This document defines an absolute isotopic scale for deuterium analysis of natural waters based on measurements of two reference standards - Standard Mean Ocean Water (SMOW) and Standard Light Antarctic Precipitation (SLAP). The absolute D/H ratios were measured through mass spectrometric comparison with calibration mixtures prepared in the laboratory. The results obtained are:
1) The absolute D/H ratio of SMOW is 155.76 ± 0.05 x 10-6.
2) The absolute D/H ratio of SLAP is 89.02 ± 0.05 x 10-6.
3) The δD value of SLAP relative to SMOW is -428.50 ±
A STUDY ON OCEAN ACIDIFICATION DUE TO CARBON DIOXIDE ALONG THE COAST OF VISAK...Soma Sekhar Sriadibhatla
Extensive Data Analytics on samples to understand Ocean Acidification process, a serious damage to ecosystem, increase in production of Carbon dioxide.
A STUDY ON OCEAN ACIDIFICATION DUE TO CARBON DIOXIDE ALONG THE COAST OF VISAK...Soma Sekhar Sriadibhatla
Extensive Data Analytics on samples to understand Ocean Acidification process, a serious damage to ecosystem, increase in production of Carbon dioxide.
The objective is to analyze and propose a methodology to manage with the attenuating effect promoted by carbon dioxide - CO2 on the performance of ultrasonic flow meter in gas flaring applications. Such methodology is based on experiments performed in a wind tunnel with a Reynolds number about 10^4 and concentration of CO2 above 60%. The results indicate that the ultrasonic meter exhibited measurement readings failures, especially in stages of abrupt changes in gas concentration, whose contents were above 5%. It is verified, as well, that the approximation of ultrasonic transducers tends to reduce such measurement failures.
1Department of Biotechnology, Techno India University, Salt Lake Campus Kolkata, India
2Department of Microbiology, Techno India University, Salt Lake Campus, Kolkata, India
3Department of Marine Science, University of Calcutta, 35 B.C. Road, Kolkata, India
*Address for Correspondence: Atanu Roy, Research Scholar, Department of Biotechnology, Techno India University,
Salt lake Campus, Kolkata, India
ABSTRACT- Three decades data (1984 – 2015) was used to study the effect of surface water temperature, pH, dissolved
oxygen, nitrate, phosphate and silicate on chlorophyll a concentration in three water bodies meant for fish culture (locally
known as Bheries) in East Kolkata Wetlands. The data revealed significant spatio-temporal variations (p < 0.01). The
increasing trend of temperature, nitrate and phosphate reflects the effect of intense urbanization at local level. The
pronounced variation of dissolved oxygen and chlorophyll a (decreasing trend) may be attributed to increased load of
sewage in the selected water bodies, which has posed an adverse impact on the phytoplankton standing stock as revealed
through decreasing chlorophyll a trend.
Key-words- East Kolkata Wetlands (EKW), Phytoplankton, Chlorophyll a, Nutrients, ANOVA
Espectroscopia de Emissão óptica com plasma induzido por laser: Um novo e ver...NetNexusBrasil
Espectroscopia de Emissão óptica com plasma induzido por laser: Um novo e versátil caminho para análise e monitoramento de solos, plantas e adubos_Giorgio Senesi_Siagro2014_Embrapa Instrumentação
Presentation given by George Romanos of the National Center for Scientific Research “Demokritos” (NCSRD), Greece, on "CO2QUEST - Fluid Properties and phase behaviour of CO2 with impurities" at the EC FP7 Projects: Leading the way in CCS implementation event, London, 14-15 April 2014
Renseanlæg
Hvordan opfører efterklaringstankene under øgede hydraulisk belastning og udvikling af simple modeller som kan anvendes til styring af efterklaringstankene under regn.
Hvilke metoder findes der for at forøge den hydrauliske kapacitet af renseanlæg under regn og praktiske erfaringer fra Spildevandscenter Avedøre ræsentation af det ambitiøse forskningsprojekt Storm- and Waste water Informatics SWI.
Project Streams?
Researchers collected samples of water from 163 streams in the Adirondack Mountains to investigate effects of acidic rain. They recorded a number of biological, chemical, and physical variables, including the stream name, the substrate of the stream (the composition of soil and rock over which they flow – limestone, shale, or mixed, the pH (acidity) of the water, the temperature (° C) of the water, the BCI ( a measure of biological diversity), and hardness of the water.
1. What does a scatterplot show about relationship between the water’s pH and its hardness?
2.
2. Is it appropriate to summarize the strength of association with a correlation? Explain.
3. Make a side by side boxplot of the pH of the streams by substrate(limestone, mixed, or shale)
4. Describe what you see in the comparative boxplots. A lower pH means the water is more acidic.
5. In this question you will compare the mean pH level of streams with limestone and shale substrates by using two sample t-test.
a. Do you think the assumptions for inference are met (Independent Group Assumption, Independent Assumption, and Nearly normal Condition?) Explain.
b. Perform a 4-step hypothesis test (two sample t-test)?
6. Make a scatterplot of BCI against pH. Describe what you see in the scatterplot .
7. Is there any evidence of an association between BCI and pH?
a. State the null and alternative hypothesis for this test.
b. Make a histogram of the residuals, Normal qq plot of residuals, and a residuals plot (predicted vs residuals). Do you think the assumptions for the inference are met(straight enough condition, Independence assumption, Does the plot thicken? Condition, Nearly normal Condition)? Explain
c. State a conclusion based on the regression analysis( use an appropriate 4-step test.
8. Write the equation of the regression line to predict BCI from pH.
9.Predict the BCI if the pH is 7.2.????????????
Oil and gas reserves sensitivity to log evaluationPeter Cockcroft
A paper by Peter Cockcroft and John Owens about sensitivity of log analysis to oil and gas reserves estimations. Presented to to the Society of Core Analysts in 1990 by John Owens
The objective is to analyze and propose a methodology to manage with the attenuating effect promoted by carbon dioxide - CO2 on the performance of ultrasonic flow meter in gas flaring applications. Such methodology is based on experiments performed in a wind tunnel with a Reynolds number about 10^4 and concentration of CO2 above 60%. The results indicate that the ultrasonic meter exhibited measurement readings failures, especially in stages of abrupt changes in gas concentration, whose contents were above 5%. It is verified, as well, that the approximation of ultrasonic transducers tends to reduce such measurement failures.
1Department of Biotechnology, Techno India University, Salt Lake Campus Kolkata, India
2Department of Microbiology, Techno India University, Salt Lake Campus, Kolkata, India
3Department of Marine Science, University of Calcutta, 35 B.C. Road, Kolkata, India
*Address for Correspondence: Atanu Roy, Research Scholar, Department of Biotechnology, Techno India University,
Salt lake Campus, Kolkata, India
ABSTRACT- Three decades data (1984 – 2015) was used to study the effect of surface water temperature, pH, dissolved
oxygen, nitrate, phosphate and silicate on chlorophyll a concentration in three water bodies meant for fish culture (locally
known as Bheries) in East Kolkata Wetlands. The data revealed significant spatio-temporal variations (p < 0.01). The
increasing trend of temperature, nitrate and phosphate reflects the effect of intense urbanization at local level. The
pronounced variation of dissolved oxygen and chlorophyll a (decreasing trend) may be attributed to increased load of
sewage in the selected water bodies, which has posed an adverse impact on the phytoplankton standing stock as revealed
through decreasing chlorophyll a trend.
Key-words- East Kolkata Wetlands (EKW), Phytoplankton, Chlorophyll a, Nutrients, ANOVA
Espectroscopia de Emissão óptica com plasma induzido por laser: Um novo e ver...NetNexusBrasil
Espectroscopia de Emissão óptica com plasma induzido por laser: Um novo e versátil caminho para análise e monitoramento de solos, plantas e adubos_Giorgio Senesi_Siagro2014_Embrapa Instrumentação
Presentation given by George Romanos of the National Center for Scientific Research “Demokritos” (NCSRD), Greece, on "CO2QUEST - Fluid Properties and phase behaviour of CO2 with impurities" at the EC FP7 Projects: Leading the way in CCS implementation event, London, 14-15 April 2014
Renseanlæg
Hvordan opfører efterklaringstankene under øgede hydraulisk belastning og udvikling af simple modeller som kan anvendes til styring af efterklaringstankene under regn.
Hvilke metoder findes der for at forøge den hydrauliske kapacitet af renseanlæg under regn og praktiske erfaringer fra Spildevandscenter Avedøre ræsentation af det ambitiøse forskningsprojekt Storm- and Waste water Informatics SWI.
Project Streams?
Researchers collected samples of water from 163 streams in the Adirondack Mountains to investigate effects of acidic rain. They recorded a number of biological, chemical, and physical variables, including the stream name, the substrate of the stream (the composition of soil and rock over which they flow – limestone, shale, or mixed, the pH (acidity) of the water, the temperature (° C) of the water, the BCI ( a measure of biological diversity), and hardness of the water.
1. What does a scatterplot show about relationship between the water’s pH and its hardness?
2.
2. Is it appropriate to summarize the strength of association with a correlation? Explain.
3. Make a side by side boxplot of the pH of the streams by substrate(limestone, mixed, or shale)
4. Describe what you see in the comparative boxplots. A lower pH means the water is more acidic.
5. In this question you will compare the mean pH level of streams with limestone and shale substrates by using two sample t-test.
a. Do you think the assumptions for inference are met (Independent Group Assumption, Independent Assumption, and Nearly normal Condition?) Explain.
b. Perform a 4-step hypothesis test (two sample t-test)?
6. Make a scatterplot of BCI against pH. Describe what you see in the scatterplot .
7. Is there any evidence of an association between BCI and pH?
a. State the null and alternative hypothesis for this test.
b. Make a histogram of the residuals, Normal qq plot of residuals, and a residuals plot (predicted vs residuals). Do you think the assumptions for the inference are met(straight enough condition, Independence assumption, Does the plot thicken? Condition, Nearly normal Condition)? Explain
c. State a conclusion based on the regression analysis( use an appropriate 4-step test.
8. Write the equation of the regression line to predict BCI from pH.
9.Predict the BCI if the pH is 7.2.????????????
Oil and gas reserves sensitivity to log evaluationPeter Cockcroft
A paper by Peter Cockcroft and John Owens about sensitivity of log analysis to oil and gas reserves estimations. Presented to to the Society of Core Analysts in 1990 by John Owens
What is the Rate Law for the Crystal Violet Reaction327-43.docxalanfhall8953
What is the Rate Law for the Crystal Violet Reaction?
3/27-4/3/2014
Section 10th
TA: Jinwei Zhang
Group 6
Daylin Morgan
Ahmed Alsharif
Shili Tong
Chang Chuan
Introduction
The main goal of this experiment was about observing the reaction between crystal violet and sodium hydroxide, CV+ + OH- -> CVOH. The objectives of this experiment are to monitor the absorbance of the crystal violet solution as a function of time, and determining the order of the reaction with respect to CV+. The pseudo rate constant k’ in this reaction is derived from the knowledge that OH- and the rate constant can be combined to a single constant. The Beer’s Law relationship between absorbance and concentration for CV+ is used to calculate the concentration in a solution given the Absorbance and a calculated constant. The half-life for this reaction with respect to CV+ and the rate law for this reactionare derived from total data.
Materials & Procedure
Materials
2.5*10-5M CV+(aq)
2.5*10-5 M OH-(aq)
Volumetric measuring equipment
Beaker
Cuvette
Stirring Rod
Spectrophotometer
Each student in a group will measure kinetics of the reaction at different concentration of sodium hydroxide. Before starting kinetic measurements, you should measure the spectrum of the crystal violet in the aqueous solution and establish the wavelength suitable for absorption measurements. Of course, this wavelength is the same for the whole class, so there is no reason to establish it once and once again.
Created 4 different solution of H2O and Crystal Violet at specific concentration. Measured the absorbance of each of these concentration using spectrophotometer and noted absorbance.
Graphed the absorbance vs. concentration, and found line of best-fit with an intercept of 0 to find value of m= εb.
Prepared spectrophotometer for kinetics measurements (separate instructions will be provided for each group).
Pour 10 mL of NaOH solution into 10 mL beaker. CAUTION: Sodium hydroxide solution is caustic. Avoid spilling it on your skin or clothing.
Pour 10 mL of 2.0 X 10-5 M crystal violet solution. CAUTION: Crystal violet is a biological stain. Avoid spilling it on your skin or clothing.
Initiated the reaction, simultaneously poured the 5-mL portions of crystal violet and sodium hydroxide into a 25-mL beaker and stirred the reaction mixture. Rinsed the cuvette with ~1-mL amounts of the reaction mixture and then filled it 3/4 full. Placed the cuvette in the cuvette slot of the spectrophotometer, and clicked "Collect" button. The program collected the absorbance data.
Analyzed the data graphically to decide if the reaction is zero, first, or second order with respect to crystal violet.
Results
Conc.(M)
A
0.000125
1.609
0.0001
1.244
0.000075
1.019
0.00005
0.53
*Measured with λmax= 600nm
Determining Beer-Lambert’s Law
A=εbC
Using the linear-fit line above εb was determined to equal 12695.
Determining the order wrt [CV+]:
To find molarity of CV+ used Beer-Lambert’s Law and value for εb.
Master Thesis Defence: Density of Oil-related Systems at High Pressures - Exp...Vasilis Vasou
The need for more energy recourses in combination with the gradual decrease of easily accessible hydrocarbons has led the industry to exploit deeper reservoirs, which are associated with higher pressures and temperatures. The correct identification of the physical properties of the reservoir hydrocarbons, such us density, is a significant parameter for estimating the amount of recourses in place and forecasting the production. Therefore in this work the measurement of the density of the binary system
methane - n-decane for four different compositions (xmethane = 0, 0.227, 0.6016, 0.8496) and under a wide range of pressure (up to 1400 bar) and temperature (up to 190 °C) was carried out with the use of an Anton Paar DMA-HPM densimeter.
The calibration of the DMA-HPM densimeter was performed for pressures up to 140 MPa (1400 bar) and temperatures up to 190 °C (463.15 K) with a modified Lagourette equation proposed by Comuñas et al and for the validation of the apparatus, the density
of n-decane was measured.
Finally a comparison between two cubic EoS (SRK and PR) and two non-cubic EoS (PC SAFT and SBWR) was performed.
Variations in concentrations of dissolved sugars were studied along the salinity gradient of a small
estuary (Elorn, Bay of Brest, France) from February 1985 to January 1986. Total dissolved carbohydrate
(TDCHO) and dissolved monosaccharides (MCHO) were measured by the methods of Burney
and Sieburth and Johnson and Sieburth respectively. It must be noted that these methods cannot
distinguish between carbohydrates and carbohydrate-like substances; consequently, these methods
probably do not closely reflect biologically available pools of carbohydrates. In the river, TDCHO and
MCHO values ranged from 230 to 970 /ig C 1"' and from 75 to 450 ngC\-^ respectively. In the
estuary, TDCHO and MCHO were usually lower; they varied respectively from 20 to 570 /zg C 1~'
and from 0 to 180/ig C1 '. In June, some TDCHO values were much higher, probably because some
polysaccharide was produced at this time by phytoplankton excretion or lysis.
The relationship between Cl%o and TDCHO was dependent on the seasons. TDCHO was conservative
in autumn, winter and early spring. TDCHO and DOC concentrations were fairly well correlated
during the same period. Similar results have been previously reported by various workers. MCHO
and TDCHO concentrations were well correlated throughout this study except in June. From these
results, it was concluded that most dissolved carbohydrates were linked to a conservative fraction of
the organic matter in periods of low biological activity, whereas newly biosynthesised carbohydrates
were responsible for non-conservative behaviour.
SIMONA CAVALU_Raman and surface-enhanced Raman spectroscopy of tempyo spin la...Simona Cavalu
Tempyo labelled ovalbumin at different pH values was prepared and investigated using Raman and SERS spectroscopy.
Raman spectra of tempyo labelled ovalbumin in the pH range from 6.7 to 11 were compared to those of the corresponding free
ovalbumin. In the basic pH range from 6.7 to 11 the molecular conformation was found to be unaffected by the tempyo
presence. Adsorption versatility to the colloidal Ag particles of pure- and tempyo labelled ovalbumin was also found to be
unchanged in this basic pH range. As the SERS binding site of protein the a-helix conformation is favourable.
Classification either on quality or type based for groundwater can offer great advantages especially in regional groundwater management. It provides a short, quick processing, interpretation for a lot of complete hydro-chemical data sets and concise presentation of the results. There is a demonstrable need for a quality assurance, with the advanced usage of world's largest fresh water storage i.e Ground water. Its getting depleted over the years and the quality of the same degrading with a rapid pace. Ground water Quality is assessed mainly by the chemical analysis of samples. The data obtained from the chemical analysis is key for the further classification, analysis, correlation etc. Graphical and Numerical interpretation of the data is the main source for Hydro-chemical studies. In this paper we test the performance of the many available graphical and statistical methodologies used to classify water samples including: Collins bar diagram, Stiff pattern diagram, Schoeller plot, Piper diagram, Durov's Double Triangular Diagram, Gibbs's Diagram, Stuyfzand Classification. This paper explains various models which classify, correlate etc., summarizing the water quality data. The basic graphs and diagrams in each category are explained by sample diagrams. In addition to the diagrams an overall characterization of hydro-chemical facies of the water can be carried out by using plots which represents a water type and hardness domain. The combination of graphical and statistical techniques provides a consistent and objective means to classify large numbers of samples while retaining the ease of classic graphical presentation.
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Absolute isotopic scale for deuterium analysis of natural waters
1. Absolute isotopic scale for deuterium analysis of natural waters.
Absolute D/H ratio for SMOW’
By R. HAGEMANN, G. NIEF and E. ROTH, Serviw des Isotopes Stables, Centre #Etudes
Nuclkaires de Saclay, B.P. No 2, Gif s/Yvette, France
(Manuscript received July 1; revised version August 31, 1970)
ABSTRACT
The absolute isotopic ratios of the hydrogen content of two referencewater standards
called ‘‘SMOW”eand “SLAP*were measured to define an absoluteisotopic scale. This
isotopic scale can be used to normalize measurements of the natural isotopic variations
in waters. The principle of the method used to define the zero of the scale is given. The
absolute D/H ratios of SMOW and SLAP were measured by mass spectrometriccom-
parison with calibration mixtures prepared in the laboratory. The followingvalues are
obtained:
(g)sMow
= 155.76f0.05 x lo-‘
@) = 89.02 0.05 x lo-‘
SLAP/SMOV=428.50+0.10
Samplesof about 20 cc of the referencestandards SMOW and SLAPare availablefrom
the International Atomic Energy Agency, on request.
Introduction
Variations of the isotopic abundance of
hydrogen in natural waters are most often ex-
pressed in 6 units based on a standard, generally
SMOW. Graig (1961) has defined SMOW with
respect to NBS 1 as (D/H)sMow
=1.050
(D/H)Nssl. From the definition of 6 units it
is clear that different values of the D/H ratio
assigned to SMOW will correspond to different
scales for 6’s. Extreme values for the absolute
D/H ratio for NBS 1 have been found to be
149 x (Horibe, 1960), and 154 x (Roth,
1963), that is for SMOW absolute D/H ratios of
156.45 x and 161.7 x 10-6. These discrepan-
cies explain at least partially why results ob-
tained from different laboratories for the same
samples are not in good agreement as shown by
l Work performed under contract with the
International Atomic Energy Agency.
a StandardMean OceanWater.
* Standard Light Antarctic Precipitation.
Halevy (1967). Moreover, when samples with
very low deuterium content are to be measured
(i.e. measurements on lunar samples), one may
question the significanceof 6 values approaching
1 000 % if the zero of the isotopic scale is not
precisely known.
In order to obtain coherent measurements it
has been shown previously (Hagemann et al.,
1968) that the assignment of deuterium content
of natural waters requires the use of two refer-
ence standards. The measurements will be eleo
accurate if the isotopic scale is defined with
absolute values according to the relation
LmD1e -lstt
4t. -lat1
6Bample/stl= 4Itrlst1
where I are the readings on the mass spectrom-
eter.
The measurements made by interpolation
will be coherent but will be exact only if the b
between the two standards is correctly known.
Tellus XXII (1970),0
2. ISOTOPIC SCdLE FOR DEUTERIUBf ANALYSIS OF NATDRAL WATERS 713
The purpose of this study, undertaken for the
International Atomic Energy Agency, is pre-
cisely to determine the abaolute deuterium con-
tent of two natural waters which could be con-
sidered as reference standards. It has been de-
cided by a panel convened by I.A.E.A. that:
(1) these two standards should be such that
practically the entire range of deuterium con-
centrations of natural waters lies between their
D/H ratios, and (2) that one of them should
have a D/H ratio as close as possible to SMOW,
so that it can validly represent an actual
SMOW sample. This latter standard was pre-
pared in the laboratory of Professor H. Graig
by distillation of Pacific Ocean water. It was
compared in our laboratory with a sample of
NBS 1 and its D/H ratio was found equal to
1.0499 (D/H)NBsl, a value in excellent agree-
ment with the previous definition (Craig, 1961).
Reasonably, therefore, this standard can be
called SMOW. The depleted standard, previ-
ously called SNOW by the I.A.E.A., was ob-
tained from snow collected on the Antarctic
continent. In order to avoid its possible confu-
sion in the future with SMOW, we propose the
name SLAP (Standard Light Antarctic Preci-
pitation).
Experimental
In order to obtain accurate absolute isotopic
ratios of both standards SMOW and SLAP,
the method used is based on the mass spectro-
metric comparison of these two standards with
calibration mixtures. These calibration mixtures
were prepared by mixing weighed amounts of
heavy water with almost pure H,O, both having
very well known isotopic ratios. These last two
waters are the two primary standards of the
laboratory. The molar concentration of the
heavy water, measured by infra-red spectros-
copy (Ceccaldi, 1964), is equal to 0.99847 f
0.00002. The absolute isotopic ratio of thealmost
pure H,O is equal to 1.71 k0.03 x 10-a. The
principle of the method used to measure this
ratio will be given. A detailed description can be
found in a previous work (Hagemann et al.,
1968).
I. Measurement of the absolute D/H ratio of a
water sample with very l
o
w deuterium content
The deuterium content of water after reduc-
tion to hydrogen over a uranium furnace is
Tellus XXII (1970). 6
measured with a mass spectrometer. The prin-
cipal difficulty encountered due to an ion mole-
cule reaction, is the presence of H
: iona which
are generally not separated from HD+ ions.
Obviously, the main point is to determine the
reading on the mass spectrometer for a water
sample without deuterium. The method devel-
oped in this laboratory involves the production
of water vapour with an isotopic ratio very close
to zero using a small distillation column directly
in the line of the mass spectrometer. This column
is shown in Fig. 1.
It consists of a Pyrex tube 50 cm long and of
4 mm internal diameter. At the bottom a 50 cc
flask is used asaboiler. The capillary of the inlet
line of the maas spectrometer fits a t the top of
the condenser. Between this capillary and the
ion source a uranium furnace reduces quantita-
tively water vapour to hydrogen. A 15 cc water
sample carefully outgassed is introduced into
the flask by complete distillation.
This system provides a depletion greater than
5 000 of the vapour at the top with respect to
the water at the bottom of the column. Starting
with low deuterium content water (D/H= 10-O)
this leads to vapour with a D/H ratio less than
10-9, i.e. negligible within the precision of the
measurements (about 10-8). Moreover, such a
system has the advantage of a “dynamic
equilibrium”. It is not imperative that the walk
release absolutely no ordinary water, whose
D/H ratio is about 150 x 10-6, in order to avoid
harmful contamination. As a distillation column
provides continuous transport of deuterium to-
wards the bottom and, if this transport is large
compared with the rate of release from the walls,
the latter does not affect the results. It was de-
monstrated in preliminary experiments that
this condition was fulfilled here (Hagemann et
al., 1968).
The mass spectrometer used for these mea-
surements has essentially the same ion optics as
described by Nief (1959). It is equipped with an
automatic device for numerical measurements
of ion currents, delivering results at regular
periods with asensitivitybetter than 0.01 x
The measurements are usually made with am
ion current a t mass 2 of 4 x 10-0 A. Under these
conditions the H
: peak is leas than 9 x 10-14 A.
The absolute isotopic ratio of the low deu-
terium content water, which serves as the pri-
mary standard in the laboratory was found by
this method to be 1.71 k0.03 x
3. 714 R. HAOEMANN, Q. NIEF AND E. ROTH
-to inlet line
for water surnples
urnnium furnace
' A
l
kcondenser
F;g. 1. Distillation column used to prepare water
vapour with almost zero deuterium content
(D/H< in the line of the mass spectrometer.
This absolute isotopic ratio was checked by
preparing about 20 cc of water without deute-
rium, with a distillation column similar to the
one described above, but equipped with a re-
servoir at the top. This reservoir permitted the
recovery, after a 60-dayrun under known condi-
tions, of 20 cc of water with a calculated D/H
ratio less than 0.01 x 10-6.
The accurate mass spectrometric comparison
between this water and the primary standard
mentioned above led to the assignment to the
latter of an absolute isotopic ratio equal to
1.72 kO.01 x 10-6.
Thus, both methods agree to within 0.01 x
10-6.
After defining the zero of the isotopic scale,
the absolute (D/H) ratios of SMOW and SLAP
were measured.
1
1
.Absolute isotopic ratios of SMOW a& SLAP
The absolute D/H ratios of SMOWand SLAP
were determined using calibration mixtures of
known D/H ratios prepared by mixing weighed
amounts of the two primary laboratory stan-
dards. To prepare the calibration mixtures, a
syringe is used to inject the waters which
constitute the mixture into a 100 cc flask. The
preparation is performed in a glove box under
dry nitrogen flow. The weights are known to a
precision of k0.1 mg. The isotopic composi-
tion of the primary laboratory standards is
taken into account in calculating the D/H
ratios. Then, with the mass spectrometer, these
calibration mixtures were accurately compared
to SMOW and SLAP.
Four calibration mixtures, El to Ed, were
prepared, two with ratios closeto that of SMOW
and two with ratios close to that of SLAP
(Table 1).
To improve the accuracy of the results, two
other methods based on the same principle
were used. In one of these, heavy water was not
used. The calibration mixtures, E, to E8,with
D/H ratios close to that of SLAP are prepared
by mixing known amounts of SMOW and light
water. This method allows the accurate deter-
mination of the 6 % of SLAP relative to SMOW.
In the other method the light primary labora-
tory standard is not used. The calibration mix-
tures, E , to El,, with D/H ratios close to that
of SMOW are prepared by mixing known
amounts of SLAP and heavy water. This method
is used to determine independently the differ-
ence between the absolute D/H ratios of EMOW
and SLAP.
The results are summarized in Table 1.
Table 1. Experimental results for RSLAP,
RsMol
and 6 % SLAP/SMOW
CalibrationConsti- Absolute values
mixtures tuents SMOW and SLAP
SLAP = 89.04 x lo-'
Heavy SLAP= 89.00 x
water
Very light SMOW= 156.78 x lo-"
water
+ SMOW= 155.75 x lo-'
6 % SLAP/SMOW= -428.58
6 % SLAP/SMOW= -428.51
6 % SLAP/SMOW= -428.47
SMOW
+
Very light S % SLAP/SMOW= -428.45
water
SLAP RsMorRsL, =x 66.63 x
+ RsMoTRsLU = 66.68 x
heavy RsMo~RsL, = 66.78 x
water R
S
M
o
r
R
,
, = 66.74 x
Tellus XXII (1970), 6
4. ISOTOPIC SCALE FOR DEUTERIUM ANALYSIS OF NATURAL WATERS 715
Discussion
absolute D/H ratios are:
From the calibration mixtures El to E,, the
RsMow= 155.76 k0.05 x
RsLAp ~ 8 9 . 0 2
k0.05 x lo-"
The quoted uncertainty includes the uncer-
tainty of the measurements on the mass spec-
trometer, (0.02 x lo-") and that of the absolute
ratio of the light primary standard (0.03 x
From the above values, the following are
deduced directly
RSM, -RSLAp e66.74 kO.04 x lo-'
6 % SLAP/SMOW= -428.48 k0.25
The absolute value of 6 % SLAP/SMOW is
found with the best accuracy from the E, to E,
calibration mixtures: 6 % SLAP/SMOW =
This value is in excellent agreement with that
obtained from El to E,.
The mean value for the difference RSMOr
RsLApis found to be 66.71k0.08 x 10-8 from
E, to EIz,this value is also in good agreement
with the one deduced from E, to E,.
-428.50 kO.10.
We retain the following absolute values:
RsMow
= 155.76 k0.05 x
RsLAp =89.02 k0.05 x lom6
6 % SLAP/SMOW = -428.50 kO.10
Conclusions
The calibration mixtures prepared in three
different ways lead to coherent results which
confirm the validity of their method of prepa-
ration. The precision of this preparation method
combined with the sensitivity of the device
used for the numerical measurement of ion cur-
rents on the mass spectrometer have permitted
the definition of the absolute D/H ratios of the
standards SMOW and SLAP to a high accuracy.
The value obtained for the ratio of SMOW is
appreciably lower, from 2 to 4% than the one
adopted in most laboratories.
The D/H ratios measured for SMOW and
SLAP and more precisely the 6 % SLAP/SMOW
define an absolute isotopic scale which may be
used to normalize measurements of the natural
isotopic variations in waters.
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