A method for separating reusable materials of a composite component comprising multiple material layers is presented. The composite component comprises a material layer which absorbs energy of a radiation source and at least one plastics film. With the aid of the radiation source, the composite component is heated in less than a second in an exposure field, with chemical compounds of the plastics material being cleaved, as a result of the heating of the absorbing material layer, in a boundary layer of the at least one plastics film which faces the absorbing material layer, resulting in a creation of gas. Prior to heating, at least one predetermined breaking point is introduced into the plastics film in such a way that the plastics film breaks in a controlled fashion at the predetermined breaking point under the pressure of the created gas.

The present invention provides systems and methods for the recycling of animal bedding and the disposal or reuse of manure, feces, urine or expectorant resulting from recycling animal bedding. The present invention provides systems and methods for the disposal of materials related to the recycling or repurposing of stall residual waste and/or soiled animal bedding which is environmentally conscious to aquifers, and further limiting off gassing of enteric methane and other gasses. Use of such methods create a healthier recycled bedding than existing new bedding materials. The reusable and clean animal bedding provides for a healthy, hygienic, sanitary and enhanced stall environment. The present invention further provides methods for infusing additives, enhancements or amendments to recycled animal bedding which promote the health and safety of the animals using the recycled animal bedding (or the humans in contact with the animal bedding or animals) and/or the barn environment.

The present invention provides systems and methods for the recycling of animal bedding and the disposal or reuse of manure, feces, urine or expectorant resulting from recycling animal bedding. The present invention provides systems and methods for the disposal of materials related to the recycling or repurposing of stall residual waste and/or soiled animal bedding which is environmentally conscious to aquifers, and further limiting off gassing of enteric methane and other gasses. Use of such methods create a healthier recycled bedding than existing new bedding materials. The reusable and clean animal bedding provides for a healthy, hygienic, sanitary and enhanced stall environment. The present invention further provides methods for infusing additives, enhancements or amendments to recycled animal bedding which promote the health and safety of the animals using the recycled animal bedding (or the humans in contact with the animal bedding or animals) and/or the barn environment.

A waste treatment device and a waste treatment method using the device are provided, and relates to the technical field. The waste treatment device includes a first treatment chamber for preliminary treatment of waste, a second treatment chamber for further treatment of the waste, a feed port for feeding the waste, a crushing component for crushing the waste, a discharge port for discharging waste residues, and light wave degradation components for releasing light waves to degrade the waste. The first treatment chamber is in communication with the second treatment chamber. A feed port is formed at the first treatment chamber. The crushing component is arranged inside the first treatment chamber. The discharge port is formed at the second treatment chamber. The light wave degradation components are arranged inside the first treatment chamber and the second treatment chamber.

A waste treatment device and a waste treatment method using the device are provided, and relates to the technical field. The waste treatment device includes a first treatment chamber for preliminary treatment of waste, a second treatment chamber for further treatment of the waste, a feed port for feeding the waste, a crushing component for crushing the waste, a discharge port for discharging waste residues, and light wave degradation components for releasing light waves to degrade the waste. The first treatment chamber is in communication with the second treatment chamber. A feed port is formed at the first treatment chamber. The crushing component is arranged inside the first treatment chamber. The discharge port is formed at the second treatment chamber. The light wave degradation components are arranged inside the first treatment chamber and the second treatment chamber.

A magnetization pyrolysis device for organic waste and a using method thereof are provided. During the magnetization pyrolysis of organic waste, the device uses perovskite as a catalyst, and includes a crushing reaction chamber combining a crushing zone with a reaction zone; a crushing mechanism for crushing waste; and a heating mechanism for heating the waste, the crushing mechanism and the heating mechanism are arranged in the crushing reaction chamber. In accordance with the present disclosure, the crushing zone is combined with the reaction zone, which significantly reduces the treatment space and cost. In-situ degradation of household waste can be achieved by the device without leaving the village, and the daily cleaning of everyday rural waste can be effectively achieved.

A magnetization pyrolysis device for organic waste and a using method thereof are provided. During the magnetization pyrolysis of organic waste, the device uses perovskite as a catalyst, and includes a crushing reaction chamber combining a crushing zone with a reaction zone; a crushing mechanism for crushing waste; and a heating mechanism for heating the waste, the crushing mechanism and the heating mechanism are arranged in the crushing reaction chamber. In accordance with the present disclosure, the crushing zone is combined with the reaction zone, which significantly reduces the treatment space and cost. In-situ degradation of household waste can be achieved by the device without leaving the village, and the daily cleaning of everyday rural waste can be effectively achieved.

Systems and methods for drying asphalt shingle waste are provided. A method comprises obtaining an asphalt shingle waste, exposing the asphalt shingle waste to microwaves emitted by a microwave dryer, and processing the asphalt shingle waste into a processed asphalt shingle waste. The asphalt shingle waste has a first moisture content at an inlet of the microwave dryer. The asphalt shingle waste has a second moisture content at an outlet of the microwave dryer. The second moisture content of the asphalt shingle waste is less than the first moisture content of the asphalt shingle waste.

Systems and methods for drying asphalt shingle waste are provided. A method comprises obtaining an asphalt shingle waste, exposing the asphalt shingle waste to microwaves emitted by a microwave dryer, and processing the asphalt shingle waste into a processed asphalt shingle waste. The asphalt shingle waste has a first moisture content at an inlet of the microwave dryer. The asphalt shingle waste has a second moisture content at an outlet of the microwave dryer. The second moisture content of the asphalt shingle waste is less than the first moisture content of the asphalt shingle waste.

A process for recycling contaminated solid material is provided. The process comprises heating the material yielding a solid phase, an oil phase, and a gas phase. Prior to being heated, the material is subjected to a pre-treatment involving a dehalogenation agent (DHA). The gas phase obtained is further subjected to a purification treatment. The DHA agent used is regenerated using a regeneration agent (RGA) and further re-used in the process.