CN106492396A - A kind of antibiotic bacterium dregs laccase enzyme solution - Google Patents
A kind of antibiotic bacterium dregs laccase enzyme solution Download PDFInfo
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- 230000003115 biocidal effect Effects 0.000 title claims abstract description 58
- 108010029541 Laccase Proteins 0.000 title claims abstract description 30
- 241000894006 Bacteria Species 0.000 title claims description 41
- 238000000034 method Methods 0.000 claims abstract description 27
- 108090000790 Enzymes Proteins 0.000 claims abstract description 26
- 102000004190 Enzymes Human genes 0.000 claims abstract description 26
- 239000002893 slag Substances 0.000 claims abstract description 15
- 239000000725 suspension Substances 0.000 claims description 30
- 239000003242 anti bacterial agent Substances 0.000 claims description 24
- 229940088710 antibiotic agent Drugs 0.000 claims description 24
- ULGZDMOVFRHVEP-RWJQBGPGSA-N Erythromycin Chemical compound O([C@@H]1[C@@H](C)C(=O)O[C@@H]([C@@]([C@H](O)[C@@H](C)C(=O)[C@H](C)C[C@@](C)(O)[C@H](O[C@H]2[C@@H]([C@H](C[C@@H](C)O2)N(C)C)O)[C@H]1C)(C)O)CC)[C@H]1C[C@@](C)(OC)[C@@H](O)[C@H](C)O1 ULGZDMOVFRHVEP-RWJQBGPGSA-N 0.000 claims description 20
- 230000000694 effects Effects 0.000 claims description 11
- 230000007071 enzymatic hydrolysis Effects 0.000 claims description 10
- 238000006047 enzymatic hydrolysis reaction Methods 0.000 claims description 10
- 229960003276 erythromycin Drugs 0.000 claims description 10
- 230000007613 environmental effect Effects 0.000 abstract description 3
- 230000002255 enzymatic effect Effects 0.000 abstract description 2
- 238000006243 chemical reaction Methods 0.000 description 5
- 230000029087 digestion Effects 0.000 description 5
- 238000002360 preparation method Methods 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 239000003674 animal food additive Substances 0.000 description 3
- 239000003337 fertilizer Substances 0.000 description 3
- 230000005764 inhibitory process Effects 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- ACTOXUHEUCPTEW-BWHGAVFKSA-N 2-[(4r,5s,6s,7r,9r,10r,11e,13e,16r)-6-[(2s,3r,4r,5s,6r)-5-[(2s,4r,5s,6s)-4,5-dihydroxy-4,6-dimethyloxan-2-yl]oxy-4-(dimethylamino)-3-hydroxy-6-methyloxan-2-yl]oxy-10-[(2s,5s,6r)-5-(dimethylamino)-6-methyloxan-2-yl]oxy-4-hydroxy-5-methoxy-9,16-dimethyl-2-o Chemical compound O([C@H]1/C=C/C=C/C[C@@H](C)OC(=O)C[C@@H](O)[C@@H]([C@H]([C@@H](CC=O)C[C@H]1C)O[C@H]1[C@@H]([C@H]([C@H](O[C@@H]2O[C@@H](C)[C@H](O)[C@](C)(O)C2)[C@@H](C)O1)N(C)C)O)OC)[C@@H]1CC[C@H](N(C)C)[C@@H](C)O1 ACTOXUHEUCPTEW-BWHGAVFKSA-N 0.000 description 2
- 241000233866 Fungi Species 0.000 description 2
- 239000004187 Spiramycin Substances 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 230000001580 bacterial effect Effects 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 238000009792 diffusion process Methods 0.000 description 2
- 238000000855 fermentation Methods 0.000 description 2
- 230000004151 fermentation Effects 0.000 description 2
- 239000002920 hazardous waste Substances 0.000 description 2
- 239000003120 macrolide antibiotic agent Substances 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 229960001294 spiramycin Drugs 0.000 description 2
- 229930191512 spiramycin Natural products 0.000 description 2
- 235000019372 spiramycin Nutrition 0.000 description 2
- 239000000758 substrate Substances 0.000 description 2
- 229920001817 Agar Polymers 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 239000008272 agar Substances 0.000 description 1
- 238000013019 agitation Methods 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 239000007857 degradation product Substances 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000009795 derivation Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 230000002538 fungal effect Effects 0.000 description 1
- 239000003102 growth factor Substances 0.000 description 1
- 238000004128 high performance liquid chromatography Methods 0.000 description 1
- 230000002779 inactivation Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000010907 mechanical stirring Methods 0.000 description 1
- 230000007721 medicinal effect Effects 0.000 description 1
- 239000002207 metabolite Substances 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 230000035515 penetration Effects 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000009270 solid waste treatment Methods 0.000 description 1
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Abstract
本发明提供了一种利用漆酶处理抗生素菌渣的方法,采用漆酶对抗生素菌渣进行处理,其中:所述抗生素菌渣为硫红霉素菌渣;采用漆酶对硫红霉素菌渣进行处理,在温度为40‑55℃,pH为6‑7,酶浓度为0.005‑0.02g/mL条件下处理4‑6h,硫红霉素菌渣的效价降低90%以上。本发明简便可行,处理成本低,不产生二次污染,节能环保,能够去除抗生素菌渣中大部分残留的抗生素,便于抗生素菌渣的后续处理,同时为酶处理抗生素菌渣技术提供了一定的数据依据。The invention provides a method for treating antibiotic scum by using laccase, wherein the antibiotic slag is treated with laccase, wherein: the antibiotic slag is thioerythromycin slag; The slag was treated at a temperature of 40-55°C, a pH of 6-7, and an enzyme concentration of 0.005-0.02g/mL for 4-6h, and the potency of the thioerythromycin residue was reduced by more than 90%. The invention is simple and feasible, has low processing cost, no secondary pollution, energy saving and environmental protection, can remove most of the antibiotic residues in antibiotic residues, facilitates the subsequent treatment of antibiotic residues, and provides a certain method for enzymatic treatment of antibiotic residues. Data basis.
Description
技术领域technical field
本发明属于环保领域,具体涉及一种抗生素菌渣残留抗生素酶解方法,尤其涉及一种使用漆酶对抗生素菌渣残留抗生素酶解方法。The invention belongs to the field of environmental protection, and in particular relates to a method for enzymatic hydrolysis of residual antibiotic residues of antibiotic bacteria, in particular to a method for enzymatic hydrolysis of residual antibiotic residues of antibiotic bacteria by using laccase.
背景技术Background technique
我国是抗生素类药物生产大国。在抗生素的发酵生产中会产生大量的固体废物,即抗生素菌渣。抗生素菌渣的主要成分为:产生特定抗生素的微生物菌丝体、提取抗生素过程中加入的试剂、未被完全利用的培养基、培养基的降解物、发酵过程中产生的代谢物、未知生长因子以及少量残留的抗生素。抗生素菌渣在露天堆放过程中,一方面会造成对大气的污染,直接影响周围居住人群的生活;另一方面菌渣残留的抗生素会进入到土壤中并在土壤中迁移,从而增加微生物的耐药性,间接影响人类的健康。并且,在2008年,抗生素菌渣作为危险废物被列入《国家危险废物名录》。因此,寻找一种环保经济的方法来处理抗生素菌渣是十分必要的。my country is a major producer of antibiotics. A large amount of solid waste, namely antibiotic residue, will be produced in the fermentation production of antibiotics. The main components of antibiotic residues are: microbial mycelia that produce specific antibiotics, reagents added during the extraction of antibiotics, incompletely utilized medium, degradation products of the medium, metabolites produced during fermentation, and unknown growth factors and small amounts of residual antibiotics. During the open-air stacking of antibiotic residues, on the one hand, it will cause air pollution and directly affect the lives of the surrounding residents; Medicinal properties indirectly affect human health. And, in 2008, antibiotic residues were included in the "National List of Hazardous Wastes" as hazardous wastes. Therefore, it is very necessary to find an environmentally friendly and economical method to deal with antibiotic residues.
CN105457968A公开了一种抗生素菌渣的无害化处理方法,其将抗生素菌渣在pH为8~11、温度90~100℃的条件下灭活。本方法将菌渣灭活,将其中的抗生素降解失去活性,失活的菌渣菌丝体包含有微生物的细胞、助凝剂和剩余营养成分,即可用于有机肥料或饲料添加剂。但如果抗生素降解不完全,易造成抗生素在有机肥料或饲料添加剂中的残留,间接危害人体健康。CN105457968A discloses a method for harmless treatment of antibiotic residues, which inactivates antibiotic residues under conditions of pH 8-11 and temperature 90-100°C. The method deactivates the fungus residue, degrades the antibiotics therein and loses its activity, and the inactivated fungus residue mycelium contains microbial cells, coagulation aids and remaining nutrients, and can be used as an organic fertilizer or a feed additive. However, if the degradation of antibiotics is not complete, it is easy to cause antibiotics to remain in organic fertilizers or feed additives, and indirectly endanger human health.
CN101380509A公开了一种大环内酯类抗生素菌渣无害化处理方法,属固体废弃物处理技术领域。该方法采用逆流机械搅拌有效破碎菌丝团,然后利用螺旋霉素无害化处理菌剂对大环内酯类抗生素菌渣进行无害化处理,将该处理过的抗生素菌渣作为植物肥料添加剂。但如果螺旋霉素无害化处理菌剂如果添加不当,易造成抗生素类的二次污染,且机械搅拌有一定的成本损耗。CN101380509A discloses a method for harmless treatment of macrolide antibiotic bacteria residue, which belongs to the technical field of solid waste treatment. The method adopts countercurrent mechanical agitation to effectively break the mycelium mass, and then uses spiramycin harmless treatment bacteria agent to carry out harmless treatment on the macrolide antibiotic bacteria residue, and the treated antibiotic bacteria residue is used as a plant fertilizer additive . However, if the spiramycin harmless treatment bacteria agent is added improperly, it is easy to cause secondary pollution of antibiotics, and mechanical stirring has a certain cost loss.
因此,希望提出一种能够快速、经济、有效的方法去除抗生素菌渣中残留抗生素。Therefore, it is hoped to propose a fast, economical and effective method for removing residual antibiotics in antibiotic residues.
发明内容Contents of the invention
本发明的目的主要在于提出一种抗生素菌渣处理的新方法,采用漆酶酶对抗生素菌渣进行处理,降低了抗生素菌渣中残留的抗生素。用于解决抗生素菌渣难处理、成本高、易产生二次污染、处理周期长、操作复杂等技术难题。The purpose of the present invention is mainly to propose a new method for treating antibiotic scum, which uses laccase to treat antibiotic slag and reduces the residual antibiotics in antibiotic slag. It is used to solve technical problems such as difficult treatment of antibiotic bacteria residue, high cost, easy secondary pollution, long treatment cycle and complicated operation.
本发明提供一种抗生素菌渣漆酶酶解方法,包括以下步骤:The invention provides a method for laccase enzymolysis of antibiotic bacteria residue, comprising the following steps:
a、配制浓度为0.001-0.005g/mL的红霉素标准样品;a. Prepare a standard sample of erythromycin with a concentration of 0.001-0.005g/mL;
b、配制浓度为0.01-0.04g/mL的抗生素菌渣悬浊液,调节pH为6-7;b. Prepare a suspension of antibiotic bacteria residue with a concentration of 0.01-0.04g/mL, and adjust the pH to 6-7;
c、在步骤b所述的菌渣悬浊液中加漆酶悬浊液,在温度为40-55℃,时间为4-6h条件下对抗生素菌渣中残留的抗生素进行消解;c. Add laccase suspension to the bacterial residue suspension described in step b, and digest the remaining antibiotics in the antibiotic bacterial residue at a temperature of 40-55° C. and a time of 4-6 hours;
优选的,步骤a中所述的红霉素标准样品的效价为920-4600U/mL。Preferably, the titer of the erythromycin standard sample described in step a is 920-4600 U/mL.
所述的抗生素菌渣选用硫红霉素菌渣,其来源不作特殊要求。Thierythromycin bacteria residue is selected as the antibiotic residue, and there is no special requirement for its source.
优选的,步骤b中所述菌渣悬浊液的原始效价为73.4-293.7U/mL。Preferably, the original potency of the suspension of fungal residues in step b is 73.4-293.7 U/mL.
优选的,步骤c中漆酶悬浊液的酶浓度为0.005-0.02g/mL。Preferably, the enzyme concentration of the laccase suspension in step c is 0.005-0.02 g/mL.
优选的,步骤c中的漆酶,酶活为35-140U/mL。Preferably, the laccase in step c has an enzyme activity of 35-140 U/mL.
步骤c中漆酶悬浊液与菌渣悬浊液的比例1:1。In step c, the ratio of the laccase suspension to the bacteria residue suspension is 1:1.
其中,抗生素在琼脂平板培养基中具有扩散渗透作用,根据扩散定律的推导,抗生素总量的对数值与抑菌圈直径的平方成线性关系,比较抗生素标准品与检品的抑菌圈大小,可计算出检品抗生素的效价。本发明中,利用已知效价的红霉素标准品与未知效价的硫红霉素检品的抑菌圈进行比较,则可计算出硫红霉素菌渣的效价。Among them, antibiotics have a diffusion and penetration effect in the agar plate medium. According to the derivation of the law of diffusion, the logarithmic value of the total amount of antibiotics is in a linear relationship with the square of the diameter of the inhibition zone. Comparing the size of the inhibition zone of the standard antibiotic and the test product, The potency of the tested antibiotic can be calculated. In the present invention, the titer of thioerythromycin slag can be calculated by comparing the inhibition zone of erythromycin standard substance with known potency and unknown potency thierythromycin test product.
本发明与现有技术相比,具有以下显著优点:Compared with the prior art, the present invention has the following significant advantages:
本发明以硫红霉素菌渣为研究对象,采用漆酶对硫红霉素菌渣进行处理,克服了专一性酶处理专一性底物的瓶颈。一般而言,酶对所作用的底物有严格的选择性。一种酶仅能作用于一种物质,或一类分子结构相似的物质,促其进行一定的化学反应,产生一定的反应产物,这种选择性作用称为酶的专一性。通常酶只能催化一种化学反应或一类相似的反应。我们进行了大量的实验,寻找硫红霉素菌渣的处理方法,然而我们吃惊的发现,漆酶对硫红霉素菌渣中残留的抗生素具有优异的消解作用,可以使硫红霉素菌渣的效价降低90%以上。The invention takes the thioerythromycin slag as the research object, and uses laccase to treat the thioerythromycin slag, which overcomes the bottleneck of specific enzyme treatment of specific substrates. In general, enzymes have strict selectivity for the substrate they act on. An enzyme can only act on one substance, or a class of substances with similar molecular structures, to promote a certain chemical reaction and produce a certain reaction product. This selective action is called the specificity of the enzyme. Usually an enzyme can only catalyze one chemical reaction or a class of similar reactions. We have conducted a lot of experiments to find the treatment method of thioerythromycin residue, but we were surprised to find that laccase has an excellent digestion effect on the residual antibiotics in thioerythromycin residue, which can make thioerythromycin bacteria The potency of slag is reduced by more than 90%.
目前,国内外处理抗生素菌渣的方法主要是,对抗生素菌渣进行高温强碱灭活处理后作为饲料添加剂或者经过物理化学处理后作为有机肥料,但若化学制剂添加不当易造成二次污染,且若菌渣内残留的抗生素降解不完全易造成抗生素的残留,间接危害人体健康,同时高温强碱处理、物理处理等都有一定的能源损耗,处理成本较高。抗生素菌渣酶解方法是基于酶微量高效的特点对抗生素菌渣进行处理,不会产生二次污染,更环保,且操作简单,反应周期短,成本低,能够去除抗生素菌渣中大部分残留的抗生素,便于抗生素菌渣的后续处理,同时提供一种酶处理抗生素菌渣的新方法。At present, the domestic and foreign methods of treating antibiotic bacteria residues are mainly to use high-temperature and strong alkali inactivation treatment of antibiotic bacteria residues as feed additives or as organic fertilizers after physical and chemical treatment, but if chemical preparations are added improperly, secondary pollution will easily occur. Moreover, if the residual antibiotics in the bacteria residues are not degraded completely, it is easy to cause antibiotic residues, which indirectly endangers human health. At the same time, high temperature and strong alkali treatment, physical treatment, etc. have certain energy losses, and the treatment cost is relatively high. The enzymatic hydrolysis method of antibiotic bacteria residue is based on the characteristics of small amount and high efficiency of enzymes to treat antibiotic residues, which will not cause secondary pollution, is more environmentally friendly, and is simple to operate, short reaction cycle, low cost, and can remove most of the residues of antibiotic bacteria residues The antibiotics are convenient for the subsequent treatment of antibiotic residues, and at the same time, a new method for enzymatic treatment of antibiotic residues is provided.
具体实施方式detailed description
为更清楚的说明本发明的技术特点,下面将通过具体实施方式对本发明进行详细阐述。In order to illustrate the technical characteristics of the present invention more clearly, the present invention will be described in detail below through specific embodiments.
本发明的抗生素菌渣残留抗生素漆酶酶解技术的研究,采用非专一性酶对抗生素菌渣进行处理,包括以下步骤:The research on the antibiotic laccase enzymatic hydrolysis technology of antibiotic slag residue of the present invention adopts non-specific enzyme to treat the antibiotic slag, comprising the following steps:
a、配制浓度为0.001-0.005g/mL的红霉素标准样品;a. Prepare a standard sample of erythromycin with a concentration of 0.001-0.005g/mL;
b、配制浓度为0.01-0.04g/mL的抗生素菌渣悬浊液,调节pH为6-7;b. Prepare a suspension of antibiotic bacteria residue with a concentration of 0.01-0.04g/mL, and adjust the pH to 6-7;
c、在该菌渣悬浊液中加漆酶悬浊液,在温度为40-55℃,时间为4-6h条件下对抗生素菌渣中残留的抗生素进行消解。c. Add laccase suspension to the bacteria residue suspension, and digest the residual antibiotics in the antibiotic bacteria residue at a temperature of 40-55° C. for 4-6 hours.
其中,所述的抗生素菌渣选用硫红霉素菌渣,原始效价为73.4-293.7U/mL;Wherein, the antibiotic residue is selected from thioerythromycin residue, and the original potency is 73.4-293.7U/mL;
其中,所述的漆酶悬浊液的酶浓度为0.005-0.02g/mL,酶活为35-140U/mLWherein, the enzyme concentration of the laccase suspension is 0.005-0.02g/mL, and the enzyme activity is 35-140U/mL
抗生素菌渣的效价、标准品的效价用管碟法测定;酶活采用高效液相色谱法测定。The potency of antibiotic bacteria residue and the potency of standard products were determined by tube and plate method; the enzyme activity was determined by high performance liquid chromatography.
实施例1Example 1
配制浓度为0.001g/mL的红霉素标准样品,其效价为920U/mL;Prepare a standard sample of erythromycin with a concentration of 0.001g/mL, and its potency is 920U/mL;
配制浓度为0.01g/mL的硫红霉素菌渣悬浊液,其原始效价为73.4U/mL,调节pH为6;The preparation concentration is 0.01g/mL suspension of thiorubicin bacteria residue, its original potency is 73.4U/mL, and the pH is adjusted to be 6;
在该硫红霉素菌渣悬浊液中加漆酶悬浊液,酶浓度为0.015g/mL,酶活为105U/mL;在温度为50℃,时间为4h条件下对抗生素菌渣中残留的抗生素进行消解,消解后,硫红霉素菌渣的效价为3.67U/mL,硫红霉素菌渣的效价降低95%。Add laccase suspension to the thioerythromycin residue suspension, the enzyme concentration is 0.015g/mL, and the enzyme activity is 105U/mL; Residual antibiotics were digested. After digestion, the titer of thioerythromycin bacteria residue was 3.67U/mL, and the titer of thioerythromycin bacteria residue was reduced by 95%.
实施例2Example 2
配制浓度为0.003g/mL的红霉素标准样品,其效价为2760U/mL;Prepare a standard sample of erythromycin with a concentration of 0.003g/mL, and its potency is 2760U/mL;
配制浓度为0.02g/mL的硫红霉素菌渣悬浊液,其原始效价为220.1U/mL,调节pH为7;The preparation concentration is 0.02g/mL suspension of thioerythromycin bacteria residue, its original potency is 220.1U/mL, and the pH is adjusted to be 7;
在该硫红霉素菌渣悬浊液中加漆酶悬浊液,酶浓度为0.007g/mL,酶活为49U/mL;在温度为45℃,时间为5h条件下对抗生素菌渣中残留的抗生素进行消解,消解后,硫红霉素菌渣的效价为15.4U/mL,硫红霉素菌渣的效价降低93%。Add laccase suspension to the thioerythromycin residue suspension, the enzyme concentration is 0.007g/mL, and the enzyme activity is 49U/mL; Residual antibiotics were digested. After digestion, the titer of thioerythromycin residue was 15.4U/mL, and the titer of thioerythromycin residue was reduced by 93%.
实施例3Example 3
配制浓度为0.005g/mL的红霉素标准样品,其效价为4600U/mL;Prepare a standard sample of erythromycin with a concentration of 0.005g/mL, and its potency is 4600U/mL;
配制浓度为0.03g/mL的硫红霉素菌渣悬浊液,其原始效价为78.15U/mL,调节pH为7;The preparation concentration is 0.03g/mL suspension of thioerythromycin bacteria residue, its original potency is 78.15U/mL, and the pH is adjusted to be 7;
在该硫红霉素菌渣悬浊液中加漆酶悬浊液,酶浓度为0.02g/mL,酶活为140U/mL;在温度为45℃,时间为4h条件下对抗生素菌渣中残留的抗生素进行消解,消解后,硫红霉素菌渣的效价为3.9U/mL,硫红霉素菌渣的效价降低95%。Add laccase suspension to the thioerythromycin residue suspension, the enzyme concentration is 0.02g/mL, and the enzyme activity is 140U/mL; Residual antibiotics were digested. After digestion, the titer of thioerythromycin residue was 3.9 U/mL, and the titer of thioerythromycin residue was reduced by 95%.
实施例4Example 4
配制浓度为0.004g/mL的红霉素标准样品,其效价为3680U/mL;Prepare a standard sample of erythromycin with a concentration of 0.004g/mL, and its potency is 3680U/mL;
配制浓度为0.04g/mL的硫红霉素菌渣悬浊液,其原始效价为293.7U/mL,调节pH为6.5;The preparation concentration is 0.04g/mL the suspension of thiorubicin bacteria residue, its original potency is 293.7U/mL, adjust pH to be 6.5;
在该硫红霉素菌渣悬浊液中加漆酶悬浊液,酶浓度为0.015g/mL,酶活为105U/mL;在温度为55℃,时间为6h条件下对抗生素菌渣中残留的抗生素进行消解,消解后,硫红霉素菌渣的效价为5.9U/mL,硫红霉素菌渣的效价降低98%。Add laccase suspension to the thioerythromycin residue suspension, the enzyme concentration is 0.015g/mL, and the enzyme activity is 105U/mL; Residual antibiotics were digested. After digestion, the titer of thioerythromycin bacteria residue was 5.9 U/mL, and the titer of thioerythromycin bacteria residue was reduced by 98%.
本发明一种抗生素菌渣酶解的方法,是利用酶处理抗生素的一种新的探索。本发明从数据出发,验证了利用酶处理抗生素菌渣方法的可行性,克服了专一性酶处理专一性菌渣的瓶颈,同时该方法操作简单,反应周期短,成本低,不产生二次污染,具有很好的环保效益。The invention discloses a method for enzymatic hydrolysis of antibiotic scum, which is a new exploration of using enzymes to treat antibiotics. Starting from the data, the present invention verifies the feasibility of using enzymes to treat antibiotic residues, and overcomes the bottleneck of specific enzymes for treating specific bacteria residues. At the same time, the method is simple in operation, short in reaction cycle, low in cost, and does not produce secondary Secondary pollution, has very good environmental protection benefits.
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CN101624605A (en) * | 2008-07-08 | 2010-01-13 | 武汉烁森生态科技有限公司 | Biological method for processing spiramycin bacteria residue |
CN101979521A (en) * | 2010-09-26 | 2011-02-23 | 吴鹏 | Complex enzyme preparation special for antibiotic dregs |
CN104328141A (en) * | 2014-10-30 | 2015-02-04 | 宁夏乙征生物工程有限公司 | Method for treating antibiotic residues by enzymic method |
EP3034186A1 (en) * | 2014-12-16 | 2016-06-22 | Luxembourg Institute of Science and Technology (LIST) | Method of degradation and inactivation of antibiotics in water by immobilized enzymes onto functionalized supports |
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CN101624605A (en) * | 2008-07-08 | 2010-01-13 | 武汉烁森生态科技有限公司 | Biological method for processing spiramycin bacteria residue |
CN101979521A (en) * | 2010-09-26 | 2011-02-23 | 吴鹏 | Complex enzyme preparation special for antibiotic dregs |
CN104328141A (en) * | 2014-10-30 | 2015-02-04 | 宁夏乙征生物工程有限公司 | Method for treating antibiotic residues by enzymic method |
EP3034186A1 (en) * | 2014-12-16 | 2016-06-22 | Luxembourg Institute of Science and Technology (LIST) | Method of degradation and inactivation of antibiotics in water by immobilized enzymes onto functionalized supports |
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