Coordinates | 28°1′0″N153°24′0″N |
---|---|
Name | Mark 84 General Purpose (GP) Bomb |
Origin | United States |
Type | Low-drag general purpose bomb |
Is explosive | yes |
Unit cost | $3,100 |
Variants | |
Weight | 2039 lb (925 kg) |
Length | 129 in (3280 mm) |
Diameter | 18 in (458 mm) |
Crew | |
Filling | Tritonal, Minol or Composition H6 |
Filling weight | 945 lb (429 kg) |
Yield | }} |
The Mark 84 is an American general-purpose bomb, it is also the largest of the Mark 80 series of weapons. Entering service during the Vietnam War, it became a commonly used US heavy unguided bomb (due to the amount of High-explosive content packed inside) to be dropped, second only to the BLU-82 "Daisy Cutter" then in service and presently third only to the GBU-43/B Massive Ordnance Air Blast bomb (MOAB) currently in service. Pilots flying the F-117 Nighthawk over Iraq during the first gulf war nicknamed it the "Hammer" (albeit fitted with the GBU-24 Paveway III kit for use specially by the ''Nighthawks''), for its considerable destructive power and blast radius.
The Mark 84 has a nominal weight of , but its actual weight varies depending on its fin, fuze options, and retardation configuration, from . It is a streamlined steel casing filled with of Tritonal high explosive.
The Mark 84 is capable of forming a crater wide and deep. It can penetrate up to of metal or of concrete, depending on the height from which it is dropped, and causes lethal fragmentation to a radius of .
Many Mark 84s have been retrofitted with stabilizing and retarding devices to provide precision guidance capabilities. They serve as the warhead of a variety of precision-guided munitions, including the GBU-10 and GBU-24 Paveway laser-guided bombs, GBU-15 electro-optical bomb, GBU-31 JDAM and Quickstrike sea mines.
According to a test report conducted by the United States Navy's Weapon System Explosives Safety Review Board (WSESRB) established in the wake of the 1967 USS Forrestal fire, the cooking off time for a Mk 84 is approximately 8 minutes 40 seconds.
Category:Cold War aerial bombs of the United States Category:Aerial bombs of the United States
cs:Mark 84 es:Mark 84 it:Mk 84 he:פצצת סימן 84 hu:Mk 84 pl:Bomba Mark 84 pt:Mark 84 ru:Mark 84 fi:Mk 84 tr:MK-84 uk:Mark 84 vi:MK 84This text is licensed under the Creative Commons CC-BY-SA License. This text was originally published on Wikipedia and was developed by the Wikipedia community.
A landfill site (also known as tip, dump or rubbish dump and historically as a midden), is a site for the disposal of waste materials by burial and is the oldest form of waste treatment. Historically, landfills have been the most common methods of organized waste disposal and remain so in many places around the world.
Landfills may include internal waste disposal sites (where a producer of waste carries out their own waste disposal at the place of production) as well as sites used by many producers. Many landfills are also used for waste management purposes, such as the temporary storage, consolidation and transfer, or processing of waste material (sorting, treatment, or recycling).
A landfill also may refer to ground that has been filled in with rocks instead of waste materials, so that it can be used for a specific purpose, such as for building houses. Unless they are stabilized, these areas may experience severe shaking or liquefaction of the ground in a large earthquake.
During landfill operations the waste collection vehicles are weighed at a weighbridge on arrival and their load is inspected for wastes that do not accord with the landfill’s waste acceptance criteria. Afterward, the waste collection vehicles use the existing road network on their way to the tipping face or working front where they unload their load. After loads are deposited, compactors or dozers are used to spread and compact the waste on the working face. Before leaving the landfill boundaries, the waste collection vehicles pass through the wheel cleaning facility. If necessary, they return to the weighbridge in order to be weighed without their load. Through the weighing process, the daily incoming waste tonnage can be calculated and listed in databases. In addition to trucks, some landfills may be equipped to handle railroad containers. The use of 'rail-haul' permits landfills to be located at more remote sites, without the problems associated with many truck trips.
Typically, in the working face, the compacted waste is covered with soil daily. Alternative waste-cover materials are several sprayed-on foam products and temporary blankets. Blankets can be lifted into place with tracked excavators and then removed the following day prior to waste placement. Chipped wood and chemically 'fixed' bio-solids may also be used as an alternate daily cover. The space that is occupied daily by the compacted waste and the cover material is called a daily cell. Waste compaction is critical to extending the life of the landfill. Factors such as waste compressibility, waste layer thickness and the number of passes of the compactor over the waste affect the waste densities.
Most modern landfills in industrialized countries are operated with controls to attempt to manage problems such as these. Analysis of common landfill operational problems are available.
Some local authorities have found it difficult to locate new landfills. Communities may charge a fee or levy in order to discourage waste and/or recover the costs of site operations. Many landfills are publicly funded, but some are commercial businesses, operated for profit.
Landfilling practices in the UK have had to change in recent years to meet the challenges of the European Landfill Directive. The UK now imposes landfill tax upon biodegradable waste which is put into landfills. In addition to this the Landfill Allowance Trading Scheme has been established for local authorities to trade landfill quotas in England. A different system operates in Wales where authorities are not able to 'trade' between themselves, but have allowances known as the Landfill Allowance Scheme.
In 2003, there were 254 licensed landfills in Scotland.
Landfills can be regarded as a viable and abundant source of materials and energy. In the developing world, this is widely understood and one may thus often find waste pickers scavenging for still usable materials. In a commercial context, landfills sites have also been discovered by companies and many have begun harvesting materials and energy . Well known examples are gas recovery facilities. Other commercial facilities include fossil fuel power plants and waste incinerators which have built-in material recovery. This material recovery is possible through the use of filters (electro filter, active carbon and potassium filter, quench, HCL-washer, SO2-washer, bottom ash-grating, etc.). An example of these is the AEB Waste Fired Power Plant. The AEB waste incinerator is hereby able to recover a large part of the burned waste in source materials. According to Marcel van Berlo (who helped build the plant), the processed waste contained higher percentages of source materials than any mine in the world. He also added that when the plant was compared to a Chilean copper mine, the waste fired plant could recover more copper. However, because of the high concentration of gases and the unpredictability of the landfill contents, which often include sharp objects, landfill excavation is generally considered dangerous. Furthermore, the quality of materials residing within landfills tends to degrade and such materials are thought to be not worth the risks required to recover them.
The alternatives to landfills are waste reduction and recycling strategies. Secondary to not creating waste, there are various alternatives to landfills. In the late 20th century, alternative methods of waste disposal to landfill and incineration have begun to gain acceptance. Anaerobic digestion, composting, mechanical biological treatment, pyrolysis and plasma arc gasification have all began to establish themselves in the market.
In recent years, some countries, such as Germany, Austria, Belgium, the Netherlands, and Switzerland, have banned the disposal of untreated waste in landfills. In these countries, only the ashes from incineration or the stabilized output of mechanical biological treatment plants may still be deposited.
ar:مركز ردم النفايات ay:T'una uchaña bn:আবর্জনাভূমি bs:Deponija ca:Abocador cs:Skládka da:Losseplads de:Deponie el:Χώρος Υγειονομικής Ταφής Απορριμμάτων es:Vertedero (basura) eo:Rubodeponejo fa:خاکچال fr:Décharge (déchet) hr:Odlagalište otpada id:Tempat pembuangan akhir is:Landfylling it:Discarica di rifiuti he:מטמנה lv:Izgāztuve lt:Sąvartynas nl:Vuilnishoop ja:最終処分場 no:Deponi oc:Descarga pl:Składowisko odpadów pt:Aterro sanitário ru:Свалка simple:Landfill sl:Smetišče sr:Депонија sh:Deponija fi:Kaatopaikka sv:Soptipp uk:Звалище zh-yue:垃圾堆填區 zh:堆填
This text is licensed under the Creative Commons CC-BY-SA License. This text was originally published on Wikipedia and was developed by the Wikipedia community.
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