942 resultados para Water Act 2007


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Wetlands are extremely valuable natural features that have decreased significantly in number over time in Illinois and the United States ... Their important functions include flood protection, water conservation in times of drought, groundwater recharge, improvement of water quality through sediment reduction and contaminant removal, and providing habitat for native animals and plants, including many sensitive and state-listed threatened and endangered species ... Due to a federal "no net loss" policy on wetlands adopted through executive order by President George H. Bush in 1990, as well as a prevailing heightened interest in conservation in general, there is currently considerable interest in the restoration and creation of wetlands. Both Section-404 of the Clean Water Act of 1972 and the Swampbuster Provision of the Food Securities Act of 1985 require compensation or mitigation for the loss of wetlands. A number of federal and state programs such as Section 319 of the Clean Water Act and the Conservation Reserve Program within the Natural Resources Conservation Service (NRCS) encourage wetland restoration and creation. In addition, various conservation organizations, such as The Nature Conservancy and Ducks Unlimited are very active in wetland restoration. Despite wetland restoration efforts and the national goal of no net loss, wetlands and wetland functions continue to be lost due to degradation of existing wetlands ... Unfortunately, no reliable information exists on the quality of existing wetlands or on trends in wetland quality over time ... The functional quality of existing wetlands is likely decreasing in many areas due to the combined effects of habitat fragmentation, alteration of hydrology, invasive species, and continued input of nutrients and pollutants. Furthermore, it is still debatable whether created or restored wetlands can adequately replace the suite of ecological functions provided by natural wetlands ... and the failure of many wetland compensation projects contributes to a continued national net loss of wetland functions ... The need for post-construction site monitoring and assessment of created and restored wetlands to evaluate functional success is widely recognized. ... At this time, there is little agreement on how to assess the success on quality of wetland restorations or creations.

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"This report was financed in part by a grant from the U.S. Environmental Protection Agency under section 314 of the Clean Water Act."

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According to Section 305(b) of the Clean Water Act (i.e. a generic name that refers to the Federal Water Pollution Control Act of 1972, the Clean Water Act of 1977, and subsequent amendments) and guidance provided by the United States Environmental Protection Agency (USEPA), each state must prepare and submit annually to the U.S. Congress and the USEPA report that describes the resource quality of the surface waters of the state. Every other year, this report, commonly referred to as the "305(b) report," must be provided in written form, whereas in alternate years each state may submit an electronic database to meet the reporting requirement. In the 305(b) report, states must also explain how they determined the resource quality of the waters of the state in terms of the degree to which predefined beneficial uses of those waters are supported. Also, in the 305(b) report when any designated use for any water body is not fully supported, the state must report potential reasons for the impairment. Herein, is explained how the Illinois Environmental Protection Agency determines the resource quality of Illinois streams, inland lakes, and Lake Michigan.

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The purpose of this report is to fulfill the requirements set forth in Section 303(d) of the Federal Clean Water Act (CWA) and the Water Quality Planning and Management regulation at 40 CFR Part 130 for the year 2002 [and to] inform the public about the Total Maximum Daily Load (TMDL) program process. This report is submitted to the USEPA for review and approval of Illinois' list of water quality limited waters. It provides the state's supporting documentation required by 40 CFR Part 130.7 and rationale in fulfilling Section 303(d) requirements.

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"Prepared for the City of Paris, Illinois."

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"This report was financed in part by a grant from the U.S. Environmental Protection Agency under Section 314 of the Clean Water Act."

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"IDNR/OWR/SPS/07-001"

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Nanotechnologies have been called the "Next Industrial Revolution." At the same time, scientists are raising concerns about the potential health and environmental risks related to the nano-sized materials used in nanotechnologies. Analyses suggest that current U.S. federal regulatory structures are not likely to adequately address these risks in a proactive manner. Given these trends, the premise of this paper is that state and local-level agencies will likely deal with many "end-of-pipe" issues as nanomaterials enter environmental media without prior toxicity testing, federal standards, or emissions controls. In this paper we (1) briefly describe potential environmental risks and benefits related to emerging nanotechnologies; (2) outline the capacities of the Toxic Substances Control Act, the Clean Air Act, the Clean Water Act, and the Resources Conservation and Recovery Act to address potential nanotechnology risks, and how risk data gaps challenge these regulations; (3) outline some of the key data gaps that challenge state-level regulatory capacities to address nanotechnologies' potential risks, using Wisconsin as a case study; and (4) discuss advantages and disadvantages of state versus federal approaches to nanotechnology risk regulation. In summary, we suggest some ways government agencies can be better prepared to address nanotechnology risk knowledge gaps and risk management.

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This factsheet for CIPD members was last updated in June 2013. Background to the Vetting and Barring Scheme The Vetting and Barring Scheme was introduced on 12 October 2009 following the Soham case which concerned the murder of Holly Wells and Jessica Chapman by Ian Huntley. The Bichard Report into the case made a series of recommendations which were implemented in England, Wales and Northern Ireland by the Safeguarding Vulnerable Groups Act 2006. It was also implemented in Scotland by the Protection of Vulnerable Groups (Scotland) Act 2007. Login or register for a free account to continue reading this factsheet and to learn about: •Background to the Vetting and Barring Scheme •Changes under the Protection of Freedoms Act 2012 •Filtering of of old and minor cautions and convictions •Barred lists •Criminal offences •Action points •Useful contacts •Further reading

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Over the past 200 years, an estimated 53% (about 47 million ha) of the original wetlands in the conterminous United States have been lost, mainly as a result of various human activities. Despite the importance of wetlands (particularly along the coast), and a longstanding federal policy framework meant to protect their integrity, the cumulative impact on these natural systems over large areas is poorly understood. We address this lack of research by mapping and conducting descriptive spatial analyses of federal wetland alteration permits (pursuant to section 404 of the Clean Water Act) across 85 watersheds in Florida and coastal Texas from 1991 to 2003. Results show that more than half of the permits issued in both states (60%) fell under the Nationwide permitting category. Permits issued in Texas were typically located outside of urban areas (78%) and outside 100-year floodplains (61%). More than half of permits issued in Florida were within urban areas (57%) and outside of 100-year floodplains (51%). The most affected wetlands types were estuarine in Texas (47%) and palustrine in Florida (55%). We expect that an additional outcome of this work will be an increased awareness of the cumulative depletion of wetlands and loss of ecological services in these urbanized areas, perhaps leading to increased conservation efforts.

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We reflect on the politics of establishing catchment management agencies in South Africa with a specific focus on the Breede-Overberg Catchment Management Agency (BOCMA), which was recently replaced by the Breede-Gouritz Catchment Management Agency (BGCMA). We do so by applying the framework of adaptive comanagement and its institutional prescriptions: collaboration, experimentation, and a bioregional approach. We start by introducing the history of this catchment management agency (CMA) and then describe the establishment of CMAs in South Africa in general and that of BOCMA in particular. We follow the framework for rule types and types of river basin organizations set out by the editors of this special feature with reference to adaptive comanagement where applicable. We then discuss the politics and strategies involved in the introduction of the CMA concept to the National Water Act and the latest developments around these institutions in South Africa. This is followed by reflections on what can be surmised about BOCMA’s democratic functioning and performance to date. We conclude by reflecting on the future of operations of the new BGCMA and CMAs in South Africa in general. While our research shows that BOCMA’s establishment process has featured several elements of adaptive comanagement and its institutional prescriptions, it remains to be seen to what extent it is possible to continue implementing this concept when further developing and operationalizing the BGCMA and the country’s other CMAs.

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Les dernières décennies ont apporté de grandes transformations à l'élevage porcin, qui est dorénavant considérée comme une agro-industrie composée de quelques grands joueurs à l’échelle internationale. Ces changements structurels ont contribué à l’apparition de problèmes associés à la quantité croissante de lisier produite par le secteur porcin aux États-Unis. Certaines préoccupations environnementales telles que les impacts sur les eaux de surface et souterraine, les effets sur la qualité de l’air et des sols sont notamment soulevées. Par contre, lorsque la gestion et l’épandage du lisier sont faits de manière adéquate en prenant soin d’éviter toute forme de pollution, le lisier est un excellent engrais, riche en nutriments essentiels aux cultures. Actuellement, deux méthodes d’entreposage sont généralisées aux États-Unis : les fosses souterraines pour entreposer le lisier non-dilué et les lagunes ouvertes pour le lisier liquide. La majorité des producteurs valorisent toujours leur lisier par épandage aux champs. Malheureusement, les méthodes actuelles de gestion utilisées ne sont pas jugées durables, ni du point de vue environnemental, social ou économique. Pourtant, plusieurs pratiques durables et efficaces existent et peuvent être introduites de façon relativement simple comme entre autres, l’implantation de bandes riveraines et l’épandage du lisier en post-levée avec des engrais verts. De plus, la valorisation énergétique grâce à un digesteur anaérobie est une option forte intéressante en raison des avantages économiques qui peuvent découler de son utilisation. Pour le moment, ces méthodes restent toujours très marginales. Certains freins sont possiblement responsables de l’inaction face aux problèmes environnementaux causés par le lisier. Entre autres, le fait que les producteurs porcins soient maintenant sous contrats avec des firmes intégratrices, le monopole de certaines compagnies agroalimentaire et les emplois précaires offerts par les industries. Ainsi, après l’analyse de la gestion des lisiers aux États-Unis, plusieurs constats et recommandations ont pu être formulés : la nécessité de mettre en place une loi sur la qualité de l’air, les changements nécessaires au Clean Water Act, l’abolition des lagunes dans le but de mettre en place des méthodes plus durables telles les digesteurs anaérobies, la mise en place de moratoire pour les cheptels dans les régions avec des surplus d’éléments nutritifs dans le sol et enfin le retour graduel à une agriculture à plus petite échelle et locale.

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Illinois State Water Survey

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To better address stream impairments due to excess nitrogen and phosphorus and to accomplish the goals of the Clean Water Act, the U.S. Environmental Protection Agency (EPA) is requiring states to develop numeric nutrient criteria. An assessment of nutrient concentrations in streams on the Delmarva Peninsula showed that nutrient levels are mostly higher than numeric criteria derived by EPA for the Eastern Coastal Plain, indicating widespread water quality degradation. Here, various approaches were used to derive numeric nutrient criteria from a set of 52 streams sampled across Delmarva. Results of the percentile and y-intercept methods were similar to those obtained elsewhere. Downstream protection values show that if numeric nutrient criteria were implemented for Delmarva streams they would be protective of the Choptank River Estuary, meeting the goals of the Chesapeake Bay Total Maximum Daily Load (TMDL).