CN205455365U - Be applied to biological breeding device of aquatic attitude risk assessment of pesticide experiment - Google Patents
Be applied to biological breeding device of aquatic attitude risk assessment of pesticide experiment Download PDFInfo
- Publication number
- CN205455365U CN205455365U CN201620286574.4U CN201620286574U CN205455365U CN 205455365 U CN205455365 U CN 205455365U CN 201620286574 U CN201620286574 U CN 201620286574U CN 205455365 U CN205455365 U CN 205455365U
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- CN
- China
- Prior art keywords
- fishing cage
- pesticide
- risk assessment
- experiment
- culturing device
- 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.)
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- 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
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- Catching Or Destruction (AREA)
Abstract
The utility model provides a be applied to biological breeding device of aquatic attitude risk assessment of pesticide experiment, including breeding the fishing cage the mount being used for raising the breed fishing cage of breeding the thing with setting up in the mount below, the lateral wall of breeding the fishing cage is equipped with fixed iron ring and buoyancy parts more than the round, breeds fishing cage top and is zha kou, and zhakou locates to tighten the after -fixing to the mount through the cotton rope. It is equipped with the opening to breed fishing cage upper end for throw the material and survey. The buoyancy parts can be allocated for control is bred the fishing cage and is gone up and down.
Description
Technical field
This utility model relates to cultivation apparatus field, a kind of biology being applied to the experiment of pesticide water ecological risk assessment
Cultivation apparatus.
Background technology
Pesticide ecological environment security evaluation is requisite link in pesticide management, pesticide action process pole in the environment
It is complicated, and laboratory test can not reflect pesticide Transport And Transformation behavior in natural environment and ecological effect thereof the most strictly according to the facts.
Hydrobiological impact can be shown on molecule, organ, tissue, individuality and population, group's varying level by pesticide,
In most cases, aquatile is exposed under low concentration (sub-lethal) pesticide, evaluates pesticide to hydrobiological impact
It is inadequate according only to toxicity assessment.The risk may brought for scientific forecasting Pesticide use, is necessary for carrying out field examination
Test research, provide observation and test data reliably for risk assessment.In order to actual response pesticide return in the environment become and
To Aquatic organisms, carry out higher level risk assessment, be therefore necessary for using in actual environment the fish through being commonly encountered,
The biology such as shrimp, Eriocheir sinensis is evaluated after actually used chemistry of pesticide product hydrobiological impact.
Utility model content
Utility model purpose: technical problem to be solved in the utility model is for the deficiencies in the prior art, it is provided that a kind of
It is applied to the biological culturing device of pesticide water ecological risk assessment experiment.
In order to solve above-mentioned technical problem, this utility model provide a kind of be applied to pesticide water ecological risk assessment experiment
Biological culturing device, including fixed mount be arranged on the cultivation fishing cage for raising material culture below fixed mount, described supports
The sidewall growing fishing cage is provided with fixing iron ring and the buoyancy member of a more than circle, and cultivation fishing cage top is tying, passes through at tying
Cotton rope is fixed on fixed mount after tightening.
In this utility model, described cultivation fishing cage upper end is provided with opening, is used for feeding intake and observing.
In this utility model, described buoyancy member is adjustable, is used for controlling to cultivate the lifting of fishing cage.
In this utility model, described opening is zipper.
In this utility model, described cultivation fishing cage is made up of fishing net.
In this utility model, described cultivation fishing cage width of mesh is adaptive with material culture.
Beneficial effect: this utility model device is simple and easy to do, can effectively control cultivation apparatus lifting in water body, reduces
The change impact of water level height, is raised and observation biology by dog-house and observation port simultaneously, effectively solves to open cultivation
The inconvenience that mouth is brought, reduces hydrobiological impact.Ensure that convenience and the operability of operation, it is operable
Property strong, simple and practical, practical, reduce objective condition to hydrobiological impact, heighten test efficiency and standard
Really property.
Accompanying drawing explanation
With detailed description of the invention this utility model done below in conjunction with the accompanying drawings and further illustrate, of the present utility model
Above-mentioned or otherwise advantage will become apparent.
Fig. 1 is the structural representation of embodiment 1.
Detailed description of the invention
Below in conjunction with accompanying drawing, this utility model is elaborated.
Embodiment 1:
Such as Fig. 1, this utility model includes fixing iron ring 1, cultivation fishing cage 2, buoyancy member 3, opening 4, fixed mount 5
With tying 7, wherein cultivation fishing cage 2 sidewall is provided with the fixing iron ring 1 of a more than circle, is provided with floating in described cultivation fishing cage 2
Power parts 3, described cultivation fishing cage 2 is arranged over fixed mount 5, and cultivation fishing cage 2 top is tying 7, logical at tying 7
Cross and be fixed on fixed mount 5 after cotton rope is tightened.
Fixing iron ring 1 struts cultivation fishing cage 2, forms the basic configuration of breeding cage, is unlikely to distort, and is conducive to
Water keeps certain shape.Generally cylindrical structural.
A circle buoyancy member 3 is contained in the upper end of cultivation fishing cage 2, and buoyancy member can select buoyant foam ball, buoyant foam
The quantity of ball can be allocated, by buoyancy member 3 make whole breeding cage the upper end moment some be positioned at above the water surface,
No matter the rising of water level or decline, all keep certain distance emerged so that the biology of cultivation can be at the water surface
Breathe, also can observe aquatic biological activity and counting at any time.
Opening 4 can be positioned at above buoyant device as dog-house and observation port, generally 20cm, by a slide fastener system
Become, when raising biology and feeding intake or observe aquatic biological activity situation, slide fastener can be opened and feed intake or observe.
The aperture of cultivation fishing cage 2 can determine different pore sizes according to the type of aquaculture organism, and the aperture of fish shrimp crab is each not
Identical.
When the experiment of pesticide water ecological risk assessment starts, place aquatile cultivation apparatus, according to kind difference by aquatic
Biological raising is in device.When reaching pesticide application condition, dispenser dosage and insecticide-applying way according to pesticide start dispenser,
Now pesticide starts to adsorb on rice leaf and fall into the water, and the pesticide fallen into the water starts to dissolve and adsorb to exist in water
Rice soil surface.Start in certain time to discharge water after dispenser terminates, rice field water in field is put into the aquatile experiment pool.With
Water in field and enter the pesticide on the aquatile experiment pool, partial action is in aquatile, and produces corresponding toxic action, separately
Outer portion starts hydrolysis or sedimentation absorption on bed mud.Final according to hydrobiological mortality rate, toxic effect, obtain
The value-at-risk of this kind of pesticide.Finally determine this kind of pesticide to different hydrobiological harm, for the Environmental risk management of pesticide
Offer data are supported.
1, experimental technique
By normal planting patterns rice cultivation in rice field, and normal management.9 observed samples points are set in testing front fish pond,
Cultivate with biological culturing device various for examination aquatile in each point respectively, treat the aquatile in biological culturing device
After growth is normal, spraying certain pesticide August when paddy growth contains the phase in rice field, formulation rate is 30g (effective ingredient)
/ mu, during spray medicine, the deep about 5cm of water in field, all enters fish pond, drainage procedure the most about 12h by water in field after 24h.From dispenser
Rear sampling determination paddy soil and certain pesticide and the residue dynamics of metabolite thereof in water in field;Certain is measured from paddy field drainage
Pesticide and metabolite residue dynamics in fishpond water and bed mud thereof.Observe aquatile in biological culturing device simultaneously
Impact.
2, test pesticide
30% certain pesticide wettable;Consumption 30g ai/ mu
3, result and discussion
1. the harm impact of prawn
Test processes ibid, from table 1: in the comparison pool, also begin to occur the phenomena of mortality, 14d mortality rate after 10d
Reach 8.9%.And shrimp starts death occur after locating Litang draining 1d, mortality rate is 2.2%;Draining 6d mortality rate reaches
After 15.5%, 14d, mortality rate reaches 20.0%.Showing under this experimental condition, certain pesticide rice field uses prawn d's
Harm risk is less.
The harm of certain pesticide prawn of table 1 affects result of the test (mortality rate, %)
2. the harm on Eriocheir sinensis affects
Test processes ibid, and from table 2, the Eriocheir sinensis in the comparison pool starts death occur, reaches after 14d after 3 days
5.0%.And after locating Litang draining 2d, death occurs in Eriocheir sinensis, after draining 3d, mortality rate is 13.3%.Show certain pesticide
When pesticide rice field uses, the hazardness to Eriocheir sinensis is little.
Certain pesticide of table 2 affects result of the test (%) to the harm of Eriocheir sinensis
4, conclusion
After dispenser 24h, water in field entering fish pond, in the comparison pool, also begins to occur the phenomena of mortality after 10d, 14d is dead
Rate reaches 8.9%.And shrimp starts death occur after locating Litang draining 1d, mortality rate is 2.2%;Draining 6d mortality rate reaches
To 15.5%, after 14d, mortality rate reaches 20.0%.Showing under this experimental condition, certain pesticide rice field uses Japan
Macrobrachium does not has big harm risk;Eriocheir sinensis in the comparison pool starts death occur after 3 days, reach 5.0% after 14d,
And after locating Litang draining 2d, death occurs in Eriocheir sinensis, after draining 3d, mortality rate is 13.3% hereafter to keep constant.Show
When certain pesticide rice field uses, the hazardness to Eriocheir sinensis is less.
This utility model provides a kind of biological culturing device being applied to the experiment of pesticide water ecological risk assessment, implements
The method of this technical scheme and approach are a lot, and the above is only preferred implementation of the present utility model, it is noted that
For those skilled in the art, on the premise of without departing from this utility model principle, it is also possible to make
Some improvements and modifications, these improvements and modifications also should be regarded as protection domain of the present utility model.In the present embodiment the clearest and the most definite
Each ingredient all can use prior art to be realized.
Claims (6)
1. the biological culturing device being applied to the experiment of pesticide water ecological risk assessment, it is characterised in that include fixed mount (5)
Be arranged on fixed mount (5) lower section for raising cultivation fishing cage (2) of material culture, described cultivation fishing cage (2)
Sidewall is provided with fixing iron ring (1) and the buoyancy member (3) of a more than circle, and cultivation fishing cage (2) top is tying (7),
Tying (7) place is fixed on fixed mount (5) after being tightened by cotton rope.
A kind of biological culturing device being applied to the experiment of pesticide water ecological risk assessment the most according to claim 1, it is special
Levying and be, described cultivation fishing cage (2) upper end is provided with opening (4), is used for feeding intake and observing.
A kind of biological culturing device being applied to the experiment of pesticide water ecological risk assessment the most according to claim 1, it is special
Levying and be, described buoyancy member (3) is adjustable, is used for controlling to cultivate fishing cage (2) lifting.
A kind of biological culturing device being applied to the experiment of pesticide water ecological risk assessment the most according to claim 2, it is special
Levying and be, described opening (4) is zipper.
A kind of biological culturing device being applied to the experiment of pesticide water ecological risk assessment the most according to claim 1, it is special
Levying and be, described cultivation fishing cage (2) is made up of fishing net.
A kind of biological culturing device being applied to the experiment of pesticide water ecological risk assessment the most according to claim 1, it is special
Levying and be, described cultivation fishing cage (2) width of mesh is adaptive with material culture.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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CN201620286574.4U CN205455365U (en) | 2016-04-07 | 2016-04-07 | Be applied to biological breeding device of aquatic attitude risk assessment of pesticide experiment |
Applications Claiming Priority (1)
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CN201620286574.4U CN205455365U (en) | 2016-04-07 | 2016-04-07 | Be applied to biological breeding device of aquatic attitude risk assessment of pesticide experiment |
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CN205455365U true CN205455365U (en) | 2016-08-17 |
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CN201620286574.4U Expired - Fee Related CN205455365U (en) | 2016-04-07 | 2016-04-07 | Be applied to biological breeding device of aquatic attitude risk assessment of pesticide experiment |
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110663590A (en) * | 2019-11-14 | 2020-01-10 | 湖南文理学院 | Method for measuring feeding power of stocking area applied to capacity estimation of breeding area |
-
2016
- 2016-04-07 CN CN201620286574.4U patent/CN205455365U/en not_active Expired - Fee Related
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110663590A (en) * | 2019-11-14 | 2020-01-10 | 湖南文理学院 | Method for measuring feeding power of stocking area applied to capacity estimation of breeding area |
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Date | Code | Title | Description |
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C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20160817 Termination date: 20170407 |