CN206089649U - Device of preliminary treatment before utilizing sewage to straw bundle fermentation - Google Patents
Device of preliminary treatment before utilizing sewage to straw bundle fermentation Download PDFInfo
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Abstract
本实用新型公开一种利用污水对秸秆捆发酵前预处理的装置,该装置包括污水回收池和入料池,入料池一端设有浸泡槽,浸泡槽与入料池的交汇口设有一对疏导轮,浸泡槽上设有转压轮和依序等距排列的滚轴,浸泡槽的末端为平缓上升的斜坡,浸泡槽的宽度大于秸秆捆的宽度,浸泡槽的深度大于秸秆捆的高度,入料池和浸泡槽的水平面一致,位于紧邻浸泡槽中滚轴下缘的控制线,排水口位于浸泡槽末端的斜坡上,污水回收池的水位低于入料池,污水回收池的污水通过泵提升到入料池;所述装置能够实现对秸秆捆完全浸泡,并可调节浸泡槽中秸秆捆的位移速度,满足预处理过程中对浸泡时间的要求。
The utility model discloses a device for pretreating straw bales by using sewage before fermentation. The device includes a sewage recovery pool and a feeding pool. Grooming wheel, the soaking tank is equipped with turning and pressing wheels and rollers arranged equidistantly in sequence. The end of the soaking tank is a gently rising slope. The width of the soaking tank is greater than the width of the straw bundle, and the depth of the soaking tank is greater than the height of the straw bundle. , the level of the feeding tank and the soaking tank is consistent, and it is located close to the control line of the lower edge of the roller in the soaking tank. The drain is located on the slope at the end of the soaking tank. The pump is lifted to the feeding pool; the device can completely soak the straw bales, and can adjust the displacement speed of the straw bales in the soaking tank to meet the soaking time requirement in the pretreatment process.
Description
技术领域technical field
本实用新型涉及一种对秸秆捆发酵前预处理的装置,尤其是一种利用污水对秸秆捆发酵前预处理的装置及其应用,它可以自动将秸秆压入污水中浸泡,使秸秆充分吸收养殖污水,为后期进行后期堆肥创造条件,属于一种农业专用的机械设备及其应用。The utility model relates to a device for pre-fermenting straw bales, in particular to a device for pre-fermenting straw bales by using sewage and its application. Breeding sewage creates conditions for post-composting in the later stage, and belongs to a kind of agricultural special machinery and equipment and its application.
背景技术Background technique
随着农村的经济和农业集约化的发展,秸秆开始成为农村的又一大废弃物源头。每年的“秸秆焚烧”问题困扰着中国很多地区。大量的小麦、玉米等秸秆在田间焚烧,产生了大量浓重的烟雾,不仅成为农村环境保护的瓶颈问题,甚至成为殃及城市环境的罪魁祸首。秸秆焚烧,并不是因为秸秆太多,而是因为没有得到充分的利用。据有关统计,我国作为农业大国,每年可生成7亿多吨秸秆,成为“用处不大”但必须处理掉的“废弃物”。在此情况下,完全由农民来处理,就出现了大量焚烧的现象。因此,利用秸秆吸收污水,转化为肥料,是一种行之有效的方法。本实用新型主要是利用秸秆打捆后,放在污水里面浸泡吸收污水,但由于打捆秸秆密度小,体积大,人工浸泡费时费力,要通过人工浸泡大量的秸秆几乎不可能。本实用新型利用自动化机械装置,将秸秆浸泡到污水中充分吸收污水后,可以用于后期堆肥。With the development of rural economy and agricultural intensification, straw has become another major source of waste in rural areas. The annual "straw burning" problem plagues many parts of China. A large amount of wheat, corn and other stalks are burned in the field, which produces a lot of thick smoke, which not only becomes the bottleneck of rural environmental protection, but even becomes the chief culprit that affects the urban environment. Straw burning is not because there are too many straws, but because they are not fully utilized. According to relevant statistics, my country, as a large agricultural country, can produce more than 700 million tons of straw every year, which becomes "waste" that is "not very useful" but must be disposed of. In this case, it is completely handled by the farmers, and a large number of burnings have occurred. Therefore, it is an effective method to use straw to absorb sewage and convert it into fertilizer. The utility model mainly utilizes the bundled straws and puts them in the sewage to soak and absorb the sewage. However, due to the low density and large volume of the bundled straws, manual soaking is time-consuming and laborious, and it is almost impossible to manually soak a large amount of straws. The utility model utilizes an automatic mechanical device to soak the straw into the sewage to fully absorb the sewage, and then can be used for post-stage composting.
随着畜禽养殖业发展,动物排泄物数量越来越多,畜禽粪便已成为重要的污染源,严重影响着生态环境安全;将畜禽粪便、养殖污水无害化处理进行农田回用是有效途径之一,特别是将畜禽养殖废弃物进行厌氧发酵产沼气、沼液沼渣农田回用,在实现养殖废弃物处置与利用的同时,又能获取生物质能。因而,以沼气工程为纽带的农牧结合型技术,得到了全社会关注与重视,并得到了大力推广应用。With the development of livestock and poultry breeding industry, the amount of animal excrement is increasing, and livestock and poultry manure has become an important source of pollution, which seriously affects the safety of the ecological environment; it is effective to reuse livestock and poultry manure and breeding sewage in a harmless manner. One of the ways, especially the anaerobic fermentation of livestock and poultry waste to produce biogas, and the reuse of biogas slurry and residue in farmland, can obtain biomass energy while realizing the disposal and utilization of breeding waste. Therefore, the technology of combining agriculture and animal husbandry with the biogas project as the link has received the attention and attention of the whole society, and has been vigorously promoted and applied.
截止2014年,全国各类沼气工程10万处,沼气年产量达180亿立方米,沼液、沼渣产生量近6亿吨/年。在养殖-种植实际工程应用中,由于污水排放具有大量性、连续性等特点,常规利用污水的方法一般作为肥料还田,而农田种植用水用肥却是季节性和定量性;因此每天大量的污水不可能及时用于农田;因而需要更多的出路利用污水或沼液。As of 2014, there were 100,000 various biogas projects across the country, with an annual output of 18 billion cubic meters of biogas and nearly 600 million tons of biogas slurry and biogas residue per year. In the actual engineering application of breeding-planting, due to the large amount and continuity of sewage discharge, the conventional method of using sewage is generally used as fertilizer to return to the field, but the water and fertilizer used for farmland planting are seasonal and quantitative; Sewage cannot be used in farmland in a timely manner; therefore, more outlets are needed using sewage or biogas slurry.
针对秸秆和污水两种农业副产品,目前也有关于秸秆吸收污水用以发酵的实用新型专利。For the two agricultural by-products of straw and sewage, there are currently utility model patents on straw absorbing sewage for fermentation.
例如:实用新型专利,一种利用回收的污水喷淋秸秆的干式厌氧发酵装置(CN104328041 A)。该实用新型设计了一种内有喷淋头、排液管和出气口的厌氧发酵罐,内装有秸秆,利用污水回流泵将污水从发酵罐上方喷淋到秸秆上。利用秸秆和污水在厌氧条件下产生沼气。本实用新型是通过传统的厌氧发酵方法回收污水,优点是速度快,自动化控制;缺点是受到罐体的限制处理量有限,且造价昂贵,适用性较差,此外,该装置是以产生污水为目的的应用,对于养殖废液或生活污水,却无能为力。For example: a utility model patent, a dry anaerobic fermentation device that uses recycled sewage to spray straw (CN104328041 A). The utility model designs an anaerobic fermentation tank with a spray head, a liquid discharge pipe and an air outlet inside, and straw is installed inside, and the sewage is sprayed from the top of the fermentation tank onto the straw by using a sewage backflow pump. Using straw and sewage to generate biogas under anaerobic conditions. The utility model recovers sewage through the traditional anaerobic fermentation method, which has the advantages of fast speed and automatic control; the disadvantage is that the limited processing capacity is limited by the tank body, and the cost is expensive and the applicability is poor. In addition, the device is used to produce sewage For the purpose of application, there is nothing that can be done for aquaculture waste or domestic sewage.
再例如,为了防止污水利用中对环境产生的二次污染,实用新型专利,一种利用改性粉煤灰处理污水的方法(CN 102775026 A),改实用新型利用改性粉煤灰处理污水,首先将污水沼渣分开,然后将污水中加入一定量改性粉煤灰,充分反映后再经SBR曝气,降低污水中污染因子至达标排放。该方法属于污水净化实用新型,与本设计的基本原理差异较大。实用新型专利,秸秆与污水同步还田作业方法及机具(CN104255202 A),在田间内将作物秸秆和根茬完成破碎、并抛撒在田间上,将生物质厌氧发酵后产生的污水喷施在破碎的秸秆和根茬上,利用铧式犁进行土地平翻耕作,将破碎秸秆、根茬与污水一并掩埋覆盖在土壤内,最后对田间土地表面进行镇压压实平整作业。该实用新型属于田间利用,与污水回收利用差异较大。Another example, in order to prevent secondary pollution to the environment during the utilization of sewage, a utility model patent, a method for treating sewage by using modified fly ash (CN 102775026 A), was modified to use modified fly ash to treat sewage, First, the sewage biogas residue is separated, and then a certain amount of modified fly ash is added to the sewage, which is fully reflected and then aerated by SBR to reduce the pollution factor in the sewage to meet the discharge standard. This method belongs to the utility model of sewage purification, and the basic principle of this design is quite different. Utility model patent, straw and sewage synchronous returning operation method and equipment (CN104255202 A), the crop straw and root stubble are crushed in the field and scattered on the field, and the sewage produced after the anaerobic fermentation of biomass is sprayed on the On the broken straw and root stubble, the plow is used to level the land, and the broken straw, root stubble and sewage are buried and covered in the soil, and finally the surface of the field is compacted and leveled. This utility model belongs to field utilization, which is quite different from sewage recycling.
再例如,为了防止生活污水中的餐厨污水对环境产生的二次污染实用新型专利,一种吸附餐厨污水中油脂的秸秆处理方法(CN104445513A),将秸秆粉碎形成颗粒,添加絮凝剂并拌匀,制成秸秆絮凝颗粒;将秸秆絮凝颗粒投入餐厨污水中,使污水中有机物吸附到秸秆絮凝颗粒上形成附油颗粒;分离和收集附油颗粒,进行后续生物发酵处理。本实用新型解决了高浓度餐厨污水处理难度大、成本高,以及餐厨污水和秸秆单独发酵时营养均衡性差的问题。Another example, in order to prevent secondary pollution of kitchen sewage in domestic sewage, a utility model patent, a straw treatment method for absorbing grease in kitchen sewage (CN104445513A), crushes straw to form particles, adds flocculant and mixes The straw flocculation particles are made into straw flocculation particles; the straw flocculation particles are put into the kitchen sewage, so that the organic matter in the sewage is adsorbed on the straw flocculation particles to form oil-attached particles; the oil-attached particles are separated and collected for subsequent biological fermentation treatment. The utility model solves the problems that the treatment of high-concentration kitchen sewage is difficult and costly, and the nutritional balance is poor when the kitchen sewage and straw are separately fermented.
还有,一种农作物秸秆与污水污泥调理共焚烧处置资源化的方法(CN200910100285.5),该方法采取以下工艺:在常温下加入重量比例为1∶5~1∶20的秸秆粉末和含水率为重量百分比70-85%的污泥,再加入适量的重金属稳定剂搅拌调理,搅拌时间为15~30min,pH为6~9,经过洗涤、压滤,秸秆与污泥混合物的含水率降到50%~70%,低温烘干后,秸秆粉末与污泥混合物可以直接燃烧作为发热发电的煤替代能源,焚烧后的残渣和焚烧飞灰可作为水泥生料,生产生态水泥。本实用新型为秸秆与污泥共处置提供了一条合理途径,使废弃物在全过程实现了无害化、稳定化和资源化处理。In addition, there is a method of co-incineration, disposal and resource utilization of crop straw and sewage sludge (CN200910100285.5), which adopts the following process: adding straw powder and water-containing Sludge at a rate of 70-85% by weight, and then add an appropriate amount of heavy metal stabilizer to stir and condition. The stirring time is 15-30min, and the pH is 6-9. After washing and pressing, the water content of the mixture of straw and sludge will drop. To 50% to 70%, after low-temperature drying, the mixture of straw powder and sludge can be directly burned as coal alternative energy for heat generation, and the residue after incineration and incineration fly ash can be used as cement raw materials to produce ecological cement. The utility model provides a reasonable way for the co-disposal of straw and sludge, and realizes harmless, stable and resourceful treatment of waste in the whole process.
通过上述专利可见,面对大量秸秆、养殖污水、生活污水对环境的污染,人们虽然采取了不少方法和措施,但每种方法都有其局限性,劳动强度相对都比较大,缺乏一种自动化程度较高的农业机械。It can be seen from the above patents that in the face of environmental pollution caused by a large amount of straw, aquaculture sewage, and domestic sewage, although people have adopted many methods and measures, each method has its limitations, and the labor intensity is relatively large. Agricultural machinery with a high degree of automation.
发明内容Contents of the invention
本实用新型的目的在于,针对目前利用污水对秸秆捆发酵前预处理时缺乏一种自动化程度较高的农业机械设备,提供一种专用设备及其应用。The purpose of the utility model is to provide a special equipment and its application in view of the lack of an agricultural mechanical equipment with a high degree of automation when using sewage to pretreat straw bales before fermentation.
本实用新型的目的是这样实现的:The purpose of this utility model is achieved in that:
一种利用污水对秸秆捆发酵前预处理的装置,包括污水回收池和入料池,入料池一端设有浸泡槽,浸泡槽与入料池的交汇口设有一对疏导轮,浸泡槽上设有转压轮和依序等距排列的滚轴,浸泡槽的末端为平缓上升的斜坡,浸泡槽的宽度大于秸秆捆的宽度,浸泡槽的深度大于秸秆捆的高度,入料池和浸泡槽的水平面一致,位于紧邻浸泡槽中滚轴下缘的控制线,排水口位于浸泡槽末端的斜坡上,污水回收池的水位低于入料池,污水回收池的污水通过泵提升到入料池。A device for pretreatment of straw bales by using sewage before fermentation, including a sewage recovery tank and a feeding tank, one end of the feeding tank is provided with a soaking tank, and a pair of guide wheels are provided at the intersection of the soaking tank and the feeding tank, and the soaking tank It is equipped with turning and pressing wheels and rollers arranged equidistantly in sequence. The end of the soaking tank is a gently rising slope. The width of the soaking tank is greater than the width of the straw bale, and the depth of the soaking tank is greater than the height of the straw bale. The horizontal plane of the tank is consistent, located at the control line next to the lower edge of the roller in the soaking tank, the drain is located on the slope at the end of the soaking tank, the water level of the sewage recovery tank is lower than that of the feeding tank, and the sewage in the sewage recovery tank is lifted to the feeding tank by a pump pool.
进一步,本实用新型所述利用污水对秸秆捆发酵前预处理的装置中,入料池与浸泡槽交汇的一端呈八字形缩口,入料池通过缩口端部与浸泡槽对接;滚轴下方的浸泡槽长度至少为两米。Further, in the device for using sewage to pretreat straw bales before fermentation described in the utility model, the end where the feeding tank and the soaking tank meet is in a figure-eight constriction, and the feeding tank is docked with the soaking tank through the necking end; the roller The length of the soaking tank below is at least two meters.
进一步,本实用新型所述利用污水对秸秆捆发酵前预处理的装置中,所述的入料池为养殖场入料池;所述的一对疏导轮和转压轮均设有匹配的驱动电机。Further, in the device for pretreatment of straw bales by using sewage in the utility model before fermentation, the feed pool is a farm feed pool; motor.
进一步,本实用新型所述利用污水对秸秆捆发酵前预处理的装置中,入料池的入水口位于与浸泡槽交汇口的对面,进入入料池的污水推动秸秆捆向浸泡槽漂移。Further, in the device for pretreating straw bales with sewage before fermentation described in the utility model, the water inlet of the feeding tank is located opposite to the intersection with the soaking tank, and the sewage entering the feeding tank pushes the straw bundles to drift toward the soaking tank.
进一步,本实用新型所述利用污水对秸秆捆发酵前预处理的装置中,转压轮紧邻疏导轮,转压轮的外缘至少设置三组拨叉,它们均匀分布在转压轮周边,每组拨叉至少含有三个沿转压轮轴向均匀排列的叉头。Further, in the device for pretreating straw bales with sewage before fermentation described in the utility model, the turning and pressing wheel is adjacent to the dredging wheel, and at least three sets of shift forks are arranged on the outer edge of the turning and pressing wheel, which are evenly distributed around the turning and pressing wheel, each The group shift fork contains at least three forks that are evenly arranged along the axial direction of the rotary pressure wheel.
一种如本实用新型所述利用污水对秸秆捆发酵前预处理的装置的应用,其特征在于,将秸秆捆抛入入料池,漂浮至入料池与浸泡槽交汇口附近被一对疏导轮夹持,被转压轮周边的拨叉压入浸泡槽送到滚轴的下方,在滚轴强制压迫下秸秆捆被浸泡于水平面以下缓慢前行,抵达终点沿斜坡上升后回收,用于后期堆肥发酵。An application of a device for pretreatment of straw bales before fermentation by using sewage as described in the utility model, characterized in that the straw bales are thrown into the feeding pool and float to the vicinity of the intersection of the feeding pool and the soaking tank and are guided by a pair of dredges. The straw bundle is clamped by the roller, pressed into the soaking tank by the fork around the rotary pressure wheel and sent to the bottom of the roller. Under the forced pressure of the roller, the straw bundle is soaked below the water level and slowly moves forward. After reaching the end point, it rises along the slope and is recycled for use Post compost fermentation.
如本实用新型所述的应用,通过调节转压轮的转速,改变秸秆捆的浸泡时间和推行速度,使秸秆捆在泡槽中的滞留时间控制在30秒至2分钟之间。According to the application of the utility model, the residence time of the straw bundle in the bubble tank is controlled between 30 seconds and 2 minutes by adjusting the rotating speed of the turning wheel, changing the soaking time and pushing speed of the straw bundle.
本实用新型的优点在于,由于入料池一端设有浸泡槽,浸泡槽与入料池的交汇口设有一对疏导轮,浸泡槽上设有转压轮和依序等距排列的滚轴,浸泡槽的末端为平缓上升的斜坡,浸泡槽的宽度大于秸秆捆的宽度,浸泡槽的深度大于秸秆捆的高度,尤其是入料池和浸泡槽的水平面一致,位于浸泡槽的滚轴控制线,这些几何特征完全能够实现对秸秆捆完全浸泡。由于入料池中污水通过泵从污水回收池中提升后输入,由浸泡槽末端的斜坡上的排水口返回污水回收池,形成流动的活水,秸秆捆完全可以借助污水的流动方向,并可以通过泵的提升水量或转压轮的转速调节浸泡槽中秸秆捆的位移速度,满足预处理过程中对浸泡时间的要求。由于入料池与浸泡槽一端呈八字形缩口,缩口端部与浸泡槽对接,一方面可以对入料池中秸秆捆引导到浸泡槽,同时,可以增加入料池和浸泡槽交汇口的流速,利于秸秆捆被疏导轮夹持,再由转压轮周边的拨叉压入浸泡槽送到滚轴的下方。由于浸泡槽的末端为平缓上升的斜坡,浸泡后的秸秆捆可以借助水流和浮力,并在后续秸秆捆的推拥下沿斜坡向上位移。当疏导轮和转压轮均设有匹配的驱动电机,也可以与浸泡槽中的污水的流速共同对进入浸泡槽的秸秆捆提供缓慢位移的推力,有利于推动斜坡上的秸秆捆继续向上位移。The utility model has the advantages that, since one end of the feeding pool is provided with a soaking tank, a pair of dredging wheels are provided at the junction of the soaking tank and the feeding tank, and the soaking tank is provided with turning and pressing wheels and rollers arranged equidistantly in order, The end of the soaking tank is a gently rising slope. The width of the soaking tank is greater than the width of the straw bale, and the depth of the soaking tank is greater than the height of the straw bale. , these geometric features can fully realize the complete immersion of the straw bales. Since the sewage in the feeding tank is lifted from the sewage recovery tank by the pump and then input, it returns to the sewage recovery tank from the outlet on the slope at the end of the soaking tank to form flowing running water. The straw bales can completely rely on the flow direction of the sewage and can pass through The lifting water volume of the pump or the rotating speed of the rotary pressure wheel adjusts the displacement speed of the straw bales in the soaking tank to meet the soaking time requirement in the pretreatment process. Since one end of the feeding pool and the soaking tank has a figure-eight constriction, and the end of the constriction is connected with the soaking tank, on the one hand, the straw bales in the feeding tank can be guided to the soaking tank, and at the same time, the intersection of the feeding tank and the soaking tank can be increased The flow rate is high, which is beneficial to the straw bales being clamped by the dredging wheel, and then pressed into the soaking tank by the fork around the turning wheel and sent to the bottom of the roller. Since the end of the soaking tank is a gently rising slope, the soaked straw bales can move upward along the slope under the push of the subsequent straw bales by means of water flow and buoyancy. When the grooming wheel and the turning wheel are equipped with matching drive motors, they can also provide a slow displacement thrust for the straw bales entering the soaking tank together with the flow rate of the sewage in the soaking tank, which is conducive to pushing the straw bales on the slope to continue to move upwards .
附图说明Description of drawings
图1是本实用新型实施例的结构示意图。Fig. 1 is a schematic structural view of an embodiment of the utility model.
图2是图1的俯视图。FIG. 2 is a top view of FIG. 1 .
图中:1、入料池,2、浸泡槽,3、疏导轮,4、转压轮,5、滚轴,6、排水口,7、斜坡,8、拨叉,9、秸秆捆。In the figure: 1. Feeding pool, 2. Soaking tank, 3. Grooming wheel, 4. Turning and pressing wheel, 5. Roller, 6. Outlet, 7. Slope, 8. Shift fork, 9. Straw bundle.
具体实施方式detailed description
附图非限制性的公开了本实用新型实施例的基本结构,下面结合附图对本实用新型实施例作进一步的描述。The accompanying drawings disclose the basic structure of the embodiment of the utility model without limitation, and the embodiment of the utility model will be further described below in conjunction with the accompanying drawings.
由图1和图2可见,本实用新型包括污水注入口的入料池1,入料池1一端设有浸泡槽2,浸泡槽2与入料池1的交汇口设有一对疏导轮3,浸泡槽3上设有转压轮4和依序等距排列的滚轴5,浸泡槽2的末端为平缓上升的斜坡7,浸泡槽2的宽度大于秸秆捆9的宽度,浸泡槽2的深度大于秸秆捆9的高度,入料池池1和浸泡槽2的水平面一致,位于紧邻浸泡槽2中滚轴5下缘的控制线,排水口6位于浸泡槽2末端的斜坡7上。As can be seen from Fig. 1 and Fig. 2, the utility model comprises a feed tank 1 of a sewage injection port, one end of the feed tank 1 is provided with a soaking tank 2, and a pair of dredging wheels 3 are provided at the intersection of the soak tank 2 and the feed tank 1, Soaking tank 3 is provided with rotary press wheel 4 and rollers 5 arranged equidistantly in sequence. The end of soaking tank 2 is a slope 7 that rises gently. The width of soaking tank 2 is greater than the width of straw bundle 9, and the depth of soaking tank 2 is Greater than the height of the straw bale 9, the level of the feeding pool 1 and the soaking tank 2 is the same, and is located close to the control line of the lower edge of the roller 5 in the soaking tank 2, and the outlet 6 is located on the slope 7 at the end of the soaking tank 2.
在本实施例中,入料池1一端通过八字形缩口与浸泡槽2对接;滚轴5下方的浸泡槽2长度为2米。转压轮4紧邻疏导轮3,转压轮4的外缘设置多组拨叉8,它们均匀分布在转压轮4周边,每组拨叉8至少含有三个沿转压轮4轴向均匀排列的叉头。In this embodiment, one end of the feeding tank 1 is connected to the soaking tank 2 through a figure-eight constriction; the length of the soaking tank 2 below the roller 5 is 2 meters. The turning and pressing wheel 4 is adjacent to the dredging wheel 3, and the outer edge of the turning and pressing wheel 4 is provided with multiple sets of shift forks 8, which are evenly distributed around the turning and pressing wheel 4, and each set of shift forks 8 contains at least three Arranged forks.
具体实施时,还配一个污水回收池,污水回收池的水位低于入料池1,污水回收池中的污水通过泵提升到入料池1的入口,再由排水口6返回污水回收池形成循环活水,入料池1的入口位于浸泡槽2的对面。所述的一对疏导轮3和转压轮4均设有匹配的驱动电机。During specific implementation, a sewage recovery tank is also equipped, the water level of the sewage recovery tank is lower than the feed tank 1, and the sewage in the sewage recovery tank is lifted to the entrance of the feed tank 1 by a pump, and then returned to the sewage recovery tank by the outlet 6 to form Circulating running water, the entrance of the feeding pool 1 is located opposite to the soaking tank 2. The pair of dredging wheels 3 and the turning and pressing wheels 4 are all provided with matching drive motors.
本实用新型使用中,将秸秆捆9抛入入料池1后,在循环活水的推动下漂浮至入料池1,与由浸泡槽2交汇口附近由一对疏导轮3夹持,被转压轮3周边的拨叉8压入浸泡槽2送到滚轴5的下方,在滚轴5强制压迫下秸秆捆9被浸泡于水平面以下缓慢前行,抵达终点后沿斜坡7上升后回收,用于后期堆肥发酵。In the use of the utility model, after the straw bundle 9 is thrown into the feeding pool 1, it floats to the feeding pool 1 under the promotion of circulating running water, and is clamped by a pair of dredging wheels 3 near the intersection with the soaking tank 2, and is turned The shift fork 8 around the pressure wheel 3 is pressed into the soaking tank 2 and sent to the bottom of the roller 5. Under the forced pressure of the roller 5, the straw bundle 9 is soaked below the water level and slowly moves forward. After reaching the end point, it rises along the slope 7 and is recovered. For post-composting fermentation.
实际使用时,可以通过转压轮4设定的转速,以及泵的提升水量都可以驱使秸秆捆9在浸泡槽2中缓慢移动,秸秆捆9在浸泡槽2中的滞留时间可以控制在30秒至2分钟之间。In actual use, the rotating speed set by the rotary pressure wheel 4 and the lifting water volume of the pump can drive the straw bundle 9 to move slowly in the soaking tank 2, and the residence time of the straw bundle 9 in the soaking tank 2 can be controlled at 30 seconds to 2 minutes.
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Cited By (2)
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CN106479859A (en) * | 2016-09-23 | 2017-03-08 | 江苏省农业科学院 | The device and its application of using sewage to pretreat straw bales before fermentation |
CN109379996A (en) * | 2017-08-08 | 2019-02-26 | 四平市顺邦农机制造有限公司 | Baler with flusher |
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CN106479859A (en) * | 2016-09-23 | 2017-03-08 | 江苏省农业科学院 | The device and its application of using sewage to pretreat straw bales before fermentation |
CN109379996A (en) * | 2017-08-08 | 2019-02-26 | 四平市顺邦农机制造有限公司 | Baler with flusher |
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