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REGULATIONS OF DIFFERENT     COUNTRIES

 

 

 

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Coalition of Northeastern Governors (CONEG)

 

Created in 1976, the Coalition of Northeastern Governors (CONEG) is a non-partisan association of the Governors of eight Northeastern states. Members include the Governors of Connecticut, Maine, Massachusetts, New Hampshire, New Jersey, New York, Rhode Island and Vermont.

CONEG encourages intergovernmental cooperation in the Northeast on shared issues relating to the economic, environmental and social well-being of the Northeast states. The Governors identify priority interests in transportation and the economy, environment and energy which set the framework for CONEG's agenda. Working through CONEG, the Governors share information and experiences on common interests and, where appropriate, forge agreements and undertake cooperative actions on a wide range of regional and state-federal issues.

CONEG works with the states to identify regional issues and provide a forum for discussion and exchange of information about issues of shared interest. CONEG tracks selected national and regional issues, assesses their implications for the Northeast, conducts policy studies and seminars, and helps coordinate the region's response. In this manner, it also provides an ongoing, informational exchange through which the Governors and their senior advisors keep abreast of national and regional policy and program initiatives important to the economic, environmental, energy and social well-being of the region.

The Governors established the CONEG Policy Research Center, Inc. (Center), an incorporated 501(c)(3) non-profit organization, as the staff arm of CONEG.

 

The Toxics in Packaging Clearinghouse (TPCH) was formed in 1992 to promote the Model Toxics in Packaging Legislation.  This model legislation was originally drafted by the Source Reduction Council of CONEG in 1989. It was developed in an effort to reduce the amount of heavy metals in packaging and packaging components that are sold or distributed throughout the United States.

 

Specifically, the law is designed to phase out the use and presence of mercury, lead, cadmium and hexavalent chromium in packaging within four years in states that enact the legislation.

 

Since packaging comprises approximately one-third of the waste stream, it is hoped that this legislation will curb the amount of heavy metals entering the municipal solid waste stream and, ultimately, landfills and incinerators.  A reduced contribution of these metals to the waste stream will gradually lower their harmful presence in the environment. 

The Clearinghouse includes a states-only voting membership and an industry/public interest advisory group. The legislation has been successfully adopted by nineteen states: California, Connecticut, Florida, Georgia, Illinois, Iowa, Maryland, Maine, Minnesota, Missouri, New Hampshire, New Jersey, New York, Pennsylvania, Rhode Island, Vermont, Virginia, Washington and Wisconsin. Other states, as well as the U.S. Congress, have also considered the legislation.

The Toxics in Packaging Clearingouse (TPCH) is now located at the Northeast Recycling Council, Inc. (NERC) in Brattleboro, Vermont. NERC performs all administrative functions of the Clearinghouse on behalf of member states.

 

 

Requirements of the “Toxics in Packaging Clearinghouse (TPCH)”

 

Toxic Elements of packaging materials: Total contents of Cadmium / Lead / Mercury / Chromium (VI) of packaging materials – individual limit / accumulative limit = 100 mg/kg

 

Packaging materials should comply with the following requirements:

 

                                                                                        Limit for individual element

Lead (Pb)                          100 mg/kg

                                                Cadmium (Cd)                   100 mg/kg

                                                Mercury (Hg)                     100 mg/kg

                                                Chromium VI (Cr VI)           100 mg/kg

                                                _______________________________

Accumulative limit of Pb + Cd + Hg + Cr VI          100 mg/kg

 

 

Environmental Pollution

 

The toxic elements Cadmium / Lead / Mercury / Chromium (VI) can be released from waste hauling, disposal activities and manufacturing process. Higher levels of these toxic elements may be found in soil or water near industrial areas or hazardous waste sites, posing health hazards to human beings through the food chain. The main objective of the regulation is to protect the environment and safeguard public health.

 

 

Frequently asked questions

 

Certificates of Compliance

 

Q: Is the supplier of a package or package component required under the law to certify to the purchaser that the four (4) heavy metals were not intentionally added during the manufacturing process or must the supplier also certify that the package or component was tested and falls at or under the parts-per-million threshold set in the law?

 

A:  The certification would require the following: The actual certificate stating that the four heavy metals were neither intentionally introduced nor are incidentally present in excess of the allowable maximum concentrations.

The state agencies responsible for enforcing this law will assume, when receiving a Certificate of Compliance consistent with the Toxics in Packaging Legislation, that the company has done what is reasonably necessary to stand behind its certification.  In cases where the company has existing documentation to verify that each package complies, further testing will not be necessary and that documentation may be substituted for actual test results.  A certification prepared without testing should be based on verifiable evidence that there has been "no intentional addition." However, for those companies that cannot document the amount of heavy metals in their package or packaging components, or know them to be present as incidental trace contaminants, a certain level of testing will be necessary. The test method chosen and its lower detection limit are at the discretion of the company and may vary from company to company and from package type to package type, provided that the test is capable of conclusively proving that the total of the four regulated metals is below regulatory limits. It is not expected that each and every package will be individually tested, although that is certainly the company's option. Instead, random sampling on a reasonable statistical basis is considered to be a sufficient level of testing to comply with the legislative requirements.

 

Q: Can a manufacturer or supplier use one Certificate of Compliance for all of its packages or packaging components, or is a separate Certificate of Compliance necessary for each type?

 

A: Packages and packaging components that use the same materials and differ only in size, shape and/or use can be included in the same Certificate of Compliance.

 

Q: How long are companies required to keep on file documentation such as Certificates of Compliance and laboratory test results?

 

A: The Model Legislation requires that the Certificate of Compliance shall be retained “for as long as the package or packaging component is in use.” Laboratory test results that support the certification should be retained as well. Although some state laws differ, it is recommended that documentation of compliance with toxics in packaging requirements be kept on file by the product manufacturer and supplier of the package or packaging component for 3 years after the package is sold, distributed, or in use by the purchaser. If the package holds a product for retail sale, it is recommended that documentation be kept on file until the product is no longer distributed or sold by retailers, even if product manufacturing has been discontinued. If the package or packaging component design, formulation or supplier changes, the Certificate of Compliance and supporting documentation must be updated by the manufacturer or distributor of the packaging component.

 

Q: What authority does the TPCH have in requesting Certificates of Compliance and test reports to prove packages are compliant with the state toxics in packaging laws?

 

A: The Toxics in Packaging Clearinghouse (TPCH) requests Certificates of Compliance from manufacturers and distributors of packaging, packaging components or packaged products on behalf of its member states. The authority of individual states to request such information can be found in the legislation and/or regulations of each state. One of the roles of the TPCH is to reduce the paperwork burden for both states and the regulated community by providing a single point of contact for such requests. If manufacturers or distributors do not respond to the TPCH request, the matter is referred to individual states for follow up action.

 

Q: What is the consequence or penalty if a company fails to present a Certificate of Compliance or supporting documentation such as actual test reports?

 

A: Enforcement is at the discretion of individual states and subject to the provisions of their statutes. Most states have penalties associated with making or submitting false or misleading statements or certificates of compliance.
Test reports are generally not required, however, if a complaint is received or if screening tests indicate a potential problem, then test reports may be required to confirm the basis for the Certificate of Compliance.

 

Enforcement

 

Q: How is enforcement coordinated by the states?

 

A: Enforcement is on a state-by-state basis.  However, the states have established the Clearinghouse for the purpose of leading a coordinated effort on implementation and enforcement of the toxics in packaging legislation.

 

Exemptions - General

 

Q: Which exemptions require petitioning to the States and which are automatic, simply requiring mention in the Certificate of Compliance?

 

A: The exemption for package and packaging components involving use of recycled material or date of manufacture prior to the effective date of the legislation do not require petitions, but must be cited in the Certificate of Compliance and must be verifiable. All other exemptions require a petition and must include supporting documentation.

 

Exemptions – Effective Date

 

Q: Is packaging manufactured before the effective date exempt even if it is sold after the effective date?

 

A: Yes. If the package has a date of manufacture or the producing company can provide documentation that the package in question was manufactured prior to the effective date, or was in the process of being manufactured prior to the effective date, it is exempt. Situations that are beyond the control of the manufacturer -- e.g., old stock being held by retailers -- should be dealt with on a case-by-case basis by the States. In all cases, packaging that was manufactured after the effective date must be in compliance or else it cannot be sold or distributed in that State. Packaging that does not bear a date of manufacture on its label, and would be considered out of compliance due to its regulated metals content, may be sold only if the manufacturer can supply other supporting documentation to the State that it was manufactured prior to the effective date.

 

Exemptions – Recycled Content  

 

Q: What is meant by the term "recycled materials" as used in Section 5, paragraph c?

 

A: Recycled materials are those materials generated by a business or a consumer that have been separated from solid waste for the purpose of recycling as a secondary material feedstock. For purposes of this legislation, recycled materials include paper, plastic, wood, glass or ceramics, metals such as steel, aluminum, stainless steel or copper, and other materials. However, recycled materials under the toxics in packaging law do not include the four regulated metals (lead, cadmium, hexavalent chromium and mercury) when the metals have been separated into their elemental or other chemical state for recycling as a secondary material feedstock. For example, lead processed from used automotive batteries and intentionally added as a component to manufacture an ink pigment that is then used to print labels on packaging would not be a "recycled" material for the purposes of Section 5 paragraph c. 

 

Q: Would a package or package component be exempt from the law if it were made wholly or in part from post-industrial waste (e.g., metal scrap purchased from automobile manufacturing plants that was subsequently made into cans or other packaging components)?

 

A: Yes. The exemption applies to both post-consumer and post-industrial waste. This example illustrates post-industrial waste. It should be noted that packages or packaging components manufactured from non-packaging post-consumer materials (e.g., used appliances and automobiles made into cans) would also be eligible for this exemption.

 

Q: Would lead chromate pigment be exempt if it were made from post-consumer recycled materials, such as scrap automobile batteries?

 

A: No. The exemption applies only to recycled composite materials such as plastic or paper, which might coincidentally contain a regulated metal but are being reprocessed for their primary material content, and not to the four regulated metals or their compounds that have been separated or isolated from recycled materials. This includes pigments.

 

Q: If a regulated metal were deliberately added to a package otherwise made of totally recycled material, for example a cadmium pigment added to change the color of a pail made of recycled plastic, would the package be exempt based on recycled content?

 

A: No. The intentional addition of a regulated metal to change the appearance or characteristics of a final package is not permitted, regardless of the source of starting material used to manufacture the package, unless the package qualifies under the "reuse" exemption whereby each individual package is reused many times and its distribution and retrieval are closely controlled and documented throughout its lifetime. To qualify for the recycling exemption, the regulated metal in question must have been present as a minor ingredient in the discarded waste material before that waste material was designated for recycling. 

 

Q: For the recycled content exemption, does the exemption/definition apply to the complete package, or only that portion of the package that is made from post- consumer recycled material?

 

A: The model legislation language differentiated between the package and packaging components; therefore, the exemption could apply to either or both. For a package where all components contain post consumer recycled content that exceeds the compliance level, the entire package is exempt. However, in the case where one packaging component contains post consumer recycled content and the other components do not, only the component containing post consumer recycled content would be exempt and not the entire package.

 

Exemptions – Vitrified Labels

 

Q: Are ceramic enamels or decals that have been vitrified, such that they become part of the glass or ceramic matrix, subject to the toxics in packaging requirements?

 

A: Glass and ceramic containers with vitrified labels or decorations that can pass the leachability test specified in the law are exempt from the restriction on “intentional use” of the regulated metals.  The exemption applies when the sample is prepared according to ASTM C1606-04 and tested in accordance with the Toxicity Characteristic Leaching Procedures of US EPA Test Method and publication SW 846, 3rd edition, Test Methods for Evaluating Solid Waste, and does not exceed 1.0 ppm for cadmium, 5.0 ppm for hexavalent chromium and 5.0 ppm for lead. Mercury is not exempt.

It has been demonstrated that ceramic and/or glass packaging having non-vitrified surface glazes, paint or enamels containing lead or cadmium may release these regulated metals upon being discarded, even where they appear to be stable under normal conditions of use, at or around room temperature. The metals may volatilize during high-temperature incineration or solubilize after landfilling (including the landfilling of incinerator ash). It has been shown that vitrification of the label before use generally prevents this release from occurring.

 

Imports

 

Q: What about packaging, including cans or other containers imported from outside the United States?

 

A:  All packaging, including cans or other containers, imported from outside the country into states that have passed the legislation must be in full compliance with the limits on the regulated metals. It should be further noted that on June 21, 1993 the Food and Drug Administration announced that it was promulgating regulations to ban the use of lead solder in food cans sold anywhere within the United States. This regulation applies equally to imported cans that might still contain lead solder as well as domestically produced cans. It is the responsibility of the importer to test or otherwise ensure that any such cans proposed to be brought anywhere into the United States have not been fabricated with lead-containing solder.

 

Q: How are importers subject to the state toxics in packaging laws?

 

A: Packaging, packaging components or products in packaging are subject to toxic in packaging laws upon entering any state with toxics in packaging legislation. If a company imports packaging, packaging components or a product in a package directly into a state with legislation, then the state has authority to request a Certificate of Compliance from the importer. If, however, the packaging, packaging components or packaged products are imported into a state without legislation by Company A and ownership is transferred to Company B, who subsequently distributes such packaging into a state with legislation, it is the responsibility of Company A to provide a Certificate of Compliance to Company B since the Model Legislation and state laws require manufacturers or suppliers to provide a Certificate of Compliance to its purchaser. An importer is considered a supplier to its purchaser.

 

Packaging - Clarifications

 

Q: Are mugs, steins, tumblers, vases and similar items subject to the law when holding candy, beverages, flowers or other products?

 

A: In cases where the items are manufactured as products (e.g., decorative mugs) and only incidentally hold other items during final distribution to the end user, the product is not considered a package. One or more of the following would have to apply.  The items: are not designed solely to contain and protect the goods inside for transport and handling during distribution; have intrinsic value as an artistic or useful object in themselves which is often reflected in the selling price if sold; and are intended to be retained beyond the life of the item inside and not promptly discarded after the contents have been consumed or used.

In cases where the item is used solely to deliver another product (e.g., a beverage sold at a food counter), the item is considered a package. An exemption for “controlled distribution and reuse” may apply if the item is not normally discarded after the product inside has been consumed.  Further, a container sold without being filled with a product, such as an empty coffee cup or empty decanter for home use, is a product itself and not subject to the law.

 

Q: Does the law apply to gift-wrapping paper (and related items) -- items purchased solely for the use of individual consumers to wrap presents in the home, or to be attached to those presents?

 

A: No. Wrapping paper, ribbons or tape, items attached to a product and related items are products, not packages, if sold to the consumer for home use and as such are not subject to the law. Packages that are sold to the consumer as "gift-wrapped" items would be subject to the law. Promotional items such as candy or toys that are attached externally to "gift-wrapped" packages are not considered part of the package and are not subject to the law (except, of course, for any additional packaging which might surround those items themselves).

 

Q: Are envelopes used by a business considered to be a "package" under the law?

 

A: Yes. The definition of a package in the law under ASTM D-996 includes the term "envelope" (85a, page 222, ASTM D-996). This would include envelopes or shipping cartons supplied by Federal or Airborne Express, U.P.S. and others. It is recommended that users of such packaging ask their respective express carrier agencies for Certificates of Compliance.

 

Q: Does the law apply to "country of origin" stickers which are required by US Federal law (19 CFR 134) on all products manufactured or assembled outside the US?

 

A: No. These stickers are not considered packaging for the purpose of this legislation.   

 

Q: Does the law apply to stickers, labels, tags or protective films which are: 1) not required by Federal law; 2) affixed directly to the product; 3) not required to remain affixed for proper or safe functioning or use of the product? 

 

A: Yes.  These stickers, labels, tags and protective films are considered packaging under this legislation.

 

Q: Does the law apply to all such cans, regardless of size or use?

 

A: Yes. The definition of a package under the law includes all steel cans and, therefore, the law applies regardless of size or use.

 

Q: Are railroad tank or box cars, refillable propane tanks, chlorine cylinders, bulk tank trucks/trailers and shipping containers considered packages under the legislation?

 

A: Railroad tank or box cars and bulk tank trucks/trailers are not packages, while refillable propane tanks, chlorine cylinders and shipping containers are considered packages under the legislation. These distinctions are based on the definition of "package" in the law under ASTM D 996.

 

Restrictions on the Use of Heavy Metals

 

Q: May a manufacturer sell a package or packaging component that has 100 parts per million or less of the regulated metal that resulted from deliberate addition during the manufacturing process, with the knowledge and intent that its presence would change the appearance or characteristics of the final package or packaging component?

 

A: No. The intent of the law is to prohibit any intentional addition of the four heavy metals in packaging, even if the concentration levels are below the threshold for incidental amounts.

 

Q: In a situation where one or more of the heavy metals were used in the manufacturing process but were not intended to be part of the final package (i.e., used as a cleaning or oxidizing agent), would the package be in compliance with the law if it contained trace amounts of heavy metal below 100 parts per million?

 

A: Yes. The package would be in compliance since the regulated heavy metal was used only to aid in a step of the manufacturing process, and any residual metal would be incidentally present if it is neither desired in, nor its continued presence imparts any desirable characteristic or appearance to, the final package. Trace amounts of residual metal resulting from the use of a processing aid or similar material during production of a product from which a package or packaging component is manufactured, and which processing aid is reasonably expected to be consumed, transformed into a non-regulated chemical during the process, washed or dissolved away, or otherwise nearly all removed during processing, would not make the final package or packaging component non-compliant if the total residual metal level were below 100 ppm, as this is not considered intentional addition of the regulated heavy metal.

 

Q: What is meant by "sum of the concentration levels" for single-component vs. multi-component packages?

 

A: Single-component Package -- The concentration level, expressed in parts per million (ppm), should be determined for each of the four metals and these numbers added together (summed). This summation must be within the limit of 100 ppm. Multi-component Package -- The four regulated metals are not summed or averaged across all packaging components that together comprise a package. Rather, the concentration level, expressed in ppm, should be individually determined for each metal and summed for each packaging component within the package. Each packaging component must comply individually with the legal limit of 100 ppm.

 

Q: Does the law apply equally to water-soluble or insoluble forms of the four heavy metals?   Does it make a difference with regard to soluble vs. insoluble forms if the package is incinerated?

 

A: The law applies to both soluble and insoluble forms of the four heavy metals and no distinction is made between them.   For example, the effects of lead uptake in the human body due to ingestion of paint chips, ink, etc. are essentially the same for the various forms of lead regardless of their initial water solubility. With regard to incineration, it is well documented that maximizing the removal of heavy metals in waste prior to incineration reduces air emissions and leachate problems from ash (bottom ash and fly ash), including when such ash is subsequently disposed of on land. High-temperature combustion normally converts the heavy metal compounds (whether initially water-soluble or insoluble) in the waste being burned into other compounds, primarily oxides, hydroxides, chlorides or other salts, or into metallic particulates, which can enter either the stack gas or the ash streams. The sole exception demonstrated to date is vitrified labels on glass or ceramic packaging, provided that such packaging has passed the test methods specified in the law. This unique behavior of vitrified glass and ceramic labels during incineration, which thus far has not been satisfactorily demonstrated for other materials, is recognized by an exemption for these labels. The exemption does not apply to non-vitrified labels or to mercury and its compounds.

 

Q: Is there an exemption for packaging that is manufactured using solder that contains lead?

 

A: No. The Model Legislation specifically prohibits the intentional introduction of the four regulated heavy metals into packaging such as from leaded solder. Originally there was a four-year period allowed for cans and other containers to achieve compliance. During that period both the can industry and the solder industry were able to come up with technical breakthroughs (i.e., deep-drawn seamless cans and lead-free tin solder, respectively) that negated any future need to exempt lead-containing solder.

 

Q: Is hexavalent chromium more toxic than other forms of chromium?

 

A: The toxicological information available on chromium compounds clearly indicates that the hexavalent form is more toxic than other forms.

 

Test Methods

 

Q: What test methods are acceptable?

 

A: TPCH cannot recommend specific test methods (with the exception of glass and ceramic containers with vitrified labels), since test methods vary depending on the metal and base material being tested. The analytic laboratory should be capable of performing tests to determine the total concentration of each of the 4 restricted metals – lead, cadmium, mercury and hexavalent chromium. TPCH recognizes the use of x-ray fluorescent (XRF) analysis, as well as traditional analytic procedures that measure total concentration of metals. Test methods that measure “leachable” metals are not appropriate (except under the permanent glass exemption). Particular attention should be paid to the sample preparation methods to determine whether the metals of interest are properly solubilized prior to testing.  The selected sample preparation and test methods should be documented in the laboratory test report. 

Testing should be performed and reported on individual packaging components (e.g., inks, resin, paperboard, adhesives). Analytic laboratories must have appropriate certifications by recognized certification organizations or authorities (e.g., National Environmental Laboratory Accreditation Program). As many analytical laboratories are not accustomed to testing the variety of package materials available in the market, it is critical to ensure the laboratory follows strict quality assurance/quality control procedures (QA/QC). TPCH recommends requesting QA/QC data be provided with analytical reports.

 

Note: To qualify for the glass exemption for glass and ceramic packages with vitrified labels, the sample must be prepared according to ASTM C1606-04 and tested in accordance with the Toxicity Characteristic Leaching Procedure of US EPA Test Method and publication SW-846, 3rd edition, Test Method for Evaluating Solid Waste. The concentration of metals in packaging cannot exceed 1.0 ppm for cadmium, 5.0 ppm for hexavalent chromium and 5.0 ppm for lead. Mercury is not exempted by this provision

 

 

 

 

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