The invention relates to the field of urban waste recycling and more particularly to municipal organic waste collection systems in multi-unit residential buildings. The invention further relates to the field of food scrap recycling in commercial food preparation areas such as food stores, restaurants, commercial kitchens and hospitality settings.
Urban recycling programs over recent decades have been very successful in the recycling of certain waste materials from residential units, particularly paper, plastics, beverage containers and the like, due to the roadside blue box programs. Recycling of organic wastes, such as kitchen food waste, food-soiled paper, garden clippings etc. has been more challenging. Such waste is separated, collected and delivered to composting centres. However composting centres must reject material which is contaminated with non-compostable plastic, metal or glass. Hence a great deal of care and attention is required in the separation and collection of the compostable material by the individuals involved. This is challenging for home-owners for a number of reasons. First the nature of organic waste is such that it attracts vermin and pests, and has strong odors. There is a tendency therefore to solve the problem by including organic waste with other non-recycled refuse. Also since the bag which is used to transfer the organic waste can only be included with the collected compostable material if such bag itself is compostable, there is a high incidence of the collected material being contaminated with non-compostable plastic, and a reluctance both on the part of users to use the system and composting centres to accept material from untrustworthy sources.
Currently many municipalities require separation of organic waste by single-family residential home-owners. An important factor is that the organic waste contains considerable water and is therefore a large portion, by weight, of the waste produced by a household, and landfills and other waste processing centres charge for processing by weight. However municipalities have been unwilling to include multi-unit residential buildings in such programs for a number of reasons. Such buildings are generally responsible for their own waste collection and pay for same on the basis of weight. However there is a difficulty in such buildings in ensuring the degree of education and care necessary to avoid contamination of the organic waste with non-compostable plastics or other material. For example, there is a high occurrence of residents of such buildings using non-compostable plastic grocery bags to collect, store and transfer the organic waste due to the cost of compostable bags. This results in much higher waste disposal costs for multi-unit residential buildings.
A further problem faced in operating organic waste recycling in multi-unit residential buildings relates to the “transition gap”. This is the distance between each multi-unit residential dwelling unit and a central deposit location for organic waste. In current systems residents transport the loose organic waste in a bucket to the central deposit area. The result is spills and leaks. Without proper containment, organic waste being transported to the central deposit area can spill or leak in common hallway areas and/or stairwells. Further if using an unlined organic waste collection kitchen bin to transport the organic waste to the central deposit area, residents must make a two-way trip, returning their soiled bin to their dwelling unit, rather than dropping the waste off on the way out of the building.
There is therefore a need for improved systems for separating, collecting and transferring organic waste from multi-unit residential buildings to deliver to composting centres which reduce contamination of the organic waste with non-compostable material. There is a further need for systems which can address the transition gap problem in operating organic waste recycling in multi-unit residential buildings.
As noted, traditional material and organic recycling through composting contribute to environmentally sustainable practices which are now mandated in many communities. Many landfills are nearing capacity and programs to divert materials from landfills must be put in place to extend the life of the landfill to avoid closures. New landfills are very difficult to site and permit, particularly near urban areas. Zero Waste Programs serve to mitigate the landfill development problem. Local and regional governments are therefore now implementing zero waste plans and are specifically calling for business community involvement in organic waste (food scraps) diversion and material recycling.
Diverting organic material and food scraps from landfills contributes to the reduction of greenhouse gas, a major contributor of global warming. Landfills account for 17% of methane gas emissions and are a major source of human-related greenhouse gas emissions in North America. Methane is a potent greenhouse gas that results when organic materials such as food scraps biodegrade in a landfill setting. In 2010, 250 million tons of municipal waste was generated in the USA alone. Organics, food scraps and recyclable materials account for as much as two-thirds of the waste currently being disposed of in landfills. Less than 2.8% of the 85 million tons of food scraps were diverted in 2010. Food scraps remain the largest discarded material category in the US municipal waste stream.
There is a significant cost advantage to diverting organic waste and food scraps from the landfill. Landfill tipping fees may be in excess of $100.00 per ton while commercial compost tipping fees can be as low as $40.00/ton for a savings of $60.00/ton. As an example, large grocery stores produce about 20 tons of waste weekly, of which about 17 tons can be diverted to composting. Multi-store grocery chains can realize significant financial savings by diverting their organic waste and thereby reduce their carbon footprint.
The foregoing examples of the related art and limitations related thereto are intended to be illustrative and not exclusive. Other limitations of the related art will become apparent to those of skill in the art upon a reading of the specification and a study of the drawings.
The following embodiments and aspects thereof are described and illustrated in conjunction with systems, tools and methods which are meant to be exemplary and illustrative, not limiting in scope. In various embodiments, one or more of the above-described problems have been reduced or eliminated, while other embodiments are directed to other improvements.
The present embodiments provide effective systems for separating, collecting and transferring organic waste from multi-unit residential buildings to deliver to composting centres which facilitate the reduction of contamination of the organic waste with non-compostable plastic bags. This is accomplished both by ensuring that the residents are constantly provided with compostable replacement bags for their kitchen caddies after each delivery of a bag by the resident to the recycling room, and through consistent marking that reminds residents of the system's requirements.
According to one embodiment, a system is provided for collecting and transferring organic waste from residential units of a multi-unit residential building to deliver to composting centres which facilitates the reduction of contamination of the organic waste with non-compostable plastic bags by ensuring that the residents are constantly provided with compostable replacement bags for their in-residence receptacles after each delivery of a bag by the resident to a recycling area, the building having one or more common recycling areas where waste material is separated and collected for recycling, the system comprising: i) a plurality of first containers each sized and adapted to be stored in a residential unit of the building for receiving a compostable bag for receiving organic waste; ii) a second container located in a recycling area provided with a compostable bag adapted to receive compostable bags from the first container; iii) proximate to the second container, a bag dispenser for dispensing compostable bags for the first container; iv) a plurality of replacement compostable bags for dispensing from the dispenser; v) a plurality of compostable bags sized to be received in the second container for receiving compostable bags from said first container; whereby the bag dispenser is provided with an indicator or signal to alert a system operator that replacement of bags in the dispenser is necessary, whereby each resident who deposits a bag of organic waste from the first container into the second container is provided with an empty compostable bag from the dispenser to replace the bag thereby deposited.
According to a further embodiment there is provided a bag dispenser for dispensing bags for collecting and transferring organic waste from a facility to deliver to composting centres which facilitates the reduction of contamination of the organic waste with non-compostable plastic bags by ensuring that users are constantly provided with compostable replacement bags, the container comprising: i) a hollow container comprising a plurality of compartments each sized and adapted to receive a roll of compostable bags for receiving organic waste; ii) wherein the container is provided with a plurality of slots, each associated with one of the compartments and sized to permit the end of a roll of compostable bags to extend therethrough; whereby the bag dispenser is provided with a plurality of unique indicators, each associated with one of the compartments to indicate the size of bag dispensed from said one of said compartments. The indicators can be associated with the receptacles using the size of bag which is dispensed from the compartment bearing that indicator.
In addition to the exemplary aspects and embodiments described above, further aspects and embodiments will become apparent by reference to the drawings and by study of the following detailed descriptions.
Exemplary embodiments are illustrated in referenced figures of the drawings. It is intended that the embodiments and figures disclosed herein are to be considered illustrative rather than restrictive.
Throughout the following description specific details are set forth in order to provide a more thorough understanding to persons skilled in the art. However, well known elements may not have been shown or described in detail to avoid unnecessarily obscuring the disclosure. Accordingly, the description and drawings are to be regarded in an illustrative, rather than a restrictive, sense.
With reference to
According to the present method, for residents to collect organic waste, a kitchen caddy or bin 12 is provided to each residential unit, preferably along with an information card or cards, for example as shown in
An organic waste container or cart 20 for receiving full or partially full bags 14 of organic waste, or unbagged organic waste, is provided in the aforementioned common areas for access by residents of building 10 to collect organic waste collected by individual residents. The resident is able to deposit the compostable bag 14 containing organic waste from kitchen caddy 12 directly into container 20. Container 20 is itself lined with a compostable plastic cart bag 27 (
To ensure that only acceptable compostable bags are used by residents of the building to deposit organic waste in container 20, adjacent to container 20 in the building's common recycling areas are provided one or more dispensers 22 for replacement compostable bags 14. Steps are taken in order to avoid running out of replacement bags at the recycling location because if the resident is unable to obtain a replacement bag, chances are high that a non-compostable bag will be used as the alternative, which will disrupt the proper operation of the system. In order to avoid running out of replacement compostable bags, slots 80 (as in
Preferably a double supply of bags is provided by using two dispensers 22 or a double-sided dispenser 60 as shown in
The preferred system also facilitates the reduction of contamination of the collected organic waste through the use of systematic educational and planning components. As shown in
The system may also include access to a secure on-line portal page where customers can access and download system components to help with planning, implementation, and ongoing support. System components include, but are not limited to:
Program Planning
Program Implementation
Program Support
Preferably the bags used in the system are certified 100% compostable plastic and meet suitable standards of compostability such as ASTM #D6400 Standard Specifications for Compostable Products, and comply with Biodegradable Products Institute (BPI) specifications or other comparable certification. Preferably the bags 14 are marked with a distinctive mark and colouring, such as the mark ECOSAFE as shown, so that composters immediately recognize that the waste is being transported in certified compostable plastic bags. The preferred bag size is about 2.5 gallons (9.46 1.).
Preferably the kitchen caddy 12 as shown in
The curbside container 20 shown in
Single roll dispenser 22 (
An example of a typical size for dispenser 90 will be 12 inches in height by 11 inches wide by 3¾ inches deep, with each compartment 92, 94, 96 being about 3⅝ inches wide. Slots 97 and 98 may be about 5 inches in height and 1 inch wide while slot 99 as shown is 6 inches in height and 1 inch wide. Such dimensions of course will vary widely depending on the application and size of bags used.
Similarly, the waste bins 110 used by the facility are numbered 1, 2, or 3 as shown in
The food service dispenser may be provided with adapters 104 for wall mounting as well as rotatable hooks 106 that can be used to rack or shelf mount. The hooks can also allow for mounting on the side of a waste cart for use in food court settings. Preferably all dispensers 22, 50, 60 and 90 are also marked with the same distinctive mark and colouring as bags 14, such as the mark ECOSAFE as shown, so that the residents are again reminded that the special compostable bags 14 must be used to collect the organic waste.
Thus the present systems facilitate the reduction of contamination of the organic waste with non-compostable plastic bags, both by ensuring the residents/users are constantly provided with compostable replacement bags for their kitchen caddies after each delivery of a bag to the recycling room, and through consistent marking that reminds residents of the system's requirements. Savings in waste disposal can thereby be realized by any commercial food preparation areas such as restaurants, commercial kitchens, and hospitality settings. Most commercial food scrap generators collect their organic waste in commercially available waste bins. The operator lines the waste bin with a compostable bag, keeping the bin clean during use and more importantly, after emptying. The bag is simply removed from the bin and the bag along with its contents is disposed of in the facilities' recycling area. The employee then removes the correct sized bag from the wall mounted dispenser 90 and installs a new bag. The use of a compostable bag will ensure the bin remains clean through the operation and consequently, the bins will not require washing.
Further the present system addresses the transition gap problem in operating organic waste recycling in multi-unit residential buildings. Regarding spills and leaks, residents can more safely carry their organic waste from their dwelling unit to the central deposit area in their compostable bag without leaks or spills. Regarding one way trips by using the compostable bag, residents can transport their organic waste from their dwelling unit to the central deposit area in one trip depositing the bag directly into the organics cart. No return trip to their dwelling unit is required so this reduces time spent by one-half.
While a number of exemplary aspects and embodiments have been discussed above, those of skill in the art will recognize certain modifications, permutations, additions and sub-combinations thereof. It is therefore intended that the following appended claims and claims hereafter introduced are interpreted to include all such modifications, permutations, additions and sub-combinations as are within their true spirit and scope.
The present application claims the benefits, under 35 U.S.C.§ 119(e), of U.S. Provisional Application Ser. No. 62/004,542 filed May 29, 2014 which is incorporated herein by this reference.
Filing Document | Filing Date | Country | Kind |
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PCT/CA2015/050499 | 5/29/2015 | WO | 00 |
Publishing Document | Publishing Date | Country | Kind |
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WO2015/179986 | 12/3/2015 | WO | A |
Number | Name | Date | Kind |
---|---|---|---|
5042687 | McKinley | Aug 1991 | A |
6578730 | Trunsky | Jun 2003 | B2 |
20050206700 | Jones | Sep 2005 | A1 |
20060163257 | Golbert | Jul 2006 | A1 |
20100025415 | Bichler | Feb 2010 | A1 |
20100170913 | Shoshani | Jul 2010 | A1 |
20110055734 | Borst | Mar 2011 | A1 |
20120279981 | Thomas | Nov 2012 | A1 |
Entry |
---|
International Search Report dated Aug. 4, 2015 issued on PCT/CA2015/050499. |
International Preliminary Report on Patentability dated Sep. 26, 2016 issued on PCT/CA2015/050499. |
http://www.armaoh.00v.uk/recycling/food-waste—Armagh City (2011) http://www.armagh.gov.uk/wp-content/uploads/2013/12/Bryson-Armagh-food-Sept13-web.pdf. |
https://www.facebook.com/230380027069450/photos/a.279255742181878.61864.230380027069450/473713992736051/?type=1&theater—K9 Community Clean—(Sep. 14, 2013). |
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20170190508 A1 | Jul 2017 | US |
Number | Date | Country | |
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62004542 | May 2014 | US |