CN104285851A - 利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法 - Google Patents
利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法 Download PDFInfo
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- CN104285851A CN104285851A CN201410119116.7A CN201410119116A CN104285851A CN 104285851 A CN104285851 A CN 104285851A CN 201410119116 A CN201410119116 A CN 201410119116A CN 104285851 A CN104285851 A CN 104285851A
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[N].N CVTZKFWZDBJAHE-UHFFFAOYSA-N 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- IOVCWXUNBOPUCH-UHFFFAOYSA-M nitrite anion Chemical compound 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- 230000000813 microbial Effects 0.000 description 2
- OAICVXFJPJFONN-UHFFFAOYSA-N phosphorus Chemical compound 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[P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 230000004083 survival Effects 0.000 description 2
- 241000276438 Gadus morhua Species 0.000 description 1
- 238000011030 bottleneck Methods 0.000 description 1
- 235000019516 cod Nutrition 0.000 description 1
- 230000000875 corresponding Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 230000000050 nutritive Effects 0.000 description 1
- 238000011017 operating method Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000001603 reducing Effects 0.000 description 1
- 238000005429 turbidity Methods 0.000 description 1
- 238000003809 water extraction Methods 0.000 description 1
Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K61/00—Culture of aquatic animals
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K61/00—Culture of aquatic animals
- A01K61/50—Culture of aquatic animals of shellfish
- A01K61/59—Culture of aquatic animals of shellfish of crustaceans, e.g. lobsters or shrimps
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
- A01K63/04—Arrangements for treating water specially adapted to receptacles for live fish
- A01K63/042—Introducing gases into the water, e.g. aerators, air pumps
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; CARE OF BIRDS, FISHES, INSECTS; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
- A01K63/04—Arrangements for treating water specially adapted to receptacles for live fish
- A01K63/045—Filters for aquaria
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/80—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
- Y02A40/81—Aquaculture, e.g. of fish
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/80—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
- Y02A40/81—Aquaculture, e.g. of fish
- Y02A40/818—Alternative feeds for fish, e.g. in aquacultures
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/80—Food processing, e.g. use of renewable energies or variable speed drives in handling, conveying or stacking
- Y02P60/87—Re-use of by-products of food processing for fodder production
Abstract
本发明公开了一种人工生态基在日本沼虾、沙塘鳢池塘生态养殖的应用方法，包括以下步骤：（1）池塘选择；（2）池塘人工生态基布局与生物膜形成；（3）苗种放养；（4）饲料投喂；（5）水质调控与日常管理；（6）成虾与成鱼捕捞。与现有技术相比，本发明能使池塘水质保持良好稳定，除水温较高的季节加注新水提升水位外，整个养殖周期不用换水，几乎无养殖废水排放，生态效益显著；而且生态基上微生物、藻类等生物群落，可为虾苗、沙塘鳢提供合适的栖息地，利用沙塘鳢捕食体弱病残的虾苗和8月份繁殖的秋苗，减少日本沼虾养殖发病率，提高成虾出池规格和产量，经济效益显著。
Description
技术领域
[0001] 本发明属于水产品生态养殖技术领域，主要涉及一种人工生态基在日本沼虾、沙 塘鳢池塘生态养殖的应用方法。
背景技术
[0002] 日本沼奸（Macrobrachium nipponense)肉质鲜美，具有很高的营养价值，价格居 高不下，市场供不应求，其养殖业已成为我国淡水养殖中的重要产业之一，至2012年其养 殖产量已达23. 74万吨。然而在传统养殖模式下，夏季放养的虾苗到8月份底开始大量繁 殖，导致世代混杂，从而造成养殖产量和品质下降、种质退化、病害多发等，使日本沼虾养殖 业发展滞缓，亟需新技术来改变现有产业状况，促进日本沼虾养殖的健康发展。
[0003] 人工生态基具有不受透明度、光照、水温等限制的特点，在水体中可附着藻类、有 机碎屑、微生物等，形成生物膜，可以显著降低水体浊度，并削减水体COD、N和P等污染 负荷，提高水体DO含量，从而增强水体自净能力。人工生态基在国内外富营养化水体修 复中已得到广泛应用，但在水产养殖中应用较少，至今尚未见到在日本沼虾池塘养殖中应 用人工生态基的技术报道。
发明内容
[0004] 本发明的目的在于克服现有技术存在的不足，提供一种利用人工生态基在池塘 生态养殖日本沼虾、沙塘鳢的方法。
[0005] 为达到上述目的，本发明采取了如下的技术方案：
[0006] 利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，它依次包括以下步 骤：
[0007] 池塘选择：选择水源良好，进排水方便的池塘，面积3-8亩，池底平坦，水深I. 0〜 1. 5米，淤泥厚度不超过20cm，塘埂夯实，每个池塘配备底部增氧机和潜水泵。
[0008] 池塘人工生态基布局与生物膜形成：在6月中下旬，对池塘进行严格干塘清淤，生 石灰消毒，一周后在池塘中放置人工生态基，人工生态基由绳子相连在池塘中呈"Z"字状排 列，绳子固定在池塘塘边上的竹子，生态基密度控制在60〜IOOm 3/亩。待人工生态基布局 好后注水，水位控制在1米左右，然后对池塘进行肥水，促进人工生态基上的微生物、藻类、 有机碎屑等的附着，形成生物膜。
[0009] 苗种放养：7月下旬放养当年日本沼虾幼虾苗种15〜25kg/亩，平均规格为5000 尾/kg，然后再放养沙塘鳢夏花300〜500尾/亩。
[0010] 饲料投喂：采用市售的优质饵料进行投喂，饲料投喂采用人工沿池塘四周投喂，每 天投喂2次，投喂时间分别为8点和19点，投喂量一般以1小时吃完为宜，而且要根据气候、 水温、生物膜、虾的生长情况随时调整。
[0011] 水质调控与日常管理：由于池塘中放置足够的人工生态基，在水体中形成了大量 的生物膜，建立了稳定的微生物生态系统，使池塘水体保持良好的水质，基本不用换水，只 需在水温高的季节适当加深水位10〜20cm。池塘由专人管理,每天根据天气情况适时开 增氧机和水泵，早晚坚持巡塘2〜3次，观察青虾、沙塘鳢、生态膜、水质等，并充分做好投饲 量、水质等必要的记录，其它管理按照常规方法进行。
[0012] 成虾与成鱼捕捞：采用"平时捕大留小，最后一次干塘"的方法，在10月上旬至翌 年5月采用地笼捕大留小，翌年6月采用干塘捕获。
[0013] 上述技术方案中，所述底部增氧机为罗氏鼓风机加纳米微孔管，每亩配置功率 0. 2kw ;所述潜水泵为普通的三相潜水泵，每亩配置功率0. 5kw。
[0014] 上述技术方案中，所述人工生态基为立体弹性生态基。
[0015] 上述技术方案中，所述人工生态基布局为：人工生态基的固定为一端系在绳子上， 另一端系上沉子，使每根人工生态基能在水体中垂直悬挂，绳子材质为聚乙烯。
[0016] 上述技术方案中，所述生物膜形成时，施肥为生石灰消毒发酵后的鸡粪、鸭粪、猪 粪、羊粪、牛粪等有机肥。
[0017] 上述技术方案中，所述沙塘鳢放养时间为日本沼虾放养后的10〜15天。
[0018] 上述技术方案中，所述饲料投喂为：人工配合饲料蛋白含量要求在38%以上，9〜 10月每天第二次投喂时，适当添加水蚯蚓等活饵，活饵量占总投饲量的60%以上。
[0019] 上述技术方案中，所述水温高时加水具体操作为：用潜水泵缓慢加注水，注水口用 双层网袋过滤，内网60目，外网120目，过滤网长度15〜20米。
[0020] 上述技术方案中，所述根据天气情况适时开增氧机和水泵具体操作为：阳光充足 的天气12:00〜14:00和22:00〜8:00开启底部增氧机，并在底部增氧机开启1小时后开 动潜水泵，使池塘水体上下充分交换，并行成一定的微流水；阴雨天气24小时开启底部增 氧机和水泵。
[0021] 与现有技术相比，本发明的有益效果是：
[0022] 1、本发明中人工生态基在池塘中应用操作方法简单实用，易于推广应。
[0023] 2、本发明中人工生态基在水体中形成生物膜，使池塘水质保持良好稳定，除水温 较高的季节加注新水提升水位外，整个养殖周期不用换水，几乎无养殖废水排放，生态效益 显著。
[0024] 3、本发明中提前在水体放置人工生态基，待生态基上微生物、藻类等生物群落稳 定后放养日本沼虾虾苗，可为虾苗提供良好的水质、适口的饵料和合适的栖息地，从而提高 了日本沼虾的成活率和产量。
[0025] 4、本发明中待虾苗适应池塘环境后放养沙塘鳢，利用沙塘鳢捕食体弱病残的虾苗 和8月份繁殖的秋苗，减少日本沼虾养殖发病率，提高成虾出池规格和品质；而且人工生态 基形成的生物群落是沙塘鳢良好的隐蔽物，利于沙塘鳢的栖息和捕食，使其自相残杀率降 低，提高了成活率、出塘规格和产量。
[0026] 因此本发明的人工生态基应用方法使用于池塘日本沼虾生态养殖，有利于解决当 前日本沼虾养殖业面临的产量和品质下降、种质退化、病害多发等瓶颈难题，提升日本沼虾 养殖技术水平，产生良好的社会和经济效益。
附图说明 图1为池塘水体中溶氧变化图； 图2为池塘水体中pH变化图； 图3为池塘水体中总氮变化图； 图4为池塘水体中总磷变化图； 图5为池塘水体中氨氮月变化图； 图6为池塘水体中亚硝酸盐月变化图。
具体实施方式
[0027] 本具体实施例仅仅是对本发明的解释，其并不是对本发明的限制，本领域技术人 员在阅读完本说明书后可以根据需要对本实施例做出没有创造性贡献的修改，但只要在本 发明的权利要求范围内都受到专利法的保护。
[0028] 实施例1
[0029] -种人工生态基在日本沼虾、沙塘鳢池塘生态养殖应用方法，包括下列步骤：
[0030] 1、池塘选择：选择水源良好，进排水方便的池塘5只，面积分别为4. 5、4. 6、4. 7、 4. 5和5. 1亩，池底平坦，水深I. 0〜1. 5米，游泥厚度不超过20cm，塘埂夯实，每个池塘配 备0. 2kw/亩的底部增氧机和0. 5kw/亩的潜水泵。
[0031] 2、池塘人工生态基布局与生物膜形成：在6月下旬，对池塘进行严格干塘清淤，生 石灰消毒，一周后在池塘中放置人工生态基，人工生态基由绳子相连在池塘中呈"Z"字状排 列，绳子用竹子在池塘边上固定，生态基密度分别为1〇〇、75、50、25和〇111 3/亩。待人工生态 基布局好后将池塘注满水，然后用生石灰消毒发酵后的鸡粪、鸭粪等有机肥对池塘水质进 行肥水，促进微生物在人工生态基上附着。
[0032] 3、苗种放养：7月下旬放养当年幼虾苗种分别为25、22、22、22、221^/亩，平均规格 为5000尾/kg，12天后再放养沙塘鳢夏花500、400、400、400、400尾/亩。
[0033] 4、饲料投喂：采用优质饵料进行投喂，人工配合饲料蛋白含量要求在38%以上， 活饵以水蚯蚓为主。饲料采用人工沿池塘四周投喂，每天投喂2次，投喂时间一般为8点和 19点，投喂量一般以1小时吃完为宜，在9〜10月份，第二次投喂时要添加水蚯蚓等活饵， 活饵量占总投饲量的60%以上，投饲量要根据气候、水温、生物膜、虾的生长情况随时调整。
[0034] 5、水质调控与日常管理：由于人工生态基中的生物膜存在，可以使池塘水体保持 良好的水质，基本不用换水。在8上旬〜9月中旬的适当加注新水，使池塘水位提高10〜 20cm。池塘由专人管理，每天根据天气情况适时开增氧机和水泵，早晚坚持巡塘2〜3次， 观察青虾、沙塘鳢、生态膜、水质等，并充分做好投饲量、水质等必要的记录，其它管理按照 常规方法进行。
[0035] 6、成虾与成鱼捕捞：采用"平时捕大留小，最后一次干塘"的方法，在10月上旬至 翌年5月采用地笼、手抄网等捕大留小，翌年6月采用干塘捕获。
[0036] 7、生产结果及经济效益分析
[0037] 5个池塘的生产结果见表1，与对照塘（1#)相比，放置不同密度生态基均能显著提 高商品虾产量和规格，同时沙塘鳢规格和产量也相应提高，而饲料下系数则显著下降。100、 75、50m 3/亩人工生态基的池塘亩产值均在10191元以上，分别比对照组提高54. 9%、46. 5% 和36. 5% ;亩效益均在4541元以上，分别比对照组提高52. 2%、52. 1%和48. 0%。
[0038] 表15个池塘商品虾、沙塘鳢亩产量及产出规格
[0040] 8、池塘水质指标与生态效益分析
[0041] 如图1〜图6所示，5个池塘的溶氧和pH随着月份的变化相对稳定，池塘中放置生 态基对溶氧和PH无显著影响。与对照组池塘相比，放置人工生态基对池塘水体中的总氮、 总磷、氨氮和亚硝酸盐有显著地降低作用，尤其是50、75和IOOm 3/亩的池塘中氨氮、亚硝酸 盐一直维持在较低的含量，保证了池塘良好的水质。
[0042] 由于池塘中放置足够的人工生态基，在水体中形成了大量的生物膜，建立了稳定 的微生物生态系统，使池塘水体保持良好的水质，基本不用换水，只需8上旬〜9月中旬的 适当加注新水，使池塘水位提高10〜20cm。因此整个养殖周期基本不用换水，几乎无养殖 废水排放，因此不用考虑养殖废水排放造成的生态足迹量，从而比传统日本沼虾养殖污染 环境程度低，对环境资源的影响小，实现水产养殖与环境资源的和谐发展。
Claims (9)
1. 利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特征在于，它依次包括 以下步骤： (1) 池塘选择：选择水源良好，进排水方便的池塘，面积3〜8亩，池底平坦，水深1. 0〜 1. 5米，淤泥厚度不超过20cm，塘埂夯实，每个池塘配备底部增氧机和潜水泵； (2) 池塘人工生态基布局与生物膜形成：在6月中下旬，对池塘进行严格干塘清淤，生 石灰消毒；一周后在池塘中放置人工生态基，人工生态基由绳子相连在池塘中呈"Z"字状 排列，绳子在池塘塘边上的竹子固定，生态基密度控制在60m 3〜100m3/亩；待人工生态基布 局好后注水，水位控制在1. 0米左右；然后对池塘水质进行肥水，促进人工生态基中的微生 物、藻类、有机碎屑等的附着，形成生物膜； (3) 苗种放养：7月下旬放养当年日本沼虾幼虾苗种15〜25kg/亩，平均规格为5000 尾/kg，然后再放养沙塘鳢夏花300〜500尾/亩； (4) 饵料投喂：采用市售的优质饵料进行投喂，饵料投喂采用人工沿池塘四周投喂，每 天投喂2次，投喂时间分别为8点和19点，投喂量一般以1小时吃完为宜； (5) 水质调控与日常管理：由于人工生态基中的生物膜存在，可以使池塘水体保持良好 的水质，基本不用换水，只需在水温高的季节适当加深水位10〜20cm ;池塘由专人管理，每 天根据天气情况适时开启底部增氧机和水泵，早晚坚持巡塘2〜3次，观察青虾、沙塘鳢生 长情况，并充分做好投饲量、水质等必要的记录，其它管理按照常规方法进行； (6) 成虾与成鱼捕捞：采用"平时捕大留小，最后一次干塘"的方法，在10月上旬至翌年 5月采用地笼捕大留小，翌年6月采用干塘捕获。
2. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述底部增氧机为罗氏鼓风机加纳米微孔管，每亩配置功率0. 2kw ;所述潜水泵为 普通的三相潜水泵，每亩配置功率0. 5kw。
3. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述人工生态基为立体弹性生态基。
4. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述人工生态基布局时，人工生态基的固定为一端系在绳子上，另一端系上沉子， 使每根人工生态基能在水体中垂直悬挂，绳子材质为聚乙烯。
5. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述生物膜形成时，施肥为生石灰消毒发酵后的鸡粪、鸭粪、猪粪、羊粪、或牛粪。
6. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述苗种放养时，沙塘鳢夏花放养时间为日本沼虾苗种放养后的10〜15天。
7. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述饲料投喂时，人工配合饲料蛋白含量要求在38%以上，9〜10月每天晚上投喂 时，适当添加水蚯蚓等活饵，活饵量占总投饲量的60%以上。
8. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述水质调控，水温高时提高水位用潜水泵缓慢加注水，注水口用双层网袋过滤， 内网60目，外网120目，过滤网袋长度15〜20米。
9. 如权利要求1所述利用人工生态基在池塘生态养殖日本沼虾、沙塘鳢的方法，其特 征在于：所述日常管理时，根据天气情况适时开增氧机和水泵具体操作为：阳光充足的天 气12:00〜14:00和24:00〜8:00开启底部增氧机，并在底部增氧机开启1小时后开动潜 水泵，使池塘水体上下充分交换，并行成一定的微流水；阴雨天气24小时开启底部增氧机 和水泵。
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| CN105248329A (zh) * | 2015-10-30 | 2016-01-20 | 滁州市南谯区长江水产良种繁育场 | 一种鲈鱼池塘循环流水养殖方法 |
| CN105557587A (zh) * | 2016-01-13 | 2016-05-11 | 中国海洋大学 | 一种藻钩虾室内人工养殖的方法 |
| CN106962238A (zh) * | 2017-05-20 | 2017-07-21 | 福建省淡水水产研究所 | 一茬半刺厚唇鱼混养两茬日本沼虾的池塘混养方法 |
| CN107079842A (zh) * | 2017-03-28 | 2017-08-22 | 陆川县恒伟养殖专业合作社 | 一种草鱼的高产养殖方法 |
| CN112021217A (zh) * | 2020-10-14 | 2020-12-04 | 江苏省淡水水产研究所 | 大规格沙塘鳢苗种的水泥池培育方法 |
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| CN104814328A (zh) * | 2015-05-14 | 2015-08-05 | 苏州市相城区阳澄湖镇剑美水产生态养殖专业合作社 | 一种青虾有机饵料 |
| CN105248329A (zh) * | 2015-10-30 | 2016-01-20 | 滁州市南谯区长江水产良种繁育场 | 一种鲈鱼池塘循环流水养殖方法 |
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| CN107079842A (zh) * | 2017-03-28 | 2017-08-22 | 陆川县恒伟养殖专业合作社 | 一种草鱼的高产养殖方法 |
| CN106962238A (zh) * | 2017-05-20 | 2017-07-21 | 福建省淡水水产研究所 | 一茬半刺厚唇鱼混养两茬日本沼虾的池塘混养方法 |
| CN106962238B (zh) * | 2017-05-20 | 2019-08-27 | 福建省淡水水产研究所 | 一茬半刺厚唇鱼混养两茬日本沼虾的池塘混养方法 |
| CN112021217A (zh) * | 2020-10-14 | 2020-12-04 | 江苏省淡水水产研究所 | 大规格沙塘鳢苗种的水泥池培育方法 |
| CN112021217B (zh) * | 2020-10-14 | 2021-11-09 | 江苏省淡水水产研究所 | 大规格沙塘鳢苗种的水泥池培育方法 |
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