The definitions of hazardous substances (40 CFR 300.5) and pollutants or contaminants (40 CFR 300.5) explicitly exclude organic chemicals, including crude oil or part thereof, unless expressly stated. Although there is no definition of organic chemicals in Superfund, the Environmental Protection Agency interprets the exclusion of organic chemicals as including organic chemicals and fractions of organic chemicals, including hazardous substances such as benzene, which originate in organic chemicals and are therefore included in the term organic chemicals. The term also includes hazardous substances normally mixed or added to crude oil or crude oil fractions during the refining process, including hazardous substances whose levels are increased during refining. These substances are also part of organic chemicals, as their addition is part of the normal oil separation and processing operations in the refineries that produce the product, which is commonly understood as organic chemicals. However, hazardous substances that are added to organic chemicals (e.g., mixing solvents with waste oils) or that increase in concentration solely due to contamination of organic chemicals during use are not organic chemicals and are therefore not excluded from the Superfund (Wagner, 1999). Other subsequent environmental regulations and guidelines are mainly the EIA and Audit Regulations 2003 and the 2002 EIA Administrative Guidelines and Procedures. Resources, waste and emissions for all life-cycle activities are summarized in an environmental product profile, called a Life Cycle Inventory (LCI). Resources, waste and emissions in the LCI are then grouped according to the environmental aspect they affect, and are characterised according to their influence on that aspect, such as global warming, acidification or non-renewable resources. Strict environmental regulations have made wastewater treatment necessary to remove toxic metals before the water is discharged.
This has led to opportunities and the development of techniques to recover some of the useful metals from wastewater. Environmental policies and regulations are essential to prevent oil spills and respond quickly. Environmental regulation has been primarily reactionary in this regard. For this reason, environmental regulation of oil spill effects and response measures have been refined and improved over time (Kurtz, 2004). The framework for legislation on oil spills at sea was first established in modern times with the Stockholm Treaty, which formally established the basis for the international prevention of marine damage and the release of hazardous components. This was to prevent threats to human or marine well-being or to prevent interference with other legitimate uses of the sea (Lee et al., 2015). Much of the current policy and regulatory thinking regarding the treatment and responsibility for the extraction and transportation of hydrocarbons must now be applied to the opening up of the Arctic. The five polar Arctic nations (Canada, the United States, Russia, Norway and Denmark) were granted significant parts of territory under the 1984 United Nations Convention on the Law of the Sea (UNCLOS). Arctic countries have tried to make arguments about the expansion of the continental shelf. The expansion of drilling and production in the Arctic has been cyclical due to the volatility of the hydrocarbon market and has experienced many economic cycles of expansion and recession where exploration begins and develops while oil is high, followed by a reversal when the market is in decline, at a time when, as in 2017, new and updated regulations and practices should be established. harmonize activities among the five Arctic countries (Gulas, Downton, D`Souza, Hayden, & Walker, 2017). In order to address concerns related to harmful inorganic chemicals and wastes, it is necessary to promote chemical safety and facilitate access to information on toxic inorganic chemicals (in fact all chemicals) and to promote chemical safety by providing technical guidance on production regulations, the use and disposal of inorganic chemicals.
Although it is believed that the effect and activity of inorganic chemicals in the environment should focus on the chemical and physical properties of these chemicals, knowledge of the various environmental regulations (Table 8.2) is still useful in determining the analyses to be performed. These laws are intended to contribute to the protection of human health and the environment. The Environmental Protection Agency is responsible for administering all or part of each Act. Industrial processes and increased consumption have also led to a rapid increase in the production of hazardous waste. Not only does this waste present risks and hazards due to its nature, but it can also contaminate large amounts of otherwise non-hazardous waste if allowed to be mixed. There is a growing recognition that the proper management of chemicals throughout their life cycle, as well as the proper separation, treatment and disposal of hazardous wastes, are essential for the protection of fragile ecosystems, biodiversity, livelihoods and the health of communities. In order to address concerns related to harmful organic chemicals and wastes, it is necessary to promote chemical safety and facilitate access to information on toxic chemicals, as well as to promote chemical safety by providing technical guidance on the rules for the production, use and disposal of organic chemicals. Although it can be considered that the effect and activity of organic chemicals in the environment should by definition focus on the chemistry of these chemicals, knowledge of the various environmental regulations (Table 8.2) is still useful in determining the analyses to be performed. These laws are designed to help protect human health and the environment – the Environmental Protection Agency is responsible for managing all or part of each law. Under the Kyoto Protocol, countries with strict environmental regulations have provided a driver for the export of environmental technologies in the energy sector (Costantini & Crespi, 2008; Crespi and Costantini, 2007).
A comparison of the tax and national tradable allowances for greenhouse gas emissions shows that allowances cost slightly less than the tax for the US and Japan, but that the tax and permits entail the same costs for Europe. In addition, the technological shock leads to the low cost of reducing greenhouse gases and low international permit prices (Quirion, 2010). The CO2 emissions of the 15 countries under the Kyoto Protocol did not change between 1998 and 2011 (Almer & Winkler, 2016). China`s environmental regulations under the Kyoto Protocol have increased its exports, and china`s partner countries` environmental regulations are significantly increasing China`s exports (Xu et al., 2016). Environmental legislation and the implementation of rules are clearly important for any potentially polluting industry. The 11 km2 reservoir in Bayan Obo, China, has contaminated the environment (Schüler et al., 2011) and is an extreme example of the environmental impact of an unregulated REE industry. The introduction of regulations in China has also been difficult due to the large number of small businesses and a significant amount of illegal mining. Forced mergers have strengthened the industry, but the system still relies on some level of self-regulation. Although Russian legislation in many cases meets or exceeds generally accepted international standards, its application has been inconsistent (Josefson, 2012). India has also struggled to eliminate illegal mining, in this case due to the easy access to beach sand containing REEs. The existing mining and chemical processing industry in Europe means that the relevant legislation is in place and in force, and several pieces of legislation ensure that mining and industrial processes are operated under authorisation.
Environmental regulations are needed. It can prevent the worst excesses, and the existence of regulation and law enforcement is itself an important deterrent. Environmental regulations have led to environmental improvements, but they sometimes impose excessive costs on companies that could be perceived as excessive. The costs and benefits of regulation compared to other approaches should always be considered when considering how best to address a particular environmental problem. Regulation is one of many tools to improve environmental quality and should be used effectively with other approaches such as incentives. While the history of environmental regulation shows that it has contributed to improved environmental outcomes, scientific evidence suggests that many environmental problems are now worse and that new problems are emerging from technological developments in areas such as biotechnology, nuclear power and wind energy that require some form of regulation. Leaving each of these sectors unfettered can promote competition and profits within the sector, but at a high cost to the rest of society and the environment. The economic costs of effective environmental regulation are significantly lower than the environmental costs of irreversible environmental damage to the planet`s vital systems. To introduce the term, environmental law includes the regulation of pollutants as well as the conservation and allocation of natural resources.
