CN105706996A - Desilting method for aquaculture pond organisms - Google Patents

Desilting method for aquaculture pond organisms Download PDF

Info

Publication number
CN105706996A
CN105706996A CN201610110782.3A CN201610110782A CN105706996A CN 105706996 A CN105706996 A CN 105706996A CN 201610110782 A CN201610110782 A CN 201610110782A CN 105706996 A CN105706996 A CN 105706996A
Authority
CN
China
Prior art keywords
water
carp
grams
aquaculture
water body
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201610110782.3A
Other languages
Chinese (zh)
Inventor
雷曼红
姜仁军
陶大勇
王选东
王时伟
任道全
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tarim University
Original Assignee
Tarim University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tarim University filed Critical Tarim University
Priority to CN201610110782.3A priority Critical patent/CN105706996A/en
Publication of CN105706996A publication Critical patent/CN105706996A/en
Pending legal-status Critical Current

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01KANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
    • A01K63/00Receptacles for live fish, e.g. aquaria; Terraria
    • A01K63/04Arrangements for treating water specially adapted to receptacles for live fish

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Environmental Sciences (AREA)
  • Marine Sciences & Fisheries (AREA)
  • Animal Husbandry (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Farming Of Fish And Shellfish (AREA)

Abstract

本发明公开了一种养殖池塘生物清淤的方法,包括如下步骤:当养殖池塘的水位达到100cm后,每亩投放规格为500克的鲢鱼和鳙鱼各为100尾,规格为30克的鲤鱼200尾,规格为30克的鲫鱼800尾;将枯草芽孢杆菌、酵母菌、光合细菌液体菌液按体积比例为1?3∶1?2∶1?3的比例混合成混合菌液,投放到养殖水体,投放量为养殖水体体积的0.1‰?0.2‰,以后每次投放菌液处理水质前,测定水质TN、TP及COD指标,根据监测结果确定连续投放混合菌液处理养殖水体时间。本发明清淤彻底,实现了节水养殖,增加了养殖水域的有效生物量,提高了经济效益,产量可提升50%,减低饵料系数,节约养殖成本,减少了疾病了发生。The invention discloses a method for biological dredging of a culture pond, which comprises the following steps: when the water level of the culture pond reaches 100 cm, 100 silver carp and bighead carp with a specification of 500 grams and 100 bighead carp with a specification of 30 grams are put in per mu. 200 carp, 800 crucian carp with a specification of 30 grams; mix Bacillus subtilis, yeast, and photosynthetic bacteria in a volume ratio of 1?3:1?2:1?3 to form a mixed bacterial liquid, and put it in To the aquaculture water body, the dosage is 0.1‰ to 0.2‰ of the volume of the aquaculture water body. Before each time the bacterial solution is used to treat the water quality, the water quality TN, TP and COD indicators are measured, and the time for continuous injection of the mixed bacterial solution to treat the aquaculture water body is determined according to the monitoring results. The invention thoroughly desilts, realizes water-saving breeding, increases the effective biomass of the breeding water area, improves economic benefits, increases the output by 50%, reduces the bait coefficient, saves the breeding cost, and reduces the occurrence of diseases.

Description

一种养殖池塘生物清淤的方法A method for biological dredging of aquaculture ponds

技术领域technical field

本发明涉及养殖池塘清淤领域,具体涉及一种养殖池塘生物清淤的方法。The invention relates to the field of dredging ponds, in particular to a biological dredging method for ponds.

背景技术Background technique

目前,我国池塘养殖水体富营养化现象普遍发生,淤泥过厚、水味腥臭、有害藻类过度繁殖、生物多样性下降,严重威胁鱼类健康,影响鱼的产量与品质。近年来,虽然在养殖水体中使用各种微生物以及底排污等措施来改善水质,但是从富营养化程度来看,水体各营养状态指数比其以前并未下降。可见养殖水体一旦形成富营养化就很难彻底恢复。At present, the phenomenon of eutrophication in pond aquaculture water is common in our country. Excessive silt, foul smell, excessive reproduction of harmful algae, and decline in biodiversity seriously threaten the health of fish and affect the yield and quality of fish. In recent years, although measures such as various microorganisms and bottom sewage have been used in aquaculture water bodies to improve water quality, from the perspective of eutrophication, the nutrient status index of water bodies has not declined compared to before. It can be seen that once the aquaculture water body becomes eutrophic, it is difficult to completely recover.

消除养殖池塘水体中的氮、磷以及有机负荷才能从根本上解决水体富营养化。目前,国内外常用物理、化学、生物方法或这几种方法相结合来处理内源性污染。底排污的方法需要大量的水资源补充,在我国西部地区,水资源严重缺乏;机械清淤的方法成本过高,且对防止水体富营养化只能起到延缓作用,从根本上解决不了养殖池塘水质逐渐恶化的问题。微生物处理的方法由于成本低、无二次污染等特点,是养殖池塘常用的方法,但是养殖池塘每天投饵量大,鱼类排泄的废物多,还有众多其它影响因素,其治理方法并不能在人为控制条件下进行。Elimination of nitrogen, phosphorus and organic loads in the water body of aquaculture ponds can fundamentally solve the eutrophication of the water body. At present, physical, chemical, biological methods or a combination of these methods are commonly used at home and abroad to deal with endogenous pollution. The method of bottom sewage discharge requires a large amount of water resources to be replenished. In the west of China, water resources are seriously lacking; the cost of mechanical dredging is too high, and it can only delay the prevention of eutrophication in water bodies, and cannot fundamentally solve the problem of aquaculture. Pond water quality is gradually deteriorating. Due to the low cost and no secondary pollution, the method of microbial treatment is a commonly used method in aquaculture ponds. However, the daily feeding amount of aquaculture ponds is large, the waste excreted by fish is large, and there are many other influencing factors. The treatment method cannot carried out under human control.

目前有人利用常用的几种微生物净化养殖水体,通过微生物对造成富营养化的某种或几种有机物污染物的吸收利用,控制藻类过度繁殖,消除底泥,但微生物对内源性有机污染物的降解速度远远小于养殖生物每天排放的粪便。在中国专利公报上曾公开了一种“一种利用微生物有效控制藻类水华的方法”的发明创造,其申请号201110021920.8,该方法利用芽孢杆菌、不动杆菌、反硝化细菌、光合细菌菌液按比例混合投放到养殖池塘,对养殖池塘水体各污染物的去除率分别是:TN为83.1%,TP为92.1%,COD为79.1%,Chla为90.1%,但在集约化养殖池塘的清淤速度还是显慢了些。。At present, some people use several commonly used microorganisms to purify aquaculture water, and control the overgrowth of algae and eliminate sediment through the absorption and utilization of certain or several organic pollutants that cause eutrophication. The degradation rate is far less than the feces discharged by farmed organisms every day. In the Chinese Patent Bulletin, an invention of "a method for effectively controlling algae blooms by using microorganisms" was disclosed. Its application number is 201110021920.8. Mixed in proportion and put into the culture pond, the removal rate of each pollutant in the culture pond water body is respectively: TN is 83.1%, TP is 92.1%, COD is 79.1%, Chla is 90.1%, but in the dredging of intensive culture pond The speed is still slow. .

发明内容Contents of the invention

为解决上述问题,本发明提供了一种养殖池塘生物清淤的方法,利用由四川华腾水产生化科技开发有限公司提供的的微生物和底栖鱼类用来养殖池塘的清淤,可以克服上述缺点,更适用于精养殖池塘的清淤。In order to solve the above problems, the invention provides a method for biological dredging of aquaculture ponds, utilizing microorganisms and benthic fish provided by Sichuan Huateng Water Production Technology Development Co., Ltd. for dredging ponds, which can overcome the above-mentioned problems. Disadvantages, it is more suitable for dredging ponds.

为实现上述目的,本发明采取的技术方案为:In order to achieve the above object, the technical scheme that the present invention takes is:

一种养殖池塘生物清淤的方法,包括如下步骤:A method for biological dredging of breeding ponds, comprising the steps of:

S1、当养殖池塘的水位达到100cm后,每亩投放规格为500克的鲢鱼和鳙鱼各为100尾,规格为30克的鲤鱼200尾,规格为30克的鲫鱼800尾;S1, when the water level of the breeding pond reaches 100cm, put in 100 tails of silver carp and bighead carp with a specification of 500 grams per mu, 200 tails of carp with a specification of 30 grams, and 800 tails of crucian carp with a specification of 30 grams;

S2、将枯草芽孢杆菌、酵母菌、光合细菌液体菌液按体积比例为1-3∶1-2∶1-3的比例混合成混合菌液,投放到养殖水体,投放量为养殖水体体积的0.1‰-0.2‰,其中,水温20℃-25℃,每隔15天投放混合菌液1次,投放量为养殖水体体积的0.2‰,水温25℃以上每隔7天投放混合菌液1次,投放量为养殖水体体积的0.1‰,以后每次投放菌液处理水质前,测定水质TN、TP及COD指标,根据监测结果确定连续投放混合菌液处理养殖水体时间。S2. Mix Bacillus subtilis, saccharomyces, and photosynthetic bacteria liquid bacteria liquid in a volume ratio of 1-3:1-2:1-3 to form a mixed bacterial liquid, and put it into the aquaculture water body, and the amount of input is 1/2 of the volume of the aquaculture water body 0.1‰-0.2‰, among them, when the water temperature is 20°C-25°C, the mixed bacterial solution is added once every 15 days, and the dosage is 0.2‰ of the volume of the aquaculture water body, and the mixed bacterial solution is added once every 7 days when the water temperature is above 25°C , the dosage is 0.1‰ of the volume of the aquaculture water body. Before each time the bacterial solution is used to treat the water quality, the water quality TN, TP and COD indicators are measured. According to the monitoring results, the time for continuous injection of the mixed bacterial solution to treat the aquaculture water body is determined.

本发明具有以下有益效果:The present invention has the following beneficial effects:

1.清淤彻底。利用几种菌混合液、滤食性鱼类及底栖鱼类,经过10-12个月,池塘淤泥由50-110cm降低到20cm以下,甚至无淤泥,节约了机械清淤的成本。1. Thorough dredging. Using several kinds of bacterial mixture, filter-feeding fish and benthic fish, after 10-12 months, the pond silt is reduced from 50-110cm to below 20cm, or even no silt, which saves the cost of mechanical dredging.

实现了节水养殖。1个养殖周期内,在水温不超过25℃的情况下,实现了只进水、不排水的养殖模式,在高温季节,20天换一次水,换水量只为10%。即使在我国西部水源紧缺地区,也可以实现高产。Water-saving farming has been realized. In one breeding cycle, when the water temperature does not exceed 25°C, the breeding mode of only water intake and no drainage is realized. In the high temperature season, the water is changed every 20 days, and the water change volume is only 10%. Even in water-scarce areas in western my country, high yields can be achieved.

增加了养殖水域的有效生物量,提高了经济效益。淤泥过厚,池塘老化,养殖水位下降,鱼的单位产量降低,通过生物清淤,产量可提升50%。The effective biomass of the breeding water area is increased, and the economic benefit is improved. The silt is too thick, the pond is aging, the water level of the culture drops, and the unit output of fish decreases. Through biological dredging, the output can be increased by 50%.

降低了饵料系数。普通的养殖模式,3+草鱼的饵料系数通常为2.3-2.5,采用这种养殖模式,饵料系数可达2.0,节约养殖成本,提高鱼产量。Reduced bait coefficient. In the common breeding mode, the bait coefficient of 3 + grass carp is usually 2.3-2.5. With this breeding mode, the bait coefficient can reach 2.0, which saves the cost of breeding and increases the fish output.

减少了疾病发生。普通养殖模式中,鱼类的肝胆综合症很常见,每年因肝胆综合症和水质恶化引起翻塘的事件很常见。利用微生物、滤食性鱼类和底栖鱼类进行清淤后,即使鱼类出现严重浮头,鱼类死亡数也不会超过1‰。Reduced disease occurrence. In the common farming mode, hepatobiliary syndrome of fish is very common, and it is very common to overturn ponds every year due to hepatobiliary syndrome and water quality deterioration. After dredging with microorganisms, filter-feeding fish and benthic fish, the number of fish deaths will not exceed 1‰ even if the fish suffers from severe head floating.

水质改善,降低了养殖水域调水药的用量。池塘淤泥厚,池塘氨氮、硫化氢含量超标,常用化学药品,造成水质二次污染。The water quality has been improved, reducing the amount of water transfer medicine used in aquaculture waters. The pond silt is thick, the content of ammonia nitrogen and hydrogen sulfide in the pond exceeds the standard, and chemicals are commonly used, causing secondary pollution of water quality.

具体实施方式detailed description

为了使本发明的目的及优点更加清楚明白,以下结合实施例对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅仅用以解释本发明,并不用于限定本发明。In order to make the objects and advantages of the present invention clearer, the present invention will be further described in detail below in conjunction with the examples. It should be understood that the specific embodiments described here are only used to explain the present invention, not to limit the present invention.

实施例1Example 1

S1、当养殖池塘的水位达到100cm后,每亩投放规格为500克的鲢鱼和鳙鱼各为100尾,规格为30克的鲤鱼200尾,规格为30克的鲫鱼800尾;每亩投放规格为500克草鱼150尾;投饵量按草鱼的体重计算。S1. When the water level of the breeding pond reaches 100cm, put 100 silver carp and bighead carp with a size of 500 grams per mu, 200 carp with a size of 30 grams, and 800 crucian carp with a size of 30 grams; The specification is 150 grass carp of 500 grams; the feeding amount is calculated according to the weight of grass carp.

、将枯草芽孢杆菌、酵母菌、光合细菌液体菌液按体积比例为1∶1∶1的比例混合成混合菌液,投放到养殖水体,投放量为养殖水体体积的0.1‰-0.2‰,其中,水温20℃-25℃,每隔15天投放混合菌液1次,投放量为养殖水体体积的0.2‰,水温25℃以上每隔7天投放混合菌液1次,投放量为养殖水体体积的0.1‰,以后每次投放菌液处理水质前,测定水质TN、TP及COD指标,根据监测结果确定连续投放混合菌液处理养殖水体时间。1. Mix Bacillus subtilis, saccharomyces, and photosynthetic bacteria liquid bacteria liquid in a volume ratio of 1:1:1 to form a mixed bacterial liquid, and put it into the aquaculture water body, and the dosage is 0.1‰-0.2‰ of the volume of the aquaculture water body, wherein , the water temperature is 20°C-25°C, the mixed bacterial solution is put in once every 15 days, and the amount is 0.2‰ of the volume of the aquaculture water body, and the mixed bacterial solution is put in once every 7 days when the water temperature is above 25°C. The 0.1‰ of the 0.1‰, after each time the bacteria solution is used to treat the water quality, the water quality TN, TP and COD indicators are measured, and the time for continuous injection of the mixed bacteria solution to treat the aquaculture water is determined according to the monitoring results.

实施例2Example 2

S1、当养殖池塘的水位达到100cm后,每亩投放规格为500克的鲢鱼和鳙鱼各为100尾,规格为30克的鲤鱼200尾,规格为30克的鲫鱼800尾;每亩投放规格为500克草鱼150尾;投饵量按草鱼的体重计算。S1. When the water level of the breeding pond reaches 100cm, put 100 silver carp and bighead carp with a size of 500 grams per mu, 200 carp with a size of 30 grams, and 800 crucian carp with a size of 30 grams; The specification is 150 grass carp of 500 grams; the feeding amount is calculated according to the weight of grass carp.

、将枯草芽孢杆菌、酵母菌、光合细菌液体菌液按体积比例为3∶2∶3的比例混合成混合菌液,投放到养殖水体,投放量为养殖水体体积的0.1‰-0.2‰,其中,水温20℃-25℃,每隔15天投放混合菌液1次,投放量为养殖水体体积的0.2‰,水温25℃以上每隔7天投放混合菌液1次,投放量为养殖水体体积的0.1‰,以后每次投放菌液处理水质前,测定水质TN、TP及COD指标,根据监测结果确定连续投放混合菌液处理养殖水体时间。1. Mix Bacillus subtilis, saccharomyces, and photosynthetic bacteria liquid bacteria liquid in a volume ratio of 3:2:3 to form a mixed bacterial liquid, and put it into the aquaculture water body, and the dosage is 0.1‰-0.2‰ of the volume of the aquaculture water body, wherein , the water temperature is 20°C-25°C, the mixed bacterial solution is put in once every 15 days, and the amount is 0.2‰ of the volume of the aquaculture water body, and the mixed bacterial solution is put in once every 7 days when the water temperature is above 25°C. The 0.1‰ of the 0.1‰, after each time the bacteria solution is used to treat the water quality, the water quality TN, TP and COD indicators are measured, and the time for continuous injection of the mixed bacteria solution to treat the aquaculture water is determined according to the monitoring results.

实施例3Example 3

S1、当养殖池塘的水位达到100cm后,每亩投放规格为500克的鲢鱼和鳙鱼各为100尾,规格为30克的鲤鱼200尾,规格为30克的鲫鱼800尾;每亩投放规格为500克草鱼150尾;投饵量按草鱼的体重计算。S1. When the water level of the breeding pond reaches 100cm, put 100 silver carp and bighead carp with a size of 500 grams per mu, 200 carp with a size of 30 grams, and 800 crucian carp with a size of 30 grams; The specification is 150 grass carp of 500 grams; the feeding amount is calculated according to the weight of grass carp.

、将枯草芽孢杆菌、酵母菌、光合细菌液体菌液按体积比例为2∶1.5∶2的比例混合成混合菌液,投放到养殖水体,投放量为养殖水体体积的0.1‰-0.2‰,其中,水温20℃-25℃,每隔15天投放混合菌液1次,投放量为养殖水体体积的0.2‰,水温25℃以上每隔7天投放混合菌液1次,投放量为养殖水体体积的0.1‰,以后每次投放菌液处理水质前,测定水质TN、TP及COD指标,根据监测结果确定连续投放混合菌液处理养殖水体时间经过10-12个月,经检测,上述实施例1-3中的池塘淤泥由50-110cm降低到20cm以下,甚至无淤泥,节约了机械清淤的成本。在1个养殖周期内,在水温不超过25℃的情况下,实现了只进水、不排水的养殖模式,同时在高温季节,20天换一次水,换水量只为10%。即使在我国西部水源紧缺地区,也可以实现亩产1500公斤,产量可提升50%;饵料系数可达2.0,节约了养殖成本,提高鱼产量,未出现鱼类出现严重浮头的情况,鱼类死亡数不会超过1‰;水质情况较好。1. Mix Bacillus subtilis, saccharomyces, and photosynthetic bacteria liquid bacteria liquid in a volume ratio of 2:1.5:2 to form a mixed bacterial liquid, and put it into the aquaculture water body, and the dosage is 0.1‰-0.2‰ of the volume of the aquaculture water body, wherein , the water temperature is 20°C-25°C, the mixed bacterial solution is put in once every 15 days, and the amount is 0.2‰ of the volume of the aquaculture water body, and the mixed bacterial solution is put in once every 7 days when the water temperature is above 25°C. 0.1‰ of the 0.1‰, after each time before putting in the bacterial solution to treat the water quality, measure the water quality TN, TP and COD indicators, determine according to the monitoring results that the time for continuous feeding of the mixed bacterial solution to treat the aquaculture water is 10-12 months, after testing, the above-mentioned embodiment 1 In -3, the pond silt is reduced from 50-110cm to below 20cm, or even no silt, which saves the cost of mechanical dredging. In one breeding cycle, when the water temperature does not exceed 25°C, the breeding mode of only water intake and no drainage is realized. At the same time, in the high temperature season, the water is changed every 20 days, and the water change volume is only 10%. Even in areas where water is scarce in western my country, it is possible to achieve a yield of 1,500 kg per mu, and the yield can be increased by 50%; the bait coefficient can reach 2.0, which saves the cost of breeding and increases the production of fish. The number will not exceed 1‰; the water quality is good.

实施例4Example 4

S1、当养殖池塘的水位达到100cm后,每亩投放规格为500克的鲢鱼和鳙鱼各为100尾,规格为30克的鲤鱼200尾,规格为30克的鲫鱼800尾;每亩投放规格为50克草鱼2000尾;投饵量按草鱼的体重计算。S1. When the water level of the breeding pond reaches 100cm, put 100 silver carp and bighead carp with a size of 500 grams per mu, 200 carp with a size of 30 grams, and 800 crucian carp with a size of 30 grams; The specification is 2000 grass carp with 50 grams; the amount of feeding is calculated according to the weight of grass carp.

、将枯草芽孢杆菌、酵母菌、光合细菌液体菌液按体积比例为1-3∶1-2∶1-3的比例混合成混合菌液,投放到养殖水体,投放量为养殖水体体积的0.1‰,以后每次投放菌液处理水质前,测定水质TN、TP、及COD指标,根据监测结果确定连续投放混合菌液处理养殖水体时间。水温20℃-25℃,每隔15天投放混合菌液1次,投放量为养殖水体体积的0.2‰,水温25℃以上每隔7天投放混合菌液1次,投放量为养殖水体体积的0.1‰。1. Mix Bacillus subtilis, saccharomyces, and photosynthetic bacteria liquid bacteria liquid in a volume ratio of 1-3:1-2:1-3 to form a mixed bacterial liquid, and put it into the aquaculture water body, and the amount of input is 0.1% of the volume of the aquaculture water body. ‰, in the future, measure the TN, TP, and COD indicators of the water quality before each time the bacterial solution is used to treat the water quality, and determine the time for continuous injection of the mixed bacterial solution to treat the aquaculture water according to the monitoring results. The water temperature is 20°C-25°C, and the mixed bacterial solution is put in once every 15 days, and the amount is 0.2‰ of the volume of the aquaculture water body. The water temperature is above 25°C. 0.1‰.

经过10-12个月,经检测,上述实施例中的池塘淤泥由50-110cm降低到20cm以下,甚至无淤泥,节约了机械清淤的成本。在1个养殖周期内,在水温不超过25℃的情况下,实现了只进水、不排水的养殖模式,同时在高温季节,20天换一次水,换水量只为10%。即使在我国西部水源紧缺地区,也可以实现亩产2000公斤,产量可提升50%;饵料系数可达1.4,节约了养殖成本,提高鱼产量,未出现草鱼“新四病”,草鱼的成活率可达99%;水质情况较好。After 10-12 months, after testing, the pond silt in the above embodiment is reduced from 50-110cm to below 20cm, even without silt, which saves the cost of mechanical dredging. In one breeding cycle, when the water temperature does not exceed 25°C, the breeding mode of only water intake and no drainage is realized. At the same time, in the high temperature season, the water is changed every 20 days, and the water change volume is only 10%. Even in areas where water is scarce in western my country, the yield per mu can be 2,000 kg, and the yield can be increased by 50%; the feed coefficient can reach 1.4, which saves the cost of breeding and increases the production of fish. The "four new diseases" of grass carp do not appear, and the survival rate of grass carp Up to 99%; the water quality is better.

以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以作出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above is only a preferred embodiment of the present invention, it should be pointed out that for those of ordinary skill in the art, without departing from the principle of the present invention, some improvements and modifications can also be made, and these improvements and modifications should also be It is regarded as the protection scope of the present invention.

Claims (1)

1.一种养殖池塘生物清淤的方法,其特征在于,包括如下步骤:1. A method for biological dredging of a breeding pond is characterized in that, comprising the steps: S1、当养殖池塘的水位达到100cm后,每亩投放规格为500克的鲢鱼和鳙鱼各为100尾,规格为30克的鲤鱼200尾,规格为30克的鲫鱼800尾;S1, when the water level of the breeding pond reaches 100cm, put in 100 tails of silver carp and bighead carp with a specification of 500 grams per mu, 200 tails of carp with a specification of 30 grams, and 800 tails of crucian carp with a specification of 30 grams; S2、将枯草芽孢杆菌、酵母菌、光合细菌液体菌液按体积比例为1-3∶1-2∶1-3的比例混合成混合菌液,投放到养殖水体,投放量为养殖水体体积的0.1‰-0.2‰,其中,水温20℃-25℃,每隔15天投放混合菌液1次,投放量为养殖水体体积的0.2‰,水温25℃以上每隔7天投放混合菌液1次,投放量为养殖水体体积的0.1‰,以后每次投放菌液处理水质前,测定水质TN、TP及COD指标,根据监测结果确定连续投放混合菌液处理养殖水体时间。S2. Mix Bacillus subtilis, saccharomyces, and photosynthetic bacteria liquid bacteria liquid in a volume ratio of 1-3:1-2:1-3 to form a mixed bacterial liquid, and put it into the aquaculture water body, and the amount of input is 1/2 of the volume of the aquaculture water body 0.1‰-0.2‰, among them, when the water temperature is 20°C-25°C, the mixed bacterial solution is added once every 15 days, and the dosage is 0.2‰ of the volume of the aquaculture water body, and the mixed bacterial solution is added once every 7 days when the water temperature is above 25°C , the dosage is 0.1‰ of the volume of the aquaculture water body. Before each time the bacterial solution is used to treat the water quality, the water quality TN, TP and COD indicators are measured. According to the monitoring results, the time for continuous injection of the mixed bacterial solution to treat the aquaculture water body is determined.
CN201610110782.3A 2016-02-22 2016-02-22 Desilting method for aquaculture pond organisms Pending CN105706996A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610110782.3A CN105706996A (en) 2016-02-22 2016-02-22 Desilting method for aquaculture pond organisms

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610110782.3A CN105706996A (en) 2016-02-22 2016-02-22 Desilting method for aquaculture pond organisms

Publications (1)

Publication Number Publication Date
CN105706996A true CN105706996A (en) 2016-06-29

Family

ID=56156337

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610110782.3A Pending CN105706996A (en) 2016-02-22 2016-02-22 Desilting method for aquaculture pond organisms

Country Status (1)

Country Link
CN (1) CN105706996A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106007307A (en) * 2016-06-30 2016-10-12 山东胜伟园林科技有限公司 Desilting agent containing reed stem-shaped methane bristle-shaped bacteria and application of desilting agent in salt elimination concealed conduit
CN108439611A (en) * 2018-03-30 2018-08-24 云南亚美湖泊水质治理有限公司 A kind of purification method of eutrophication water
CN109504628A (en) * 2018-12-11 2019-03-22 南开大学 A kind of preparation method of microbial deoderizer

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104026052A (en) * 2014-06-25 2014-09-10 广西博士海意信息科技有限公司 Breeding method of crucians
CN104961311A (en) * 2015-06-11 2015-10-07 耿跃 Method for manufacturing biological preparations for treating silt at bottoms of fish ponds
CN104982355A (en) * 2015-06-10 2015-10-21 周天赐 Cultivation method with high production of grass carp in pool
CN104986930A (en) * 2015-06-11 2015-10-21 耿跃 Biological agent for treating sludge on bottom of fish pond
CN105454117A (en) * 2015-12-30 2016-04-06 陈东 Method for culturing crucian

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104026052A (en) * 2014-06-25 2014-09-10 广西博士海意信息科技有限公司 Breeding method of crucians
CN104982355A (en) * 2015-06-10 2015-10-21 周天赐 Cultivation method with high production of grass carp in pool
CN104961311A (en) * 2015-06-11 2015-10-07 耿跃 Method for manufacturing biological preparations for treating silt at bottoms of fish ponds
CN104986930A (en) * 2015-06-11 2015-10-21 耿跃 Biological agent for treating sludge on bottom of fish pond
CN105454117A (en) * 2015-12-30 2016-04-06 陈东 Method for culturing crucian

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106007307A (en) * 2016-06-30 2016-10-12 山东胜伟园林科技有限公司 Desilting agent containing reed stem-shaped methane bristle-shaped bacteria and application of desilting agent in salt elimination concealed conduit
CN108439611A (en) * 2018-03-30 2018-08-24 云南亚美湖泊水质治理有限公司 A kind of purification method of eutrophication water
CN108439611B (en) * 2018-03-30 2020-08-04 云南亚美湖泊水质治理有限公司 Method for purifying eutrophic water body
CN109504628A (en) * 2018-12-11 2019-03-22 南开大学 A kind of preparation method of microbial deoderizer

Similar Documents

Publication Publication Date Title
Hu et al. Monitoring and research of microcystins and environmental factors in a typical artificial freshwater aquaculture pond
CN101475265B (en) Water purification method for circulating water industrialized aquiculture system and complex bacterial agent thereof
Tello et al. How do land-based salmonid farms affect stream ecology?
CN104285868B (en) A kind of ecological cultivation method of Environment of Litopenaeus vannamei Low Fish-shrimp mix-culture
CN107324504B (en) A kind of compound algae microbial inoculum and preparation method thereof for culture-pool water quality improvement
CN103193329B (en) Biological agent for controlling excessive propagation of blue-green algae of aquaculture water and preparation method of biological agent
CN109122531B (en) Method for culturing hilsa herring
CN102674563A (en) Novel environment-friendly efficient microorganism water quality purifying mixture and preparation method thereof
CN104843876A (en) Microbial preparation for purifying water and improving water quality
CN104593303A (en) Liquid composite microbial agent and production method thereof
CN114317365A (en) A kind of biological bottom modification compound microbial inoculant and preparation method thereof
CN105706996A (en) Desilting method for aquaculture pond organisms
CN1760146A (en) Nourishing water transfer agent for aquiculture
CN106719193A (en) A kind of method of utilization biological flocculation technical optimization Environment of Litopenaeus vannamei Low seed rearing
CN101451111B (en) Enhanced type microbiological preparation for regulating water quality in fresh water aquiculture and use thereof
Catalani et al. Comparison between biofloc technology system and aquamimicry in the cultivation of Litopenaeus vannamei in lined ponds in Southern Brazil
CN116332335A (en) A treatment method for antibiotics in aquatic product farming wastewater
CN108046520A (en) A kind of low stimulating organism flocculation aquaculture method of low cost
WO2020009073A1 (en) Method for modifying aquaculture tank, and aquaculture method
CN101536736B (en) Special fishing fertilizer for aquaculture and preparation method thereof
CN101543190A (en) Method for cultivating tilapia by sea ice water
CN108911146B (en) Ecological treatment system for domestic sewage
CN109133356B (en) Method for removing algae by using filter feeders
CN108793646B (en) Landscape type domestic sewage ecological treatment system
CN107555611A (en) A kind of efficiently fishing improver of water quality and its preparation method and application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20160629

RJ01 Rejection of invention patent application after publication