CN103276042B - Method for detecting genetic toxicity of organic pollutants in water - Google Patents

Method for detecting genetic toxicity of organic pollutants in water Download PDF

Info

Publication number
CN103276042B
CN103276042B CN201310200244.XA CN201310200244A CN103276042B CN 103276042 B CN103276042 B CN 103276042B CN 201310200244 A CN201310200244 A CN 201310200244A CN 103276042 B CN103276042 B CN 103276042B
Authority
CN
China
Prior art keywords
gobiocypris rarus
determinand
aqueous solution
gobiocypris
rarus
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.)
Expired - Fee Related
Application number
CN201310200244.XA
Other languages
Chinese (zh)
Other versions
CN103276042A (en
Inventor
王子健
刘楠楠
马梅
査金苗
许宜平
饶凯锋
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.)
Research Center for Eco Environmental Sciences of CAS
Original Assignee
Research Center for Eco Environmental Sciences of CAS
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 Research Center for Eco Environmental Sciences of CAS filed Critical Research Center for Eco Environmental Sciences of CAS
Priority to CN201310200244.XA priority Critical patent/CN103276042B/en
Publication of CN103276042A publication Critical patent/CN103276042A/en
Application granted granted Critical
Publication of CN103276042B publication Critical patent/CN103276042B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)

Abstract

The invention provides a method for detecting the genetic toxicity of organic pollutants. The method comprises the following steps of: (1) treating gobiocypris rarus by a water solution of an organic-pollutant-containing sample to be detected in an exposed way; and (2) detecting the peripheral blood erythrocyte of the gobiocypris rarus which is treated in the exposed way, carrying out statistics on cell micronucleus rate and drawing a dosage-effect curve. The detection method is sensitive, simple, convenient, rapid, more visual and accurate, has good result repeatability, and has important significance for the research of genetic toxicity of water quality.

Description

A kind of genotoxic method of detection organic pollutants
Technical field
The invention belongs to Study of Water Environment field, relate to a kind of genotoxic method of detection organic pollutant.
Background technology
Environmental pollution increases the weight of, and brings threat to the health of people.Various research method has been carried out and has been evaluated genetoxic, proposes micronucleus test so far first from Heddle etc., micronucleus test because it is economical, simple and easy to do, confidence level advantages of higher is more and more widely used in karyomit(e)/detection of spindle body damaging effect.
Hereditary poisonous substance in water surrounding can bring out fish body and produce micronucleus, by the change of monitoring Erythrocyte Micronucleus of Fishes rate can Study of Exogenous thing genetoxic and evaluate ambient water quality.At present, investigator discusses to the validity that the micronucleus in erythrocytes of multiple fish is tested, domestic scholars application Chinese tradition fish crucian, carp, silver carp and bighead etc. successfully take in situ test to evaluate ambient water quality, confirm the feasibility of fish peripheral red blood cells as the biomarker of the hereditary poisonous substance chromosome damage of monitoring.And along with Economic development and process of industrialization aggravation, water body is polluted by a large amount of organic pollutant, wherein manyly belong to carcinogenic, teratogenesis, mutagenic matter.Organic Pollutants In Water is not yet carried out Gobiocypris rarus peripheral red blood cells genotoxicity testing method detect delay.
Summary of the invention
An object of the present invention is to provide a kind of genotoxic detection method detecting organic pollutant in sample, comprise following steps:
(1) with the aqueous solution of testing sample, process Gobiocypris rarus is exposed;
(2) peripheral red blood cells of the Gobiocypris rarus after exposing process is detected, statistics cell micronucleus rate.
Described detection method is the genetoxic judging organic pollutant in testing sample according to cell micronucleus rate.
In described step (1), before described exposure process, the peripheral red blood cells micronuclear rates of Gobiocypris rarus is 0.1 ‰.
In described step (1), the described method exposing process is: Gobiocypris rarus is placed in the described aqueous solution containing testing sample, and between resting period, every 2-3d changes and exposes treatment solution once, replaces half at every turn.
In described step (1), lucifuge in described exposure treating processes.
In described step (1), the described time exposing process is 21-28d; Be specially 28d.
In described step (1), the compound method of the aqueous solution of described testing sample is: dilute with water and get final product again after determinand being dissolved in organic solvent.
In described step (2), the described method of peripheral red blood cells detecting the Gobiocypris rarus after exposing process is: after exposing process from step (1), put to death after Gobiocypris rarus get blood, smear, fix, dry, the dyeing of Giemsa application liquid, clean dye liquor, dry, microscopy.
In described method, described organic pollutant is benzo [a] pyrene or 4-nitroquinoline-1-oxide compound.
Another object of the present invention is to provide Gobiocypris rarus and is detecting the application in the genetoxic that causes of organic pollutants.
In described application, described organic pollutant is benzo [a] pyrene or 4-nitroquinoline-1-oxide compound.
Also object of the present invention is to provide a kind of method of auxiliary detection organic pollutants content, comprises following steps:
(1) production standard curve:
A, the determinand preparing a series of concentration known are dissolved in the solution storing solution of organic solvent, and after being diluted in activated carbon treatment, water obtains the determinand aqueous solution of various different concns;
B, expose process Gobiocypris rarus with the determinand aqueous solution of various concentration respectively;
The peripheral red blood cells of the Gobiocypris rarus after C, detection exposure process, statistics cell micronucleus rate;
D, with cell micronucleus rate for ordinate zou, with the concentration of determinand in the described determinand aqueous solution for X-coordinate, production standard curve;
(2) get water sample to be measured, according to method identical in step B and C, exposure process and statistics cell micronucleus rate are carried out to Gobiocypris rarus; Cell micronucleus rate is substituted into the typical curve in above-mentioned steps D, namely obtains the content of determinand in water sample to be measured.
In described step B, before described exposure process, the peripheral red blood cells micronuclear rates of Gobiocypris rarus is 0.1 ‰.
In described step B, the described method exposing process is: Gobiocypris rarus is placed in the described aqueous solution containing testing sample, places, and period every 2-3d changes and exposes treatment solution once, replaces half at every turn.
In described step B, lucifuge in described exposure treating processes.
In described step B, the described time exposing process is 21-28d; Be specially 28d.
In described step C, the described method of peripheral red blood cells detecting the Gobiocypris rarus after exposing process is: after exposing process from step B, put to death after Gobiocypris rarus get blood, smear, fix, dry, the dyeing of Giemsa application liquid, clean dye liquor, dry, microscopy.
In described method, described organic pollutant is benzo [a] pyrene or 4-nitroquinoline-1-oxide compound.
Compared with prior art, tool has the following advantages in the present invention:
1. Gobiocypris rarus is Chinese peculiar small-scale test fish, is easy to standardized study, and reduce the impact of other experimental factors, its peripheral red blood cells micronucleus test can detect organic pollutants genetoxic hazard conditions well.
2. exploitation is for organism exposure chamber and the micronucleus test technology of open-assembly time, and draws dose-effect curve, realizes the quantitative evaluation to hereditary poisonous substance toxicity.
Therefore, the inventive method is sensitive, easy, fast, more directly perceived, accurately, result favorable reproducibility, studies significant for water quality genetoxic.
Accompanying drawing explanation
Fig. 1 is benzo [a] pyrene dose-effect curve.
Fig. 2 is 4-nitroquinoline-1-oxide compound dose-effect curve.
Embodiment
The experimental technique used in following embodiment if no special instructions, is ordinary method.
Material used in following embodiment, reagent etc., if no special instructions, all can obtain from commercial channels.
Below in conjunction with specific embodiment, the invention will be further described, but the present invention is not limited to following examples.
The genotoxic detection of embodiment 1, dimethyl sulfoxide (DMSO)
(1) detection method and step
(1) the raising and train of Gobiocypris rarus: raise and train same batch, Gobiocypris rarus 14d that body weight gain is close, period, its Micronucleus Rate of Peripheral Lymphocytes rate reached about 0.1 ‰ without natural death fish phenomenon, namely can be used for test;
(2) trial test selects the dimethyl sulfoxide (DMSO) of appropriate concentration range to process, without dead fish phenomenon under plan adopts the highest exposure concentrations;
(3) preparation for the treatment of solution is exposed: dimethyl sulfoxide (DMSO) is dissolved in activated carbon treatment tap water, is mixed with the aqueous solution of Volume fraction 0.03%, be the exposure treatment solution prepared;
(4) process is exposed: establish the blank not adding dimethyl sulfoxide (DMSO); Experiment exposure group selects 5 tail Gobiocypris rarus at random, and lucifuge exposes 28d, every 2-3d and changes exposure treatment solution half;
(5) blood smear of Gobiocypris rarus erythrocyte is made: get blood by exposing after the fish after processing is put to death, methyl alcohol fixes 10min, dries, and through Giemsa application liquid dyeing 15min, cleans dye liquor, dries and get final product immediately with the phosphate buffered saline buffer of pH=6.8;
(6) detection of cell micronucleus rate: blood smear is placed in basis of microscopic observation, 10*100 doubly observes, count, choose complete in the visual field, be uniformly dispersed and painted suitable cell, double-blind method diagosis, often open the erythrocytic micronuclear rates of fish of smear counting about 5000 endochylema complete displays, result represents with permillage (‰).The cell micronucleus rate that dimethyl sulfoxide (DMSO) exposed volume mark is corresponding when being 0%, 0.03% is respectively 0.29 ± 0.04 ‰, 0.37 ± 0.06 ‰, and there was no significant difference, shows that dimethyl sulfoxide (DMSO) does not show genetic toxic effect under this test condition.
Embodiment 2, the genotoxic detection of benzo [a] pyrene
(1) detection method and step
(1) the raising and train of Gobiocypris rarus: raise and train same batch, Gobiocypris rarus 14d that body weight gain is close, period, its Micronucleus Rate of Peripheral Lymphocytes rate reached about 0.1 ‰ without natural death fish phenomenon, namely can be used for test;
(2) trial test selects appropriate concentration range to process; Do not observe dead fish phenomenon to intend adopting the highest exposure concentrations to expose process, show to can be used for follow-up micronucleus exposure test.
(3) preparation for the treatment of solution is exposed: be dissolved in dimethyl sulfoxide (DMSO) by benzo [a] pyrene, be mixed with the mother liquor that concentration is respectively 0mg/L, 4/3mg/L, 20/3mg/L, 100/3mg/L, 500/3mg/L, then the mother liquor getting same volume product is respectively dissolved in the tap water of activated carbon filtration, be mixed with the solution of benzo [a] pyrene concentration difference 0 μ g/L, 0.4 μ g/L, 2.0 μ g/L, 10.0 μ g/L, 50.0 μ g/L, be the 5 groups of exposure treatment solutions prepared;
(4) process is exposed: set the dimethyl sulfoxide (DMSO) blank solution that do not add benzo [a] pyrene as control group; Often group selects 10 tail Gobiocypris rarus; Adopt semi-static exposure chamber, namely every 2-3d changes and exposes treatment solution once, a half; Lucifuge exposes 28d;
(5) blood smear of Gobiocypris rarus erythrocyte is made: get blood after being put to death by the fish after exposing process, smear, methyl alcohol fixes 10min, dry, through Giemsa application liquid dyeing 15min, clean dye liquor with the phosphate buffered saline buffer of pH=6.8, dry and get final product immediately;
(6) detection of cell micronucleus rate: blood smear is placed in basis of microscopic observation, 10*100 doubly observes, count, choose complete in the visual field, be uniformly dispersed and painted suitable cell, double-blind method diagosis, often open the erythrocytic micronuclear rates of fish of smear counting about 5000 endochylema complete displays, result represents with permillage (‰).The cell micronucleus rate that exposure concentrations increases successively is respectively 0.37 ± 0.06 ‰, 1.53 ± 0.11 ‰, 4.19 ± 0.08 ‰, 10.29 ± 0.93 ‰, 17.93 ± 0.43 ‰.
Result shows, and when benzo [a] pyrene concentration is 0.4 μ g/L, cell micronucleus rate and blank have significant difference.The detection method of existing bibliographical information is as shown in table 1.
Table 1
Table 1 result shows, compared with existing detection method, detection method sensitivity provided by the invention is higher.
(2) dose-effect curve
With benzo [a] pyrene concentration for X-coordinate, micronucleus permillage is ordinate zou, draws dose-effect curve, as shown in Figure 2.Quantizing dose-effect relationship by dose-effect curve is following formula:
y=2.14(1-e -1.76x)+16.30(1-e -0.069x)
Benzo [a] pyrene 28d exposes fit curve equation change: R 2=0.9994; Adjusted R 2=0.9974
Multiple comparisons shows and to there are differences extremely remarkable between each concentration group, illustrates that benzo [a] pyrene has Genotoxic Effect to Gobiocypris rarus peripheral red blood cells, and has obvious dose-effect relationship.
Embodiment 3,4-nitroquinoline-1-oxide compound (4-NQO) genotoxic detection
(1) detection method and step
(1) the raising and train of Gobiocypris rarus: raise and train same batch, Gobiocypris rarus 14d that body weight gain is close, period, its Micronucleus Rate of Peripheral Lymphocytes rate reached about 0.1 ‰ without natural death fish phenomenon, namely can be used for test;
(2) trial test selects appropriate concentration range to process; Do not observe dead fish phenomenon to intend adopting the highest exposure concentrations to expose process, show to can be used for follow-up micronucleus exposure test;
(3) preparation for the treatment of solution is exposed: be dissolved in dimethyl sulfoxide (DMSO) by 4-nitroquinoline-1-oxide compound (4-NQO), be mixed with the mother liquor that concentration is respectively 0mg/L, 1/3mg/L, 5/3mg/L, 25/3mg/L, 125/3mg/L, then the mother liquor getting same volume product is respectively dissolved in the tap water of activated carbon filtration, be mixed with the solution of 4-NQO concentration difference 0 μ g/L, 0.1 μ g/L, 0.5 μ g/L, 2.5 μ g/L, 12.5 μ g/L, be the 5 groups of exposure treatment solutions prepared;
(4) process is exposed: set the dimethyl sulfoxide (DMSO) blank solution that do not add 4-nitroquinoline-1-oxide compound as control group; Often group selects 10 tail Gobiocypris rarus; Adopt semi-static exposure chamber, namely every 2-3d changes and exposes treatment solution once, a half; Lucifuge exposes 28d;
(5) blood smear of Gobiocypris rarus erythrocyte is made: get blood after being put to death by the fish after exposing process, smear, methyl alcohol fixes 10min, dry, through Giemsa application liquid dyeing 15min, clean dye liquor with the phosphate buffered saline buffer of pH=6.8, dry and get final product immediately;
(6) detection of cell micronucleus rate: blood smear is placed in basis of microscopic observation, 10*100 doubly observes, count, choose complete in the visual field, be uniformly dispersed and painted suitable cell, double-blind method diagosis, often open the erythrocytic micronuclear rates of fish of smear counting about 5000 endochylema complete displays, result represents with permillage (‰).The cell micronucleus rate that exposure concentrations increases successively is respectively 0.37 ± 0.06 ‰, 1.36 ± 0.08 ‰, 4.35 ± 0.40 ‰, 8.89 ± 0.26 ‰, 22.69 ± 0.56 ‰.
Result shows, and when 4-nitroquinoline-1-oxide concentration is 0.1 μ g/L, has significant difference with blank.Document Valentin-Severin, I.et al.Mutation Research-Genetic Toxicology andEnvironmental Mutagenesis [J] .536 (1-2): the genetoxic being detected 4-nitroquinoline-1-oxide compound in 79-90. by human liver cancer cell HepG2, experimental result shows, when cell micronucleus rate reaches two times of negative control micronuclear rates, the concentration of 4-nitroquinoline-1-oxide compound is 22.8 μ g/L.This shows compared with existing detection method, and detection method sensitivity provided by the invention is higher.
(2) dose-effect curve
With 4-nitroquinoline-1-oxide concentration for X-coordinate, micronucleus permillage is ordinate zou, draws dose-effect curve, as shown in Figure 2.Quantizing dose-effect relationship by dose-effect curve is following formula:
y=4.19(1-e -3.24x)+39.26(1-e -0.05x)
4-nitroquinoline-1-oxide compound (4-NQO) 28d exposes fit curve equation change: R 2=0.9996; AdjustedR 2=0.9983
Multiple comparisons shows and to there are differences extremely remarkable between each concentration group, illustrates that 4-nitroquinoline-1-oxide compound has Genotoxic Effect to Gobiocypris rarus peripheral red blood cells, and has obvious dose-effect relationship.

Claims (5)

1. detect a genotoxic detection method for organic pollutant in sample, comprise following steps:
(1) with the aqueous solution of testing sample, process Gobiocypris rarus is exposed;
(2) peripheral red blood cells of the Gobiocypris rarus after exposing process is detected, statistics cell micronucleus rate;
In step (1), the described method exposing process is: Gobiocypris rarus is placed in the described aqueous solution containing testing sample, places, and period every 2-3d changes and exposes treatment solution once, replaces half at every turn;
In described step (1), lucifuge in described exposure treating processes;
In described step (1), the described time exposing process is 21-28d;
In described method, described organic pollutant is benzo [a] pyrene or 4-nitroquinoline-1-oxide compound.
2. method according to claim 1, is characterized in that: in step (1), and before described exposure process, the peripheral red blood cells micronuclear rates of Gobiocypris rarus is 0.1 ‰.
3. Gobiocypris rarus is detecting the application in the genetoxic that causes of organic pollutants.
4. a method for auxiliary detection organic pollutants content, comprises following steps:
(1) production standard curve:
A, the determinand preparing a series of concentration known are dissolved in the solution storing solution of organic solvent, and after being diluted in activated carbon treatment, water obtains the determinand aqueous solution of various different concns;
B, expose process Gobiocypris rarus with the determinand aqueous solution of various concentration respectively;
The peripheral red blood cells of the Gobiocypris rarus after C, detection exposure process, statistics cell micronucleus rate;
D, with cell micronucleus rate for ordinate zou, with the concentration of determinand in the described determinand aqueous solution for X-coordinate, production standard curve;
(2) get water sample to be measured, according to method identical in step B and C, exposure process and statistics cell micronucleus rate are carried out to Gobiocypris rarus; Cell micronucleus rate is substituted into the typical curve in above-mentioned steps D, namely obtains the content of determinand in water sample to be measured;
In step B, the described method exposing process is: Gobiocypris rarus is placed in the described aqueous solution containing testing sample, places, and period every 2-3d changes and exposes treatment solution once, replaces half at every turn;
In described step B, lucifuge in described exposure treating processes;
In described step B, the described time exposing process is 21-28d;
In described method, described organic pollutant is benzo [a] pyrene or 4-nitroquinoline-1-oxide compound.
5. method according to claim 4, is characterized in that: in step B, and before described exposure process, the peripheral red blood cells micronuclear rates of Gobiocypris rarus is 0.1 ‰.
CN201310200244.XA 2013-05-27 2013-05-27 Method for detecting genetic toxicity of organic pollutants in water Expired - Fee Related CN103276042B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310200244.XA CN103276042B (en) 2013-05-27 2013-05-27 Method for detecting genetic toxicity of organic pollutants in water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310200244.XA CN103276042B (en) 2013-05-27 2013-05-27 Method for detecting genetic toxicity of organic pollutants in water

Publications (2)

Publication Number Publication Date
CN103276042A CN103276042A (en) 2013-09-04
CN103276042B true CN103276042B (en) 2015-04-01

Family

ID=49058659

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310200244.XA Expired - Fee Related CN103276042B (en) 2013-05-27 2013-05-27 Method for detecting genetic toxicity of organic pollutants in water

Country Status (1)

Country Link
CN (1) CN103276042B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105301211B (en) * 2014-07-04 2017-07-14 中国环境科学研究院 Semi-static temperature controlled toxicity test device of fishes
CN104830946B (en) * 2015-05-13 2018-07-17 中国环境科学研究院 Environment water causes TK6 cell chromosome damages genetic toxicology assays and application
CN105548514A (en) * 2015-12-25 2016-05-04 哈尔滨工业大学 Multi-genetic terminal biological group test method for evaluating genetic toxicity of industrial wastewater reuse of water treatment plant

Also Published As

Publication number Publication date
CN103276042A (en) 2013-09-04

Similar Documents

Publication Publication Date Title
CN103276042B (en) Method for detecting genetic toxicity of organic pollutants in water
CN102175828B (en) Method for evaluating water quality health risk with chromium ion as standard toxic substance
CN106841334A (en) It is a kind of can real time on-line monitoring contents of many kinds of heavy metal ion detecting system and method
CN105241859A (en) CTS-ZnO fluorescent test paper and preparation method and application thereof
CN1687754A (en) Test paper for detecting heavy metal lead, cadmium, and mercury rapidly, preparation method and application
CN102368053B (en) Detection method of lead ion
Ghaedi et al. Design of an efficient uranyl ion optical sensor based on 1′-2, 2′-(1, 2-phenylene) bis (ethene-2, 1-diyl) dinaphthalen-2-ol
CN104198480A (en) Aqueous quaternary ammonium salt detection test paper and preparation method thereof
CN105510543A (en) Method for detecting genotoxic agent in water by utilization of Pseudorasbora parva
CN103323453B (en) Cadmium detects liquid, testing cassete and assay method fast
CN204575541U (en) A kind of heavy metal ion quick detection test paper box of even colour developing
CN104931668B (en) Biological method for detecting genetic toxicity of polluted water body
CN1687752A (en) Test paper for detecting heavy metal mercury rapidly, preparation method and application
CN206684096U (en) It is a kind of can real time on-line monitoring contents of many kinds of heavy metal ion detecting system
CN105300947A (en) Fluorescence spectrum technology-based dissolved organic matter (DOM) water quality monitoring and early warning method
CN105203510B (en) A kind of microorganism in food rapid detection method
CN102127588A (en) Method for quantitatively detecting toxicity of water quality
CN103472046A (en) Method of analyzing heavy metal pollution of vegetable based on reactive oxygen species level
Rychtecký et al. Spatio-temporal study of phytoplankton cell viability in a eutrophic reservoir using SYTOX Green nucleic acid stain
CN104140997A (en) In-vitro micronucleus detection method for genetic toxicity of water outlet of drinking water disinfection process
CN106018688A (en) Method for estimating toxicity contribution rate of metal nanoparticle ions and nano effect
CN103308659B (en) Water body organic pollution toxicity assessment method based on human-mouse hybridoma cell
CN104865204A (en) Method for F<-> colorimetric detection
CN204575540U (en) A kind of paper box for detecting contents of many kinds of heavy metal ion fast
CN104120179B (en) The detection method of a kind of ocean Petroleum Hydrocarbon concentration

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20150401

Termination date: 20170527

CF01 Termination of patent right due to non-payment of annual fee