Method for determining the carbon source of chemical substances

Abstract

Provided is a method for determining the origin of a carbon raw material in a chemical substance, whereby it can be determined whether carbon that is resource-recycled is used as a carbon raw material from a chemical substance in various products.　This method for determining the origin of a carbon raw in a chemical substance includes: a step S1 for acquiring carbon-14 content percentage R1 in a standard chemical substance comprising carbon in which the carbon element is recycled; a step S2 for acquiring carbon-14 content percentage R2 in a chemical substance to be identified; a step S3 for calculating a ratio (R2 / R1) of the content percentage R2 to the content percentage R1; and a step S4 for determining, by means of the ratio (R2 / R1), whether a carbon raw material in a chemical substance to be identified contains carbon that is resource-recycled.

Description

[Technical field]

[0001] The present invention relates to a method for determining the origin of the carbon raw material of a chemical substance, and more particularly to a method for determining whether the carbon raw material of a chemical substance is recycled carbon. [Background technology]

[0002] In recent years, in view of the concern of the depletion of fossil fuel resources and the global environmental problem of the increase in carbon dioxide in the atmosphere, there is an increasing demand for a method of producing various organic substances from raw materials other than fossil fuel resources. As a method of producing various organic substances from raw materials other than fossil fuel resources, for example, a method of producing biomass-derived ethanol from biomass resources by sugar fermentation has attracted attention. However, the sugar fermentation method using edible biomass resources such as corn has problems such as causing a rise in food prices because a limited agricultural land area is used for production other than food, and there is a demand for the use of raw materials that do not compete with food. In addition, from the viewpoint of environmental problems, there is a demand for the use of recycled raw materials that do not use new resources such as fossil fuel resources and biomass resources.

[0003] In order to meet such demands, methods are being considered for producing chemical substances that were previously produced from fossil fuel resources by using waste as recycled raw materials. Specifically, a method has been proposed for producing ethanol by microbial fermentation from synthetic gas obtained by gasifying waste (see, for example, Patent Document 1). Waste-derived ethanol as described above does not use new resources as a carbon raw material, but uses carbon derived from recycled raw materials (waste) that have been circulated, and is expected to have the smallest impact on the global environment. [Prior art documents] [Patent documents]

[0004] [Patent Document 1] JP 2007-45857 A Summary of the Invention [Problem to be solved by the invention]

[0005] Meanwhile, as general consumers and companies and other consumers of chemical substances become more and more interested in environmental issues, they are increasingly purchasing products made of chemical substances containing recycled carbon. Therefore, in order to meet consumers' purchasing desire, suppliers may proactively display that each product uses recycled carbon as a carbon raw material. However, it is difficult to determine whether a product made of chemical substances uses recycled carbon as a carbon raw material, and a system is needed to inspect whether the display of the use of recycled carbon is appropriate.

[0006] The present invention has been made in consideration of the above-mentioned problems, and an object of the present invention is to provide a method for determining the origin of the carbon raw material of a chemical substance, which is capable of determining whether the chemical substance in each product uses recycled carbon as a carbon raw material. [Means for solving the problem]

[0007] As a result of intensive research aimed at solving the above problems, the present inventors have discovered that the carbon-14( 14 They have discovered that it is possible to determine whether the carbon raw material of a chemical substance is recycled carbon or not by using the ratio of the carbon-14 content of the chemical substance to the carbon-14 content of the other carbon-containing compounds (C), and have completed the present invention as described below. That is, the present invention provides the following [1] to

[10] .

[0008] [1] A method for determining the origin of the carbon raw material of a chemical substance, comprising the steps of: acquiring a carbon-14 content R1 of a standard chemical substance whose carbon element is made of recycled carbon; acquiring a carbon-14 content R2 of a chemical substance to be determined; calculating the ratio (R2 / R1) of the R2 content to the R1 content; and determining that the carbon raw material of the chemical substance to be determined contains recycled carbon based on the ratio (R2 / R1). [2] The method for determining the origin of carbon raw materials of a chemical substance according to [1], wherein the determining step determines that the carbon raw material of the chemical substance to be determined is recycled carbon if the ratio (R2 / R1) is 0.5 or more and 2.0 or less. [3] The method for determining the origin of a carbon raw material of a chemical substance according to [1] or [2], wherein the determining step determines that the carbon raw material of the chemical substance to be determined is recycled carbon if the ratio (R2 / R1) is 1.0. [4] The method for determining the origin of a carbon raw material of a chemical substance according to any one of [1] to [3], wherein the standard chemical substance is ethanol. [5] The method for determining the origin of the carbon raw material of a chemical substance described in any one of [1] to [4], wherein the chemical substance to be determined is one selected from the group consisting of ethylene and polyethylene resin. [6] A method for determining the origin of the carbon raw material of a chemical substance described in any one of claims 1 to 5, wherein the content R1 is an average value of the carbon-14 contents of multiple standard chemical substances. [7] The method for determining the origin of the carbon raw material of a chemical substance described in [6], wherein the average carbon-14 content of the multiple standard chemical substances is the average carbon-14 content of the standard chemical substances produced at multiple locations. [8] A method for determining the origin of the carbon raw material of a chemical substance described in [6] or [7], wherein the average carbon-14 content of the multiple standard chemical substances is the average carbon-14 content of the standard chemical substances produced multiple times. [9] The method for determining the origin of the carbon raw material of a chemical substance described in any one of [1] to [5], wherein the content R1 is the carbon-14 content for each production lot in which the standard chemical substance is produced from the recycled carbon.

[10] A method for determining the origin of a carbon raw material of a chemical substance according to any one of [1] to [9], comprising a step of calculating the utilization rate of the recycled carbon as [100-|(R2 / R1)-1|×100] (%). Effect of the Invention

[0009] According to the present invention, it is possible to provide a method for determining the origin of the carbon raw material of a chemical substance, which makes it possible to determine whether the chemical substance in each product uses recycled carbon as a carbon raw material. [Brief description of the drawings]

[0010] [Figure 1] 1 is a flowchart showing a method for determining the origin of a carbon raw material according to an embodiment of the present invention. DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS

[0011] The present invention will be described below through embodiments of the invention. However, the following embodiments do not limit the invention according to the claims, and not all of the combinations of features described in the embodiments are necessarily essential to the solution of the invention.

[0012] [Method of determining the origin of carbon raw materials] A method for determining the origin of a carbon raw material according to an embodiment of the present invention, as shown in FIG. 1, is a method for determining the origin of the carbon raw material of a chemical substance, and includes a step S1 of acquiring a carbon-14 content R1 of a standard chemical substance whose carbon element is made of recycled carbon, a step S2 of acquiring a carbon-14 content R2 of the chemical substance to be determined, a step S3 of calculating the ratio (R2 / R1) of the content R2 to the content R1, and a step S4 of determining that the carbon raw material of the chemical substance to be determined contains recycled carbon based on the ratio (R2 / R1).

[0013] <Process for obtaining content rate R1> In step S1, the carbon-14 content R1 of a standard chemical substance whose carbon element is made of recycled carbon is obtained.

[0014] In this specification, the term "standard chemical substance" refers to a chemical substance in which all carbon elements are recycled carbon and which is produced from waste-derived gas obtained by burning or pyrolyzing recycled raw materials (waste). Examples of standard chemical substances include ethanol and ethylene. Among them, ethanol is preferable because it can be used as a raw material for various chemical substances and can be easily produced from waste materials. Here, "ethanol" used as a standard chemical does not mean only pure ethanol (chemical formula: CH3CH2OH) as a compound, but a composition containing impurities (contaminant components) that are inevitably contained in ethanol produced through synthesis or purification. The same applies to other substances such as "ethylene" used as a standard chemical. The raw materials for recycling (waste) may be industrial waste such as industrial solid waste, or general waste such as municipal solid waste (MSW), including combustible materials such as plastic waste, food waste, discarded tires, biomass waste, food waste, building materials, wood, wood chips, fiber, paper, etc. Among these, municipal solid waste (MSW) is preferred.

[0015] The carbon-14 content R1 of a standard chemical substance made from recycled carbon is the amount of carbon-14 in the standard chemical substance relative to the total amount of carbon in the standard chemical substance, as shown in the following formula. Content R1 (%) = (amount of carbon-14 in the standard chemical / total amount of carbon in the standard chemical) x 100 Methods for obtaining the carbon-14 content R1 of a standard chemical substance include liquid scintillation counting, gas proportional counting, and accelerator mass spectrometry, of which liquid scintillation counting is preferred from the standpoints of ease of operation, ease of correction, and high accuracy. The carbon-14 content R1 of the standard chemical substance can be expressed as a Percentage of Modern Carbon (PMC) value, which is the carbon-14 concentration when the carbon concentration in 1950 is set to 100, for example.

[0016] The carbon-14 content R1 of a standard chemical substance depends on the recycled carbon used as its raw material, and coincides with the carbon-14 content in the recycled carbon. The carbon-14 content in recycled carbon depends on the recycled raw material (waste), and coincides with the carbon-14 content of the carbon element contained in the recycled raw material (waste). In the future, when we reach a completely resource-circulating society where chemical substances are manufactured using 100% recycled raw materials (waste), recycled raw materials (waste) consisting of carbon elements with a constant carbon-14 content will be circulated, and the carbon-14 content R1 of the standard chemical substance will converge to a constant value. In other words, when we reach a completely resource-circulating society, the carbon-14 content R1 of the standard chemical substance will become a constant value, and this value will be adopted.

[0017] Currently, we are not yet in a completely resource-recycling society, and the carbon-14 content R1 of a standard chemical substance has not yet reached a fixed value, so the content R1 varies depending on differences in the types of waste from region to region, differences in the types of waste from manufacturing plant to manufacturing plant, etc. Therefore, it is preferable to use a chemical substance actually manufactured from recycled materials (waste) at a manufacturing plant as the standard chemical substance and to use the carbon-14 content of that standard chemical substance. In addition, currently, we are in the process of moving towards a resource recycling society, and as described above, it is considered that the content rate R1 is in the process of converging to a certain value. Therefore, it is more preferable to use, as the standard chemical substance, a chemical substance that has recently been produced from recycled raw materials (waste materials) at a manufacturing plant.

[0018] It is also preferable to use, for example, the average value of the carbon-14 contents of a plurality of standard chemical substances as the carbon-14 content R1 of the standard chemical substance. When using the average value of the carbon-14 contents of multiple acquired standard chemical substances, a preferred method for obtaining the average value is, for example, to average the carbon-14 contents of standard chemical substances made of recycled carbon obtained at multiple locations. Generally, there are multiple manufacturing plants that manufacture chemical substances from recycled materials (waste), but the carbon-14 content of the chemical substances obtained from each manufacturing plant may differ due to regional differences. Therefore, by taking the average carbon-14 content of standard chemical substances made from recycled carbon obtained at multiple locations, it is possible to reduce bias in the content rate R1 due to regional differences. The multiple manufacturing plants may be multiple locations in the same region (e.g., within the same prefecture, within the same commercial area), within the same country (e.g., within Japan), within the same region (e.g., within the European Union), or multiple locations around the world. For example, obtaining the carbon-14 content of a standard chemical substance at multiple locations within the same country and calculating the average value is useful for determining whether a chemical substance manufactured in that country is derived from recycled carbon.

[0019] It is also preferable to use the average value of the carbon-14 contents of standard chemical substances made of recycled carbon obtained multiple times as the carbon-14 content R1 of the standard chemical substance. Here, the standard chemical substances obtained multiple times are obtained at the same place (i.e., the same production plant). By setting the content R1 to the average value of the carbon-14 contents of standard chemical substances made of recycled carbon obtained multiple times, it is possible to reduce bias in the content R1 that depends on the type of waste material obtained in each time that the recycled carbon is obtained at the same production plant, which differs in time series. Generally, when chemical substances are manufactured from recycled materials (waste) at each plant, lots are often assigned in chronological order. Therefore, it is advisable to set the average carbon-14 content of multiple lots of standard chemical substances as the content rate R1. For example, obtaining the carbon-14 content of multiple lots of standard chemical substances and calculating the average value is useful for determining whether the standard chemical substances manufactured in multiple lots are derived from recycled carbon or not.

[0020] It is also preferable to use the average carbon-14 content of standard chemical substances made of recycled carbon obtained multiple times at multiple locations as the carbon-14 content R1 of the standard chemical substance. By setting the content R1 to the average carbon-14 content of standard chemical substances made of recycled carbon obtained multiple times at multiple locations, it is possible to reduce bias in the content R1 due to regional differences and bias in the content R1 due to differences over time.

[0021] For example, the carbon-14 content R1 of the standard chemical substance may be the carbon-14 content of each production lot in which the standard chemical substance is produced from recycled carbon. By setting the content R1 as the carbon-14 content of each production lot of the standard chemical substance, it is possible to identify the carbon-14 content R1 of the standard chemical substance obtained in each production lot, and by comparing it with the carbon-14 content of chemical substances in each product and finding a match, it is possible to trace which production lot the standard chemical substance was obtained from.

[0022] As described above, the carbon-14 content R1 of the standard chemical substance can be determined from various viewpoints, and these may be adopted alone or in combination.

[0023] <Process for obtaining content rate R2> In step S2, the carbon-14 content R2 of the chemical substance to be discriminated is obtained.

[0024] The chemical substance to be identified is not particularly limited as long as it is an organic compound. The form of the chemical substance to be identified is not particularly limited, and may be the chemical substance itself, or a mixture of the chemical substance to be identified and other chemical substances. The other chemical substances may be inorganic substances, or organic compounds other than the chemical substance to be identified. The chemical substance to be identified may be a single type of chemical substance, or two or more types of chemical substances may be identified. The chemical substance to be identified may be a chemical substance that has been subjected to various processes. Specifically, the chemical substance to be identified may be a molded article made of the chemical substance to be identified, or may be a molded article of a composition containing the chemical substance to be identified and other chemical substances. Examples of the molded article include films, sheets, thin-walled molded articles, and hollow molded articles. Examples of the molding method for the molded article include injection molding, blow molding, extrusion molding, compression molding, stretch molding, vacuum molding, internal pressure molding, and tear molding. When the chemical substance is mixed with other chemical substances, it is advisable to separate the chemical substance to be identified from the other chemical substances.

[0025] Specific examples of chemical substances to be identified are not particularly limited as long as they can be composed of recycled carbon, and include, for example, ethanol, ethylene, polymers having structural units derived from ethylene such as polyethylene resin, butadiene, ethylene, propylene, isobutene, acetaldehyde, acetic acid, ethyl acetate, methyl (meth)acrylate, ethyl-t-butyl ether ethylene glycol, ester compositions, acrylic acid, aminohexanoic acid, diethyl carbonate, polyester resin, polyethylene resin (PE), polyethylene terephthalate resin (PET), polypropylene resin (PP), polyisobutylene resin, polymethyl methacrylate resin (PMMA), ethylene propylene diene rubber (EPDM), polybutylene terephthalate resin (PBT), polyethylene furanoate resin (PEF), polyurethane resin (PU), etc. From the viewpoint of usability and versatility, it is preferable that the chemical substance to be identified is one selected from the group consisting of ethylene and polyethylene resin.

[0026] The carbon-14 content R2 of the chemical substance to be discriminated is the amount of carbon-14 in the chemical substance to be discriminated relative to the total amount of carbon in the chemical substance to be discriminated, as shown in the following formula. Content R2 (%) = (amount of carbon-14 in the chemical substance being identified / total amount of carbon in the chemical substance being identified) x 100 The method of acquiring the carbon-14 content R2 of the chemical substance to be discriminated can be the same as the method of acquiring the carbon-14 content R1 of the standard chemical substance described above.

[0027] <Step to calculate the ratio (R2 / R1)> In step S3, the ratio (R2 / R1) of the content rate R2 to the content rate R1 is calculated. The ratio (R2 / R1) is calculated using the content rate R1 obtained in step S1 and the content rate R2 obtained in step S2.

[0028] <Discrimination process> In step S4, it is determined whether the carbon raw material of the chemical substance to be determined contains recycled carbon based on the ratio (R2 / R1). A specific example of the determination step is shown below.

[0029] In the present invention, the carbon raw material of the chemical substance to be identified can be identified as containing recycled carbon by using the ratio (R2 / R1). Specifically, it is determined whether the ratio (R2 / R1) is 0.5 or more and 2.0 or less, and if the ratio (R2 / R1) is 0.5 or more and 2.0 or less, it is identified that the carbon raw material of the chemical substance to be identified contains recycled carbon. From the viewpoint of improving the discrimination accuracy, the criterion for the ratio (R2 / R1) is preferably 0.75 or more and 1.3 or less, more preferably 0.9 or more and 1.1 or less, and even more preferably 0.95 or more and 1.05 or less.

[0030] Here, the physical properties such as molecular weight, melting point, and mechanical properties of chemical substances do not differ whether recycled carbon, biomass resource-derived carbon, or fossil fuel resource-derived carbon is used as the carbon raw material. However, the carbon-14 content of chemical substances using recycled carbon, biomass resource-derived carbon, and fossil fuel resource-derived carbon differs. Specifically, the carbon-14 content of chemical substances using recycled carbon is roughly the same as that of the standard chemical substances, as described above. Carbon derived from fossil fuel resources does not contain carbon-14, which has a half-life of 5730 years, so the content rate R2 (%) of chemical substances using carbon derived from fossil fuel resources is low. Carbon derived from biomass resources contains carbon-14, so the content rate R2 (%) of chemical substances using carbon derived from biomass resources is high. In other words, when the ratio (R2 / R1) is 0.5 or more and 2.0 or less, it can be determined that the main carbon raw material of the chemical substance to be identified is recycled carbon. In particular, when the ratio (R2 / R1) is 1, it can be determined that all of the carbon raw materials of the chemical substance to be identified are recycled carbon. Also, when the ratio (R2 / R1) is less than 1, it can be determined that the carbon raw material to be identified contains a large amount of carbon derived from fossil fuel resources other than recycled carbon. Furthermore, when the ratio (R2 / R1) exceeds 1, it can be determined that the carbon raw material to be discriminated contains carbon derived from biomass resources other than recycled carbon. From the viewpoint of reducing the burden on the global environment, it is preferable to use more carbon derived from biomass resources than from fossil fuel resources, and therefore the ratio (R2 / R1) is preferably 1 or more. Moreover, from the viewpoint of mainly using recycled carbon and reducing the burden on the global environment, it is preferable that the ratio (R2 / R1) has a high usage rate of recycled carbon as a carbon raw material, and is preferably 0.75 to 1.3, more preferably 0.9 to 1.1, and even more preferably 0.95 to 1.05.

[0031] Calculating the usage rate of recycled carbon In addition, in the present invention, the ratio (R2 / R1) of the content rate R2 to the content rate R1 obtained in step S3 can also be used to calculate the usage rate of resource-recycled carbon in the carbon element of the chemical substance. Specifically, the utilization rate of recycled carbon in the carbon element of a chemical substance can be calculated by [100-|(R2 / R1)-1|×100] (%).

[0032] By displaying the recycled carbon usage rate in the carbon element of a chemical substance calculated by the above formula, it is possible to show that the carbon element of the chemical substance contains recycled carbon. The recycled carbon usage rate in the carbon element of a chemical substance may be displayed on each product, such as a molded product made of a chemical substance, or on the packaging of each product. This makes it possible to inform consumers whether the carbon element of the chemical substance is derived from recycled carbon. Similarly, it is possible to clearly inform consumers of the recycled carbon usage rate in the carbon element of a chemical substance.

[0033] [Ethanol production method] Next, a detailed description will be given of ethanol as a standard chemical and a method for producing ethanol from recycled raw materials. The ethanol is preferably obtained by converting waste-derived gas with either a gas-utilizing microorganism or a metal catalyst. The waste-derived gas is preferably a synthesis gas containing carbon monoxide and hydrogen. A detailed description will be given below of a method for producing ethanol when the waste-derived gas is a synthesis gas.

[0034] The method for producing ethanol includes a raw material gas production process, a synthesis gas purification process, an ethanol conversion process, and a purification process.

[0035] (Raw material gas generation process) In the raw gas generation process, the waste may be gasified using, for example, a gasification furnace. The gasification furnace is a furnace that burns (incompletely combusts) a carbon source, and examples of such furnaces include shaft furnaces, kiln furnaces, fluidized bed furnaces, and gasification reforming furnaces. The temperature at which the waste is gasified into the raw gas is not particularly limited, but is usually 100 to 2,500°C, and preferably 200 to 2,100°C.

[0036] The raw material gas obtained by gasifying waste preferably contains carbon monoxide and hydrogen, but may further contain carbon dioxide, oxygen, and nitrogen. The raw material gas may further contain components such as soot, tar, nitrogen compounds, sulfur compounds, phosphorus compounds, and organic compounds. The raw material gas typically contains 0.1% to 80% by volume of carbon monoxide and 0.1% to 80% by volume of hydrogen. The raw material gas may also contain 0.1% to 70% by volume of carbon dioxide.

[0037] The raw material gas is produced by subjecting waste to a heat treatment (commonly known as gasification) in which the waste is combusted (incompletely combusted), i.e., by partially oxidizing the waste, and the gas contains carbon monoxide in an amount of, although not particularly limited, 0.1% by volume or more, preferably 10% by volume or more, and more preferably 20% by volume or more.

[0038] (Synthetic gas refining process) As described above, the raw gas may be converted into a synthetic gas by removing or reducing specific substances such as various pollutants, soot particles, impurities, and undesirable amounts of compounds. When obtaining ethanol from a synthetic gas by microbial fermentation, it is preferable to reduce or remove substances that are undesirable for stable cultivation of microorganisms and undesirable amounts of compounds from the raw gas so that the content of each component contained in the raw gas is within a range suitable for stable cultivation of microorganisms. Also, when obtaining ethanol from a synthetic gas using a metal catalyst, it is preferable to reduce or remove substances that deactivate the metal catalyst.

[0039] In the synthesis gas purification process, the raw material gas may be purified by processing using one or more of the following: a moisture separator consisting of a gas chiller or the like, a low-temperature separation type (cryogenic type) separator, a fine particle separator for separating fine particles such as soot, represented by various filters such as a cyclone or a bag filter, a water-soluble impurity separator such as a scrubber, a desulfurization device (sulfide separator), a membrane separation type separator, a deoxygenation device, a pressure swing adsorption type separator (PSA), a temperature swing adsorption type separator (TSA), a pressure temperature swing adsorption type separator (PTSA), a separator using activated carbon, and a separator using a deoxygenation catalyst, specifically a separator using a copper catalyst or a palladium catalyst, to obtain a synthesis gas.

[0040] In addition, when ethanol is obtained by microbial fermentation, it is preferable to reduce the carbon dioxide gas concentration in the raw material gas. For example, it is preferable to use a pressure swing adsorption type separation device filled with a regenerated adsorbent containing zeolite to adsorb the carbon dioxide gas in the synthesis gas onto the regenerated adsorbent, thereby reducing the carbon dioxide gas concentration in the synthesis gas.

[0041] The resulting synthesis gas contains at least carbon monoxide and hydrogen as essential components as described above, and may further contain carbon dioxide and nitrogen. The carbon monoxide concentration in the synthesis gas is usually 20% by volume or more and 80% by volume or less, preferably 25% by volume or more and 50% by volume or less, and more preferably 30% by volume or more and 45% by volume or less, based on the total concentration of carbon monoxide, carbon dioxide, hydrogen, and nitrogen in the synthesis gas. The hydrogen concentration in the synthesis gas is usually 10 vol. % or more and 80 vol. % or less, preferably 30 vol. % or more and 55 vol. % or less, and more preferably 30 vol. % or more and 50 vol. % or less, based on the total concentration of carbon monoxide, carbon dioxide, hydrogen, and nitrogen in the synthesis gas.

[0042] The carbon dioxide concentration in the synthesis gas is not particularly limited, but is usually 0.1 to 40% by volume, preferably 0.3 to 30% by volume, based on the total concentration of carbon monoxide, carbon dioxide, hydrogen, and nitrogen in the synthesis gas. When ethanol is produced from the synthesis gas by microbial fermentation, it is particularly preferable to lower the carbon dioxide concentration in the synthesis gas, and from this viewpoint, the carbon dioxide concentration is more preferably 0.5 to 25% by volume. The nitrogen concentration in the synthesis gas is the sum of carbon monoxide, carbon dioxide, hydrogen, and nitrogen in the synthesis gas. The total concentration is usually 40% by volume or less, and preferably 1% by volume or more and 20% by volume or less. and more preferably, from 5 volume % to 15 volume %.

[0043] The concentrations of carbon monoxide, carbon dioxide, hydrogen and nitrogen in the synthesis gas can be adjusted to within a predetermined range by appropriately changing combustion conditions such as the type of waste, the gasification temperature in the raw material gas production process, and the oxygen concentration of the supply gas during gasification. For example, if you want to change the carbon monoxide or hydrogen concentration, you can change to waste with a higher ratio of hydrocarbons (carbon and hydrogen), such as waste plastic, and if you want to reduce the nitrogen concentration, you can supply gas with a higher oxygen concentration in the raw gas production process. Furthermore, at least one of the raw material gas and the synthesis gas may be appropriately adjusted in the concentration of each component, namely, carbon monoxide, carbon dioxide, hydrogen, and nitrogen. The concentration adjustment may be performed by adding at least one of these components to the raw material gas or the synthesis gas. The amount added is, for example, less than 50% by volume, preferably less than 30% by volume, and more preferably less than 10% by volume, based on the total amount of the raw material gas or the synthesis gas. However, when producing a standard chemical substance, the carbon monoxide and carbon dioxide to be added must be waste-derived gas.

[0044] (Ethanol conversion process) The synthesis gas is converted to ethanol in the ethanol conversion step. As described above, the synthesis gas may be converted to ethanol in the ethanol conversion step by a gas-utilizing microorganism or a metal catalyst, but conversion by a gas-utilizing microorganism is preferred.

[0045] Ethanol conversion through microbial fermentation When gas is converted to ethanol using a gas-utilizing microorganism, the synthesis gas is supplied to a microbial fermenter, and the synthesis gas is fermented by the microorganisms in the microbial fermenter to produce ethanol. The microbial fermenter is preferably a continuous fermentation apparatus. The microbial fermenter may be of any shape, including agitation type, airlift type, bubble column type, loop type, open bond type, and photobio type. In the present invention, the microbial fermenter can preferably be a known loop reactor having a main tank section and a reflux section. The synthesis gas to be supplied to the microbial fermentation tank may be the synthesis gas obtained through the synthesis gas purification process described above, or may be supplied after adding another specified gas. Examples of the other specified gas include at least one selected from the group consisting of sulfur compounds such as sulfur dioxide, phosphorus compounds, and nitrogen compounds.

[0046] The microbial fermenter may be continuously supplied with synthesis gas and a microbial culture solution, but it is not necessary to supply the synthesis gas and the microbial culture solution simultaneously, and the synthesis gas may be supplied to a microbial fermenter to which a microbial culture solution has been previously supplied. It is known that certain anaerobic microorganisms produce ethanol and the like from substrate gases such as synthesis gas by fermentation, and this type of gas-utilizing microorganism is cultured in a liquid medium. For example, a liquid medium and gas-utilizing bacteria may be supplied and accommodated, and synthesis gas may be supplied into the microbial fermenter while stirring the liquid medium in this state. This allows the gas-utilizing bacteria to be cultured in the liquid medium, and ethanol to be produced from the synthesis gas by the fermentation action of the bacteria.

[0047] In the microbial fermenter, the temperature of the medium (culture temperature) may be any temperature, but is preferably about 30 to 45° C., more preferably about 33 to 42° C., and even more preferably about 36.5 to 37.5° C. The culture time is preferably 1 hour or more in continuous culture, more preferably 7 days or more, particularly preferably 30 days or more, and most preferably 60 days or more, and although there is no particular upper limit, from the viewpoint of regular maintenance of the equipment, it is preferably 720 days or less, and more preferably 365 days or less. The culture time means the time from adding the seed bacteria to the culture tank to discharging the entire amount of the culture liquid in the culture tank.

[0048] The microorganisms (species) contained in the microbial culture solution are not particularly limited as long as they are capable of producing ethanol by microbial fermentation of a synthesis gas using carbon monoxide as a main raw material. For example, the microorganism (species) is preferably one that produces ethanol from synthetic gas by the fermentation action of gas-utilizing bacteria, and in particular, a microorganism having a metabolic pathway for acetyl-COA. Among gas-utilizing bacteria, the genus Clostridium is more preferable, and examples thereof include Clostridium autoethanogenum, Clostridium ljungdahlii, Clostridium aceticum, Clostridium carboxidivorans, Moorella thermoacetica, and Acetobacterium woodii, and among these, Clostridium autoethanogenum is particularly preferable.

[0049] The medium used to culture the above-mentioned microorganisms (species) is not particularly limited as long as it has an appropriate composition according to the bacteria, but is a liquid containing water as the main component and nutrients (e.g., vitamins, phosphoric acid, etc.) dissolved or dispersed in the water. The composition of such a medium is prepared so that the gas-utilizing bacteria can grow well. For example, when the microorganism is a Clostridium genus, the medium can be prepared by referring to

[0097] to

[0099] of U.S. Patent Application Publication No. 2017 / 260552.

[0050] <<Separation process of ethanol conversion by microbial fermentation>> A culture solution containing ethanol (ethanol-containing culture solution) is obtained by microbial fermentation. The culture solution containing ethanol is then subjected to a separation step. In the separation step, for example, the ethanol-containing culture liquid may be heated to 23 to 500° C. under conditions of 0.01 to 1,000 kPa (absolute pressure) to separate it into a liquid or solid component containing the microorganism and a gas component containing ethanol. By carrying out such a separation step, foaming does not occur in the distillation apparatus during the distillation operation for separating and purifying ethanol, which will be described later, so that the distillation operation can be carried out continuously. In addition, the separation and purification of ethanol can be carried out efficiently during the separation and purification, which will be described later.

[0051] In the separation step, from the viewpoint of efficiently separating the ethanol into a liquid or solid component containing microorganisms, their carcasses, proteins derived from microorganisms, etc., and a gaseous component containing ethanol, the ethanol-containing culture solution is heated preferably under conditions of 10 to 200 kPa, more preferably under conditions of 50 to 150 kPa, and even more preferably under normal pressure, at a temperature of preferably 50 to 200°C, more preferably at a temperature of 80°C to 180°C, and even more preferably at a temperature of 100 to 150°C. The gaseous component containing ethanol obtained in the above separation step may be liquefied by condensation to obtain an ethanol-containing liquid. The device used in the liquefaction step is not particularly limited, but it is preferable to use a heat exchanger, particularly a condenser. Examples of the condenser include a water-cooled type, an air-cooled type, and an evaporative type, and among these, a water-cooled type is preferable. The condenser may be a single-stage condenser or a multi-stage condenser.

[0052] In the separation step, instead of separating into a liquid or solid component containing microorganisms and a gaseous component containing ethanol as described above, a solid component containing microorganisms and a liquid component containing ethanol (ethanol-containing liquid) may be separated using a solid-liquid separation device such as a solid-liquid separation filter device.

[0053] Ethanol conversion using metal catalysts Ethanol may also be produced from synthesis gas using metal catalysts, as described above, including hydrogenation active metals or conglomerates of hydrogenation active metals and co-active metals. The hydrogenation active metal may be any metal that is conventionally known as a metal capable of synthesizing ethanol from a mixed gas, and examples thereof include alkali metals such as lithium and sodium, elements belonging to Group 7 of the periodic table such as manganese and rhenium, elements belonging to Group 8 of the periodic table such as ruthenium, elements belonging to Group 9 of the periodic table such as cobalt and rhodium, and elements belonging to Group 10 of the periodic table such as nickel and palladium. These hydrogenation active metals may be used alone or in combination of two or more. As the hydrogenation active metal, a combination of rhodium or ruthenium with an alkali metal and another hydrogenation active metal, such as a combination of rhodium, manganese and lithium, or a combination of ruthenium, rhenium and sodium, is preferred from the viewpoint of further improving the CO conversion rate and the ethanol selectivity.

[0054] Examples of the promoter active metal include titanium, magnesium, vanadium, etc. By supporting a promoter active metal in addition to a hydrogenation active metal, it is possible to further increase the CO conversion rate, ethanol selectivity, and the like. The metal catalyst is preferably a rhodium catalyst. The rhodium catalyst may be used in combination with a metal catalyst other than the rhodium catalyst. Examples of the other metal catalyst include a catalyst in which copper alone or copper and a transition metal other than copper are supported on a carrier. When a metal catalyst is used, a product containing acetaldehyde and acetic acid in addition to ethanol is usually obtained, and it is preferable to remove such products through an ethanol purification step such as distillation.

[0055] (purification process) After the ethanol conversion step, a purification step may be carried out to further purify the ethanol-containing liquid. In addition, when the ethanol-containing liquid obtained by microbial fermentation has already had components such as microorganisms removed, the purification step may be carried out without going through the above-mentioned separation step. The purification step is a step of separating an ethanol-containing liquid into a distillate having an increased ethanol concentration and a bottoms liquid having a decreased ethanol concentration. Examples of the apparatus used in the purification step include a distillation apparatus, a treatment apparatus including a pervaporation membrane, a treatment apparatus including a zeolite membrane, a treatment apparatus for removing low-boiling substances having a boiling point lower than that of ethanol, a treatment apparatus for removing high-boiling substances having a boiling point higher than that of ethanol, and a treatment apparatus including an ion exchange membrane. These apparatuses may be used alone or in combination of two or more. As the unit operation, a distillation apparatus or membrane separation can be suitably used, and a distillation apparatus is more preferred. Furthermore, as the membrane separation, a zeolite membrane can be suitably used.

[0056] When a distillation apparatus is used, heat distillation is performed. In the heat distillation, the desired ethanol can be obtained as a distillate with high purity. The temperature inside the distillation apparatus during the distillation of ethanol is not particularly limited, but is preferably 110°C or less, and more preferably about 70 to 105°C. By setting the temperature inside the distillation apparatus within the above range, separation of ethanol from other components, i.e., distillation of ethanol can be performed more reliably.

[0057] In the heat distillation, the ethanol-containing liquid is introduced into a distillation apparatus equipped with a heater using steam at 100°C or higher, and the temperature of the bottom of the distillation column is increased to 90°C or higher within 30 minutes, and then the ethanol-containing liquid is introduced from the middle of the distillation column. In addition, in the heat distillation using a distillation apparatus, it is preferable to perform the distillation process with the temperature difference between the bottom, middle, and top of the column being within ±15°C. When the temperature difference is within ±15°C, high-purity ethanol is easily obtained. The distillation temperature difference is preferably ±13°C, more preferably ±11°C. With these distillation temperature differences, separation from other components, i.e., purification by distillation of ethanol can be more reliably performed.

[0058] The pressure in the distillation apparatus during the distillation of ethanol may be normal pressure, but is preferably less than atmospheric pressure, more preferably about 60 to 95 kPa (absolute pressure). By setting the pressure in the distillation apparatus within the above range, the separation efficiency of ethanol can be improved, and the ethanol yield can be improved.

[0059] [How ethylene is produced] Next, methods for producing ethylene as a standard chemical and ethylene as a chemical obtained from recycled feedstocks will be described in detail. The ethanol produced by the above-mentioned production method using recycled carbon as a carbon raw material is converted into ethylene in an ethylene production step, thereby obtaining an ethylene-containing product. Specifically, the ethanol is brought into contact with a catalyst to be converted into ethylene. The ethanol is converted into ethylene by a dehydration reaction.

[0060] The catalyst used for producing ethylene is not limited as long as it can convert ethanol into ethylene, but examples of the catalyst include zeolite, modified zeolite such as P-modified zeolite, silica-alumina, alumina, silicated, titanated, zirconated or fluorinated alumina, and acid catalysts such as silicoaluminophosphate (hereinafter, these may be collectively referred to as "zeolite or alumina catalysts"). Other examples include heteropolyacid-supported catalysts.

[0061] Advantageously, the zeolite contains at least one 10-membered ring in its structure and is a microporous material consisting of silicon, aluminum, oxygen and, optionally, boron, such as MFI (ZSM-5, silicalite-1, boralite C, TS-1), MEL (ZSM-11, silicalite-2, boralite D, TS-2, SSZ-46), FER (ferrierite, FU-9, ZSM-35), MTT (ZSM-23), MWW (MCM-22, PSH-3, ITQ-1, MCM-49), TON (ZSM-22, Theta-1, NU-10), EUO (ZSM-50, EU-1), MFS (ZSM-57), ZSM-48, etc.

[0062] The zeolite is preferably a zeolite having a Si / Al ratio of at least 10. The zeolite having a Si / Al ratio of at least 10 preferably has a Si / Al ratio of at least 100, and preferably contains at least one selected from MFI and MEL.

[0063] The zeolite is also preferably a dealuminated zeolite, from which about 10% by weight of aluminum is advantageously removed, the dealumination being advantageously carried out by steam treatment, optionally followed by leaching. The zeolite and the dealuminated zeolite are advantageously essentially in H type and may contain, as a secondary component (component amounting to about 50% or less), at least one metal compensation ion selected from the group consisting of Na, Mg, Ca, La, Ni, Ce, Zn and Co.

[0064] The zeolite is mixed with a binder, preferably an inorganic binder, and formed into a desired shape, such as pellets. The binder is selected to be durable at the temperatures and other conditions used in the dehydration process of the present invention. The binder is at least one inorganic material selected from clay, silica, metal silicates, metal oxides (e.g., ZrO2), or gels containing mixtures of silica and metal oxides.

[0065] The P-modified zeolite is a phosphorus modified zeolite. In the ethylene production process, a preferred embodiment is one in which the P-modified zeolite is used. The phosphorus modified zeolite can be produced, for example, based on a zeolite having microporosity with an initial Si / Al atomic ratio of 4 to 500, specifically, MFI, MOR, MEL, clinoptilolite, FER, MWW, TON, EUO, MFS, ZSM-48, etc. The initial Si / Al atomic ratio is preferably 100 or less, more preferably 4 to 30. The P-modified zeolite of the present production method can also be obtained based on an inexpensive zeolite with a low Si / Al ratio (30 or less).

[0066] In addition, the P-modified zeolite can also be further modified with at least one metal selected from Mg, Ca, La, Ni, Ce, Zn, Co, Ag, Fe and Cu. Advantageously, the phosphorus atom content in the P-modified zeolite is at least 0.05% by mass, preferably 0.3-7% by mass. It is also advantageous if, for the starting zeolite, at least 10% by weight of aluminium has been extracted and removed from the zeolite by leaching.

[0067] The catalyst using P-modified zeolite may be the P-modified zeolite itself, or may be a blended type P-modified zeolite that combines P-modified zeolite with other materials. By using the blended type, the hardness or catalytic activity of the catalyst can be improved. Materials that can be mixed with the P-modified zeolite include various inert or catalytically active materials, or various binder materials. These include compositions such as kaolin, other clays, various forms of rare earth metals, phosphates, alumina or alumina sol, titania, zirconia, quartz, silica or silica sol, and mixtures thereof. These components are effective in increasing the compressive strength of the catalyst and catalyst formulations. The catalyst can be formed into pellets, spheres, extruded into other shapes, or spray-dried particles. The amount of P-modified zeolite in the final catalyst product is 10-90% by weight of the total catalyst, preferably 20-70% by weight of the total catalyst. Suitable examples of P-modified zeolites are silicoaluminophosphates, more preferably silicoaluminophosphates of the AEL group, a representative example of which is SAPO-11. SAPO-11 is based on ALPO-11, with an Al / P ratio of essentially 1 atom / atom. Silicon is inserted into the ALPO framework by adding a silicon precursor during synthesis, resulting in acid sites on the surface of the micropores of the 10-membered ring zeolite. The silicon content is 0.1-10 atomic % (Al+P+Si is 100).

[0068] It is also preferred to use alumina as a catalyst in the ethylene production step, and it is also preferred to use alumina which has been silicated, zirconated, titanated or fluorinated. Alumina is generally characterized by having a wide range of acid strength distribution and Lewis-type and Bronsted-type acid sites. Activated alumina is preferably used as the alumina.

[0069] It is also preferable to improve the selectivity of the catalyst by depositing silicon, zirconium, titanium, fluorite, etc. on the surface of the alumina. That is, the selectivity of the catalyst may be improved by silicating, zirconating, or titanating. To prepare such a catalyst, a suitable commercially available alumina, preferably alumina having a surface area of ​​10 to 500 m, is used. 2 It is preferable to use eta- or gamma-alumina having an alkali content of 0.5% or less per 1000 g of fluorinated alumina. It is also preferable to add silicon, zirconium, titanium, etc. in a total amount of 0.05 to 10 mass%. These metals may be added during the production of the alumina, or may be added to the alumina after production, or these metals may be added in the form of a precursor. Fluorinated alumina itself is known and can be produced according to conventional techniques.

[0070] In the ethylene production step, a heteropolyacid supported catalyst is also preferred as the catalyst. The heteropolyacid supported catalyst comprises a heteropolyacid supported on a suitable catalyst carrier. The term "heteropolyacid" refers to a heteropolyacid compound in the form of a free acid or in the form of a heteropolyacid salt such as an alkali metal salt, an alkaline earth metal salt, an ammonium salt, a salt of a bulky cation, and / or a metal salt (in these cases, the salt may be either a complete salt or a partial salt). The anion of a heteropolyacid typically comprises a polyvalent metal atom with 12 to 18 oxygen atoms attached thereto, known as peripheral atoms, which surround one or more central atoms in a symmetrical manner. The peripheral atoms are suitably selected from molybdenum, tungsten, vanadium, niobium, tantalum, and combinations thereof. The central atom is preferably silicon or phosphorus. The central atom may also comprise any one selected from the atoms of Groups I to VIII of the Periodic Table of Elements, such as copper, beryllium, zinc, cobalt, nickel, boron, aluminum, gallium, iron, cerium, arsenic, antimony, bismuth, chromium, rhodium, silicon, germanium, tin, titanium, zirconium, vanadium, sulfur, tellurium, manganese nickel, platinum, thorium, hafnium, tellurium, and iodine. Suitable heteropolyacids include Keggin, Wells-Dawson, and Anderson-Evans-Perloff heteropolyacids.

[0071] The heteropolyacid component of the heteropolyacid supported catalyst is preferably a heteropolytungstic acid, which is a heteropolyacid in which the peripheral atoms are tungsten atoms. Preferred heteropolytungstic acids are any based on the Keggin or Wells-Dawson structure. An example of a suitable heteropolytungstic acid is 18-phosphotungstic acid (H6[P2W 18 O 62 ]·xH2O), 12-phosphotungstic acid (H3[PW 12 O 40 ]·xH2O), 12-tungstosilicic acid (H4[SiW 12 O 40 ]·xH2O), cesium hydrogen silicotungstate (Cs3H[SiW 12 O 40 ]·xH2O), monopotassium phosphotungstate (KH5[P2W 18 O 62 ]·xH2O), 12-monosodium silicotungstate (NaK3[SiW 12 O 40 ]·xH2O), and potassium phosphotungstic acid (K6[P2W 18 O62 ]·xH2O). Mixtures of two or more different heteropolytungstic acids and salts can also be used.

[0072] More preferably, the heteropolyacid component of the heteropolyacid supported catalyst is silicotungstic acid, phosphotungstic acid, and mixtures thereof, such as 12-silicotungstic acid (H4[SiW 12 O 40 ]·xH2O), 12-phosphotungstic acid (H3[PW 12 O 40 ]·xH2O), and mixtures thereof. More preferably, the heteropolyacid is silicotungstic acid, and the most preferred heteropolyacid is 12-silicotungstic acid.

[0073] The molecular weight of the heteropolyacid is preferably greater than 700 and less than 8,500, more preferably greater than 2,800 and less than 6,000. Such heteropolyacids also include dimerized complexes thereof.

[0074] The catalyst support used in the heteropolyacid supported catalyst may be any suitable catalyst support known in the art. Suitable sources of catalyst support include mordenite (e.g., montmorillonite), clay, bentonite, diatomaceous earth, titania, activated carbon, alumina, silica, silica-alumina, silica-titania cogel, silica-zirconia cogel, carbon-coated alumina, zeolite, zinc oxide, and flame pyrolysis oxide. Silica-based catalyst supports, such as silica gel supports and supports produced by flame hydrolysis of SiCl4, are preferred. The shape of the catalyst support is not particularly limited and may be, for example, in powder form, granular form, pelletized form, spherical form, or extruded form.

[0075] Although not particularly limited, ethanol is preferably converted to ethylene in a gas phase by contacting the catalyst. Ethanol may be further mixed with water, or may be mixed with optional components other than ethanol and water, and one or both of water and optional components may be contacted with the catalyst as a gas together with ethanol. For example, a reaction vessel may be filled with the catalyst, and ethanol or ethanol and at least one selected from water and other optional components may be supplied as a gas to the reaction vessel filled with the catalyst to carry out a gas-phase dehydration reaction, thereby discharging an ethylene-containing product in the gas phase from the reaction vessel. When ethanol remains in the gas discharged from the reaction vessel, the component containing ethanol may be separated from the ethylene-containing product, and the component containing ethanol may be supplied again to the reaction vessel.

[0076] In the case of a zeolite or alumina catalyst, the temperature of the reaction vessel is, for example, 280 to 600° C., preferably 300 to 550° C., and more preferably 330 to 530° C. The pressure (absolute pressure) of the reaction vessel is, for example, 50 kPa to 3 MPa, preferably 50 kPa to 1 MPa, and more preferably 0.12 MPa to 0.65 MPa.

[0077] In the case of a heteropolyacid supported catalyst, the temperature in the reaction vessel is, for example, 170° C. or higher, preferably within the range of 180 to 270° C., more preferably within the range of 190 to 260° C., and even more preferably within the range of 200 to 250° C. The pressure in the reaction vessel is preferably within the range of 0.1 to 4.5 MPa, more preferably within the range of 1.0 to 3.5 MPa, and even more preferably within the range of 1.0 to 2.8 MPa. In the case of a supported heteropolyacid catalyst, the supported heteropolyacid catalyst may be heated to a temperature of 220°C or higher before contacting with ethanol and kept at that temperature for a sufficient period of time to remove bound water from the heteropolyacid component of the supported heteropolyacid catalyst.

[0078] [Polymer manufacturing method] Next, a method for producing the above-mentioned polymer having constitutional units derived from ethylene as a chemical substance obtained from recycled raw materials will be described. The polymer containing the ethylene-derived structural unit is obtained by polymerizing the ethylene-containing monomer. The polymer may be a homopolyethylene obtained by polymerizing ethylene alone, or a copolymer obtained by polymerizing ethylene and a monomer component other than ethylene.

[0079] The polymer is preferably a polyethylene resin such as low density polyethylene (LDPE), high density polyethylene (HDPE), linear low density polyethylene (LLDPE), or ultra-high molecular weight polyethylene (UHMWPE). In addition, other polymers may be used as long as they contain the above-mentioned ethylene-derived structural units, and examples of such polymers include copolymers of ethylene and monomers other than ethylene, such as ethylene-vinyl acetate copolymer (EVA), ethylene-methyl acrylate copolymer, ethylene-ethyl (meth)acrylate copolymer, ethylene-(meth)acrylic acid copolymer, ethylene-propylene rubber (EPM), and ethylene-propylene diene rubber (EPDM).

[0080] Low density polyethylene has a molecular structure that includes short chain branches and long chain branches, and has a density of 0.910 g / cm 3 More than 0.942g / cm 3 typically has a density of less than 0.930 g / cm 3 The density is 0.930g / cm 3 More than 0.942g / cm 3 Polyethylene with a molecular structure of less than 0.942 g / cm is sometimes called medium density polyethylene. High density polyethylene has a molecular structure with less branching and a density of 0.942 g / cm 3 The above polyethylene. Linear low density polyethylene is generally a copolymer of ethylene and a small amount of α-olefin other than ethylene. Examples of the α-olefin other than ethylene include α-olefins having 3 to 10 carbon atoms, specifically propylene, butene-1, pentene-1, 4-methyl-pentene-1, hexene-1, octene-1, decene-1, etc. The density of linear low density polyethylene is 0.942 g / cm 3 typically has a density of 0.930 g / cm 3 For example, 0.880 g / cm 3 More than 0.910g / cm 3 That's all.

[0081] Ultra-high molecular weight polyethylene (UHMWPE) is a polyethylene having a larger molecular weight than general polyethylene, for example, a polyethylene resin having a weight-average molecular weight of 400,000 or more, preferably a weight-average molecular weight of 1 million or more. With an increased weight-average molecular weight, the ultra-high molecular weight polyethylene (UHMWPE) has good mechanical strength in various respects. From the viewpoint of ease of polymerization, the weight-average molecular weight of the ultra-high molecular weight polyethylene (UHMWPE) is preferably 7 million or less, more preferably 4 million or less. The weight-average molecular weight is the weight-average molecular weight measured by gel permeation chromatography (GPC) in terms of standard polystyrene. The ultra-high molecular weight polyethylene (UHMWPE) may be an ethylene homopolymer, or may be a copolymer of ethylene and an α-olefin other than ethylene. The α-olefin other than ethylene is as described above for linear low density polyethylene (LLDPE).

[0082] Ethylene, for example, can be polymerized in the presence of a radical initiator to form a polyethylene resin. Radical initiators include, but are not limited to, oxygen-based initiators such as organic peroxides, peroxyesters, dialkyl peroxides, or combinations thereof. Specific examples of radical initiators include, but are not limited to, t-butyl peroxypivalate, di-t-butyl peroxide (DTBP), t-butyl peroxyacetate (TBPO), t-butyl peroxy-2-ethylhexanoate, t-butyl peroxyneodecanoate (PND), t-butyl peroxyoctoate, and combinations of any two or more thereof.

[0083] Ethylene can also be polymerized in the presence of a catalyst, such as a redox catalyst, to produce polyethylene resin. Redox catalysts include Ziegler-Natta catalysts, metallocene catalysts, Phillips catalysts, and standard catalysts.

[0084] As the Ziegler-Natta catalyst, for example, a triethylaluminum-titanium tetrachloride solid composite is used. The Ziegler-Natta catalyst may be, for example, a combination of a titanium trichloride composition obtained by reducing titanium tetrachloride with an organoaluminum compound and further treating it with various electron donors and electron acceptors, an organoaluminum compound, and an aromatic carboxylic acid ester, or a supported catalyst may be prepared by contacting magnesium halide with titanium tetrachloride and various electron donors. Examples of metallocene catalysts include compounds such as bis(cyclopentadienyl) metal complexes having a structure in which a transition metal is sandwiched between π-electron unsaturated compounds. More specifically, compounds in which one or more cyclopentadienyl rings or analogs thereof exist as ligands on a tetravalent transition metal such as titanium, zirconium, nickel, palladium, hafnium, or platinum can be mentioned. The Ziegler-Natta catalyst and the metallocene catalyst may each be used in combination with a specific cocatalyst (promoter). Specific cocatalysts include methylaluminoxane (MAO) and boron compounds.

[0085] An example of a Phillips catalyst is a catalyst system containing a chromium compound such as chromium oxide. Specific examples include catalysts in which a chromium compound such as chromium trioxide or a chromate ester is supported on a solid oxide such as silica, alumina, silica-alumina, or silica-titania. Standard catalysts are known catalysts using molybdenum oxide, such as gamma-alumina-molybdenum oxide.

[0086] When a radical initiator is used as a method for polymerizing ethylene, a high-pressure method can be mentioned. In the high-pressure method, ethylene is polymerized, for example, using a multi-stage gas compressor under an environment of 1,000 to 4,000 atmospheres and 100 to 350°C. The residual monomer is then separated and cooled to obtain the product. Low-density polyethylene (LDPE) can be produced from ethylene produced by the high-pressure method.

[0087] When using catalysts such as Ziegler-Natta catalysts, metallocene catalysts, Phillips catalysts, and standard catalysts, ethylene is preferably polymerized by low pressure or medium pressure methods. When using these catalysts, it is preferable to use either liquid phase polymerization, gas phase polymerization, or suspension polymerization. HDPE can be produced by polymerizing ethylene using these catalysts by low pressure or medium pressure methods. Linear low density polyethylene (LLDPE) can also be produced by copolymerizing ethylene and a small amount of α-olefins other than ethylene using these catalysts. Furthermore, ultra-high molecular weight polyethylene (UHMWPE) can be obtained by long-term polymerization using low pressure suspension polymerization.

Claims

1. 1. A method for determining whether a carbon raw material of a chemical substance contains carbon derived from resource-circulated waste, comprising the steps of: Carbon-14 content R of a standard chemical substance whose carbon element is made of recycled carbon １ and obtaining Carbon-14 content R of the chemical substance to be discriminated ２ and obtaining The content rate R １ The content R ２ The ratio (R ２ / R １ ) and The ratio (R ２ / R １ ) determining that the carbon raw material of the chemical substance to be determined contains recycled carbon; the determining step determines that the carbon raw material of the chemical substance to be determined is recycled carbon when the ratio (R2 / R1) is 0.5 or more and 2.0 or less; the chemical substance to be identified is one selected from the group consisting of ethanol, ethylene, and a polymer having a structural unit derived from ethylene, The method for determining whether a carbon raw material of a chemical substance contains carbon derived from resource-recycled waste, wherein the standard chemical substance is ethanol.

2. The determining step is performed by determining whether the ratio (R ２ / R １ 2. The method of claim 1 , wherein the carbon raw material of the chemical substance being determined to contain carbon derived from resource-circulated waste is determined to be resource-circulated carbon if the carbon raw material of the chemical substance being determined to contain carbon derived from resource-circulated waste when the carbon raw material of the chemical substance being determined to contain carbon derived from resource-circulated waste is determined to be resource-circulated carbon if the carbon raw material of the chemical substance being determined to contain carbon derived from resource-circulated waste when the carbon raw material of the chemical substance being determined to contain carbon derived from resource-circulated waste is determined to be resource-circulated carbon if the carbon raw material of the chemical substance being determined to contain carbon derived from resource-circulated waste when the carbon raw material of the chemical substance being determined to contain carbon derived from resource-circulated waste is determined to be resource-circulated carbon when ...

3. The content rate R １ is an average value of the carbon-14 content of a plurality of standard chemical substances.

4. 4. The method of claim 3, wherein the average value of the carbon-14 content of the plurality of standard chemical substances is an average value of the carbon-14 content of the standard chemical substances produced at a plurality of locations.

5. 5. The method for determining whether a carbon raw material of a chemical substance contains carbon derived from resource-circulated waste, as described in claim 3 or 4, wherein the average value of the carbon-14 content of the plurality of standard chemical substances is an average value of the carbon-14 content of the standard chemical substances produced in a plurality of times.

6. The content rate R １ is the carbon-14 content of each production lot in which the standard chemical substance is produced from the recycled carbon.

7. The utilization rate of the recycled carbon is expressed as [100-|(R ２ / R １ 7. A method for determining whether a carbon raw material of a chemical substance according to claim 1 contains carbon derived from resource-circulated waste, comprising a step of calculating [(a)−1|×100)] (%).

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