JP2008195872A - Production method of heavy metal-eliminated oil or fat - Google Patents
Production method of heavy metal-eliminated oil or fat Download PDFInfo
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- JP2008195872A JP2008195872A JP2007034054A JP2007034054A JP2008195872A JP 2008195872 A JP2008195872 A JP 2008195872A JP 2007034054 A JP2007034054 A JP 2007034054A JP 2007034054 A JP2007034054 A JP 2007034054A JP 2008195872 A JP2008195872 A JP 2008195872A
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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Abstract
Description
本発明は、重金属が溶解した油または脂肪中から、重金属が除去された油または脂肪の製造方法に関する。 The present invention relates to a method for producing oil or fat from which heavy metal is removed from oil or fat in which heavy metal is dissolved.
潤滑油は、内燃機関、車輛、工作機械、産業機械等の駆動装置に広く使用されており、とりわけ最近のモータリゼイションによる自動車の普及、人手不足解消のための作業の機械化等のためエンジン油、シリンダー油、作動油、極圧潤滑油等の消費量は急増している。これらの潤滑油は、相当時間使用後にその性状が劣化した時点で、現状では廃油(以下、廃潤滑油という)として処分されている。このような廃潤滑油のリサイクル方法として、燃料化することが検討されている。 Lubricating oils are widely used in driving devices for internal combustion engines, vehicles, machine tools, industrial machines, etc., especially engine oils for the spread of automobiles due to recent motorization and mechanization of work to eliminate labor shortages. Consumption of cylinder oil, hydraulic oil, extreme pressure lubricant, etc. is increasing rapidly. These lubricating oils are currently disposed of as waste oil (hereinafter referred to as waste lubricating oil) when their properties deteriorate after a considerable period of use. As a method for recycling such waste lubricating oil, it is considered to use it as a fuel.
潤滑油には、各種の添加剤が配合されている。これらの添加剤の中には重金属を含むものがある。重金属を含む廃潤滑油をボイラー燃料などとして再利用する場合、重金属が灰分に含まれ、環境汚染の原因となる。このため、廃潤滑油中から重金属を除去することが試みられている(例えば、特許文献1参照)。この文献に記載されている方法では、廃潤滑油にエチレンジアミン四酢酸などのキレート剤の水溶液と接触させて、重金属を錯塩化して水溶液側に移行させて除去する。 Various additives are blended in the lubricating oil. Some of these additives contain heavy metals. When waste lubricating oil containing heavy metals is reused as boiler fuel, heavy metals are contained in ash and cause environmental pollution. For this reason, removal of heavy metals from waste lubricating oil has been attempted (for example, see Patent Document 1). In the method described in this document, waste lubricating oil is brought into contact with an aqueous solution of a chelating agent such as ethylenediaminetetraacetic acid, and heavy metals are complexed and transferred to the aqueous solution side for removal.
また、ホタテ貝の中腸線(ウロ)やイカの内臓(ゴロ)などの水産物の内臓は、機能性脂質として利用可能な油分などの有用物質を多量に有することが知られている。一方、これらの水産物の内臓には、カドミウムなどの重金属を高濃度に含むことも知られている。このため、水産廃棄物などの有害な重金属を含む食品または食品加工副産物に含まれる重金属を除去することが試みられている(例えば、特許文献2参照)。この文献に記載されている方法では、食品または食品加工副産物から、酸水溶液に移行させた重金属をキレート樹脂で除去する。
これらの文献に記載の方法は、いずれも重金属を水相に移行させてから除去する。このため、複雑な手順が必要となる。 In any of the methods described in these documents, heavy metals are transferred to an aqueous phase and then removed. For this reason, a complicated procedure is required.
一方、油の中に含まれる重金属を回収するものとして、油溶性キレート剤が知られている。しかし、油中で重金属がキレート剤に捕捉されたとしても、油中から除去するためには複雑な液−液分離をする必要がある。 On the other hand, oil-soluble chelating agents are known for recovering heavy metals contained in oil. However, even if heavy metals are trapped by the chelating agent in the oil, a complicated liquid-liquid separation is required to remove them from the oil.
すなわち、本発明は、上記問題に鑑みなされたものであり、その目的は、重金属が溶解した油または脂肪から、重金属を容易に除去して、重金属が除去された油または脂肪の製造方法を提供することにある。 That is, the present invention has been made in view of the above problems, and an object thereof is to provide a method for producing oil or fat from which heavy metals are removed by easily removing heavy metals from oils or fats in which heavy metals are dissolved. There is to do.
本発明者は、上記課題を解決すべく、鋭意検討した結果、重金属が溶解した油または脂肪を、通常水中で用いられるキレート樹脂に直接接触させることで、重金属が除去されることを見出し、本発明を完成した。すなわち、本発明は以下のとおりである。 As a result of intensive studies to solve the above-mentioned problems, the present inventors have found that heavy metals are removed by directly contacting oils or fats in which heavy metals are dissolved with a chelate resin usually used in water. Completed the invention. That is, the present invention is as follows.
本発明は、重金属が溶解した油または脂肪を、キレート樹脂に接触させて、重金属が除去された油または脂肪の製造方法である。 The present invention is a method for producing oil or fat from which heavy metal is removed by bringing oil or fat in which heavy metal is dissolved into contact with a chelating resin.
前記油または脂肪は、液状であればよい。 The oil or fat may be liquid.
前記回収する重金属が銅、亜鉛、鉛、およびカドミウムから選択される1種であればよい。 The recovered heavy metal may be one selected from copper, zinc, lead, and cadmium.
本発明は、重金属を含む処理物を、亜臨界状態または超臨界状態の水で処理をする工程と、前記処理により得られた重金属が溶解した油または脂肪を、キレート樹脂に接触させる工程とを含む、重金属が除去された油または脂肪の製造方法であってもよい。 The present invention includes a step of treating a treated product containing heavy metal with water in a subcritical state or a supercritical state, and a step of bringing oil or fat in which the heavy metal obtained by the treatment is dissolved into contact with a chelate resin. It may be a method for producing oil or fat from which heavy metals have been removed.
本発明の方法によれば、重金属が溶解した油または脂肪から、キレート樹脂に接触させるという簡単な方法で、重金属をほぼ完全に除去することができる。この結果、処理後の油または脂肪をそのまま利用することができる。 According to the method of the present invention, heavy metal can be almost completely removed from oil or fat in which heavy metal is dissolved by a simple method of contacting the chelate resin. As a result, the treated oil or fat can be used as it is.
以下に、本発明を詳細に説明する。 The present invention is described in detail below.
[重金属が溶解した油または脂肪]
本発明で使用される重金属が溶解した油または脂肪としては、重金属を含む油または脂肪であれば特に制限はなく、例えば、廃潤滑油、重金属を有する炭化水素油(原油、石油製品など)、あるいは魚介類等の水産物、動物または植物から選択される少なくとも1種から得られる油または脂肪などが挙げられる。本発明の方法によれば、廃潤滑油のリサイクルを容易にすることができる。また、ホタテ貝の中腸線(ウロ)やイカの内臓(ゴロ)などの水産物の内臓など従来廃棄されていた部分から、重金属が除去された機能性脂質を得ることができる。
[Oil or fat in which heavy metals are dissolved]
The oil or fat in which heavy metal used in the present invention is dissolved is not particularly limited as long as it is an oil or fat containing heavy metal. For example, waste lubricating oil, hydrocarbon oil having heavy metal (crude oil, petroleum products, etc.), Or the oil or fat obtained from at least 1 sort (s) selected from marine products, such as seafood, an animal, or a plant is mentioned. According to the method of the present invention, the waste lubricating oil can be easily recycled. In addition, functional lipids from which heavy metals have been removed can be obtained from previously discarded portions such as visceral fisheries such as scallop midgut (uro) and squid internal organs (goro).
本発明の方法で除去される重金属としては、カドミウム、クロム、銅、錫、水銀、マンガン、モリブデン、ニッケル、鉛、亜鉛などが挙げられる。特に、銅、亜鉛、鉛、カドミウムは、効果的に除去できる。これらの重金属には、重金属単体およびこれらの化合物が含まれる。 Examples of the heavy metal removed by the method of the present invention include cadmium, chromium, copper, tin, mercury, manganese, molybdenum, nickel, lead, and zinc. In particular, copper, zinc, lead and cadmium can be effectively removed. These heavy metals include simple heavy metals and compounds thereof.
[前処理]
本発明で処理対象が、魚介類等の水産物、動物または植物から選択される少なくとも1種から得られる油または脂肪である場合には、これらの油または脂肪の抽出は、公知の技術を用いればよいが、魚介類等の水産物、動物または植物から選択される少なくとも1種を亜臨界または超臨界状態の水と接触させて抽出するのが好ましい。亜臨界または超臨界状態の水を用いて抽出すると、処理対象に含まれる重金属が油層または脂肪層に移動する。この結果、油または脂肪中から重金属を除去すれば水層から重金属を除去する必要はない。また、亜臨界または超臨界状態の水の接触条件(温度、圧力、時間、混合比など)を適宜選択することで、水可溶成分から有効成分を得ることができる。
[Preprocessing]
In the present invention, when the treatment target is oil or fat obtained from at least one selected from marine products such as seafood, animals or plants, extraction of these oils or fats can be performed using a known technique. However, it is preferable to extract at least one selected from marine products such as fish and shellfish, animals or plants in contact with subcritical or supercritical water. When extraction is performed using water in a subcritical or supercritical state, heavy metals contained in the treatment target move to the oil layer or fat layer. As a result, if heavy metals are removed from oil or fat, it is not necessary to remove heavy metals from the aqueous layer. Moreover, an active ingredient can be obtained from a water-soluble component by appropriately selecting the contact conditions (temperature, pressure, time, mixing ratio, etc.) of water in a subcritical or supercritical state.
ここで、水の超臨界状態とは、温度及び圧力が臨界点(374℃、22MPa)以上の状態にあることを言い、水の亜臨界状態とは、例えば374℃以上、2.5MPa以上22MPa未満あるいは374℃以下、22MPa以上の状態、あるいは374℃以下、22MPa未満であっても臨界点に近い高温高圧状態をいう。好ましくは、270℃以上、320℃以下の水の亜臨界状態である。 Here, the supercritical state of water means that the temperature and pressure are in a state of a critical point (374 ° C., 22 MPa) or higher, and the subcritical state of water is, for example, 374 ° C. or higher, 2.5 MPa or higher and 22 MPa. Or a state of 374 ° C. or lower and 22 MPa or higher, or a temperature of 374 ° C. or lower and lower than 22 MPa, a high temperature and high pressure state close to the critical point. Preferably, it is the subcritical state of 270 degreeC or more and 320 degrees C or less of water.
接触後、液体を冷却することで、水層、脂肪層、油層にそれぞれ分離する。脂肪層と油層とは、処理物により、共存する場合もあり、それぞれ単独で存在する場合もある。脂肪層または油層を本発明の方法に用いる。 After the contact, the liquid is cooled to separate into a water layer, a fat layer, and an oil layer. The fat layer and the oil layer may coexist depending on the processed product, or may exist independently. A fat layer or oil layer is used in the method of the present invention.
[金属除去処理]
本発明においては、重金属を含む脂肪または油をキレート樹脂で直接処理することにより、重金属を処理する。脂肪の場合は、加温して液体状態でキレート樹脂に接触させる。
[Metal removal treatment]
In the present invention, a heavy metal is treated by directly treating a fat or oil containing the heavy metal with a chelate resin. In the case of fat, it is heated and brought into contact with the chelate resin in a liquid state.
本発明で使用することのできるキレート樹脂としてはイミノジ酢酸基あるいはイミノジプロピオン酸基を有する樹脂であってカルボキシル基において重金属イオンとキレート結合することができるものであれば特に限定されない。例えば、多孔性の架橋ポリスチレン基体、スチレン・ジビニルベンゼン共重合体やカルバミン酸系樹脂等にイミノジ酢酸基やイミノジプロピオン酸基を結合させた樹脂のようなキレート樹脂が好ましい。イミノジ酢酸基を有するキレート樹脂の具体例としては、三菱化学株式会社製「ダイヤイオンCR11」、ローム&ハース社製「アンバーライトIRC748」、ミヨシ油脂株式会社製「エポラスMX-10」、イミノジプロピオン酸基を有するキレート樹脂の具体例としては、株式会社モリテックス製「エポラスMX-8,8C」、その他住化ケムテックス株式会社製「スミキレート」、旭硝子エンジニアリング株式会社製「アクリーンZ」、ユニチカテキスタイル株式会社製「ユニセレックUR-10S」、浦野株式会社製「ピュロライト、レバチット」が挙げられる。 The chelate resin that can be used in the present invention is not particularly limited as long as it is a resin having an iminodiacetic acid group or an iminodipropionic acid group and can chelate-bond with a heavy metal ion at a carboxyl group. For example, a chelating resin such as a resin obtained by binding an iminodiacetic acid group or an iminodipropionic acid group to a porous crosslinked polystyrene substrate, a styrene / divinylbenzene copolymer, a carbamic acid resin, or the like is preferable. Specific examples of chelating resins having an iminodiacetic acid group include “Diaion CR11” manufactured by Mitsubishi Chemical Corporation, “Amberlite IRC748” manufactured by Rohm & Haas, “Eporus MX-10” manufactured by Miyoshi Oil & Fats Co., Ltd., and Iminodipropion. Specific examples of chelate resins having acid groups include "Epolas MX-8, 8C" manufactured by Moritex Co., Ltd., "Sumichel" manufactured by Sumika Chemtex Co., Ltd., "Aclean Z" manufactured by Asahi Glass Engineering Co., Ltd. Examples include “Uniselec UR-10S” manufactured by the company and “Purolite, Levacit” manufactured by Urano Co., Ltd.
接触させる方法は、キレート樹脂を脂肪または油中に直接投入する、あるいはキレート樹脂カラムを通過させることによる。キレート樹脂を脂肪または油中に直接投入した場合には、ろ過等の簡単な分離により、重金属が除去された脂肪または油を得ることができる。回収された脂肪または油は人体に有害な成分を含有せず、そのまま機能性脂質として利用することができる。 The contact method is by directly feeding the chelate resin into fat or oil, or by passing it through a chelate resin column. When the chelate resin is directly put into fat or oil, fat or oil from which heavy metals have been removed can be obtained by simple separation such as filtration. The recovered fat or oil does not contain a component harmful to the human body and can be used as a functional lipid as it is.
以下、実施例により本発明を説明するが、本発明はかかる実施例に限定されるものではない。 EXAMPLES Hereinafter, although an Example demonstrates this invention, this invention is not limited to this Example.
[キレート樹脂、超多孔性PEIキレートキトサンビーズ、キトサン繊維における銅イオンの除去率]
(実施例1)
ホタテの内臓から得た油3.5mlと、硝酸第銅(II)水溶液(濃度0.01mol/L)と、アルゴンガスとを、反応管(SUS316)に充填して密閉した。硝酸第銅(II)水溶液は、水溶液中に含まれる銅イオンが全て油層に移行するとして、得られる油層中の銅イオンが、0.05〜1.4gになるような水溶液量とした。この反応管を、250℃の恒温槽に浸漬して急激に加熱し、10分間保持して、硝酸第銅(II)水溶液中の銅イオンを油層に移行させた。その後反応管を恒温槽から取り出して冷却槽に浸漬して、急冷させて常温まで戻した。
[Removal rate of copper ions in chelate resin, superporous PEI chelate chitosan beads, and chitosan fiber]
(Example 1)
A reaction tube (SUS316) was filled with 3.5 ml of oil obtained from the internal organs of scallops, an aqueous solution of cupric nitrate (II) (concentration 0.01 mol / L), and sealed. The aqueous solution of cupric nitrate (II) was such that the total amount of copper ions contained in the aqueous solution was transferred to the oil layer, so that the copper ion in the resulting oil layer was 0.05 to 1.4 g. This reaction tube was immersed in a constant temperature bath at 250 ° C. and rapidly heated and held for 10 minutes to transfer the copper ions in the cupric nitrate aqueous solution to the oil layer. Thereafter, the reaction tube was taken out of the thermostatic bath, immersed in a cooling bath, rapidly cooled, and returned to room temperature.
得られた油を誘導結合プラズマ(Inductively Coupled Plasma)で、油層中に含まれる銅イオンを定量した。油層中に銅イオンが、0.05〜1.4g含まれる銅含有サンプル(サンプル1〜8)を得た。 The obtained oil was quantified for copper ions contained in the oil layer with an inductively coupled plasma (Inductively Coupled Plasma). A copper-containing sample (samples 1 to 8) containing 0.05 to 1.4 g of copper ions in the oil layer was obtained.
これらの得られた油に、水酸化ナトリウム水溶液を添加して中和したイミノジ酢酸基を有するキレート樹脂(三菱化学株式会社製、製品名:ダイヤイオンCR−11)を投入し、銅イオンをキレート樹脂に結合させた。このキレート樹脂をろ別した。残りの油を、硝酸を用いて処理し、硝酸層をICPにより分析して、キレート樹脂により除去された銅イオン量を測定した。表1に、油層に含まれる銅イオンの量、油層中に含まれる銅イオン量(C0)(mol/l)、キレート樹脂により除去された後の油層中に含まれる銅イオン量(C)(mol/l)、除去率((C0−C)/C0)×100(%)を示す。
表1から、キレート樹脂を用いた場合は、ほぼ完全に銅イオンが除去されていることがわかる。 From Table 1, it can be seen that when the chelate resin is used, the copper ions are almost completely removed.
(比較例1)
キレート樹脂の代わりにキトサンビーズを用いた以外は、実施例1と同様に試験を行った。結果を表2に示す。なお、本明細書で使用した超多孔性PEIキトサンビーズは、キトサンをビーズ状に成形した後架橋処理し、さらにポリエチレンイミン(PEI)を導入したものを用いた。
(Comparative Example 1)
The test was performed in the same manner as in Example 1 except that chitosan beads were used instead of the chelating resin. The results are shown in Table 2. In addition, the superporous PEI chitosan beads used in the present specification were obtained by forming chitosan into beads and then cross-linking and further introducing polyethyleneimine (PEI).
(比較例2)
キレート樹脂の代わりにキトサン繊維を用いた以外は、実施例1と同様に試験を行った。なお、本明細書中で、キトサン繊維とは、キトサンを繊維状に成形した後、架橋したものである。結果を表2に示す。
(Comparative Example 2)
The test was performed in the same manner as in Example 1 except that chitosan fiber was used instead of the chelate resin. In the present specification, chitosan fibers are those obtained by forming chitosan into a fibrous form and then crosslinking. The results are shown in Table 2.
実施例1、比較例1、2の結果から、実施例1のようにキレート樹脂を用いると、銅イオン除去率が75%以上と、比較例1、2に比べ、銅イオンの除去率が高いことがわかった。 From the results of Example 1 and Comparative Examples 1 and 2, when a chelate resin is used as in Example 1, the copper ion removal rate is 75% or higher, which is higher than that of Comparative Examples 1 and 2. I understood it.
[キレート樹脂、超多孔性PEIキレートキトサンビーズ、キトサン繊維における鉛イオンの除去率]
(実施例2)
銅イオンの代わりに、鉛イオン(硝酸鉛)を用いた以外は、実施例1と同様に試験を行った。結果を表4に示す。
(Example 2)
The test was performed in the same manner as in Example 1 except that lead ion (lead nitrate) was used instead of copper ion. The results are shown in Table 4.
(比較例3)
銅イオンの代わりに、鉛イオン(硝酸鉛)を用いた以外は、比較例1と同様に試験を行った。結果を表5に示す。
(Comparative Example 3)
The test was performed in the same manner as in Comparative Example 1 except that lead ion (lead nitrate) was used instead of copper ion. The results are shown in Table 5.
(比較例4)
銅イオンの代わりに、鉛イオン(硝酸鉛)を用いた以外は、比較例2と同様に試験を行った。結果を表6示す。
A test was performed in the same manner as in Comparative Example 2 except that lead ion (lead nitrate) was used instead of copper ion. The results are shown in Table 6.
実施例2、比較例3、4の結果から、実施例2のようにキレート樹脂を用いると、鉛イオン除去率が27.8%以上と、比較例3、4に比べ、鉛イオンの除去率が高いことがわかった。 From the results of Example 2 and Comparative Examples 3 and 4, when a chelate resin is used as in Example 2, the lead ion removal rate is 27.8% or more, compared to Comparative Examples 3 and 4, and the removal rate of lead ions. Was found to be expensive.
[キレート樹脂、超多孔性PEIキレートキトサンビーズ、超多孔性PEIキレートキトサン繊維における亜鉛イオンの除去率]
(実施例3)
銅イオンの代わりに、亜鉛イオン(硝酸亜鉛)を用いた以外は、実施例1と同様に試験を行った。結果を表7に示す。
(Example 3)
The test was performed in the same manner as in Example 1 except that zinc ions (zinc nitrate) were used instead of copper ions. The results are shown in Table 7.
(比較例5) 銅イオンの代わりに、亜鉛イオン(硝酸亜鉛)を用いた以外は、比較例1と同様に試験を行った。結果を表8に示す。
(比較例6)
銅イオンの代わりに、亜鉛イオン(硝酸亜鉛)を用いた以外は、比較例2と同様に試験を行った。結果を表9示す。
The test was performed in the same manner as in Comparative Example 2 except that zinc ions (zinc nitrate) were used instead of copper ions. The results are shown in Table 9.
実施例3、比較例5、6の結果から、実施例3のようにキレート樹脂を用いると、亜鉛イオン除去率が94.8%以上と、比較例5、6に比べ、亜鉛イオンの除去率が極めて高いことがわかった。 From the results of Example 3 and Comparative Examples 5 and 6, when a chelate resin was used as in Example 3, the zinc ion removal rate was 94.8% or more, compared with Comparative Examples 5 and 6, and the zinc ion removal rate. Was found to be extremely high.
[亜臨界処理温度変化におけるキレート樹脂における重金属イオンの除去率の変化]
[亜臨界処理温度:225℃]
(実施例4)
(銅イオンの除去)
亜臨界処理を225℃で行った以外は、実施例1と同様に試験を行った。結果を表10に示す。
(実施例5)
(亜鉛イオンの除去)
亜臨界処理を225℃で行い、銅イオンの代わりに亜鉛イオンを用いた以外は、実施例1と同様に試験を行った。結果を表11に示す。
[Subcritical processing temperature: 225 ° C]
Example 4
(Removal of copper ions)
The test was performed in the same manner as in Example 1 except that the subcritical treatment was performed at 225 ° C. The results are shown in Table 10.
(Example 5)
(Zinc ion removal)
The test was conducted in the same manner as in Example 1 except that the subcritical treatment was performed at 225 ° C. and zinc ions were used instead of copper ions. The results are shown in Table 11.
(実施例6)
(カドミウムイオンの除去)
亜臨界処理を225℃で行い、銅イオンの代わりにカドミウムイオン(硝酸カドミウム0.01mol/l)を用いた以外は、実施例1と同様に試験を行った。結果を表12に示す。
(Example 6)
(Removal of cadmium ions)
The test was performed in the same manner as in Example 1 except that the subcritical treatment was performed at 225 ° C. and cadmium ions (cadmium nitrate 0.01 mol / l) were used instead of copper ions. The results are shown in Table 12.
(実施例7)
(鉛イオンの除去)
亜臨界処理を225℃で行い、銅イオンの代わりに鉛イオンを用いた以外は、実施例1と同様に試験を行った。結果を表13に示す。
(Removal of lead ions)
The test was performed in the same manner as in Example 1 except that the subcritical treatment was performed at 225 ° C. and lead ions were used instead of copper ions. The results are shown in Table 13.
[亜臨界処理温度変化におけるキレート樹脂における重金属イオンの除去率の変化]
[亜臨界処理温度:275℃]
(実施例8)
(銅イオンの除去)
亜臨界処理を275℃で行った以外は、実施例1と同様に試験を行った。結果を表14に示す。
[Subcritical processing temperature: 275 ° C]
(Example 8)
(Removal of copper ions)
The test was performed in the same manner as in Example 1 except that the subcritical treatment was performed at 275 ° C. The results are shown in Table 14.
(実施例9)
(カドミウムイオンの除去)
亜臨界処理を275℃で行い、銅イオンの代わりにカドミウムイオンを用いた以外は、実施例1と同様に試験を行った。結果を表15に示す。
(Removal of cadmium ions)
The test was performed in the same manner as in Example 1 except that the subcritical treatment was performed at 275 ° C. and cadmium ions were used instead of copper ions. The results are shown in Table 15.
(実施例10)
(鉛イオンの除去)
亜臨界処理を275℃で行い、銅イオンの代わりに鉛イオンを用いた以外は、実施例1と同様に試験を行った。結果を表16に示す。
(Removal of lead ions)
The test was conducted in the same manner as in Example 1 except that the subcritical treatment was performed at 275 ° C. and lead ions were used instead of copper ions. The results are shown in Table 16.
[亜臨界処理温度変化におけるキレート樹脂における重金属イオンの除去率の変化]
[亜臨界処理温度:300℃]
(実施例11)
(銅イオンの除去)
亜臨界処理を300℃で行った以外は、実施例1と同様に試験を行った。結果を表17に示す。
[Subcritical processing temperature: 300 ° C]
(Example 11)
(Removal of copper ions)
The test was performed in the same manner as in Example 1 except that the subcritical treatment was performed at 300 ° C. The results are shown in Table 17.
(実施例12)
(カドミウムイオンの除去)
亜臨界処理を300℃で行い、銅イオンの代わりにカドミウムイオンを用いた以外は、実施例1と同様に試験を行った。結果を表18に示す。
(Removal of cadmium ions)
The test was conducted in the same manner as in Example 1 except that the subcritical treatment was performed at 300 ° C. and cadmium ions were used instead of copper ions. The results are shown in Table 18.
(実施例13)
(鉛イオンの除去)
亜臨界処理を300℃で行い、銅イオンの代わりに鉛イオンを用いた以外は、実施例1と同様に試験を行った。結果を表19に示す。
(Removal of lead ions)
The test was conducted in the same manner as in Example 1 except that the subcritical treatment was performed at 300 ° C. and lead ions were used instead of copper ions. The results are shown in Table 19.
(結論)
実施例4〜13から、銅イオン、カドミウムイオン、亜鉛イオン、鉛イオンは、前処理の亜臨界処理条件により、キレート樹脂に捕捉される量が代わることがわかった。具体的には、225℃の低温では、銅イオンが、カドミウムイオン、亜鉛イオン、鉛イオンに比べ、キレート樹脂により除去される割合が高いことがわかる。275℃、300℃では、亜鉛イオンが、銅イオン、カドミウムイオン、鉛イオンに比べ、キレート樹脂により除去される割合が高いことがわかる。
(Conclusion)
From Examples 4 to 13, it was found that the amount of copper ions, cadmium ions, zinc ions, and lead ions captured by the chelate resin was changed depending on the subcritical treatment conditions of the pretreatment. Specifically, it can be seen that at a low temperature of 225 ° C., the proportion of copper ions removed by the chelate resin is higher than that of cadmium ions, zinc ions, and lead ions. It can be seen that at 275 ° C. and 300 ° C., the proportion of zinc ions removed by the chelate resin is higher than copper ions, cadmium ions, and lead ions.
[キレート樹脂における脂肪に溶解した重金属イオンの除去率の変化]
(実施例11)
(銅イオンの除去)
油の代わりに脂肪を用い、亜臨界処理を300℃で行った以外は、実施例1と同様に試験を行った。なお、キレート樹脂による処理は、脂肪を溶解させた状態で行なった。結果を表20に示す。
(Example 11)
(Removal of copper ions)
The test was performed in the same manner as in Example 1 except that fat was used instead of oil and subcritical treatment was performed at 300 ° C. The treatment with the chelate resin was performed in a state where fat was dissolved. The results are shown in Table 20.
(実施例12)
(亜鉛イオンの除去)
油の代わりに脂肪を用い、亜臨界処理を300℃で行い、銅イオンの代わりに亜鉛イオンを用いた以外は、実施例1と同様に試験を行った。結果を表21に示す。
(Zinc ion removal)
A test was conducted in the same manner as in Example 1 except that fat was used instead of oil, subcritical treatment was performed at 300 ° C., and zinc ions were used instead of copper ions. The results are shown in Table 21.
(実施例13)
(カドミウムイオンの除去)
油の代わりに脂肪を用い、亜臨界処理を300℃で行い、銅イオンの代わりにカドミウムイオンを用いた以外は、実施例1と同様に試験を行った。結果を表22に示す。
(Removal of cadmium ions)
A test was conducted in the same manner as in Example 1 except that fat was used instead of oil, subcritical treatment was performed at 300 ° C., and cadmium ions were used instead of copper ions. The results are shown in Table 22.
(実施例14)
(鉛イオンの除去)
油の代わりに脂肪を用い、亜臨界処理を300℃で行い、銅イオンの代わりに鉛イオンを用いた以外は、実施例1と同様に試験を行った。結果を表23に示す。
(Removal of lead ions)
A test was conducted in the same manner as in Example 1 except that fat was used instead of oil, subcritical treatment was performed at 300 ° C., and lead ions were used instead of copper ions. The results are shown in Table 23.
(結論)
実施例11〜14から、脂肪においても、亜臨界処理をすると重金属が溶解することがわかった。また、脂肪に溶解した重金属イオンは、キレート樹脂によって除去できることがわかった。
(Conclusion)
From Examples 11 to 14, it was found that heavy metals dissolve in fat even when subcritical treatment is performed. It was also found that heavy metal ions dissolved in fat can be removed by a chelate resin.
以上より、油または脂肪に溶解した重金属イオンは、キレート樹脂を用いれば有効に除去できることがわかった。
From the above, it was found that heavy metal ions dissolved in oil or fat can be effectively removed by using a chelate resin.
Claims (4)
前記処理により得られた重金属が溶解した油または脂肪を、キレート樹脂に接触させる工程と
を含む、重金属が除去された油または脂肪の製造方法。
Treating a treated product containing heavy metal with subcritical or supercritical water;
A method for producing oil or fat from which heavy metals have been removed, comprising the step of bringing oil or fat in which heavy metals obtained by the treatment are dissolved into contact with a chelate resin.
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JP2011218312A (en) * | 2010-04-12 | 2011-11-04 | Miike Iron Works Co Ltd | Recycling plant for fishery waste |
CN108707509A (en) * | 2018-07-23 | 2018-10-26 | 昆明理工大学 | A kind of device and method reducing biodiesel metal ion content |
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JP2004097939A (en) * | 2002-09-09 | 2004-04-02 | Marine Science Kk | Method for processing scallop internal organ |
JP2005081330A (en) * | 2003-09-11 | 2005-03-31 | Osaka Industrial Promotion Organization | Method for treating waste originated from mollusk |
JP2007152217A (en) * | 2005-12-05 | 2007-06-21 | Shimizu Corp | Treatment method for fishery waste |
JP2007282572A (en) * | 2006-04-17 | 2007-11-01 | Hokkaido Univ | Method for removing heavy metal from organic substance containing heavy metal, and method for producing food obtained by the same |
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JP2004097939A (en) * | 2002-09-09 | 2004-04-02 | Marine Science Kk | Method for processing scallop internal organ |
JP2005081330A (en) * | 2003-09-11 | 2005-03-31 | Osaka Industrial Promotion Organization | Method for treating waste originated from mollusk |
JP2007152217A (en) * | 2005-12-05 | 2007-06-21 | Shimizu Corp | Treatment method for fishery waste |
JP2007282572A (en) * | 2006-04-17 | 2007-11-01 | Hokkaido Univ | Method for removing heavy metal from organic substance containing heavy metal, and method for producing food obtained by the same |
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JP2011218312A (en) * | 2010-04-12 | 2011-11-04 | Miike Iron Works Co Ltd | Recycling plant for fishery waste |
CN108707509A (en) * | 2018-07-23 | 2018-10-26 | 昆明理工大学 | A kind of device and method reducing biodiesel metal ion content |
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