CN102520084B - Method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water - Google Patents

Method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water Download PDF

Info

Publication number
CN102520084B
CN102520084B CN201110412710.1A CN201110412710A CN102520084B CN 102520084 B CN102520084 B CN 102520084B CN 201110412710 A CN201110412710 A CN 201110412710A CN 102520084 B CN102520084 B CN 102520084B
Authority
CN
China
Prior art keywords
water
phase extraction
solid
described step
acidifying
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.)
Active
Application number
CN201110412710.1A
Other languages
Chinese (zh)
Other versions
CN102520084A (en
Inventor
覃操
徐斌
徐倩
李冕
夏圣骥
高乃云
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.)
Tongji University
Original Assignee
Tongji 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 Tongji University filed Critical Tongji University
Priority to CN201110412710.1A priority Critical patent/CN102520084B/en
Publication of CN102520084A publication Critical patent/CN102520084A/en
Application granted granted Critical
Publication of CN102520084B publication Critical patent/CN102520084B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Other Investigation Or Analysis Of Materials By Electrical Means (AREA)
  • Sampling And Sample Adjustment (AREA)

Abstract

The invention belongs to the environmental protection and water treatment technical field, and discloses a method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water. The method comprises the following steps 1) acidifying and pretreating a sample; 2) acidifying, drying and filling a solid phase extraction material; 3) controlling a solid phase extraction process, eluting and purifying an eluate; 4) naturally volatilizing the sample and controlling with constant volume; 5) using a liquid chromatography-mass spectrometry for analyzing dimethyl nitrosamine to obtain the determination result. Compared with the current international test methods, the method of the invention has the characteristics of rapidity, simpleness, little application amount of the poisonous and harmful organic solvent, accurate analysis and the like.

Description

A kind of method of measuring trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water
Technical field
The invention belongs to environmental protection and water-treatment technology field, relate to the method for a kind of mensuration trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water (NDMA).
Background technology
N-nitrosodimethylamine (NDMA) is a kind of new Chlorination Disinfection By-products recently extensively detecting in the potable water on the ground such as America & Canada.In water, NDMA is found for 1989 in the waterworks of an employing chloramines disinfection in Ontario, Canada province Ohsweken district, then in the water factory of other several the identical sterilization process of employing, NDMA also detected.The report that at present has NDMA to detect in water factories such as the U.S., Canada, Europe.Investigation is found, adopt the water factory of combined chlorine sterilization, even adopt in the water factory of ion-exchange process and also detected this material [Choi J, Valentine R L.Formation of N-nitrosodimethylamine (NDMA) from reaction of monochloramine:a new disinfection by-product[J] .WaterRes, 2002,36 (4), 817-824.].U.S. EPA is classified as one of 200 kinds of carcinogens [USEPA.Integrated Risk Information Service[R] .USA:United States Environmental Protection Agency, Office of Research and Development, National Center for Environmental Assessment, 1991.], its carcinogenic grade is 2 grades, in exposure concentrations, be only under the condition of 0.7ng/L, theoretical carcinogenic risk coefficient can reach 10 -6.
Conventionally in potable water the concentration of NDMA all in the level of ng/L, conventional sense method is generally carried out water sample by liquid-liquid extraction or Solid-Phase Extraction and is concentrated, and then carry out separation and quantitative [Charrois J W A by chromatograph-mas spectrometer, Arend M W, Froese K L, Hrudey S E.Detecting N-nitrosamines in drinking water at nonogram per litre levels using ammonia positive chemical ionization[J] .Environ Sci Technol, 2004,38 (21): 4835-4841.].2004, EPA (USEPA) has announced the detection method of nitrosamines material in potable water [EPA/600/R-05/054, Determination of Nitrosamines in Drinking Water by Solid Phase Extraction and Capillary Column Gas Chromatographywith Large Volume Injection and Chemical Ionization Tandem Mass Spectrometry (MS/MS) [S] .] Solid-Phase Extraction/capillary gas chromatography/chemical ionization source mass spectrometry.The method adopts Lichrolut EN and Ambersorb 572 as solid phase extraction adsorbents, and NDMA-d6 is internal standard compound, and its analyzing and testing limit (DL) is 0.28ng/L, and report detectability (RDL) is 1.6ng/L.Ontario Ministry of environment (OME) has announced [OME.The Determination of N-nitrosodimethylamine (NDMA) in Water bv Gas Chromatography high Resolution Mass Spectrometry (GC-HRMS) [R] the .Canada:On-tarioMinistry of Environment of NDMA assay method in detection potable water in same year, 2004.], Solid-Phase Extraction adopts Ambersorb 572 as adsorbent, with methylene chloride, carry out elution, by gas chromatography and high resolution mass spectrometry, complete separated and quantitative, its detectability (DL) is 0.4ng/L, report detectability (RDL) is 1.0ng/L.It is reported, there is problem [the Cheng R C.AlternativeMethods for the Analysis of NDMA and Other Nitrosamines in Water and Wastewater such as the recovery is low, measuring accuracy stability is bad, sense cycle is long, operation steps is complicated in these methods, ReportWRF-01-001[R] .Long Beach, California:Water Reuse Foundation, 2006.].
Summary of the invention
The problems such as, sense cycle low for the current conventional sense method recovery is long, operation steps is complicated, the object of this invention is to provide the method for a kind of mensuration trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water (NDMA); The method is simple to operate, measuring accuracy is high, can effectively reduce sense cycle.
Technical scheme of the present invention is as follows:
The invention provides a kind of method of measuring trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water, the method comprises the following steps: 1) water sample acidifying pre-service; 2) acidifying of Solid-Phase Extraction material, dry and filling; 3) control Solid-Phase Extraction process, wash-out and purify eluent; 4) volatilization naturally of sample is controlled with constant volume; 5) application liquid chromatography mass technical Analysis N-nitrosodimethylamine, obtains measurement result.
Described water sample is selected from surface water, underground water or potable water.
Described step 1) in, water sample acidifying pre-service takes a step forward and comprises particle removal step.
In described water sample, particle removal method is: with the membrane filtration of aperture≤0.45 μ m, remove graininess impurity, material selection cellulose acetate film or the poly (ether sulfone) film of filter membrane.
Described step 1) in, acidifying preprocess method is: collect and filter rear water sample to 500mL or 1000mL, then add sulfuric acid or NaOH to regulate pH value to 6~8, then water sample be positioned in brown bottle and adopt lucifuge measure.
Described step 2), in, Solid-Phase Extraction material adopts wooden powder's activated charcoal, its average particle size≤40 μ m.
Described step 2) in, the acidifying of Solid-Phase Extraction material is to adopt the sulfuric acid water acidifying that pH is 2.3.
Described step 2) in, the dry of Solid-Phase Extraction material is by the 105 ℃ of oven dry in baking oven of Solid-Phase Extraction material after acidifying.
Described step 2) in, the packing method of Solid-Phase Extraction material is: weigh the Solid-Phase Extraction material of getting after 1g is dried in the balance, be packed in Solid-Phase Extraction (SPE) void column of the high-molecular polythene of 6mL, sieve plate adopts ultra-high molecular weight polyethylene material, fills out tight and compacting.
Described step 3) method of controlling Solid-Phase Extraction process in is: regulate the vacuum tightness of SPE device, the filtering velocity that makes water sample is 2~5mL/min, by the SPE void column filling; In water sample filter process, should avoid occurring cutout phenomenon.
Described step 3) in, the method for wash-out is: adopt 2ml acetonitrile, and twice-2ml methyl alcohol, twice-2ml acetone, twice wash-out, drains front solvent and in post, soaks 3~4min, guarantees to add the front pillar of solvent thoroughly to drain at every turn.
Described step 3) method that purifies eluent in is: under extraction pillar, add florisil post (Florey tripoli pillar), specification is 0.5g * 3mL, makes solvent when flowing through florisil post, and the impurity that may contain in solvent is removed.
Described step 4) in, the volatilization naturally of sample with constant volume control method is: adopt band scale tapered tube splendid attire eluent, and be placed in 35~40 ℃ of sand-baths, lucifuge evaporates into 1mL naturally, accurate recording final volume.
Described step 5) in, liquid chromatography mass technology adopts ESI source triple level Four bar liquid chromatography mass combined instrument, chromatographic column is C8 and C18 separating column, and mobile phase is adopted as methyl alcohol+2mmol/L ammonium acetate, and flow velocity is 150 μ L/min, sampling volume is 50 μ L, and the bulk analysis time is 10min; Mass spectrographic ion injection electric is 4500kv, and ion source temperature is 350 ℃, and the monitoring ion quantitative result of NDMA is that m/z 75-43 and qualitative results are m/z 75-58, and the monitoring ion of internal standard compound NDMA-d6 is m/z 81-46.
Described step 5) in, Instrument measuring value is for this assay method is by the concentration of N-nitrosodimethylamine in the concentrated water sample obtaining, and actual water sample N-nitrosodimethylamine concentration is that Instrument measuring value is divided by cycles of concentration.
The present invention compared with the existing technology, has the following advantages and beneficial effect:
1, by assay method of the present invention, can effectively improve the extraction efficiency of underwater trace NDMA, greatly reduce the matrix interference in liquid matter analytic process simultaneously, guarantee accuracy and the accuracy of test;
2, the inventive method is compared with existing method of testing in the world, and it is quick, easy that this method has, and poisonous and harmful organic solvent use amount seldom, is analyzed the features such as accurate.
3, the present invention has improved accuracy and analysis precision that NDMA detects greatly, and detectability can reach 2ng/L, has effectively overcome the difficult problems such as conventional sense method NDMA detects limit for height, and the liquid-liquid extraction recovery is low, and toxic solvent use amount is few simultaneously.
4, the whole mensuration process of method of the present invention easy operating, cost are lower, can be widely used in earth's surface and groundwater monitoring, large, the monitoring and the analysis that neutralize small-sized water factory.
5, detection method step of the present invention is less, simple to operate, and sense cycle is shorter; Because mobile phase adopts methyl alcohol and 2mmol/L ammonium acetate and gradient is set, N-nitrosodimethylamine is can be in LC-MS-MS detection method effectively separated and go out peak, select that to NDMA, to have compared with wooden powder's activated charcoal of high absorption capacity be solid phase extraction adsorbents simultaneously, thereby can obtain the higher NDMA recovery, measuring accuracy good stability.
Accompanying drawing explanation
Fig. 1 is the operational flowchart of the embodiment of the present invention.
Fig. 2 be in the embodiment of the present invention the different pH of water sample to measurement result figure.
Fig. 3 be in the embodiment of the present invention different types of elution to measurement result figure.
Fig. 4 applies this method to measure NDMA concentration change figure in water-purifying process in the embodiment of the present invention.
Embodiment
Below in conjunction with accompanying drawing illustrated embodiment, the present invention is further illustrated.
Embodiment 1
Water sample is Mill-Q water (ultrapure water).At 12 groups of volumes, be in 500mLMill-Q water (ultrapure water) and add NDMA standard items, making NDMA concentration is 1 μ g/L, due to this water sample no suspended substance and granule foreign, thereby without filtration.
Acidifying preprocess method: using NaOH or sulfuric acid to regulate the pH value of 12 groups of water samples to be measured water sample is 1,2,3,4,5,6,7,8,9,10,11,12, is positioned in brown bottle by water sample and adopts lucifuge measure to preserve.
The acidifying of Solid-Phase Extraction material, dry and filling; Using wooden powder's activated charcoal of using as Solid-Phase Extraction, its average particle size≤40 μ m, is used the sulfuric acid water acidifying that pH is 2.3, wooden powder's activated charcoal 105 ℃ of oven dry in baking oven after acidifying; Weigh wooden powder's activated charcoal of getting after 1g is dried in the balance and be packed in Solid-Phase Extraction (SPE) void column of the high-molecular polythene of 6mL, sieve plate adopts ultra-high molecular weight polyethylene material, fills out tight and compacting, will extract pillar access extraction equipment.
Control Solid-Phase Extraction process, wash-out and purify eluent; Adopt commercially available SPE device, regulate the vacuum tightness of SPE device, make the filtering velocity of water sample in 2mL/min, by the SPE post filling; In water sample filter process, should avoid occurring cutout phenomenon, the general no more than 24h of adsorption time.When being about to find time, takes off water sample extraction pillar.
The method that purifies eluent is: under extraction pillar, access florisil post (Florey tripoli pillar, 0.5g, 3mL specification), access washing device.Elution step is 2ml acetonitrile (twice)-2ml methyl alcohol (twice)-2ml acetone (twice) wash-out, drains front solvent and in post, soaks 4min, guarantees to add the front pillar of solvent thoroughly to drain at every turn.In elution process, solvent streams, through florisil post, is removed the impurity that may contain in solvent in florisil post.
Naturally the volatilization of sample with constant volume control method is: adopt the tapered tube splendid attire eluent with scale, and be placed in 40 ℃ of sand-baths, lucifuge evaporates into 1mL naturally, accurate recording final volume.
Application liquid chromatography mass technical Analysis NDMA, obtains measurement result; Liquid chromatography mass technology adopts ESI source triple level Four bar liquid chromatography mass combined instrument, and chromatographic column is C18 separating column, and mobile phase is adopted as methyl alcohol+2mmol/L ammonium acetate, and flow velocity is 150 μ L/min, and sampling volume is 50 μ L, and the bulk analysis time is 10min; Mass spectrographic ion injection electric is 4500kv, and ion source temperature is 350 ℃, and the monitoring ion quantitative result of NDMA is that m/z 75-43 and qualitative results are m/z 75-58, and the monitoring ion of internal standard compound NDMA-d6 is m/z 81-46.
Instrument measuring value is for this assay method is by the concentration of NDMA in the concentrated water sample obtaining, and actual water sample NDMA concentration is that Instrument measuring value is divided by cycles of concentration.By actual water sample NDMA concentration, divided by 1ug/L, as shown in Figure 2, wherein every kind of pH value is done three groups of parallel laboratory tests to obtain under different water sample pH value conditions recovery variation tendency.
Fig. 2 be in embodiment the different pH of water sample to measurement result figure.As shown in Figure 2, under condition of neutral pH, the NDMA recovery is higher, is positioned at 70%~90%, and relative standard deviation is positioned at 1.70%~2.60%, has higher stability.Under peracid and excessively alkali condition, the recovery declines to some extent, and especially pH is that 2 o'clock recovery are down to 40% left and right, and under extreme pH condition, the recovery is unstable, and relative standard deviation is up to 6.40%, and therefore, while detecting sample, the control of pH value is most important.
Embodiment 2
Water sample is Mill-Q water (ultrapure water).At 5 groups of volumes, be in 500mLMill-Q water (ultrapure water) and add NDMA standard items, making NDMA concentration is 1 μ g/L, and water sample pH value is 7, so this water sample is without filtering and regulate pH.
Acidifying preprocess method: water sampling 500mL, is positioned in brown bottle by water sample and adopts lucifuge measure to preserve.
The acidifying of Solid-Phase Extraction material, dry and filling; Using wooden powder's activated charcoal of using as Solid-Phase Extraction, its average particle size≤40 μ m, is used the sulfuric acid water acidifying that pH is 2.3, wooden powder's activated charcoal 105 ℃ of oven dry in baking oven after acidifying.Weigh wooden powder's activated charcoal of getting after 1g is dried in the balance and be packed in Solid-Phase Extraction (SPE) void column of the high-molecular polythene of 6mL, sieve plate adopts ultra-high molecular weight polyethylene material, fills out tight and compacting, will extract pillar access extraction equipment.
Control Solid-Phase Extraction process, wash-out and purify eluent; Adopt commercially available SPE device, regulate the vacuum tightness of SPE device, make the filtering velocity of water sample in 2mL/min, by the SPE post filling; In water sample filter process, should avoid occurring cutout phenomenon, the general no more than 24h of adsorption time.When being about to find time, takes off water sample extraction pillar.
The method that purifies eluent is: under extraction pillar, access florisil post (Florey tripoli pillar, 0.5g, 3mL specification), access washing device.Five groups of water samples adopt respectively five kinds of types of elution in table 1, investigate respectively eluant, eluent kind, eluting order, the impact of eluant, eluent volume on the recovery.Drain front solvent and in post, soak 4min, guarantee to add the front pillar of solvent thoroughly to drain at every turn.In elution process, solvent streams, through florisil post, is removed the impurity that may contain in solvent in florisil post.
Table 1
Naturally the volatilization of sample with constant volume control method is: adopt the tapered tube splendid attire eluent with scale, and be placed in 40 ℃ of sand-baths, lucifuge evaporates into 1mL naturally, accurate recording final volume.
Application liquid chromatography mass technical Analysis NDMA, obtains measurement result; Liquid chromatography mass technology adopts ESI source triple level Four bar liquid chromatography mass combined instrument, and chromatographic column is C8 separating column, and mobile phase is adopted as methyl alcohol+2mmol/L ammonium acetate, and flow velocity is 150 μ L/min, and sampling volume is 50 μ L, and the bulk analysis time is 10min; Mass spectrographic ion injection electric is 4500kv, and ion source temperature is 350 ℃, and the monitoring ion quantitative result of NDMA is that m/z 75-43 and qualitative results are m/z 75-58, and the monitoring ion of internal standard compound NDMA-d6 is m/z 81-46.
Instrument measuring value is for this assay method is by the concentration of NDMA in the concentrated water sample obtaining, and actual water sample NDMA concentration is that Instrument measuring value is divided by cycles of concentration.
Fig. 3 be in embodiment different types of elution to measurement result figure.As shown in Figure 3, there is no acetone in type of elution B, the recovery is minimum, so the effective wash-out NDMA of acetone.The type of elution A recovery is the highest, and therefore, when investigation other factors affects the recovery, type of elution can be defined as A, and concrete operations mode is: 2mL acetonitrile (twice)-2mL methyl alcohol (twice)-2mL acetone (twice).Before elution, 2mL solvent soaks 3-4 minute in post.Before adding 2mL solvent, should make pillar drain at every turn.
Embodiment 3
Fig. 1 is the operational flowchart of the embodiment of the present invention.Water sample is surface water.Set-up procedure before extraction: the cellulose acetate film that first each water sample of water purification process is less than or equal to 0.45 μ m by aperture filters, elimination suspension, granule foreign, each water sample of water purification process is faintly acid.Acidifying preprocess method: get and filter rear water sample 500mL, be positioned in brown bottle and adopt lucifuge measure, using NaOH to regulate the pH value of water sample to be measured is 7, and keeps in Dark Place.
The acidifying of Solid-Phase Extraction material, dry and filling; Using wooden powder's activated charcoal of using as Solid-Phase Extraction, its average particle size≤40 μ m, is used the sulfuric acid water acidifying that pH is 2.3, wooden powder's activated charcoal 105 ℃ of oven dry in baking oven after acidifying.Weigh wooden powder's activated charcoal of getting after 1g is dried in the balance and be packed in Solid-Phase Extraction (SPE) void column of the high-molecular polythene of 6mL, sieve plate adopts ultra-high molecular weight polyethylene material, fills out tight and compacting, will extract pillar access extraction equipment.
Control Solid-Phase Extraction process, wash-out and purify eluent; Adopt commercially available SPE device, regulate the vacuum tightness of SPE device, make the filtering velocity of water sample in 2mL/min, by the SPE post filling; In water sample filter process, should avoid occurring cutout phenomenon, the general no more than 24h of adsorption time.When being about to find time, takes off water sample extraction pillar.
The method that purifies eluent is: under extraction pillar, access florisil post (Florey tripoli pillar, 0.5g, 3mL specification), access washing device.Elution step is 2ml acetonitrile (twice)-2ml methyl alcohol (twice)-2ml acetone (twice) wash-out, drains front solvent and in post, soaks 3~4min, guarantees to add the front pillar of solvent thoroughly to drain at every turn.In elution process, solvent streams, through florisil post, is removed the impurity that may contain in solvent in florisil post.
Naturally the volatilization of sample with constant volume control method is: adopt the tapered tube splendid attire eluent with scale, and be placed in 40 ℃ of sand-baths, lucifuge evaporates into 1mL naturally, accurate recording final volume.
Application liquid chromatography mass technical Analysis NDMA, obtains measurement result; Liquid chromatography mass technology adopts ESI source triple level Four bar liquid chromatography mass combined instrument, and chromatographic column is C18 separating column, and mobile phase is adopted as methyl alcohol+2mmol/L ammonium acetate, and flow velocity is 150 μ L/min, and sampling volume is 50 μ L, and the bulk analysis time is 10min; Mass spectrographic ion injection electric is 4500kv, and ion source temperature is 350 ℃, and the monitoring ion quantitative result of NDMA is that m/z 75-43 and qualitative results are m/z 75-58, and the monitoring ion of internal standard compound NDMA-d6 is m/z 81-46.
Instrument measuring value is for this assay method is by the concentration of NDMA in the concentrated water sample obtaining, by the numerical value of measuring divided by cycles of concentration, thereby draw the concentration of NDMA in former water sample.
Fig. 4 applies this method to measure NDMA concentration change figure in water-purifying process in embodiment.The former water of Raw=in figure, BP=Biological Pretreatment, Sed=precipitation, Fil=filters, ozone after PO=, BAC=biological activated carbon, Fin=water outlet.
As can be seen from Figure 4, all do not detect NDMA in micro-polluted raw, in Biological Pretreatment, precipitation, filtering technique, do not generate NDMA, rear ozone treatment can directly generate finite concentration NDMA, and its concentration can reach 13.7ng/L.Follow-up BAC process has certain removal effect to NDMA, the NDMA that can adsorb and degrade in part water, and its clearance can reach 21.3%.In water outlet, NDMA concentration is 11.5ng/L.
The above-mentioned description to embodiment is can understand and apply the invention for ease of those skilled in the art.Person skilled in the art obviously can easily make various modifications to these embodiment, and General Principle described herein is applied in other embodiment and needn't passes through performing creative labour.Therefore, the invention is not restricted to the embodiment here, those skilled in the art are according to announcement of the present invention, and not departing from the improvement that category of the present invention makes and revise all should be within protection scope of the present invention.

Claims (2)

1. a method of measuring trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water, is characterized in that: the method comprises the following steps: 1) water sample acidifying pre-service; 2) acidifying of Solid-Phase Extraction material, dry and filling; 3) control Solid-Phase Extraction process, wash-out and purify eluent; 4) volatilization naturally of sample is controlled with constant volume; 5) application liquid chromatography mass technical Analysis N-nitrosodimethylamine, obtains measurement result;
Described step 1) in, water sample acidifying pre-service takes a step forward and comprises particle removal step;
In described water sample, particle removal method is: with the membrane filtration of aperture≤0.45 μ m, material selection cellulose acetate film or the poly (ether sulfone) film of filter membrane;
Described step 1) in, acidifying preprocess method is: collect and filter rear water sample to 500mL or 1000mL, then add sulfuric acid or NaOH to regulate pH value to 6~8, then water sample be positioned in brown bottle and adopt lucifuge measure;
Described step 2), in, Solid-Phase Extraction material adopts wooden powder's activated charcoal, its average particle size≤40 μ m; Described step 2) in, the acidifying of Solid-Phase Extraction material is to adopt the sulfuric acid water acidifying that pH is 2.3; Described step 2) in, the dry of Solid-Phase Extraction material is by the 105 ℃ of oven dry in baking oven of Solid-Phase Extraction material after acidifying; Described step 2) in, the packing method of Solid-Phase Extraction material is: weigh the Solid-Phase Extraction material of getting after 1g is dried in the balance, be packed in the Solid-Phase Extraction SPE void column of high-molecular polythene of 6mL, sieve plate adopts ultra-high molecular weight polyethylene material, fills out tight and compacting;
Described step 3) method of controlling Solid-Phase Extraction process in is: regulate the vacuum tightness of SPE device, the filtering velocity that makes water sample is 2~5mL/min, by the SPE void column filling; Described step 3) in, the method for wash-out is: adopt 2ml acetonitrile-twice, and 2ml methyl alcohol-twice, 2ml acetone-twice, wash-out, drains front solvent and in post, soaks 3~4min;
Described step 3) method that purifies eluent in is: under extraction pillar, add florisil post, specification is 0.5g * 3mL;
Described step 4) in, the volatilization naturally of sample with constant volume control method is: adopt band scale tapered tube splendid attire eluent, and be placed in 35~40 ℃ of sand-baths, lucifuge evaporates into 1mL naturally, accurate recording final volume;
Described step 5) in, liquid chromatography mass technology adopts ESI source triple level Four bar liquid chromatography mass combined instrument, chromatographic column is C8 or C18 separating column, and mobile phase is adopted as methyl alcohol+2mmol/L ammonium acetate, and flow velocity is 150 μ L/min, sampling volume is 50 μ L, and the bulk analysis time is 10min; Mass spectrographic ion injection electric is 4500kv, and ion source temperature is 350 ℃, and the monitoring ion quantitative result of N-nitrosodimethylamine is that m/z75-43 and qualitative results are m/z75-58, and the monitoring ion of internal standard compound N-nitrosodimethylamine-d6 is m/z81 – 46; Described step 5) in, Instrument measuring value is for this assay method is by the concentration of N-nitrosodimethylamine in the concentrated water sample obtaining, and actual water sample N-nitrosodimethylamine concentration is that Instrument measuring value is divided by cycles of concentration.
2. the method for mensuration trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water according to claim 1, is characterized in that: described water sample is selected from surface water, underground water or potable water.
CN201110412710.1A 2011-12-12 2011-12-12 Method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water Active CN102520084B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201110412710.1A CN102520084B (en) 2011-12-12 2011-12-12 Method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201110412710.1A CN102520084B (en) 2011-12-12 2011-12-12 Method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water

Publications (2)

Publication Number Publication Date
CN102520084A CN102520084A (en) 2012-06-27
CN102520084B true CN102520084B (en) 2014-12-10

Family

ID=46291072

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201110412710.1A Active CN102520084B (en) 2011-12-12 2011-12-12 Method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water

Country Status (1)

Country Link
CN (1) CN102520084B (en)

Families Citing this family (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104163526B (en) * 2014-08-28 2016-07-06 清华大学 A kind of pH that regulates strengthens the method for nitrosamine precursor in ion exchange removal water
CN104568562B (en) * 2014-12-31 2017-12-29 中国地质大学(武汉) The preprocess method of nitrosamine compound in a kind of water sample and its suspension
CN106018632B (en) * 2016-05-11 2018-04-10 清华大学 A kind of method of nitrosamine precursor in enriching and purifying water based on ion exchange technique
CN105842329A (en) * 2016-05-25 2016-08-10 中国环境科学研究院 Device and method for representing organic nitrogen in deposit on basis of high resolution mass spectrum
CN105948215A (en) * 2016-06-29 2016-09-21 同济大学 Water sample preservation method of iodo nitrogen-containing disinfection by-product
CN106950297B (en) * 2017-03-07 2019-05-28 大连理工大学 A method of it is analyzed and identified for nicotine disinfection by-products
CN108508111A (en) * 2018-04-08 2018-09-07 哈尔滨工业大学 Analysis method that is a kind of while detecting 9 kinds of trace nitrosamines disinfection by-products in water
CN109613155A (en) * 2018-11-29 2019-04-12 同济大学 A kind of detection method of armaticity nitrogenous disinfection byproducts
CN109856260B (en) * 2018-12-29 2021-12-03 广电计量检测(南宁)有限公司 Method for detecting N-dimethyl nitrosamine in meat products
CN111122739A (en) * 2019-12-31 2020-05-08 苏州弘森药业股份有限公司 Method for detecting N-dimethyl nitrosamine in ranitidine
CN112129853A (en) * 2020-09-07 2020-12-25 天地恒一制药股份有限公司 Method for detecting nitrosamine impurities in candesartan cilexetil
CN112710763B (en) * 2021-01-06 2023-07-28 湖南威特制药股份有限公司 Method for detecting N-nitrosodimethylamine in nizatidine by HPLC method
CN113390998A (en) * 2021-06-23 2021-09-14 福州水质监测有限公司 Method for detecting N-nitrosodimethylamine in drinking water

Non-Patent Citations (8)

* Cited by examiner, † Cited by third party
Title
Megan H. Plumlee et al..N-nitrosodimethylamine (NDMA) removal by reverse osmosis and UV treatment and analysis via LC-MS/MS.《WATER RESEARCH》.2007,第42卷347-355. *
MODIFICATION OF THE SURFACES OF A GAS-ACTIVATED CARBON AND A CHEMICALLY ACTIVATED CARBON WITH NITRIC ACID, HYPOCHLORITE,AND AMMONIA;P.VINKE et al.;《Carbon》;19941231;第32卷(第4期);675-686 *
N-nitrosodimethylamine (NDMA) removal by reverse osmosis and UV treatment and analysis via LC-MS/MS;Megan H. Plumlee et al.;《WATER RESEARCH》;20070726;第42卷;347-355 *
P.VINKE et al..MODIFICATION OF THE SURFACES OF A GAS-ACTIVATED CARBON AND A CHEMICALLY ACTIVATED CARBON WITH NITRIC ACID, HYPOCHLORITE,AND AMMONIA.《Carbon》.1994,第32卷(第4期),675-686. *
SPE/LC/MS/MS检测水中痕量二甲基亚硝胺;梁闯等;《中国给水排水》;20090731;第25卷(第14期);82-85,92 *
梁闯等.SPE/LC/MS/MS检测水中痕量二甲基亚硝胺.《中国给水排水》.2009,第25卷(第14期),82-85,92. *
活性炭吸附水中新型含氮消毒副产物二甲基亚硝胺;田康宁等;《净水技术》;20111025;第30卷(第5期);34-39 *
田康宁等.活性炭吸附水中新型含氮消毒副产物二甲基亚硝胺.《净水技术》.2011,第30卷(第5期),34-39. *

Also Published As

Publication number Publication date
CN102520084A (en) 2012-06-27

Similar Documents

Publication Publication Date Title
CN102520084B (en) Method for determining trace nitrogen-containing disinfection by-product dimethyl nitrosamine in water
Pavón et al. Determination of trihalomethanes in water samples: a review
Ngongang et al. Analysis of nine N-nitrosamines using liquid chromatography-accurate mass high resolution-mass spectrometry on a Q-Exactive instrument
Fang et al. N-Methylimidazolium ionic liquid-functionalized silica as a sorbent for selective solid-phase extraction of 12 sulfonylurea herbicides in environmental water and soil samples
Zhou et al. Optimization of antibiotic analysis in water by solid-phase extraction and high performance liquid chromatography–mass spectrometry/mass spectrometry
Oliferova et al. On-line solid-phase extraction and HPLC determination of polycyclic aromatic hydrocarbons in water using fluorocarbon polymer sorbents
Barco-Bonilla et al. Comprehensive analysis of polycyclic aromatic hydrocarbons in wastewater using stir bar sorptive extraction and gas chromatography coupled to tandem mass spectrometry
Araújo et al. Development of a flow system for the determination of low concentrations of silver using Moringa oleifera seeds as biosorbent and flame atomic absorption spectrometry
Chen et al. Simultaneous determination of ten taste and odor compounds in drinking water by solid-phase microextraction combined with gas chromatography-mass spectrometry
CN105651922B (en) Method for determining PPCPs in environmental water sample
Chen et al. Comparison of gas chromatography-mass spectrometry and gas chromatography-tandem mass spectrometry with electron ionization for determination of N-nitrosamines in environmental water
Lu et al. Molecularly imprinted polymers for dispersive solid‐phase extraction of phenolic compounds in aqueous samples coupled with capillary electrophoresis
Calisto et al. Adsorption of the antiepileptic carbamazepine onto agricultural soils
Teo et al. Simple and accurate measurement of carbamazepine in surface water by use of porous membrane-protected micro-solid-phase extraction coupled with isotope dilution mass spectrometry
Zhu et al. Interaction of bisphenol A with dissolved organic matter in extractive and adsorptive removal processes
CN105784858B (en) Method for measuring PPCPs in environmental soil
Zhang et al. Simultaneous determination of phenol and p-nitrophenol in wastewater using near-infrared diffuse reflectance spectroscopy with adsorption preconcentration
Wu et al. Determination of secondary and tertiary amines as N-nitrosamine precursors in drinking water system using ultra-fast liquid chromatography–tandem mass spectrometry
CN105784881A (en) Determination method of perfluorinated compound isomer in soil and/or plants
Sibiya et al. Development and application of solid phase extraction method for polycyclic aromatic hydrocarbons in water samples in Johannesburg area, South Africa
Kinani et al. Formation and determination of organohalogen by-products in water–Part II. Sample preparation techniques for analytical approaches
JP2008224461A (en) Chemical sensor material
Zhao et al. LC-QTOF-MS method for the analysis of residual pharmaceuticals in wastewater: application to a comparative multiresidue trace analysis between spring and winter water
HUANG et al. Supported ionic liquids solid-phase extraction coupled to electrochemical detection for determination of trace bisphenol A
Zhu et al. Preparation of a mixed-mode silica-based sorbent by click reaction and its application in the determination of primary aromatic amines in environmental water samples

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