NL2030349B1 - Method for isolation and screening and evaluation of antibiotic resistance of e. coli and s. aureus in estuary and nearshore marine environment - Google Patents
Method for isolation and screening and evaluation of antibiotic resistance of e. coli and s. aureus in estuary and nearshore marine environment Download PDFInfo
- Publication number
- NL2030349B1 NL2030349B1 NL2030349A NL2030349A NL2030349B1 NL 2030349 B1 NL2030349 B1 NL 2030349B1 NL 2030349 A NL2030349 A NL 2030349A NL 2030349 A NL2030349 A NL 2030349A NL 2030349 B1 NL2030349 B1 NL 2030349B1
- Authority
- NL
- Netherlands
- Prior art keywords
- aureus
- coli
- filter membrane
- colonies
- antibiotic resistance
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12Q—MEASURING OR TESTING PROCESSES INVOLVING ENZYMES, NUCLEIC ACIDS OR MICROORGANISMS; COMPOSITIONS OR TEST PAPERS THEREFOR; PROCESSES OF PREPARING SUCH COMPOSITIONS; CONDITION-RESPONSIVE CONTROL IN MICROBIOLOGICAL OR ENZYMOLOGICAL PROCESSES
- C12Q1/00—Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions
- C12Q1/02—Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms
- C12Q1/04—Determining presence or kind of microorganism; Use of selective media for testing antibiotics or bacteriocides; Compositions containing a chemical indicator therefor
- C12Q1/10—Enterobacteria
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12Q—MEASURING OR TESTING PROCESSES INVOLVING ENZYMES, NUCLEIC ACIDS OR MICROORGANISMS; COMPOSITIONS OR TEST PAPERS THEREFOR; PROCESSES OF PREPARING SUCH COMPOSITIONS; CONDITION-RESPONSIVE CONTROL IN MICROBIOLOGICAL OR ENZYMOLOGICAL PROCESSES
- C12Q1/00—Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions
- C12Q1/02—Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms
- C12Q1/04—Determining presence or kind of microorganism; Use of selective media for testing antibiotics or bacteriocides; Compositions containing a chemical indicator therefor
- C12Q1/14—Streptococcus; Staphylococcus
Abstract
The present disclosure discloses a method for isolation and screening and evaluation of antibiotic resistance of E. coli and S. aureus in an estuary and a nearshore marine 5 environment. In this method, an MI agar and a VJ agar are immersed with screening antibiotics (such as tetracycline, sulfa and quinolone) to prepare sensitive specific selection agars, and antibiotic-resistant E. coli and S. aureus in the estuary and the nearshore marine environment are quickly isolated and counted to evaluate a resistance level thereof. In the present disclosure, the method for isolation and screening and 10 evaluation of antibiotic resistance of E. coli and S. aureus in an estuary and a nearshore marine environment has simple and easy operations, high accuracy, safety and environmental protection. The method is suitable for rapid analysis and detection of antibiotic resistance levels of the E. coli and the S. aureus in water and sediment samples of coastal oceans, estuaries and sewage outlets into the sea.
Description
METHOD FOR ISOLATION AND SCREENING AND EVALUATION OF
ANTIBIOTIC RESISTANCE OF E. COLI AND S. AUREUS IN ESTUARY AND
NEARSHORE MARINE ENVIRONMENT
S TECHNICAL FIELD
[01] The present disclosure belongs to the technical field of environmental monitoring, and relates to a method for isolation and screening and evaluation of antibiotic resistance of I. coli and S. aureus in an estuary and a nearshore marine environment.
[02] In the field of environmental scientific research and monitoring, there is still a lack of detection methods for antibiotic resistance levels of typical pathogenic microorganisms £. coli and S. aureus.
[03] In the existing technology, the E. coli in environmental media is counted and detected mainly using a fermentation experiment combined with eosin-methylene blue agar or violet red bile agar; and the S. aureus is counted and detected using a Baird-Parker plate and a blood plate combined with Gram staining experiment. However, due to the cumbersome experimental process, long period and requirement of multiple detection and identification tests such as staining microscopy and plasma coagulase test, the above methods are difficult to truly and effectively reflect the true abundance levels of the above two pathogenic microorganisms in the environmental medium, let alone assess the antibiotic resistance levels of the two pathogenic microorganisms.
[04] The present disclosure provides a method for isolation and screening and evaluation of antibiotic resistance of £. coli and S. aureus in an estuary and a nearshore marine environment.
[05] In this method, MI agar and VJ agar are immersed with screening antibiotics (such as tetracycline, sulfa and quinolone) to prepare sensitive specific selection agars, and antibiotic-resistant £. coli and S. aureus in the estuary and the nearshore marine environment are quickly isolated and counted to evaluate a resistance level thereof.
[06] The present disclosure employs the following technical solutions.
[07] A method for isolation and screening and evaluation of antibiotic resistance of £.
coli and S. aureus in an estuary and a nearshore marine environment specifically includes the following steps:
[08] (1) sterilization;
[09] before the experiment, putting a filter membrane between filter papers, and autoclaving the filter membrane together with a filter and a petri dish that are wrapped in a kraft paper at 121°C for 15 min, where before filtering different samples each time, a top of a funnel is scrubbed with alcohol and burned with a flame to eliminate interferences between the samples;
[10] (2) preparation of culture media:
[11] S. aureus: accurately weighing 60 g of a VJ medium (BectonDickinson, New
Jersey), adding 1 L of sterile water, heating to dissolve the VJ medium under constant stirring, boiling for 1 min and sterilizing (103 Kpa, 121°C for 15 min); put a sterilized VJ medium into a 45+1°C water bath to cool, and adding 20 ml of (1%) potassium tellurite; dividing a prepared medium into Erlenmeyer flasks, where one part is used as a VJ agar plate for S. aureus screening (without antibiotics), and the other part is immersed with antibiotics at the minimum inhibitory concentration as a VJ-R agar plate for antibiotic resistance screening;
[12] FE. coli: accurately weighing 36.5 g of an MI medium (BectonDickinson, New
Jersey), adding 1 L of sterile water, heating to dissolve the MI medium under constant stirring, boiling for 1 min and sterilizing (103 Kpa, 121°C for 15 min); put a sterilized MI medium into a 45+1°C water bath to cool, preparing and adding cefsulodine sodium to a final concentration of 5 pg/ml; dividing a prepared medium into Erlenmeyer flasks, where one part is used as an MI agar plate for £. coli screening (without antibiotics), and the other part is immersed with antibiotics at the minimum inhibitory concentration as an MI-
R agar plate for antibiotic resistance screening;
[13] (3) antibiotic resistance test:
[14] 3.1, antibiotic resistance test of water samples:
[15] 3.1.1, selecting appropriate an appropriate volume of samples according to an estimation of a sample collection area and a contamination status, and complementing using a 0.1 M phosphate-buffered saline (PBS) with a pH of 6 when an initial volume of a sample is not more than 50 ml, to prepare a 10-fold gradient dilution homogenate, where it takes not more than 15 min from preparation of sample homogenate to completion of sample inoculation;
[16] 3.1.2, selecting 3 serial dilutions of the sample homogenate, filtering a homogenized test solution through a sterile 0.45 um filter membrane, removing the filter membrane and moving the test solution to solidified MI and VJ control petri dishes and solidified MI-R and VJ-R resistant petri dishes, where three parallel groups are made for each dilution;
[17] 3.1.3, diluting a standard E. coli solution without antibiotic resistances and a standard S. aureus solution without antibiotic resistances to a 0.5 McFarland turbidity standard, operating following steps in 3.1.1 and 3.1.2 and filtering through a sterile filter membrane, and moving the above two bacterial solutions to MI and VJ (as a positive control) culture plates and MI-R and VJ-R (as a negative control) culture plates as a quality control group;
[18] 3.1.4, after the sample is filtered each time, weighing 100 ml of ultrapure water or physiological saline with a graduated cylinder, pouring into a funnel to rinse the funnel twice, scrubbing a top of the funnel with alcohol and burning with a flame to eliminate interferences between the samples;
[19] 3.1.5, holding sterile forceps on an edge of the filter membrane, and lifting the filter membrane slightly to move the filter membrane onto an agar plate, to slide the filter membrane onto the agar plate, wherein a rolling action is conducted to avoid bubbles between the filter membrane and the agar at a bottom; if bubbles appear in non-wet areas, the filter membrane is reset; and
[20] 3.1.6, turning over the petri dish and placing in an incubator, and conducting incubation at a constant temperature of 35+0.5°C for 24-36 h; after the incubation, counting blue colonies on the membrane in the MI petri dish under natural light, and counting gray-black round colonies on the membrane in the VJ petri dish under the natural light, and repeating the counting under long-wave ultraviolet (366 nm) to determine results;
[21] 3.2, antibiotic resistance test of sediment samples:
[22] 3.2.1, selecting appropriate weight of samples according to an estimation of a sample collection area and a contamination status, putting weighed sediment samples into a sterile centrifuge tube containing 50 mL of sterile seawater, vortex-shaking for 3 min and standing for 1 min;
[23] 3.2.2, filtering a test solution after standing for 1 min through a sterile 0.45 um filter membrane, removing the filter membrane and moving the test solution to solidified
MI and VJ control petri dishes and solidified MI-R and VJ-R resistant petri dishes, wherein three parallel groups are made for each sample;
[24] 3.2.3, diluting a standard E. coli solution without antibiotic resistances and a standard S. aureus solution without antibiotic resistances to a 0.5 McFarland turbidity standard, operating following steps in 3.1.1 and 3.1.2 and filtering through a sterile filter membrane, and moving the above two bacterial solutions to MI and VJ (as a positive control) culture plates and MI-R and VJ-R (as a negative control) culture plates as a quality control group;
[25] 3.2.4, after the sample is filtered each time, weighing 100 ml of ultrapure water or physiological saline with a graduated cylinder, pouring into a funnel to rinse the funnel twice, scrubbing a top of the funnel with alcohol and burning with a flame to eliminate interferences between the samples;
[26] 3.2.5, holding sterile forceps on an edge of the filter membrane, and lifting the filter membrane slightly to move the filter membrane onto an agar plate, to slide the filter membrane onto the agar plate, wherein a rolling action is conducted to avoid bubbles between the filter membrane and the agar at a bottom; if bubbles appear in non-wet areas, the filter membrane is reset; and
[27] 3.2.6, turning over the petri dish and placing in an incubator, and conducting incubation at a constant temperature of 35+0.5°C for 24-36 h; after the incubation, counting blue colonies on the membrane in the MI petri dish under natural light, and counting gray-black round colonies on the membrane in the VJ petri dish under the natural light, and repeating the counting under long-wave ultraviolet (366 nm) to determine results; and
[28] (4) data analysis and calculation:
[29] calculating abundance and resistance level of the £. coli and the S. aureus in the sample, where the following basic conditions are needed:
[30] 4.1, a total number of the colonies on the plate 1s <200/plate;
[31] 4.2, atarget number of the colonies on the plate is <100/plate (20-80 is the best);
[32] 4.3, a calculation formula for the abundance of the £. coli and the S. aureus is as follows:
[33] E.coli (S.aureus)/ 100ml =
Number of blue colonies (black colonies)
Ere 100
Number of blue colonies (black colonies) , on a culture plate
[34] E.coli (S.aureus)/g = ee E
[35] 4.4, a calculation formula for the antibiotic resistance rate of the £. coli and the
S. aureus is as follows:
Number of blue colonies (black colonies)
[36] Antibiotic resistance rate % = a oF Solan Ey x 100%. on a control agar plate 5 [37] When collecting samples, sampling tools and related reagent materials should be prepared and sterilized in advance. The water and the sediment samples are collected in a sterile leak-proof polypropylene sample container, refrigerated at 1-4°C and sent back to the laboratory for analysis as soon as possible. The samples should be analyzed within 12 h after collection, and the analysis of a single sample should not exceed 15 min.
[38] Instep 3.1.1, the initial volume selection is as follows: the estuary and the sewage outlet into the sea: 10 ml; the coastal ocean: 300-500 ml.
[39] In step 3.2.1, the initial sample mass selection is as follows: the estuary and the sewage outlet into the sea: 0.1-0.3 g; the coastal ocean: 0.3-0.5 g.
[40] In the MI medium, the E. coli in water is detected using a specific enzyme reaction. The medium includes two enzyme substrates: MUGal (fluorescence) and IBDG (color). Coliform bacteria can produce B-galactosidase to react with the MUGal, to generate a compound that emits fluorescence under the long-wave ultraviolet (366 nm); the E. coli can produce B-glucosidase to react with the IBDG, to produce a blue compound, such that the colony is blue under natural light. A certain concentration of the cefsulodine sodium is added to the medium to inhibit the growth of gram-positive bacteria and other gram-negative bacteria that belong to non-coliform bacteria. In addition, antibiotic- resistant microorganisms are selected by immersing antibiotics at the minimum inhibitory concentration in the medium.
[41] Inthe Vogel-Johnson (VJ) medium, due to the reducing capacity to tellurium and the adaptability to potassium chloride of the S. aureus, the growth of gram-negative bacteria and other bacteria are inhibited by the potassium chloride and the potassium tellurite in the agar medium. In addition, sodium pyruvate is added to repair damaged cells to stimulate the growth of S. aureus, to further increase the detection rate. The 5. aureus can reduce the tellurium to make the colony gray-black.
[42] The present disclosure has the following beneficial effects.
[43] In the present disclosure, the method for isolation and screening and evaluation of antibiotic resistance of £. coli and S. aureus in an estuary and a nearshore marine environment has simple and easy operations, high accuracy, safety and environmental protection. The method is suitable for rapid analysis and detection of antibiotic resistance levels of the £. coli and the S. aureus in water and sediment samples of coastal oceans, estuaries and sewage outlets into the sea.
[44] Although the embodiments of the present disclosure have been illustrated and described, it should be understood that those of ordinary skill in the art may make various changes, modifications, replacements, and variations to the above embodiments without departing from the principle and spirit of the present disclosure, and the scope of the present disclosure is limited by the appended claims and their legal equivalents.
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
NL2030349A NL2030349B1 (en) | 2021-12-29 | 2021-12-29 | Method for isolation and screening and evaluation of antibiotic resistance of e. coli and s. aureus in estuary and nearshore marine environment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
NL2030349A NL2030349B1 (en) | 2021-12-29 | 2021-12-29 | Method for isolation and screening and evaluation of antibiotic resistance of e. coli and s. aureus in estuary and nearshore marine environment |
Publications (1)
Publication Number | Publication Date |
---|---|
NL2030349B1 true NL2030349B1 (en) | 2023-07-04 |
Family
ID=87202420
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
NL2030349A NL2030349B1 (en) | 2021-12-29 | 2021-12-29 | Method for isolation and screening and evaluation of antibiotic resistance of e. coli and s. aureus in estuary and nearshore marine environment |
Country Status (1)
Country | Link |
---|---|
NL (1) | NL2030349B1 (en) |
-
2021
- 2021-12-29 NL NL2030349A patent/NL2030349B1/en active
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP5420566B2 (en) | Microbial system and fluid sample analysis method | |
Madrid et al. | Microbial biomass estimation | |
US20050282244A1 (en) | Method and apparatus for viable and nonviable prokaryotic and eukaryotic cell quantitation | |
US20070003997A1 (en) | Method and apparatus for detecting bacteria | |
CN102071243B (en) | Method for quickly detecting harmful bacteria in beer | |
Ogodo et al. | Microbial techniques and methods: Basic techniques and microscopy | |
Yin et al. | Establishment and application of a novel fluorescence-based analytical method for the rapid detection of viable bacteria in different samples | |
NL2030349B1 (en) | Method for isolation and screening and evaluation of antibiotic resistance of e. coli and s. aureus in estuary and nearshore marine environment | |
CN111041063B (en) | ATP-based method for rapidly evaluating microbial stability in drinking water | |
CN109207554B (en) | Method for rapidly detecting bacteriostatic effect of daily chemical product by using TTC agar culture medium | |
Lee | Quantitation of microorganisms | |
CN111607633A (en) | Total bacterial count counting card and preparation method thereof | |
CN105112497A (en) | Method for separating and screening escherichia coli and staphylococcus aureus in estuary and nearshore marine environments and evaluating resistance of antibiotics | |
CN102517231A (en) | Manganese oxidizing microbe separating and screening method | |
CN110760559A (en) | Rapid detection method for microbial antibiotic sensitivity | |
CN112980917A (en) | Method for quickly quantifying escherichia coli in water | |
CN110272937B (en) | Sensitive detection method for microorganisms in packaged drinking water | |
CN107764754A (en) | A kind of online test method of microbes biomass | |
Dufour | A short history of methods used to measure bathing beach water quality | |
Seeley et al. | Selected Exercises for Microbes in Action | |
JP4510222B2 (en) | Bacteria identification method | |
CN113897411A (en) | Method for quickly, simply and conveniently evaluating microbial safety of source water and drinking water | |
CN111549093A (en) | Rapid counting method of amoeba spores in water and application thereof | |
CN111088314A (en) | Improved viable bacteria counting method | |
JPH0383598A (en) | Rapid method for inspecting microorganism |