N-Nitrosodimethylamine, C2H6N2O, is a semi-volatile organic chemical of the nitrosamine group that is extremely toxic and is a suspected human carcinogen. It may show in a assortment of nutrients, drinkable H2O and effluent ( Woosuk Cha 2006 ) . NDMA is one of the emerging chemicals in treated sewerage that is highly soluble in H2O and is an industrial byproduct that may happen during chlorination and chloramination. Wastewater that contains organic N is able to excite the byproduct formation procedure. NDMA can besides organize or be leached during intervention of H2O by ion exchange rosins ( ALS ) . The unit hazard is the quantitative estimation in footings of either hazard per ug/L imbibing H2O or hazard per ug/cu.m air breathed ( hypertext transfer protocol: //www.epa.gov/ncea/iris/subst/0045.htm )

1.2 Concentrations of concern in imbibing H2O and effluent

The concentration of NDMA occurs in imbibing H2O is of great concern as its carcinogenic belongings is highly related to human wellness, an acceptable concentration of 9ng/L is issued in 2003 by Ontario in imbibing H2O quality ( www.ene.gov.on.ca/envision/gp/4449e.pdf ) . However, current techniques are of great trouble in observing the chemical in such a low concentration, therefore do it much more hard to acquire removed from imbibing H2O. In add-on, although there is small information sing the potency for biological remotion of NDMA, NDMA is slightly immune to biodegradation and is hard to take by air depriving and ozonation ( J. Chung et Al. 2009 ) .

As it is for effluent, recycled H2O that is for irrigation usage or other recreative H2O usage should besides be taken into history when making effluent quality rating. Peoples may consume a little sum of H2O straight or indirectly when they are utilizing diversion activities, such as unwritten exposure or inspiration exposure. Thus it is besides needed to take NDMA analysis is wastewater. NDMA concentration in secondary effluent wastewaters is typically exceed 100ng/L ( W.A. Mitch et Al. 2003 ) . In 1994, a regulative degree of 200ng/L in wastewaters was established for NDMA by the Ministry of Environment and Energy ( V.Y. Taguchi et Al. 1994 ) .

1.3 Toxic belongings sing to NDMA

The toxic effects on worlds is still non clear yet as experiments merely taken on animate beings and the results are remain unpublished. Symptoms related to NDMA toxic include concern, febrility, purging, abdominal hurting, scattered intradermic bleeding, lassitude, sickness, and diarrhoea ( http: //en.wikipedia.org/wiki/N-Nitrosodimethylamine ) . Toxicity and carcinogenicity associated with NDMA has been taken experiments on rats, and that can do unrecorded tumors at a comparatively low doses ( ALS ) .

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Monitoring plan lineation

In this paper, we are traveling to take out a monitoring plan at the Hydrophobia Water Quality Laboratory in Western Sydney. The chemical we focus on is NDMA, which is detected as a chlorination byproduct in H2O and effluent intervention processes.

To analysis the chemical in H2O and effluent, sample aggregation including trying frequence, trying location is described in the first portion, following sample extraction methods and associated techniques. Advantages and disadvantages of each technique are besides described in the undermentioned portion.

Instrumentality for sample analysis including HLPC, GC, GC-MS/MS and LC-MS/MS are introduced briefly every bit good as pros and cons of each. A suited attack is to be taken for accurate quantitation of the analyte. Quality control processs such as analytical spaces is to be analyzed in inside informations. As for the concluding portion, typical analytical sensing bounds including LODs and LOQs that can be achieved will be briefly discussed.

Water and effluent sample aggregation

2.1 Water sample aggregation location and frequence

Chart 2.1 Process schematic in Drinking Water Treatment Plant



Sand filtration

Dilution with groundwater


GAC filtration

Concluding postchlorination


– Sampling points

Harmonizing to the DWTP procedure flow chart, 8 sampling points are indicated, therefore samples should be collected pre-chlorination, pre-flocculation, pre-sane filtration, pre-dilution, pre-ozonation, pre-GAC filtration, post-GAC filtration and post-final chlorination, severally. Due to the high relationship between NDMA concentration and human wellness, trying anterior to and after each procedure is required for NDMA concentration analysis, and for farther remotion analysis.

Besides, the aggregation comes up one time per month and 2 samples of each point are required when analysing.

n = 8*2 = 16 samples/month ( C. Planas et Al. 2008 )

2.2 Wastewater sample aggregation location and frequence

Chart 2.2 Process conventional in Wastewater Treatment Plant ( Megan H. Plumlee et Al. )


Rearward Osmisis

UV intervention

Blending reservoir

Injection Wellss



Secondary wastewater



Drinkable H2O

– Sampling points

The chart above is the procedure flow chart of the Interim Water Purification Facility ( IWPF ) , a now-decommissioned advanced effluent intervention works operated by the OGWD in Southern California. This system comprises dosage of Na hypochlorite prior to micro filtration, therefore chloramines were formed due to the high ammonium hydroxide concentration. NDMA is likely to organize during disinfection procedure and do this illustration typical for analysis.

6 point samples are to be collected one time per month, and the points are outflowing, chloraminated wastewater, pre-RO, pre-UV, post-UV and post-blending, severally. Natural H2O and treated H2O require NDMA trying as they are of import informations for intervention procedure and human wellness. Sampling after Na hypochlorite dosage is to analysis the influence of hypochlorite dosage to NDMA formation. Post-microfiltration sampling is required to analysis MF to NDMA remotion. As for UV procedure, it is highly important for NDMA remotion, therefore trying anterior to and after UV procedure are indispensable.

2 samples of each point each clip are required when taking samples.

n = 6*2 = 12 samples/month

2.3 Sample transit

Samples collected at both workss are to be transported to research labs to make farther analysis therefore should be good kept after trying. Collection of all samples are utilizing 1L brownish-yellow glass bottles as the organic compounds are sensitive to light, a extinction agent – 100 milligram of Na thiosulfate is added into bottles every bit shortly as trying to slake Cl.

Samples should be kept in cool and dark status and transported to laboratory instantly after aggregation. All the samples will be stored at 4A°C anterior to analysis. Following measure of extraction should be taken within 7 yearss ( Megan H. Plumlee et Al. 2008 ) .

Available techniques for sample extraction

Extraction of NDMA from aqueous samples is necessary for sensitive sensing and is known to be hard because of the hydrophilic and non-adsorptive features of NDMA ( Woosuk Cha 2006 ) . Methods associated with NDMA extraction include liquid-liquid extraction ( LLE ) , solid-phase extraction ( SPE ) and solid-phase microextraction ( SPME ) .

3.1 Liquid-liquid extraction ( LLE )

Liquid-liquid extraction, besides known as solvent extraction and breakdown, is a method to divide compounds based on their comparative solubilities in two different non-miscible liquids, normally H2O and an organic dissolver. It is an extraction of a substance from one liquid stage into another liquid stage ( Wikipedia ) .

To get by with LLE, a separatory funnel is used on a little graduated table in research lab analysis. , it is usually done on the industrial graduated table utilizing machines that bring the two liquid stages into contact with each other. Such machines include centrifugal contactors, thin bed extractors, spray columns, pulsed columns, and mixer-settlers ( Wikipedia ) .

Dichloromethane is used to better extraction efficiency in LLE, bookmans adopted 100 to 300mL of methylene chloride to LLE with a extraction clip of 6 to 18 hours, and so utilize rotary evaporator or N denudation, methylene chloride infusions to 1mL or less. Though it has improved extraction efficiency, it still can non make the ng/L degree in imbibing H2O ( Raksit A. & A ; Johri S. 2001 ) . LLE is typically coupled with GC for NDMA analysis.

3.2 Solid-phase extraction ( SPE )

In late old ages, SPE has been developed quickly due to its evident advantages. Thus has been adopted as the chief technique for extraction. Solid-phase extraction is a separation procedure by which compounds that are dissolved or suspended in a liquid mixture are separated from other compounds in the mixture harmonizing to their physical and chemical belongingss. Analytic research labs use solid stage extraction to concentrate and sublimate samples for analysis ( Wikipedia ) .

SPE can be conducted in either batch or continues manners ( CSPE ) . In batch SPE, suspended extraction medium in sample solution is required for a specified clip to reach with NDMA. In continues SPE ( CSPE ) , H2O samples flow through a fixed medium at a comparatively low rate. Hydrophilic stuff such as ambersorb 572 is used to pull out NDMA selectively from aqueous solution. Normally, ambersorb 572 and CSPE are combined to better recovery efficiency of NDMA from H2O samples ( Woosuk Cha et Al. 2006 ) .

Two methods based on SPE techniques can be used for extaction: manual SPE and automated SPE ( C. Planas et Al. 2008 ) .

3.2.1 Sorbent Ambersorb 572

This method is based on manual SPE with a hydrophilic stuff sorbent ambersorb 572. Add 2mL of methyl alcohol into 50I?L of the internal criterion solution, add 300mg of Ambersorb 572 into 1L of sample that is contained in an brownish-yellow glass bottle. After stirred with a magnet at 50rpm for 1 hr and filtered through a filter paper, Ambersorb 572 is collected through this manner. The bottle will be rinsed with high-purity H2O and the suspension will be filtered to guarantee a complete transportation of the Ambersorb 572 to the filter. Following, air dry the filter paper with Ambersorb 572 for 60 proceedingss and the dried Ambersorb 572 will be transferred to an brownish-yellow phial, and 950I?L of methylene chloride along with 50I?L of the recovery standard solution ( toluene-d8 at 1 ng/I?L ) will be added ( C. Planas et Al. 2008 ) .

3.2.2 Coconut wood coal EPA 521 cartridges

25I?L of internal standard solution and 2mL of methyl alcohol spiked is added into 500mL of sample. Then the sample will be homogenised by sonication and extracted utilizing the automated SPE system Power-Prep/SPE. 20mL of methylene chloride, methyl alcohol and Milli-Qwaterwere will go through through an SPE coconut wood coal EPA521 cartridge at a flow rate of 10 mL/min. Then the sample base on balls through the cartridge at a flow rate of 10mL/min, and the sorbent will be dried under vacuity for 10 min. Elution was performed with 2A- 6mL of methylene chloride and the eluate was passed through an SPE cartridge Isolute Na2SO4. The infusion was concentrated to a volume of 500I?L on a Turbo Vap II evaporator ( Zymark, Hopkinton, MA, USA ) , utilizing a H2O bath near room temperature ( 20-25 a-¦C ) and a soft watercourse of N, and transferred to an brownish-yellow glass phial. Finally, 25I?L of the recovery standard solution were added ( C. Planas et Al. 2008 ) .

3.2.3 Comparison between two methods

Harmonizing to Planas C.2008, NDMA extraction utilizing Coconut wood coal EPA 521 cartridges are likely to acquire a better recovery than the other method. Eight analysed nitrosamines out of nine shows that above 70 % recovery can be achieved by Coconut wood coal EPA 521 cartridges method, and seven of them exceed a recovery rate of 80 % . Compared with Sorbent Ambersorb 572, this method is much more likely to accomplish a better recovery efficiency. It is besides automatic plenty to cut down the operation cost, particularly labour cost ( C. Planas et Al. 2008 ) .

3.3 Solid-phase microextraction ( SPME )

A solid-phase microextraction method has been developed late by Grebel et Al. for NDMA and other nitrosamines. The advantage for this method include a short analysis clip require. However, utilizing this method can non accomplish sensing bounds in the 1-10 ng/l scope required for imbibing H2O ( Grebel et al. 2006 ) .

Solid-phase microextraction ( SPME ) , is a sample readying technique used both in the research lab and on-site. it is a simple and cheap technique where the usage of dissolvers is non necessary. Solid-phase microextraction involves the usage of a fiber coated with an pull outing liquid stage when making NDMA analysis ( Wikipedia ) .

SPME fibres were foremost conditioned to take any contaminations. Each fibre was conditioned prior to utilize in a GC split-splitless recess, at the temperature and length of clip recommended by the maker for each fibre type. 15mL brownish-yellow unfastened top phials with septa were used for extraction. Sodium chloride and a magnetic splash saloon were added to the sample phial, followed by the aqueous sample. The sample was placed on a heater/magnetic scaremonger and the septa pierced by the SPME holder. The SPME fibre was instantly exposed to the sample headspace. During extraction merely a little fraction of analyte mass is sorbed into the fiber stage. After a set extraction clip, the fibre was retracted and removed ( Janel E. Grebel et Al. 2006 ) .

3.4 Advantages and disadvantages of each extraction method

Table 3.1 Advantages and disadvantages of each extraction method







SPE uses a little sum of dissolver for NDMA extraction, which can cut down the sum of clip for concentration while treating large-volumes of samples simultaneously.This methold is able to treating big sum of H2O samples.

The attractive force of SPME is that the extraction is fast and simple and can be done without dissolvers, therefore cut downing costs and bring forthing less waste. Detection bounds can make parts per trillion ( ppt ) degrees for certain compounds. SPME besides has great possible for field applications ; on-site sampling can be done even by nonscientists without the demand to hold gas chromatography-mass spectrometry equipment at each location. When decently stored, samples can be analyzed yearss later in the research lab without important loss of volatiles.

Dis- advantages

LLE consumes comparatively big sum of dissolver and is arduous for large-volume samples. It is besides labour intensive and achieve low recoveries ( Megan H. Plumlee et Al. 2008 ) .

The procedure is complex, the present technique necessitate a long clip for extraction. Low recovery rate utilizing Ambersorb 572 as carbonous adsorbents ( C. Planas et Al. 2008 ) .

Samples should be analyzed every bit shortly as possible following extraction.aˆˆIt has greater standard divergence for replicate analyses ( Janel E. Grebel et Al. 2006 ) .

Current techniques for sample analysis

Further analysis on NDMA can be carried out utilizing HLPC, GC, GC-MS/MS and LC-MS/MS, GC/NPD.

Harmonizing from a fact sheet of United States,

For imbibing H2O, EPA Method 521 utilizations solid stage extraction ( SPE ) and capillary column gas chromatography ( GC ) with large-volume injection and chemical ionisation tandem mass spectrometry ( MS ) ( Munch and Bassett 2004 ) .

For effluent, EPA Method 607 utilizations methylene chloride extraction, GC, and a nitrogen-phosphorus sensor ( EPA 2002 ) .

For effluent, EPA Method 1625 uses isotope dilution, GC and mass spectroscopy ( MS ) ( EPA 2002 ) .

An analytical method has besides been developed specifically for NDMA precursors such as alkylamines in waste or effluent ( Mitch, Gerecke, and Sedlak 2003 ) .

A late developed method utilizing liquid chromatography tandem MS ( LC/MS/MS ) detects both thermally stable and unstable nitrosamines ( Zhao et al. 2006 ) .

4.1 High public presentation liquid chromatography ( HPLC )

High public presentation liquid chromatography is a signifier of column chromatography used often in biochemistry and analytical chemical science to divide, place, and quantify compounds based on their idiosyncratic mutual oppositions and interactions with the column ‘s stationary stage ( Wikipedia ) .

4.1.1 Reagent dosage

For the intent of better the selectivity and sensitiveness of HPLC analytical methods, fluorescence derivatization has been used for NDMA sensing. Dansyl chloride is by and large used as derivatizing reagent to respond with aminic acid and peptides to organize a extremely fluorescent derived function ( Lawrence J. & A ; Frei R. 1976 ) . NDMA must be denitrosated to bring forth dimethylamine ( DMA ) -a secondary aminoalkane to respond with dansyl chloride to organize a fluorescent dansyl aminoalkane ( R. Frei & A ; J. Lawrence 1982 ) .

4.1.2 Instrumental setup

Derivatized samples were measured with a Waters ( Milford, MA, USA ) high-performance liquid chromatography ( HPLC ) unit, which consisted of a Waters 600 Multisolvent bringing system, Waters 600E system accountant, Waters 2475 Multi I» Fluorescence Detector, and Waters 717Plus Autosampler. A NovaPakA® C18 column ( 3.9mmA-150 millimeter, atom size of 4I?m ) was supplied by Waters and used as an analytical column. A lookout guard column ( Waters ) was used in concurrence with the analytical column. Data acquisition and processing was done with Millenium32 ( Waters ) package. An acetonitrile-water mixture ( 2:1, in volume ) was used as a nomadic stage ( eluent ) after degassing for at least 20 min with an ultrahigh-pure class He gas. Degassing was continued during analysis at a gas flow rate of 20 milliliter mina?’1. The flow rate of the eluent was 1 milliliter mina?’1 ( isocratic manner ) . The optimal excitement and emanation wave lengths for fluorescence sensing were determined utilizing standard solutions and changing the wavelengths. The injection volume to the HPLC was 10-20 I?l ( Woosuk Cha et Al. 2006 ) .

Figure 4.2 HPLC setup ( hypertext transfer protocol: //en.wikipedia.org/wiki/File: HPLC_apparatus.svg )

( 1 ) Solvent reservoirs, ( 2 ) Solvent degasser, ( 3 ) Gradient valve, ( 4 ) Mixing vas for bringing of the nomadic stage, ( 5 ) High-pressure pump, ( 6 ) Switch overing valve in “ inject place ” , ( 6 ‘ ) Switch overing valve in “ load place ” , ( 7 ) Sample injection cringle, ( 8 ) Pre-column ( guard column ) , ( 9 ) Analytical column, ( 10 ) Detector ( i.e. IR, UV ) , ( 11 ) Data acquisition, ( 12 ) Waste or fraction aggregator ( hypertext transfer protocol: //en.wikipedia.org/wiki/File: HPLC_apparatus.svg ) .

4.2 LC-MS/MS

As LC demand a dry nomadic stage added to the complexness and disbursal of the chromatographic technique, LC is typically coupled with MS for aquatic sample analysis ( Water and effluent analysis and quality demands )

A liquid chromatograph from Shimadzu ( LC-10AD VP ) with a Shimadzu SIL-10AD VP autosampler ( Columbia, MD, USA ) connected to a ternary quadrupole mass spectrometer ( API3000 ) from Applied Biosystems ( Foster City, CA, USA ) was used for analysis of the nitrosamines. A volume of 50 milliliter of sample was injected at a flow rate of 0.15 ml/min onto a 50mm*2.1mm Targa Sprite C18 column ( 5 millimeter pore size, Higgins Analytical, Mountain View, CA, USA ) equipped with a C18 Guard Column ( Higgins Analytical ) . The mass spectrometer was operated in multiple reaction-monitoring passage manner at an optimized electromotive force for each passage in positive-ion manner. NDMA-d6 at a concentration of 110mg/L is added as an internal criterion to try infusions and nitrosamine criterions at a ratio of 0.3 internal criterion volume ( Megan H. Plumlee et Al. 2008 ) .

4.3 GC/MS

In gas chromatography, the injected sample is volatilized in the injection port after which the gaseous nomadic stage introduces the analyte species to the stationary stage. In aquatic H2O analysis, GC is typically coupled to MS to better analysis efficiency. Gas chromatography coupled with mass spectroscopy sensing is a really powerful technique for both qualitative and quantitative analysis of many categories of organic compounds

4.4 Comparison among different sensing techniques

Table 4.1 Comparison among different sensing techniques





Low-cost and simple to run, generates a distinguishable extremum for NDMA without intervention even in the complex matrix of effluent wastewaters. The HPLC with fluorescence derivatization method may be applicable for finding NDMA in H2O and effluent samples for assorted research intents and for testing environmental samples.

Necessitate the add-on of volatile acids/bases or ion-pairing reagents.


High sensitiveness to observe NDMA concentration every bit low as 1 ng/L. Useful when merchandise analysis is required.

GC/MS/MS is non able to make research on unstable nitrosamines under thermic status.


Used in analysis of a big figure of polar contamintants in H2O samples, it is a highly utile quantitative tool.

Requires a high-cost instrument and comparatively high operational accomplishment. Insufficient sensitiveness, selectivity, can non observe ng/L degree of NDMA in aquatic samples.


Able to make research on thermic instability nitrosamines.

The cost related to the method is comparatively high on aquatic NDMA analysis ( CHU Wenhai et Al. 2008 ) .

Quantitation of the analyte

5.1 Quantitation methods

In sample readying procedure, it is impossible to avoid analyte losingss utilizing readying techniques such as SPE and SPME as mentioned in Part 3. Therefore, quantitation of the mark analyte is required. Typical quantitation methods include internal criterion, external criterion, standard add-on and standardization.

Merely two quantitation processs provide a compensation to aim compounds: Internal criterion and standard add-on. Standard compounds are frequently added to samples prior to analysis to either compare comparative keeping times or to counterbalance for analytical fluctuations in sample dilution, sample bringing and sample sensing ( Lecture Notes 2010, Stuart Khan ) . In this paper, a traditional individual internal criterion process is introduced for NDMA quantitation.

5.2 Internal criterion debut

An internal criterion in analytical chemical science is a chemical substance that is added in a changeless sum to samples, the space and standardization criterions in a chemical analysis. This substance can so be used for standardization by plotting the ratio of the analyte signal to the internal standard signal as a map of the analyte concentration of the criterions. This is done to rectify for the loss of analyte during sample readying or sample recess ( Wikipedia ) .

5.3 Internal criterion quantitation

Take GC-MS technique for case, isotope dilution is used with this instrumentality, NDMA-6 is used as quantitation criterion. Their ratios in prepared investigations straight correspond to their ratios in initial samples ; there is no dependance on compound losingss during sample readying. Concentration ratios can be measured in individual ion monitoring ( SIM ) manner with MS sensing. Depending on the chemical beginning of analytes this method provides the comparative criterion divergence ( RSD ) of consequences in the scope 0.5-20 % ( 5-15 % in most practical instances ) which is considered as appropriate mistake at low contents of analytes ( Igor G. Zenkevich & A ; Evgeny D. Makarov 2007 ) .

Equation associated with the method is outlined as below ( Igor G. Zenkevich & A ; Evgeny D. Makarov 2007 ) :

qx = fx, stand Px qstand/Pstand

qx – concentrations of NDMA in initial sample

qstand – concentrations of NDMA-6 in initial sample

Px – parametric quantities of chromatographic extremums i??areai?‰of NDMA

Pstand – parametric quantities of chromatographic extremums i??areai?‰of NDMA-6

fx, stand- standardization coefficient

Early methods used to quantify country include secret plan on graph paper and count squares, cut out and weigh. Now we use computing machines to incorporate extremum, Through comparison terra incognitas to standard standardization curve, we are able to cipher comparative response of sample and internal criterion ( Lecture Notes 2010, Stuart Khan ) .

Quality control processs


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