Legislation for

In such cases the development scheme for the original reserves may have to be modified to make processing capacity available for the new hydrocarbons. The economics of such a scheme can be affected negatively if substantial engineering modifications have to made to meet new safety legislation. For more background to ERD refer to Section 3. 

Table 2. Chemical Control Legislation for Dyes and Pigments...

Bentazone has been monitored in the NRA Anglian Region since 1993 and the results show that bentazone is regularly present in surface and groundwaters. Currently there are no restrictions on its use, but bentazone is due to be reviewed under the Authorizations Directive, the new European legislation for pesticide approvals, and the issue of water pollution will be raised. 

The chapter on Radioactive chemicals (Chapter 11) has been updated. Considerations of safety in design (Chapter 12) are presented separately from systems of work requirements, i.e. Operating procedures (Chapter 13). Tlie considerations for Marketing and transportation of hazardous chemicals are now addressed in two separate chapters (Chapters 14 and 15). Chemicals and the Environment are now also covered in two chapters (Chapters 16 and 17) to reflect the requirement that the impact of chemicals on the environment should be properly assessed, monitored and controlled. Although a substantial contribution to atmospheric pollution is made by emissions from road vehicles and other means of transport, and this is now strictly legislated for, this topic is outside the scope of this text. Chapter 18 provides useful conversion factors to help with the myriad of units used internationally. 

Employers and others who now have duties under the 1974 Act will have had some form of responsibilities under previous legislation (e.g. the Factories Act 1961) to ensure the health and safety and welfare of people at work. However, a number of employers will be subject to such legislation for the first time. 

Vitrified slag. This has a quality that meets the requirements of Dutch legislation for secondary building materials. 

Legislation for pesticide residues, including the setting of MRLs in food commodities, is a shared responsibility between the Commission and the Member States. To date, Community MRLs have been established for about 130 pesticide a.i. For pesticides and commodities where no Community MRL exists, the situation is not harmonized and the Member States may set MRLs at national levels to protect the health of its citizens. 

Although these are all used across Europe, the hierarchy of these has altered slightly due to the influences of environmental legislation. For example, Chloro-isothiazolone has been identified as a skin sensitiser and hence therefore lost its number one position as a controlling agent. New actives such as the Octyl - isothiazolone have recently been introduced as a more stable molecule where it is hoped that lower levels can be used reducing environmental and human safety aspects. 

The basis for applications will follow the principles laid down in basic European level legislation for the pharmaceutical sector. This is more or less common regardless of the actual mechanism used to gain an approval. The basic requirements for pharmaceutical marketing authorization applications are laid down in Directive 65/65/EEC (as amended). There are no specific requirements for pharmaceutical development or process validation included in the text of that document. 

The relevant legislation for tanneries regarding the use of chemicals can be found both in legislation regarding environmental permits for the industrial installations which in some cases addresses substitution of chemicals. One example of this is the EU Industrial Emissions Directive [4] which regulates emissions from industrial installation within the EU. One key aspect in this directive is how problematic chemicals should be substituted to more environmentally friendly alternatives by tanneries. 

At the member state level, some countries, such as the Netherlands, a pioneer in the protection of soil, have their own national policies and regulations for the management of contaminated soils that were adopted before the Soil Framework Directive [132], Protection guidelines vary from country to country, and specific legislation for soil contamination only exists for some member states, including the Netherlands, Italy, Austria, France, Belgium, Germany, the UK, Denmark, Spain and Finland [128],... 

There is special legislation for other countries. For example Canada, one of the most important pulp and paper producing countries, has set several general guidelines, and the actual limits and guidelines can be different in each state [5]. The wastewater limit systems in Canada are mostly based on load kilograms per tonne production. Different limits are applied for different types of mills. Some parameters are measured as concentrations. Toxicity limits are also used. 

In the EU, the current chemical control measures, based on a network of legislation for hazard communication and safety assessment, are soon to be dramatically revised. To set the scene for this forthcoming fundamental change to chemical control in the EU, the key facets of the existing measures are described briefly i.e., notification of new chemical substances, the relatively-limited measures to evaluate existing substances and hazard communication. There have been problems with the current scheme, principally the disparity between the safety data on new and existing substances. 

Current EU Chemical Control Legislation for New and Existing Chemicals... 

The new Biocidal Products Directive is examined, which closes the gap in European legislation for products such as disinfectants and anti-foulants where there has not, until now, been a Europe-wide standard. The basic goals of the directive are to simplify and harmonise Europe s regulatory framework for biocides, and to remove trade barriers within the EU, and to improve the protection of both human health and the environment. The new directive must be enforced as national legislation in all member countries by 14 May 2000. Details are given of products defined within the directive, and ways in which the directive will be put into practice in the UK are discussed. The implications of the legislation on the industry in terms of time and money spent on testing for each active substance involved are examined. 

Federal legislation for ASTs is also in the process of being mandated under RCRA. This bill would include requirements for development and implementation of a release prevention plan, a tank system that is capable of containing 110% of the content of the tank and preventing off-site release, and inspection of tank systems by a qualified professional engineer. Provisions will also include evidence of financial responsibility and cleanup of product releases. There is little doubt that legislation for ASTs will be more stringent in the years to come. 

Some regulatory authorities have foreseen the future impact of TM and set up appropriate guidelines. The European Union has legislation for traditional herbal products. Another example is the Therapeutic Goods Administration of Australia, which has set up a complementary medicine section that controls the regulatory practices for TM. 

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