Following its quarterly Guide to Greener Electronics, Greenpeace invited electronics manufacturers in 2008 to submit their most environmentally friendly products/models for evaluation, surveying the most environmentally friendly products on the market and publishing the results in December 2008. This survey, titled "Green Electronic…The search continues," included 15 participating manufacturers: Acer, Dell, Fujitsu Siemens, Hewlett Packard, Lenovo, LG Electronics, Motorola, Nokia, Panasonic, RIM/Blackberry, Sharp, Samsung, Sony, Sony Ericsson, and Toshiba. These 15 manufacturers submitted 50 products for Greenpeace to evaluate. The evaluation criteria were divided into four main categories: 1. Use of hazardous chemical substances: Hazardous substances included PVC, brominated flame retardants (BRFs), antimony, and phthalates.

To accelerate energy conservation and carbon reduction, gradually phase out incandescent lamps, and expedite the promotion of energy-saving lamps, the National Development and Reform Commission (NDRC), in cooperation with the United Nations Development Programme (UNDP) and the Global Environment Facility (GEF), has launched the "China's Phasing Out of Incandescent Lamps and Accelerating the Promotion of Energy-Saving Lamps" project, supporting the research and development of the "Action Plan for China's Phasing Out of Incandescent Lamps and Accelerating the Promotion of Energy-Saving Lamps." Currently, related research has begun. China is a major producer and consumer of lighting products. In 2007, China produced 4.44 billion incandescent lamps, accounting for one-third of the world's production, with 2.98 billion exported; and produced 3 billion compact fluorescent lamps, accounting for 80% of the world's production, with 2.2 billion exported. Lighting accounts for approximately 12% of China's total electricity consumption. Replacing incandescent lamps with energy-saving lamps can save 60% to 80% of electricity. If all existing incandescent lamps were replaced with energy-saving lamps, 48 ​​billion kilowatt-hours of electricity could be saved annually, representing a huge potential and an important way to achieve energy conservation and carbon reduction goals. – Reference source: Hong Kong Trade Development Council (HKTDC) 2009-02-01

Chapter 108 of the U.S. Consumer Product Safety Improvement Act (CPSIA) restricts the levels of phthalates in children's toys and child care products. Three phthalates (DEHP, DBP, and BBP) are permanently banned, and their permitted concentration in children's toys and child care products is 0.1%. The other three temporarily banned substances, DINP, DIDP, and DnOP, must not exceed 0.1% in "children's toys that can be put in a child's mouth" and "child care products." This ban took effect on February 10, 2009. Definitions such as "children's toys," "children's toys that can be put in a child's mouth," and "child care products" are detailed in Chapter 108. It is important to note that these definitions apply only to Chapter 108 of the CPSIA. The U.S. Consumer Product Safety Commission (CPSC) has received numerous inquiries from manufacturers potentially affected by the act; therefore, the Commission is currently developing guidelines for manufacturers to determine whether their products must comply with the requirements of the act. Currently, it is known that products already regulated by other federal agencies, such as food, cosmetics, and medical devices, generally do not fall under the category of "consumer products." However, items like baby pacifiers and cups are subject to the jurisdiction of both the CPSC and the FDA (Food and Drug Administration). The FDA regulates additives that are indirectly added to food, such as those that may be released from the container.

According to the manufacturer registration fee schedule published by NERIC (National Electronics Recycling Infrastructure Clearinghouse) (see table below), in 2009, manufacturers of electronic products subject to mandatory recycling in the United States were required to pay at least $50,000 annually in registration fees for nationwide product recycling, depending on the state. Several U.S. states have implemented mandatory electronic recycling programs, and the administrative costs of these programs are covered by registration fees levied on electronic product manufacturers. Maryland and West Virginia use these funds to subsidize local electronic waste collection and recycling, while other states typically use them to pay employee salaries, extend services, and for implementation. State Name | Manufacturer Registration Fee California | None Connecticut | To be determined Hawaii | $5,000 Illinois | $5,000 Maine | None Maryland | $5,000

Washington state is considering legislation to ban the manufacture, sale, and distribution of water bottles, children's water bottles, cups, and other containers containing bisphenol A (BPA), effective July 1, 2010. If passed, the ban would cover: BPA is used to manufacture epoxy resins and polycarbonate plastics, and is a major component of hard polycarbonate plastics. Polycarbonate plastics are used in various food and beverage packaging products, while epoxy resins are commonly used as a clear coating for metal products. BPA is also used in various children's products, such as toys, pacifiers, bottles, and teethers; however, due to increasing public concern, many manufacturers have voluntarily phased out the use of BPA in their products. Several U.S. states and cities have attempted to ban the use of BPA in children's products, but failed, including San Francisco and California. The Consumer Product Safety Enhancement Act prohibits the use of certain phthalates, but does not restrict BPA. At the federal level, the U.S. Food and Drug Administration (FDA) is reviewing data on all products regulated by the agency, including those known to contain bisphenol A (BPA). The Obama administration is expected to take a more proactive approach to the BPA issue, and future federal regulations on this chemical may become even stricter. – Reference source:

In accordance with the requirements of the EU WEEE Directive, EU member states must convert the WEEE Directive into the domestic laws of each member state. The British government submitted its domestic WEEE regulations (SI 2006 No. 3289) to Parliament on December 12, 2006, and submitted it to Parliament in January 2007. Effective on March 2nd. Before the British WEEE regulations are about to enter into force for the fourth year (January 1st to December 31st, 2010), the British government conducted an impact assessment (Impact Assessment) on its domestic WEEE implementation status and implementation experience, and announced the upcoming regulations. Draft regulations are available for public consultation. The deadline for this public consultation is April 6, 2009. The British government recently announced a report titled “The Waste Electrical and Electronic Equipment Regulations: Government consultation on new regulations and further development of the supporting infrastructure to take effect from the fourth compliance period (1 January – 31 December

Companies that have obtained FSC-mixed certification and use controlled timber will find that since the FSC organization implemented the FSC-STD-40-005 V2 standard (Company Assessment Standard for FSC Controlled Timber) on January 1, 2007, the requirements for controlling FSC-controlled timber have become increasingly detailed and stringent. Many companies feel that the new standard adds significantly more content than FSC-STD-40-005 V1 in implementing controlled timber management. Some companies even believe that controlling timber management is impossible for some domestic timber processors to fully implement, especially in the risk assessment stage. However, it is important to note that if a company purchases controlled timber but neglects certain requirements during the risk assessment process, the purchased materials may not be usable in the production of FSC-mixed products, or the produced products may not be able to be sold as FSC-certified products. The resulting economic losses could be substantial. Therefore, we should spend more time conducting risk assessments for controlled timber. FSC-controlled timber should avoid the following five sources: FSC-STD-40-005 V2 provides two methods for sourcing controlled timber. The first is to purchase raw materials from suppliers who have obtained FSC-controlled timber sales qualifications. The second is for the company to conduct its own FSC-controlled timber assessment process and purchase raw materials from non-certified suppliers. The first method is the simplest, but currently only two companies in China have obtained FSC certification.

The "European Union Regulations on the Registration, Evaluation, Authorization and Restriction of Chemicals" (REACH) is called "the most complex foreign technical barrier with the widest impact that China has ever encountered". The scope and extent of its impact can be imagined Know. The impact of REACH on different manufacturing industries can be easily found in various media and professional journals, which is very helpful for manufacturing companies. So, does REACH only affect product manufacturers? Does REACH have any direct requirements for dealers who export to the EU? Will it have an impact? What are the impacts? What needs to be done to ensure normal trade? These will be the main focus of this article, and they are also issues that European dealers must pay attention to. 1. Distributors and export trade categories The REACH regulations clearly define "distributors", which refer to natural or legal persons in the EU who only store substances or place substances on the market for third parties, including retailers. Distributors within the scope of this definition obviously refer to companies established in the EU that are engaged in product storage or sales. Domestic distributors do not fall into the category of EU distributors. The dealers considered in this article are enterprises that only engage in import and export trade and do not produce themselves, especially those that export to the EU. If a dealer is producing at the same time, he is actually a "non-EU manufacturer" within the scope of REACH, and the terms of "non-EU manufacturer" apply, which is beyond the scope of this article. Judging from the registered address and scope of operations, distribution

7.1 Planning of Hazardous Substance Reduction Processes and Product Realization The requirements of ISO 9001 shall be used in conjunction with the following requirements. The organization shall plan and develop processes for the realization of hazardous substances-reduced products. In planning the realization of hazardous substances-reduced products, the organization shall, where appropriate, determine the following: a) Quality objectives and requirements for the hazardous substances-reduced product; b) The need to establish hazardous substances reduction processes, documentation, and resources for the hazardous substances-reduced product; c) The verification, validation, monitoring, inspection, and testing activities required for the hazardous substances-reduced product, and the acceptance criteria for the product. Where appropriate, information service providers shall be included; d) Procedure documents or work instructions for processes using restricted substances, so as to include preventative measures in the presence of contamination; e) Evidence required to demonstrate that the hazardous substances reduction realization process and the resulting product meet the requirements; f) The output of the hazardous substances reduction planning shall be in a form suitable to the organization's operating methods. Note 1: Documents used to determine the hazardous substances reduction process (including product realization process) and resources for a product may be called a quality plan. c. On-site audits; d. Random spot checks (the frequency and sampling plan are determined based on risk analysis); e. Management of samples sent by customers. Product realization refers to all processes involved in creating a product. Essentially, it's the process from customer needs to mass production of a product. This differs from product design and development, which involves translating regulatory, technical, safety, functional, market, or other product requirements into technical specifications.

1. Some companies believe that as long as a test report shows the content of heavy metals such as lead, cadmium, mercury, and hexavalent metals, it can be used to determine the RoHS compliance of materials. For example, some companies use test reports collected regarding the European EN71-3 toy safety standard to determine RoHS compliance. Is this acceptable? Answer: No. EN71-3-9 specifies the "leaching amount" under certain environmental conditions, while RoHS specifies the "content" of materials. The sample preparation methods for the two tests are different, and the results may differ greatly. Test data cannot be substituted for each other. 2. The purchased parts contain multiple colors, but the test report only shows the content of hazardous substances in one color. Can such a report be used to determine the RoHS compliance of materials? Answer: No. 3. When there is only a test result for a single homogeneous material in an assembly, can it be used to determine the RoHS compliance of the entire assembly? Answer: No. It can only prove that this one product is compliant. 4. For processes that may involve contamination, switching cleaning methods are usually used to prevent cross-contamination, but their effectiveness is difficult to verify. What are some reference suggestions (or experiences) for practice? A: The cleaning and verification methods should be determined based on the level of pollution risk. Evidence of cleaning capability can be considered from several aspects: 5. For factories that have completed RoHS switching, all products need to meet RoHS requirements. In this case, is labeling a key control item? A: 6. How to verify the materials provided by the supplier?