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Construction waste or debris is any kind of debris from the construction process. Different government agencies have clear definitions. For example, the United States Environmental Protection Agency EPA defines construction and demolition materials as “debris generated during the construction, renovation and demolition of buildings, roads, and bridges.” Additionally, the EPA has categorized Construction and Demolition (C&D) waste into three categories:  non-dangerous, hazardous, and semi-hazardous.^[1]

Of total construction and demolition (C&D) waste in the United States, 90% comes from the demolition of structures, while waste generated during construction accounts for less than 10%.^[2] Construction waste frequently includes materials that are hazardous if disposed of in landfills. Such items include fluorescent lights, batteries, and other electrical equipment.^[3]

When waste is created, options of disposal include exportation to a landfill, incineration, direct site reuse through integration into construction or as fill dirt, and recycling for a new use if applicable. In dealing with construction and demolition waste products, it is often hard to recycle and repurpose because of the cost of processing. Businesses recycling materials must compete with often the low cost of landfills and new construction commodities.^[4] Data provided by 24 states reported that solid waste from construction and demolition (C&D) accounts for 23% of total waste in the U.S.^[5] This is almost a quarter of the total solid waste produced by the United States. During construction a lot of this waste spends in a landfill leaching toxic chemicals into the surrounding environment. Results of a recent questionnaire demonstrate that although 95.71% of construction projects indicate that construction waste is problematic, only 57.14% of those companies collect any relevant data.^[6]

C&D Materials, construction and demolition materials, are materials used in and harvested from new building and civil engineer structures.^[3] Much building waste is made up of materials such as bricks, concrete and wood damaged or unused during construction. Observational research has shown that this can be as high as 10 to 15% of the materials that go into a building, a much higher percentage than the 2.5-5% usually assumed by quantity surveyors and the construction industry. Since considerable variability exists between construction sites, there is much opportunity for reducing this waste.^[7]

There has been a massive increase in construction and demolition waste created over the last 30 years in the United States. In 1990, 135 million tons of construction and demolition debris by weight were created and had risen to 600 million tons by the year 2018. This is a 300% increase, but it is important to note that since 2015 the EPA has kept records of how the waste is disposed of. In 2018, 600 million tons of waste was created due to construction and demolition, and 143 million tons of it resides in landfills.^[2] This means that about 76% of waste is now retained and repurposed in the industry, but there is still more waste being exported to landfills than the entire amount of waste created in 1990.

This unsustainable consumption of raw materials creates increasing business risks. This includes higher material costs or disruptions in the supply chains.^[8] In 2010, the EPA created the Sustainable Materials Management (SMM) Program Strategic Plan which marked a strategic shift by the EPA to move emphasis from broad resource recovery initiative to sustainable materials management. Since material management regulations largely exist at a state and local level, this is no real standard practice across the nation for responsible waste mitigation strategies for construction materials. The EPA aims to increase access to collection, processing, and recycling infrastructure in order to meet this issue head on.

Construction waste can be categorized as follows: Design, Handling, Worker, Management, Site condition, Procurement and External.  These categories were derived from data collected from past research concerning the frequency of different types of waste noted during each type of these activities.^[9] Examples of this type of waste are as follows:

Steel is used as reinforcement and structural integrity in the vast majority of construction projects. The main reasons steel is wasted on a site is due to irresponsible beam cutting and fabrication issues. The worst sites usually end up being the ones that do not have adequate design details and standards, which can result in waste due to short ends of bars being discarded due to improper planning of cuts.^[10] Many companies now choose to purchase preassembled steel reinforcement pieces. This reduces waste by outsourcing the bar cutting to companies that prioritize responsible material use.

Premixed concrete has one of the lowest waste indices when compared to other building materials. Many site managers site the difficulties controlling concrete delivery amounts as a major issue in accurately quantifying concrete needed for a site. The deviations from actually constructed concrete slabs and beams and the design amounts necessary were found to be 5.4% and 2.7% larger than expected, respectively, when comparing the data from 30 Brazilian sites. Many of these issues were attributed to inadequate form layout or lack of precision in excavation for foundation piles. Additionally, site managers know that additional concrete may be needed, and they will often order excess material to not interrupt the concrete pouring.^[10]

It is often difficult to plan and keep track of all the pipes and wires on a site as they are used in so many different areas of a project, especially when electrical and plumbing services are routinely subcontracted. Many issues of waste arise in this area of the construction process because of poorly designed details and irresponsible cutting of pipes and wires leaving short, wasted pipes and wires.^[10]

The second leading cause of construction waste production is improper material storage. Exposure to the elements and miss handling by persons are due to human error.^[10] Part of this human error can lead to illegal dumping and illegal transportation volume of waste from a jobsite.^[11]

Most guidelines on C&D waste management follows the waste managing hierarchy framework. This framework involves a set of alternatives for dealing with waste arranged in descending order of preference. The waste hierarchy is a nationally and internationally accepted concept used to priorities and guide efforts to manage waste. Under the idea of Waste Hierarchy, there is the concept of the "3R's," often known as "reduce, reuse, recycle." Certain countries adopt different numbers of "R's." The European Union, for example, puts principal to the "4R" system which includes "Recovery" in order to reduce waste of materials.^[12] Alternatives include prevention, energy recovery, (treatment) and disposal.

It is possible to recycle many elements of construction waste. Often roll-off containers are used to transport the waste. Rubble can be crushed and reused in construction projects. Waste wood can also be recovered and recycled.

Some certain components of construction waste such as plasterboard are hazardous once landfilled. Plasterboard is broken down in landfill conditions releasing hydrogen sulfide, a toxic gas. Once broken down, Plasterboard poses a threat for increases Arsenic concentration Levels in its toxic inorganic form.^[13] The traditional disposal way for construction waste is to send it to landfill sites. In the U.S., federal regulations now require groundwater monitoring, waste screening, and operator training, due to the environmental impact of waste in C&D landfills (CFR 1996).^[14] Sending the waste directly to a landfill causes many problems:

• Waste of natural resources
• Increases construction cost, especially the transportation process^[15]
• Occupies a large area of land
• Reduces soil quality
• Causes water pollution (Leachate)
• Causes air pollution
• Produces security risks etc.^[16]

Where recycling is not an option, the disposal of construction waste and hazardous materials must be carried out according to legislation of relevant councils and regulatory bodies. The penalties for improper disposal of construction waste and hazardous waste, including asbestos, can reach into the tens of thousands of dollars for businesses and individuals.

Waste-to-energy facilities burn more than 13% of solid municipal waste. The toxic fumes emitted by WTE plants can contain harmful chemicals such as mercury and other heavy metals, carbon monoxide, sulfur dioxide, and dioxins.

Dioxin was used as a waste oil in Times Beach, Missouri. Days after the chemicals were introduced to the community animals began dying. By the time the EPA deemed dioxins to be highly toxic in the 1980s, the CDC recommended the town be abandoned entirely due to contaminated waste products in the area. By 1985, the entire population of Times Beach had been relocated, prompting Missouri to build a new incinerator on the contaminated land. They continued to burn 265,000 tons of dioxin-contaminated waste until 1997.

Dioxins are a family of chemicals produced as a byproduct during the manufacturing of many pesticides and construction materials like carpeting and PVC. These chemicals exist in the environment attached to soil or dust particles that are invisible to the naked eye.

Dioxins break down slowly. It still threatens public health at low levels. Since industry has mostly stopped producing dioxins, one of the largest contributors releasing harmful dioxins left in the United States is waste incineration. Dioxins have been proven to cause cancer, reproductive and developmental issues, and immune system damage. Rates of cancer such as non-Hodgkin's lymphoma and soft tissue sarcoma rise significantly the closer one lives to the pollutants' source.^[17]

Waste management fees, under the 'polluter pays principle', can help mitigate levels of construction waste.^[18] There is very little information on determining a waste management fee for construction waste created. Many models for this have been created in the past, but they are subjective and flawed. In 2019, a study method was proposed to optimize the construction waste management fee. The new model expands on previous ones by considering life-cycle costs of construction waste and weighs it against the willingness to improve construction waste management. The study was based out of China. China has a large waste management issue, and their landfills are mostly filled in urban areas. The results of the study indicated different waste management fees for metal, wood, and masonry waste as $9.30, $5.92, and $4.25, respectively. The cost of waste management per square meter, or just under 11 square feet, on average was found to be $0.12.^[19] This type of waste management system requires top-down legislative action. It is not a choice the contractor has the luxury of making on his/her own.

In the European Union (EU), there is now significant emphasis on recycling building materials and adopting a cradle-to-grave ideology when it comes to building design, construction, and demolition. Their suggestions are much clearer and easier at the local or regional level, depending on government structure. In the 2016 EU Construction & Demolition Waste Management Protocol, they emphasize the benefits beyond financial gains for recycling such as job creation and reduced landfilling. They also emphasize the consideration of supply and demand geography; if the recycling plants are closer to urban areas than the aggregate quarries this can incentivize companies to use this recycled product even if it is not initially cheaper. In Austria, there are new improvements in the recycling of unusable wood products to be burnt in the creation of cement which offsets the carbon footprint of both products.^[20]

The EU urges local authorities who issue demolition and renovation permits to ensure that a high-quality waste management plan is being followed, and they emphasize the need for post-demolition follow-ups in order to determine if the implemented plans are being followed. They also suggest the use of taxation to reduce the economic advantage of the landfills to create a situation where recycling becomes a reasonable choice financially. However, they do include the fact that the tax should only apply to recyclable waste materials. The main points of how the Europeans choose to address this issue of waste management is through the utilization of the tools given to a governing body to keep its people safe. Unlike in the United States, the EU's philosophy on waste management is not that it is an optional good thing to do when you can but a mandatory part of construction in the 21st century to ensure a healthy future for generations to follow.

Taxing landfill has been most effective in Belgium, Denmark and Austria, which have all decreased their landfill disposal by over 30% since introducing the tax. Denmark successfully cut its landfill use by over 80%, reaching a recycling rate over 60%. In the United Kingdom, all personnel performing builders or construction waste clearance are required by law to be working for a CIS registered business.^[21] However, the waste generation in the UK continues to grow, but the rate of increase has slowed.^[22]

 

A panorama of construction waste in Horton, Norway

The United States has no national landfill tax or fee, but many states and local governments collect taxes and fees on the disposal of solid waste. The California Department of Resource Recycling and Recovery (CalRecycle) was created in 2010 to address the growing C&D waste problem in the United States. CalRecycle aids in the creation of C&D waste diversion model ordinance in local jurisdictions. They also provide information and other educational material on alternative C&D waste facilities. They promote these ordinances by creating incentive programs to encourage companies to participate in the waste diversion practices. There are also available grants and loans to aid organizations in their waste reduction strategies.^[22] According to a survey, financially incentivizing stakeholders to reduce construction waste demonstrates favorable results.  This information provides an alternative way to reduce the cost so that the industry is more careful in their project decisions from beginning to end.^[23]

• ATSDR
• Carcinogen
• Construction dust | Metal dust | Metal swarf | Lead dust | Asbestos | Cement dust | Concrete dust | Wood dust | Paint dust
• Concrete recycling
• COPD
• COSHH
• Demolition waste
• NIEHS
• Particulates | Ultrafine particle
• Power tool
• Recycling
• Silicosis
• VOC
• Waste management
• Welding
• Embodied carbon

• Construction Waste Management Database from the Whole Building Design Guide of the National Institute of Building Sciences

This article needs additional citations for verification. Please help improve this article by adding citations to reliable sources. Unsourced material may be challenged and removed. Find sources: "Waste container" – news · newspapers · books · scholar · JSTOR (August 2021) (Learn how and when to remove this message)

A waste container, also known as a dustbin,^[1] rubbish bin, trash can, garbage can, wastepaper basket, and wastebasket, among other names, is a type of container intended to store waste that is usually made out of metal or plastic. The words "rubbish", "basket" and "bin" are more common in British English usage; "trash" and "can" are more common in American English usage. "Garbage" may refer to food waste specifically (when distinguished from "trash") or to municipal solid waste in general. The word "dumpster" refers to a large outdoor waste container for garbage collectors to pick up the contents.

Trash cans are typically made of steel or plastic (most commonly polyethylene), although some are made of wood or wicker.

A pedal bin is a container with a lid operated by a foot pedal. Lillian Moller Gilbreth, an industrial engineer and efficiency expert,^[2] invented the pedal bin in the 1920s for the disposal of kitchen waste. The foot pedal enables the user to open the lid without touching it with their hands.

In the 2010s, some bins have begun to include automated mechanisms such as a lid with infrared detection on the top of the can powered by batteries to open it rather than a foot pedal, freeing the user from touching the bin in any way. This helps prevent the bin lids becoming clogged with trash. These wastes containers are mostly made of stainless steel.^{[citation needed]} Some bin models also include a small receptable for an air freshener.

Legislation surrounding waste receptacles was first introduced in France in an 1883 prefectural order signed by Eugène Poubelle, from whose name the French word for a waste receptacle comes. This order mandated the provision and collection of waste bins to each household in Paris. These bins were specified as having to be between 80 and 120 litres in volume and having a handle and a lid^{[citation needed]}. Three waste bins were to be allocated to each household in order to sort refuse from reclaimable fibres such as paper and cloth and other reusable materials like ceramics, glasses and oyster shells.^[3]

Legislation setting out the responsibilities for the provision and collection of "receptacles for the temporary deposit and collection of dust ashes and rubbish" by local authorities in Britain was first set out in the Public Health Act 1875.^[4] However, this did not mandate the use of them, leaving the decision to offer the service to local government instead.

In many cities and towns, there is a public waste collection service which regularly collects household waste from outside buildings. The waste is loaded into a garbage truck and driven to a landfill, incinerator or crush facility to be disposed of.

In some areas, each household has multiple bins for different categories of rubbish (usually represented by colours) depending on its suitability for recycling, which will instead be routed to a recycling center.^[5]

Roadside waste collection is often done by means of larger metal containers of varying designs, mostly called dumpsters in the US, and skips in the UK. However the functionalities of dumpsters and skips are somewhat different: while a skip is intended to be loaded onto a vehicle and transported, the contents of a dumpster are emptied into a garbage truck on site and the dumpster remains and its designated location.^[6] Adding to this, there is another type of container known as a roll-off dumpster. This type is unique because it's designed for easy transportation and disposal of large amounts of waste. Roll-off dumpsters are set on a truck with a roll-off mechanism, allowing them to be rolled onto and off of the truck bed. This feature makes them particularly useful for large projects like construction, renovation, or extensive clean-ups where substantial amounts of waste are generated. They come in various sizes to accommodate different needs, and unlike regular dumpsters, they are open-topped for easier loading of large or irregularly shaped debris.

Public areas such as parks, often have litter bins placed to improve the social environment by encouraging people not to litter. Such bins in outdoor locations or other busy public areas are usually mounted to the ground or wall to discourage theft, and reduce vandalism, and to improve their appearance are sometimes deliberately artistic or cute.^[7][8] In dense urban areas, trash is stored underground below the receptacle.^[9] Many are lined with a plastic or paper bin bag to help contain liquids.

The term "garbage can" is also used for a model of decision making, the "Garbage Can Model" of decision making. It is concerned with cases of decision making in great aggregate uncertainty which can cause decisions to arise that from a distant point of view might seem irrational.

A "trash can" metaphor is often used in computer operating system desktop environments as a place files can be moved for deletion.

In a workplace setting, a bin may be euphemistically called "the circular file", "the round file" or "the janitor's file". Whereas useful documents are filed in a filing cabinet, which is rectangular, junk mail and other worthless items are "filed" in the bin, which is often round.

The term "wastebasket" is occasionally used in taxonomy to refer to less formal (and often paraphyletic) groupings that pose problems in classification (e.g., the proposed order Insectivora is considered a "wastebasket taxon", as it groups small mammals that do not fit nicely into other taxa), and the Nilo-Saharan language family is sometimes called "Greenberg's wastebasket", as it was a grouping made by him to fit the languages of Africa that did not fall into the other groups, Afroasiatic, Niger–Congo, and Khoisan.

• 
  Public waste container in Nacka, Sweden
• 
  Waste container in Tampere, Finland
• 
  Waste containers at the National Theater in Taipei, Taiwan
• 
  Art on waste containers
• 
  Animal trash can where the opening is the mouth
• 
  Waste container in Tarifa, Spain
• 
  Waste containers in Greece
• 
  A public waste container with a saying in Traiskirchen, Austria
• 
  A recycling bin (blue) and garbage disposal bin (black) available to patrons in a Municipal Park within Toronto, ON
• 
  Waste container typically used in American public schools.
• 
  Garbage can in Pyrgi (Chios). The cover is locked to prevent inserting large items.

• Bin bug
• Clever Bins
• Compost
• Pot farming
• Push the Talking Trash Can
• Recycling bin
• Roll-off (dumpster)
• Waste management
• Oscar the Grouch

• American Public Transportation Association (2008-09-26). "Recommended Practice for Trash/Recycling Container Placement to Mitigate the Effects of an Explosive Event" (PDF). Archived from the original (PDF) on 2016-03-04. Retrieved 2014-09-15.

Wikimedia Commons has media related to Waste containers.

• Example of Waste Design for Recycling in Public Spaces