United States of America

Author(s):  
James Salzman

This chapter examines environmental law in the United States. It begins with a discussion of the US approach to environmental law, describing it as a system striving for balance, including balance in terms of the allocation of powers between federal and state legislatures. The chapter provides an overview of the constitutional bases of US environmental law, delegation of authority to regulatory agencies, and environmental regulation in relation to private property. It then considers the structure and substance of environmental law, focusing on five pieces of legislation: Clean Air Act, Clean Water Act, National Environmental Policy Act, Resource Conservation and Recovery Act, and Comprehensive Environmental Response, Compensation and Liability Act (CERCLA). The chapter concludes with an analysis of the implementation framework and how it affects environmental law in practice, taking into account the role of agency authorities, administrative enforcement, civil remedies, criminal sanctions, and relevant provisions on citizen suits.

2021 ◽  
Author(s):  
E. Donald Elliot ◽  
Daniel C. Esty

Providing a comprehensive overview of the current and developing state of environmental governance in the United States, this Advanced Introduction lays out the foundations of U.S. environmental law. E. Donald Elliott and Daniel C. Esty explore how federal environmental law is made and how it interacts with state law, highlighting the important role that administrative agencies play in the creation, implementation, and enforcement of U.S. environmental law.


Author(s):  
Affolder Natasha

This chapter assesses international environmental law in the courts of North America. In particular, it explores the minimal engagement of US, Canadian, and Mexican courts with international environmental law. Environmental law cases in Canada, Mexico, and the United States are not immune to international law and international norms. However, international environmental lawyers may be forced to look to some unlikely and unusual places to find international environmental law's normative influence. Environmental law cases in North America seem poised to engage most significantly with international law not in the ‘bright lights’ but rather on the side-lines, where environmental law norms interface with climate law, private international law, Indigenous law, and human rights law.


2002 ◽  
Vol 17 (2) ◽  
pp. 195-233 ◽  
Author(s):  
Gerard J. Mangone

AbstractConstraints upon the uses of private property in the United States have increased very far beyond the doctrines of Grotius, Locke, Blackstone, and the framers of the Constitution. In the 19th century, both public nuisance limitations and eminent domain takings were applied to particular holdings, with the latter requiring compensation under the Fifth Amendment. The New Deal of the 1930s and the envirommental movement of the 1960s radically changed the relationship of government to private property. Sweeping economic reforms and the exercise of broad regulatory powers by public agencies for a clean environment and biological diversity led to a wholesale "taking" of private property without compensation. Recent cases of the Supreme Court involving wetlands and coastal property reveal the tensions that exist between sovereign power for the public good and the protection of individual property as a bulwark against arbitrary government.


2013 ◽  
Vol 25 (1) ◽  
pp. 322

The FDA has been regulating genetically engineered (GE) animals under the new animal drug provisions of the Federal Food, Drug, and Cosmetic Act (FD&C Act or the Act) since producers of these animals first approached the agency in the mid-1990s, although it did not issue a final Guidance for Industry clarifying its statutory authority until 2009 (Regulation of Genetically Engineered Animals Containing Heritable rDNA Constructs: http://www.fda.gov/downloads/AnimalVeterinary/GuidanceComplianceEnforcement/GuidanceforIndustry/UCM113903.pdf). The regulatory trigger that enables the regulation of these animals under the new animal drug provisions of the Act is the definition of a drug as “an article (other than food) that is intended to affect the structure or any function of the body of man or other animals.” The products of modern biotechnology (such as spliced recombinant DNA) are technically the “articles” that must be approved, but for shorthand, we often refer to the regulation of “genetically engineered” animals. For the purpose of the guidance, FDA defined “genetically engineered (GE) animals” as those animals modified by rDNA techniques, including all progeny that contain the modification. The term GE animal can refer both to an animal with a heritable rDNA construct or its residues and to an animal with a nonheritable rDNA construct (e.g. a construct intended as therapy for a disease in that animal). If the agency engages in an “action,” such as an approval, obligations under the National Environmental Policy Act (NEPA) are triggered, such that the agency must perform an environmental assessment to determine whether a significant impact is likely to occur on the environment of the United States. If not, the agency issues a Finding of No Significant Impact (FONSI). If a significant impact is likely to occur as the result of an agency action, the agency must engage in a more complex process to characterise that impact in an Environmental Impact Statement (EIS). This regulation is consistent with the Coordinated Framework for the Regulation of Biotechnology, a policy that was first issued by issued by the Office of Science and Technology Policy [51 Fed Reg 23,302 (1986)] of the United States Government. It describes the interagency mechanism for “sharing scientific information related to biotechnology,” and states that, to the extent possible, jurisdiction of the products of biotechnology lies with a single agency. Where more than one agency will review a particular product, “the policy establishes a lead agency and consolidated or coordinated reviews.” Consistent with this policy, FDA has leveraged, and intends to continue to leverage, the expertise of other agencies in the review of GE animal-related applications. Under certain conditions, based on risk, the agency may not enforce the premarket approval requirement for some GE animals. In general, these include GE animals of non-food species that are regulated by other government agencies or entities, such as GE animals of non-food species that are raised and used in contained and controlled conditions such as GE laboratory animals (e.g. mice, rats, some model fish) used in research institutions. In addition, on a case-by-case basis, the agency may consider exercising enforcement discretion for GE animals of very low risk, non-food species GE animals, such as the Zebra danio aquarium fish genetically engineered to fluoresce in the dark (GloFish). An exemption from the prohibition on introducing an unapproved new animal drug in interstate commerce is provided for in the regulations covering “investigations,” which allow for lawful research to occur, including the shipping of GE animals or their gametes from the sponsor of an investigation to other qualified investigators. These and other responsibilities are outlined in GFI 187, as are recommendations for the submission of data to be reviewed by CVM’s hierarchical risk-based review, and will be the subject of this talk.


2003 ◽  
Vol 13 (3) ◽  
pp. 99-111 ◽  
Author(s):  
Edwin Barth ◽  
Richard Rupert ◽  
Fred Stroud ◽  
Eugene Rice ◽  
Bruce Potoka

2010 ◽  
Vol 7 (4) ◽  
pp. 437-450
Author(s):  
Rik Mellenbergh

AbstractEnvironmental issues, such as site contamination and compliance with environmental permits and rules, are often of importance with respect to corporate mergers and acquisitions or transfers of sites. This paper focuses on specific environmental acts applicable in some states in the United States and in the region of Flanders (Belgium), the so called transaction (or transfer) triggered environmental acts. These acts are applicable—'triggered'—if a transaction or transfer as defined in the transaction triggered environmental act occurs. The applicability of these acts is thus linked to a transaction or transfer as defined in the transaction triggered environmental act. In this paper these transaction triggered environmental acts will be analyzed, and both possible positive and negative effects linked to the introduction of such an act will be discussed with respect to the transaction triggered environmental acts currently applicable in certain states in the United States and in the region of Flanders (Belgium).


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