Lexikon

regulation (EC) No 1013/2006 of the European Parliament and of the Council of 14 June 2006 on shipments of waste.

See: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:190:0001:0098:EN:PDF

1272/2008 regulation of the European Parliament and of the Council of 16 December 2008 on classification, labelling and packaging of substances and mixtures, amending and repealing Directives 67/548/EEC and 1999/45/EC, and amending Regulation (EC) No 1907/2006.

http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2008:353:0001:1355:EN:PDF

REACH is the Regulation for Registration, Evaluation, Authorisation and Restriction of Chemicals. It entered into force on 1^st June 2007 to streamline and improve the former legislative framework on chemicals of the European Union (EU). REACH places greater responsibility on industry to manage the risks that chemicals may pose to the health and the environment.
In principle REACH applies to all chemicals: not only chemicals used in industrial processes but also in our day-to-day life, for example in cleaning products, paints as well as in articles such as clothes, furniture and electrical appliances.
The aims of REACH are to:

• Improve the protection of human health and the environment from the risks that can be posed by chemicals

• Enhance the competitiveness of the EU chemicals industry, a key sector for the economy of the EU
• Promote alternative methods for the assessment of hazards of substances
• Ensure the free circulation of substances on the internal market of the European Union.

Source: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:396:0001:0849:EN:PDF

directive 1999/45/EC OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL of 31 May 1999, concerning the approximation of the laws, regulations and administrative provisions of the Member States relating to the classification, packaging and labelling of dangerous preparations.

http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:1999:200:0001:0068:EN:PDF

2000/532/EC, commission decision of 3 May 2000 on the list of wastes.
List of wastes pursuant to Article 1(a) of Directive 75/442/EEC on waste and Article 1(4) of Directive 91/689/EEC on hazardous waste.
The present list is a harmonised list of wastes. It will be periodically reviewed and if necessary revised in accordance
with Article 18 of Directive 75/442/EEC. However, the inclusion of a material in the list does not mean that the
material is a waste in all circumstances. Materials are considered to be waste only where the definition of waste in
Article 1(a) of Directive 75/442/EEC is met. Wastes included in the list are subject to the provisions of Directive 75/442/EEC except where Article 2(1)(b) of this Directive applies.
The different types of waste in the list are fully defined by the six-digit code for the waste and the respective two-digit and four-digit chapter headings. This implies that the following steps should be taken to identify a waste in the list.
As the first step, identify the source generating the waste in Chapters 01 to 12 or 17 to 20 and identify the appropriate six-digit code of the waste. If no appropriate waste code can be found in Chapters 01 to 12 or 17 to 20 the Chapters 13, 14 and 15 must be examined to identify the waste. If none of these waste codes apply, the waste must be identified according to Chapter 16. If the waste is not in Chapter 16 either, the 99 code (wastes not otherwise specified) must be used in the section of the list corresponding to the activity identified in step one.
Any waste marked with an asterisk (*) is considered as a hazardous waste pursuant to Article 1(4), first indent, of
Directive 91/689/EEC on hazardous waste, and subject to the provisions of that Directive unless Article 1(5) of that
Directive applies.
For the purpose of this Decision, ‘dangerous substance’ means any substance that has been or will be classified as
dangerous in Directive 67/548/EEC as amended; ‘heavy metal’ means any compound of antimony, arsenic, cadmium,
chromium (VI), copper, lead, mercury, nickel, selenium, tellurium, thallium and tin, including these metals in metallic
form, as far as these are classified as dangerous substances. If a waste is identified as hazardous by a specific or general reference to dangerous substances, the waste is hazardous only if the concentrations of those substances are such (i.e. percentage by weight) that the waste presents one or more of the properties listed in Annex III to Council Directive 91/689/EEC.

Chapters of the list: two-digit codes:
01 Wastes resulting from exploration, mining, dressing and further treatment of minerals and quarry
02 Wastes from agricultural, horticultural, hunting, fishing and aquacultural primary production, food preparation and
processing
03 Wastes from wood processing and the production of paper, cardboard, pulp, panels and furniture
04 Wastes from the leather, fur and textile industries
05 Wastes from petroleum refining, natural gas purification and pyrolytic treatment of coal
06 Wastes from inorganic chemical processes
07 Wastes from organic chemical processes
08 Wastes from the manufacture, formulation, supply and use (MFSU) of coatings (paints, varnishes and vitreous
enamels), adhesives, sealants and printing inks
09 Wastes from the photographic industry
10 Inorganic wastes from thermal processes
11 Inorganic metal-containing wastes from metal treatment and the coating of metals, and non-ferrous hydrometallurgy
12 Wastes from shaping and surface treatment of metals and plastics
13 Oil wastes (except edible oils, 05 anbd 12)
14 Wastes from organic substances used as solvents (except 07 and 08)
15 Waste packaging; absorbents, wiping cloths, filter materials and protective clothing not otherwise specified
16 Wastes not otherwise specified in the list
17 Construction and demolition wastes (including road construction)
18 Wastes from human or animal health care and/or related research (except kitchen and restaurant wastes not arising
from immediate health care)
19 Wastes from waste treatment facilities, off-site waste water treatment plants and the water industry
20 Municipal wastes and similar commercial, industrial and institutional wastes including separately collected fractions.

Source: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2000:226:0003:0024:EN:PDF

directive on classification, packaging and labelling of dangerous substances. Commission Directive 2001/59/EC of 6 August 2001 adapting to technical progress for the 28th time Council Directive 67/548/EEC on the approximation of the laws, regulations and administrative provisions relating to the classification, packaging and labelling of dangerous substances: OJEC L225, 21.8.2001, pp. 1–333.

The danger symbols are defined in Annex II of the directive. A consolidated list with translations into other EU languages can be found in Directive 2001/59/EC.

The standard phrases are defined in Annexes III and IV of the Directive. Annex III defines phrases relating to the Nature of special risks attributed to dangerous substances and preparations, often referred to as R-phrases. Annex IV defines phrases relating to Safety advice concerning dangerous substances and preparations, often referred to as S-phrases.

The appropriate standard phrases must appear on the packaging and label of the product and on its MSDS (Material Safety data Sheet). Annex I specifies the standard phrases to be used for substances that are listed there: these are obligatory.

The lists of standard phrases were last updated in 2001, and Directive 2001/59/EC provides a consolidated list in all EU languages. In general, the label on the packaging of a dangerous substance or preparation must clearly indicate the following items:

• the name of the substance; for substances listed in Annex I, the name indicated must be one of those listed in the Annex (many substances appear in the Annex under different synonyms): otherwise, the name should be "internationally recognized"
• the name, full address and telephone number of the person or company which has placed the substance on the market (manufacturer, importer or distributor);
• the danger symbols, if any;
• the standard phrases, if any; (certain exemptions are permitted)
• the EINECS number or equivalent;
• for substances listed in Annex I, the words EC label.

On 20 January 2009 the new (EC) 1272/2008 on classification, labelling and packaging of substances and mixtures entered into force. It aligns existing EU legislation to the United Nations Globally Harmonised System (GHS).

Source: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=CELEX:32001L0059:EN:NOT and
http://en.wikipedia.org/wiki/Dangerous_Substances_Directive_%2867/548/EEC%29#cite_note-2001-59-EC-6

DIRECTIVE 2006/12/EC of the European Parliament and of the Council of 5 April 2006, on waste.
Some important issues:
The essential objective of all provisions relating to waste management should be the protection of human health and the environment against harmful effects caused by the collection, transport, treatment, storage and tipping of waste.
Common terminology and a definition of waste are needed in order to improve the efficiency of waste management in the Community.
Effective and consistent rules on waste disposal and recovery should be applied, subject to certain exceptions, to movable property which the holder discards or intends or is required to discard.
The recovery of waste and the use of recovered materials as raw materials should be encouraged in order to conserve natural resources. It may be necessary to adopt specific rules for re‑usable waste.
In order to achieve a high level of environmental protection, Member States should, in addition to taking responsible action to ensure the disposal and recovery of waste, take measures to restrict the production of waste particularly by promoting clean technologies and products which can be recycled and re‑used, taking into consideration existing or potential market opportunities for recovered waste.
Moreover, discrepancies between Member States’ legislation with regard to waste disposal and recovery may affect the quality of the environment and the smooth operation of the internal market. It is important for the Community as a whole to become self‑sufficient in waste disposal and desirable for Member States individually to aim at such self‑sufficiency. In order to achieve those objectives, waste management plans should be drawn up in the Member States.
Movements of waste should be reduced and Member States may take the necessary measures to that end in their management plans.
To ensure a high level of protection and effective control, it is necessary to provide for authorisation and inspection
of undertakings which carry out waste disposal and recovery.
In order that waste can be monitored from its production to its final disposal, other undertakings involved with waste, such as waste collectors, carriers and brokers should also be subject to authorisation or registration and appropriate inspection.
That proportion of the costs not covered by the proceeds of treating the waste must be defrayed in accordance
with the ‘polluter pays’ principle.

Source: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2006:114:0009:0021:EN:PDF

2008/1/EC directive of the European Parliament and of the Council of 15 January 2008 on Integrated Pollution Prevention and Control (IPPC).

Source: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=OJ:L:2008:024:0008:0029:EN:PDF

see Dangerous Substances Directive (67/548/EEC)

Council Directive 67/548/EEC of 27 June 1967 on the approximation of laws, regulation and administrative provision relatingto the classification, packaging and labelling of dangerous substances.

Source: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=CELEX:31967L0548:EN:HTML

Plant Protection Products (PPPs) are regulated by the Council Directive 91/414/EEC concerning the placing of plant protection products on the market lays down rules and procedures for approval of the active substances at EU-level and for the authorisation at Member State level of plant protection products (PPPs) containing these substances. This Directive states that substances cannot be used in plant protection products unless they are included in a positive EU list. Once a substance is included in the positive list Member States may authorise the use of products containing them.

Pesticides residues in food are regulated by Regulation (EC) No 396/2005. The legislation covers the setting, monitoring and control of pesticides residues in products of plant and animal origin that may arise from their use in plant protection.

Both Directive 91/414 on the placing on the market of plant protection products and Regulation 396/2005 on pesticide residues in food and feed aim at a high level of protection of human health and the environment.

Source: http://ec.europa.eu/food/plant/protection/index_en.htm

directive 98/8/EC of the European Parliament and of the Council of 16 february 1998, concerning the placing of biocidal products on the market.

Biocidal products are active substances and preparations containing one or more active substances, put up in the form in which they are supplied to the user, intended to destroy, deter, render harmless, prevent the action of, or otherwise exert a controlling effect on any harmful organism by chemical or biological means.

Harmful is an organism which has an unwanted presence or a detrimental effect for humans, their activities or the products they use or produce, or for animals or for the environment.

Commission Regulation (EC) No 1451/2007 of 4 December 2007 on the second phase of the 10-year work programme referred to in Article 16(2) of Directive 98/8/EC of the European Parliament and of the Council concerning the placing of biocidal products on the market. Pursuant to Directive 98/8/EC, Member States may only authorise the placing on the market of biocidal products containing active substances included in Annex I, to that Directive.

Biocidal products containing active substances listed in Annex II to the Regulation 1451/2007 for which a decision was taken not to include these active substances for certain or all of their notified product types in Annex I (or IA) to Directive
98/8/EC, shall no longer be placed on the market.

Annex I and Annex II list can be find in: http://ecb.jrc.ec.europa.eu/legislation/2007R1451EC.pdf

Sourcec: http://ecb.jrc.ec.europa.eu/legislation/1998L0008EC.pdf, and
http://ecb.jrc.ec.europa.eu/legislation/2007R1451EC.pdf

the integrated effect of more toxic substances, mixtures of chemical substances, xenobiotica or drogs, which can be quantified as the sum of the effects of the components, contrary to not additive effects, such as antagonism or sinergism.

to transport or carry. For example particulate matter is transported in air by wind, liquid form matter is flowing and contaminants are transported by this flow, etc.

change in morphology, physiology, growth, development or lifespan of an organism which results in impairment of its functional capacity or impairment of its capacity to compensate for additional stress or increased susceptibility to the harmful effects of other environmental influences. (Source: REACH Glossary)

a change in body function or cell structure that might lead to disease or health problems.

see air injection into soil

Annex I of Directive 67/548/EEC contains a list of harmonised classifications and labellings for substances or groups of substances, which are legally binding within the EU.
The list is regularly updated through Adaptations to Technical Progress (ATP). Revised and new classifications inserted to the list are proposed by DG ENV (EC Directorate General responsible for environment) and agreed by a Member State vote.
The DG ENV proposal is based on advice from the Technical Committee for Classification and Labelling (TC C&L) with participation of experts from the Member States.
The list is published in OJ L 152 of 30/04/2004 and can be found on the following web-address: http://www.reach-compliance.eu/english/legislation/docs/launchers/launch-annex-1-67-548-EEC.html

Best Available Techniques Not Entailing Excessive Cost.

BEVs store electricity in batteries and draw power from the batteries to run an electric motor that drives the vehicle. So long as the ultimat electricity source is clean, the BEV system can reduce emissions significantly compared with an internal combustion engine vehicle (ICEV) run on a liquid fuel. Indeed, BEVs using WWS power would be completely zero-emission vehicles. Moreover, BEVs get about 5 times more work (in miles of travel) per unit of input energy than do ICEVs (mi/kWh-outlet versus mi/kWh-gasoline). BEVs have existed for decades in small levels of production, and today most major automobile companies are developing BEVs. The latest generation of vehicles uses lithium-ion batteries, which do not use the toxic chemicals associated with lead-acid or the nickel-cadmium batteries (1).

Vehicles using both electric motors and internal combustion engines are examples of hybrid electric vehicles, and are not considered pure (or all) EVs because they operate in a charge-sustaining mode.

• Regular hybrid electric vehicles cannot be externally charged.
• Hybrid vehicles with batteries that can be charged externally to displace some or all of their internal combustion engine power and gasoline fuel are called plug-in hybrid electric vehicles (PHEV), and are BEVs during their charge-depleting mode.

All-electric and plug-in hybrids are off-vehicle charge capable. (“OVCC” or pluginable), which means their batteries can be charged from an off-vehicle electric energy source that cannot be connected or coupled to the vehicle while the vehicle is being driven (2)

Sources:

(1) Mark Z. Jacobson and Mark A. Delucchi: Evaluating the Feasibility of a Large-Scale Wind, Water, and Sun Energy Infrastructure

(2) http://en.wikipedia.org/wiki/Battery_electric_vehicle

Directive 98/8/EC of the European Parliament and of the Council on the placing on the market of biocidal products was adopted in 1998. According to the Directive, Member States had to transpose the rules before 14 May 2000 into national law.

The Commission adopted the original proposal for the Directive in 1993. Directive 91/414/EEC on plant protection products, adopted in 1991, served as a model for the new Directive.

The Biocidal Product Directive aims to harmonise the European market for biocidal products and their active substances. At the same time it aims to provide a high level of protection for humans, animals and the environment.

Concerted Action on brownfield and Economic Regeneration Network.

The CABERNET network consists of 55 Members, including 8 Team Leaders and 4 Coordination Team members, originating from 21 countries across Europe.

The groups cover the different aspects of rehabilitation of brownfield sites. The network has been divided into 8 distinct stakeholder groups. A number of Stakeholder Groups also have invited non-contracted Associate Members.

CABERNET has a distinct multi-disciplinary flavour, consisting of members from a wide range of professional backgrounds including environmental science, engineering, spatial and urban planning, and political administration.

The Members, drawn from across the European Community and accession countries, represent interests that span the stakeholder spectrum.

Source: http://www.cabernet.org.uk/index.asp?c=1125

Concerted Action on risk Assessment for Contaminated Land
http://www.umweltbundesamt.at/en/umweltschutz/
altlasten/projekte1/international1/caracas

carcinogenic effect has a substance or a mixture of substances which induces cancer or increases its incidence and/or malignancy or shorten the time to tumour occurrence. Causing cancer may be due to the ability to damage the genome or to the disruption of cellular metabolic processes. Carcinogenic chemicals have conventionally been divided into two categories according to the presumed mode of action. Non-genotoxic modes of action include epigenetic changes, i.e., effects that do not involve alterations in DNA but that may influence gene expression, altered cell-cell communication, or other factors involved in the carcinogenic process.

Cancer is a disorder of the cells, characterized by the lack of programmed cell death. Carcinogens induces the uncontrolled, malignant division pf cells, ultimately leading to the formation of tumors. Usually DNA damage leads to programmed cell death, but if the programmed cell death pathway is damaged, then the cell cannot prevent itself from becoming a cancer cell. The objective of investigating the carcinogenicity of chemicals is to identify potential human carcinogens, their modes of action, and their potency. Once a chemical has been identified as a carcinogen, there is a need to elucidate the underlying mode of action, i.e. whether the chemical is directly genotoxic or not. For genotoxic carcinogens it is assumed that, unless exception, there is no discernible threshold and that any level of exposure carries a risk. For non-genotoxic carcinogens, no-effect-thresholds are assumed to exist and to be discernable. Human studies are generally not available for making a distinction between the above mentioned modes of action; and a conclusion on this, in fact, depends on the outcome of mutagenicity testing and other mechanistic studies. In addition to this, animal studies may also inform on the underlying mode of carcinogenic action.

The cancer hazard and mode of action may also be highly dependent on exposure conditions such as the route of exposure. Therefore, all relevant effect data and information on human exposure conditions are evaluated.

Central and Eastern European Countries.

in Annexes VII and VIII to Directive 79/831/EEC, methods for the determination of the ecotoxicity of chemical substances are enlisted. The methods are based on those recognized and recommended by competent international bodies (in particular OECD).

General introduction
1 acute toxicity for fish
2 acute toxicity for Daphnia
3 algal inhibition test
4 biodegradation: determination of the "ready" biodegradability
  4-a dissolved organic carbon (doc) die-away test
  4-b modified oecd screening test
  4-c carbon dioxide evolution test
  4-d manometric respirometry test
  4-e closed bottle test
  4-f miti test
5 degradation : biochemical oxygen demand
6 degradation: chemical oxygen demand
7 degradation: abiotic degradation: hydrolysis as a function of ph
8 toxicity for earthworms : artificial soil test
9 biodegradation: Zahn−Wellens test
10 biodegradation: activated sludge simulation test
11 biodegradation: activated sludge respiration inhibition test
12 biodegradation: modified scas test
13 bioconcentration: flow-through fish test
14 fish juvenile growth test
15 fish, short-term toxicity test on embryo and sac-fry stages
16 honeybees, acute oral toxicity test
17 honeybees, acute contact toxicity test
18 adsorption/desorption using a batch equilibrium method
19 estimation of the adsorption coefficient (koc) on soil and on sewage sludge using high performance liquid chromatography (hplc)
20 Daphnia magna reproduction test
21 soil microorganisms: nitrogen transformation test
22 soil microorganisms: carbon transformation test
23 aerobic and anaerobic transformation in soil
24 aerobic and anaerobic transformation in aquatic sediment systems

An Analysis of National and EU RTD Programmes related to Sustainable Land and Groundwater Management
Proceedings of the Conference on "Sustainable Management of Contaminated Land"
Variation in calculated human exposure. Comparison of calculations with seven European human exposure models
Special Edition on Land Contamination and Reclamation: The Sustainable Management and remediation of Contaminated Land

1999/45/EC directive on classification, packaging, labellingis the Directive of the European Parliament and of the Council of 31 May 1999, concerning the approximation of the laws, regulations and administrative provisions of the Member States relating to the classification, packaging and labelling of dangerous preparations.

common technical specification is a technical specification drawn up in accordance with a procedure recognized by the Member States with a view to uniform application in all Member States and published in the Official Journal of the European Communities.

Source: Council Directive 93/38/EEC of 14 June 1993 coordinating the procurement procedures of entities operating in the water, energy, transport and telecommunications sectors.
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=CELEX:31993L0038:EN:HTML

conservation status of a species means the sum of the influences acting on the species concerned that may affect the long-term distribution and abundance of its populations within the territory referred to in Article 2;

The conservation status will be taken as "favourable" when:

- population dynamics data on the species concerned indicate that it is maintaining itself on a long-term basis as a viable component of its natural habitats, and

- the natural range of the species is neither being reduced nor is likely to be reduced for the foreseeable future, and

- there is, and will probably continue to be, a sufficiently large habitat to maintain its populations on a long-term basis.

Source: Council Directive 92/43/EEC of 21 May 1992 on the conservation of natural habitats and of wild fauna and flora.
http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=CELEX:31992L0043:EN:html

Coordination of Information on the Environment
http://en.wikipedia.org/wiki/
Coordination_of_Information_on_the_Environment

corrective action in environmental management means the process, when failure occurs, of investigation, correction and institution of preventative measures to preclude the recurrence of failure. An important component of corrective action is documentation of both problem and remedial measures taken.