The authorities in charge of managing our Andean basins work in unimaginable water-powered landscapes from the Peruvian legislator point of view. They should generate and apply peculiar mechanisms. Why? Because the national legislator is traditionally positioned on the coast, a region very different to the Andean highlands and punas. The use of ethnographic evidence coming from a drainage basin in the Central Andes (Mantaro River, Junin) lets me depict in detail how public officers appeal to mechanisms of location, adaptation and regulation in order to adjust the official regulations, to cover the needs of the farming organizations of watering, and to affirm their positions as representatives of the Peruvian government. The consequence is that they exceed and also violate the regulatory channels that control their administrative functions. In this way, they incorporate a new function to their official position, that is, to develop peculiar administrative patterns to process the tightness between the inflexibility of the State Water Right and the demands of recognition and balance that the andean watering organizations propose to the Government. / Las autoridades encargadas de gestionar nuestras cuencas andinas ejercen sus funciones en paisajes hidráulicos inimaginables para el legislador peruano. Para ello deben generar y aplicar mecanismos peculiares. ¿Por qué? Porque el legislador nacional se encuentra tradicionalmente parapetado en la costa, una región muy diferente a las sierras y punas andinas. El uso de evidencia etnográfica proveniente de una cuenca hidrográfica de los Andes Centrales (Río Mantaro, Junín) me permite detallar cómo los funcionarios estatales apelan a los mecanismos de localización, adaptación y regularización con el fin de modular la normatividad oficial, atender las necesidades de las organizaciones campesinas de riego y afirmar su papel como representantes del Estado peruano. El resultado es que desbordan y hasta violan los cauces normativos que regulan sus funciones administrativas. De este modo, incorporan una nueva función a su papel oficial que consiste en desarrollar peculiares prácticas administrativas para procesar la tensión entre la rigidez del derecho estatal de aguas y las demandas de reconocimiento y articulación que los regantes andinos le plantean al Estado.

Section 316(b) of the Clean Water Act requires thermal power generating facilities to minimize adverse environmental impact resulting from the operation of cooling water intake structures (CWIS). Adverse environmental impact can occur when aquatic organisms are impinged on traveling water screens. Modified traveling screens were developed to improve the post-impingement survival of organisms. These screens have been used at a few power plants and are now being considered at additional facilities to reduce the mortality of juvenile and adult fish. Existing biological efficacy data show that post-impingement survival is highly variable by species. The majority of previous installations are at estuarine facilities. As such, there is a lack of biological efficacy data with many of the freshwater species commonly impinged at CWIS. In addition, most of the existing modified screen installations were installed prior to 1990. Since that time, improvements in screen designs have increased survival. For these reasons, the existing biological efficacy of the new screen designs was limited and largely unknown for many freshwater species. The mortality, injury, and scale loss rates of 10 species of freshwater fish impinged and recovered with a modified traveling screen were evaluated in the laboratory. Species tested included: golden shiner (Notemigonus crysoleucas); fathead minnow (Pimephales promelas); white sucker (Catostomus commersoni); bigmouth buffalo (Ictiobus cyprinellus); channel catfish (Ictalurus punctatus); hybrid striped bass (Morone chrysops × M. saxatilis); bluegill (Lepomis macrochirus); largemouth bass (Micropterus salmoides); yellow perch (Perca flavescens); and freshwater drum (Aplodinotus grunniens). Fish were impinged at 0.3, 0.6, or 0.9 m•s-1 velocity. Mortality, injury, and scale loss rates were generally low. Mortality rates did not exceed 5% for any species and velocity tested, indicating that this technology has potential to substantially reduce impingement mortality at CWIS. Despite a general trend toward increasing mortality at higher velocities, velocity was only a significant factor in the mortality of bluegill (P=0.0005). Injury and scale loss rates were low for most species tested, although they were more variable than observed rates of mortality. There was a trend toward lower mortality, injury, and scale loss in larger fish. In all cases where fish length was a significant factor (P<0.05), the pattern of decreasing mortality, injury, and scale loss as fish increased in length was constantly observed. Additional tests were undertaken with channel catfish, fathead minnow, and golden shiner to assess the effect of duration of impingement on mortality, injury, and scale loss. Longer durations of impingement appeared to result in higher mortality, injury, and scale loss, especially at durations of impingement greater than 6 minutes. However, longer durations of impingement could be avoided at most cooling water intake structures by continuously rotating screens.

No description available.

This paper tries to answer the question related to the implementation of one of Europe's most influential EU-directives, the Water Framework Directive. The Directive requires Member States to achieve good ecological potential and good surface water chemical status for bodies of water until year 2015. If the states cannot achieve those objectives within this period, then there may be grounds for exemptions from the requirement to prevent further deterioration of to achieve good status under specific conditions. One of those conditions could be that, the completing the improvements within the timescale would be disproportionately expensive. Question which is examined in this paper is, what criteria would be most appropriate for determining the disproportionate costs. Based on the review of most WFD-related studies and EU legislation are selected criteria, which should be used for the assessment of the disproportionate costs.

No description available.

No description available.

Text in Afrikaans / Die private persoon het sekere bevoegdhede betreffende die arrestasie en die gebruik van geweld tydens arrestasie van lede van die publiek wat misdade pleeg/gepleeg het. Hierdie bevoegdheid spruit uit sowel die gemenereg as die wettereg. Kragtens die Suid-Afrikaanse Strafproseswet word hierdie bevoegdhede gereel deur aa 42 en 49. Oewerbewoners as eienaars van grand is geregtig op die onverstoorde gebruik en genot van hulle eiendom. Daarteenoor is kanovaarders ook daarop geregtig om op openbare ri vi ere vir wedvaarte te oefen. Di t is egter belangrik om vas te stel of die portage van kano's op die oewer insidenteel is tot die reg om op die rivier te vaar. Ewewig moet bewerkstellig word tussen die botsende belange. Die Waterwet 54 van 1956 behoort gewysig en vereenvoudig te word, aangesien Suid-Afrika nie slegs op die RomeinsHollandse reg kan staatmaak nie - ons waterprobleme staan direk teenoor die van die Nederlande. / The private person has certain powers regarding the arrest and the use of force to effect the arrest of members of the public who have committed/are committing offences. These powers are derived from either common law or statutory law. In terms of the South African Criminal Procedure Act these powers are regulated by ss 42 and 49. Riparian owners are entitled to the undisturbed use and enjoyment of their property. On the other hand, canoeists are also entitled to practise on public rivers. It is important, however, to ascertain whether portage of canoes on the river bank is incidental to the right of canoeing on the river. A balance should be struck between these conflicting interests. The Water Act 54 of 1956 should be amended and simplified, since South Africa cannot rely on Roman Dutch law alone - our water problems are the complete opposite of those in the Netherlands. / Criminal & Procedural Law / LL.M. (Straf- en Strafprosesreg)

This study assessed the feasibility and suitability of a Water Quality Trading (WQT) program within the Kentucky River Basin (KRB). The study’s focal point was based on five success factors of a WQT program: environmental suitability, geospatial orientation, participant availability, regulatory incentive, and economic incentive. The study utilized these five success factors, geographical characteristics, and Discharge Monitoring Reports (DMR) to assess the feasibility of a WQT program. The assessment divided the KRB into five eight digit Hydrologic Unit Codes (HUC), North, Middle, and South Fork, Middle Basin, and Lower Basin, to determine regional impacts caused by the nutrient PSs. Individual nutrient profiles were generated to show the number of point sources (PS) operating in the KRB, their geospatial orientation to one another, and their permitted nutrient limits and nutrient discharges in form of total phosphorus (TP), total nitrogen (TN), and total nitrogen (as ammonia) (TA). Findings suggest trading is highly unlikely for TP and TN PSs due to the lack of regulatory standards, limited number of TN and TP PSs, and an inadequate demand for offset credits. Trading is also unlikely in all the HUC 8 watersheds except for the Lower Basin due to the lack of nutrient impaired waters. Key Words: Point Source, Non-Point Source, Water Quality Trading, TMDL, Impaired Waters

Thesis (M. En.)--Miami University, Institute of Environmental Sciences, 2006. / Title from first page of PDF document. Includes bibliographical references (p. 35 [1st set of paginations]).

Thesis (Ph. D.)--Miami University, Dept. of Botany, 2004. / Title from second page of PDF document. Includes bibliographical references.