CN101946742A - Method for processing and recycling aquaculture water in intensive culture pond - Google Patents
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Abstract
一种水产精养池塘养殖用水处理和循环利用方法,包括以下步骤:①增氧措施,将污染物集中到中央排污口;②在中央排水口设置排污管道连通到排水闸闸门口;③使用抽水设备从抽水管道抽取池塘污水;④采用泡沫分离器分离污水;⑤采用臭氧发生器处理清水中病原体,处理后循环进入池塘使用,污水收集,进行生化处理,达标后排放。实施本技术的精养池塘可减少养殖用水使用量70-80%,减少污水排放量,减轻环境污染,提高养殖产量,而且有利于切断病原体的水平传播途径,可用于鱼类,对虾、罗氏沼虾和蟹类等水产经济品种精养池塘养殖过程养殖过程的水处理和循环利用,有利于水产养殖业的健康和可持续发展,具有很高的使用价值。
A method for treating and recycling water in aquaculture intensive ponds, comprising the following steps: ①Aeration measures to concentrate pollutants to a central sewage outlet; ②Set a sewage pipe at the central drainage outlet to connect to the gate of the drainage gate; ③Use water pumping The equipment extracts pond sewage from the pumping pipeline; ④uses a foam separator to separate the sewage; ⑤uses an ozone generator to treat pathogens in clean water, and after treatment, it circulates into the pond for use, and the sewage is collected for biochemical treatment and discharged after reaching the standard. The intensive culture ponds implementing this technology can reduce the consumption of breeding water by 70-80%, reduce sewage discharge, reduce environmental pollution, increase breeding production, and help cut off the horizontal transmission of pathogens, and can be used for fish, prawns, and marshes. The water treatment and recycling of aquatic economic species such as shrimps and crabs in the intensive pond breeding process are conducive to the healthy and sustainable development of the aquaculture industry and have high use value.
Description
技术领域technical field
本发明为水产养殖领域,涉及一种水产精养池塘养殖用水处理和循环利用方法。The invention belongs to the field of aquaculture, and relates to a water treatment and recycling method for intensive aquaculture pond cultivation.
技术背景technical background
我国是全球水产业第一大国,2002年水产品产量达4561.8万吨,占全球产量40%左右,其中海淡水养殖产量2907万吨,占总产量的64%,约占全球养殖产量近60%。对虾养殖业是我国海水养殖支柱产业,1992年养殖面积超过14万公顷,产量22万吨,平均产量每公顷1.57吨。1993年开始对虾养殖产量开始下滑,1995年我国只有5万吨,平均单产0.36吨/公顷。1993年至1995年间,对虾养殖业年直接经济损失达30亿元。病害成为我国对虾养殖业最重要的制约因素。自1992年在福建和粤东暴发对虾病毒病,尤其是白斑综合症(white spot syndrome,WSS),1993年流行全国以来,WSS已成为对虾养殖业最严重的疾病。1993年至1995年三年间我国对虾养殖池塘WSS发生率90%以上,发病虾池对虾死亡率接近100%。my country is the largest country in the world's aquaculture industry. In 2002, the output of aquatic products reached 45.618 million tons, accounting for about 40% of the global output, of which the output of sea and freshwater aquaculture was 29.07 million tons, accounting for 64% of the total output, accounting for nearly 60% of the global aquaculture output . Shrimp aquaculture is the pillar industry of marine aquaculture in my country. In 1992, the aquaculture area exceeded 140,000 hectares, and the output was 220,000 tons, with an average output of 1.57 tons per hectare. Since 1993, the output of shrimp farming began to decline. In 1995, my country had only 50,000 tons, with an average yield of 0.36 tons/ha. From 1993 to 1995, the annual direct economic loss of the shrimp farming industry reached 3 billion yuan. Diseases have become the most important restrictive factors for the shrimp farming industry in my country. Since the outbreak of shrimp virus diseases in Fujian and eastern Guangdong in 1992, especially white spot syndrome (white spot syndrome, WSS), since it became popular in the whole country in 1993, WSS has become the most serious disease in the shrimp farming industry. During the three years from 1993 to 1995, the occurrence rate of WSS in shrimp culture ponds in my country was over 90%, and the mortality rate of shrimp in affected shrimp ponds was close to 100%.
我国主要水产经济品种包括对虾、鱼类等养殖生产以池塘养殖为主体,采用“三塘合一”的养殖模式,对虾、鱼类的摄食、排泄和活动在同一个池塘里完成。而传统对虾、鱼类养殖模式是通过潮差大量换水的方式调控养殖池塘水质,一方面不能依据养殖状况进行全人工调控水质,另一方没有经过处理水进行水体交换也加剧了疾病的传播和流行。养殖水质全人工调控技术的缺乏,限制了水产养殖养殖业的健康发展。高位池和地膜池等精养模式主要采用沙滤,或者沙滤加中间蓄水池消毒处理病原,需要中间蓄水池,浪费大量人力、物力和财力,在养殖过程中主要采用微生态制剂和化学药品处理,成本高,而且化学药品容易造成残留,同时养殖过程中需要大量换水。The main aquaculture production of my country's main aquatic economic species including prawns and fishes is pond aquaculture, adopting the "three ponds in one" farming model, and the feeding, excretion and activities of prawns and fishes are completed in the same pond. The traditional prawn and fish culture mode regulates the water quality of the culture pond through a large amount of tidal range water exchange. On the one hand, the water quality cannot be fully artificially adjusted according to the culture status, and on the other hand, the water body exchange without treated water also exacerbates the spread of diseases and diseases. Popularity. The lack of fully artificial control technology for aquaculture water quality limits the healthy development of the aquaculture industry. Intensive farming models such as high level ponds and plastic film ponds mainly use sand filtration, or sand filtration plus intermediate reservoirs to disinfect and treat pathogens, requiring intermediate reservoirs, which wastes a lot of manpower, material and financial resources. Microecological preparations and The cost of chemical treatment is high, and chemicals are easy to cause residues. At the same time, a large number of water changes are required during the breeding process.
目前管理良好的集约化、半集约化对虾养殖模式,使用营养配方合理的人工配合饲料进行饲喂养殖对虾,饲料系数平均约为1.3,即养成1kg的成品对虾需要投入1.3kg饲料。而1kg对虾仅有262.75g干物质,1.3kg配合饲料有1144g干物质。以饲料系数1.3计算,每养成1kg对虾,有881.25g的饲料干物质变成了代谢产物进入了养殖水体环境中。据研究,当平均温度为28℃时,从体重0.02g的南美白对虾虾苗养成至体重20g的成虾,养殖期间每个体的累积排泄和排出氮1086.3mg,累积排泄和排出磷228.7mg。集约化、半集约化养殖模式进行对虾养殖生产,通常一年养殖2茬,每茬养殖90-130天,前期30天内基本不换水,视情况适量添水,保持水深120-180cm。中期开始适量换水,一般每7-10天换水1次,每次换水20%-30%。若以平均水深150cm计,每茬养殖110天,中后期每8.5天换水25%,则每公顷虾池每年养殖排放水量为1.02×105m3,而2008年我国对虾养殖面积为40万公顷左右,则当年向环境中所排放养殖废水共计约4.08×1010m3。因此,综合分析可知,对虾养殖过程中不仅水资源消耗巨大,而且向环境所排放出的废水、废物数量惊人,影响了对虾养殖业的健康可持续发展。The current well-managed intensive and semi-intensive shrimp farming models use artificial compound feeds with reasonable nutritional formulas to feed farmed shrimps. The average feed coefficient is about 1.3, that is, 1.3 kg of feed is required to grow 1 kg of finished shrimps. While 1kg of prawns has only 262.75g of dry matter, 1.3kg of compound feed has 1144g of dry matter. Calculated with a feed factor of 1.3, for every 1kg of prawns grown, 881.25g of dry matter in the feed will be transformed into metabolites and enter the aquaculture water environment. According to research, when the average temperature is 28°C, from the growth of Penaeus vannamei juveniles with a weight of 0.02g to adult shrimp with a weight of 20g, the cumulative excretion and discharge of nitrogen per body during the culture period is 1086.3mg, and the cumulative excretion and discharge of phosphorus is 228.7mg . Intensive and semi-intensive farming models are used for shrimp farming. Usually, 2 crops are cultured a year, and each crop is cultivated for 90-130 days. The water is basically not changed in the first 30 days. Water is added appropriately according to the situation, and the water depth is maintained at 120-180cm. In the mid-term, start to change the water in an appropriate amount, generally every 7-10 days, and change the water 20%-30% each time. If the average water depth is 150cm, each crop is cultivated for 110 days, and the water is changed every 8.5 days in the middle and late stages by 25%, then the annual water discharge per hectare of shrimp ponds is 1.02×10 5 m 3 , and in 2008, the shrimp farming area in China was 400,000 Hectares, the total amount of aquaculture wastewater discharged to the environment in that year was about 4.08×10 10 m 3 . Therefore, a comprehensive analysis shows that not only the consumption of water resources in the process of shrimp farming is huge, but also the amount of waste water and waste discharged into the environment is astonishing, which affects the healthy and sustainable development of the shrimp farming industry.
发明内容Contents of the invention
本发明的目的是提供一种水产精养池塘养殖用水处理和循环利用方法,是通过物理的、化学、管理等结合起来的综合处理养殖用水达到循环使用的技术方法,能有效去除养殖水中溶解态和悬浮态污染物的,可以将蛋白质等有机物在未被矿化成氨化物和其他有毒物质前就已被去除,避免了有毒物质在水体中积累,而且可向养殖水体提供所必需的溶解氧,对维护养殖水体生态环境有良好作用到减少鱼虾养殖用水使用量,零交换,隔绝外界病原体的进入,减少病害的发生,减轻池塘有机负载,实施本技术鱼虾养殖用水处理量60-100m3/h,可减少养殖用水使用量70-80%,减少环境污染,提高养殖产量,而且水生生物生长快,规格整齐,养殖产量高。可用于鱼类,对虾、罗氏沼虾和蟹类等水产经济品种精养池塘养殖过程养殖用水的处理和循环利用,有利于水产养殖业的健康和可持续发展,具有很高的使用价值。The purpose of the present invention is to provide a method for the treatment and recycling of aquaculture water in intensive aquaculture ponds, which is a technical method for comprehensively treating aquaculture water through physical, chemical, management, etc. to achieve recycling, and can effectively remove dissolved substances in aquaculture water. and suspended pollutants, organic matter such as protein can be removed before being mineralized into ammonia and other toxic substances, avoiding the accumulation of toxic substances in the water body, and can provide the necessary dissolved oxygen to the aquaculture water body, It has a good effect on maintaining the ecological environment of aquaculture water, reducing the amount of water used for fish and shrimp aquaculture, zero exchange, isolating the entry of external pathogens, reducing the occurrence of diseases, reducing the organic load of ponds, and implementing this technology to treat fish and shrimp aquaculture water of 60-100m 3 /h, can reduce the consumption of aquaculture water by 70-80%, reduce environmental pollution, increase aquaculture output, and the aquatic organisms grow fast, the specifications are neat, and the aquaculture output is high. It can be used for the treatment and recycling of aquaculture water in the process of intensive pond aquaculture of fish, prawns, giant giant rosenbergii and crabs and other aquatic economic species, which is conducive to the healthy and sustainable development of aquaculture industry and has high use value.
本发明包括以下步骤:设置增氧机增氧,满足水产经济动物营养需求,同时要求池塘水要形成环流,有利于溶解和悬浮的污染物集中到中央排污口,便于收集;在中央排水区设置的PVC管道排污管道连通到排水闸闸门口;在闸门口设置一个PVC弯头,上插PVC管道,采用水泵通过抽水管从排污管抽水到泡沫分离器;采用泡沫分离器进行泡沫分离,泡沫分离器设有排水口,清水进入臭氧发生器,污水进入排水闸门,经排水道进入污水处理设施,经过生化处理达标后排放;采用臭氧发生器处理清水中的病原生物,臭氧发生器设有清水口,清水进入养殖池塘后循环利用。The present invention includes the following steps: setting up an aerator to increase oxygen to meet the nutritional needs of aquatic economic animals, and at the same time requiring pond water to form a circulation, which is conducive to the concentration of dissolved and suspended pollutants into the central sewage outlet for easy collection; The sewage pipe of the PVC pipe is connected to the gate of the drainage gate; a PVC elbow is set at the gate, and the PVC pipe is inserted up, and the water pump is used to pump water from the sewage pipe to the foam separator through the suction pipe; the foam separator is used for foam separation, and the foam separation The device is equipped with a drainage port, clean water enters the ozone generator, sewage enters the drainage gate, enters the sewage treatment facility through the drainage channel, and is discharged after biochemical treatment reaches the standard; the ozone generator is used to treat pathogenic organisms in the clean water, and the ozone generator is equipped with a clean water port. The clean water is recycled after entering the aquaculture pond.
本发明处理鱼虾养殖水,可减少养殖用水使用量70-80%,减轻环境污染,提高养殖产量,而且水生生物生长快,规格整齐,养殖产量高。可用于鱼类,对虾、罗氏沼虾和蟹类等水产经济品种精养池塘养殖过程养殖用水的处理和循环利用,有利于水产养殖业的健康和可持续发展,具有很高的使用价值。The method for treating fish and shrimp culture water in the invention can reduce the consumption of culture water by 70-80%, reduce environmental pollution, improve culture yield, and the aquatic organisms grow fast, have neat specifications and high culture yield. It can be used for the treatment and recycling of aquaculture water in the process of intensive pond aquaculture of fish, prawns, giant giant rosenbergii and crabs and other aquatic economic species, which is conducive to the healthy and sustainable development of aquaculture industry and has high use value.
附图说明Description of drawings
图1是本发明结构示意图。Fig. 1 is a schematic diagram of the structure of the present invention.
具体实施方式Detailed ways
实施例1Example 1
①2个面积为0.23hm2,池深为2.3m,水深1.6m的凡纳滨对虾冬棚精养池塘,放苗密度300万尾/hm2,产量为30000-37500kg/hm2,每个池塘配备底部充氧设施,同时在池塘四角配备4-6台水车式增氧机1,养殖30天以后,开动水车式增氧机1形成环流,将污染物集中到中央排污口2;①Two ponds with an area of 0.23hm 2 , a pond depth of 2.3m, and a water depth of 1.6m for intensive culture of Litopenaeus vannamei in winter sheds, with a stocking density of 3 million fish/hm 2 and a yield of 30,000-37,500kg/hm 2 . Equipped with bottom oxygenation facilities, and equipped with 4-6 waterwheel aerators 1 at the four corners of the pond. After 30 days of breeding, the waterwheel aerator 1 is turned on to form a circulation and concentrate pollutants to the
②每个池塘在中央排污口2设置内径为26.4cm的PVC管道排污管3连通到排水闸闸门口4;在闸门口4设置一个内径为26.4cm的PVC弯头,上插内径为26.4cm的PVC管道;②In each pond, a PVC pipe with an inner diameter of 26.4cm is installed at the
③在2个池塘的排水闸门附近堤坝上,配备功率为3kw,扬程为5m左右的抽水泵6一台,从PVC管道中抽取池中水进入泡沫分离器4,抽水软管共用,消毒后可以自由转换到每个池塘。③ On the dams near the drainage gates of the two ponds, 6 sets of water pumps with a power of 3kw and a head of about 5m are equipped. The water in the pool is drawn from the PVC pipe and enters the foam separator 4. Freely transition to each pond.
④在2个池塘的排水闸门附近堤坝上,配备功率为3kw的泡沫分离器7一台和臭氧发生器8一台,泡沫分离器7设有排水口9,泡沫分离器7分离污水,采用臭氧发生器8处理清水中病原体,清水经清水口10然后循环流回池塘使用,分离的污水则收集到集污池经过生化处理达标后排放。效率为60-100m3/h;一般5-7天,处理时间为24-48小时,视水质污染情况调整处理时间,水质污染污染严重可以增加处理时间,水质状况良好可以减少处理时间,一般池塘养殖水可保持80-100天稳定,不用从外海提水交换,减少白斑综合症病毒等病原体的水平传播途径,减少病害的发生。而且水温稳定,避免交换外界海水,引起水温变化,对虾产生应激发应,发生意外,排水软管共用,消毒后可以自由转换到每个池塘。④ On the dams near the drainage gates of the two ponds, a foam separator 7 with a power of 3kw and an ozone generator 8 are equipped. The generator 8 treats pathogens in the clear water, and the clear water passes through the clear water outlet 10 and then circulates back to the pond for use. The separated sewage is collected in the sewage collection tank and discharged after biochemical treatment up to standard. The efficiency is 60-100m 3 /h; generally 5-7 days, the treatment time is 24-48 hours, the treatment time is adjusted according to the water pollution situation, the treatment time can be increased if the water pollution is serious, and the treatment time can be reduced if the water quality is good. Generally, ponds The aquaculture water can be kept stable for 80-100 days, and there is no need to exchange water from the open sea, reducing the horizontal transmission of pathogens such as white spot syndrome virus and reducing the occurrence of diseases. Moreover, the water temperature is stable, avoiding the exchange of external seawater, causing changes in water temperature, stress on shrimp, and accidents. The drainage hose is shared, and it can be freely switched to each pond after disinfection.
实施例2Example 2
①4个面积分别为0.23hm2,池深为2.5m,水深2.0m的斜带石斑鱼精养池塘,放苗密度3万尾/hm2,产量为15000kg/hm2左右,在每个池塘四角配备4-6台水车式增氧机,养殖60天以后,开动水车式增氧机1形成环流,将污染物集中到中央排污口2;① 4 intensive culture ponds with an area of 0.23hm 2 , a pool depth of 2.5m, and a water depth of 2.0m, with a stocking density of 30,000 fish/hm 2 and a yield of about 15,000kg/hm 2 . The four corners are equipped with 4-6 water wheel aerators. After 60 days of breeding, the water wheel aerator 1 is turned on to form a circulation, and the pollutants are concentrated to the
②每个池塘在中央排污口2设置内径为26.4cm的PVC管道排污管3连通到排水闸闸门口4;在闸门口4设置一个内径为26.4cm的PVC弯头,上插内径为26.4cm的PVC管道;②In each pond, a PVC pipe with an inner diameter of 26.4cm is installed at the
③在4个池塘的排水闸门附近堤坝上,配备功率为3kw,扬程为5m左右的抽水泵3一台,从PVC管道中抽取池中水进入泡沫分离器7,抽水软管共用,消毒后可以自由转换到每个池塘。③On the dams near the drainage gates of the four ponds, 3 pumps with a power of 3kw and a lift of about 5m are equipped to pump water from the PVC pipes into the foam separator 7. The pumping hoses are shared and can be used after disinfection. Freely transition to each pond.
④在4个池塘的排水闸门附近堤坝上,配备功率为3kw的泡沫分离器7一台和臭氧发生器8一台,泡沫分离器7设有排水口9,泡沫分离器7分离污水,采用臭氧发生器8处理清水中病原体,清水经清水口10然后循环流回池塘使用,分离的污水则收集到集污池排放。效率为60-100m3/h;一般7-10天,开动24-48小时,视水质污染情况调整使用时间,水质污染污染严重可以增加处理时间,水质状况可以减少处理时间,一般池塘养殖水可保持240-300天稳定,不用从外海提水交换,可减少神经坏死病毒等病原体的水平传播途径,减少病害的发生。而且水温稳定,避免交换外界海水,引起水温变化,造成鱼产生应激发应,发生病害和意外。排水软管共用,消毒后可以自由转换到每个池塘。④ On the dams near the drainage gates of the four ponds, a foam separator 7 with a power of 3kw and an ozone generator 8 are equipped. The foam separator 7 is provided with a water outlet 9. The generator 8 treats pathogens in the clear water, and the clear water passes through the clear water outlet 10 and then circulates back to the pond for use, and the separated sewage is collected into the sewage collection tank for discharge. The efficiency is 60-100m 3 /h; generally 7-10 days, start for 24-48 hours, adjust the use time according to the water pollution situation, if the water pollution is serious, the treatment time can be increased, and the water quality can reduce the treatment time. Keeping it stable for 240-300 days without extracting water from the open sea for exchange can reduce the horizontal transmission of pathogens such as nerve necrosis virus and reduce the occurrence of diseases. Moreover, the water temperature is stable, avoiding the exchange of external seawater, causing changes in water temperature, causing stress reactions in fish, diseases and accidents. Drainage hoses are shared and can be freely switched to each pond after disinfection.
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Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102342259A (en) * | 2011-09-06 | 2012-02-08 | 叶勤 | Water circulation treatment system of outdoor high-level shrimp tank |
| CN102805048A (en) * | 2012-08-17 | 2012-12-05 | 中国水产科学研究院渔业机械仪器研究所 | Air inflating, pollutant discharging and water injecting device for net cage culture |
| CN103911287A (en) * | 2014-03-12 | 2014-07-09 | 广东美瑞科海洋生物科技有限公司 | Industrial culturing method of microbial biomass, and system used for realizing industrial culturing method |
| CN104585113A (en) * | 2014-12-30 | 2015-05-06 | 浙江海洋学院 | Super-intensive breeding device with low circulation rate |
| CN104839079A (en) * | 2015-06-09 | 2015-08-19 | 广东海洋大学 | Method and facility for cultivating parents of Sillago sihama indoors on large scale via prawn cultivation wastewater |
| CN104872027A (en) * | 2015-06-09 | 2015-09-02 | 广东海洋大学 | Facility and method for indoor large-scale cultivation of larvae and juveniles of Sillago sihama using prawn cultivation wastewater |
| CN110565788A (en) * | 2019-09-29 | 2019-12-13 | 唐海波 | pond water changing device |
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2010
- 2010-01-29 CN CN2010101054354A patent/CN101946742A/en active Pending
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102342259A (en) * | 2011-09-06 | 2012-02-08 | 叶勤 | Water circulation treatment system of outdoor high-level shrimp tank |
| CN102342259B (en) * | 2011-09-06 | 2013-03-27 | 叶勤 | Water circulation treatment system of outdoor high-level shrimp tank |
| CN102805048A (en) * | 2012-08-17 | 2012-12-05 | 中国水产科学研究院渔业机械仪器研究所 | Air inflating, pollutant discharging and water injecting device for net cage culture |
| CN103911287A (en) * | 2014-03-12 | 2014-07-09 | 广东美瑞科海洋生物科技有限公司 | Industrial culturing method of microbial biomass, and system used for realizing industrial culturing method |
| CN104585113A (en) * | 2014-12-30 | 2015-05-06 | 浙江海洋学院 | Super-intensive breeding device with low circulation rate |
| CN104839079A (en) * | 2015-06-09 | 2015-08-19 | 广东海洋大学 | Method and facility for cultivating parents of Sillago sihama indoors on large scale via prawn cultivation wastewater |
| CN104872027A (en) * | 2015-06-09 | 2015-09-02 | 广东海洋大学 | Facility and method for indoor large-scale cultivation of larvae and juveniles of Sillago sihama using prawn cultivation wastewater |
| CN110565788A (en) * | 2019-09-29 | 2019-12-13 | 唐海波 | pond water changing device |
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