Handling Heavy Debris: The Right Dumpster for the Job

North American open-top dumpster

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: "Roll-off" dumpster – news · newspapers · books · scholar · JSTOR (February 2015) (Learn how and when to remove this message)

The examples and perspective in this article may not represent a worldwide view of the subject. You may improve this article, discuss the issue on the talk page, or create a new article, as appropriate. (December 2010) (Learn how and when to remove this message)

This article has multiple issues. Please help improve it or discuss these issues on the talk page. (Learn how and when to remove these messages)

(Learn how and when to remove this message)

In North America, a roll-off is usually an open-top dumpster characterized by a rectangular footprint, utilizing wheels to facilitate rolling the dumpster in place. The container is designed to be transported by special roll-off trucks. There are two types of delivery trucks for the bins based on bin size, and they are: Hook lift bins and Roll-off bins.^[1] Roll-offs are commonly used to contain loads of construction and demolition waste or other waste types. While most roll-off containers have a swinging door on the end for easier disposal of waste, some roll-off containers are not open-top and are used with commercial or industrial trash compactors.

Construction debris may originate from a building site where something is being built, renovated, or demolished. Roll-off dumpsters are also used for various jobs that need much material to be taken away. The material in the roll-off may be taken to a landfill, recycled or disposed/recovered of in some other way.

Size

[edit]

Roll-off containers have a rectangular footprint, typically determined by the size of typical trucks. Roll-off container sizes are determined by the amount of debris they can hold, measured in cubic yards.^[2] Container sizes commonly found in the United States include 10, 15, 20, 30, and 40 cubic yards, equivalent to approximately 7.65 m³, 11.47 m³, 15.29 m³, 22.94 m³, and 30.58 m³.^[3][4] In other countries, these sizes span from 2 to 40 cubic meters, approximately ranging from 2.6 to 52.3 cubic yards.

While the roll-offs may be rented by volume, there may be weight limitations. Weight limits may be necessary to ensure compliance with road-use and safety laws and regulations. Most roll-off providers will have a weight limit for each container size. Containers loaded with more weight than allowed typically will not be hauled away due to safety reasons. Containers that are overloaded can result in damage to the roll-off truck and the road it drives on. The maximum weight is specified at the beginning of the job. In cases where the material to be disposed of is especially dense, such as dirt, rock, or concrete, a container with lower sidewalls is used. This is to help reduce the risk of exceeding the weight limit. The standard weight limit determined by the department of transportation is not to exceed ten (10) tons of debris. ^{[citation needed]}

Operation

[edit]

After the container is picked up, it is taken to a disposal facility where it is weighed before (gross) and after (tare) dumping. The difference is the net weight, and is used to calculate charges to the customer. For efficiency, some facilities pre-record weights of trucks and containers. This allows the tare weight to be looked up and eliminates the need for a second weighing.

Roll-offs are placed by roll-off trucks. As the roll-off truck raises its hydraulically operated bed, the roll-off container rolls off the bed. A cable is used to slowly lower the container. After the waste container is loaded, the roll-off truck pulls the filled container onto the roll-off truck with the cable and winch system. If the roll-off truck is not a winch system, then it is most likely a hook-lift system. A hook-lift system works by the truck extending a 90 degree arm with a hook on the end which hooks under a bar and gently lifts the dumpster onto the truck. Most hook-lift systems are on smaller roll-off trucks, as they are usually used for 20-yard containers and under. These smaller systems are usually the preferred option on smaller scale construction jobs such as roof replacement, kitchen remodels, and garage clean-outs. Smaller single-axle trucks are generally viewed as safer operations as they are much lighter and more easily transported in residential areas. When carried, the roll-off must be covered with a tarp.

Cost factors

[edit]

There are three parts to roll-off dumpster pricing: dump rate, haul rate, and overage fees. Dumpster rental companies pay the landfill, transfer station, recycling center, or other type of disposal facility a fee to dump the customer's waste. Fees fluctuate from area to area and facility to facility. Dump fees can be the majority of the cost for the dumpster, and are measured in short tons in the U.S. The haul rate is the rate that roll-off rental companies charge to cover operating costs and generate profit. Overage fees are additional fees the customer must pay if the dumpster is loaded more than the allotted tonnage limit. Overage fees are typically prorated and the same as the company's dump rate.

Disadvantages

[edit]

This section does not cite any sources. Please help improve this section by adding citations to reliable sources. Unsourced material may be challenged and removed. (July 2020) (Learn how and when to remove this message)

One problem often encountered with roll-off containers is the liability of scratching or damaging the surface they are placed on. Most roll-off containers have metal rollers for wheels, which can at times scratch or be abrasive to a concrete or asphalt surface. It is recommended to place a protective board such as plywood under the container to avoid a situation where the placement surface can be damaged. Most roll-off companies do not offer plywood, but will place the container on the wood if supplied. The roll-off must be placed on a hard surface other than dirt. Gravel, asphalt, and concrete are all acceptable. If the container is placed on dirt, the wheels may sink after a rainfall event and the truck could get stuck.

There are many items that are not accepted by roll-off rental companies. These items include but are not limited to chemicals, including paint and petroleum products, tires, and electronics. The prohibition of items is often to comply with laws and regulations concerning disposal of hazardous materials. Roll-off drivers may refuse to pick up loads containing prohibited materials. If the load is picked up, the roll-off rental company may charge the customer additional for cleaning the load and proper handling of the contaminating material.

Some municipalities require that a permit be obtained in order to have a roll-off dumpster delivered. If the container is being set on private property, most cities will not require a permit. Some municipalities require the permit to be obtained by the customer, while others require the permit to be obtained by the roll-off provider. However, many cities do not require permits to have a dumpster delivered.

There are usually prohibited items that are commonly not allowed for disposal, such as hazardous materials, tires, freon appliances, televisions, paint, asbestos, batteries, oils, fuels, and tar-treated railroad ties because of regulations affecting final waste disposal.^[5]

Part of a series on
Pollution
Polyurethane insulator material marked for removal of the construction site (of a residential building)
Air Acid rain Air quality index Atmospheric dispersion modeling Chlorofluorocarbon Combustion Exhaust gas Haze Global dimming Global distillation Indoor air quality Non-exhaust emissions Ozone depletion Particulates Persistent organic pollutant Smog Soot Volatile organic compound
Biological Biological hazard Genetic Illegal logging Introduced species Invasive species
Digital Information
Electromagnetic Light Ecological Overillumination Radio spectrum
Natural Ozone Radium and radon in the environment Volcanic ash Wildfire
Noise Transportation Health effects from noise Marine mammals and sonar Noise barrier Noise control Soundproofing
Radiation Actinides Bioremediation Depleted uranium Nuclear fission Nuclear fallout Plutonium Poisoning Radioactivity Uranium Radioactive waste
Soil Agricultural Land degradation Bioremediation Defecation Electrical resistance heating Illegal mining Soil guideline values Phytoremediation
Solid waste Advertising mail Biodegradable waste Brown waste Electronic waste Foam food container Food waste Green waste Hazardous waste Industrial waste Litter Mining Municipal solid waste Nanomaterials Plastic Packaging waste Post-consumer waste Waste management
Space Space debris
Thermal Urban heat island
Visual Air travel Advertising clutter Overhead power lines Traffic signs Urban blight Vandalism
War Chemical warfare Herbicidal warfare Agent Orange Nuclear holocaust Nuclear fallout Nuclear famine Nuclear winter Scorched earth Unexploded ordnance War and environmental law
Water Agricultural wastewater Biosolids Diseases Eutrophication Firewater Freshwater Groundwater Hypoxia Industrial wastewater Marine Monitoring Nonpoint source Nutrient Ocean acidification Oil spill Pharmaceuticals Freshwater salinization Septic tanks Sewage Shipping Sludge Stagnation Sulfur water Surface runoff Turbidity Urban runoff Water quality Wastewater
Topics History Pollutants Heavy metals Paint
Misc Area source Brain health and pollution Debris Dust Garbology Legacy Midden Point source Waste Toxic Lists Diseases Law by country Most polluted cities Least polluted cities by PM2.5 Treaties Most polluted rivers Categories By country
Environment portal Ecology portal

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