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CN105254346B - The minimizing technology of fluoroquinolone antibiotics in a kind of birds and beasts excrement - Google Patents
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CN105254346B - The minimizing technology of fluoroquinolone antibiotics in a kind of birds and beasts excrement - Google Patents

The minimizing technology of fluoroquinolone antibiotics in a kind of birds and beasts excrement Download PDF

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CN105254346B
CN105254346B CN201510636598.8A CN201510636598A CN105254346B CN 105254346 B CN105254346 B CN 105254346B CN 201510636598 A CN201510636598 A CN 201510636598A CN 105254346 B CN105254346 B CN 105254346B
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temperature
composting
method described
compost
fluoroquinolone antibiotics
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CN105254346A (en
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薛南冬
孟磊
张石磊
杨兵
王继勇
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Chinese Research Academy of Environmental Sciences
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

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Abstract

本发明公开了一种禽兽粪便中氟喹诺酮类抗生素的去除方法,步骤包括:(1)配置堆肥原料:将鸡粪、锯末、无菌蒸馏水和耐高温菌剂制成堆肥原料,其中鸡粪与锯末的质量比为5~10:1,堆肥原料含水率在55%~60%之间,耐高温菌剂制为产黄纤维单胞菌;(2)高温堆肥:控制翻堆频率以使堆肥温度在45~65℃之间,实现高温发酵;(3)中温堆肥:经高温发酵后,控制人工翻堆频率,使堆肥产品温度在30~45℃之间,实现中温发酵。本发明方法充分利用其中耐高温菌种及相关微生物的降解作用去除禽兽粪便中氟喹诺酮类抗生素,使有机肥料中氟喹诺酮类抗生素降低至安全量。The invention discloses a method for removing fluoroquinolone antibiotics in poultry feces. The steps include: (1) configuring composting raw materials: making composting raw materials from chicken manure, sawdust, sterile distilled water and high-temperature-resistant bacterial agents, wherein chicken manure is mixed with The mass ratio of sawdust is 5-10:1, the moisture content of compost raw materials is between 55% and 60%, and the high-temperature-resistant bacterial agent is made of Cellulomonas flavinogenes; (2) High-temperature composting: control the frequency of composting so that The temperature is between 45-65°C to achieve high-temperature fermentation; (3) Medium-temperature composting: After high-temperature fermentation, the frequency of manual turning is controlled so that the temperature of the compost product is between 30-45°C to achieve medium-temperature fermentation. The method of the invention fully utilizes the degradation effect of the high-temperature-resistant strains and related microorganisms to remove the fluoroquinolone antibiotics in poultry manure, and reduces the fluoroquinolone antibiotics in the organic fertilizer to a safe amount.

Description

一种禽兽粪便中氟喹诺酮类抗生素的去除方法A method for removing fluoroquinolone antibiotics in poultry feces

技术领域technical field

本发明涉及一种禽兽粪便有机肥中抗生素的去除方法,具体地说是六种氟喹诺酮类(FQs) 抗生素的去除方法。The invention relates to a method for removing antibiotics in poultry manure organic fertilizer, in particular to a method for removing six kinds of fluoroquinolone (FQs) antibiotics.

背景技术Background technique

抗生素广泛应用于人类医疗、畜禽养殖、水产养殖等。作为动物促生长剂和治疗用药物,畜牧业已成为使用抗生素量最大的行业,据统计,每年消费的抗生素约有50%~70%被用于畜牧业。抗生素进入动物体内后40%~90%以母体或代谢物的形式随畜禽粪便进入环境。早在2007年有学者调查了我国8个省份的143家牲畜饲养场,发现调查样本氟喹诺酮类抗生素含量较高,其中猪粪及牛粪中恩诺沙星浓度为33.26 mg·kg-1,环丙沙星浓度为33.98mg·kg-1;鸡粪中诺氟沙星最大浓度为225.45 mg·kg-1,环丙沙星最大浓度为45.59 mg·kg-1,恩诺沙星最大浓度为1420.76 mg·kg-1Antibiotics are widely used in human medicine, livestock and poultry farming, aquaculture, etc. As animal growth promoters and therapeutic drugs, animal husbandry has become the industry that uses the largest amount of antibiotics. According to statistics, about 50% to 70% of antibiotics consumed each year are used in animal husbandry. After antibiotics enter the animal body, 40% to 90% enter the environment in the form of the mother or metabolites along with the manure of livestock and poultry. As early as 2007, some scholars investigated 143 livestock farms in 8 provinces of China, and found that the survey samples contained high levels of fluoroquinolone antibiotics, among which the concentration of enrofloxacin in pig manure and cow manure was 33.26 mg·kg -1 , The concentration of ciprofloxacin was 33.98 mg·kg -1 ; the maximum concentration of norfloxacin in chicken manure was 225.45 mg·kg -1 , the maximum concentration of ciprofloxacin was 45.59 mg·kg -1 , the maximum concentration of enrofloxacin It is 1420.76 mg·kg -1 .

环境中残留的抗生素威胁动植物及人类健康。有研究发现,喹诺酮类抗生素对胎儿有致畸作用,对人体神经系统和消化吸收系统、心脏和血管系统也有很大危害。研究结果表明,抗生素的大量使用会导致病原微生物产生耐药性,使抗生素能够杀死细菌的有效剂量不断增加,例如将牛粪施于花园后,导致该土壤对特定抗生素抗性增加70%。此外抗生素的使用会影响土壤中微生物的性质,例如马驿等研究表明含量高于0.1μg/g的恩诺沙星会显著降低土壤微生物的丰富度和多样性,进而降低其降解其他有机污染物及重金属的能力。Antibiotic residues in the environment threaten the health of animals, plants and humans. Studies have found that quinolone antibiotics have teratogenic effects on the fetus, and are also very harmful to the human nervous system, digestive and absorption system, heart and vascular system. The results of the study show that the heavy use of antibiotics will lead to the development of resistance of pathogenic microorganisms, so that the effective dose of antibiotics to kill bacteria is continuously increasing. For example, after applying cow manure to the garden, the soil resistance to specific antibiotics increases by 70%. In addition, the use of antibiotics will affect the properties of microorganisms in the soil. For example, Ma Yi et al. have shown that enrofloxacin with a content higher than 0.1 μg/g will significantly reduce the richness and diversity of soil microorganisms, thereby reducing their degradation of other organic pollutants. and heavy metals.

氟喹诺酮类抗生素广泛存在于土壤环境尤其是禽畜粪便中,对土壤环境,动植物及人类健康构成严重威胁,因此亟需研发相关技术以降低或去除环境中氟喹诺酮类抗生素浓度。目前对去除水体中抗生素有少量研究,例如超声波降解法、人工湿地法等,超声波法降解速度快,适用范围广,但其能耗大、成本高且反应条件难控制;人工湿地法成本低,易维护但其占地面积大且会散发恶臭。对禽畜粪便中氟喹诺酮类抗生素的研究主要停留在其检测分析方法方面,对其去除方法研究较少。Fluoroquinolone antibiotics widely exist in the soil environment, especially in poultry manure, and pose a serious threat to the soil environment, animals, plants, and human health. Therefore, it is urgent to develop related technologies to reduce or remove the concentration of fluoroquinolone antibiotics in the environment. At present, there is a small amount of research on the removal of antibiotics in water, such as ultrasonic degradation, artificial wetland, etc. Ultrasonic degradation is fast and has a wide range of applications, but its energy consumption is high, the cost is high, and the reaction conditions are difficult to control; the artificial wetland is low in cost. It is easy to maintain but it occupies a large area and emits a foul smell. The research on fluoroquinolone antibiotics in poultry feces mainly stays in its detection and analysis methods, and there are few studies on their removal methods.

发明内容Contents of the invention

本发明的目的在于突破去除禽畜粪便中抗生素类污染物技术瓶颈,提出一种去除禽畜粪便中氟喹诺酮类抗生素的方法,以降低其浓度,实现禽畜粪便作为有机肥的无害化。The purpose of the present invention is to break through the technical bottleneck of removing antibiotic pollutants in poultry manure, and propose a method for removing fluoroquinolone antibiotics in poultry manure to reduce its concentration and realize the harmlessness of poultry manure as organic fertilizer.

本发明提供的技术方案是:一种去除禽畜粪便中氟喹诺酮类抗生素的方法,包括如下步骤:The technical scheme provided by the invention is: a method for removing fluoroquinolone antibiotics in poultry manure, comprising the steps of:

(1) 配置堆肥原料:将鸡粪、锯末、无菌蒸馏水和耐高温菌剂制成堆肥原料,其中鸡粪与锯末的质量比为5~10:1,堆肥原料含水率在55%~60%之间,耐高温菌剂制为产黄纤维单胞菌;(1) Composting raw materials: Chicken manure, sawdust, sterile distilled water and high-temperature-resistant bacterial agents are used to make compost raw materials. The mass ratio of chicken manure to sawdust is 5-10:1, and the moisture content of compost raw materials is 55%-60. %, the high temperature-resistant bacterial agent is prepared as Cellulomonas flavogenes;

(2) 高温堆肥:控制翻堆频率以使堆肥温度在45~65℃之间,实现高温发酵;(2) High-temperature composting: control the turning frequency so that the composting temperature is between 45 and 65°C to achieve high-temperature fermentation;

(3) 中温堆肥:经高温发酵后,控制人工翻堆频率,使堆肥产品温度在30~45℃之间,实现中温发酵。(3) Medium-temperature composting: After high-temperature fermentation, the frequency of manual turning is controlled so that the temperature of the compost product is between 30 and 45°C to achieve medium-temperature fermentation.

所述的方法,所述耐高温菌剂以液体菌剂形式投加,投加比例为1:10~1:25(v/w),优选为1:20(v/w)。In the method described above, the high-temperature-resistant bacterial agent is added in the form of liquid bacterial agent, and the dosage ratio is 1:10-1:25 (v/w), preferably 1:20 (v/w).

所述的方法,其中,所述菌种为产黄纤维单胞菌,其驯化制备耐高温菌种步骤如下:The method, wherein, the bacterial strain is Cellulomonas flavogenes, and the steps of domesticating and preparing the high-temperature-resistant strain are as follows:

将保存在LB培养基上的产黄纤维单胞菌进行活化,将黄纤维单胞菌按2%接种至选择性培养基中,在恒温60℃条件下连续震荡72小时。Cellulomonas flavogenes stored on LB medium was activated, and Cellulomonas flavogenes was inoculated into selective medium at 2% and shaken continuously for 72 hours at a constant temperature of 60°C.

选择性培养基:KH2PO4:0.5g ,NaCI :0.5g , 蛋白胨:0.5g,MgCI2 :0.5g, (NH4)SO4 :0.5g,NH4NO3:1.0g,K2HPO4 :1.5g ,蒸馏水1000ml,pH为中性。Selective medium: KH 2 PO 4 : 0.5g, NaCI : 0.5g, Peptone: 0.5g, MgCI 2 : 0.5g, (NH 4 )SO 4 : 0.5g, NH 4 NO 3 : 1.0g, K 2 HPO 4 : 1.5g, distilled water 1000ml, pH is neutral.

LB培养基:蛋白胨:10g;酵母膏:5g;NaCI:10g;蒸馏水1000ml;PH:7.0。LB medium: peptone: 10g; yeast extract: 5g; NaCI: 10g; distilled water 1000ml; PH: 7.0.

本发明所接种的生产菌株性质如下:革兰氏阳性,其细胞为球形,能产纤维素酶和蛋白酶,在选择性培养基中,其纤维素酶活为20.79 u/ml,蛋白酶酶活为18.52 u/ml,细菌在55 ℃仍保持较高的活性。The properties of the inoculated production strain of the present invention are as follows: Gram-positive, its cells are spherical, capable of producing cellulase and protease, and in the selective medium, its cellulase activity is 20.79 u/ml, and the protease activity is 18.52 u/ml, the bacteria still maintained high activity at 55 ℃.

所述的方法,所述鸡粪为.新鲜鸡粪,其与锯末的质量比为6~8:1,并且C/N保持在20:1。In the method, the chicken manure is fresh chicken manure, the mass ratio of it to sawdust is 6-8:1, and the C/N is kept at 20:1.

所述的方法,配置的堆肥原料含水率在55%~60%之间;堆肥室内温度控制在25~30℃。According to the method, the moisture content of the prepared compost raw materials is between 55% and 60%, and the temperature in the composting chamber is controlled at 25 to 30°C.

所述的方法,所述高温堆肥步骤,堆肥3~4天后达到高温阶段,温度控制在45~60℃之间持续10~12天,实现高温发酵。In the method, in the high-temperature composting step, the high-temperature stage is reached after 3-4 days of composting, and the temperature is controlled at 45-60° C. for 10-12 days to realize high-temperature fermentation.

所述的方法,所述中温堆肥步骤,堆肥产品温度在30~45℃之间,持续10~14天。In the method, in the medium-temperature composting step, the temperature of the composting product is between 30-45° C. for 10-14 days.

所述的方法,所述氟喹诺酮类抗生素包括诺氟沙星、环丙沙星、沙拉沙星、洛美沙星、恩诺沙星中的一种或多种。In the method, the fluoroquinolone antibiotics include one or more of norfloxacin, ciprofloxacin, sarafloxacin, lomefloxacin, and enrofloxacin.

本发明提出了一种采用堆肥结合外源添加菌剂的方法以去除禽畜粪便中的氟喹诺酮类抗生素。本发明方法充分利用其中耐高温菌种及相关微生物的降解作用去除禽兽粪便中氟喹诺酮类抗生素,使有机肥料中氟喹诺酮类抗生素降低至安全量,填补了去除禽畜粪便中氟喹诺酮类抗生素的技术空白。同时,具有如下的优点:The invention proposes a method for removing fluoroquinolone antibiotics in poultry manure by combining composting with exogenous bacterial agent addition. The method of the present invention makes full use of the degradation effect of heat-resistant bacteria and related microorganisms to remove fluoroquinolone antibiotics in poultry manure, reduces the fluoroquinolone antibiotics in organic fertilizers to a safe amount, and fills the gap of removing fluoroquinolone antibiotics in poultry manure. Technology gap. At the same time, it has the following advantages:

(1) 以禽畜粪便为原料,无需添加其他化学试剂,不会对环境产生二次污染;(2)采用堆肥技术,无需产生电能等能耗,经济成本低;(3) 采用人工翻堆供氧,便于操作及推广。(1) Using poultry and livestock manure as raw material, no need to add other chemical reagents, and will not cause secondary pollution to the environment; (2) Adopting composting technology, no need to generate electricity and other energy consumption, and low economic cost; (3) Using manual turning Oxygen supply, easy to operate and popularize.

具体实施方式Detailed ways

下面通过具体实施方式的详细描述来进一步阐明本发明,但并不是对本发明的限制,仅仅作示例说明。The present invention will be further clarified through the detailed description of specific embodiments below, but it is not intended to limit the present invention, but only for illustration.

实施例1Example 1

本发明去除禽畜粪便中氟喹诺酮类抗生素的方法,其步骤如下:The present invention removes the method for fluoroquinolone antibiotics in poultry manure, and its steps are as follows:

步骤一:将保存在LB培养基上的产黄纤维单胞菌进行活化,将黄纤维单胞菌按2%接种至选择性培养基中,在恒温60℃条件下连续震荡72小时。Step 1: Activate the Cellulomonas flavogenes stored on the LB medium, inoculate 2% of the Cellulomonas flavogenes into the selective medium, and shake continuously for 72 hours at a constant temperature of 60°C.

LB培养基:蛋白胨:10g;酵母膏:5g;NaCI:10g;蒸馏水1000ml;PH:7.0。LB medium: peptone: 10g; yeast extract: 5g; NaCI: 10g; distilled water 1000ml; PH: 7.0.

选择性培养基:KH2PO4:0.5g ,NaCI :0.5g , 蛋白胨:0.5g,MgCI2 :0.5g, (NH4)SO4 :0.5g,NH4NO3:1.0g,K2HPO4 :1.5g ,蒸馏水1000ml,PH为6.8~7.2。Selective medium: KH 2 PO 4 : 0.5g, NaCI : 0.5g, Peptone: 0.5g, MgCI 2 : 0.5g, (NH 4 )SO 4 : 0.5g, NH 4 NO 3 : 1.0g, K 2 HPO 4 : 1.5g, distilled water 1000ml, pH 6.8~7.2.

步骤二:将含水率约为65.0%,有机碳含量约为20%的新鲜鸡粪与锯末、蒸馏水混合均匀,控制其C/N比在20:1,含水率在55%~60%之间,菌剂用量约为堆肥物料体积的5%。Step 2: Mix fresh chicken manure with a moisture content of about 65.0% and an organic carbon content of about 20% with sawdust and distilled water to control the C/N ratio at 20:1 and the moisture content between 55% and 60%. , the amount of bacteria agent is about 5% of the volume of the compost material.

步骤三:堆体的起始物料温度为25℃,堆体高度为1.0 m,保持室温25~30℃,采用人工翻堆方式供氧,经过2~3天发酵后,堆体温度上升至45℃,进入高温期,堆肥的第3~8天,堆体温度迅速上升至60℃,第8~17天,堆体温度由60℃逐渐下降至45℃,本发明中高温堆肥可持续10~12天。Step 3: The initial material temperature of the pile is 25°C, the height of the pile is 1.0 m, and the room temperature is kept at 25~30°C. The oxygen is supplied by manual turning. After 2~3 days of fermentation, the temperature of the pile rises to 45 ℃, entering the high temperature period, the composting temperature rises rapidly to 60°C on the 3rd to 8th day of composting, and gradually drops from 60°C to 45°C on the 8th to 17th day. 12 days.

该步骤中所述堆肥物料成弱碱性,pH稳定在7.3~8.1之间,含水率稳定在55%~65%之间。In this step, the compost material becomes weakly alkaline, the pH is stable between 7.3 and 8.1, and the moisture content is stable between 55% and 65%.

步骤四:经上述高温发酵的堆肥物料,室温25~30℃,采用人工翻堆方式供氧,进入中温期。堆肥物料温度在30℃~45℃之间持续10~14天。Step 4: The compost material fermented by the above-mentioned high temperature, the room temperature is 25~30°C, and the oxygen is supplied by manual turning, and it enters the medium temperature period. The temperature of the compost material lasts for 10 to 14 days between 30°C and 45°C.

该步骤中所述堆肥物料呈弱碱性,pH稳定在7.6~8.1之间,含水率稳定在50%~55%之间。In this step, the compost material is weakly alkaline, the pH is stable between 7.6 and 8.1, and the moisture content is stable between 50% and 55%.

截至中温发酵阶段结束,种子发芽率指数(GI)已经达到85%以上。By the end of the middle temperature fermentation stage, the seed germination index (GI) has reached more than 85%.

经过三次平行试验,氟喹诺酮类抗生素降解效果见表1。After three parallel experiments, the degradation effects of fluoroquinolone antibiotics are shown in Table 1.

表1 诺氟沙星 环丙沙星 沙拉沙星 洛美沙星 恩诺沙星 初始浓度(mg/kg) 12.11 11.79 12.34 15.35 14.88 去除率1(高温段,%) 58.31 59.62 55.28 43.19 65.32 去除率2(中温段,%) 37.43 15.97 23.62 33.08 17.12 总去除率(%) 73.91 66.06 65.84 61.99 71.26 Table 1 Norfloxacin Ciprofloxacin Sarafloxacin Lomefloxacin Enrofloxacin Initial concentration (mg/kg) 12.11 11.79 12.34 15.35 14.88 Removal rate 1 (high temperature section, %) 58.31 59.62 55.28 43.19 65.32 Removal rate 2 (medium temperature section, %) 37.43 15.97 23.62 33.08 17.12 Total removal rate (%) 73.91 66.06 65.84 61.99 71.26

实施例2Example 2

按实施例1的物料配比及操作方法,再次进行了实验,实施例1与本实施例2不同之处是:鸡粪中氟喹诺酮类抗生素初始浓度不同,经过三次平行试验,氟喹诺酮类抗生素降解效果见表2。According to the proportioning of materials and the method of operation of Example 1, the experiment was carried out again. The difference between Example 1 and this Example 2 is: the initial concentration of fluoroquinolone antibiotics in the chicken manure is different. Through three parallel tests, the fluoroquinolone antibiotics The degradation effect is shown in Table 2.

表2 诺氟沙星 环丙沙星 沙拉沙星 洛美沙星 恩诺沙星 初始浓度(mg/kg) 21.72 22.19 22.39 27.73 24.71 去除率1(高温段,%) 48.25 52.07 63.39 35.89 54.40 去除率2(中温段,%) 66.81 56.18 35.87 39.31 27.93 总去除率(%) 82.82 79.00 76.52 61.09 67.13 Table 2 Norfloxacin Ciprofloxacin Sarafloxacin Lomefloxacin Enrofloxacin Initial concentration (mg/kg) 21.72 22.19 22.39 27.73 24.71 Removal rate 1 (high temperature section, %) 48.25 52.07 63.39 35.89 54.40 Removal rate 2 (medium temperature section, %) 66.81 56.18 35.87 39.31 27.93 Total removal rate (%) 82.82 79.00 76.52 61.09 67.13

从上面两个实施例表明,经采用本发明处理鸡粪中氟喹诺酮类抗生素,使得鸡粪中61.09~82.82%的氟喹诺酮类抗生素得到去除,降低了鸡粪作为有机肥料的危害,使其中氟喹诺酮类抗生素含量达到安全限值。Show from above two examples, through adopting the present invention to process fluoroquinolone antibiotics in chicken manure, make the fluoroquinolone antibiotics of 61.09~82.82% in chicken manure be removed, reduce the harm of chicken manure as organic fertilizer, make wherein fluorine The content of quinolone antibiotics reached the safe limit.

Claims (9)

  1. A kind of 1. method for removing fluoroquinolone antibiotics in fowl and animal excrement, which is characterized in that include the following steps:
    (1) composting material is configured:Composting material, wherein chicken manure is made in chicken manure, sawdust, sterile distilled water and high temperature resistant microbial inoculum Mass ratio with sawdust is 5 ~ 10:1, for composting material moisture content between 55% ~ 60%, high temperature resistant microbial inoculum is made as production yellowish fiber unit cell Bacterium;The high temperature resistant microbial inoculum is added in the form of liquid bacterial agent, and the ratio that adds is 1:10~1:25(v/w);
    (2) During High-Temperature Composting:Control turn pile frequency is so that compost temperature between 45 ~ 65 DEG C, realizes hot fermentation;
    (3) medium temperature compost:After hot fermentation, artificial turn pile frequency is controlled, makes composting production temperature between 30 ~ 45 DEG C, it is real Existing mesophilic digestion.
  2. 2. according to the method described in claim 1, it is characterized in that, the high temperature resistant microbial inoculum is added in the form of liquid bacterial agent, throw It is 1 to add ratio:20(v/w).
  3. 3. according to the method described in claim 1, it is characterized in that, the preparation process of high temperature resistant microbial inoculum is as follows:Activation production is yellow fine Monad is tieed up, yellowish fiber monad is seeded to by 2% in selective medium, it is small continuously to shake 72 under the conditions of 60 DEG C of constant temperature When.
  4. 4. according to the method described in claim 1, it is characterized in that, the chicken manure be fresh chicken manures, the mass ratio with sawdust It is 6 ~ 8:1, and C/N is maintained at 20:1.
  5. 5. according to the method described in claim 1, it is characterized in that, the composting material moisture content of configuration is between 55% ~ 60%.
  6. 6. according to the method described in claim 1, it is characterized in that, the control of compost indoor temperature is at 25 ~ 30 DEG C.
  7. 7. according to the method described in claim 1, it is characterized in that, the During High-Temperature Composting step, compost reach a high temperature after 3 ~ 4 days Stage, temperature control continue 10 ~ 12 days between 45 ~ 60 DEG C, realize hot fermentation.
  8. 8. according to the method described in claim 1, it is characterized in that, the medium temperature composting step, composting production temperature is 30 ~ 45 Between DEG C, continue 10 ~ 14 days.
  9. 9. according to claim 1 to 8 any one of them method, which is characterized in that the fluoroquinolone antibiotics include promise It is one or more in Flucloxacillin, Ciprofloxacin, sarafloxacin, Lomefloxacin, Enrofloxacin.
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CN106929442B (en) * 2017-02-24 2020-05-08 暨南大学 A quinolone antibiotic degrading bacteria and its application
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