WO2017018524A1 - エンドトキシン吸着剤 - Google Patents
エンドトキシン吸着剤 Download PDFInfo
- Publication number
- WO2017018524A1 WO2017018524A1 PCT/JP2016/072347 JP2016072347W WO2017018524A1 WO 2017018524 A1 WO2017018524 A1 WO 2017018524A1 JP 2016072347 W JP2016072347 W JP 2016072347W WO 2017018524 A1 WO2017018524 A1 WO 2017018524A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- cellulose
- adsorbent
- present
- endotoxin
- less
- Prior art date
Links
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/24—Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
-
- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61K—PREPARATIONS FOR MEDICAL, DENTAL OR TOILETRY PURPOSES
- A61K47/00—Medicinal preparations characterised by the non-active ingredients used, e.g. carriers or inert additives; Targeting or modifying agents chemically bound to the active ingredient
- A61K47/30—Macromolecular organic or inorganic compounds, e.g. inorganic polyphosphates
- A61K47/36—Polysaccharides; Derivatives thereof, e.g. gums, starch, alginate, dextrin, hyaluronic acid, chitosan, inulin, agar or pectin
- A61K47/38—Cellulose; Derivatives thereof
-
- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61K—PREPARATIONS FOR MEDICAL, DENTAL OR TOILETRY PURPOSES
- A61K9/00—Medicinal preparations characterised by special physical form
- A61K9/70—Web, sheet or filament bases ; Films; Fibres of the matrix type containing drug
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction
- B01D15/361—Ion-exchange
- B01D15/363—Anion-exchange
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
- B01J20/262—Synthetic macromolecular compounds obtained otherwise than by reactions only involving carbon to carbon unsaturated bonds, e.g. obtained by polycondensation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
- B01J20/265—Synthetic macromolecular compounds modified or post-treated polymers
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28002—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
- B01J20/28004—Sorbent size or size distribution, e.g. particle size
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28002—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
- B01J20/28004—Sorbent size or size distribution, e.g. particle size
- B01J20/28007—Sorbent size or size distribution, e.g. particle size with size in the range 1-100 nanometers, e.g. nanosized particles, nanofibers, nanotubes, nanowires or the like
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28014—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
- B01J20/28023—Fibres or filaments
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3085—Chemical treatments not covered by groups B01J20/3007 - B01J20/3078
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
- B01J20/3202—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the carrier, support or substrate used for impregnation or coating
- B01J20/3206—Organic carriers, supports or substrates
- B01J20/3208—Polymeric carriers, supports or substrates
- B01J20/3212—Polymeric carriers, supports or substrates consisting of a polymer obtained by reactions otherwise than involving only carbon to carbon unsaturated bonds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
- B01J20/3231—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
- B01J20/3242—Layers with a functional group, e.g. an affinity material, a ligand, a reactant or a complexing group
- B01J20/3244—Non-macromolecular compounds
- B01J20/3246—Non-macromolecular compounds having a well defined chemical structure
- B01J20/3248—Non-macromolecular compounds having a well defined chemical structure the functional group or the linking, spacer or anchoring group as a whole comprising at least one type of heteroatom selected from a nitrogen, oxygen or sulfur, these atoms not being part of the carrier as such
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
- C02F2001/422—Treatment of water, waste water, or sewage by ion-exchange using anionic exchangers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/34—Organic compounds containing oxygen
-
- 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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/30—Against vector-borne diseases, e.g. mosquito-borne, fly-borne, tick-borne or waterborne diseases whose impact is exacerbated by climate change
Definitions
- the present invention relates to an endotoxin adsorbent and a method for removing endotoxin using the same.
- Endotoxin is one of toxic substances, and specifically refers to lipopolysaccharide (LPS) which is a component of the outer membrane of Gram-negative bacteria.
- LPS lipopolysaccharide
- ET is composed of a polysaccharide and lipid A, and lipid A mainly contributes to toxicity.
- ET causes a fever and a shock reaction when taken into a living body by mixing into an injection solution or the like. Therefore, the Japanese Pharmacopoeia stipulates that the ET concentration of an injectable solution should be 10-100 pg / mL (0.1-1.0 endotoxin unit (EU) / mL) or less.
- ET adsorbent for example, a cationic ET adsorbent such as poly ( ⁇ -lysine) -immobilized cellulose particles (Non-patent Document 1) is known.
- cationic ET adsorbents also show ionic interactions with acidic substances such as nucleic acids and acidic proteins, ET is selectively removed in the presence of acidic substances using cationic ET adsorbents. It was difficult. Therefore, an ET adsorbent capable of selectively removing ET is eagerly desired.
- an ET adsorbent capable of selectively removing ET in the presence of an acidic protein such as BSA for example, polyethyleneimine-immobilized regenerated cellulose fiber is known (Non-patent Document 2).
- An object of the present invention is to provide a novel ET adsorbent having high ET adsorption ability.
- the present inventors have introduced an amino group into cellulose nanofibers, so that the ET adsorbent having high ET adsorbing ability, particularly high selection in the coexistence of acidic protein.
- the present invention was completed by finding that an ET adsorbent exhibiting a specific ET adsorption ability was obtained.
- the present invention includes the following configuration.
- An endotoxin adsorbent comprising cellulose nanofibers having amino groups.
- the endotoxin adsorbent wherein the amount of amino groups in the cellulose nanofiber is 0.05 to 3.0 meq / dry-g.
- the endotoxin adsorbent, wherein the cellulose nanofiber has an average fiber diameter of 1 nm to 1000 nm.
- a method for producing the endotoxin adsorbent, comprising a step of introducing an amino group into cellulose nanofibers.
- a method for removing endotoxin comprising bringing the endotoxin adsorbent into contact with a liquid containing endotoxin.
- a method for producing a liquid from which endotoxin has been removed comprising bringing the endotoxin adsorbent into contact with a liquid containing endotoxin.
- a method for removing endotoxin comprising contacting the endotoxin adsorbent with a liquid containing the target substance and endotoxin.
- a method for producing a liquid containing a target substance from which endotoxin has been removed comprising bringing the endotoxin adsorbent into contact with a liquid containing the target substance and endotoxin.
- the method, wherein the target substance is a substance showing a negative charge.
- the method, wherein the target substance is a protein having an isoelectric point of 4.0 to 10.5.
- Endotoxin adsorbent of the present invention is an ET adsorbent comprising cellulose nanofibers having amino groups.
- the cellulose nanofiber having an amino group is also referred to as “cellulose nanofiber used in the present invention”.
- ET is also referred to as “LPS”.
- Cellulose nanofiber refers to fibrous cellulose having an average fiber diameter on the order of nanometers.
- the “cellulose nanofiber” may specifically be fibrous cellulose having an average fiber diameter of 1 nm to 1000 nm.
- the average fiber diameter of the cellulose nanofiber is not particularly limited as long as it is within the above range.
- the average fiber diameter of the cellulose nanofiber may be, for example, 1 nm or more, 3 nm or more, 5 nm or more, 10 nm or more, 20 nm or more, or 30 nm or more, 1000 nm or less, 500 nm or less, 300 nm or less, 200 nm or less, 150 nm or less, It may be 100 nm or less, 90 nm or less, 80 nm or less, 70 nm or less, 60 nm or less, or 50 nm or less, or a combination thereof.
- the average fiber diameter of the cellulose nanofiber may be, for example, 3 nm to 500 nm, 5 nm to 300 nm, or 10 nm to 200 nm.
- the cellulose nanofiber may have high uniformity about the fiber diameter. That is, the standard deviation of the fiber diameter distribution of the cellulose nanofiber may be, for example, 100 nm or less, 70 nm or less, 50 nm or less, 40 nm or less, 30 nm or less, or 20 nm or less.
- the average fiber length of the cellulose nanofiber is not particularly limited as long as the desired ET adsorption ability is obtained.
- the average fiber length of the cellulose nanofiber may be, for example, 5 ⁇ m or more, 10 ⁇ m or more, 50 ⁇ m or more, 100 ⁇ m or more, 200 ⁇ m or more, 300 ⁇ m or more, 500 ⁇ m or more, or 1000 ⁇ m or more, 100000 ⁇ m or less, 10,000 ⁇ m or less, 3000 ⁇ m or less, It may be 2500 ⁇ m or less, 2000 ⁇ m or less, 1500 ⁇ m or less, or 1200 ⁇ m or less, or a combination thereof.
- the average fiber length of the cellulose nanofiber may be, for example, 10 ⁇ m to 3000 ⁇ m, 100 ⁇ m to 2500 ⁇ m, 200 ⁇ m to 2000 ⁇ m, 300 ⁇ m to 1500 ⁇ m, or 500 ⁇ m to 1200 ⁇ m.
- the average aspect ratio of the cellulose nanofiber is not particularly limited as long as a desired ET adsorption ability is obtained.
- Average aspect ratio refers to the ratio of average fiber length to average fiber diameter (ie, average fiber length / average fiber diameter).
- the average aspect ratio of the cellulose nanofiber may be, for example, 100 or more, 500 or more, 1000 or more, 2000 or more, 3000 or more, 5000 or more, 10,000 or more, or 20000 or more, and may be 100000 or less, 80000 or less, 50000 or less, It may be 40000 or less, or 35000 or less, or a combination thereof.
- the average aspect ratio of the cellulose nanofiber may be, for example, 2000-100000, 3000-80000, 5000-50000, 10000-40000, or 20000-35000.
- the average fiber diameter, the standard deviation of the fiber diameter distribution, the average fiber length, and the average aspect ratio are all based on the results of measuring the dimensions of at least 20 randomly selected cellulose nanofibers using an electron microscope. Shall be calculated.
- the average fiber diameter, the standard deviation of the fiber diameter distribution, the average fiber length, and the average aspect ratio are respectively obtained when cellulose nanofibers having amino groups are obtained by introducing amino groups into cellulose nanofibers. It may mean the average fiber diameter, standard deviation of fiber diameter distribution, average fiber length, and average aspect ratio of cellulose nanofibers before introduction of amino groups. By introducing an amino group into the cellulose nanofiber, the cellulose nanofiber can swell. Therefore, for example, the average fiber diameter of the cellulose nanofibers after the introduction of amino groups can be larger than the average fiber diameter of the cellulose nanofibers exemplified above.
- the method for producing cellulose nanofiber is not particularly limited.
- Cellulose nanofibers can be produced, for example, by a known method.
- Cellulose nanofibers are obtained, for example, by appropriately processing cellulose fibers so as to obtain a desired average fiber diameter.
- Cellulose fibers which are raw materials for producing cellulose nanofibers are also referred to as “raw fiber”.
- the origin of the raw fiber is not particularly limited.
- the raw material fibers include cellulose fibers derived from higher plants, cellulose fibers derived from animals, cellulose fibers derived from algae, cellulose fibers derived from bacteria, chemically synthesized cellulose fibers, and derivatives thereof.
- Cellulose fibers derived from higher plants include: wood fibers such as wood pulp derived from conifers and broad-leaved trees; seed hair fibers such as cotton linters, Bombax cotton and kapok; bast fibers such as hemp, mulberry, and mitsumata; Manila hemp and sisal hemp , New Zealand hemp and other leaf vein fibers; bamboo fibers; sugarcane fibers.
- a cellulose fiber derived from an animal a sea squirt is mentioned.
- the cellulose fiber derived from algae include valonia cellulose.
- the cellulose fiber derived from bacteria include cellulose produced by acetic acid bacteria.
- the chemically synthesized cellulose fiber include alkyl celluloses such as methyl cellulose and ethyl cellulose.
- the derivatives include cellulose fibers having a functional group introduced (substituted). That is, in the present invention, the term “cellulose” includes those having such a functional group. There are no particular limitations on the type or amount of the functional group introduced (substituted) as long as the cellulose nanofiber used in the present invention can be produced.
- the functional group include amino groups and “other functional groups” (functional groups other than amino groups) described later.
- a method for producing cellulose nanofibers from raw material fibers a method of producing cellulose nanofibers by microfibrating raw material fibers using a crushing device such as a refiner, a homogenizer, a medium stirring mill, a stone mortar, or a grinder (Japanese Patent Laid-Open No. 2003-260707) 2011-026760, JP 2012-025833, JP 2012-036517, JP 2012-036518, JP 2013-236585), cellulose by mixing raw fibers and functional particles and kneading under pressure conditions
- a method for producing nanofibers Japanese Patent Laid-Open No.
- raw fiber is disaggregated by wet process, preliminarily defibrated, steamed, and microfibrillated using a crushing device to produce cellulose nanofibers
- a method in which an enzyme is used in combination Japanese Patent Application Laid-Open No. 2008-075214
- the raw fiber is disaggregated in a wet manner, preliminarily defibrated, and microscopically treated by ultrasonic treatment.
- a method for producing a cellulose nanofibers by Iburiru of, and how to use the enzyme is.
- Cellulose nanofibers can also be produced, for example, by spinning from an ionic liquid solution of cellulose or an organic solvent solution of cellulose (JP 2015-004151, JP 2009-203467).
- the cellulose fiber having an average fiber diameter as described above can be used as it is or after being appropriately processed.
- the cellulose fiber having an average fiber diameter as described above include cellulose produced by acetic acid bacteria.
- cellulose nanofiber a commercially available product can be used as the cellulose nanofiber.
- examples of commercially available cellulose nanofibers include Selish (registered trademark) manufactured by Daicel Finechem Co., Ltd. and Cellulon (registered trademark) manufactured by Kelco.
- Examples of serisch include KY-100S, KY-100G, KY-110N, and KY-1005.
- the cellulose nanofiber used in the present invention has an amino group (—NH 2 ).
- the cellulose nanofiber used in the present invention may inherently have an amino group or may be modified to have an amino group.
- Cellulose nanofibers modified to have amino groups are also referred to as “aminated cellulose nanofibers”.
- Aminated cellulose nanofibers can be obtained, for example, by introducing amino groups into cellulose nanofibers.
- the method for introducing an amino group into cellulose nanofiber is not particularly limited.
- the amino group can be introduced into the cellulose nanofiber by, for example, a known method for introducing an amino group into cellulose.
- the amino group can be introduced into the hydroxyl group of cellulose, for example.
- Introduction of an amino group into a hydroxyl group can be performed by, for example, a known method.
- Examples of a method for introducing an amino group into a hydroxyl group of cellulose include a method in which a hydroxyl group of cellulose is activated with an activator and then reacted with an amino group donor (JP 2003-048902, JP 2009-167307).
- the activator include chloromethyloxirane (epichlorohydrin), p-toluenesulfonic acid chloride, and 2-fluoro-1-methylpyridinium.
- Examples of the amino group donor include those described later such as polyethyleneimine and ethylenediamine.
- cellulose having an amino group introduced into a hydroxyl group is obtained by epoxidizing the hydroxyl group of cellulose with chloromethyloxirane and then reacting with polyethyleneimine or ethylenediamine (see Examples).
- an amino group can also be selectively introduce
- a specific hydroxyl group of cellulose includes a hydroxyl group at the 6-position of cellulose.
- cellulose having an amino group introduced at the 6-position hydroxyl group can be produced (Carbohydrate Research, 340 (2005) 1403-1406, Carbohydrate Research, 208 (1990) 183-191, JP 2009-293017).
- Examples of amino group donors include ammonia and amines.
- Examples of the amine include a monovalent amine (an amine having one amino group) and a polyvalent amine (an amine having two or more amino groups).
- Examples of monovalent amines include alkylamines such as methylamine, ethylamine, dimethylamine, and diethylamine; amino alcohols such as methanolamine, ethanolamine, methylethanolamine, ethylethanolamine, dimethylethanolamine, and diethylethanolamine; Aromatic amines are mentioned.
- polyvalent amines examples include aliphatic diamines such as ethylenediamine, tetramethylenediamine, and hexamethylenediamine; alicyclic diamines such as 4,4'-diamino-3,3'dimethyldicyclohexylmethane, diaminecyclohexane, and isophoronediamine; phenylenediamine , Aromatic amines such as diaminonaphthalene and xylylenediamine; trivalent or higher aliphatic amines such as diethylenetriamine, triethylenetetramine, tetraethylenepentamine, tris (2-aminoethyl) amine, and tris (3-aminopropyl) amine A trivalent or higher valent aromatic amine such as melamine; and polymers having amino groups such as polyethyleneimine, polyvinylamine, and polyallylamine.
- aliphatic diamines such as ethylenediamine, tetramethyl
- Such polymers may be linear (linear type) or branched (branch type).
- the number average molecular weight of such a polymer is not particularly limited.
- the number average molecular weight of such a polymer may be, for example, 200 or more, 300 or more, or 400 or more, 1,000,000 or less, 100,000 or less, 10,000 or less, 5,000 or less, 1,000 or less, or 1,000 or less, or a combination thereof.
- the number average molecular weight of such a polymer may be, for example, 400 to 100,000.
- the polyvalent amine include polyethyleneimine, ethylenediamine, diethylenetriamine, triethylenetetramine, tetraethylenepentamine, and pentaethylenehexamine.
- the amino group donor one amino group donor may be used, or two or more amino group donors may be used.
- an epoxy group donor such as glycidyl methacrylate or glycidyl acrylate is introduced into cellulose by a graft reaction, and then an amino group donor such as ammonia or amine is added to the epoxy group.
- an amino group donor such as ammonia or amine is added to the epoxy group.
- the method of making it react is also mentioned.
- the content of amino groups in the cellulose nanofiber used in the present invention is not particularly limited as long as a desired ET adsorption ability is obtained.
- the content of amino groups in the cellulose nanofiber is, for example, 0.01 meq / dry-g or more, 0.03 meq / dry-g or more, 0.05 meq / dry-g or more, as anion exchange capacity (AEC).
- 0.07 meq / dry-g or more 0.07 meq / dry-g or more, 0.1 meq / dry-g or more, 0.3 meq / dry-g or more, or 0.5 meq / dry-g or more, or 10.0 meq / dry-g or less, 5.0 meq / dry-g or less, 3.0 meq / dry-g or less, 2.5 meq / dry-g or less, 2.0 meq / dry-g or less, 1.5 meq / dry-g or less, 1.2 meq / dry -G or less, or 1.0 meq / dry-g or less, or a combination thereof.
- the content of amino groups in the cellulose nanofiber is specifically an anion exchange capacity (AEC), for example, 0.05 to 3.0 meq / dry-g, 0.1 to 2.0 meq / dry-g. Or 0.5 to 1.0 meq / dry-g.
- AEC anion exchange capacity
- the cellulose nanofiber used in the present invention has a functional group other than an amino group (hereinafter also referred to as “other functional group”) as long as the fiber form can be maintained and a desired ET adsorption ability can be obtained. You may do it.
- the cellulose nanofibers used in the present invention may inherently have other functional groups, or may be modified so as to have other functional groups. Examples of other functional groups include alkyl groups, alkoxy groups, epoxy groups, carboxyl groups, hydroxyl groups, phosphate groups, sulfate groups, formyl groups, acetyl groups, hydrogen, and halogens. Examples of the alkyl group include alkyl groups having 1 to 10, 1 to 7, 1 to 5, or 1 to 3 carbon atoms.
- the alkyl group may be a straight chain or may have a branch.
- the alkoxy group include an alkoxy group having 1 to 10, 1 to 7, 1 to 5, or 1 to 3 carbon atoms.
- the alkoxy group may be a straight chain or may have a branch.
- the hydrogen of the alkyl group or alkoxy group may be further independently substituted with another functional group such as another functional group or amino group as exemplified above.
- the halogen include fluorine, chlorine, bromine and iodine.
- some or all of the hydroxyl groups inherently possessed by the cellulose nanofibers may remain, or one of functional groups such as epoxy groups used for introducing amino groups. The part may remain.
- the cellulose nanofiber used in the present invention may have one type of other functional group, or may have two or more types of other functional groups.
- the content of other functional groups in the cellulose nanofiber used in the present invention is not particularly limited as long as the fiber form can be maintained and a desired ET adsorption ability can be obtained.
- a substance having a negative charge such as an acidic substance
- it is used in the present invention from the viewpoint of reducing nonspecific adsorption of the substance having a negative charge.
- the content of anion exchange groups other than amino groups in cellulose nanofibers is small.
- the content of anion exchange groups other than amino groups in the cellulose nanofiber used in the present invention is, for example, 1 meq / g or less, 0.7 meq / g or less, 0.5 meq / g as anion exchange capacity (AEC). Hereinafter, it may be 0.3 meq / g or less, 0.1 meq / g or less, 0.05 meq / g or less, or 0 (zero). Further, for example, in the case where a substance having a positive charge such as a basic substance is present in a sample to be treated with the ET adsorbent of the present invention, the present invention is used from the viewpoint of reducing nonspecific adsorption of the substance having a positive charge.
- AEC anion exchange capacity
- the content of the cation exchange group in the cellulose nanofiber used in is low.
- the cation exchange group content in the cellulose nanofibers used in the present invention is, for example, 1 meq / g or less, 0.7 meq / g or less, 0.5 meq / g or less, as cation exchange capacity (CEC). It may be 3 meq / g or less, 0.1 meq / g or less, 0.05 meq / g or less, or 0 (zero).
- the ion exchange capacity can be quantified by pH titration method.
- the description of the examples can be referred to.
- the cellulose nanofiber used in the present invention may have a large ET adsorption capacity.
- the ET adsorption capacity of the cellulose nanofiber used in the present invention may be, for example, 500 ⁇ g or more, 700 ⁇ g or more, 800 ⁇ g or more, or 850 ⁇ g or more per 1 wet-g.
- the cellulose nanofibers used in the present invention may have a small apparent ET dissociation constant.
- the apparent ET dissociation constant of the cellulose nanofiber used in the present invention is, for example, 2.0 ⁇ 10 ⁇ 11 M or less, 1.7 ⁇ 10 ⁇ 11 M or less, 1.5 ⁇ 10 ⁇ 11 M or less, or 1.3 ⁇ 10 ⁇ 11 M. It may be the following.
- the ET adsorption capacity and the apparent ET dissociation constant can be calculated from a linear equation obtained from a Scatchard plot created based on the ET adsorption isotherm.
- the description of the examples can be referred to.
- the cellulose nanofiber having an amino group can be dispersed and stored in an appropriate dispersion medium such as methanol or ethanol.
- the cellulose nanofiber having an amino group can be used alone or in combination with other components as the ET adsorbent of the present invention. That is, the ET adsorbent of the present invention may be composed of cellulose nanofibers having amino groups, and may further comprise other components. Other components are not particularly limited as long as a desired ET adsorption capacity is obtained.
- ET-free can be performed by a conventional method. Specifically, ET-free can be performed, for example, by washing the ET adsorbent of the present invention once or a plurality of times using an appropriate washing solution. Although it does not restrict
- the ET adsorbent of the present invention may be provided as it is or after being appropriately processed.
- the ET adsorbent of the present invention may be provided in a form that can be suitably used for the ET removal method of the present invention.
- the ET adsorbent of the present invention can be used after being processed into an arbitrary form such as a particle or film.
- the ET adsorbent of the present invention can be packed in a column and used. That is, the ET adsorbent of the present invention may be provided, for example, as a column for removing ET by filling the column. That is, the present invention provides an ET removal column packed with the ET adsorbent of the present invention.
- ET Adsorbent of the Present Invention ET can be removed using the ET adsorbent of the present invention. That is, the present invention provides a method for removing ET, which comprises contacting the ET adsorbent of the present invention with a liquid containing ET. This method is also referred to as “ET removal method of the present invention”. “Liquid containing ET” is also referred to as “ET-containing liquid”.
- ET removal method of the present invention a liquid from which ET has been removed is obtained. That is, the ET removal method of the present invention may be a method for producing a liquid from which ET has been removed, which comprises contacting the ET adsorbent of the present invention with a liquid containing ET.
- the ET-containing liquid is not particularly limited as long as it is a liquid containing ET.
- the ET-containing liquid may further contain substances other than ET.
- the liquid include water, a solution such as an aqueous solution, and a suspension such as an aqueous suspension.
- water include medical water such as water for injection.
- one aspect of the ET removal method of the present invention is a method for removing ET, which comprises contacting the ET adsorbent of the present invention with a liquid containing the target substance and ET. According to one embodiment of the ET removal method of the present invention, a liquid containing a target substance from which ET has been removed can be obtained.
- one aspect of the ET removal method of the present invention includes the step of bringing the ET adsorbent of the present invention into contact with a liquid containing the target substance and ET, and producing a liquid containing the target substance from which the ET has been removed. It may be a method.
- the target substance from which the ET has been removed can be obtained by recovering the target substance from the liquid containing the target substance from which the ET has been removed, obtained by one embodiment of the ET removal method of the present invention. That is, in one aspect of the ET removal method of the present invention, ET has been removed, including contacting the ET adsorbent of the present invention with a liquid containing the target substance and ET, and collecting the target substance. It may be a method for producing a target substance.
- the ET-containing liquid may, for example, originally contain the target substance and ET, or may be prepared by dissolving or suspending the target substance contaminated with ET in a liquid medium. Good.
- the ET-containing liquid may contain one kind of target substance or may contain two or more kinds of target substances.
- the target substance is not particularly limited.
- the ET adsorbent of the present invention can be used particularly for selectively removing ET in the presence of a negative charge substance or a viscous substance. Therefore, examples of the target substance include a substance showing a negative charge and a viscous substance. Examples of the target substance include active ingredients contained in pharmaceutical products such as injection solutions, and pharmaceutical raw materials such as polymer materials used as raw materials for artificial organs and artificial bones. These target substances may belong to two or more categories.
- the target substance may be a viscous substance exhibiting negative charge, or may be an active ingredient or a pharmaceutical raw material exhibiting negative charge or viscosity.
- a substance that exhibits a negative charge refers to a substance having a functional group that easily becomes an anion in the molecule.
- the “functional group that easily becomes an anion” refers to a functional group that can become an anion in any liquid containing a substance having the functional group.
- a functional group that can become an anion in the ET-containing liquid is a “functional group that easily becomes an anion”. That is, the “substance exhibiting a minus charge” may indicate a minus charge in an arbitrary liquid containing the substance, for example, in an ET-containing liquid.
- the “functional group that easily becomes an anion” include acidic groups such as a carboxyl group, a sulfate group, and a phosphate group.
- examples of the “substance exhibiting negative charge” include acidic substances.
- examples of the “substance exhibiting negative charge” include proteins, peptides, hormones, polysaccharides, nucleic acids, lipids, vitamins, and artificial polymers that exhibit negative charge.
- proteins and peptides exhibiting a negative charge include proteins and peptides containing acidic amino acid residues.
- acidic amino acid residues include glutamic acid residues and aspartic acid residues.
- Proteins and peptides exhibiting a negative charge may mean, for example, proteins and peptides having an isoelectric point of 4.0 to 10.5.
- ET can be selectively removed in the presence of a protein or peptide having an isoelectric point of 4.0 to 10.5.
- proteins having an isoelectric point of 4.0 to 10.5 include bovine serum albumin (BSA), globulin, myoglobin, and lysozyme.
- polysaccharides that exhibit a negative charge include polyanion derivatives of polysaccharides such as cellulose, amylose, pullulan, starch, and dextrin, and glucosaminoglycans such as heparin, hyaluronic acid, and chondroitin sulfate.
- Examples of the polyanion derivative of cellulose include carboxymethyl cellulose and sulfated cellulose.
- Nucleic acid is an acidic substance containing a large amount of phosphate ester in the molecule, and examples of the nucleic acid include DNA and RNA.
- Examples of the artificial polymer exhibiting a negative charge include polyacrylic acid. These “substances exhibiting a negative charge” may be natural products such as biological substances, or may be artificially modified or synthesized.
- “Viscous substance” includes, for example, fibrous viscous polymer.
- fibrous viscous polymer include polysaccharides exhibiting a negative charge, and fibrous proteins such as collagen and gelatin.
- the ET-containing liquid may be appropriately subjected to pretreatment or the like before contacting with the ET adsorbent of the present invention.
- the ET-containing liquid may be diluted or concentrated and then contacted with the ET adsorbent of the present invention.
- the pH of the ET-containing liquid may or may not be adjusted.
- the pH of the ET-containing liquid is not particularly limited as long as ET is removed.
- the pH of the ET-containing liquid may be, for example, 3 to 10, preferably 4 to 9, and more preferably 4 to 6.
- the pH of the ET-containing liquid may be adjusted in consideration of, for example, the stability of the target substance at each pH.
- the pH can be adjusted using, for example, a buffer solution.
- the type of buffer solution is not particularly limited, and can be appropriately selected according to various conditions such as desired pH.
- the ionic strength of the ET-containing liquid may or may not be adjusted.
- the ionic strength ( ⁇ ) of the ET-containing liquid is not particularly limited as long as ET is removed.
- the ionic strength ( ⁇ ) of the ET-containing liquid may be, for example, 0.05 to 0.8, 0.05 to 0.6, or 0.05 to 0.4.
- the ET adsorbent of the present invention may be used as it is or after being appropriately processed.
- a column filled with the ET adsorbent of the present invention can be used.
- the means for bringing the ET adsorbent of the present invention into contact with the ET-containing liquid is not particularly limited.
- the means for bringing the ET adsorbent of the present invention into contact with the ET-containing liquid can be appropriately selected according to various conditions such as the aspect of the ET adsorbent of the present invention and the aspect of the ET-containing liquid.
- the contact between the ET adsorbent of the present invention and the ET-containing liquid can be performed with reference to a known means for treating a liquid sample with a solid carrier, for example.
- the contact between the ET adsorbent of the present invention and the ET-containing liquid can be performed, for example, by a batch method.
- the “batch method” is a technique in which the ET adsorbent of the present invention and the ET-containing liquid are brought into contact with each other by mixing the ET adsorbent of the present invention and the ET-containing liquid in an appropriate container. That is, for example, the ET adsorbent of the present invention can be brought into contact with the ET-containing liquid by introducing the ET adsorbent of the present invention into the ET-containing liquid.
- the batch method may be carried out by standing or may be carried out with stirring or shaking. After the ET is adsorbed on the ET adsorbent of the present invention, the ET adsorbent of the present invention is removed from the mixture to obtain a liquid from which ET has been removed.
- the contact between the ET adsorbent of the present invention and the ET-containing liquid can be performed, for example, by a fluid separation method.
- the “fluid separation method” is a technique of bringing the ET adsorbent of the present invention into contact with the ET-containing liquid by passing the ET-containing liquid through the ET adsorbent of the present invention. That is, for example, when the ET adsorbent of the present invention is packed in a column and used, the ET adsorbent of the present invention can be obtained by passing the ET-containing liquid through the column packed with the ET adsorbent of the present invention. An ET-containing liquid can be contacted (column method).
- the ET adsorbent of the present invention when configured as a filter, the ET adsorbent of the present invention and the ET-containing liquid can be contacted by passing the ET-containing liquid through the filter.
- the fluid separation method include chromatography such as liquid chromatography, membrane chromatography, and monolith chromatography; filtration using a hollow fiber membrane, tubular membrane, flat membrane, membrane filter, filter paper, etc .; solid phase extraction; Examples of the method include purification of a sample such as a body fluid using an adsorption column.
- the processing speed that is, the contact time between the ET adsorbent of the present invention and the ET-containing liquid in the batch method and the flow rate (liquid passing speed) of the ET-containing liquid in the fluid separation method is ET.
- the processing speed can be appropriately set according to various conditions such as the ET content in the ET-containing liquid and the content and type of the target substance.
- the contact time may be, for example, 5 minutes to 120 hours, 30 minutes to 24 hours, 1 to 12 hours, or 2 to 4 hours.
- the liquid passing speed may be set equally.
- the treatment temperature is not particularly limited as long as ET is removed.
- the treatment temperature can be appropriately set according to various conditions such as the type of the target substance.
- the treatment temperature may be, for example, 5-80 ° C, 15-65 ° C, or 25-50 ° C.
- ET in the ET-containing liquid is removed by the ET removal method of the present invention.
- the ET content in the liquid after treatment is lower than that before treatment (before contact with the ET adsorbent of the present invention). If it is, it will not be restrict
- ET is removed means, for example, that the ET content in the treated liquid is 0.5 EU / mL or less, 0.2 EU / mL or less, 0.1 EU / mL or less, 0.05 EU / mL It may be less than mL, less than 0.02 EU / mL, less than 0.01 EU / mL, less than 0.005 EU / mL, less than 0.002 EU / mL, or less than 0.001 EU / mL. In the ET removal method of the present invention, it is particularly preferable that ET can be removed from a diluted ET-containing liquid.
- the ET content in the liquid after treatment as exemplified above
- the ET may be removed to an amount, eg, 0.1 EU / mL or less.
- the target substance is left in the liquid after the treatment.
- the degree of remaining of the target substance is not particularly limited as long as the target substance remains in a desired amount in the treated liquid. It is preferable that the target substance is not substantially removed. “The target substance is not substantially removed” means, for example, that the content of the target substance in the liquid after the treatment is 90% or more, 95% or more, 97% or more, or 99%, compared with that before the treatment. It may be maintained above.
- the removal of ET can be confirmed by quantifying ET in the treated liquid.
- a quantitative method of ET there is a Limulus test using Limulus reagent.
- the Limulus test can be performed by a conventional method.
- the Limulus test can be performed, for example, by a colorimetric method, a turbidimetric method, or a gelation method.
- aminated cellulose nanofibers As aminated cellulose nanofibers, polyethyleneimine (PEI) -immobilized cellulose nanofibers and ethylenediamine (EDA) -immobilized cellulose nanofibers were synthesized by the following procedure.
- PEI polyethyleneimine
- EDA ethylenediamine
- the reaction product was subjected to suction filtration on a filter cloth (Toray silk, cocoon mesh size ⁇ 20 ⁇ m, manufactured by Sakai Toray Co., Ltd.) to obtain epoxy-activated cellulose nanofibers as a solid content (filtration residue).
- a filter cloth Toray silk, cocoon mesh size ⁇ 20 ⁇ m, manufactured by Sakai Toray Co., Ltd.
- epoxy-activated cellulose nanofibers as a solid content (filtration residue).
- 30% (v / v) PEI aqueous solution mixture of 30 mL PEI (linear; number average molecular weight approximately 423; manufactured by Aldrich) and 70 mL water
- Cell-PEI PEI-immobilized cellulose nanofiber
- LPS ET-immobilized cellulose nanofiber
- aminated cellulose nanofibers thus obtained were partly collected for AEC measurement, and the remainder was dispersed in methanol and stored refrigerated until use.
- AEC measurement The amount of amino groups introduced into the aminated cellulose nanofibers was determined by measuring the anion exchange capacity (AEC) of the synthesized aminated cellulose nanofibers. That is, the amount of primary amine (—NH 2 ) that is a terminal group can be determined by AEC measurement. AEC was measured by a back titration method. The procedure is shown below.
- Each aminated cellulose nanofiber was dried under reduced pressure for 24 hours or more, and was precisely weighed and placed in an Erlenmeyer flask. 30 ml of 0.1 mol / l hydrochloric acid with a known factor was added and shaken with a shaker for 2 hours (200 rpm, 25 ° C.). Filtration was performed using filter paper, and 20 ml of the filtrate was diluted to 100 ml with distilled water. 10 ml of the diluted solution was placed in another Erlenmeyer flask and titrated with 0.05 mol / l sodium hydroxide of known factor using phenolphthalein as an indicator. The AEC of the aminated cellulose nanofiber was calculated by the following formula (I).
- AEC of Cell-PEI was 0.64 (meq / dry-g), and the AEC of Cell-EDA was 0.83 (meq / dry-g).
- AEC (meq / dry-g) (0.1 ⁇ f HCl ⁇ 30 ⁇ 0.05 ⁇ f NaOH ⁇ V ⁇ 30/20 ⁇ 100/10) ⁇ W ⁇ ⁇ ⁇ (I)
- f HCl Factor of used hydrochloric acid
- f NaOH Factor of used aqueous sodium hydroxide solution
- V Titration (ml)
- W Dry weight of particles (dry-g)
- one test tube of Endspecy ES-24M (a set including 24 test tubes containing lyophilized horseshoe crab blood cell extract, manufactured by Kasei Chemical Industry Co., Ltd.), a commercially available Limulus reagent. Then, 0.2 ml of the attached buffer solution was added to the Limulus reagent to dissolve the contents.
- the filtrate was diluted 100 times with Otsuka Minamata (LPS-free distilled water; manufactured by Otsuka Pharmaceutical Co., Ltd.).
- the diluted solution was added to each test tube containing the Limulus reagent in an amount of 0.2 ml and mixed well by vortexing.
- a test tube was installed in EG-Leader SV-12 (manufactured by Seikagaku Corporation), and the residual ET concentration was determined by a colorimetric time method.
- the LPS adsorption capacity of Cell-PEI is higher than poly ( ⁇ -lysine) -cellulose beads (1.34 times), and the LPS dissociation constant of Cell-PEI is lower than poly ( ⁇ -lysine) -cellulose beads (0.66 times) )
- a larger LPS adsorption capacity of the adsorbent is preferred, and a smaller LPS dissociation constant of the adsorbent is preferred because LPS can be removed from a dilute LPS solution. Therefore, it was shown that Cell-PEI has a better ET adsorption capacity than poly ( ⁇ -lysine) -cellulose beads.
- BSA Albumin
- Cell-EDA was shown to have a higher selective ET adsorption capacity than poly ( ⁇ -lysine) -cellulose beads.
- the ET adsorbent of the present invention exhibits high selective ET adsorption ability in the presence of a negatively charged substance such as an acidic protein.
- Non-patent Document 2 polyethyleneimine-immobilized regenerated cellulose fiber
- ET an unknown component of polyethyleneimine-immobilized regenerated cellulose fiber (which may be derived from the component used for spinning the regenerated fiber)
- ET it has become clear that there are difficulties in putting it into practical use as an adsorbent.
- the ET adsorbent of the present invention does not elute such eluate and can be suitably used as an ET adsorbent. That is, the ET adsorbent of the present invention is an extremely excellent ET adsorbent as compared with polyethyleneimine-immobilized regenerated cellulose fibers.
- a sample solution containing a sample solution containing a phosphorylated polysaccharide was used under the conditions shown in Table 1. Then, an ET adsorption test by a batch method was performed to evaluate the ET (LPS) adsorption ability. In the batch method, 0.2 wet-g was used as the adsorbent, and 2 mL was used as the sample solution. The results are shown in the sample name “phosphorylated polysaccharide aqueous solution” in Table 1. All the aminated cellulose nanofibers showed high ET adsorption ability in the presence of phosphorylated polysaccharide.
- the ET adsorbent of the present invention exhibits high ET adsorption ability or high selective ET adsorption ability even for a highly viscous sample such as a fibrous viscous polymer solution.
- an ET adsorbent having a high ET adsorbing ability can be provided.
- ET can be selectively removed from a liquid containing a substance exhibiting ET and negative charge.
Landscapes
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Veterinary Medicine (AREA)
- Public Health (AREA)
- Animal Behavior & Ethology (AREA)
- Epidemiology (AREA)
- Pharmacology & Pharmacy (AREA)
- Medicinal Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Nanotechnology (AREA)
- Materials Engineering (AREA)
- Crystallography & Structural Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Polysaccharides And Polysaccharide Derivatives (AREA)
- Treatment Of Liquids With Adsorbents In General (AREA)
- Water Treatment By Sorption (AREA)
Abstract
Description
[1]
アミノ基を有するセルロースナノファイバーを備える、エンドトキシン吸着剤。
[2]
前記セルロースナノファイバーにおけるアミノ基の量が、0.05~3.0meq/dry-gである、前記エンドトキシン吸着剤。
[3]
前記セルロースナノファイバーが、1nm~1000nmの平均繊維径を有する、前記エンドトキシン吸着剤。
[4]
セルロースナノファイバーにアミノ基を導入する工程を含む、前記エンドトキシン吸着剤を製造する方法。
[5]
前記エンドトキシン吸着剤と、エンドトキシンを含有する液体とを接触させることを含む、エンドトキシンを除去する方法。
[6]
前記エンドトキシン吸着剤と、エンドトキシンを含有する液体とを接触させることを含む、エンドトキシンの除去された液体の製造方法。
[7]
前記エンドトキシン吸着剤と、目的物質およびエンドトキシンを含有する液体とを接触させることを含む、エンドトキシンを除去する方法。
[8]
前記エンドトキシン吸着剤と、目的物質およびエンドトキシンを含有する液体とを接触させることを含む、エンドトキシンの除去された目的物質を含有する液体の製造方法。
[9]
前記目的物質が、マイナスチャージを示す物質である、前記方法。
[10]
前記目的物質が、等電点が4.0~10.5のタンパク質である、前記方法。
本発明のエンドトキシン吸着剤(ET吸着剤)は、アミノ基を有するセルロースナノファイバーを備える、ET吸着剤である。当該アミノ基を有するセルロースナノファイバーを、「本発明で用いられるセルロースナノファイバー」ともいう。ETを、「LPS」ともいう。
本発明のET吸着剤を利用して、ETを除去することができる。すなわち、本発明は、本発明のET吸着剤と、ETを含有する液体とを接触させることを含む、ETを除去する方法を提供する。同方法を「本発明のET除去方法」ともいう。「ETを含有する液体」を「ET含有液」ともいう。本発明のET除去方法により、ETの除去された液体が得られる。すなわち、本発明のET除去方法は、本発明のET吸着剤と、ETを含有する液体とを接触させることを含む、ETの除去された液体の製造方法であってもよい。
アミノ化セルロースナノファイバーとして、ポリエチレンイミン(PEI)固定化セルロースナノファイバーとエチレンジアミン(EDA)固定化セルロースナノファイバーを、以下の手順で合成した。
合成したアミノ化セルロースナノファイバーの陰イオン交換容量(Anion Exchange Capacity;AEC)を測定することにより、アミノ化セルロースナノファイバーのアミノ基導入量を決定した。すなわち、AEC測定により、末端基である第1級アミン(-NH2)の導入量を決定できる。AECは、逆滴定法により測定した。手順を以下に示す。
AEC (meq/dry-g) = (0.1×fHCl×30-0.05×fNaOH×V×30/20×100/10)÷W ・・・(I)
fHCl :使用した塩酸のファクター
fNaOH :使用した水酸化ナトリウム水溶液のファクター
V :滴定量 (ml)
W :粒子の乾燥重量 (dry-g)
合成したアミノ化セルロースナノファイバーのET吸着能を測定し、既知のET吸着剤のET吸着能と比較した。既知のET吸着剤としてはcellulose-polylysine(J. LIQ. CHROM. & REL. TECHNOL., 2002, 25(4): 601-614.)を用いた。cellulose-polylysineは、ポリ(ε-リジン)を固定化したセルロース粒子(AEC=0.45 meq/g)である。以下、cellulose-polylysineを「poly(ε-lysine)-cellulose beads」ともいう。
ET吸着能の評価はバッチ法により行った。手順を以下に示す。
各吸着剤(Cell-PEIおよびpoly(ε-lysine)-cellulose beads)について、種々のET濃度の試料溶液(1~10000 EU/mL, pH 7.0, μ= 0.05)を用いてバッチ法によるET吸着試験を行い、吸着剤のET吸着等温線を作製した。バッチ法において、吸着剤は0.1 wet-g、試料溶液は4 mLを使用した。同吸着等温線よりScatchard plotを算出した。結果を図1に示す。同Scatchard plotより得られた直線式より、吸着剤とETとの見かけ上の解離定数および吸着容量を算出した。
見かけ上のエンドトキシン解離定数= 1/|a|×1012
エンドトキシン吸着容量 (μg/wet-g of adsorbent) = -(b/a)
各吸着剤(Cell-EDAおよびpoly(ε-lysine)-cellulose beads)について、アルブミン(BSA)を含有する種々のイオン強度の試料溶液(アルブミン(BSA) 500 μg/mL, LPS (E. Coli UKT-B) 25 EU/mL, pH 7.0)を用いてバッチ法によるET吸着試験を行い、選択的ET(LPS)吸着能を評価した。バッチ法において、吸着剤は0.2 wet-g、試料溶液は2 mLを使用し、温度は25℃、反応時間(撹拌時間)は2時間とした。アルブミン(BSA)の定量は、UV-visスペクトル測定装置(GeneQuant 1300、GEヘルスケア・ジャパン株式会社製)にて試料溶液のUV測定を行い、BSAのピーク(280 nm)における吸光度に基づいて行った。結果を図2に示す。Cell-EDAは、いずれのイオン強度(μ)においても、タンパク質を吸着することなく、LPSに高い選択性を示し、特にイオン強度μ=0.05~0.4において高い効果(LPS吸着率99%,LPS残存濃度<0.1 EU/mL)が得られた。一方、poly(ε-lysine)-cellulose beadsは、イオン強度μ=0.05~0.4において高いLPS吸着能(LPS吸着率99%)を示したが、LPS選択性は乏しかった。これは、poly(ε-lysine)-cellulose beadsにおいては、BSAが細孔に吸着されるためであると考えられる。よって、Cell-EDAはpoly(ε-lysine)-cellulose beadsよりも高い選択的ET吸着能を有することが示された。
<3-4-1>リン酸化多糖溶液からのET(LPS)吸着能の評価
Cell-EDAについて、リン酸化多糖を含有する試料溶液(リン酸化多糖溶液10mlと0.02Mリン酸Buffer 10ml(pH6.0, μ=0.2)を混合しリン酸化多糖濃度1.55%に調整, 標準LPS (E. Coli UKT-B) 換算で25 EU/mLのLPSを含有)を用いて種々の反応時間(撹拌時間)でバッチ法によるET吸着試験を行い、ET(LPS)吸着能を評価した。バッチ法において、吸着剤は0.2 wet-g、試料溶液は2 mLを使用し、温度は30℃とした。結果を表2に示す。いずれの反応時間(撹拌時間)においても、Cell-EDAは、高いLPS吸着率を示した。
各吸着剤(Cell-PEIおよびpoly(ε-lysine)-cellulose beads)について、表1に記載の条件で、コラーゲンを含有する試料溶液(コラーゲンペプチド粉末1.5gを40mL Buffer(pH7.0, μ=0.2)で溶解, LPS (E. Coli UKT-B Lot.TFJ5099) 26 EU/mL)を用いてバッチ法によるET吸着試験を行い、選択的ET(LPS)吸着能を評価した。バッチ法において、吸着剤は0.2 wet-g、試料溶液は2 mLを使用した。結果を表1の試料名「コラーゲンペプチド溶液」に示す。いずれのアミノ化セルロースナノファイバーも、コラーゲンの共存下で高い選択的ET吸着能を示した。
各吸着剤(Cell-PEIおよびpoly(ε-lysine)-cellulose beads)について、表3に記載の条件で、ゼラチンまたは豚コラーゲンを含有する試料溶液を用いてバッチ法によるET吸着試験を行い、選択的ET(LPS)吸着能を評価した。結果を表3に示す。アミノ化セルロースナノファイバー(Cell-PEI)は、ゼラチンまたは豚コラーゲンの共存下で高い選択的ET吸着能を示した。
Claims (10)
- アミノ基を有するセルロースナノファイバーを備える、エンドトキシン吸着剤。
- 前記セルロースナノファイバーにおけるアミノ基の量が、0.05~3.0meq/dry-gである、請求項1に記載のエンドトキシン吸着剤。
- 前記セルロースナノファイバーが、1nm~1000nmの平均繊維径を有する、請求項1または2に記載のエンドトキシン吸着剤。
- セルロースナノファイバーにアミノ基を導入する工程を含む、請求項1~3のいずれか1項に記載のエンドトキシン吸着剤を製造する方法。
- 請求項1~3のいずれか1項に記載のエンドトキシン吸着剤と、エンドトキシンを含有する液体とを接触させることを含む、エンドトキシンを除去する方法。
- 請求項1~3のいずれか1項に記載のエンドトキシン吸着剤と、エンドトキシンを含有する液体とを接触させることを含む、エンドトキシンの除去された液体の製造方法。
- 請求項1~3のいずれか1項に記載のエンドトキシン吸着剤と、目的物質およびエンドトキシンを含有する液体とを接触させることを含む、エンドトキシンを除去する方法。
- 請求項1~3のいずれか1項に記載のエンドトキシン吸着剤と、目的物質およびエンドトキシンを含有する液体とを接触させることを含む、エンドトキシンの除去された目的物質を含有する液体の製造方法。
- 前記目的物質が、マイナスチャージを示す物質である、請求項7または8に記載の方法。
- 前記目的物質が、等電点が4.0~10.5のタンパク質である、請求項7~9のいずれか1項に記載の方法。
Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US15/748,542 US10987651B2 (en) | 2015-07-30 | 2016-07-29 | Endotoxin adsorbent |
JP2017530944A JP6467652B2 (ja) | 2015-07-30 | 2016-07-29 | エンドトキシン吸着剤 |
KR1020187005910A KR102624853B1 (ko) | 2015-07-30 | 2016-07-29 | 내독소 흡착제 |
EP16830627.2A EP3329989B1 (en) | 2015-07-30 | 2016-07-29 | Use of endotoxin adsorbent |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2015151271 | 2015-07-30 | ||
JP2015-151271 | 2015-07-30 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2017018524A1 true WO2017018524A1 (ja) | 2017-02-02 |
Family
ID=57884465
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/JP2016/072347 WO2017018524A1 (ja) | 2015-07-30 | 2016-07-29 | エンドトキシン吸着剤 |
Country Status (5)
Country | Link |
---|---|
US (1) | US10987651B2 (ja) |
EP (1) | EP3329989B1 (ja) |
JP (1) | JP6467652B2 (ja) |
KR (1) | KR102624853B1 (ja) |
WO (1) | WO2017018524A1 (ja) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2019136669A (ja) * | 2018-02-13 | 2019-08-22 | 真庭バイオケミカル株式会社 | 吸着材及びその製造方法 |
JP2019527617A (ja) * | 2016-07-14 | 2019-10-03 | ピュリディファイ リミテッド | ポリマーナノファイバーを含む官能化クロマトグラフィー媒体及びそれを製造する方法 |
JP2020152702A (ja) * | 2019-03-22 | 2020-09-24 | ナガセケムテックス株式会社 | 核酸吸着材 |
US11141710B2 (en) | 2017-01-25 | 2021-10-12 | Nagase Chemtex Corporation | Endotoxin adsorbent |
JP7462901B2 (ja) | 2020-05-11 | 2024-04-08 | 国立大学法人 熊本大学 | エンドトキシン吸着剤及びその製造方法 |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB201800448D0 (en) | 2018-01-11 | 2018-02-28 | Puridify Ltd | Chromatography media and methods for producing them |
CA3148773A1 (en) * | 2019-08-01 | 2021-02-04 | Sigyn Therapeutics, Inc. | Devices, systems and methods for the broad-spectrum reduction of pro-inflammatory cytokines in blood |
GB202202713D0 (en) * | 2022-02-28 | 2022-04-13 | Cytiva Bioprocess R & D Ab | Method of preparing a functionalised chromatography medium |
KR20240039511A (ko) | 2022-09-19 | 2024-03-26 | (주)에스에스메디컬 | 고분자의 이온 반응을 이용한 소듐 알지네이트의 내독소 제거 방법 |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS59112888A (ja) * | 1982-12-17 | 1984-06-29 | Toray Ind Inc | 水溶液中のパイロジエンの除去方法 |
JP2002263486A (ja) * | 2001-03-14 | 2002-09-17 | Chisso Corp | エンドトキシン吸着体、及びそれを用いたエンドトキシンの除去方法 |
JP2007145743A (ja) * | 2005-11-25 | 2007-06-14 | Chisso Corp | エンドトキシン吸着体、およびそれを用いたエンドトキシンの除去方法 |
JP2015507181A (ja) * | 2011-12-22 | 2015-03-05 | ユー ピー エム キュンメネ コーポレーション | 分離方法における、フィブリルセルロースを含む固定相の使用 |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4505950B2 (ja) * | 2000-06-06 | 2010-07-21 | 東レ株式会社 | 吸着材および体外循環用カラム |
US6838005B2 (en) * | 2001-06-22 | 2005-01-04 | Frederick Tepper | Nanosize electropositive fibrous adsorbent |
WO2015052460A1 (en) * | 2013-10-09 | 2015-04-16 | Ucl Business Plc | Chromatography medium |
-
2016
- 2016-07-29 JP JP2017530944A patent/JP6467652B2/ja active Active
- 2016-07-29 KR KR1020187005910A patent/KR102624853B1/ko active IP Right Grant
- 2016-07-29 EP EP16830627.2A patent/EP3329989B1/en active Active
- 2016-07-29 WO PCT/JP2016/072347 patent/WO2017018524A1/ja active Application Filing
- 2016-07-29 US US15/748,542 patent/US10987651B2/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS59112888A (ja) * | 1982-12-17 | 1984-06-29 | Toray Ind Inc | 水溶液中のパイロジエンの除去方法 |
JP2002263486A (ja) * | 2001-03-14 | 2002-09-17 | Chisso Corp | エンドトキシン吸着体、及びそれを用いたエンドトキシンの除去方法 |
JP2007145743A (ja) * | 2005-11-25 | 2007-06-14 | Chisso Corp | エンドトキシン吸着体、およびそれを用いたエンドトキシンの除去方法 |
JP2015507181A (ja) * | 2011-12-22 | 2015-03-05 | ユー ピー エム キュンメネ コーポレーション | 分離方法における、フィブリルセルロースを含む固定相の使用 |
Non-Patent Citations (1)
Title |
---|
MORIMOTO, S. ET AL.: "Preparations and Applications of Polyethyleneimine-Immobilized Cellulose Fibers for Endotoxin Removal", POLYMER JOURNAL, vol. 27, no. 8, 1995, pages 831 - 839, XP055349940, ISSN: 0032-3896 * |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2019527617A (ja) * | 2016-07-14 | 2019-10-03 | ピュリディファイ リミテッド | ポリマーナノファイバーを含む官能化クロマトグラフィー媒体及びそれを製造する方法 |
JP7055538B2 (ja) | 2016-07-14 | 2022-04-18 | ピュリディファイ リミテッド | ポリマーナノファイバーを含む官能化クロマトグラフィー媒体及びそれを製造する方法 |
US11141710B2 (en) | 2017-01-25 | 2021-10-12 | Nagase Chemtex Corporation | Endotoxin adsorbent |
JP2019136669A (ja) * | 2018-02-13 | 2019-08-22 | 真庭バイオケミカル株式会社 | 吸着材及びその製造方法 |
JP2020152702A (ja) * | 2019-03-22 | 2020-09-24 | ナガセケムテックス株式会社 | 核酸吸着材 |
JP7385095B2 (ja) | 2019-03-22 | 2023-11-22 | ナガセケムテックス株式会社 | 核酸吸着材 |
JP7462901B2 (ja) | 2020-05-11 | 2024-04-08 | 国立大学法人 熊本大学 | エンドトキシン吸着剤及びその製造方法 |
Also Published As
Publication number | Publication date |
---|---|
KR102624853B1 (ko) | 2024-01-12 |
JPWO2017018524A1 (ja) | 2018-07-05 |
US20180178192A1 (en) | 2018-06-28 |
US10987651B2 (en) | 2021-04-27 |
EP3329989A1 (en) | 2018-06-06 |
EP3329989A4 (en) | 2018-12-26 |
KR20180036750A (ko) | 2018-04-09 |
JP6467652B2 (ja) | 2019-02-13 |
EP3329989B1 (en) | 2022-08-31 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP6467652B2 (ja) | エンドトキシン吸着剤 | |
Ahmad et al. | Adsorption of heavy metal ions: role of chitosan and cellulose for water treatment | |
Gericke et al. | Functional cellulose beads: preparation, characterization, and applications | |
JP6424343B2 (ja) | エンドトキシン吸着剤 | |
US6699386B2 (en) | Endotoxin adsorbent, and a method of removing endotoxin by using the same | |
JP7080186B2 (ja) | エンドトキシン吸着剤 | |
DE102006055558A1 (de) | Endotoxinadsorber und Verfahren zur Entfernung von Endotoxin unter dessen Verwendung | |
US9352298B2 (en) | Method for producing polymer particles, and polymer particles | |
JP6159737B2 (ja) | 分離方法における、フィブリルセルロースを含む固定相の使用 | |
Ng et al. | Enhancement of C-phycocyanin purity using negative chromatography with chitosan-modified nanofiber membrane | |
US10155217B2 (en) | Endotoxin adsorbent | |
JP7462901B2 (ja) | エンドトキシン吸着剤及びその製造方法 | |
WO2011032126A1 (en) | Protein imprinting by means of alginate-based polymer microcapsules | |
Zhang et al. | Silica Gel Functionalized with Polyethylenimine as Advanced Sorbents for the Removal of Endotoxin from Gelatin | |
JP2020152702A (ja) | 核酸吸着材 | |
JP2024128845A (ja) | ペプチドグリカン吸着材 | |
Tan et al. | Cellulose and its application in biomolecules purification | |
JP2024093058A (ja) | エンドトキシン吸着材 | |
WO2023190628A1 (ja) | エンドトキシン吸着材 | |
TW593342B (en) | Method for reducing endotoxin contained in chitosan | |
Nurul Mujahidah | Immobilization of bovine serum albumin on chitosan/PVA film: Physical and mechanical properties investigation/Nurul Mujahidah Ahmad Khairuddin | |
Sikora et al. | Chitosan-based matrixes for recombinant protein purification from LPS | |
JP3401773B2 (ja) | エンドトキシンまたは核酸の除去剤 | |
Digel et al. | Usage of Carbonized Plant Wastes for Purification of Aqueous Solutions |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 16830627 Country of ref document: EP Kind code of ref document: A1 |
|
ENP | Entry into the national phase |
Ref document number: 2017530944 Country of ref document: JP Kind code of ref document: A |
|
WWE | Wipo information: entry into national phase |
Ref document number: 15748542 Country of ref document: US |
|
NENP | Non-entry into the national phase |
Ref country code: DE |
|
ENP | Entry into the national phase |
Ref document number: 20187005910 Country of ref document: KR Kind code of ref document: A |