CN106431555A - Method for preparing methane and organic compound fertilizer from plant straws - Google Patents
Method for preparing methane and organic compound fertilizer from plant straws Download PDFInfo
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Abstract
本发明公开了一种植物秸秆制备沼气和有机复合肥的方法,该方法包括以下过程:植物秸秆粉碎后与驯化的污泥和人畜粪便搅拌混合进行一次发酵;一次发酵完成后,将发酵的沼渣与草木灰和骨粉混合,同时加入植物秸秆进行二次堆肥发酵;二次堆肥发酵完成后对发酵物进行筛分,筛上物和植物秸秆混合加入沼渣中进行二次堆肥发酵,筛下物进行造粒,烘干后包装。本发明方法制备沼气和有机复合肥,能够充分利用固体废物资源,利用成本低,见效快,实现固体废物的完全资源化,经济效益和环境效益显著。
The invention discloses a method for preparing biogas and organic compound fertilizer from plant stalks. The method comprises the following steps: stirring and mixing the plant stalks with domesticated sludge and human and livestock manure for primary fermentation; after the primary fermentation is completed, the fermented biogas The slag is mixed with plant ash and bone meal, and plant straw is added for secondary composting fermentation; after the secondary composting fermentation is completed, the fermented product is sieved, and the sieved material and plant straw are mixed into the biogas residue for secondary composting fermentation. Carry out granulation, pack after drying. The method of the invention prepares biogas and organic compound fertilizer, can make full use of solid waste resources, has low utilization cost, quick effect, realizes complete recycling of solid waste, and has remarkable economic and environmental benefits.
Description
技术领域technical field
本发明涉及一种植物秸秆制备沼气和有机复合肥的方法,属于固体资源化利用技术领域。The invention relates to a method for preparing biogas and organic compound fertilizer from plant stalks, and belongs to the technical field of solid resource utilization.
背景技术Background technique
近些年来,植物秸秆焚烧后严重污染空气,若资源化利用,不仅解决空气污染问题,而且可以作为资源来缓解能源短缺问题。当前植物秸秆的用途主要有三个方面,一是作为生物质能发电,二是作为燃料利用热能,三是作为发酵原料制备沼气和有机肥。相比之下,作为发酵原料制备沼气和有机肥是目前资源化利用水平最高的一种,不仅实现废物的完全资源化,而且不产生二次污染,经济效益和环境效益显著。In recent years, the incineration of plant straw has seriously polluted the air. If it is used as a resource, it will not only solve the problem of air pollution, but also be used as a resource to alleviate the problem of energy shortage. At present, there are three main uses of plant straw, one is to generate electricity as biomass energy, the other is to use heat energy as fuel, and the third is to prepare biogas and organic fertilizer as fermentation raw materials. In contrast, the preparation of biogas and organic fertilizer as fermentation raw materials is currently the highest level of resource utilization. It not only realizes the complete recycling of waste, but also does not produce secondary pollution, and has significant economic and environmental benefits.
植物秸秆制备沼气和有机肥的原理是首先通过加入驯化后的污泥一次发酵制备沼气,制备后的沼渣加入植物秸秆、草木灰和骨粉进行二次堆肥发酵制备有机肥,二次堆肥发酵加入的植物秸秆不需要粉碎,少量没有发酵完全的植物秸秆通过筛分再回到制肥发酵池。此方法成本低,沼气产量大,制备的有机肥肥效高。The principle of preparing biogas and organic fertilizer from plant straw is firstly to prepare biogas by adding domesticated sludge for primary fermentation, and then add plant straw, plant ash and bone meal to the prepared biogas residue for secondary composting and fermentation to prepare organic fertilizer. Plant stalks do not need to be crushed, and a small amount of unfermented plant stalks are sieved and returned to the fertilizer fermentation tank. The method has the advantages of low cost, large biogas output, and high fertilizer efficiency of the prepared organic fertilizer.
目前制备沼气和有机肥的专利包括:利用发酵隧道快速发酵畜禽粪便生产有机肥的方法(201511030820.6)、一种兔粪便有机肥的制备方法(201510959405.2)、一种醋槽蚯蚓粪便防土传病害缓释颗粒有机肥的制备方法(201510951429.3)、利用马铃薯渣和畜禽粪便复配有机肥的方法(201510785700.0)、利用化粪池内粪便生产生物有机肥的装置和方法(201510766980.0)、一种利用动物肠胃内容物及粪便生产有机肥的工艺(201510746406.9)、一种用粪便、秸秆生产可溶性有机肥的方法(201510707613.3)、一种以高水分畜禽粪便生产有机肥的发酵系统及发酵方法(201510667261.3)、利用畜禽粪便发酵生产多元素生物有机肥(201510462478.0)、一种畜禽粪便无害化生产有机肥的方法(201510344607.6)、利用高含水量禽畜粪便制备保水生物有机肥的方法(201510260833.6)、一种利用动物粪便制作的有机肥及其制备工艺(201510137802.1)、一种猪粪、鸡粪混合粪便无害化处理制有机肥(201410255921.2)、一种利用秸秆直接制肥的方法及制备的秸秆有机肥(201610131358.7)、秸秆无害转化制肥装置(201520040808.2)、一种利用植物秸秆制备水溶性生态有机碳肥的方法(201510965747.5)、一种有机复合肥的制备方法(201510298512.5)、利用秸秆快速制肥系统(201420044634.2)等。但上述专利因存在工艺复杂、成本高、技术水平低和易产生二次污染等一项或多项缺点,使用范围受到很大局限,应用效果不明显,推广困难。The current patents for the preparation of biogas and organic fertilizer include: a method for rapidly fermenting livestock and poultry manure to produce organic fertilizer using a fermentation tunnel (201511030820.6), a method for preparing organic fertilizer from rabbit manure (201510959405.2), a method for preventing soil-borne diseases from earthworm manure in a vinegar tank Preparation method of slow-release granular organic fertilizer (201510951429.3), method of compounding organic fertilizer by using potato dregs and livestock and poultry manure (201510785700.0), device and method for producing bio-organic fertilizer by using manure in septic tank (201510766980.0), a method of using animal manure Process for producing organic fertilizer from gastrointestinal contents and manure (201510746406.9), a method for producing soluble organic fertilizer from manure and straw (201510707613.3), a fermentation system and method for producing organic fertilizer with high-moisture livestock and poultry manure (201510667261.3) , Fermentation of livestock and poultry manure to produce multi-element bio-organic fertilizer (201510462478.0), a method for the harmless production of organic fertilizer from livestock and poultry manure (201510344607.6), a method for preparing water-retaining bio-organic fertilizer by using high-water-content poultry and livestock manure (201510260833.6) , An organic fertilizer made by using animal manure and its preparation process (201510137802.1), a kind of organic fertilizer made by harmless treatment of mixed manure from pig manure and chicken manure (201410255921.2), a method of directly making fertilizer from straw and the prepared straw Organic fertilizer (201610131358.7), straw harmless conversion fertilizer making device (201520040808.2), a method of using plant straw to prepare water-soluble ecological organic Fertilizer system (201420044634.2), etc. However, due to one or more disadvantages of the above-mentioned patents, such as complex process, high cost, low technical level and easy generation of secondary pollution, the scope of application is greatly limited, the application effect is not obvious, and it is difficult to popularize.
因此,开发一个简单实用、可操作性强,特别是有效的利用植物秸秆废物,实现废物的完全资源化,将具有重要意义。Therefore, it will be of great significance to develop a simple, practical, operable, especially effective utilization of plant straw waste to realize the complete recycling of waste.
发明内容Contents of the invention
本发明的目的是提供一种植物秸秆制备沼气和有机复合肥的方法,提高植物秸秆的资源化利用水平,降低制备沼气和有机肥的成本。The purpose of the present invention is to provide a method for preparing biogas and organic compound fertilizer from plant straws, improve the resource utilization level of plant straws, and reduce the cost of preparing biogas and organic fertilizers.
本发明的技术方案是这样实现的,一种植物秸秆制备沼气和有机复合肥的方法,该方法包括以下过程:植物秸秆粉碎后与驯化的污泥和人畜粪便搅拌混合进行一次发酵;一次发酵完成后,将发酵的沼渣与草木灰和骨粉混合,同时加入植物秸秆进行二次堆肥发酵;二次堆肥发酵完成后对发酵物进行筛分,筛上物和植物秸秆混合加入沼渣中进行二次堆肥发酵,筛下物进行造粒,烘干后包装。The technical solution of the present invention is achieved in this way, a method for preparing biogas and organic compound fertilizer from plant straws, the method includes the following process: After the plant straws are pulverized, they are stirred and mixed with domesticated sludge and human and animal manure for primary fermentation; the primary fermentation is completed Finally, mix the fermented biogas residue with plant ash and bone meal, and at the same time add plant straw for secondary composting fermentation; after the secondary composting fermentation is completed, sieve the fermented product, and mix the sieved material and plant straw into the biogas residue for secondary composting. Composting and fermentation, granulation of undersieve, drying and packaging.
所述的植物秸秆粉碎加工后的长度不超过8cm;所述的污泥采用污水处理厂的污泥或河流湖泊的底泥,要求污泥重金属含量不超过现行国家标准要求,驯化时间为7~14天。The length of the crushed plant straw is no more than 8cm; the sludge is sludge from a sewage treatment plant or sediment from rivers and lakes, and the heavy metal content of the sludge is required not to exceed the requirements of the current national standards, and the acclimation time is 7 to 10 cm. 14 days.
所述的一次发酵产生的沼气进行净化处理后输送给用户,沼气净化处理方法为采用饱和的碳酸钠溶液或活性炭;所述的一次发酵原料的混合物比例为植物秸秆:污泥:人畜粪便=0.45~0.65:0.15~0.25:0.15~0.45,该比例为干物料的比例;所述的一次发酵过程中,采用泵抽取沼液,再循环回流到发酵池进行液动搅拌,每天启动泵循环一次,每次开启5~10分钟。The biogas produced by the primary fermentation is purified and delivered to the user. The biogas purification method is to use saturated sodium carbonate solution or activated carbon; the mixture ratio of the primary fermentation raw materials is plant straw: sludge: human and animal manure = 0.45 ~0.65: 0.15~0.25: 0.15~0.45, the ratio is the ratio of dry materials; in the primary fermentation process, the biogas slurry is pumped out and recirculated back to the fermentation tank for hydraulic agitation, and the pump is started to circulate once a day. Turn on for 5-10 minutes each time.
所述的二次堆肥发酵中物料比例为沼渣:骨粉:草木灰:植物秸秆=1:0.07~0.15:0.05~0.12:0.45~0.55,该比例为干物料的比例;植物秸秆首次加入的为新鲜的植物秸秆,以后为筛上物与新加入的新鲜植物秸秆的混合物;二次堆肥发酵混合物中加入发酵剂,发酵剂的加入量为100~200克/吨,通过加入骨粉中,在发酵开始时加入二次堆肥发酵混合物中;所述二次堆肥发酵混合物开始发酵时的含水量控制在55%~65%;堆肥高度夏季控制在0.6~1.0m,冬季控制在0.8~1.6m;发酵时采用薄膜或草帘覆盖,待内部温度升到25℃时,将覆盖物揭开,夏季待温度升到45℃以上时开始一次翻堆,冬季温度升到55℃以上时开始一次翻堆,以后每当温度达到60℃以上时需进行翻堆;所述的发酵剂有效活菌数≥200亿/克。The ratio of materials in the secondary composting fermentation is biogas residue: bone meal: plant ash: plant straw = 1: 0.07-0.15: 0.05-0.12: 0.45-0.55, the ratio is the ratio of dry materials; the first addition of plant straw is fresh The plant stalks of the sieve will be the mixture of the sieved material and the newly added fresh plant stalks in the future; a starter is added to the secondary composting fermentation mixture, and the amount of the starter is 100-200 g/ton. When adding the secondary composting fermentation mixture; the water content when the secondary composting fermentation mixture starts to ferment is controlled at 55% to 65%; the compost height is controlled at 0.6 to 1.0m in summer and 0.8 to 1.6m in winter; Cover with film or straw curtains. When the internal temperature rises to 25°C, uncover the cover. In summer, when the temperature rises above 45°C, turn over once, and in winter, turn once when the temperature rises above 55°C. Every time the temperature reaches above 60°C, the compost needs to be turned over; the number of effective viable bacteria in the starter is ≥20 billion/g.
所述的筛分,采用筛网的孔径为10~20mm;所述的造粒烘干后,其含水量低于15%;包装采用塑料袋密封包装。The sieving uses a sieve with an aperture of 10-20 mm; the granulation and drying have a water content lower than 15%; and the packaging is sealed in a plastic bag.
所述的一次发酵终止时间为最大产气量的40%以下,一次发酵温度不低于15℃;二次堆肥发酵的时间为10~20天,发酵终止前一天控制温度为70℃以上,且时间不少于3小时。The termination time of the primary fermentation is less than 40% of the maximum gas production, and the temperature of the primary fermentation is not lower than 15°C; the time of the secondary composting fermentation is 10 to 20 days, and the temperature is controlled to be above 70°C one day before the termination of the fermentation, and the time Not less than 3 hours.
所述的净化处理的碳酸钠溶液或活性炭,在总吸收率低于70%时,需进行处理;对碳酸钠溶液处理方法为在温度为50~80℃条件下加热,加热时间为20~30分钟;对活性炭的处理方法为在80~100℃温度条件下加热,加热时间为10~20分钟。The sodium carbonate solution or activated carbon of the purification treatment needs to be treated when the total absorption rate is lower than 70%; the sodium carbonate solution treatment method is to heat at a temperature of 50-80°C, and the heating time is 20-30 Minutes; the treatment method for activated carbon is to heat at a temperature of 80-100°C, and the heating time is 10-20 minutes.
所述的二次堆肥发酵加入的新鲜植物秸秆,在加入前进行碾压,碾压接触压力为100~200kPa,秸秆铺设厚度为100~200mm,碾压3~5次;在发酵结束后,发酵混合料温度低于40℃,加入枯草芽孢杆菌可制备生物菌肥。The fresh plant stalks added in the secondary composting fermentation are rolled before adding, the rolling contact pressure is 100-200kPa, the thickness of the straw laying is 100-200mm, and the rolling is 3-5 times; after the fermentation is finished, the fermentation The temperature of the mixture is lower than 40°C, and the biological fertilizer can be prepared by adding Bacillus subtilis.
本发明的积极效果是能够充分利用固体废物,实现固体废物的完全资源化,该方法简单,成本低,见效快,经济效益和环境效益显著。The positive effect of the invention is that the solid waste can be fully utilized and the complete recycling of the solid waste can be realized. The method is simple, low in cost, quick in effect and remarkable in economic and environmental benefits.
附图说明Description of drawings
图1为本发明的工艺流程示意图。Figure 1 is a schematic diagram of the process flow of the present invention.
具体实施方式detailed description
下面结合附图对本发明作进一步的说明Below in conjunction with accompanying drawing, the present invention will be further described
实施例1:用玉米秸秆制备沼气和有机复合肥Example 1: Preparation of biogas and organic compound fertilizer with corn stalks
如图1所示,该工艺过程包括:在玉米秸秆粉碎后与驯化的污泥和人畜粪便搅拌混合进行一次发酵;一次发酵完成后,将发酵的沼渣与草木灰和骨粉混合,同时加入玉米秸秆进行二次堆肥发酵;二次堆肥发酵完成后对发酵物进行筛分,筛上物和玉米秸秆混合加入沼渣中进行二次堆肥发酵,筛下物进行造粒,烘干后包装。As shown in Figure 1, the process includes: after the corn stalks are pulverized, they are stirred and mixed with domesticated sludge and human and animal manure for primary fermentation; after the primary fermentation is completed, the fermented biogas residue is mixed with plant ash and bone meal, and corn stalks are added at the same time Carry out secondary composting fermentation; after the secondary composting fermentation is completed, the fermented product is sieved, and the sieved material and corn stalks are mixed and added to the biogas residue for secondary composting fermentation, and the sieved material is granulated, dried and packaged.
植物秸秆粉碎加工后的长度不超过8cm,污泥采用污水处理厂的污泥,要求污泥重金属含量不超过现行国家标准要求,驯化时间为7天。The length of the crushed and processed plant straw shall not exceed 8cm. The sludge shall be sludge from a sewage treatment plant, and the heavy metal content of the sludge shall not exceed the requirements of the current national standard, and the domestication time shall be 7 days.
一次发酵产生的沼气进行净化处理后输送给用户,沼气净化处理方法为采用饱和的碳酸钠溶液;一次发酵原料的混合物比例为植物秸秆:污泥:人畜粪便=0.45:0.15:0.40,该比例为干物料的比例;一次发酵过程中,通过泵抽取沼液,再循环回流到发酵池,实现搅拌功能,每天启动泵循环一次,每次开启5分钟。The biogas produced by the primary fermentation is purified and delivered to the user. The biogas purification method is to use saturated sodium carbonate solution; the mixture ratio of primary fermentation raw materials is plant straw: sludge: human and animal manure = 0.45: 0.15: 0.40, the ratio is The proportion of dry materials; during a fermentation process, the biogas slurry is pumped through the pump and recirculated back to the fermentation tank to realize the stirring function. The pump cycle is started once a day, and each time it is turned on for 5 minutes.
二次堆肥发酵混合料干物料比例为沼渣:骨粉:草木灰:植物秸秆=1:0.07:0.05:0.45;植物秸秆首次加入的为新鲜的植物秸秆,以后为筛上物与新加入的新鲜植物秸秆的混合物;二次堆肥发酵混合物中加入发酵剂,发酵剂的加入量为200克/吨,通过加入骨粉中,在发酵开始时加入二次堆肥发酵混合物中;所述二次堆肥发酵混合物开始发酵时的含水量控制在55%~65%;堆肥夏季高度为1.0m,冬季高度为1.6m;发酵时采用薄膜覆盖,待内部温度升到25℃时,将覆盖物揭开,夏季待温度升到45℃以上时开始一次翻堆,冬季温度升到55℃以上时开始一次翻堆,以后每当温度达到60℃以上时需进行翻堆;所述的发酵剂有效活菌数≥200亿/克,发酵剂采用山东高龙生物科技有限公司生产的强效型有机肥发酵剂。The dry material ratio of the secondary composting fermentation mixture is biogas residue: bone meal: plant ash: plant straw = 1:0.07:0.05:0.45; the plant straw is added for the first time as fresh plant straw, and then it is the sieve and the newly added fresh plant A mixture of straw; a starter is added to the secondary composting fermentation mixture, and the amount of the starter is 200 grams per ton. By adding bone meal, it is added to the secondary composting fermentation mixture at the beginning of fermentation; the secondary composting fermentation mixture begins The water content during fermentation is controlled at 55% to 65%; the height of the compost in summer is 1.0m, and the height in winter is 1.6m; during fermentation, it is covered with a film. When the internal temperature rises to 25°C, the cover is uncovered, and the temperature When the temperature rises above 45°C, turn over once, and when the temperature rises above 55°C in winter, turn over once, and then turn over every time the temperature reaches above 60°C; the number of effective viable bacteria in the starter is ≥ 20 billion / gram, the leavening agent adopts the potent organic fertilizer starter produced by Shandong Gaolong Biotechnology Co., Ltd.
筛分采用的筛孔的孔径为10~20mm,造粒烘干后含水量低于15%,包装采用塑料袋密封包装。The aperture of the sieve used for screening is 10-20mm, the water content after granulation and drying is lower than 15%, and the packaging is sealed in a plastic bag.
一次发酵终止时间为最大产气量的40%以下,一次发酵温度不低于15℃;二次堆肥发酵的时间为20天,发酵终止前一天控制温度为70℃以上,且时间不少于3小时。The termination time of the primary fermentation is less than 40% of the maximum gas production, and the temperature of the primary fermentation is not lower than 15°C; the time of the secondary composting fermentation is 20 days, and the temperature is controlled to be above 70°C the day before the termination of the fermentation, and the time is not less than 3 hours .
净化处理的碳酸钠溶液,在总吸收率低于70%时,进行处理;对碳酸钠溶液处理方法为在温度为50~80℃条件下加热,加热时间为20分钟。The purified sodium carbonate solution is processed when the total absorption rate is lower than 70%. The sodium carbonate solution is treated by heating at a temperature of 50-80° C. for 20 minutes.
二次堆肥发酵加入的新鲜植物秸秆,在加入前进行碾压,碾压接触压力为100kPa,秸秆铺设厚度为100mm,碾压3次;在发酵结束后,发酵混合料温度低于40℃,加入枯草芽孢杆菌可制备生物菌肥。The fresh plant straw added in the secondary composting fermentation should be rolled before adding, the rolling contact pressure is 100kPa, the straw laying thickness is 100mm, and rolled three times; after the fermentation, the temperature of the fermentation mixture is lower than 40°C, Bacillus subtilis can prepare biological fertilizer.
实施例2:用稻草制备沼气和有机复合肥Embodiment 2: Prepare biogas and organic compound fertilizer with rice straw
如图1所示,按照工艺流程制备沼气和有机肥,植物秸秆粉碎加工后的长度不超过8cm,污泥采用河流的底泥,驯化时间为14天。As shown in Figure 1, biogas and organic fertilizers were prepared according to the technological process. The length of the plant straw after crushing and processing was not more than 8cm.
沼气采用活性炭净化,一次发酵原料的混合物干物料比例为植物秸秆:污泥:人畜粪便=0.65:0.15:0.20,每天启动泵循环一次,每次开启10分钟。The biogas is purified by activated carbon, and the dry material ratio of the primary fermentation raw material mixture is plant straw: sludge: human and animal manure = 0.65: 0.15: 0.20. Start the pump cycle once a day for 10 minutes each time.
二次堆肥发酵中混合物干物料比例为沼渣:骨粉:草木灰:植物秸秆=1:0.15:0.12:0.55;二次堆肥发酵混合物中发酵剂的加入量为100克/吨,通过加入骨粉中,在发酵开始时加入二次堆肥发酵混合物中;二次堆肥发酵混合物开始发酵时的含水量控制在55%~65%;堆肥高度夏季控制在0.6m,冬季控制在0.8m;发酵时采用草帘覆盖,待内部温度升到25℃时,将覆盖物揭开,夏季待温度升到45℃以上时开始一次翻堆,冬季温度升到55℃以上时开始一次翻堆,以后每当温度达到60℃以上时需进行翻堆;发酵剂有效活菌数≥200亿/克,发酵剂采用山东高龙生物科技有限公司生产的强效型有机肥发酵剂。The dry material ratio of the mixture in the secondary composting fermentation is biogas residue: bone meal: plant ash: plant straw = 1: 0.15: 0.12: 0.55; the amount of starter in the secondary composting fermentation mixture is 100 g/ton. Add the secondary composting fermentation mixture at the beginning of fermentation; the water content of the secondary composting fermentation mixture is controlled at 55% to 65% at the beginning of fermentation; the compost height is controlled at 0.6m in summer and 0.8m in winter; straw mats are used for fermentation Covering, when the internal temperature rises to 25°C, uncover the cover, and start turning once when the temperature rises above 45°C in summer, and start turning once when the temperature rises above 55°C in winter, and then whenever the temperature reaches 60°C When the temperature is above ℃, it is necessary to turn the compost; the effective number of viable bacteria in the starter is ≥20 billion/g, and the starter is a powerful organic fertilizer starter produced by Shandong Gaolong Biotechnology Co., Ltd.
筛分所用筛的孔径为10~20mm,造粒烘干后,其含水量低于15%,包装采用塑料袋密封包装。The aperture of the sieve used for sieving is 10-20 mm. After granulation and drying, its water content is lower than 15%. The packaging is sealed in plastic bags.
一次发酵终止时间为最大产气量的40%以下,一次发酵温度不低于15℃;二次堆肥发酵的时间为10天,发酵终止前一天控制温度为70℃以上,且时间不少于3小时。The termination time of primary fermentation is less than 40% of the maximum gas production, and the temperature of primary fermentation is not lower than 15°C; the time of secondary composting fermentation is 10 days, and the temperature is controlled to be above 70°C the day before the termination of fermentation, and the time is not less than 3 hours .
二次堆肥发酵加入的新鲜植物秸秆,在加入前进行碾压,碾压接触压力为200kPa,秸秆铺设厚度为200mm,碾压5次。The fresh plant straw added in the secondary composting fermentation should be rolled before adding, the rolling contact pressure is 200kPa, the straw laying thickness is 200mm, and the rolling is done 5 times.
净化处理的活性炭,在总吸收率低于70%时,进行处理;对活性炭的处理方法为在温度为80~100℃条件下加热,加热时间为10分钟。The purified activated carbon is treated when the total absorption rate is lower than 70%. The activated carbon is treated by heating at a temperature of 80-100°C for 10 minutes.
以上公开具体实施例对本发明进行了揭示,但本发明并非局限于此,任何本领域的技术人员能想到的变化,在不脱离本发明的设计思想和范围内,对本发明进行的各种改动,都应在本发明的保护范围之内。The specific embodiments disclosed above have disclosed the present invention, but the present invention is not limited thereto, any changes conceivable by those skilled in the art, without departing from the design idea and scope of the present invention, the various changes carried out to the present invention, All should be within the protection scope of the present invention.
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