CN101698862A - Detection method for acute biological toxicity of drinking water contained in plastic bottle - Google Patents

Detection method for acute biological toxicity of drinking water contained in plastic bottle Download PDF

Info

Publication number
CN101698862A
CN101698862A CN200910196924A CN200910196924A CN101698862A CN 101698862 A CN101698862 A CN 101698862A CN 200910196924 A CN200910196924 A CN 200910196924A CN 200910196924 A CN200910196924 A CN 200910196924A CN 101698862 A CN101698862 A CN 101698862A
Authority
CN
China
Prior art keywords
sample
liquid
plastic bottle
test
bacterium liquid
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
CN200910196924A
Other languages
Chinese (zh)
Inventor
朱文杰
徐亚同
张亚旦
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.)
East China Normal University
Original Assignee
East China Normal 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 East China Normal University filed Critical East China Normal University
Priority to CN200910196924A priority Critical patent/CN101698862A/en
Publication of CN101698862A publication Critical patent/CN101698862A/en
Pending legal-status Critical Current

Links

Landscapes

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

Abstract

The invention relates to a detection method for the acute biological toxicity of drinking water contained in a plastic bottle, belonging to the technical field of drinking water detection. The method comprises the following steps: preparing a bacterial liquid used in tests from a fresh bacterial liquid or a bacterial liquid of freeze-dried powder, preparing a drinking water sample liquid, a control sample liquid, and a detection sample liquid for a plastic bottle, preparing a set of sample parallel samples by using the drinking water sample liquid or the detection sample liquid for the plastic bottle, then preparing a set of control parallel samples, adding 0.1 ml of fresh bacterial liquid or 0.05 ml of bacterial liquid of freeze-dried powder to each set of parallel samples, respectively placing for 15 min, determining the illumination intensity of one sample in each small test cup by a luminescence detecting device, and then calculating the relative illumination intensity. Compared with the prior art, the invention uses a freshwater luminescent bacterium peculiar to China, Vibrio-qinghaiensissp, as a detection strain, and the luminescent bacteria can grow and give out light without sodium chlorides. The invention has the advantages that the physical and chemical characteristics of the samples can not be changed, the correctness of the tests is ensured, and the detection speed is high.

Description

A kind of detection method of acute biological toxicity of drinking water contained in plastic bottle
[technical field]
The present invention relates to tap water detection technique field, relate in particular to a kind of detection method of acute biological toxicity of drinking water contained in plastic bottle.
[background technology]
People need drink water every day, and safety of drinking water can not be ignored.The sales volume of bottled drinking water is very big at present, kind is also various, existing pure water, distilled water, natural mineral water or artificial mineralized water are also arranged, and their majorities all use Plastic Bottle as container, for these commodity tap water, the standard that country has " bottle (bucket) dress sanitary standard for drinking water " GB 19298-2003 to determine, wherein stipulated the detection index that some are main, comprised sense organ, physics and chemistry and microbiological indicator, this type of detects the assessment that index does not relate to bio-toxicity basically.With regard to existing situation as can be known, the detection that lacks bio-toxicity is a great disappearance of safety control, and for example the people is for poisoning, the illegally appearance of foodstuff additive, or the existence of heavy metal ion, health that all can the serious threat drinking person.
With regard to existing detection means supervision is helpless, because the detection method of physics or chemistry often relatively lags behind, only detect at known chemical substance, and the appearance of at present a large amount of syntheticses, make the conventional sense method hard to guard against, if the detection method with present national standard detects, often want several talentes to have the result, can not before listing, just judge; In addition, except learning the concentration that detects thing, the judgement that lacks bio-toxicity, for example: can find the content of the heavy metal of mercury and so on, but can't judge when this kind content status, this tap water is to eater's safety whether, especially a certain method that adopts in the GB can only be at certain material, material for not regulation detection then can not detect, so often have omission, causes the generation of acute poisoning incident.
Be the incident that prevents that posing a health risk from appearring in tap water, be necessary to carry out a kind of brand-new safety detection method.
At present, photogenic bacterium toxicity detection method has been widely used in the pollution of water quality and bio-toxicity is judged, and is simple and easy to do with it, detect advantage such as with low cost and receive publicity, can be referring to the mensuration of acute toxicity of water quality---photogenic bacterium method, GB/T15441-1995; But if detect, then need in sample, to add sodium-chlor and reach 3% final concentration, might change the physicochemical property of sample after so the sodium-chlor of high density adds, the exactness of influence test with the ocean luminescent bacteria.But Shang Weijian is useful on the detection fast and safely of drinking bottled water.
[summary of the invention]
The objective of the invention is to overcome the deficiencies in the prior art, employing Qinghai Vibrion Q67 substratum is made fresh bacterium liquid or is adopted the Qinghai Vibrion lyophilized powder to make test and use bacterium liquid, and a kind of method that detects the bottled drinking water security fast of designing.
For achieving the above object, the present invention proposes a kind of detection method of acute biological toxicity of drinking water contained in plastic bottle, it is characterized in that step is as follows: bacterium liquid is used in (1) preparation test: adopt fresh bacterium liquid or lyophilisate bacterium liquid, described fresh bacterium liquid is the slant strains with Qinghai Vibrion Q67 bacterial strain, move and receive on the fresh inclined-plane, cultivate 12h-18h for 15-25 ℃, this moment, bacterial luminescence was bright, with 10ml 0.85% physiological saline lawn is softly washed away from the inclined-plane, shake up, adjust bacterial concentration with a small amount of physiological saline, get the adjusted bacterium liquid of 0.1ml, add and to be equipped with in the sample test cell of 2ml0.85% physiological saline, detect with photometer luminous, select for use luminous intensity at the bacterium liquid of 200-500 ten thousand photons/second as fresh bacterium liquid; Described lyophilisate bacterium liquid is to add the 5mL resuscitation fluid in Qinghai Vibrion Q67 lyophilisate, thorough mixing, and the following placement of room temperature 8-15 minute makes bacterium recover luminous, promptly can be used as test bacterium liquid; (2) preparation sample: get bottled drinking water to be detected, add NaCl to final concentration be 0.8% as the tap water sample liquid; The inferior boiling point distilled water that adopts secondary heavily to steam, add NaCl to final concentration be 0.8% sample liquid in contrast; Clip Plastic Bottle 2g puts into triangular flask, adds the NaCl solution of 15ml 0.8%, and with 108 ℃ of sterilization 30min, gained solution is the Plastic Bottle steeping fluid, makes extract, and is as the test sample liquid of Plastic Bottle, standby; (3) to the luminous detection of sample: get six test cuvettes, wherein three test cuvettes add 2ml tap water sample liquid or Plastic Bottle respectively test sample liquid as one group of parallel sample of sample, in addition three test cuvettes are put into 2ml control sample liquid respectively and are also contrasted parallel sample as one group; Add fresh bacterium liquid of 0.1ml or 0.05ml lyophilisate bacterium liquid successively every 15s in three test cuvettes in every group of parallel sample, after placing 15min respectively, just adopt the luminous detection instrument to test the luminous intensity of sample in the cuvette every 15s between every group of parallel sample like this, calculate relative luminous intensity then.
It is OD that a small amount of physiological saline of described usefulness is adjusted bacterial concentration 660Be 0.2~0.5.
Described resuscitation fluid is that volumetric molar concentration is 0.05-0.2M, and pH value is the phosphoric acid buffer of 6.0-9.0, or quality-concentration of volume percent is the Glucose Liquid of 0.5-8.0%.
The relative luminous intensity of tap water is 95%~150% safety, and>150% or 80~95% is suspicious, and<80% is dangerous.
The relative luminous intensity of tap water Plastic Bottle is 95%~120% safety, and>120% or 80~95% is suspicious, and<80% is dangerous.
The present invention compares with prior art, utilize photogenic bacterium to external world poisonous substance the characteristics of sensitive reaction are arranged, adopting the exclusive a kind of fresh water photogenic bacterium of China---Qinghai Vibrion is used bacterial classification as detecting, adopt the exclusive a kind of fresh water photogenic bacterium Qinghai Vibrion Q67 bacterial strain of China that all kinds of poisonous substances are all had the sensitive reaction, and used Qinghai Vibrion is a fresh water type luminescent bacteria, need not sodium-chlor just can grow with luminous, therefore need not to add high density chlorination sodium in the specimen, can not change the physicochemical property of sample, guarantee the exactness of test, the safety detection that is used for bottled water, at first be that detection speed is fast: in 1 hour, can obtain a result, generally can whether assess its edible safety selling the previous crops detection; Secondly, be judgement: whether have the acute biological toxicity material to be present in the sample, can make safe, dangerous or suspicious judgement to sample to edible safety.
[embodiment]
Adopt the distinctive fresh water photogenic bacterium of China-Qinghai Vibrion Q67 bacterial strain Vibrio qinghaiensis Q67 among the present invention; be to being present in the reflection of the comprehensive toxicity of institute's Toxic in the sample; even the new synthetics that never occurred; as long as it is poisonous to organism; can make a difference to photogenic bacterium; and reflect from the luminous power of photogenic bacterium delicately; modern photon detection technique is very sensitive; atomic weak light intensity has taken place to change and also can detect; so extremely sensitive with the luminous detection of photogenic bacterium to the reaction of poisonous substance, than the general biomass cells several magnitude that is quick on the draw.
The luminous detection instrument: the BHP95114 type water quality toxicity analyser that adopts Binsong Photon Technology Co., Ltd. Beijing to produce is the test instrument.
The Qinghai Vibrion Q67 bacterial strain Vibrio qinghaiensis Q67 that adopts among the present invention is by red legend outstanding person, Wang Jie; the novel species of a kind of photogenic bacterium that Chen Xiaoyun etc. find; be published in document: Oceanologia et Limnologia Sinica, 25 (3): 273-278, this Qinghai Vibrion Q67 medium component is as follows:
MgSO 42.47g, MgCO 30.79g, MgBr 20.09g, MgCl 20.109g, CaCO 30.103g, KCl 0.122g, NaCl 8.29g, Mg (HCO 3) 20.50g, yeast extract paste 5g, tryptone 5g, glycerine 3g, agar 20g, be dissolved in the 1000mL distilled water, with its bevel, in 121 ℃ of sterilization 20min, it is standby to store in 4 ℃ of refrigerators.
The luminescent bacteria lyophilisate, the lyophilisate that employing is made into by above-mentioned bacterial classification, the patent No. of this lyophilisate: 97106203.X, can buy by market, be stored among-20 ℃ of refrigerators, use front opening, make it dissolving with an amount of resuscitation fluid, about 10 minutes, recover luminous vigor, just can be used for detecting, this resuscitation fluid is with reference to East China Normal University's journal (natural science edition, 2008,4,58-65 delivers, " isolation identification of Qinghai Lake photogenic bacterium and the electron microscopic observation " write articles by Mi Qin etc.
The luminous detection data computing adopts following formula:
The tap water evaluation of result:
The effect toxicity grading Relative luminous intensity
Safety ?95%~150%
Suspicious >150% or 80~95%
Dangerous ?<80%
Tap water Plastic Bottle evaluation of result:
The effect classification Relative luminous intensity
Safety 95%~120%
Suspicious >120% or 80~95%
Dangerous <80%
Embodiment 1
One, test is prepared with bacterium liquid
1, the preparation of fresh bacterium liquid:
With the slant strains of above-mentioned Qinghai Vibrion Q67 bacterial strain, move and receive on the fresh inclined-plane, cultivate 12h-18h for 15-25 ℃; this moment, bacterial luminescence was bright, with 10ml 0.85%NaCl solution, lawn was softly washed away from the inclined-plane; shake up, adjust bacterial concentration, make bacterial concentration OD with a small amount of physiological saline 660About ≈ 0.3, get 0.1ml bacterium liquid, adding is equipped with in the sample test cell of 2ml physiological saline, and is luminous with the photometer detection, and luminous intensity is when 200-500 ten thousand photons/second, and this fresh bacterium liquid just can be used as the bacterium liquid of test usefulness.
2, the preparation of lyophilisate bacterium liquid:
In Qinghai Vibrion Q67 bacterial strain lyophilisate, add the 5ml resuscitation fluid, thorough mixing, the following placement of room temperature about 10 minutes makes bacterium recover luminous, obtains lyophilisate bacterium liquid, also can be used as test bacterium liquid.
Embodiment 1
The bottled pure water water quality toxicity detects
One, sampling
(1) bottled water sample liquid: an amount of with bottled pure water, add NaCl to final concentration be 0.8%.
(2) contrast water sample liquid: with the inferior boiling point distilled water that secondary heavily steams, add NaCl to final concentration be 0.8%.
Two, luminous detection
Be ready to three test cuvettes, each cuvette respectively adds 2ml bottled water sample liquid, is made as three parallel samples; Control sample liquid is also got three test cuvettes, each adds 2ml, three parallel samples are set equally, add fresh bacterium liquid 0.1ml or lyophilized powder bacterium liquid 0.05ml successively as test bacterium liquid, the timed interval that each test cuvette adds bacterium liquid is 15s, after placing 15min, measure the luminous intensity of each measuring cup, calculating relative luminous intensity with the luminous detection instrument 15s of being separated by successively.
Three, luminous detection data computing:
Four, test result evaluation:
Figure G2009101969242D0000071
Figure G2009101969242D0000072
Embodiment 2
Bottled distilled water water quality toxicity detects:
One, sampling
(1) directly get the distilled water sample: it is an amount of to get bottled distilled water, add NaCl to final concentration be 0.8%.
(2) blank water sample contrast, with the inferior boiling point distilled water that secondary heavily steams, add NaCl to final concentration be 0.8%.
Two, luminous detection
The BHP95114 type water quality toxicity analyser that adopts Binsong Photon Technology Co., Ltd. Beijing to produce is the test instrument.
Can use lyophilized powder bacterium liquid, also can use fresh bacterium liquid.
Be ready to three test cuvettes, each cuvette respectively adds 2ml distilled water sample, be made as three parallel samples, three test cuvettes are also got in blank water sample contrast, and each adds 2ml, three parallel samples are set equally, each test cuvette 15s at interval adds fresh bacterium liquid 0.1ml or lyophilisate bacterium liquid 0.05ml successively, as test bacterium liquid, after each test cuvette is placed 15min, measure the luminous intensity respectively test cuvette with the luminous detection instrument 15s of being separated by successively, calculate relative luminous intensity.
Three, luminous detection data computing
Four, test result evaluation
Figure G2009101969242D0000081
Figure G2009101969242D0000082
Embodiment 3
The detection of bottled natural mineral water
One, sampling
(1) directly get the preparation that mineral water is cooked sample liquid: an amount of with bottled natural mineral water, add NaCl to final concentration be 0.8%.
(2) preparation of blank sample liquid: the inferior boiling point distilled water that heavily steams with secondary, add NaCl to final concentration be 0.8%.
Two, luminous detection
Be ready to three test cuvettes, each cuvette respectively adds 2ml mineral water sample liquid, is made as three parallel samples; Control sample liquid is also got three test cuvettes, each adds 2ml, three parallel samples are set equally, add fresh bacterium liquid 0.1ml or lyophilized powder bacterium liquid 0.05ml successively as test bacterium liquid, the timed interval that each test cuvette adds bacterium liquid is 15s, after placing 15min, measure the luminous intensity of each measuring cup, calculating relative luminous intensity with the luminous detection instrument 15s of being separated by successively.
Three, luminous detection data computing:
Test result is estimated:
Figure G2009101969242D0000091
Figure G2009101969242D0000092
Embodiment 4
Bottled artificial mineral water's detection
One, sampling
(1) directly get the preparation of artificial mineral water's sample liquid: an amount of with bottled natural mineral water, add NaCl to final concentration be 0.8%.
(2) preparation of blank sample liquid: the inferior boiling point distilled water that heavily steams with secondary, add NaCl to final concentration be 0.8%.
Two, luminous detection
Be ready to three test cuvettes, each cuvette respectively adds 2ml artificial mineral water sample liquid, is made as three parallel samples; Control sample liquid is also got three test cuvettes, each adds 2ml, three parallel samples are set equally, add fresh bacterium liquid 0.1ml or lyophilized powder bacterium liquid 0.05ml successively as test bacterium liquid, the timed interval that each test cuvette adds bacterium liquid is 15s, after placing 15min, measure the luminous intensity of each measuring cup, calculating relative luminous intensity with the luminous detection instrument 15s of being separated by successively.
Three, luminous detection data computing
Four, test result evaluation:
Figure G2009101969242D0000101
Embodiment 5
The detection of Plastic Bottle
One, sampling
(1) blank sample liquid: the inferior boiling point distilled water that heavily steams with secondary, add NaCl to final concentration be 0.8%.
(2) preparation of Plastic Bottle sample steeping fluid: the Plastic Bottle sample is cut into the square of 1cm * 1cm, takes by weighing 2g and put in the triangular flask, add 15ml 0.8%NaCl solution, with 108 ℃ of sterilization 30min, gained solution is Plastic Bottle sample extract, and is as Plastic Bottle detected sample liquid, stand-by.
Two, luminous detection
Be ready to three test cuvettes, each cuvette respectively adds the detected sample liquid of 2ml Plastic Bottle, is made as three parallel samples; Control sample liquid is also got three test cuvettes, each adds 2ml, three parallel samples are set equally, add fresh bacterium liquid 0.1ml or lyophilized powder bacterium liquid 0.05ml successively as test bacterium liquid, the timed interval that each test cuvette adds bacterium liquid is 15s, after placing 15min, measure the luminous intensity of each measuring cup, calculating relative luminous intensity with the luminous detection instrument 15s of being separated by successively.
Three, luminous detection data computing
Four, test result evaluation:
Sample liquid (adopting the test of lyophilisate bacterium liquid) Luminous intensity (%) The effect toxicity grading
?F ??100.5 Safety
?Z ??89 Suspicious
?S ??74 Dangerous

Claims (5)

1. the detection method of an acute biological toxicity of drinking water contained in plastic bottle, it is characterized in that step is as follows: bacterium liquid is used in (1) preparation test: adopt fresh bacterium liquid or lyophilisate bacterium liquid, described fresh bacterium liquid is the slant strains with Qinghai Vibrion Q67 bacterial strain, move and receive on the fresh inclined-plane, cultivate 12h-18h for 15-25 ℃, this moment, bacterial luminescence was bright, with 10ml 0.85% physiological saline lawn is softly washed away from the inclined-plane, shake up, adjust bacterial concentration with a small amount of physiological saline, get the adjusted bacterium liquid of 0.1ml, add and be equipped with in the sample test cell of 2ml 0.85% physiological saline, detect with photometer luminous, select for use luminous intensity at the bacterium liquid of 200-500 ten thousand photons/second as fresh bacterium liquid; Described lyophilisate bacterium liquid is to add the 5mL resuscitation fluid in Qinghai Vibrion Q67 lyophilisate, thorough mixing, and the following placement of room temperature 8-15 minute makes bacterium recover luminous, promptly can be used as test bacterium liquid; (2) preparation sample: get bottled drinking water to be detected, add NaCl to final concentration be 0.8% as the tap water sample liquid; The inferior boiling point distilled water that adopts secondary heavily to steam, add NaCl to final concentration be 0.8% sample liquid in contrast; Clip Plastic Bottle 2g puts into triangular flask, adds the NaCl solution of 15ml 0.8%, and with 108 ℃ of sterilization 30min, gained solution is the Plastic Bottle steeping fluid, makes extract, and is as the test sample liquid of Plastic Bottle, standby; (3) to the luminous detection of sample: get six test cuvettes, wherein three test cuvettes add 2ml tap water sample liquid or Plastic Bottle respectively test sample liquid as one group of parallel sample of sample, in addition three test cuvettes are put into 2ml control sample liquid respectively and are also contrasted parallel sample as one group; Add fresh bacterium liquid of 0.1ml or 0.05ml lyophilisate bacterium liquid successively every 15s in three test cuvettes in every group of parallel sample, after placing 15min respectively, just adopt the luminous detection instrument to test the luminous intensity of sample in the cuvette every 15s between every group of parallel sample like this, calculate relative luminous intensity then.
2. the detection method of a kind of acute biological toxicity of drinking water contained in plastic bottle as claimed in claim 1 is characterized in that: it is OD that a small amount of physiological saline of described usefulness is adjusted bacterial concentration 660Be 0.2~0.5.
3. the detection method of a kind of acute biological toxicity of drinking water contained in plastic bottle as claimed in claim 1, it is characterized in that: described resuscitation fluid is that volumetric molar concentration is 0.05-0.2M, pH value is the phosphoric acid buffer of 6.0-9.0, or quality-concentration of volume percent is the Glucose Liquid of 0.5-8.0%.
4. the detection method of a kind of acute biological toxicity of drinking water contained in plastic bottle as claimed in claim 1, it is characterized in that: the relative luminous intensity of tap water is 95%~150% safety, and>150% or 80~95% is suspicious, and<80% is dangerous.
5. the detection method of a kind of acute biological toxicity of drinking water contained in plastic bottle as claimed in claim 1, it is characterized in that: the relative luminous intensity of tap water Plastic Bottle is 95%~120% safety, and>120% or 80~95% is suspicious, and<80% is dangerous.
CN200910196924A 2009-10-09 2009-10-09 Detection method for acute biological toxicity of drinking water contained in plastic bottle Pending CN101698862A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN200910196924A CN101698862A (en) 2009-10-09 2009-10-09 Detection method for acute biological toxicity of drinking water contained in plastic bottle

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN200910196924A CN101698862A (en) 2009-10-09 2009-10-09 Detection method for acute biological toxicity of drinking water contained in plastic bottle

Publications (1)

Publication Number Publication Date
CN101698862A true CN101698862A (en) 2010-04-28

Family

ID=42147327

Family Applications (1)

Application Number Title Priority Date Filing Date
CN200910196924A Pending CN101698862A (en) 2009-10-09 2009-10-09 Detection method for acute biological toxicity of drinking water contained in plastic bottle

Country Status (1)

Country Link
CN (1) CN101698862A (en)

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102175828A (en) * 2011-01-20 2011-09-07 济南市供排水监测中心 Method for evaluating water quality health risk with chromium ion as standard toxic substance
CN102435599A (en) * 2011-09-14 2012-05-02 同济大学 Method for predicting combined chronic toxicity of antibiotic pollutant
CN102453743A (en) * 2010-10-28 2012-05-16 华东师范大学 Method for preparing source water quality acute biotoxicity detection reagent and detection method of detection reagent
CN102507447A (en) * 2011-10-25 2012-06-20 中国科学院华南植物园 Method for measuring mycotoxin fusaric acid by using Vibrio-qinghaiensis Sp.Nov. (strain Q67)
CN103149199A (en) * 2012-12-25 2013-06-12 北京城市排水集团有限责任公司 Manufacturing method of water-quality acute toxicity high throughput rapid determination reagent kit and using method thereof
CN103424401A (en) * 2013-08-22 2013-12-04 四川省中医药科学院 Biological testing method for quickly testing comprehensive toxicity of herba houttuyniae injection
CN105588831A (en) * 2016-01-04 2016-05-18 中国科学院城市环境研究所 Method for detecting acute toxicity of rare earth tailing pond surrounding groundwater pollution by using freshwater luminescent bacteria
CN105987898A (en) * 2015-03-05 2016-10-05 上海市南洋模范中学 Detection method for acute biological toxicities of pollutants on dust-haze day
CN106546579A (en) * 2016-10-28 2017-03-29 华南理工大学 A kind of organic solvent improves the method that photobacteria detects toxicant susceptibility
CN107045026A (en) * 2017-03-28 2017-08-15 中国科学院华南植物园 A kind of method that utilization Qinghai Vibrion q67 detects mycotoxin
CN108507999A (en) * 2018-03-26 2018-09-07 成都飞航智库科技有限公司 One kind being applied to bio-toxicity detection method in biotechnology

Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102453743A (en) * 2010-10-28 2012-05-16 华东师范大学 Method for preparing source water quality acute biotoxicity detection reagent and detection method of detection reagent
CN102175828A (en) * 2011-01-20 2011-09-07 济南市供排水监测中心 Method for evaluating water quality health risk with chromium ion as standard toxic substance
CN102175828B (en) * 2011-01-20 2014-06-11 济南市供排水监测中心 Method for evaluating water quality health risk with chromium ion as standard toxic substance
CN102435599A (en) * 2011-09-14 2012-05-02 同济大学 Method for predicting combined chronic toxicity of antibiotic pollutant
CN102507447B (en) * 2011-10-25 2013-12-18 中国科学院华南植物园 Method for measuring mycotoxin fusaric acid by using Vibrio-qinghaiensis Sp.Nov. (strain Q67)
CN102507447A (en) * 2011-10-25 2012-06-20 中国科学院华南植物园 Method for measuring mycotoxin fusaric acid by using Vibrio-qinghaiensis Sp.Nov. (strain Q67)
CN103149199A (en) * 2012-12-25 2013-06-12 北京城市排水集团有限责任公司 Manufacturing method of water-quality acute toxicity high throughput rapid determination reagent kit and using method thereof
CN103149199B (en) * 2012-12-25 2015-05-27 北京城市排水集团有限责任公司 Manufacturing method of water-quality acute toxicity high throughput rapid determination reagent kit and using method thereof
CN103424401A (en) * 2013-08-22 2013-12-04 四川省中医药科学院 Biological testing method for quickly testing comprehensive toxicity of herba houttuyniae injection
CN103424401B (en) * 2013-08-22 2016-02-17 四川省中医药科学院 A kind of biological test method of quick detection houttuynia cordata injection comprehensive toxicity
CN105987898A (en) * 2015-03-05 2016-10-05 上海市南洋模范中学 Detection method for acute biological toxicities of pollutants on dust-haze day
CN105588831A (en) * 2016-01-04 2016-05-18 中国科学院城市环境研究所 Method for detecting acute toxicity of rare earth tailing pond surrounding groundwater pollution by using freshwater luminescent bacteria
CN106546579A (en) * 2016-10-28 2017-03-29 华南理工大学 A kind of organic solvent improves the method that photobacteria detects toxicant susceptibility
CN107045026A (en) * 2017-03-28 2017-08-15 中国科学院华南植物园 A kind of method that utilization Qinghai Vibrion q67 detects mycotoxin
CN108507999A (en) * 2018-03-26 2018-09-07 成都飞航智库科技有限公司 One kind being applied to bio-toxicity detection method in biotechnology

Similar Documents

Publication Publication Date Title
CN101698862A (en) Detection method for acute biological toxicity of drinking water contained in plastic bottle
Das et al. Dental fluorosis and urinary fluoride concentration as a reflection of fluoride exposure and its impact on IQ level and BMI of children of Laxmisagar, Simlapal Block of Bankura District, WB, India
Ardyna et al. Environmental forcing of phytoplankton community structure and function in the Canadian High Arctic: contrasting oligotrophic and eutrophic regions
Wynne et al. Characterizing a cyanobacterial bloom in western Lake Erie using satellite imagery and meteorological data
Lennon et al. Source and supply of terrestrial organic matter affects aquatic microbial metabolism
Bouvy et al. Trophic interactions between viruses, bacteria and nanoflagellates under various nutrient conditions and simulated climate change
Latasa et al. Preferences of phytoplankton groups for waters of different trophic status in the northwestern Mediterranean Sea
CN102453743A (en) Method for preparing source water quality acute biotoxicity detection reagent and detection method of detection reagent
Ket et al. Effects of five years of nitrogen and phosphorus additions on a Zizaniopsis miliacea tidal freshwater marsh
Caburlotto et al. Integrated evaluation of environmental parameters influencing Vibrio occurrence in the coastal Northern Adriatic Sea (Italy) facing the Venetian lagoon
CN101071103B (en) Method for detecting comprehensive toxicity of fresh meat, fresh milk and food
Alonso-Laita et al. Contrasting patterns of phytoplankton viability in the subtropical NE Atlantic Ocean
Hollingdale et al. Feasibility study on production of a matrix reference material for cyanobacterial toxins
Xu et al. Investigations on boron levels in drinking water sources in China
CN101339134A (en) Method for quickly detecting vegetable integrated toxicity
Lasternas et al. The percentage of living bacterial cells related to organic carbon release from senescent oceanic phytoplankton
Zhai et al. Phytoplankton pigment patterns and community composition in the northern South China Sea during winter
Putland et al. Microzooplankton: major herbivores in an estuarine planktonic food web
White et al. Changes in cyanoprokaryote populations, Microcystis morphology, and microcystin concentrations in Lake Elphinstone (Central Queensland, Australia)
Hay et al. Distribution of diatom surface sediment assemblages within Effingham Inlet, a temperate fjord on the west coast of Vancouver Island (Canada)
CN103045524A (en) Vibrio qinghaiensis Q67B and separation, screening and application thereof
Krivokapić et al. Algal pigments distribution and phytoplankton group assemblages in the coastal transitional environment–Boka Kotorska Bay (Southeastern Adriatic Sea)
Šupraha et al. The phytoplankton composition and spatial distribution in the north-eastern Adriatic Channel in autumn 2008
CN104833779B (en) A kind of high-quality pickles bittern detection method
Fauziah et al. Status of groundwater contamination in rural area, Kelantan

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20100428