DIAGNOSIS METHOD AND DIAGNOSIS DEVICE OF ECOTOXICITY OF SOLID WASTE SOIL IN PESTICIDE PRODUCTION SITE
20220241768 · 2022-08-04
Assignee
Inventors
- Shengmin WU (Nanjing, CN)
- Feng TIAN (Nanjing, CN)
- Yang GONG (Nanjing, CN)
- Zhenqian ZHAO (Nanjing, CN)
- Jing Tian (Nanjing, CN)
Cpc classification
B01L2300/168
PERFORMING OPERATIONS; TRANSPORTING
B01L2300/1805
PERFORMING OPERATIONS; TRANSPORTING
B01L2400/0487
PERFORMING OPERATIONS; TRANSPORTING
B01L2200/026
PERFORMING OPERATIONS; TRANSPORTING
A61K49/0004
HUMAN NECESSITIES
B01L3/502
PERFORMING OPERATIONS; TRANSPORTING
International classification
B01L3/00
PERFORMING OPERATIONS; TRANSPORTING
Abstract
The disclosure relates to a diagnosis method and diagnosis device of ecotoxicity of solid waste soil in a pesticide production site. The diagnosis method is as follows: performing multi-point distributed collection on solid waste soil of a to-be-diagnosed pesticide production site, and subsequently pretreating the connected soil sample; synchronously performing a first toxicity test, a second toxicity test and a third toxicity test on the pretreated solid waste soil by using the diagnosis device. The diagnosis device comprises a first test device, a second test device and a third test device. The method of the disclosure is used for synchronous diagnosis of ecotoxicity by utilizing multiple diagnosis methods, and therefore is high in diagnosis efficiency and high in accuracy rate.
Claims
1-6. (canceled)
7. A method for diagnosing the ecotoxicity of the solid waste soil in the pesticide production field is characterized by comprising the following steps of: the method comprises the following steps: step one: collection of field solid waste soil, carrying out multi-point collection on solid waste soil of an insecticide and pesticide production field to be diagnosed by combining with an investigation point distribution principle of the insecticide and pesticide production field; step two: pretreatment of solid waste soil, removing impurities from the collected soil, crushing, and sieving by using a 5-10 mm sieve to obtain pretreated solid waste soil; step three: diagnosis of ecotoxicity, synchronously carrying out a first toxicity test, a second toxicity test and a third toxicity test on the pretreated solid waste soil by using a diagnosis device; wherein the first toxicity test is an earthworm toxicity test and a plant germination toxicity test, the second toxicity test is a fish feeding toxicity test, and the third toxicity test is a plant root system extending toxicity test; wherein the diagnostic device comprises a first test device (1) for performing a first toxicity test, a second test device (2) for performing a second toxicity test, and a third test device (3) for performing a third test; the first test equipment (1), the second test equipment (2) and the third test equipment (3) are connected in sequence; wherein the first test device (1) comprises 5-8 first test cavities (11) which are identical in structure and are arranged in parallel at intervals, first monitoring devices (12) arranged in the intervals of the first test cavities (11), and first connecting devices (13) used for connecting the first test cavities (11) with the second test devices (2); wherein the first test cavity (11) comprises a first shell (111) and 3-5 embedding partition plates (112) which are clamped in the first shell (11) from top to bottom in sequence; the first shell (111) adopts a transparent acrylic plate; the embedding partition plate (112) comprises partition plates (1121), embedding holes (1122) which are uniformly arranged on the partition plates (1121) and used for embedding seeds, and perforation slots through which earthworms can pass; wherein the number of the first monitoring devices (12) is multiple, and the multiple first monitoring devices (12) are uniformly arranged in intervals of the first test cavity (11); wherein the first connecting device (13) comprises a plurality of liquid supply devices for respectively supplying liquid to 5-8 first test cavities (11), a liquid seepage device arranged at the lower end of each first test cavity (11), and a first connecting device with one end connected with the liquid seepage device; wherein the second test device (2) comprises 5-8 second test cavities (21) which are identical in structure and are arranged in parallel, second monitoring devices (22) arranged in the second test cavities (21), and auxiliary devices (23) erected above the second test cavities (21); wherein 5-8 second test cavities (21) are respectively connected with the other end of the first connecting device; wherein the third test equipment (3) comprises 5-8 third test cavities (31) which are identical in structure and are arranged in parallel, and second connecting devices which are used for connecting the 5-8 third test cavities (31) and the 5-8 second test cavities (21) in a one-to-one correspondence mode.
8. The method as claimed in claim 7, wherein the liquid supply device comprises a storage tank for storing deionized water, a spraying device arranged on the inner wall of the first shell (111), and a pipeline and a connecting pump for connecting the storage tank and the spraying device; and a soil humidity sensor is arranged inside the first shell (111).
9. The method as claimed in claim 7, wherein the liquid permeating device comprises 5 to 8 buffer chambers which are installed at the bottom of the first casing (111) in a one-to-one correspondence and are communicated with the first casing (111), and an intercepting screen which is arranged at the communication position of the buffer chambers and the first casing (111).
10. The method as claimed in claim 7, wherein the auxiliary device (23) comprises an air pump for supplying oxygen to the second test chamber (21), and a heating device for the auxiliary heating of the second test chamber (21).
11. The method as claimed in claim 7, wherein earthworms, in particular Eisenia foetida, are placed inside the first casing (111); the method comprises the following steps of pretreating earthworms before placing, specifically: and (3) putting the earthworms in a humid environment for gut purging for 3-5 hours.
12. The method as claimed in claim 7, wherein inside said second test chamber (21) is placed a zebrafish; the zebra fish is pretreated before being placed, and the pretreatment method specifically comprises the following steps: the feeding is stopped for 36-48 h before placing.
13. The method as claimed in claim 7, wherein a hydroponic vegetable is placed inside the third test chamber (31).
Description
BRIEF DESCRIPTION OF THE DRAWINGS
[0042]
[0043]
[0044]
[0045]
[0046]
[0047]
[0048]
[0049]
[0050]
[0051]
[0052] In which, 1—first test device, 11—first test chamber, 111—first housing, 112 embedded clapboard, 1121—embedded hole, 1122—perforated groove, 12—first monitoring device, 13—first connection device, 131—first connection component, 132—storage box, 133—spraying member, 134—buffer cavity, 135—intercepting filter screen and 136—water tank,
[0053] 2—second test device, 21—second test chamber, 22—second monitoring device, 23—auxiliary device, 231—air pipe, 232—heating plate,
[0054] 3—third test device, 31—third test chamber, 32—second connection component,
[0055] 4—abutment component, 41—abutment sleeve, 411—arc groove, 412—strip-shaped hole, 413—clamp seat, 42—abutment rod, 43—transmission sleeve, 431—guide block, 432—through hole, 44—first clamp head, 441—clamp slot, 45—second clamp head, and 46—torsion spring.
DETAILED DESCRIPTION OF THE EMBODIMENTS
[0056] The disclosure will be further described in detail in combination with specific embodiments to better embody the advantages of the disclosure.
Example 1
[0057] A diagnosis method of ecotoxicity of solid waste soil of a pesticide production site includes the following steps:
[0058] step 1: collection of solid waste soil in a site
[0059] Multi-point distributed collection was performed on to-be-to diagnosed solid waste soil in a pesticide production site in combination with a layout principle of survey spots in the pesticide production site to obtain a soil sample;
[0060] step 2: pretreatment of solid waste soil
[0061] The impurities in the collected soil sample was removed, and the soil sample without the impurities were smashed and screened via a 5 mm sieve to obtain pretreated solid waste soil; and
[0062] step 3: diagnosis of ecotoxicity
[0063] A first toxicity test, a second toxicity test and a third toxicity test were performed on the pretreated solid waste soil by using a diagnosis device the first toxicity test was an earthworm toxicity test and a plant germination toxicity test, the second toxicity test was a fish feeding toxicity test, and the third toxicity test was a plant root extension toxicity test.
Example 2
[0064] A diagnostic device special for the diagnostic method in example 1 was recorded in this example, as shown in
[0065] As shown in
[0066] the first test device 1 includes:
[0067] as shown in
[0068] as shown in
[0069] as shown in
[0070] as shown in
[0071] as shown in
[0072] the second test device 2 includes:
[0073] as shown in
[0074] as shown in
[0075] the third test device 3 includes:
[0076] as shown in
Example 3
[0077] This example is basically the same as example 2, and the difference is that as shown in
[0078] as shown in
[0079] and as shown in
[0080] as shown in
[0081] Through the arrangement of the above abutment component 4, the quick plug-in installation of the embedded clapboard 112 and the first housing 111 can be realized, so as to improve the installation efficiency of the first test chambers 11, and the quantity of the first test chambers 11 is rapidly adjusted according to demand on the practical diagnosis method.
[0082] The working method of the above abutment component 4 is as follows:
[0083] When the abutment rod 42 is not inserted or clamped, as shown in
[0084] when the abutment rod 42 is not inserted or clamped, as shown in
[0085] when the abutment rod 42 is inserted into the abutment sleeve 41, a state as shown in
[0086] when the through hole 432 of the transmission sleeve 43 rotates from a vertical direction to a horizontal direction, as shown in
[0087] when it is necessary to separate the abutment rod 42 from the transmission sleeve 43, the first clamp head 44 is rotated to be kept in the horizontal direction, the abutment rod 42 is pulled toward an opposite direction so that the abutment rod is separated from the transmission sleeve 43, and then the transmission sleeve 43 resets under the action of the magnetic repulsion force.
Example 4
[0088] The difference between this example and example 1 is that:
[0089] In the step 2, the impurities in the collected soil sample are removed, and the soil sample without the impurities are smashed and screened via a 10 mm sieve to obtain pretreated solid waste soil.
Example 5
[0090] The difference between this example and example 2 is that:
[0091] Eisenia foetidas which are subjected to intestinal cleaning treatment for 5 h in a humid environment are placed in the first test chamber 11 of the first test device 1;
[0092] Zebrafish which are subjected to fasting for 48 hours are placed in the second test chamber 21 of the second test device 2.
Example 6
[0093] The difference between this example and example 3 is that:
[0094] The first test device 1 includes 5 first test chambers 11 with the same structure and arranged in parallel at equal intervals in the first test chamber 11 of the first test device 1,
[0095] the first connection device 13 includes a liquid supply component which was in one-to-one correspondence to 5 first test chambers 11 and used for supplying liquid to the first test chambers 11,
[0096] the liquid infiltration component includes 5 buffer cavities 134 correspondingly installed at the bottom of the first housing 111 one by one and communicated with the first test chambers 11,
[0097] the second test device 2 includes 5 second test chambers 21 with the same structure and arranged in parallel.
Example 7
[0098] The difference between this example and example 3 is that:
[0099] The first test device 1 includes 8 first test chambers 11 with the same structure and arranged in parallel at equal intervals in the first test chambers 11 of the first test device 1,
[0100] the first connection device 13 includes a liquid supply component corresponding to eight first test chambers 11 one by one and used for supplying liquid to the first test chambers 11,
[0101] the liquid infiltration component includes 8 buffer cavities 134 correspondingly installed at the bottom of the first housing 111 one by one and communicated with the first test chambers 11,
[0102] the second test device 2 includes 8 second test chambers 21 with the same structure and arranged in parallel.
Application Example
[0103] By taking examples 1 and 2 as examples, a diagnosis method of ecotoxicity of solid waste soil in a pesticide production site includes the following steps:
[0104] step 1: collection of solid waste soil in a site
[0105] multi-point distributed collection was performed on to-be-to diagnosed solid waste soil in a pesticide production site in combination with a layout principle of survey spots in the pesticide production site, soils in different collection sites were separately and independently stored at 5° C. and labeled to obtain a soil sample;
[0106] step 2: pretreatment of solid waste soil
[0107] the impurities in the collected soil sample were removed, the soil sampled without the impurities were smashed, and screened via a 5-10 mm sieve to obtain pretreated solid waste soil; and
[0108] step 3: diagnosis of ecotoxicity
[0109] the pretreated solid waste soils in different collection sites were labeled in 5 groups for one experiment batch to labeled solid waste soils in group A1, group A2, group A3, group A4 and group A5; then the labeled solid waste soils were mixed with normal soils in 4 ratios to obtain 4 different experiment soils; wherein the solid waste soils labeled in this example were mixed with normal soils respectively in a mass ratio of 1:1, 1:2, 1:3 and 1:4 to obtain test soils;
[0110] Group A1: a11, A12, A13, A14,
[0111] Group A2: A21, A22, A23, A24,
[0112] Group A3: A31, A32, A33, A34,
[0113] Group A4: A41, A42, A43, A44,
[0114] Group A5: A51, A52, A53 and A54
[0115] Then the solid waste soil in group A1, group A2, group A3, group A4 and group A5 was put into 5 different first test chambers 11 respectively, the normal soil was recorded as group A6 and put into the sixth first test chamber 11, and each soil in each group was placed in different cavity layers of the first test chamber 11; the specific operations were as follows: A11 parts of experimental soil were placed into the bottom layer of the first test chamber 11 until A11 parts of experimental soil were located at the height of the first embedded clapboard 112, then the pretreated earthworm was put, then wheat seeds were put in the embedded hole 1121, and then the embedded clapboard 112 was inserted into the first housing 111; then the above steps were repeated successively, and A12 parts of test soil, A13 parts of test soil and A14 parts of test soil were loaded into the first test chamber 11 from bottom to upper layer; the steps were repeated to put the test soil in group A1, A2, A3, A4 and A5 and the normal soil in group A6 into the first test chambers 11;
[0116] then, zebrafish and deionized water were put into the second test chambers 21; wherein, 20 zebrafish were placed in each second test chamber 21;
[0117] hydroponic vegetables and deionized water were placed inside the third test chamber 31; wherein, the hydroponic vegetables were lettuce seedlings growing for day 10;
[0118] Initiate an experiment: the spraying member 133 was used to always maintain the maximum water content of the test soil inside the first test chambers 11 to be 60%; water containing pollutants, permeable from the first test chambers 11 and temporarily stored in the buffer cavities 134 was introduced into the second test chamber 21 by utilizing the first connection component 131;
[0119] the second connection component 32 was used to always maintain the one-to-one correspondence circulation of water currents in the second test chambers 21 and the third test chambers 31.