM AISE 4.1.v2 ERC_4 100.0 Water-borne processing aids are disposed off quantitatively to the process wastewater. Prior to discharging, the spent process water may be treated on-site. 0.0 Processing aids in aqueous solutions are not volatile and are intended to remain in the application solution. Spray applications are housed-in 0.0 Water-borne processing aids are disposed off quantitatively to the process wastewater. Releases to soil do not occur during normal operation. 0.0 Water-borne processing aids are disposed off quantitatively to the process wastewater. Releases to waste do not occur during normal operation. RELEASE_MODULE_DAILY_USE_AT_SITE As default tonnage, the typical maximum site tonnage, based on sector knowledge was taken. The continuous release (Msperc) is 50 kg/day. Optional are intermittent release. 220 emission days per year are assumed. false true 0.05 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR 6cc66b74-7f9f-43b5-b46c-bc66b418954d false true b6b02eaa-c95f-4dba-b8ff-6cc355b402bc 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 face09ad-036f-4a00-8ad1-6f5ac8c426d6 false true adf95e21-12d5-4088-8df5-a2af0f92b604 c989e5eb-db6f-4639-8a86-945fb0254ddc Processing fluid can be kept in reservoir or treatment baths. Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. This may involve disposal to the wastewater. In some instances on-site pre-treatment (de-emulsification, pH-adjustment, and filtration) may be required. Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. false true a1b3e8b7-5df5-4ccc-bc0f-050d80d90b35 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T15:16:41 2020-04-21T14:08:49 OBSOLETE Oct 2012 fa2ce360-6d5f-446b-8b4e-500549996bde AISE 8a.1b.v2 Covers the use of substances in solvents in Cleaning and Maintenance Products for consumers and professional users. Substance Domain: Non-Volatiles The quantitative risk characterisation for this environmental exposure has been calculated using name of calculation model uses. The environmental exposure calculation per compartment is based on name of algorithms used (i.e. the algorithms of the EU TGD 2003 Risk Assessment Spreadsheet Model 1.24a) http://www.aise.eu false CONSUMER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 2.05E-6 Wide Dispersive Use in aerosol products for cleaning and maintenance products (non-propellants);Wide Dispersive Use in aerosol products for cleaning and maintenance products (non-propellants) AISE 8a.1b.v2 ERC_8a 100.0 Nonvolatile constituents air care products or cleaning and maintenance sprays will deposit on surface and will be transferred to the waste water system in the next cleaning event. 0.0 Nonvolatile constituents air care products or cleaning and maintenance sprays will deposit on surface and will be transferred to the waste water system in the next cleaning event. 0.0 Nonvolatile constituents air care products or cleaning and maintenance sprays will deposit on surface and will be transferred to the waste water system in the next cleaning event. 0.0 Nonvolatile constituents air care products or cleaning and maintenance sprays will deposit on surface and will be transferred to the waste water system in the next cleaning event. EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION false false 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 66ad9081-ad6e-4571-8cb7-4506161f4ed8 RELEASE_MODULE_REGIONAL_SCALE false false 4.0 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR_OUTDOOR Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:34:51 2022-03-18T11:26:51 ACTIVE March 2022 AISE 2.1a.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of granular and tableted detergents and maintenance products Additional specification of product types covered: regular powders with apparent density below ca. 0.75kg/L. Compact powders may be extruded (e.g. pearls) or tableted (tabs) detergents reaching densities of ca. 1.4kg/l. Covers the whole process of formulation as it occurs in the manufacturing of granular cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Granular detergents are obtained by drying liquid slurries. Tablets are made by compressing powder material https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of granular Detergents/ Maintenance Products: Regular & Compact (large scale >10,000t product/a) AISE 2.1a.v3 ERC_2 0.05 0.1 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background information. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. manufacturing of different products from one premix (masterbatch), to which certain ingredients are added to yield the final products and/or Dedicated storage tanks for raw materials, premixes and final products and/or Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries false true e5bf56dd-7306-4865-8d63-f1c642de0263 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true 73d80ba6-6ebf-426b-8a88-df2841a3e626 8bacf2ff-f392-4079-95fc-2ccf0f496374 Dry cleaning of equipment, use of Central or Peripheral Vacuum Cleaning and/or cleaning involving so-called pigs in sub-processes involving liquid slurries and/or re-Use of process grey water for cleaning false true 02326a9e-b0b6-4cb0-a545-3f509cdd6fd9 ec2738fd-8167-49a2-ac0f-87329ad0519e false true 3dbe75c1-81f1-4d9b-8754-a2378661dc54 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T13:40:20 2018-01-23T17:18:10 OBSOLETE Oct 2012 092c7052-0d9d-44b0-85ac-3626cd9995b7 AISE 2.1b.v2 Covers the whole process of formulation as it occurs in the manufacturing of granular cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of preparations) and equipment cleaning, maintenance and associated laboratory activities. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover medium operations, which produce up to 10.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of granular cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into product. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of granular Detergents/ Maintenance Products: Regular & Compact (medium scale);Formulation of granular Detergents/ Maintenance Products: Regular & Compact (medium scale) AISE 2.1b.v2 ERC_2 0.1 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The numbers that are presented in this SPERC are consistent with the emissions used as default in published Life Cycle Inventories (LCI) for the manufacturing of detergents and cleaners. These data were the basis for the A/B Tables of the EU Technical Guidance Document have been adopted as defaults in this SPERC. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization of granulars are non-existent. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries. Residues which cannot be recycled are disposed off as chemical waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As default daily use amount the indicative worst case value for the substance use rate per site (Msperc) was selected. MSPERC can be used by the registrant when starting the environmental assessment. The MSPERC values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are estimated false true 4.5 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false fe89366f-9e97-429d-ab19-a5239f7d0ea0 false true 9082f8c9-0a0d-4b3c-85c8-568f8a13461d ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 38aec4a0-96e0-4a33-94c3-97a07ae2ab81 e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 Typical measures may include e.g. - Closed batch systems and / or - Semi-closed transfer system and/or - Batch production of final product Reduced number of transfer and cleaning operations through e.g. - Dedicated storage tanks for raw materials, premixes and final products false true a36fffc0-a9de-47be-b7c0-d36e161d49ac Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:44:47 2022-03-18T11:31:03 ACTIVE March 2022 AISE 4.1.v3 Substance types / functions / properties included or excluded: Substances used as processing aids in the chemical industries not becoming part the article Additional specification of product types covered: Processing aids as defined covers substances in a broad range of specific applications, e.g. industrial laundry, car washing, boat cleaning, process cleaning, CIP cleaning, surface cleaning Industrial uses of aqueous process solution comprise of preparation of baths and automated cleaning steps prior to any on-site RMM. Spent process fluid is discharged to wastewater. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false INDUSTRIAL_USE INDUSTRIAL PC_35 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Industrial use of Water-borne Processing Aids AISE 4.1.v3 ERC_4 100.0 0.0 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative worst case substance use rates (MSPERC) of several ingredient types and guidance for refinement can be found in the AISE background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 6b70cae5-0bc7-4bc1-81ef-8b2829412318 The application fluid is kept in a reservoir. The fluid is pumped to dedicated machine(s) in order to be applied to the substrate or it is kept in a treatment bath (e.g. vehicle cleaning, metal working fluids, etc.). With each piece of substrate a fraction of the application fluid is carried-over from the treatment bath. Via a sequence of rinsing steps this fraction of the application fluid is continuously emitted to the wastewater. The reservoir is continuously replenished; and/or The application fluid in the reservoir can be disposed of periodically: This may or may not involve on-site pre-treatment or disposal to the wastewater. As a result, constituents of the application fluid are removed during the on-site treatment according to the efficiency of the selected emission reduction. In addition, raw materials may be recovered. The choice of suitable emission reduction technology depends on the process; and/or Closed system with regards to emissions to the environment. Spent application fluid is not released to the environment. It is disposed of periodically as waste (with or without prior treatment). This type of application includes several surface finishing, water conditioning etc. applications. No emissions to the wastewater occur. The local waste handling regulations have to be followed. Additional instructions for handling waste may be included in the safety data sheet; and/or Optimized water use due to e.g.: Re-use of rinsing water false true 8f771761-9030-4dcc-bab4-a1f5accbdef8 ec2738fd-8167-49a2-ac0f-87329ad0519e false true ce920cfd-3a3c-4a48-8f24-6d4d2ca15c61 20.01.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T13:46:50 2018-01-23T17:19:00 OBSOLETE Oct 2012 d9990d26-4786-4427-81b6-4264756a190b AISE 2.1k.v2 Covers the whole process of manufacturing water-borne mixtures for liquid cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of mixtures) and equipment cleaning, maintenance and associated laboratory activities. High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.), and hand dishwash. Typically, the viscosity of these products is specified and may need adjustment. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover medium operations, which produce up to 10.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of water-borne liquid cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into products. Losses of raw materials via volatilization are negligible. Significant losses to the environment can be the result of cleaning of mixing vessels, tubing, production/packaging lines. High viscosity products adhere more strongly to the walls of mixing vessels, tubing, production/packaging lines. They are less efficiently transferred into the packaging. Hence, emissions caused by equipment cleaning are higher and lower for high and low viscosity products, respectively. These losses occur irrespective of the physical-chemical properties of the detergent ingredient substances. For that reason, this SPERC pertains to all substances. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of liquid Detergents/ Maintenance Products: High Viscosity (medium scale);Formulation of liquid Detergents/ Maintenance Products: High Viscosity (medium scale) AISE 2.1k.v2 ERC_2 0.2 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The numbers that are presented in this SPERC originate from the study by Royal Haskoning (2009) f EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization are quantitatively very low. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As daily use amount, the indicative worst case value for the substance use rate per site (Msperc) was selected. Msperc can be used by the registrant when starting the environmental assessment. The Msperc values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are assumed. false true 4.5 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 Typical measures may include e.g. - Closed batch systems and / or - Semi-closed transfer system and/or - Batch production of final product Reduced number of transfer and cleaning operations through e.g. - Dedicated storage tanks for raw materials, premixes and final products false true a36fffc0-a9de-47be-b7c0-d36e161d49ac 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 fe89366f-9e97-429d-ab19-a5239f7d0ea0 Typically implemented measures for reducing emissions to waste water may include: - Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) - use of two-liner systems (i.e. single use disposable reactor cover that is incinerated after use as solid waste) false true e1134849-4da6-4f95-8ada-d773b2e07c74 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T19:18:11 2018-01-23T17:20:28 OBSOLETE Oct 2012 4831f71b-972e-4826-a377-61fd66b79845 AISE 2.1i.v2 Covers the whole process of manufacturing water-borne mixtures for liquid cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of mixtures) and equipment cleaning, maintenance and associated laboratory activities. Low viscosity products include the following: floor cleaner, all purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim. Typically, the viscosity of these products is not specified and not adjusted. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover small operations, which produce less than 1.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of water-borne liquid cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into products. Losses of raw materials via volatilization are negligible. Significant losses to the environment can be the result of cleaning of mixing vessels, tubing, production/packaging lines. High viscosity products adhere more strongly to the walls of mixing vessels, tubing, production/packaging lines. They are less efficiently transferred into the packaging. Hence, emissions caused by equipment cleaning are higher and lower for high and low viscosity products, respectively. These losses occur irrespective of the physical-chemical properties of the detergent ingredient substances. For that reason, this SPERC pertains to all substances. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (small scale);Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (small scale) AISE 2.1i.v2 ERC_2 0.2 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The numbers that are presented in this SPERC originate from the study by Royal Haskoning (2009) EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization are quantitatively very low. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As daily use amount, the indicative worst case value for the substance use rate per site (Msperc) was selected. Msperc can be used by the registrant when starting the environmental assessment. The Msperc values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are assumed. false true 0.45 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 false true ad4db595-f2b7-4649-8422-96a939d2404b ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR fe89366f-9e97-429d-ab19-a5239f7d0ea0 false true 9550d8ee-92b8-4d50-8454-fcaf7a3da0ba Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:15:40 2022-03-18T11:31:50 ACTIVE March 2022 AISE 5.1b.v3 Substance types / functions / properties included or excluded: Covers the use of Zinc-, Chromium, Coper-, Manganese- salts in metal surface Coating applications Additional specification of product types covered: broad range of specific applications, e.g. surface treatment, metal treatment, surface finishing, conversion coating, corrosion inhibition etc. includes the core process of treating metal surfaces and/or plastics (e.g. Phosphating, Coil coating, Electroplating, Anodizing, Autocatalytic plating) as well as those processes required to support the core process such as storing, mixing, equipment cleaning, maintenance and associated laboratory activities. The treatment of the metal parts can occur by dipping, rolling or by spraying. Product applied in aqueous process solution with negligible volatilization. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false INDUSTRIAL_USE INDUSTRIAL PC_14 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Industrial use of Me-salts in surface treatment of metals and plastics – Zinc, Chromium, Copper, Manganese AISE 5.1b.v3 ERC_5 1.0 0.0 0.0 5.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative worst case substance use rates (MSPERC) of several ingredient types and guidance for refinement can be found in background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 6b70cae5-0bc7-4bc1-81ef-8b2829412318 Metal salts are dissolved in a water-borne application fluid, which is kept in a reservoir or treatment baths. Metal fluids are continuously emitted to the wastewater via a sequence of rinsing steps. For details of OCs refer to background document”; and/or Spray applications are housed-in for the sake of worker protection; and/or Optimized water use due to e.g.: Re-use of rinsing water; and/or Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. false true 4334460e-b0a5-43ff-9eb3-a8e63ac82e62 ec2738fd-8167-49a2-ac0f-87329ad0519e false true ee79f0a9-6969-4b35-b2bb-cc6a0bc191d4 1a6e55bf-fe3d-4248-8716-928f29cf6e5a cf. AISE Background document false true 7056993d-3468-4df7-a102-1b0a2f92aeb2 WATER 99.0 cf. AISE Background document 26.06.2020 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T13:18:18 2018-01-23T17:18:29 OBSOLETE Oct 2012 e0c8a3ec-fcad-40a0-8c88-5aaa80806f94 AISE 2.1c.v2 Covers the whole process of formulation as it occurs in the manufacturing of granular cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of preparations) and equipment cleaning, maintenance and associated laboratory activities. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover small operations, which produce less than 1.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of granular cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into product. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 Formulation of granular Detergents/ Maintenance Products: Regular & Compact (small scale);Formulation of granular Detergents/ Maintenance Products: Regular & Compact (small scale) AISE 2.1c.v2 ERC_2 0.2 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The numbers that are presented in this SPERC are consistent with the emissions used as default in published Life Cycle Inventories (LCI) for the manufacturing of detergents and cleaners. These data were the basis for the A/B Tables of the EU Technical Guidance Document have been adopted as defaults in this SPERC. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization of granulars are non-existent. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries. Residues which cannot be recycled are disposed off as chemical waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514 Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As default daily use amount the indicative worst case value for the substance use rate per site (Msperc) was selected. MSPERC can be used by the registrant when starting the environmental assessment. The MSPERC values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are estimated false true 0.45 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false fe89366f-9e97-429d-ab19-a5239f7d0ea0 false true 9082f8c9-0a0d-4b3c-85c8-568f8a13461d ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 Typically implemented measures for reducing emissions to waste water may include: - Closed batch systems false true ad4db595-f2b7-4649-8422-96a939d2404b 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 38aec4a0-96e0-4a33-94c3-97a07ae2ab81 Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:42:20 2022-03-18T11:30:13 ACTIVE March 2022 AISE 2.1k.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of liquid detergents and maintenance products Additional specification of product types covered: High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.) and hand dishwash. Typically, the viscosity of these products is specified and may need adjustment. Covers the whole process of formulation water-borne mixtures for liquid cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Routine equipment cleaning and maintenance is also included and leads to the highest contribution to environmental release. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of liquid Detergents/ Maintenance Products: High Viscosity (medium scale 1,000 - 10,000t product/a) AISE 2.1k.v3 ERC_2 0.2 0.0 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process false true deeba449-3aaa-4072-a351-eca062e6b948 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true f3d0d496-f151-4c1f-a18a-e98e874c626f 8bacf2ff-f392-4079-95fc-2ccf0f496374 Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills false true 56fddd1f-bf93-41cc-bd35-3f1128b9e0cb ec2738fd-8167-49a2-ac0f-87329ad0519e false true 11d0321b-c37a-46fa-8e52-4c24b680ca45 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:43:21 2022-03-18T11:30:31 ACTIVE March 2022 AISE 2.1l.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of liquid detergents and maintenance products Additional specification of product types covered: High viscosity products include the following: fabric finisher, liquid detergents, liquid detergent gels, detergent paste (hand detergents), cleaner gels (WC, bathroom, etc.) and hand dishwash. Typically, the viscosity of these products is specified and may need adjustment. Covers the whole process of formulating water-borne mixtures for liquid cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Routine equipment cleaning and maintenance is also included and leads to the highest impact to environmental release. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 150.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of liquid Detergents/ Maintenance Products: High Viscosity (small scale <1,000t product/a) AISE 2.1l.v3 ERC_2 0.4 0.0 0.0 0.0 APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background documentation. false true WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process false true deeba449-3aaa-4072-a351-eca062e6b948 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true f3d0d496-f151-4c1f-a18a-e98e874c626f 8bacf2ff-f392-4079-95fc-2ccf0f496374 Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills false true 56fddd1f-bf93-41cc-bd35-3f1128b9e0cb ec2738fd-8167-49a2-ac0f-87329ad0519e false true 11d0321b-c37a-46fa-8e52-4c24b680ca45 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:36:46 2022-03-18T11:28:15 ACTIVE March 2022 AISE 2.1c.v3 Substance types / functions / properties included or excluded: solid and liquid substances used for the formulation of granular detergents and maintenance products. Additional specification of product types covered: regular powders with apparent density below ca. 0.75kg/L. Compact powders may be extruded (e.g. pearls) or tableted (tabs) detergents reaching densities of ca. 1.4kg/l. Covers the whole process of formulation as it occurs in the manufacturing of granular cleaning and maintenance products. This includes typical process steps, such as storing, mixing, packaging of substances (as part of mixtures) and associated laboratory activities. Granular detergents are obtained by drying liquid slurries. Tablets are made by compressing powder material https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false FORMULATION INDUSTRIAL PC_35 150.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Formulation of granular Detergents/ Maintenance Products: Regular & Compact (small scale <1,000t product/a) AISE 2.1c.v3 ERC_2 0.2 0.1 0.0 0.0 RELEASE_MODULE_DAILY_USE_AT_SITE The daily max amount per site (Msafe) is used. The indicative substance use rate (MSPERC) for several ingredient types and guidance for refinement can be found in background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 18f21585-d45e-4d7d-9be6-d6c3612484cc Reduced number of transfer and cleaning operations through e.g. manufacturing of different products from one premix (masterbatch), to which certain ingredients are added to yield the final products and/or Dedicated storage tanks for raw materials, premixes and final products and/or Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries false true e5bf56dd-7306-4865-8d63-f1c642de0263 c531adf9-d9ca-41e9-a5b8-83525d0158c7 false true 2093dcfc-05f9-4683-932e-460d146b1a63 8bacf2ff-f392-4079-95fc-2ccf0f496374 Dry cleaning of equipment, use of Central or Peripheral Vacuum Cleaning and/or cleaning involving so-called pigs in sub-processes involving liquid slurries and/or re-Use of process grey water for cleaning false true 02326a9e-b0b6-4cb0-a545-3f509cdd6fd9 ec2738fd-8167-49a2-ac0f-87329ad0519e false true 3dbe75c1-81f1-4d9b-8754-a2378661dc54 20.08.2021 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T20:13:49 2022-03-18T11:31:28 ACTIVE March 2022 AISE 5.1a.v3 Substance types / functions / properties included or excluded: Covers the use of Nickel-salts in metal surface coating applications. Additional specification of product types covered: broad range of specific water-based applications, e.g. surface treatment, metal treatment, conversion coating, surface finishing, corrosion inhibition etc. includes the core process of treating metal and/or plastic surfaces (e.g. Phosphating, Electroplating, Cold sealing, Autocatalytic plating) as well as those processes required to support the core process such as storing, mixing, equipment cleaning, maintenance and associated laboratory activities. The treatment of the metal parts can occur by dipping, rolling or by spraying. Product applied in aqueous process solution with negligible volatilization. Spent fluid discharged to wastewater. https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false INDUSTRIAL_USE INDUSTRIAL PC_14 300.0 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Industrial use of Me-salts in surface treatment of metals and plastics – Nickel AISE 5.1a.v3 ERC_5 5.0 0.0 0.0 5.0 RELEASE_MODULE_DAILY_USE_AT_SITE the daily max amount per site (Msafe) is used. The indicative worst case substance use rates (MSPERC) of several ingredient types and guidance for refinement can be found in background documentation. false true EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR ec2738fd-8167-49a2-ac0f-87329ad0519e false true ee79f0a9-6969-4b35-b2bb-cc6a0bc191d4 WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 6b70cae5-0bc7-4bc1-81ef-8b2829412318 Metal salts are dissolved in a water-borne application fluid, which is kept in a reservoir or treatment baths. Metal fluids are continuously emitted to the wastewater via a sequence of rinsing steps. For details of OCs refer to background document”; and/or Spray applications are housed-in for the sake of worker protection; and/or Optimized water use due to e.g.: Re-use of rinsing water; and/or Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. false true 4334460e-b0a5-43ff-9eb3-a8e63ac82e62 1a6e55bf-fe3d-4248-8716-928f29cf6e5a false true 7056993d-3468-4df7-a102-1b0a2f92aeb2 WATER 95.0 cf. AISE Background document 26.06.2020 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2017-12-15T13:26:34 2018-01-23T17:20:13 OBSOLETE Oct 2012 0c213476-8283-4e9a-be28-7d308a50a05a AISE 2.1h.v2 Covers the whole process of manufacturing water-borne mixtures for liquid cleaning and maintenance products. This includes storing, mixing, packaging of substances (as part of mixtures) and equipment cleaning, maintenance and associated laboratory activities. Low viscosity products include the following: floor cleaner, all purpose cleaner, bathroom cleaner, kitchen cleaner, window cleaner, liquid WC-rim. Typically, the viscosity of these products is not specified and not adjusted. The SPERCs are relevant for operations which discharge their wastewater to treatment by a municipal sewage treatment plant. The SPERCs cover medium operations, which produce up to 10.000 tons of finished products per year, respectively. Substance Domain: All This SPERC describes SPERC parameters relevant to the manufacturing of water-borne liquid cleaning and maintenance products. Losses from the processes constitute losses of raw materials, which for economic reasons have to be avoided. Formulation of preparations requires optimized use of raw materials for inclusion into products. Losses of raw materials via volatilization are negligible. Significant losses to the environment can be the result of cleaning of mixing vessels, tubing, production/packaging lines. High viscosity products adhere more strongly to the walls of mixing vessels, tubing, production/packaging lines. They are less efficiently transferred into the packaging. Hence, emissions caused by equipment cleaning are higher and lower for high and low viscosity products, respectively. These losses occur irrespective of the physical-chemical properties of the detergent ingredient substances. For that reason, this SPERC pertains to all substances. http://www.aise.eu false FORMULATION INDUSTRIAL PC_35 250.0 Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (medium scale);Formulation of liquid Detergents/ Maintenance Products: Low Viscosity (medium scale) AISE 2.1h.v2 ERC_2 0.1 Releases to the wastewater can be the result of cleaning of mixing vessels, tubing, production/packaging lines with water. The spent cleaning water is discharged to the wastewater. The numbers that are presented in this SPERC originate from the study by Royal Haskoning (2009) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Releases of raw materials via volatilization are quantitatively very low. For that reason, the study by Royal Haskoning (2009) does not consider to establish release factors for the use of fragrance materials in the manufacturing of detergent products. For that reason, the release factor is set to zero. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Must be avoided EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). 0.0 Not relevant – no obligatory RMM which divert substances to waste. EU TGD 2003 Technical Guidance Document on Risk Assessment. Part II, Appendix1 A Table A2 (p 226) Franke et al., 1995 Ökobilanzierung- Sachbilanz für die Waschmittel-Konfektionierung Tenside Surf. Det, 32:(508-514) Royal Haskoning 2009 Review and evaluation of environmental emission scenarios for fragrance materials during compounding of perfume oils and formulation of consumer products (Research Institute for Fragrance Materials. Ref.:9S3975.01/R0007/Nijm, 2009). RELEASE_MODULE_DAILY_USE_AT_SITE As daily use amount, the indicative worst case value for the substance use rate per site (Msperc) was selected. Msperc can be used by the registrant when starting the environmental assessment. The Msperc values have been estimated in dependence of the size of the operation, the number of days emitting, and the concentration of the substance in a finished product (i.e. mixture). 250 emission days per year are assumed. false true 4.5 EUSES_DISCHARGE_RATE_OF_STP false true 2000.0 a6bd8edd-2a2c-4495-8eb1-89753d930dd1 false true ca394e7c-f065-4582-9b0d-05d5fd239722 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER APPLICATION_OF_THE_STP false false APPLICATION_OF_THE_STP-YES WASTE_TREATMENT_CONSIDERATION false false ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR 543cc1b6-cf09-454e-83fa-da04509b1d14 false true 3964f564-2bd2-406a-aeec-08928ff91aa8 fe89366f-9e97-429d-ab19-a5239f7d0ea0 Typically implemented measures for reducing emissions to waste water may include: - Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) - use of two-liner systems (i.e. single use disposable reactor cover that is incinerated after use as solid waste) false true e1134849-4da6-4f95-8ada-d773b2e07c74 e3307e75-bcf4-4aec-bcd4-a913c4ce4e60 Typical measures may include e.g. - Closed batch systems and / or - Semi-closed transfer system and/or - Batch production of final product Reduced number of transfer and cleaning operations through e.g. - Dedicated storage tanks for raw materials, premixes and final products false true a36fffc0-a9de-47be-b7c0-d36e161d49ac Oct 2012 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-09T19:37:56 2022-03-18T11:34:00 ACTIVE Nov 2021 AISE 8a.1b.v3 Substance types / functions / properties included or excluded: Covers the use of non-volatile substances in cleaning and maintenance aerosol products. Volatile substances are defined by a boiling point threshold of <250°C. Non-volatile constituents which will be picked up by a cleaning cloth after spraying onto cleaning surface and will be transferred to the waste water system in the next washing event. cf. background document for further details. Additional specification of product types covered: covers professional and consumer aerosol applications Spraying of non-volatile solids to indoor surfaces for cleaning and maintenance purposes https://echa.europa.eu/csr-es-roadmap/use-maps/use-maps-library false CONSUMER_USE INDUSTRIAL PC_3 PC_35 PC_8 PC_31 7.5E-4 cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document cf. AISE Background document Wide Spread Use in Aerosol products for cleaning and maintenance products (non-volatile) AISE 8a.1b.v3 ERC_8a 100.0 0.0 0.0 0.004 EUSES_BIOLOGICAL_STP false true EUSES_BIOLOGICAL_STP-STANDARD WATER WASTE_TREATMENT_CONSIDERATION "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: false true WASTE_CONSIDERATION_OTHER_TREATMENT RELEASE_MODULE_REGIONAL_SCALE cf. AISE Background document false false 4.0 ENVIRONMENT_PLACE_OF_USE false true ENVIRONMENT_PLACE_OF_USE_INDOOR WATER_CONTACT_DURING_USE false true WATER_CONTACT_DURING_USE_YES 21f4b32b-ab1b-4fdc-9ae4-314b84e94e94 false false 95babb9e-8ade-44ca-947b-3349a763eee6 ec2738fd-8167-49a2-ac0f-87329ad0519e false true d8e2a5fc-30da-4bca-92ee-ce1a3400b725 14.07.2020 A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T20:56:59 2021-11-07T20:56:59 ACTIVE ENVIRONMENT Laundry detergents, cleaners and maintenance products are applied as additives to water. After cleaning of substrate the washing / cleaning solutions are disposed of with the waste water. false WATER E_W_6 E_C_4 ... true Laundry detergents, cleaners and maintenance products are applied as additives to water. After cleaning of substrate the washing / cleaning solutions are disposed of with the waste water. true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T19:46:42 2021-11-07T20:52:35 ACTIVE ENVIRONMENT Measures to achieve efficient raw material use false AIR SOIL WATER E_W_3 E_C_4 Reduced number of transfer and cleaning operations and/or dedicated storage tanks for raw materials, premixes and final products and/or residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into slurries true Reduced number of transfer and cleaning operations through e.g. manufacturing of different products from one premix (masterbatch), to which certain ingredients are added to yield the final products and/or Dedicated storage tanks for raw materials, premixes and final products and/or Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries Reduced number of transfer and cleaning operations through e.g. manufacturing of different products from one premix (masterbatch), to which certain ingredients are added to yield the final products and/or Dedicated storage tanks for raw materials, premixes and final products and/or Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries true Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling Residues of powder ingredients in cleaning steps at packaging or transfer line false Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process Reduced number of transfer and cleaning operations through e.g. Dedicated storage tanks for raw materials and final products and/or Recovery of materials through e.g. recycling residues of powder ingredients in cleaning steps at packaging or transfer line into the process true Closed batch process and/or batch production of final product and/or (Dry) cleaning procedures with maximization of waste reuse in the process and/or Reduced number of transfer and cleaning operations and/or Dedicated storage tanks and/or Spill protection false Closed batch process and/or batch production of final product and/or (Dry) cleaning procedures with maximization of waste reuse in the process and/or Reduced number of transfer and cleaning operations through e.g. manufacturing of different products from one premix, to which certain ingredients are added to yield the final products and/or Dedicated storage tanks for raw materials, premixes and final products and/or Spill protection including reuse of Spill Closed batch process and/or batch production of final product and/or (Dry) cleaning procedures with maximization of waste reuse in the process and/or Reduced number of transfer and cleaning operations through e.g. manufacturing of different products from one premix, to which certain ingredients are added to yield the final products and/or Dedicated storage tanks for raw materials, premixes and final products and/or Spill protection including reuse of Spill true Reduced number of transfer and cleaning operations through e.g. dedicated storage tanks for raw materials, premixes and final products and/or Spill protection including reuse of spill false Reduced number of transfer and cleaning operations through e.g. dedicated storage tanks for raw materials, premixes and final products and/or Spill protection including reuse of spill Reduced number of transfer and cleaning operations through e.g. dedicated storage tanks for raw materials, premixes and final products and/or Spill protection including reuse of spill true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2022-03-03T19:45:59 2022-03-03T19:48:28 ACTIVE ENVIRONMENT pH adjustment and/or precipitation e.g. by air flotation and/or filtration or other suitable techniques. Sites are operated to meet the local requirements for emissions of metals. false WATER E_W_3 E_C_4 RMM true pH adjustment and/or precipitation e.g. by air flotation and/or filtration or other suitable techniques. Sites are operated to meet the local requirements for emissions of metals. true WATER 95.0 95.0 99.0 cf. AISE Background document A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T20:01:26 2021-11-07T20:55:45 ACTIVE ENVIRONMENT Propellants of air care products or cleaning and maintenance sprays completely evaporate during application. false AIR E_W_6 E_C_4 ... true Propellants of air care products or cleaning and maintenance sprays completely evaporate during application. false A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2013-08-14T15:45:58 2015-02-05T11:06:56 ACTIVE ENVIRONMENT Type of process Type of process false AIR WATER E_W_3 E_C_4 Substance applied in aqueous process solution with negligible volatilization false ESCom-10133220222 true Granular detergents are obtained by drying liquid slurries. true ESCom-12355002149 true Spraying of involatile solids, which finally are disposed off via wastewater. false ESCom-12355002151 true Spray application with complete evaporation of volatiles false Spray application with complete evaporation of volatiles true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T20:19:55 2021-11-07T20:55:23 ACTIVE ENVIRONMENT Industrial applications of water borne processing aids or conversion coatings vary in daily consumption of application fluid, product concentrations and product dilutions. They can typically be described by the following conditions: false AIR SOIL WATER E_W_6 E_C_4 The application fluid is kept in a reservoir and/or The application fluid in the reservoir can be disposed of periodically and/or Closed system with regards to emissions to the environment and/or Optimized water use due to e.g.: Re-use of rinsing water true The application fluid is kept in a reservoir. The fluid is pumped to dedicated machine(s) in order to be applied to the substrate or it is kept in a treatment bath (e.g. vehicle cleaning, metal working fluids, etc.). With each piece of substrate a fraction of the application fluid is carried-over from the treatment bath. Via a sequence of rinsing steps this fraction of the application fluid is continuously emitted to the wastewater. The reservoir is continuously replenished; and/or The application fluid in the reservoir can be disposed of periodically: This may or may not involve on-site pre-treatment or disposal to the wastewater. As a result, constituents of the application fluid are removed during the on-site treatment according to the efficiency of the selected emission reduction. In addition, raw materials may be recovered. The choice of suitable emission reduction technology depends on the process; and/or Closed system with regards to emissions to the environment. Spent application fluid is not released to the environment. It is disposed of periodically as waste (with or without prior treatment). This type of application includes several surface finishing, water conditioning etc. applications. No emissions to the wastewater occur. The local waste handling regulations have to be followed. Additional instructions for handling waste may be included in the safety data sheet; and/or Optimized water use due to e.g.: Re-use of rinsing water The application fluid is kept in a reservoir and/or The application fluid in the reservoir can be disposed of periodically and/or Closed system with regards to emissions to the environment and/or Optimized water use due to e.g.: Re-use of rinsing water true Metal salts are dissolved in a water-borne application fluid, which is kept in a reservoir or treatment baths and/or Spray applications are housed-in for the sake of worker protection; and/or Optimized water use; and/or Periodically emptying and refilling false Metal salts are dissolved in a water-borne application fluid, which is kept in a reservoir or treatment baths. Metal fluids are continuously emitted to the wastewater via a sequence of rinsing steps. For details of OCs refer to background document”; and/or Spray applications are housed-in for the sake of worker protection; and/or Optimized water use due to e.g.: Re-use of rinsing water; and/or Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. Metal salts are dissolved in a water-borne application fluid, which is kept in a reservoir or treatment baths. Metal fluids are continuously emitted to the wastewater via a sequence of rinsing steps. For details of OCs refer to background document”; and/or Spray applications are housed-in for the sake of worker protection; and/or Optimized water use due to e.g.: Re-use of rinsing water; and/or Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2012-12-06T15:09:30 2015-02-05T11:10:39 ACTIVE ENVIRONMENT Process efficiency Process efficiency false WATER E_W_3 Optimized water use due to e.g. re-use of rinsing water true ESCom-11133171513 true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T20:57:30 2021-11-07T20:57:30 ACTIVE ENVIRONMENT - product Residues remaining on the substrate are likely to be washed off in the next cleaning event false WATER E_W_6 E_C_4 ... true product residues remaining on the substrate are likely to be washed off in the next cleaning event true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T19:58:18 2021-11-07T20:54:26 ACTIVE ENVIRONMENT Equipment cleaning with minimized emissions to wastewater may include: false WATER E_W_3 E_C_4 Dry cleaning of equipment, use of Central or Peripheral Vacuum Cleaning and/or cleaning involving so-called pigs in sub-processes involving liquid slurries and/or re-Use of process grey water for cleaning true Dry cleaning of equipment, use of Central or Peripheral Vacuum Cleaning and/or cleaning involving so-called pigs in sub-processes involving liquid slurries and/or re-Use of process grey water for cleaning Dry cleaning of equipment, use of Central or Peripheral Vacuum Cleaning and/or cleaning involving so-called pigs in sub-processes involving liquid slurries and/or re-Use of process grey water for cleaning true Manual removal of residual products adhering to equipment and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills false Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Use of adsorption pads to clean spills true Dry cleaning of equipment and/or Steam cleaning and/or cleaning involving so-called pigs and/or "Cleaning in place" CIP-System and/or Use of two-liner systems and/or Manual removal of residual products adhering to equipment and/or re-Use of grey water false Dry cleaning of equipment (Use of absorbent materials including incineration of resulting solid waste) and/or Steam cleaning and/or cleaning involving so-called pigs and/or "Cleaning in place" CIP-System and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or re-Use of process grey water for cleaning Dry cleaning of equipment (Use of absorbent materials including incineration of resulting solid waste) and/or Steam cleaning and/or cleaning involving so-called pigs and/or "Cleaning in place" CIP-System and/or Use of two-liner systems (i.e. single Use disposable reactor cover that is incinerated after Use as solid waste) and/or Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) and/or re-Use of process grey water for cleaning true (Dry) cleaning procedures with maximization of waste reuse in the process and/or Use of two-liner systems (i.e. single use disposable reactor cover that is incinerated after use as solid waste) and/or Manual removal of residual products false (Dry) cleaning procedures with maximization of waste reuse in the process and/or Use of two-liner systems (i.e. single use disposable reactor cover that is incinerated after use as solid waste) and/or Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) (Dry) cleaning procedures with maximization of waste reuse in the process and/or Use of two-liner systems (i.e. single use disposable reactor cover that is incinerated after use as solid waste) and/or Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) true Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 2015-03-16T16:40:11 ACTIVE ENVIRONMENT Application of the STP sludge on agricultural soil EUSES Determinant true WATER E_W_4 EUSES 2.1.2 Yes true false No false ESCom-11133170644 true Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 2015-03-16T16:40:11 ACTIVE ENVIRONMENT Place of use true AIR SOIL WATER E_W_6 E_C_4 Indoor false ESCom-9313213237 true Outdoor false ESCom-9313213238 true Indoor/Outdoor false ESCom-10133220202 true Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 2015-03-16T16:40:11 ACTIVE ENVIRONMENT Biological STP EUSES Determinant true WATER E_W_4 E_C_4 EUSES 2.1.2 Standard true ESCom-11133170613 true WATER 0.0 100.0 Site specific false ESCom-11133171638 true WATER 0.0 100.0 None false false WATER 0.0 0.0 0.0 Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 2015-03-16T16:40:11 ACTIVE ENVIRONMENT Discharge rate of STP EUSES Determinant true WATER E_W_4 EUSES 2.1.2 2000.0 0.0 >= ESCom-11133170818 ESCom-10133222104 true Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 2015-03-16T16:40:11 ACTIVE ENVIRONMENT Daily use amount at site ReleaseModule's Determinant true AIR SOIL WATER E_W_2 EUSES 2.1.2 0.0 <= ESCom-15193135620 ESCom-10076084403 true Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 2015-03-16T16:40:11 ACTIVE ENVIRONMENT Percentage of EU tonnage used at regional scale ReleaseModule's Determinant true AIR SOIL WATER E_W_2 E_C_2 EUSES 2.1.2 0.0 100.0 = ESCom-9269144102 false Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 2015-03-16T16:40:11 ACTIVE ENVIRONMENT Particular considerations on the waste treatment operations Specific 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. true WATER E_W_5 E_C_3 EUSES 2.1.2 No (no waste) false No waste generated. ESCom-11133170674 true No (low risk) false ERC 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-11133171479 true No (low amount) false Particular 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-11133171479 true No (low concentration) false Particular risks from waste treatment unlikely due low concentration of substance in waste stream. Waste disposal according to national/local legislation is sufficient. ESCom-11133171479 true No (other reason) false Waste disposal according to national/local legislation is sufficient. "Explanation for the CSR" to be reported by each registrant: ESCom-11133171479 true Dedicated recollection infrastructure required false ESCom-12355002107 true Biological treatment not appropriate false ESCom-12355002101 true Incineration not appropriate false ESCom-12355002100 true Prevent formation of hazardous break down products during thermal waste treatment destruction. false Prevent formation of hazardous break down products during thermal waste treatment. true Closed system required to minimise release to the environment. false Closed system required to minimise release to the environment during waste treatment. true Other false "Explanation for the CSR" to be reported by each registrant on the specific conditions required for waste treatment: true Chesar IUC5-97ce9eec-ebfd-4b2d-a61b-b9a975e920b5 ACTIVE ENVIRONMENT Water contact during use true WATER E_W_6 E_C_4 Yes false false No false ESCom-16354140700 true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2012-11-09T10:09:20 2015-02-05T10:59:20 ACTIVE ENVIRONMENT General good practice General good practice false AIR SOIL WATER E_W_6 Trained staff, spill protection including waste reuse true ESCom-12355002133 true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T19:51:55 2021-11-07T20:53:40 ACTIVE ENVIRONMENT Automation in raw materials handling (manual / automatic dosing) false AIR SOIL WATER E_W_3 E_C_4 Closed automated process for the transport and handling of raw materials and/or Closed transfer system and/or Centralized process control and/or Use of robotics technology true Closed automated process for the transport and handling of raw materials and/or Closed transfer system and/or Centralized process control and/or Use of robotics technology true Closed automated process for the transport and handling of raw materials and/or Closed transfer system and/or Centralized process control false Closed automated process for the transport and handling of raw materials and/or Closed transfer system and/or Centralized process control true Closed batch production process and/or Semi-Closed transfer system and/or Dedicated storage tanks for raw materials, premixes and final products and/or Use of robotics technology false Closed batch production process and/or Semi-Closed transfer system and/or Dedicated storage tanks for raw materials, premixes and final products and/or Use of robotics technology true Closed batch production process and/or Semi-Closed transfer system and/or Dedicated storage tanks for raw materials, premixes and final products false Closed batch production process and/or Semi-Closed transfer system and/or Dedicated storage tanks for raw materials, premixes and final products true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2012-12-20T10:56:25 2015-02-05T10:57:49 ACTIVE ENVIRONMENT Chemical waste - discontinuous generation Chemical waste - discontinuous generation false WATER E_W_6 E_C_4 Spent fluid discharged to wastewater. true Processing fluid can be kept in reservoir or treatment baths. Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. This may involve disposal to the wastewater. In some instances on-site pre-treatment (de-emulsification, pH-adjustment, and filtration) may be required. Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. ESCom-10133220218 true Spent process fluid to be disposed of as chemical waste false Processing fluid can be kept in reservoir or treatment baths. Periodically, the reservoirs are emptied of the spent reservoir fluid and refilled with fresh reservoir fluid. The spent reservoir fluid is treated as chemical waste.Operators minimize the frequency of exchanging the reservoir fluid to reduce the cost of process chemicals, waste treatment and equipment downtime. ESCom-12355002114 true Cosmetics Europe - The Personal Care Association IUC5-ded2fbb1-c0f4-41d1-8a52-b5d38cdb6ee0 2018-04-13T13:03:50 2018-04-20T11:02:09 OBSOLETE ENVIRONMENT Process efficiency Process efficiency false WATER E_W_3 Process optimized for efficient use of raw materials. false Typical measures may include e.g. - Closed batch systems and / or - Semi-closed transfer system and/or - Batch production of final product Reduced number of transfer and cleaning operations through e.g. - Dedicated storage tanks for raw materials, premixes and final products Process optimized for efficient use of raw materials. true Process optimized for highly efficient use of raw materials (II) false Typical measures may include e.g. - Closed automated process and/or - Closed transfer system and/or - Centralized process control and/or - re-use of process grey water for cleaning - optimized and/or automated systems for the transport and handling of raw materials, that minimize overall exposure levels and incidental spills - Reduced number of transfer and cleaning operations through e.g. - Manufacturing of different products from one premix (masterbatch), to which certain ingredients are added to yield the final products. - Dedicated storage tanks for raw materials, premixes and final products Recovery of materials through e.g. - Recycling Residues of granular detergents in cleaning steps at packaging or transfer lines into the slurries. Process optiomized for highly efficient use of raw materials. true Process with efficient use of raw materials. true Typically implemented measures for reducing emissions to waste water may include: - Closed batch systems Process with efficient use of raw materials. true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2021-11-07T20:50:19 2021-11-07T20:50:54 ACTIVE ENVIRONMENT Waste Handling and Disposal false AIR SOIL WATER E_W_5 E_C_3 Residues which cannot be recycled are disposed off as chemical waste and/or Spill protection including waste reuse true Residues which cannot be recycled are disposed off as chemical waste and/or Spill protection including waste reuse true What cannot be recycled into the process will become waste that needs to be disposed of. Liquid waste is typically directed to waste water, while solid waste can be treated as industrial waste and incinerated. and/or Spill protection including waste reuse false What cannot be recycled into the process will become waste that needs to be disposed of. Liquid waste is typically directed to waste water, while solid waste can be treated as industrial waste and incinerated. and/or Spill protection including waste reuse true Manual removal of residual products adhering to equipment (e.g. by scrubbing, vacuum cleaning, etc.) and/or Residues which cannot be recycled are disposed of as chemical waste false Manual removal of residual products adhering to equipment (e.g. by scrubbing, vacuum cleaning, etc.) and/or Residues which cannot be recycled are disposed of as chemical waste true Residues which cannot be recycled are disposed of as chemical waste which may be handled by an external third party false Residues which cannot be recycled are disposed of as chemical waste which may be handled by an external third party true Product residues are disposed with industrial waste. Empty large containments (e.g. IBC) are returned to the manufacturer. false Product residues are disposed with industrial waste. Empty large containments (e.g. IBC) are returned to the manufacturer. true Spill protection including waste reuse and/or the treatment of the spent process fluids by pH-adjustment and/or subsequent filtration/sedimentation results in slurries or solid waste which is treated off-site. false Spill protection including waste reuse and/or the treatment of the spent process fluids by pH-adjustment and/or subsequent filtration/sedimentation results in slurries or solid waste which is treated off-site. true product residues remaining in the product packaging are disposed of via domestic waste false product residues remaining in the product packaging are disposed of via domestic waste true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2013-08-14T15:45:58 2015-02-05T10:57:42 ACTIVE ENVIRONMENT Chemical waste - continuous generation Chemical waste - continuous generation false WATER E_W_6 E_C_4 Spent fluid discharged to wastewater. true ESCom-10133220218 true A.I.S.E. IUC5-8da076c6-3275-4851-a726-2586b783a7e8 2013-02-22T08:33:56 2015-02-05T10:58:06 ACTIVE ENVIRONMENT Equipment cleaning Equipment cleaning false WATER E_W_3 Equipment cleaning with minimized emissions to wastewater false Typically implemented measures for reducing emissions to waste water may include: - Dry cleaning of equipment (Use of absorbent materials and vacuum cleaning including incineration of resulting solid waste) - Cleaning involving so-called pigs - Cleaning involving so-called ""cleaning in place"" (CIP System) - Steam cleaning and/or - Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) - use of two-liner systems (i.e. single use disposable reactor cover that is incinerated after use as solid waste) ESCom-12355002119 true Equipment cleaning with reduced emissions to wastewater true Typically implemented measures for reducing emissions to waste water may include: - Manual removal of residual products adhering to equipment (e.g. by manual scrubbing, vacuum cleaning, etc.) - use of two-liner systems (i.e. single use disposable reactor cover that is incinerated after use as solid waste) ESCom-12355002120 true Equipment cleaned with water, washing disposed of with wastewater. false ESCom-12355002130 true Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries. false ESCom-12355002131 true Daily amount per site true true true Indoor or outdoor use false false false Spent process fluid discharged to wastewater for subsequent treatment. false false false Product applied in aqueous process solution with negligible volatilization. false false false Assumed domestic sewage treatment plant flow true true true Municipal sewage treatment plant is assumed. false false false No application of sewage sludge to soil false false false No waste from process false false false m3/day false false false Dispose of waste product or used containers according to local regulations. false false false Maximize waste water reuse. false false false Provide onsite wastewater treatment. false false false Incineration is not appropriate for waste. false false false Biological treatment is not appropriate for waste. false false false Dedicated recollection infrastructure required for waste false false false Residues which cannot be recycled are disposed off as chemical waste. false false false Equipment cleaning with minimised emissions to wastewater false false false Equipment cleaning with reduced emissions to wastewater false false false Equipment cleaned with water, washing disposed of with wastewater. Worst case assumption for solvent-borne products false false false Residues of granular detergents recovered in cleaning steps at packaging or transfer lines are recycled into the slurries. false false false Trained staff, spill protection including waste reuse false false false Granular detergents are obtained by drying liquid slurries. false false false Spraying of involatile solids, which finally are disposed off via wastewater. false false false tonnes/day false false false No water contact during use. false false false % false false false Indoor use false false false Outdoor use false false false