Em 4 de dezembro de 2017, a Consumer Product Safety Commission (CPSC) emitiu uma Direct Final Rule (16 CFR 1112 e 1250) por meio do Federal Register, 82 FR 57119, referente à adoção do padrão atualizado, ASTM F963-17 Standard Consumer Safety Specification for Toy Safety.
Em 24 de agosto de 2017, foi publicada uma nova versão do padrão de segurança para brinquedos, ASTM F963-17. Em 1º de setembro de 2017, a Consumer Product Safety Commission (CPSC) foi notificada pela ASTM sobre a publicação da norma atualizada. (Consulte test)
Recentemente, a CPSC emitiu a Direct Final Rule para confirmar a adoção do padrão atualizado com uma exceção. Um novo texto foi adicionado ao método de teste de brinquedos que produzem som na ASTM F963-17. No entanto, considerou-se que ele reduz a segurança porque o texto isenta os brinquedos de empurrar/puxar dos requisitos de nível de pressão sonora máxima ponderada A. Portanto, a CPSC determinou que essa disposição não deve fazer parte do padrão obrigatório da CPSC e que nenhuma isenção é permitida.
Enquanto isso, na regra, o 16 CFR 1112 foi alterado para incluir que as seções específicas da ASTM F963-17 devem ser submetidas a testes de terceiros e, portanto, a CPSC só aceita que organismos de avaliação de conformidade de terceiros credenciados testem essas seções. Além dessa emenda, o 16 CFR 1250 foi adicionado ao Código de Regulamentações Federais para abordar o fato de que os brinquedos devem estar em conformidade com as disposições da ASTM F963-17.
A data de vigência da regra final direta para adotar o padrão atualizado de segurança de brinquedos é 28 de fevereiro de 2018, a menos que comentários adversos significativos sejam recebidos até 3 de janeiro de 2018.
On October 25, 2017, the Environmental Protection Agency (EPA) issued a Direct Final Rule through the Federal Register, 82 FR 49287, regarding the update in voluntary consensus standards for formaldehyde emissions in composite wood.
In the rule, multiple consensus standards have been updated, superseded or withdrawn. The key updates are summarized below:
Consensus standard before updates | Consensus standard after updates | Changes |
ANSI/AITC A190.1-2002 American National Standard for Structural Glued Laminated Timber | ANSI A190.1-2017 Standard for Wood Products— Structural Glued Laminated Timber | Updated version |
ANSI A208.1-2009 American National Standard for Particleboard | ANSI A208.1-2016 American National Standard for Particleboard | Updated version |
ANSI A208.2-2009 American National Standard for Medium Density Fiberboard for Interior Applications | ANSI A208.2-2016 American National Standard for Medium Density Fiberboard for Interior Applications | Updated version |
ANSI-HPVA HP-1-2009 American National Standard for Hardwood and Decorative Plywood | ANSI-HPVA HP-1-2016 American National Standard for Hardwood and Decorative Plywood | Updated version |
ASTM D5055-05 Standard Specification for Establishing and Monitoring Structural Capacities of Prefabricated Wood I-Joists | ASTM D5055-16 Standard Specification for Establishing and Monitoring Structural Capacities of Prefabricated Wood I-Joists | Updated version |
ASTM D5456-06 Standard Specification for Evaluation of Structural Composite Lumber Products | ASTM D5456-14b Standard Specification for Evaluation of Structural Composite Lumber Products | Updated version |
ASTM D5582-00 Standard Test Method for Determining Formaldehyde Levels from Wood Products Using a Desiccator | ASTM D5582-14 Standard Test Method for Determining Formaldehyde Levels from Wood Products Using a Desiccator | Updated version |
ASTM D6007-02 Standard Test Method for Determining Formaldehyde Concentrations in Air from Wood Products Using a Small-Scale Chamber | ASTM D6007-14 Standard Test Method for Determining Formaldehyde Concentrations in Air from Wood Products Using a Small-Scale Chamber | Updated version |
ASTM E1333-10 Standard Test Method for Determining Formaldehyde Concentration in Air and Emission Rates from Wood Products Using a Large Chamber | ASTM E1333-14 Standard Test Method for Determining Formaldehyde Concentration in Air and Emission Rates from Wood Products Using a Large Chamber | Updated version |
BS EN 717-2: 1995 Wood-based panels—Determination of formaldehyde release—Part 2: Formaldehyde release by the gas analysis method | BS EN ISO 12460-3:2015 Wood-based panels—Determination of formaldehyde release. Part 3: Gas analysis method | Withdrawn, superseded by BS EN ISO 12460- 3:2015. |
BS EN 120: 1992 Wood-based panels. Determination of formaldehyde content—Extraction method called the perforator method | BS EN ISO 12460-5:2015 Wood-based panels—Determination of formaldehyde release. Part 5: Extraction method (called the perforator method) | Withdrawn, superseded by BS EN ISO 12460- 5:2015. |
JIS A1460:2001(E) Building boards-determination of formaldehyde emission—Desiccator method | JIS A1460:2015 Determination of the emission of formaldehyde from building boards—Desiccator method | Updated version |
PS-1-07 Structural Plywood | PS-1-09 Structural Plywood | Updated version |
PS-2-04 Performance Standard for Wood-Based Structural-Use Panels | PS-2-10 Performance Standard for Wood-Based Structural-Use Panels | Updated version |
The final rule became effective on December 11, 2017.
On November 2, 2017, US Senator Merkley introduced Senate Bill No. S.2072, the Alan Reinstein Ban Asbestos Now Act of 2017. The bill proposes prohibitions on the manufacture, processing, use, distribution and disposal of asbestos and articles containing asbestos under the Toxic Substances Control Act (TSCA).
In the proposed bill, no person shall manufacture, process, use, distribute or dispose of any form of asbestos or article containing asbestos. This would be effective no later than 18 months after the enactment of the bill. However, exemptions can be granted if it meets the following requirements:
The use of asbestos is necessary to protect national security interests
No reasonable alternative to the use of asbestos exists for the intended purpose
The use of asbestos will not result in an unreasonable risk to health or the environment
Recently, the California Office of Environmental Health Hazard Assessment (OEHHA) added certain chemicals to the Proposition 65 List. The new chemicals are as follows:
The added chemicals meet the requirements for listing purposes of Proposition 65 as known to the State of California to cause Cancer toxicity. The chemical details are provided below:
Date of addition | Chemical | Chemical Abstracts Service Number (CAS No.) | Types of Toxicity |
July 7, 2017 | Glyphosate | 1071-83-6 | Cancer |
Pentabromodiphenyl ether mixture [DE-71 (technical grade)] | --- | Cancer | |
October 27, 2017 | N,N-Dimethylformamide | 68-12-2 | Cancer |
2-Mercaptobenzothiazole | 149-30-4 | Cancer | |
Tetrabromobisphenol A | 79-94-7 | Cancer | |
November 10, 2017 | Perfluorooctane sulfonate (PFOS) | 1763-23-1 | Developmental |
Perfluorooctanoic acid (PFOA) | 335-67-1 | Developmental | |
December 15, 2017 | Chlorpyrifos | 2921-88-2 | Developmental |
n-Hexane | 110-54-3 | Male Reproductive Toxicity |
In November 2017, the California Department of Toxic Substances Control (DTSC) proposed amendment on California Code of Regulations to list paint or varnish strippers containing methylene chloride as priority products to be regulated under the Safer Consumer Products (SCP) Regulations (See test).
In the proposed amendment, paint or varnish stripper is defined as any product designed to break down paint, varnish or any other surface coating to facilitate its removal from any surface. It applies to products for both indoor or outdoor use.
Upon approval, manufacturers of paint or varnish stripper containing methylene chloride are required to notify the DTSC within 60 days.
On November 3, 2017, the proposal, Ordinance No. 211-17, to amend Environment Code - Flame Retardant Chemicals in Upholstered Furniture and Juvenile Products, was approved by the Mayor of San Francisco.
The approved amendment revises the existing law to restrict flame retardants at a level above 1000 ppm in upholstered furniture, reupholstered furniture and juvenile products. The flame retardant chemicals include, but are not limited to, halogenated, phosphorous based, nitrogen based, and nanoscale flame retardants.
The implementation of the new restriction begins January 1, 2019. Meanwhile, if the product contains electrical or electronic components, the implementation will begin July 1, 2019.
On October 23, 2017, the County Executive approved the amendment Resolution No. 884-2017 to amend the Toxic Free Toys Act. Since the Legislature finds that the County has encountered problems in implementing the Act, the amendment aims to correct the problem and ensure that testing is done accurately and effectively.
The key amendments are summarized below:
Removed Cobalt from the toxic heavy metal content restriction and updated the concentration limits as below:
| Before amendment | After amendment |
Mercury | 40 ppm | 60 ppm |
Antimony | 40 ppm | 60 ppm |
Arsenic | 40 ppm | 25 ppm |
Cobalt | 40 ppm | - |
Clarified the scope of cadmium restriction applies to accessible content
Removed preemption to Federal legislation and required the County to automatically incorporate any additional metals restriction levels under Federal law on children’s products in the future
Clarified the testing procedures in random inspections of retailers of children’s products
The amendment became effective on November 1, 2017.
Em novembro de 2017, entrou em vigor o padrão atualizado de segurança de bens de consumo (óculos de sol e óculos de moda) de 2017. A norma de segurança atualizada adotou uma nova versão da AS/NZS 1067.1, substituindo a Norma de Segurança de Produtos de Consumo anterior: Sunglasses and Fashion Spectacles (Óculos de sol e óculos da moda).
Na norma de segurança atualizada, foi adotada uma nova versão da norma australiana/neozelandesa AS/NZS 1067.1:2016 Eye and Face Protection - Sunglasses and Fashion Spectacles, com exceção de algumas cláusulas. O período de transição da norma de segurança foi concedido até 1º de julho de 2019. Até 1º de julho de 2019, os óculos de sol e de moda podem estar em conformidade com a versão antiga (2003) ou com a nova versão (2016) da AS/NZS 1067.1.
Em novembro de 2017, entrou em vigor o padrão atualizado de segurança de bens de consumo (auxiliares de banho para bebês) de 2017. O novo padrão de segurança atualizou os requisitos e adotou parcialmente o padrão dos EUA, ASTM F1967-13 Standard Consumer Safety Specification for Infant Bath Seats.
No padrão de segurança atualizado, os produtos para banho de bebês e qualquer embalagem devem atender aos requisitos de conteúdo da declaração de advertência. Um exemplo é fornecido abaixo:
Além dos requisitos de conteúdo de advertência, a declaração de advertência deve ser fixada permanentemente, verificada por meio da subcláusula específica da ASTM F1967-13, no produto e localizada em um local bem visível.
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