WO2018099223A1 - Biodegradable additive and plastic product added with same - Google Patents

Biodegradable additive and plastic product added with same Download PDF

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WO2018099223A1
WO2018099223A1 PCT/CN2017/108044 CN2017108044W WO2018099223A1 WO 2018099223 A1 WO2018099223 A1 WO 2018099223A1 CN 2017108044 W CN2017108044 W CN 2017108044W WO 2018099223 A1 WO2018099223 A1 WO 2018099223A1
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mass
coupling agent
zone
powder
biodegradable
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PCT/CN2017/108044
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French (fr)
Chinese (zh)
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陆海荣
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苏州天兼新材料科技有限公司
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    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J5/00Manufacture of articles or shaped materials containing macromolecular substances
    • C08J5/18Manufacture of films or sheets
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K3/00Use of inorganic substances as compounding ingredients
    • C08K3/02Elements
    • C08K3/08Metals
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K9/00Use of pretreated ingredients
    • C08K9/04Ingredients treated with organic substances
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K9/00Use of pretreated ingredients
    • C08K9/04Ingredients treated with organic substances
    • C08K9/06Ingredients treated with organic substances with silicon-containing compounds
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08LCOMPOSITIONS OF MACROMOLECULAR COMPOUNDS
    • C08L23/00Compositions of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Compositions of derivatives of such polymers
    • C08L23/02Compositions of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Compositions of derivatives of such polymers not modified by chemical after-treatment
    • C08L23/04Homopolymers or copolymers of ethene
    • C08L23/06Polyethene
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J2323/00Characterised by the use of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Derivatives of such polymers
    • C08J2323/02Characterised by the use of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Derivatives of such polymers not modified by chemical after treatment
    • C08J2323/04Homopolymers or copolymers of ethene
    • C08J2323/06Polyethene
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J2423/00Characterised by the use of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Derivatives of such polymers
    • C08J2423/02Characterised by the use of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Derivatives of such polymers not modified by chemical after treatment
    • C08J2423/04Homopolymers or copolymers of ethene
    • C08J2423/06Polyethene
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K3/00Use of inorganic substances as compounding ingredients
    • C08K3/02Elements
    • C08K3/08Metals
    • C08K2003/085Copper
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K3/00Use of inorganic substances as compounding ingredients
    • C08K3/02Elements
    • C08K3/08Metals
    • C08K2003/0856Iron
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K2201/00Specific properties of additives
    • C08K2201/002Physical properties
    • C08K2201/003Additives being defined by their diameter
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K2201/00Specific properties of additives
    • C08K2201/018Additives for biodegradable polymeric composition
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08LCOMPOSITIONS OF MACROMOLECULAR COMPOUNDS
    • C08L2201/00Properties
    • C08L2201/06Biodegradable
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08LCOMPOSITIONS OF MACROMOLECULAR COMPOUNDS
    • C08L2203/00Applications
    • C08L2203/16Applications used for films
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08LCOMPOSITIONS OF MACROMOLECULAR COMPOUNDS
    • C08L2205/00Polymer mixtures characterised by other features
    • C08L2205/02Polymer mixtures characterised by other features containing two or more polymers of the same C08L -group
    • C08L2205/025Polymer mixtures characterised by other features containing two or more polymers of the same C08L -group containing two or more polymers of the same hierarchy C08L, and differing only in parameters such as density, comonomer content, molecular weight, structure
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08LCOMPOSITIONS OF MACROMOLECULAR COMPOUNDS
    • C08L2207/00Properties characterising the ingredient of the composition
    • C08L2207/06Properties of polyethylene
    • C08L2207/066LDPE (radical process)

Definitions

  • the present invention relates to a biodegradable additive capable of imparting biodegradability to a plastic article.
  • the present invention also relates to a plastic article prepared by adding the biodegradable additive, and more particularly to a polyethylene plastic film prepared by adding the biodegradable additive.
  • Plastic is a cheap and good material.
  • plastic convenience bags and plastic films the problem of "white pollution” has become increasingly prominent. This is due to the inherent life of the plastic product (from the finished product to the complete natural decomposition) is much longer than its service life.
  • the inherent durability of plastics has long existed in nature and has accumulated more and more if it is not treated.
  • the methods to solve this problem mainly include deep burial and incineration, but deep burying of cultivated land, polluting groundwater, changing soil structure, affecting normal plant growth, and high cost; incineration is currently the most widely used white pollution control method.
  • the advantage is that the processing speed is fast and the cost is low, but the significant disadvantage is that it brings additional air pollution.
  • biodegradable plastics can be naturally degraded under the influence of natural conditions such as ultraviolet rays, rainwater, and the like, and no pollutants are generated after degradation, this problem can be fundamentally solved.
  • biodegradable plastics have been developed such as polylactic acid, polybutylene succinate, polycaprolactone, polyvinyl alcohol, carbon dioxide copolymer, aliphatic aromatic copolymer, etc., which have the following advantages: (1) degradation After the volume is reduced, it can save land occupation land and save land resources; (2) no need to incinerate, reduce harmful gas emissions; (3) can be made into compost to return to nature.
  • an object of the present invention is to provide a biodegradable additive, and a plastic article prepared by adding the biodegradable additive.
  • a biodegradable additive prepared by using copper powder, iron powder, a silane coupling agent, a titanate coupling agent and a low density polyethylene as raw materials, wherein each component is prepared.
  • the copper powder is 8 to 12% by mass
  • the iron powder is 8 to 12% by mass
  • the silane coupling agent is 0.5 to 1.5% by mass
  • the titanic acid coupling agent is 0.5 to 1.0% by mass.
  • the balance is low density polyethylene.
  • a biodegradation additive according to an embodiment of the present invention wherein the composition of the components is as follows: copper powder 10% by mass, iron powder 10% by mass, silane coupling agent 1% by mass, titanate coupling agent 0.6 % by mass, the balance is low density polyethylene.
  • a biodegradation additive according to an embodiment of the present invention wherein the copper powder has a particle diameter of 3 ⁇ m or less, and the iron powder has a particle diameter of 3 ⁇ m or less.
  • a biodegradation additive according to an embodiment of the present invention wherein the silane coupling agent is 3-aminopropyltriethoxysilane, and the titanate coupling agent is isopropyl tris(dioctyl coke) Phosphate acyloxy) titanate.
  • a method for preparing the above biodegradable additive comprising the steps of: Step 1: weighing each component in proportion, and then using a silane coupling agent and a titanate coupling agent Copper powder and iron powder are surface-treated; Step 2: mixing the surface treated copper powder and iron powder with low-density polyethylene in a mixer; Step 3: passing the material after being uniformly mixed through the second step through the twin-screw The granulator is made into pellets.
  • a method of preparing the above biodegradable additive according to an embodiment of the present invention wherein the mixing time in the second step is 10 minutes.
  • a method of producing the above biodegradable additive according to an embodiment of the present invention wherein, in the third step, the twin-screw granulator has an aspect ratio of 40.
  • a method of preparing the above biodegradable additive according to an embodiment of the present invention wherein, in the third step, the temperature of the two zones of the twin-screw granulator is set to be the highest, that is, 180 ° C, one zone ratio two zones The temperature is 5 ⁇ 15°C, the temperature in the third zone and the fourth zone is the same as that in the second zone. From the beginning of the five zones to the nose, the temperature gradually decreases according to the temperature gradient, and the temperature of the head is kept constant.
  • a plastic article comprising 2 to 10% by mass of the biodegradation additive described above.
  • a polyethylene plastic film product prepared by the above-mentioned biodegradation additive, calcium carbonate powder and LDPE, wherein the ratio of each component is: the organism
  • the degradation additive is 2 to 10% by mass
  • the calcium carbonate powder is 3% by mass
  • the balance is LDPE.
  • the biodegradation additive provided by the invention can impart biodegradability to a plastic product, and the plastic product prepared by adding the biodegradation additive can be oxidatively decomposed and decomposed by ultraviolet irradiation or the like under natural conditions without incineration or burial treatment. No pollutants are produced during the process.
  • 1 is a graph showing the relationship between the concentration of adenosine triphosphate (ATP) and time in a bacterial culture control experiment of the membrane A and the blank group of the present invention
  • Fig. 2 is a graph showing the relationship between the concentration of adenosine triphosphate (ATP) and the time in a bacterial culture control test of the film B and the blank group of the present invention.
  • ATP adenosine triphosphate
  • the biodegradation additive of the present invention is prepared from the following raw materials: 8 to 12% by mass of copper powder having a particle diameter of 3 ⁇ m or less, 8 to 12% by mass of iron powder having a particle diameter of 3 ⁇ m or less, and silane coupling agent 0.5 to ⁇ . 1.5% by mass, the titanic acid coupling agent is 0.5 to 1.0% by mass, and the balance is low density polyethylene.
  • the amount of the copper powder is 10% by mass
  • the amount of the iron powder is 10% by mass
  • the silane coupling agent is 3-aminopropyltriethoxysilane in an amount of 1 mass.
  • the titanate coupling agent is isopropyl tris(dioctylpyrophosphate acyloxy) titanate in an amount of 0.6% by mass
  • the low density polyethylene is a low density polyethylene having a lower melting point. 78.4% by mass, and prepared by the following steps:
  • Step 1 Mixing the predetermined mass percentage of copper powder and iron powder uniformly and surface treatment with silane coupling agent and titanic acid coupling agent (copper powder and iron powder can also be combined with silane coupling agent and titanic acid coupling agent, respectively) Performing a surface treatment);
  • Step 2 mixing the mixture obtained in the first step and a predetermined mass percentage of the low density polyethylene in a blender for 10 minutes;
  • Step 3 passing the uniformly mixed material obtained in the second step through the twin-screw granulation
  • the mechanism is granulated, ie, made into a biodegradable additive.
  • the particles are preferably particles having the same or similar particle size as the polyethylene plastic particles.
  • the length ratio of the triple-screw granulator is 40, the temperature in the second zone is set to the highest, and the control is 180 ° C, and the setting is maintained.
  • the temperature of the zone is about 10 °C lower than the temperature of the second zone.
  • the temperature of the third zone and the fourth zone is basically the same as that of the second zone. From the fifth zone until the nose gradually decreases according to the gradient, the temperature of the head is kept constant (130-150). °C).
  • the biodegradation additive is an environmentally-friendly modified polymer new material particle, which can be directly added to various plastics such as polyethylene in a proportion of 2 to 10% by mass, so that the conventional plastic product becomes a biodegradable plastic in a natural environment. product.
  • Biodegradable additive 10 Calcium carbonate powder 3 LDPE 87
  • the film forming process was the same as above except that the component content was as shown in Table 2.
  • the life cycle of general plastic film products can be divided into three parts, namely the storage period (usually six months to one and a half years), the use period (such as half a year) and the final disposal.
  • the film A and the film B are subjected to (1) first thermal oxygen treatment, (2) photothermal treatment, and (3) second thermal oxygen treatment, respectively.
  • the conditions for the thermal oxygen treatment are in accordance with American Standard ASTM D5510-94 (2001).
  • Photothermal treatment is a fluorescent ultraviolet light exposure treatment, reference to the American standard ASTM D5208-01.
  • the light source used was a UV lamp emitting 340 nm with a strength of 0.78 ⁇ 0.02 W/m 2 ⁇ mm, a blackboard temperature of 50 ⁇ 3 ° C, and a radiation exposure of 300 hours.
  • the sample exposed to the fluorescent ultraviolet light was placed in an oven at a temperature of 70 ⁇ 2 ° C for a period of 15 days. The oven passes the air every three days.
  • Table 3 The properties of Film A and Film B at each stage of the test are shown in Table 3 below.
  • the biodegradable plastic film of the present invention has a markedly decreased elongation under ultraviolet light and heat treatment conditions, indicating that it can be rapidly decomposed into pieces after being lost in the natural light-heat condition.
  • the photodegradation of the film product after oxidative degradation by FTIR (Fourier Transform Infrared Spectroscopy) absorption curve increased at 1714 cm -1 , indicating that oxidative degradation caused an increase in relative carboxylic acid groups, relative to the production of carboxylic acid groups.
  • FTIR Fastier Transform Infrared Spectroscopy
  • test results show that the biodegradable polyethylene film of the present invention can be rapidly broken and decomposed under thermal oxidative degradation and photooxidative degradation, and can obtain biodegradability, and is a biodegradable polyethylene film product.
  • the plastic samples were subjected to an acquired biodegradation test after (1) 30 days of the first thermal oxygen treatment, (2) 300 hours of photothermal treatment, and (3) 15 days of the second thermal oxygen treatment.
  • the acquired biodegradation test is divided into three parts. The first part measures the concentration of adenosine triphosphate in the culture solution containing the oxidatively degraded film sample; the second part measures the ratio of adenosine monophosphate to adenosine monophosphate after 180 days; the third part measures the viability of the bacteria after 180 days.
  • the above plastic sample was pulverized and passed through a metal sieve having a pore size of about 1 mm.
  • a powdered plastic sample is added to the culture solution for bacterial culture, and an equal amount of bacteria (such as Rhodococcus) is added to each test vessel, and the test is started (0 days), 4 days, 8 days, 12 days, The concentration of adenosine triphosphate in the solution at 30 days, 60 days, 90 days, 120 days, and 180 days.
  • Each set of test samples was set to a corresponding blank group containing no carbon source.
  • Figure 1 shows the relationship between adenosine triphosphate (ATP) concentration and time in the membrane A and blank groups.
  • Figure 2 shows the relationship between ATP concentration and time in the membrane B and blank groups.
  • Figure 1 and Figure 2 show that in the six-month test period, the concentration of adenosine triphosphate in the culture solution containing the film A and film B after oxidation is not containing the film A and film B after oxidation.
  • the concentration of adenosine triphosphate in the blank flask was more than three times.
  • Adenosine triphosphate is an energy transport molecule of all living organisms on the earth. It is an essential molecule for microorganisms. Its quantity is directly related to the number of living cells. All living organisms must maintain cell integrity, biological survival and fission and other biological functions through adenosine triphosphate. Both rely on the energy of adenosine triphosphate.
  • test results show that the oxidized film A and film B of the present invention can be sufficiently bio-utilized by microorganisms as nutrients.
  • AMP adenosine monophosphate
  • ATP adenosine triphosphate
  • the bacterial population in the culture medium containing the membrane A sample and the membrane B sample was visible after a few days of incubation in a (27 ⁇ 1) °C incubator, and the viability test showed positive. It was proved that film A and film B were not toxic to microorganisms after oxidation, and the bacteria did not affect the reproductive ability of the bacteria after passing through the medium containing the oxidized polyethylene sample for 6 months.
  • the environmentally-friendly modified polymer new material of the invention can be used to produce biodegradable polyethylene materials after being added to ordinary polyethylene polymer materials.
  • the biodegradable additive of the invention is not only suitable for the production of degradable polyethylene film materials, but also suitable for other kinds of plastic products such as environmentally-friendly packaging materials, disposable plastic products, agricultural disposable films (especially mulch products) and the like. plastic products. In the natural environment, these products undergo an oxidation reaction by light or heat, causing an increase in relative carboxylic acid groups, and obtaining biodegradable properties of the biodegradable plastic article. These environmentally friendly plastic products eventually degrade into carbon dioxide, water and humus by further thermal oxidative degradation, photothermal oxidative degradation or biodegradation.

Abstract

The present invention relates to a biodegradable additive prepared from copper powders, iron powders, a silane coupling agent, a titanate coupling agent, and low density polyethylene as raw materials, wherein the biodegradable additive comprises the following components: 8-12% by mass of the copper powder, 8-12% by mass of the iron powder, 0.5-1.5% by mass of the silane coupling agent, 0.5-1.0% by mass of the titanate coupling agent, and the balance of the low density polyethylene. The present invention also relates to a method for preparing the biodegradable additive and a plastic product prepared by adding the biodegradable additive, particularly a polyethylene film product, which has good biodegradability without producing white pollution.

Description

一种生物降解添加剂及添加了该添加剂的塑料制品Biodegradable additive and plastic product added with the additive 技术领域Technical field
本发明涉及一种生物降解添加剂,其能够赋予塑料制品生物降解性能,本发明还涉及添加该生物降解添加剂制备而成的塑料制品,特别涉及添加该生物降解添加剂制备而成的聚乙烯塑料薄膜。The present invention relates to a biodegradable additive capable of imparting biodegradability to a plastic article. The present invention also relates to a plastic article prepared by adding the biodegradable additive, and more particularly to a polyethylene plastic film prepared by adding the biodegradable additive.
背景技术Background technique
塑料是一种价廉物美的材料,然而,随着以塑料方便袋、塑料薄膜等塑料制品的广泛使用,“白色污染”问题也日益凸显。这是由于塑料制品的内在寿命(从制得成品到完全自然分解)远远长于其使用寿命。塑料内在的耐久性导致如不对其进行处理则长久存在于自然界并越积越多。目前解决这一问题的方法主要有深埋和焚烧等,但深埋占用耕地,污染地下水原,改变土壤结构,影响植物正常生长,且成本较高;焚烧是目前使用最为广泛的白色污染治理方法,优点是处理速度快,成本低,但显著缺点是带来了额外的大气污染。Plastic is a cheap and good material. However, with the widespread use of plastic products such as plastic convenience bags and plastic films, the problem of "white pollution" has become increasingly prominent. This is due to the inherent life of the plastic product (from the finished product to the complete natural decomposition) is much longer than its service life. The inherent durability of plastics has long existed in nature and has accumulated more and more if it is not treated. At present, the methods to solve this problem mainly include deep burial and incineration, but deep burying of cultivated land, polluting groundwater, changing soil structure, affecting normal plant growth, and high cost; incineration is currently the most widely used white pollution control method. The advantage is that the processing speed is fast and the cost is low, but the significant disadvantage is that it brings additional air pollution.
已经提出了可生物降解塑料的技术方案,由于可生物降解塑料能够在自然条件如紫外线、雨水等的影响下自然降解,且降解之后不产生污染物,因此能够从根本上解决这一问题。目前已开发的可生物降解塑料有聚乳酸、聚丁二酸丁二醇酯、聚己内酯、聚乙烯醇、二氧化碳共聚物、脂肪族芳香族共聚物等,具有如下优点:(1)降解后体积减小,能节省占用填埋场土地,节约土地资源;(2)无需焚烧,减少有害气体排放;(3)可制成堆肥回归自然。A technical solution for biodegradable plastics has been proposed. Since biodegradable plastics can be naturally degraded under the influence of natural conditions such as ultraviolet rays, rainwater, and the like, and no pollutants are generated after degradation, this problem can be fundamentally solved. Currently, biodegradable plastics have been developed such as polylactic acid, polybutylene succinate, polycaprolactone, polyvinyl alcohol, carbon dioxide copolymer, aliphatic aromatic copolymer, etc., which have the following advantages: (1) degradation After the volume is reduced, it can save land occupation land and save land resources; (2) no need to incinerate, reduce harmful gas emissions; (3) can be made into compost to return to nature.
但是,目前的可生物降解塑料存在如下问题:(1)生产成本偏高;(2)物理力学性能较传统的塑料制品差,例如大多数可生物降解塑料的拉伸强度、断裂伸长率、顶破和撕裂强度、光透明性、湿强度等都偏低,影响了 其应用范围。However, current biodegradable plastics have the following problems: (1) high production cost; (2) poor physical and mechanical properties compared to conventional plastic products, such as tensile strength, elongation at break, and elongation at break of most biodegradable plastics. The bursting and tearing strength, light transparency, wet strength, etc. are all low, affecting Its scope of application.
发明内容Summary of the invention
针对上述问题,本发明的目的是提供一种生物降解添加剂,以及添加该生物降解添加剂制备而成的塑料制品。In view of the above problems, an object of the present invention is to provide a biodegradable additive, and a plastic article prepared by adding the biodegradable additive.
为达到上述目的,本发明采用如下技术方案:In order to achieve the above object, the present invention adopts the following technical solutions:
根据本发明的一个具体实施方式,提供了一种生物降解添加剂,其以铜粉、铁粉、硅烷偶联剂、钛酸偶联剂和低密度聚乙烯为原料制备而成,其中各组分的配比如下:铜粉8~12质量%、铁粉8~12质量%、硅烷偶联剂0.5~1.5质量%、钛酸偶联剂0.5~1.0质量%,余量为低密度聚乙烯。According to a specific embodiment of the present invention, there is provided a biodegradable additive prepared by using copper powder, iron powder, a silane coupling agent, a titanate coupling agent and a low density polyethylene as raw materials, wherein each component is prepared. For example, the copper powder is 8 to 12% by mass, the iron powder is 8 to 12% by mass, the silane coupling agent is 0.5 to 1.5% by mass, and the titanic acid coupling agent is 0.5 to 1.0% by mass. The balance is low density polyethylene.
根据本发明的一个实施例的生物降解添加剂,其中,所述各组分的配比如下:铜粉10质量%,铁粉10质量%,硅烷偶联剂1质量%,钛酸偶联剂0.6质量%,余量为低密度聚乙烯。A biodegradation additive according to an embodiment of the present invention, wherein the composition of the components is as follows: copper powder 10% by mass, iron powder 10% by mass, silane coupling agent 1% by mass, titanate coupling agent 0.6 % by mass, the balance is low density polyethylene.
根据本发明的一个实施例的生物降解添加剂,其中,所述铜粉粒径为3微米以下,并且所述铁粉粒径为3微米以下。A biodegradation additive according to an embodiment of the present invention, wherein the copper powder has a particle diameter of 3 μm or less, and the iron powder has a particle diameter of 3 μm or less.
根据本发明的一个实施例的生物降解添加剂,其中,所述硅烷偶联剂为3-氨丙基三乙氧基硅烷,并且所述钛酸偶联剂为异丙基三(二辛基焦磷酸酰氧基)钛酸酯。A biodegradation additive according to an embodiment of the present invention, wherein the silane coupling agent is 3-aminopropyltriethoxysilane, and the titanate coupling agent is isopropyl tris(dioctyl coke) Phosphate acyloxy) titanate.
根据本发明的一个具体实施方式,提供了一种制备上述生物降解添加剂的方法,其包含以下步骤:步骤一:按比例称量各组分,然后采用硅烷偶联剂和钛酸偶联剂对铜粉和铁粉进行表面处理;步骤二:将表面处理之后的铜粉和铁粉与低密度聚乙烯放入搅拌机进行混合;步骤三:将通过所述步骤二混合均匀之后的物料通过双螺杆造粒机制成颗粒状。According to a specific embodiment of the present invention, there is provided a method for preparing the above biodegradable additive, comprising the steps of: Step 1: weighing each component in proportion, and then using a silane coupling agent and a titanate coupling agent Copper powder and iron powder are surface-treated; Step 2: mixing the surface treated copper powder and iron powder with low-density polyethylene in a mixer; Step 3: passing the material after being uniformly mixed through the second step through the twin-screw The granulator is made into pellets.
根据本发明的一个实施例的制备上述生物降解添加剂的方法,其中,所述步骤二中混合时间为10分钟。A method of preparing the above biodegradable additive according to an embodiment of the present invention, wherein the mixing time in the second step is 10 minutes.
根据本发明的一个实施例的制备上述生物降解添加剂的方法,其中,在所述步骤三中,所述双螺杆造粒机的长径比为40。 A method of producing the above biodegradable additive according to an embodiment of the present invention, wherein, in the third step, the twin-screw granulator has an aspect ratio of 40.
根据本发明的一个实施例的制备上述生物降解添加剂的方法,其中,在所述步骤三中,将所述双螺杆造粒机的二区温度设为最高,即180℃,一区比二区低5~15℃,三区、四区温度与二区相同,从五区开始至机头按照温度梯度逐渐降低,保持机头温度为恒定温度。A method of preparing the above biodegradable additive according to an embodiment of the present invention, wherein, in the third step, the temperature of the two zones of the twin-screw granulator is set to be the highest, that is, 180 ° C, one zone ratio two zones The temperature is 5~15°C, the temperature in the third zone and the fourth zone is the same as that in the second zone. From the beginning of the five zones to the nose, the temperature gradually decreases according to the temperature gradient, and the temperature of the head is kept constant.
根据本发明一个具体实施方式,提供了一种塑料制品,其含有以上所述的生物降解添加剂2~10质量%。According to a specific embodiment of the present invention, there is provided a plastic article comprising 2 to 10% by mass of the biodegradation additive described above.
根据本发明的一个具体实施方式,提供了一种聚乙烯塑料薄膜制品,其以以上所述的生物降解添加剂、碳酸钙粉末和LDPE制备而成,其中各组分的配比为:所述生物降解添加剂2~10质量%、碳酸钙粉末3质量%,余量为LDPE。According to a specific embodiment of the present invention, there is provided a polyethylene plastic film product prepared by the above-mentioned biodegradation additive, calcium carbonate powder and LDPE, wherein the ratio of each component is: the organism The degradation additive is 2 to 10% by mass, and the calcium carbonate powder is 3% by mass, and the balance is LDPE.
本发明提供的生物降解添加剂能够赋予塑料制品生物降解性能,通过添加该生物降解添加剂制备而成的塑料制品无需焚烧或掩埋处理,在自然条件下即可因紫外线照射等原因而氧化分解,且分解过程中不产生污染物。The biodegradation additive provided by the invention can impart biodegradability to a plastic product, and the plastic product prepared by adding the biodegradation additive can be oxidatively decomposed and decomposed by ultraviolet irradiation or the like under natural conditions without incineration or burial treatment. No pollutants are produced during the process.
附图说明DRAWINGS
图1为本发明的薄膜A和空白组进行细菌培养对照实验时三磷酸腺苷(ATP)浓度和时间的关系;1 is a graph showing the relationship between the concentration of adenosine triphosphate (ATP) and time in a bacterial culture control experiment of the membrane A and the blank group of the present invention;
图2为本发明的薄膜B和空白组进行细菌培养对照试验三磷酸腺苷(ATP)浓度和时间的关系。Fig. 2 is a graph showing the relationship between the concentration of adenosine triphosphate (ATP) and the time in a bacterial culture control test of the film B and the blank group of the present invention.
具体实施方式detailed description
为了使本发明的目的、技术方案及优点更加清楚明白,下面结合附图及实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅用以解释本发明,并不用于限定本发明。The present invention will be further described in detail below with reference to the accompanying drawings and embodiments. It is understood that the specific embodiments described herein are merely illustrative of the invention and are not intended to limit the invention.
生物降解添加剂的制备Preparation of biodegradable additives
本发明的生物降解添加剂,由以下原料制备而成:粒径3微米以下的铜粉8~12质量%、粒径3微米以下的铁粉8~12质量%、硅烷偶联剂0.5~ 1.5质量%、钛酸偶联剂0.5~1.0质量%,余量为低密度聚乙烯。The biodegradation additive of the present invention is prepared from the following raw materials: 8 to 12% by mass of copper powder having a particle diameter of 3 μm or less, 8 to 12% by mass of iron powder having a particle diameter of 3 μm or less, and silane coupling agent 0.5 to ~. 1.5% by mass, the titanic acid coupling agent is 0.5 to 1.0% by mass, and the balance is low density polyethylene.
根据本发明的一个进一步优选的实施例,铜粉的用量为10质量%,铁粉的用量为10质量%,硅烷偶联剂为3-氨丙基三乙氧基硅烷,其用量为1质量%,钛酸偶联剂为异丙基三(二辛基焦磷酸酰氧基)钛酸酯,其用量为0.6质量%,低密度聚乙烯为熔点较低的低密度聚乙烯,其用量为78.4质量%,并通过如下步骤制备而成:According to a further preferred embodiment of the present invention, the amount of the copper powder is 10% by mass, the amount of the iron powder is 10% by mass, and the silane coupling agent is 3-aminopropyltriethoxysilane in an amount of 1 mass. %, the titanate coupling agent is isopropyl tris(dioctylpyrophosphate acyloxy) titanate in an amount of 0.6% by mass, and the low density polyethylene is a low density polyethylene having a lower melting point. 78.4% by mass, and prepared by the following steps:
步骤一:将预定质量百分数的铜粉和铁粉混合均匀并用硅烷偶联剂和钛酸偶联剂进行表面处理(也可将铜粉和铁粉分别与硅烷偶联剂和钛酸偶联剂进行表面处理);步骤二:将步骤一中所得的混合物和预定质量百分数的低密度聚乙烯放入搅拌机混合10分钟;步骤三:将步骤二中所得的均匀混合后的物料通过双螺杆造粒机制成颗粒,即,制成生物降解添加剂。该颗粒优选为粒径与聚乙烯塑料粒子相同或相近的颗粒,在此步骤中三双螺杆造粒机的长径比为40,将二区温度设为最高,控制为180℃,保持设定的温度,使一区比二区温度低10℃左右,三区、四区温度与二区基本相同,从五区开始直至机头按梯度逐渐降低,保持机头温度为恒定温度(130~150℃)。Step 1: Mixing the predetermined mass percentage of copper powder and iron powder uniformly and surface treatment with silane coupling agent and titanic acid coupling agent (copper powder and iron powder can also be combined with silane coupling agent and titanic acid coupling agent, respectively) Performing a surface treatment); Step 2: mixing the mixture obtained in the first step and a predetermined mass percentage of the low density polyethylene in a blender for 10 minutes; Step 3: passing the uniformly mixed material obtained in the second step through the twin-screw granulation The mechanism is granulated, ie, made into a biodegradable additive. The particles are preferably particles having the same or similar particle size as the polyethylene plastic particles. In this step, the length ratio of the triple-screw granulator is 40, the temperature in the second zone is set to the highest, and the control is 180 ° C, and the setting is maintained. The temperature of the zone is about 10 °C lower than the temperature of the second zone. The temperature of the third zone and the fourth zone is basically the same as that of the second zone. From the fifth zone until the nose gradually decreases according to the gradient, the temperature of the head is kept constant (130-150). °C).
该生物降解添加剂是一种环保改性高分子新材料颗粒,其可直接按2~10质量%的比例添加到聚乙烯等各种塑料中,使常规的塑料制品成为自然环境下可生物降解塑料制品。The biodegradation additive is an environmentally-friendly modified polymer new material particle, which can be directly added to various plastics such as polyethylene in a proportion of 2 to 10% by mass, so that the conventional plastic product becomes a biodegradable plastic in a natural environment. product.
可生物降解塑料制品的制备Preparation of biodegradable plastic products
进一步,采用如下实施例阐述了采用本发明的生物降解添加剂制备可降解塑料制品的方法,但本发明并不限于此。Further, a method of producing a degradable plastic article using the biodegradable additive of the present invention is explained using the following examples, but the present invention is not limited thereto.
实施例1Example 1
生物降解聚乙烯薄膜ABiodegradable polyethylene film A
表1:生物降解聚乙烯薄膜A的组成Table 1: Composition of biodegradable polyethylene film A
组分Component 含量(质量%)Content (% by mass)
生物降解添加剂 Biodegradable additive 22
碳酸钙粉末 Calcium carbonate powder 33
LDPELDPE 9595
将如表1所示的各组分材料充分混合后,加入单螺杆挤出机(挤出机的长径比为20~30),吹成厚度为25微米生物降解薄膜。The components of the respective materials as shown in Table 1 were thoroughly mixed, and then added to a single-screw extruder (the length to diameter ratio of the extruder was 20 to 30), and a biodegradable film having a thickness of 25 μm was blown.
实施例2Example 2
生物降解聚乙烯薄膜BBiodegradable polyethylene film B
表2:生物降解聚乙烯薄膜A的组成Table 2: Composition of biodegradable polyethylene film A
组分Component 含量(质量%)Content (% by mass)
生物降解添加剂Biodegradable additive 1010
碳酸钙粉末 Calcium carbonate powder 33
LDPELDPE 8787
除组分含量如表2所示外,制膜工艺同上。The film forming process was the same as above except that the component content was as shown in Table 2.
生物降解性能测试Biodegradability test
一般塑料薄膜制品的使用周期可分为三大部分,即储存期(通常为半年到一年半),使用期(如半年)和最后的废弃。根据使用周期,分别对薄膜A和薄膜B进行(1)第一次热氧处理、(2)光热处理和(3)第二次热氧处理。热氧处理的条件根据美国标准ASTM D5510-94(2001)。The life cycle of general plastic film products can be divided into three parts, namely the storage period (usually six months to one and a half years), the use period (such as half a year) and the final disposal. According to the use period, the film A and the film B are subjected to (1) first thermal oxygen treatment, (2) photothermal treatment, and (3) second thermal oxygen treatment, respectively. The conditions for the thermal oxygen treatment are in accordance with American Standard ASTM D5510-94 (2001).
将试样放入烘箱内,烘箱的温度为70±2℃,放置时间为30天。烘箱每三天通一下空气。然后进行光热处理。光热处理为荧光紫外光暴露处理,参考美国标准ASTM D5208-01。所用光源为发射340纳米的紫外灯,强度为0.78±0.02W/m2·mm,黑板温度为50±3℃,辐射暴露为300小时。最后,将经过荧光紫外光暴露处理的样品再放入烘箱内,烘箱的温度为70±2℃,放置时间为15天。烘箱每三天通一下空气。试验各阶段薄膜A和薄膜B的性能如下表3所示。The sample was placed in an oven at a temperature of 70 ± 2 ° C for a period of 30 days. The oven passes the air every three days. Then photothermal treatment is carried out. Photothermal treatment is a fluorescent ultraviolet light exposure treatment, reference to the American standard ASTM D5208-01. The light source used was a UV lamp emitting 340 nm with a strength of 0.78 ± 0.02 W/m 2 · mm, a blackboard temperature of 50 ± 3 ° C, and a radiation exposure of 300 hours. Finally, the sample exposed to the fluorescent ultraviolet light was placed in an oven at a temperature of 70 ± 2 ° C for a period of 15 days. The oven passes the air every three days. The properties of Film A and Film B at each stage of the test are shown in Table 3 below.
表3:光、热处理后可生物降解聚乙烯薄膜A和B的性能测试Table 3: Performance test of biodegradable polyethylene films A and B after light and heat treatment
Figure PCTCN2017108044-appb-000001
Figure PCTCN2017108044-appb-000001
Figure PCTCN2017108044-appb-000002
Figure PCTCN2017108044-appb-000002
注*:薄膜已断裂成碎片,无法测定伸长率值。Note*: The film has broken into pieces and the elongation value cannot be measured.
由表3可见,本发明的可生物降解塑料薄膜在紫外线和热处理条件下伸长率显著下降,说明其能够在自然界的光热条件下在失去使用寿命之后能够迅速变为碎片而分解。光热处理使之氧化降解后的薄膜制品在FTIR(傅利叶转换红外光谱分析仪)吸收曲线1714cm-1上吸收光谱增加,这表明氧化降解引起相对羧酸基团的增加,相对羧酸基团的产生和增加使非生物降解的聚乙烯薄膜制品获得了生物降解性能。As can be seen from Table 3, the biodegradable plastic film of the present invention has a markedly decreased elongation under ultraviolet light and heat treatment conditions, indicating that it can be rapidly decomposed into pieces after being lost in the natural light-heat condition. The photodegradation of the film product after oxidative degradation by FTIR (Fourier Transform Infrared Spectroscopy) absorption curve increased at 1714 cm -1 , indicating that oxidative degradation caused an increase in relative carboxylic acid groups, relative to the production of carboxylic acid groups. And the addition of biodegradable properties to non-biodegradable polyethylene film products.
综上,测试结果显示,本发明的可生物降解聚乙烯薄膜在热氧化降解和光氧化降解作用下能够迅速破碎、分解,均可以获得生物降解性能,是可生物降解的聚乙烯薄膜制品。In summary, the test results show that the biodegradable polyethylene film of the present invention can be rapidly broken and decomposed under thermal oxidative degradation and photooxidative degradation, and can obtain biodegradability, and is a biodegradable polyethylene film product.
对上述塑料样品经过(1)30天第一次热氧处理,(2)300小时光热处理,和(3)15天第二次热氧处理后的样品进行获得性生物降解试验。获得性生物降解试验分三部分。第一部分测定含氧化降解后薄膜样品的培养液中三磷酸腺苷的浓度;第二部分测定180天后单磷酸腺苷和三磷酸腺苷的比值;第三部分测定180天后细菌的活力。The plastic samples were subjected to an acquired biodegradation test after (1) 30 days of the first thermal oxygen treatment, (2) 300 hours of photothermal treatment, and (3) 15 days of the second thermal oxygen treatment. The acquired biodegradation test is divided into three parts. The first part measures the concentration of adenosine triphosphate in the culture solution containing the oxidatively degraded film sample; the second part measures the ratio of adenosine monophosphate to adenosine monophosphate after 180 days; the third part measures the viability of the bacteria after 180 days.
将上述塑料样品弄碎,使其通过孔径大约为1mm的金属筛子。将粉状的塑料样品加入到用于细菌培养的培养液中,各试验器皿中加入等量的细菌(如红球菌),测定开始试验时(0天)、4天、8天、12天、30天、60天、90天、120天和180天溶液中三磷酸腺苷的浓度。每组试验样品设置对应的不含有碳源的空白组。The above plastic sample was pulverized and passed through a metal sieve having a pore size of about 1 mm. A powdered plastic sample is added to the culture solution for bacterial culture, and an equal amount of bacteria (such as Rhodococcus) is added to each test vessel, and the test is started (0 days), 4 days, 8 days, 12 days, The concentration of adenosine triphosphate in the solution at 30 days, 60 days, 90 days, 120 days, and 180 days. Each set of test samples was set to a corresponding blank group containing no carbon source.
如图1所示为薄膜A和空白组中三磷酸腺苷(ATP)浓度和时间的关系,如图2所示为薄膜B和空白组中三磷酸腺苷(ATP)浓度和时间的关系。图1和图2均显示在六个月试验周期内,含有氧化后薄膜A和薄膜B样品的培养液内,三磷酸腺苷浓度为不含有氧化后薄膜A和薄膜B样品 空白烧瓶的三磷酸腺苷的浓度的3倍以上。三磷酸腺苷是地球上所有生命体的能量传输分子,是微生物所必需的分子,它的数量直接和活细胞的数量相关,所有生命体要通过三磷酸腺苷维持细胞的整体性,生物生存和裂变等生物功能,都依赖三磷酸腺苷的能量。Figure 1 shows the relationship between adenosine triphosphate (ATP) concentration and time in the membrane A and blank groups. Figure 2 shows the relationship between ATP concentration and time in the membrane B and blank groups. Figure 1 and Figure 2 show that in the six-month test period, the concentration of adenosine triphosphate in the culture solution containing the film A and film B after oxidation is not containing the film A and film B after oxidation. The concentration of adenosine triphosphate in the blank flask was more than three times. Adenosine triphosphate is an energy transport molecule of all living organisms on the earth. It is an essential molecule for microorganisms. Its quantity is directly related to the number of living cells. All living organisms must maintain cell integrity, biological survival and fission and other biological functions through adenosine triphosphate. Both rely on the energy of adenosine triphosphate.
因此,试验结果表明氧化后的本发明的薄膜A和薄膜B能被微生物作为养分进行充分的生物利用。Therefore, the test results show that the oxidized film A and film B of the present invention can be sufficiently bio-utilized by microorganisms as nutrients.
在180天试验结束时,测试了含有氧化后薄膜样品的培养液内单磷酸腺苷(AMP)和三磷酸腺苷(ATP)之比。含薄膜A样品和薄膜B样品的培养液的AMP/ATP之比分别为2.4和2.2。AMP/ATP之比小于3表明氧化后的塑料能给微生物提供足够的能量,证明细菌处于能量旺盛的水平。At the end of the 180 day test, the ratio of adenosine monophosphate (AMP) to adenosine triphosphate (ATP) in the culture solution containing the oxidized film sample was tested. The AMP/ATP ratio of the culture solution containing the film A sample and the film B sample was 2.4 and 2.2, respectively. An AMP/ATP ratio of less than 3 indicates that the oxidized plastic provides sufficient energy to the microorganisms, demonstrating that the bacteria are at an energy level.
180天试验结束时,含薄膜A样品和薄膜B样品的培养液中的细菌群体在(27±1)℃培养箱内培养几天后都能看得见,活力测试显示阳性。证明氧化后薄膜A和薄膜B对微生物没有毒性,细菌在经过含有氧化后聚乙烯样品的培养基中6个月后,没有影响细菌的繁殖能力。At the end of the 180-day test, the bacterial population in the culture medium containing the membrane A sample and the membrane B sample was visible after a few days of incubation in a (27 ± 1) °C incubator, and the viability test showed positive. It was proved that film A and film B were not toxic to microorganisms after oxidation, and the bacteria did not affect the reproductive ability of the bacteria after passing through the medium containing the oxidized polyethylene sample for 6 months.
获得性生物降解试验证明,薄膜A和薄膜B为获得性生物降解材料。本发明的环保改性高分子新材料加入到普通聚乙烯高分子材料中后,能生产生物降解聚乙烯材料。Acquired biodegradation tests demonstrate that Film A and Film B are acquired biodegradable materials. The environmentally-friendly modified polymer new material of the invention can be used to produce biodegradable polyethylene materials after being added to ordinary polyethylene polymer materials.
本发明的生物降解添加剂不仅适用于可降解聚乙烯薄膜材料的生产,还适合用于其他种类塑料产品如环保型包装材料、一次性塑料制品、农用一次性薄膜(特别是地膜制品)等薄膜类塑料制品。这些制品在自然环境下,通过光或热的作用,发生氧化反应,引起相对羧酸基团的增加,使不能生物降解的塑料制品获得生物降解性能。通过进一步的热氧化降解、光热氧化降解或生物降解,这些环保类塑料制品最终降解为二氧化碳、水和腐殖质。The biodegradable additive of the invention is not only suitable for the production of degradable polyethylene film materials, but also suitable for other kinds of plastic products such as environmentally-friendly packaging materials, disposable plastic products, agricultural disposable films (especially mulch products) and the like. plastic products. In the natural environment, these products undergo an oxidation reaction by light or heat, causing an increase in relative carboxylic acid groups, and obtaining biodegradable properties of the biodegradable plastic article. These environmentally friendly plastic products eventually degrade into carbon dioxide, water and humus by further thermal oxidative degradation, photothermal oxidative degradation or biodegradation.
以上所述仅为本发明的较佳实施例,并非用来限定本发明的实施范围;如果不脱离本发明的精神和范围,对本发明进行修改或者等同替换,均应涵盖在本发明权利要求的保护范围当中。 The above is only the preferred embodiment of the present invention, and is not intended to limit the scope of the present invention. The invention is intended to be modified or equivalently substituted without departing from the spirit and scope of the invention. Within the scope of protection.

Claims (10)

  1. 一种生物降解添加剂,其特征在于,其以铜粉、铁粉、硅烷偶联剂、钛酸偶联剂和低密度聚乙烯为原料制备而成,其中各组分的配比如下:铜粉8~12质量%、铁粉8~12质量%、硅烷偶联剂0.5~1.5质量%、钛酸偶联剂0.5~1.0质量%,余量为低密度聚乙烯。The invention relates to a biodegradation additive, which is prepared by using copper powder, iron powder, silane coupling agent, titanic acid coupling agent and low density polyethylene as raw materials, wherein the components are as follows: copper powder 8 to 12% by mass, 8 to 12% by mass of iron powder, 0.5 to 1.5% by mass of a silane coupling agent, and 0.5 to 1.0% by mass of a titanic acid coupling agent, and the balance is low-density polyethylene.
  2. 根据权利要求1所述的生物降解添加剂,其特征在于,所述各组分的配比如下:铜粉10质量%,铁粉10质量%,硅烷偶联剂1质量%,钛酸偶联剂0.6质量%,余量为低密度聚乙烯。The biodegradation additive according to claim 1, wherein the composition is as follows: copper powder 10% by mass, iron powder 10% by mass, silane coupling agent 1% by mass, titanate coupling agent 0.6% by mass, the balance being low density polyethylene.
  3. 根据权利要求1或2所述的生物降解添加剂,其特征在于,所述铜粉粒径为3微米以下,并且所述铁粉粒径为3微米以下。The biodegradable additive according to claim 1 or 2, wherein the copper powder has a particle diameter of 3 μm or less, and the iron powder has a particle diameter of 3 μm or less.
  4. 根据权利要求3所述的生物降解添加剂,其特征在于,所述硅烷偶联剂为3-氨丙基三乙氧基硅烷,并且所述钛酸偶联剂为异丙基三(二辛基焦磷酸酰氧基)钛酸酯。The biodegradation additive according to claim 3, wherein the silane coupling agent is 3-aminopropyltriethoxysilane, and the titanate coupling agent is isopropyltris(dioctyl) Pyrophosphoryloxy) titanate.
  5. 一种制备权利要求1-4任一项所述的生物降解添加剂的方法,包含以下步骤:A method of preparing the biodegradable additive of any of claims 1-4, comprising the steps of:
    步骤一:按比例称量各组分,然后采用硅烷偶联剂和钛酸偶联剂对铜粉和铁粉进行表面处理;Step 1: Weigh the components in proportion, and then surface-treat the copper powder and the iron powder with a silane coupling agent and a titanate coupling agent;
    步骤二:将表面处理之后的铜粉和铁粉与低密度聚乙烯放入搅拌机进行混合;Step 2: mixing the surface treated copper powder and iron powder with low density polyethylene in a blender;
    步骤三:将通过所述步骤二混合均匀之后的物料通过双螺杆造粒机制成颗粒状。Step 3: The material after being uniformly mixed by the second step is granulated by a twin-screw granulator.
  6. 根据权利要求5所述的方法,其特征在于,所述步骤二中混合时间为10分钟。The method according to claim 5, wherein the mixing time in the second step is 10 minutes.
  7. 根据权利要求5所述的方法,其特征在于,在所述步骤三中,所述双螺杆造粒机的长径比为40。The method according to claim 5, wherein in said step three, said twin-screw granulator has an aspect ratio of 40.
  8. 根据权利要求5所述的方法,其特征在于,在所述步骤三中,将所 述双螺杆造粒机的二区温度设为最高,即180℃,一区比二区低5~15℃,三区、四区温度与二区相同,从五区开始至机头按照温度梯度逐渐降低,保持机头温度为恒定温度。The method according to claim 5, wherein in said step three, The temperature of the second zone of the twin-screw granulator is set to the highest, that is, 180 °C, one zone is 5-15 °C lower than the second zone, and the temperature of the third zone and the fourth zone is the same as that of the second zone. From the five zones to the temperature gradient of the nose. Gradually lower, keeping the head temperature constant.
  9. 一种塑料制品,其特征在于,其含有根据权利要求1~4任一项所述的生物降解添加剂2~10质量%。A plastic product comprising 2 to 10% by mass of the biodegradation additive according to any one of claims 1 to 4.
  10. 一种聚乙烯塑料薄膜制品,其特征在于,其以权利要求1~4任一项所述的生物降解添加剂、碳酸钙粉末和LDPE制备而成,其中各组分的配比为:所述生物降解添加剂2~10质量%、碳酸钙粉末3质量%,余量为LDPE。 A polyethylene plastic film product, which is prepared by the biodegradation additive according to any one of claims 1 to 4, calcium carbonate powder and LDPE, wherein the ratio of each component is: the organism The degradation additive is 2 to 10% by mass, and the calcium carbonate powder is 3% by mass, and the balance is LDPE.
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