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1
The world leader in serving science
Improve Analysis Precision for ICP-OES
and ICP-MS for Environmental and
Geological Applications
Speaker 1:
Wei Liu, Ph.D., MBA
Thermo Fisher Scientific
April 14, 2015
Speaker 2:
Guangchao Li, Ph.D.
Stanford University
PP71621-EN 0415S
2
Outline
• Metals geochemical cycling in our environment
• Analysis of metals for the environmental and geological applications
• Brief review of ICP-OES and ICP-MS
• Comparison and selection criteria between ICP-OES and ICP-MS
• Choices of trace metal analysis tools
• Application resources
3
Metals in the Environment
Natural
sources
Industrial
sources
Geochemical
cycling
Uptake in
Food Chain
Wastes
4
Environmental Sample Analysis
• Waters – drinking-, surface-, ground-, waste-
• Soils – soils, sediments, foliage, biota
• Sludges – solid and digested waste
• Air – chimney exhaust filters, air filters of contaminated
sites, dusts
• Applications:
• Trace metal analysis in drinking water and wastewater
• Trace metals analysis in solid waste and groundwater
5
Geological Analyses
• Typical samples: rocks, sediments, slags, ceramics, cements
• Types of work: survey work, quality control, raw material screening
• Applications:
•  Rare earth element analysis
•  Digested rock sample analysis
•  Isotope ratio analysis
• Different needs:
•  Robust to deal with high and low analyte concentrations and demanding
sample preparation
•  Matrix tolerance (TDS) and stability to avoid signal drift
•  Detection limits (traces)
•  Precision and high throughput for isotope analysis
6
General Sample Preparation
• Some samples just require preservation in dilute acid
• Others need full acid digestion with HNO3 and/or HCl and Aqua Regia
e.g. soils and solid wastes
• Digestion can be on a hot plate or using a microwave
• Complete digestion is achieved dependant on method used (for total or
water soluble metals)
• Some applications need to extract elements from samples (soil and
sediments)
• Samples may require filtering after digestion
7
How Does ICP-OES Work?
Sample
atomization in
argon plasma
Liquid
sample
introduction
Detection of
light as
amplified
signals
Excited elements emit
specific wavelengths of light
8
What is ICP-MS?
1. Sample Introduction
Inductively Coupled Plasma - Mass Spectrometry
2. Elements in sample
ionized in Inductively
Coupled Plasma
3. Sampling Interface
4. Interference
removal - CRC
5. Quadrupole Mass
Spectrometer
6. Detector
9
Trace Elemental Analysis Techniques
H
Li
Fr Ra
Sc
Ac
Zr
Hf
Nb
Ta
Tc
Re
Ru
Os
Rh
Ir Hg
In
Tl
Ge
Sb
Bi
S
Te
Po
Cl
F
At
He
Ar
Ne
Kr
Xe
Rn
Pa Pu Am Cm Bk Cf Es Fm Md No LwNp
Not measurable
ICP-MS
Unstable elements
AA/ICP/ICP-MS ICP/ICP-MS
IC
Na
K
Rb
Cs
Be
Mg
Ca
Sr
Ba
Y
La
Ti V Cr
Mo
W
Mn Fe Co Ni
Pd
Pt
Cu
Ag
Au
Zn
Cd
Al
Ga
Sn
Pb
B C ON
Br
I
Si P
As Se
Ce Pr
Th
Nd Pm Sm Eu Gd Tb Dy Ho Er Tm Yb Lu
U
10
Comparison ICP-OES – ICP-MS
Technology
ICP-OES ICP-MS
Detection Limit
Linear Dynamic Range
Isotope Ratio Analysis No Yes
Matrix tolerance high lower
Coupling for Speciation Yes Yes
Speciation No No
Sample recovery No No
106 109
(<1ppb) (<1ppt)
11
Choose Between ICP-OES and ICP-MS
Important factors to consider:
• Applications and regulations
•  What is your application?
•  Does the application need to be regulated?
•  What is the detection limit?
• Sample types and concentration range
•  What matrix for the samples do you use?
•  What concentration range are the samples in?
Other factors to consider:
• Cost ownership
•  How much budget do you plan for ?
•  How clean is the working environment for analysis?
• Operator skills/expertise
•  Will you have a dedicated personnel to run it?
vs.
12
Steps to Ensure Good Precision in ICP-OES and
ICP-MS
•  Ensure peristaltic pump tubing changed regularly and inspected daily
•  Check it’s not crushed (as a result of the pump clamps being left on) or
worn before use
•  Choose best nebulizer type for your samples
•  Glass concentric good for general use
•  High solids nebulisers (e.g. Parallel path type) for heavier matrix samples
•  Low flow if you’re limited in sample volume
•  Optimize the nebuliser gas flow for the most stable signal, while meeting other
required criteria
•  For ICP-OES ensure mirror positions optimized before run, using auto-
optimization routines on the instrument as required
•  For ICP-MS, ensure interface cone orifices are free from deposited material and
ion lens and detector voltages optimized as required before operation
13
Sensitivity
Performance
Thermo Scientific Trace Elemental Analysis
iCE 3300 Series AAS iCAP 7000 Series
Thermo ScientificTM
ELEMENTTM 2 / XRTM ICP-MS
Thermo ScientificTM iCAPTM
Q ICP-MS
Thermo Scientific(TM) iCETM 3500
AAS Atomic Absorption
Spectrometer
AA
ICP-MSICP-OES
14
Environmental Community Pages
Community and landing pages with
hyperlinks:
• Environmental
• Air quality
• Water analysis
• Drinking water analysis
• Wastewater
• Chromium (VI)
• Hydraulic fracturing
• Water analysis resource library
• Water regulations
• Environmental knowledge library
Comprehensive analytical
information provided on the
community and landing
pages:
• Featured brochure/flyers
• Application/technical notes
• White papers
• Poster notes
• Articles
• Case studies
• Webinars
Website: thermoscientific.com/environmental-community
15
Recent Related Webinars
•  Speciation using IC-ICP-MS
•  Complete Inorganic Elemental Speciation Solutions for Environmental Applications
•  www.spectroscopyonline.com/Environmental
•  Overcoming interferences in ICP-OES and ICP-MS
•  Demystifying Interference Removal
•  http://info1.thermoscientific.com/content/CMD_KL_Webinars?kl=ENV_#&rid=10518
•  Cost and ownership
•  Speed and Cost of Ownership
•  http://info1.thermoscientific.com/content/CMD_KL_Webinars?kl=ENV_#&rid=10432
•  The basics of ICP-MS
•  Fundamentals of ICP-MS
•  http://www.chromacademy.com/Fundamentals-of-ICP-MS.html
•  Sample preparation:
•  Demystifying sample preparation for trace metal analysis (April 28, 2015)
•  www.spectroscopyonline.com/spec/Demystifying
Guangchao	
  Li	
  
Environmental	
  Measurements	
  Facility(EMF)	
  
School	
  of	
  Earth,	
  Energy,	
  and	
  Environmental	
  Sciences	
  
Stanford	
  University	
  
Stanford University
Environmental Measurements
Facility (EMF)
• Established	
  in	
  2006	
  by	
  Dean	
  Pam	
  Matson	
  
• Provides	
  quanCtaCve	
  analyses	
  and	
  technical	
  
experCse	
  to	
  members	
  of	
  the	
  Stanford	
  community	
  
needing	
  to	
  conduct	
  gas,	
  solid,	
  and	
  water	
  
measurements	
  
• Accessibility,	
  affordability,	
  and	
  convenience	
  
• Customized	
  analyses	
  for	
  the	
  research	
  needs	
  
Analyses We Provide:
• Gas	
  samples	
  for	
  green	
  house	
  gas	
  analyses-­‐	
  N2O,	
  
CH4,	
  CO2,	
  CO,	
  O2,	
  and	
  N2.	
  	
  
• Solid	
  samples-­‐direct	
  analysis	
  for	
  metal	
  elements	
  
inn	
  soils	
  and	
  sediments:	
  composiCon	
  or	
  
digesCon	
  for	
  later	
  ICP	
  and	
  ICP-­‐MS	
  analyses.	
  
• Aqueous	
  samples	
  for	
  elemental	
  and	
  molecular	
  
analyses.	
  
• Most	
  analyses	
  require	
  high	
  precision	
  and	
  
accuracy	
  due	
  to	
  the	
  low	
  levels	
  of	
  analytes.	
  
Samples We Work With
• Sample	
  Sources:	
  Environmental	
  and	
  geological	
  samples	
  
plus	
  other	
  research	
  samples.	
  
• For	
  solid	
  and	
  gas	
  samples,	
  analyses	
  are	
  preTy	
  straight	
  
forward.	
  	
  
• For	
  aqueous	
  samples,	
  we	
  have	
  very	
  challenging	
  
situaCons.	
  
• Sample	
  types	
  and	
  matrix	
  are	
  very	
  diversified.	
  
•  Simple	
  samples:	
  field	
  collected	
  soluCons	
  
•  Ground	
  water	
  
•  Surface	
  water	
  	
  
•  Complex	
  samples:	
  lab	
  created	
  soluCons	
  
•  ReacCon	
  samples-­‐various	
  matrix	
  and	
  composiCon.	
  
•  ExtracCon	
  (acid,	
  salt,	
  mixed,	
  organic,	
  carbonate)	
  
•  DigesCon	
  (Nitric	
  acid,	
  HCl,	
  HF,	
  Aqua	
  Regia)	
  	
  
Some Typical Projects Creating
Samples
• Arsenic	
  cycling	
  in	
  Cambodia	
  and	
  China.	
  
• Microbial	
  remediaCon	
  of	
  heavy	
  metals	
  
• Mineral	
  weathering	
  
• Surface	
  soil	
  and	
  water	
  contaminaCon	
  from	
  coal	
  
power	
  plants	
  
• Spectranomics	
  	
  
• Radiology	
  research	
  for	
  development	
  of	
  new	
  
technology	
  
• New	
  drug	
  developments	
  
• New	
  material	
  developments	
  
• …	
  	
  
ICP-OES and ICP-MS
• Were	
  used	
  for	
  environmental	
  and	
  geological	
  sample	
  
analysis	
  for	
  many	
  years	
  due	
  to	
  its	
  great	
  sensiCvity,	
  
accuracy	
  and	
  precision,	
  and	
  versaClity	
  	
  	
  
• Helps	
  us	
  beTer	
  understand	
  the	
  environmental	
  
polluCons	
  of	
  heavy	
  metals	
  	
  	
  
• Both	
  instruments	
  have	
  been	
  improved	
  to	
  increase	
  their	
  
popularity:	
  
•  ICP-­‐OES:	
  both	
  radial	
  and	
  axial	
  view	
  for	
  increases	
  of	
  linear	
  
dynamic	
  range	
  
•  ICP-­‐MS:	
  collision/reacCon	
  cell	
  technology	
  	
  for	
  reducCon	
  of	
  
spectral	
  interference	
  
• However,	
  there	
  are	
  many	
  factors	
  impacCng	
  the	
  
measurement	
  precision	
  that	
  are	
  sCll	
  not	
  easy	
  to	
  
overcome	
  or	
  neglected	
  for	
  everyday	
  use	
  	
  	
  
Covered Factors to Improve
Precision
• Among	
  them,	
  some	
  special	
  sample	
  
preparaCon	
  and	
  rinsing	
  have	
  not	
  been	
  paid	
  
much	
  aTenCon.	
  	
  By	
  improving	
  sample	
  
preparaCon	
  and	
  customizing	
  rinse	
  soluCons,	
  
some	
  interesCng	
  results	
  were	
  obtained:	
  
1.  Improved	
  the	
  analysis	
  precision	
  	
  
2.  Made	
  impossible	
  samples	
  to	
  possible	
  to	
  minimize	
  
extra	
  sample	
  preparaCon	
  	
  
3.  Eliminated	
  or	
  reduced	
  diluCon	
  of	
  samples	
  in	
  order	
  
to	
  minimize	
  the	
  error	
  introducCon	
  and	
  detecCon	
  	
  	
  
General Solutions for
Improving Analysis
Precision-1
• Sample	
  prep	
  
•  DigesCon	
  (solid	
  and	
  liquid)	
  
•  FiltraCon	
  (0.2	
  µm	
  filter)	
  to	
  ensure	
  soluCon	
  is	
  parCculates	
  free	
  
•  DiluCon-­‐DiluCon	
  usually	
  can	
  solve	
  much	
  of	
  the	
  problem	
  but	
  it	
  
could	
  introduce	
  error.	
  
•  AcidificaCon	
  	
  
•  Carbonate	
  samples:	
  Pre-­‐acidificaCon	
  will	
  release	
  the	
  CO2	
  
generated	
  
•  PIPES:	
  acidificaCon	
  will	
  precipitate	
  PIPES	
  and	
  then,	
  run	
  the	
  
samples	
  
•  Acid	
  selecCon:	
  	
  	
  
•  Use	
  nitric	
  acid	
  over	
  HCl	
  	
  
•  Use	
  nitric	
  and/or	
  HCl	
  for	
  digesCon	
  if	
  HF	
  can	
  be	
  avoided	
  
•  Dry-­‐down	
  and	
  redissolve-­‐HF	
  digested	
  samples	
  
• Rinse	
  soluCon	
  
• Dilute	
  acid	
  (3%	
  nitric	
  acid)	
  
•  For	
  most	
  of	
  samples	
  such	
  as	
  water,	
  digesCon,	
  extracCon	
  
• Water	
  
•  For	
  any	
  samples	
  that	
  could	
  precipitate	
  in	
  acid	
  condiCon	
  
• Matching	
  matrix	
  soluCon/compaCble	
  rinse	
  
soluCon	
  
•  For	
  samples	
  that	
  precipitate	
  in	
  acidic	
  condiCon	
  but	
  need	
  more	
  
cleaning	
  power,	
  NH4OH	
  can	
  be	
  used	
  for	
  halogens	
  if	
  metals	
  are	
  not	
  
present	
  and	
  interested	
  in	
  or	
  matching/	
  compaCble	
  soluCon	
  
General Solutions for
Improving Analysis Precision-2
Problems We Ran into
• Matrix	
  build-­‐up:	
  sampler	
  and	
  skimmer	
  cones	
  are	
  
easy	
  clogged	
  with	
  matrix	
  build-­‐up	
  and	
  reduces	
  
signal	
  intensity	
  over	
  Cme	
  of	
  the	
  sample	
  analysis	
  
• Plasma	
  shut	
  down:	
  a_er	
  running	
  a	
  few	
  samples,	
  the	
  
plasma	
  shut	
  down	
  and	
  the	
  sample	
  running	
  stops	
  
• PrecipitaCon/clogging:	
  reacCon	
  of	
  sample	
  buffers	
  or	
  
soluCons	
  with	
  rinsing	
  soluCon	
  to	
  generate	
  
precipitates	
  and	
  clog	
  the	
  nebulizer	
  and	
  tubing	
  
Case Study-Matrix Build-up
or Signal Loss
• Causes:	
  
•  High	
  HCl	
  caused	
  down-­‐dri_	
  dramaCcally	
  over	
  Cme.	
  
•  High	
  TDS	
  
• SoluCons:	
  
• High	
  acid	
  conc.:	
  DiluCon	
  with	
  DI	
  water	
  to	
  <5	
  or	
  3%	
  acid	
  
concentraCon	
  in	
  final	
  soluCon	
  
• High	
  TDS:	
  	
  
•  DiluCon	
  with	
  dilute	
  acid	
  (nitric	
  acid	
  over	
  HCl)	
  if	
  compaCble.	
  
•  Dilute	
  with	
  compaCble	
  soluCon	
  but	
  not	
  causing	
  problems	
  with	
  
ICP	
  analysis	
  
Impact of High HCl Matrix on ICP-OES
Analysis
• High	
  concentraCon	
  of	
  acids	
  etc.	
  
•  Many	
  types	
  of	
  geological	
  and	
  environmental	
  samples	
  require	
  
digesCon	
  by	
  acid.	
  	
  High	
  HCl	
  can	
  cause	
  down-­‐dri_	
  dramaCcally	
  
over	
  Cme.	
  
•  High	
  TDS	
  
0	
  
5	
  
10	
  
15	
  
20	
  
25	
  
0	
   10	
   20	
   30	
   40	
  
Conc.,	
  ppm	
  
Time,	
  min	
  
Long	
  Cme	
  rinse	
  to	
  bring	
  reading	
  
back	
  on	
  ICP-­‐OES	
  
Al3092	
   Ba2335	
  
0	
  
5	
  
10	
  
15	
  
20	
  
25	
  
0	
   55	
  
Conc,	
  ppm	
  
Time,	
  min	
  
QC	
  dropped	
  a_er	
  1	
  hrs	
  run.	
  
Begin 48	
  min.	
  
later	
  
•  25%	
  of	
  concentrate	
  HCl.	
  
•  Almost	
  no	
  elements	
  detecCble.	
  
•  Take	
  about	
  30	
  min.	
  rinsing	
  to	
  bring	
  the	
  
signal	
  back.	
  
Solution for High Matrix
Samples
15	
  
16	
  
17	
  
18	
  
19	
  
20	
  
21	
  
22	
  
23	
  
24	
  
25	
  
0	
   50	
   100	
   150	
   200	
   250	
   300	
  
Conc,	
  ppm	
  
Time,	
  min	
  
QC	
  monitoring	
  a1er	
  dilu5ng	
  acid	
  
concentra5on	
  to	
  5%	
  with	
  DI	
  water	
  
Al	
   Ba	
  
Case Study: Plasma Shut-
down
• Causes:	
  carbonate	
  extracted	
  samples	
  
• Na2CO3/NaHCO3	
  is	
  used	
  to	
  extract	
  P	
  in	
  soil	
  
samples	
  	
  
• CO2	
  was	
  produced	
  during	
  rinsing	
  with	
  3%	
  
nitric	
  acid	
  and	
  sample	
  flushing	
  
• Produced	
  CO2	
  either	
  shutdown	
  plasma	
  if	
  the	
  
concentraCon	
  is	
  high	
  or	
  cause	
  bad	
  precision	
  
when	
  it	
  is	
  low	
  
Solutions for Plasma Shut-
down
9	
  
9.2	
  
9.4	
  
9.6	
  
9.8	
  
10	
  
10.2	
  
10.4	
  
10.6	
  
10.8	
  
11	
  
0	
   50	
   100	
   150	
   200	
   250	
  
Conc,	
  ppm	
  
Time,	
  min	
  
QC	
  monitoring	
  a1er	
  pre-­‐acidified	
  
carbonate	
  solu5on	
  
P	
  
•  SoluCons:	
  
•  Pre-­‐acidify	
  the	
  samples	
  
to	
  release	
  the	
  CO2	
  from	
  
soluCon.	
  
•  Take	
  over	
  night	
  to	
  
complete	
  the	
  CO2	
  
release.	
  
Case Study: Precipitation
Clogging•  Causes:	
  
•  Buffer	
  or	
  soluCon	
  reacts	
  with	
  
the	
  rinse	
  soluCon,	
  then	
  forms	
  
precipitate	
  to	
  clog	
  the	
  
nebulizer	
  and	
  tubing	
  
•  Examples:	
  
•  Sodium	
  dithionate	
  extraxcCon	
  
•  Humic	
  acid	
  samples	
  
•  DNA	
  soluCon	
  
•  Oxalate	
  extracCon	
  
•  PIPES	
  
•  SoluCons:	
  
•  Switching	
  rinse	
  
soluCon	
  to	
  water,	
  or	
  
other	
  dilute	
  acid,	
  or	
  
with	
  extra	
  cleaning	
  
soluCon	
  
1. Samples of Sodium Dithionite
Extraction
•  Sodium	
  Dithionite	
  is	
  used	
  with	
  
citrate	
  and	
  bicarbonate	
  to	
  extract	
  
crystalline	
  Fe	
  in	
  environmental	
  
research	
  	
  
•  Problems:	
  
•  High	
  sodium	
  and	
  sulfur	
  contents	
  
•  Elemental	
  sulfur	
  was	
  formed	
  during	
  
rinsing	
  and	
  sample	
  flushing	
  
•  PrecipitaCon	
  of	
  sulfur	
  compounds	
  
•  Clogging	
  nebulizer	
  or	
  line	
  	
  
•  Not	
  possible	
  to	
  run	
  samples	
  
•  How	
  to	
  deal	
  with	
  it:	
  
•  DiluCon	
  with	
  DI	
  water	
  
•  Switching	
  rinse	
  soluCon	
  from	
  3%	
  
nitric	
  acid	
  to	
  DI	
  water,	
  it	
  minimized	
  
the	
  reacCon/decomposiCon	
  of	
  
NaS2O4	
  
0	
  
1	
  
2	
  
3	
  
4	
  
5	
  
6	
  
0	
   50	
   100	
   150	
   200	
   250	
  
Conc.	
  ppb	
  
Time,	
  min.	
  
Dithionite	
  	
  with	
  DI	
  water	
  rinse	
  
Al	
   As	
   B	
   Ca	
   Fe	
  
K	
   Mg	
   Mn	
   P	
   Si	
  
QC	
  varia5on	
  a1er	
  dilu5on	
  
and	
  switching	
  rinse	
  solu5on	
  	
  
2. Humic Acid Samples on
ICP-MS
90	
  
95	
  
100	
  
105	
  
110	
  
115	
  
120	
  
125	
  
130	
  
135	
  
140	
  
0	
   50	
   100	
   150	
   200	
   250	
   300	
   350	
  
Conc,	
  ppb	
  
Time,	
  min.	
  
Dri_	
  Using	
  3%	
  Nitric	
  Acid	
  as	
  
Rinse	
  
Na	
   Fe	
   U	
  
•  Humic	
  acid	
  can	
  
precipitate	
  in	
  
acidic	
  condiCon	
  
•  If	
  dilute	
  acid	
  is	
  
used	
  as	
  rinse	
  
soluCon,	
  ppt	
  
will	
  be	
  formed	
  
either	
  in	
  
sample	
  tubes	
  
or	
  line	
  	
  
•  Nebulizer	
  and	
  
tubing	
  get	
  
clogged	
  
•  NebulizaCon	
  
gets	
  impacted	
  	
  
90	
  
95	
  
100	
  
105	
  
110	
  
115	
  
120	
  
125	
  
0	
   50	
   100	
   150	
   200	
   250	
   300	
   350	
  
Conc,	
  ppb	
  
Time,	
  min.	
  
Water	
  rinse	
  
Na	
   Fe	
  
stdev	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.6	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.2	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  
1.3	
  
QC	
  monitoring	
  a1er	
  switching	
  rinse	
  	
  
to	
  DI	
  water	
  
3. DNA Solution on ICP-MS
70	
  
90	
  
110	
  
130	
  
150	
  
170	
  
190	
  
0	
   50	
   100	
   150	
   200	
   250	
   300	
   350	
  
Conc,	
  ppb	
  
Time,	
  min.	
  
Dri_	
  of	
  DNA	
  soluCon	
  over	
  5.5	
  hrs	
  with	
  3%	
  Nitric	
  
Acid	
  	
  
Li	
   Na	
   P	
   Br	
   Rb	
   Rb	
  
stdev	
  	
  	
  13.4	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  16.6	
  	
  	
  	
  	
  	
  	
  	
  	
  15.4	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  8.1	
  	
  	
  	
  	
  	
  	
  	
  5.3	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  5.2	
  
•  DNA	
  was	
  used	
  in	
  drug	
  
development	
  research	
  	
  
•  DNA	
  can	
  precipitate	
  in	
  
acidic	
  condiCon	
  
•  If	
  dilute	
  acid	
  is	
  used	
  as	
  
rinse	
  soluCon,	
  ppt	
  will	
  be	
  
formed	
  either	
  in	
  sample	
  
tubes	
  or	
  line	
  	
  
•  Nebulizer	
  and	
  tubing	
  get	
  
clogged.	
  
•  NebulizaCon	
  gets	
  impacted	
  	
  
QC Variation of DNA Samples
after Switching to DI Water
Rinse on ICP-MS
90	
  
95	
  
100	
  
105	
  
110	
  
115	
  
120	
  
125	
  
0	
   50	
   100	
   150	
   200	
   250	
   300	
   350	
  
Conc,	
  ppb	
  	
  
Time,	
  min.	
  
Li	
   Na	
   P	
   Br	
   Rb	
  
Stdev	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.5	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.2	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.1	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.0	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  0.8	
  
QC after Switching Rinse with
Extra Cleaning of 5% of NH4OH
90	
  
95	
  
100	
  
105	
  
110	
  
115	
  
120	
  
125	
  
0	
   50	
   100	
   150	
   200	
   250	
   300	
   350	
   400	
  
Conc.	
  ppb	
  
Time,	
  min.	
  
Na	
   P	
   As	
   Br	
   Cs	
  
Stdev	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  0.61	
  	
  	
  	
  	
  	
  	
  	
  0.68	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.21	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1.32	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  0.76	
  	
  
4. Oxalate Extraction on ICP-
OES
4	
  
4.2	
  
4.4	
  
4.6	
  
4.8	
  
5	
  
5.2	
  
5.4	
  
5.6	
  
5.8	
  
0	
   100	
   200	
   300	
   400	
  
Conc,	
  ppm	
  
Time,	
  min.	
  
Al	
   Ca	
  
• 	
  3%	
  nitric	
  acid	
  
as	
  rinse	
  
• 	
  Oxalate	
  
extracCon	
  
soluCon	
  
caused	
  back	
  
pressure	
  of	
  
nebulizer	
  
increase	
  
• 	
  Results	
  
started	
  
fluctuaCng	
  or	
  
dri_ing	
  	
  	
  
4	
  
4.2	
  
4.4	
  
4.6	
  
4.8	
  
5	
  
5.2	
  
5.4	
  
5.6	
  
5.8	
  
0	
   50	
   100	
   150	
   200	
   250	
  
Conc,	
  ppm	
  
Time,	
  min.	
  
Al	
   Ca	
   Fe	
  
K	
   Mg	
   Mn	
  
Improvement of Standard
Deviation After Switching Rinse
Solution on ICP-OES
Rinse
Solution
Al3961 Al3961 Ca3179 Fe2599 Fe2599 K_7664 Mg2852 Mn2576 Mo2020 P_2136 Si2516
	
  3%	
  Acid 0.28 0.27 0.03 0.28 0.23 0.06 0.03 0.02 0.01 0.02 0.08
1%	
  
Oxalic	
  
Acid
0.07 0.05 0.01 0.05 0.05 0.00 0.01 0.00 0.00 0.01 0.02
5. PIPES Samples on ICP-OES
•  PIPES	
  is	
  used	
  as	
  biological	
  buffer	
  
•  PIPES	
  can	
  precipitate	
  in	
  acidic	
  condiCon	
  
•  If	
  dilute	
  acid	
  is	
  used	
  as	
  rinse	
  soluCon,	
  precipitate	
  
will	
  be	
  formed	
  either	
  in	
  sample	
  tubes	
  or	
  line	
  	
  
•  Nebulizer	
  and	
  tubing	
  get	
  clogged	
  
•  NebulizaCon	
  gets	
  impacted	
  	
  
•  What	
  we	
  did:	
  	
  
•  We	
  pre-­‐acidified	
  samples	
  with	
  dilute	
  acid	
  
and	
  stored	
  samples	
  in	
  fridge	
  overnight	
  to	
  
help	
  with	
  the	
  precipitaCon	
  of	
  PIPES	
  
•  Make	
  sure	
  precipitate	
  seTle	
  to	
  boTom	
  
QC Monitoring before and after Precipitating
PIPES
0	
  
5	
  
10	
  
15	
  
20	
  
25	
  
30	
  
35	
  
0	
   50	
   100	
   150	
   200	
  
Conc.	
  ppm	
  
Time,	
  Min	
  
Ca	
   Fe	
   U	
  
0.000	
  
1.000	
  
2.000	
  
3.000	
  
4.000	
  
5.000	
  
6.000	
  
0	
   50	
   100	
   150	
   200	
   250	
   300	
   350	
  
Conc,	
  ppm	
  
Time,	
  min.	
  
PIPES	
  Samples	
  with	
  3%	
  nitric	
  
acid	
  on	
  ICP-­‐OES	
  
Our Findings
•  DiluCon	
  
•  Dilute	
  with	
  dilute	
  acid,	
  nitric	
  or	
  HCl,	
  preferred	
  acid	
  is	
  nitric	
  acid	
  
•  Dilute	
  with	
  water	
  or	
  compaCble	
  soluCon	
  if	
  any	
  matrix	
  could	
  precipitate	
  in	
  
acidic	
  condiCon.	
  
•  Pre-­‐acidificaCon	
  
•  PIPES	
  samples	
  -­‐	
  pre-­‐acidify	
  the	
  samples	
  with	
  dilute	
  acid	
  to	
  precipitate	
  
PIPES	
  
•  Carbonate	
  extracCon	
  samples	
  -­‐	
  should	
  be	
  pre-­‐acidified	
  and	
  let	
  CO2	
  escape	
  
•  Customizing	
  rinse	
  soluCons	
  based	
  on	
  the	
  matrix	
  and	
  compaCbility	
  
•  Oxalate	
  matrix	
  should	
  use	
  dilute	
  oxalic	
  acid	
  
•  Samples	
  with	
  humic	
  acid	
  matrix	
  should	
  use	
  water	
  and	
  diluCon	
  
•  Samples	
  with	
  protein/DNA	
  should	
  use	
  water	
  
•  ...	
  
•  Clean	
  nebulizer	
  and	
  spray	
  chamber	
  with	
  both	
  acid	
  and	
  base	
  
soluCons	
  
Take-home Message
• Sample	
  prep:	
  DiluCon	
  is	
  a	
  very	
  effecCve	
  way	
  to	
  improve	
  
the	
  precision	
  during	
  sample	
  prep,	
  but	
  error	
  introducCon	
  
can	
  impact	
  the	
  precision.	
  So,	
  make	
  decision	
  based	
  on	
  
your	
  precision	
  requirement	
  of	
  research	
  project	
  
• Pre-­‐treat	
  samples	
  if	
  needed	
  to	
  eliminate	
  problems	
  
• Customize	
  rinse	
  soluCon	
  to	
  prevent	
  precipitaCon	
  
Guangchao	
  Li	
  
Environmental	
  Measurements	
  Facility(EMF)	
  
School	
  of	
  Earth,	
  Energy,	
  and	
  Environmental	
  Sciences	
  
Stanford	
  University	
  

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Improve Analysis Precision for ICP-OES and ICP-MS for Environmental and Geological Applications

  • 1. 1 The world leader in serving science Improve Analysis Precision for ICP-OES and ICP-MS for Environmental and Geological Applications Speaker 1: Wei Liu, Ph.D., MBA Thermo Fisher Scientific April 14, 2015 Speaker 2: Guangchao Li, Ph.D. Stanford University PP71621-EN 0415S
  • 2. 2 Outline • Metals geochemical cycling in our environment • Analysis of metals for the environmental and geological applications • Brief review of ICP-OES and ICP-MS • Comparison and selection criteria between ICP-OES and ICP-MS • Choices of trace metal analysis tools • Application resources
  • 3. 3 Metals in the Environment Natural sources Industrial sources Geochemical cycling Uptake in Food Chain Wastes
  • 4. 4 Environmental Sample Analysis • Waters – drinking-, surface-, ground-, waste- • Soils – soils, sediments, foliage, biota • Sludges – solid and digested waste • Air – chimney exhaust filters, air filters of contaminated sites, dusts • Applications: • Trace metal analysis in drinking water and wastewater • Trace metals analysis in solid waste and groundwater
  • 5. 5 Geological Analyses • Typical samples: rocks, sediments, slags, ceramics, cements • Types of work: survey work, quality control, raw material screening • Applications: •  Rare earth element analysis •  Digested rock sample analysis •  Isotope ratio analysis • Different needs: •  Robust to deal with high and low analyte concentrations and demanding sample preparation •  Matrix tolerance (TDS) and stability to avoid signal drift •  Detection limits (traces) •  Precision and high throughput for isotope analysis
  • 6. 6 General Sample Preparation • Some samples just require preservation in dilute acid • Others need full acid digestion with HNO3 and/or HCl and Aqua Regia e.g. soils and solid wastes • Digestion can be on a hot plate or using a microwave • Complete digestion is achieved dependant on method used (for total or water soluble metals) • Some applications need to extract elements from samples (soil and sediments) • Samples may require filtering after digestion
  • 7. 7 How Does ICP-OES Work? Sample atomization in argon plasma Liquid sample introduction Detection of light as amplified signals Excited elements emit specific wavelengths of light
  • 8. 8 What is ICP-MS? 1. Sample Introduction Inductively Coupled Plasma - Mass Spectrometry 2. Elements in sample ionized in Inductively Coupled Plasma 3. Sampling Interface 4. Interference removal - CRC 5. Quadrupole Mass Spectrometer 6. Detector
  • 9. 9 Trace Elemental Analysis Techniques H Li Fr Ra Sc Ac Zr Hf Nb Ta Tc Re Ru Os Rh Ir Hg In Tl Ge Sb Bi S Te Po Cl F At He Ar Ne Kr Xe Rn Pa Pu Am Cm Bk Cf Es Fm Md No LwNp Not measurable ICP-MS Unstable elements AA/ICP/ICP-MS ICP/ICP-MS IC Na K Rb Cs Be Mg Ca Sr Ba Y La Ti V Cr Mo W Mn Fe Co Ni Pd Pt Cu Ag Au Zn Cd Al Ga Sn Pb B C ON Br I Si P As Se Ce Pr Th Nd Pm Sm Eu Gd Tb Dy Ho Er Tm Yb Lu U
  • 10. 10 Comparison ICP-OES – ICP-MS Technology ICP-OES ICP-MS Detection Limit Linear Dynamic Range Isotope Ratio Analysis No Yes Matrix tolerance high lower Coupling for Speciation Yes Yes Speciation No No Sample recovery No No 106 109 (<1ppb) (<1ppt)
  • 11. 11 Choose Between ICP-OES and ICP-MS Important factors to consider: • Applications and regulations •  What is your application? •  Does the application need to be regulated? •  What is the detection limit? • Sample types and concentration range •  What matrix for the samples do you use? •  What concentration range are the samples in? Other factors to consider: • Cost ownership •  How much budget do you plan for ? •  How clean is the working environment for analysis? • Operator skills/expertise •  Will you have a dedicated personnel to run it? vs.
  • 12. 12 Steps to Ensure Good Precision in ICP-OES and ICP-MS •  Ensure peristaltic pump tubing changed regularly and inspected daily •  Check it’s not crushed (as a result of the pump clamps being left on) or worn before use •  Choose best nebulizer type for your samples •  Glass concentric good for general use •  High solids nebulisers (e.g. Parallel path type) for heavier matrix samples •  Low flow if you’re limited in sample volume •  Optimize the nebuliser gas flow for the most stable signal, while meeting other required criteria •  For ICP-OES ensure mirror positions optimized before run, using auto- optimization routines on the instrument as required •  For ICP-MS, ensure interface cone orifices are free from deposited material and ion lens and detector voltages optimized as required before operation
  • 13. 13 Sensitivity Performance Thermo Scientific Trace Elemental Analysis iCE 3300 Series AAS iCAP 7000 Series Thermo ScientificTM ELEMENTTM 2 / XRTM ICP-MS Thermo ScientificTM iCAPTM Q ICP-MS Thermo Scientific(TM) iCETM 3500 AAS Atomic Absorption Spectrometer AA ICP-MSICP-OES
  • 14. 14 Environmental Community Pages Community and landing pages with hyperlinks: • Environmental • Air quality • Water analysis • Drinking water analysis • Wastewater • Chromium (VI) • Hydraulic fracturing • Water analysis resource library • Water regulations • Environmental knowledge library Comprehensive analytical information provided on the community and landing pages: • Featured brochure/flyers • Application/technical notes • White papers • Poster notes • Articles • Case studies • Webinars Website: thermoscientific.com/environmental-community
  • 15. 15 Recent Related Webinars •  Speciation using IC-ICP-MS •  Complete Inorganic Elemental Speciation Solutions for Environmental Applications •  www.spectroscopyonline.com/Environmental •  Overcoming interferences in ICP-OES and ICP-MS •  Demystifying Interference Removal •  http://info1.thermoscientific.com/content/CMD_KL_Webinars?kl=ENV_#&rid=10518 •  Cost and ownership •  Speed and Cost of Ownership •  http://info1.thermoscientific.com/content/CMD_KL_Webinars?kl=ENV_#&rid=10432 •  The basics of ICP-MS •  Fundamentals of ICP-MS •  http://www.chromacademy.com/Fundamentals-of-ICP-MS.html •  Sample preparation: •  Demystifying sample preparation for trace metal analysis (April 28, 2015) •  www.spectroscopyonline.com/spec/Demystifying
  • 16. Guangchao  Li   Environmental  Measurements  Facility(EMF)   School  of  Earth,  Energy,  and  Environmental  Sciences   Stanford  University  
  • 17. Stanford University Environmental Measurements Facility (EMF) • Established  in  2006  by  Dean  Pam  Matson   • Provides  quanCtaCve  analyses  and  technical   experCse  to  members  of  the  Stanford  community   needing  to  conduct  gas,  solid,  and  water   measurements   • Accessibility,  affordability,  and  convenience   • Customized  analyses  for  the  research  needs  
  • 18.
  • 19. Analyses We Provide: • Gas  samples  for  green  house  gas  analyses-­‐  N2O,   CH4,  CO2,  CO,  O2,  and  N2.     • Solid  samples-­‐direct  analysis  for  metal  elements   inn  soils  and  sediments:  composiCon  or   digesCon  for  later  ICP  and  ICP-­‐MS  analyses.   • Aqueous  samples  for  elemental  and  molecular   analyses.   • Most  analyses  require  high  precision  and   accuracy  due  to  the  low  levels  of  analytes.  
  • 20. Samples We Work With • Sample  Sources:  Environmental  and  geological  samples   plus  other  research  samples.   • For  solid  and  gas  samples,  analyses  are  preTy  straight   forward.     • For  aqueous  samples,  we  have  very  challenging   situaCons.   • Sample  types  and  matrix  are  very  diversified.   •  Simple  samples:  field  collected  soluCons   •  Ground  water   •  Surface  water     •  Complex  samples:  lab  created  soluCons   •  ReacCon  samples-­‐various  matrix  and  composiCon.   •  ExtracCon  (acid,  salt,  mixed,  organic,  carbonate)   •  DigesCon  (Nitric  acid,  HCl,  HF,  Aqua  Regia)    
  • 21. Some Typical Projects Creating Samples • Arsenic  cycling  in  Cambodia  and  China.   • Microbial  remediaCon  of  heavy  metals   • Mineral  weathering   • Surface  soil  and  water  contaminaCon  from  coal   power  plants   • Spectranomics     • Radiology  research  for  development  of  new   technology   • New  drug  developments   • New  material  developments   • …    
  • 22. ICP-OES and ICP-MS • Were  used  for  environmental  and  geological  sample   analysis  for  many  years  due  to  its  great  sensiCvity,   accuracy  and  precision,  and  versaClity       • Helps  us  beTer  understand  the  environmental   polluCons  of  heavy  metals       • Both  instruments  have  been  improved  to  increase  their   popularity:   •  ICP-­‐OES:  both  radial  and  axial  view  for  increases  of  linear   dynamic  range   •  ICP-­‐MS:  collision/reacCon  cell  technology    for  reducCon  of   spectral  interference   • However,  there  are  many  factors  impacCng  the   measurement  precision  that  are  sCll  not  easy  to   overcome  or  neglected  for  everyday  use      
  • 23. Covered Factors to Improve Precision • Among  them,  some  special  sample   preparaCon  and  rinsing  have  not  been  paid   much  aTenCon.    By  improving  sample   preparaCon  and  customizing  rinse  soluCons,   some  interesCng  results  were  obtained:   1.  Improved  the  analysis  precision     2.  Made  impossible  samples  to  possible  to  minimize   extra  sample  preparaCon     3.  Eliminated  or  reduced  diluCon  of  samples  in  order   to  minimize  the  error  introducCon  and  detecCon      
  • 24. General Solutions for Improving Analysis Precision-1 • Sample  prep   •  DigesCon  (solid  and  liquid)   •  FiltraCon  (0.2  µm  filter)  to  ensure  soluCon  is  parCculates  free   •  DiluCon-­‐DiluCon  usually  can  solve  much  of  the  problem  but  it   could  introduce  error.   •  AcidificaCon     •  Carbonate  samples:  Pre-­‐acidificaCon  will  release  the  CO2   generated   •  PIPES:  acidificaCon  will  precipitate  PIPES  and  then,  run  the   samples   •  Acid  selecCon:       •  Use  nitric  acid  over  HCl     •  Use  nitric  and/or  HCl  for  digesCon  if  HF  can  be  avoided   •  Dry-­‐down  and  redissolve-­‐HF  digested  samples  
  • 25. • Rinse  soluCon   • Dilute  acid  (3%  nitric  acid)   •  For  most  of  samples  such  as  water,  digesCon,  extracCon   • Water   •  For  any  samples  that  could  precipitate  in  acid  condiCon   • Matching  matrix  soluCon/compaCble  rinse   soluCon   •  For  samples  that  precipitate  in  acidic  condiCon  but  need  more   cleaning  power,  NH4OH  can  be  used  for  halogens  if  metals  are  not   present  and  interested  in  or  matching/  compaCble  soluCon   General Solutions for Improving Analysis Precision-2
  • 26. Problems We Ran into • Matrix  build-­‐up:  sampler  and  skimmer  cones  are   easy  clogged  with  matrix  build-­‐up  and  reduces   signal  intensity  over  Cme  of  the  sample  analysis   • Plasma  shut  down:  a_er  running  a  few  samples,  the   plasma  shut  down  and  the  sample  running  stops   • PrecipitaCon/clogging:  reacCon  of  sample  buffers  or   soluCons  with  rinsing  soluCon  to  generate   precipitates  and  clog  the  nebulizer  and  tubing  
  • 27. Case Study-Matrix Build-up or Signal Loss • Causes:   •  High  HCl  caused  down-­‐dri_  dramaCcally  over  Cme.   •  High  TDS   • SoluCons:   • High  acid  conc.:  DiluCon  with  DI  water  to  <5  or  3%  acid   concentraCon  in  final  soluCon   • High  TDS:     •  DiluCon  with  dilute  acid  (nitric  acid  over  HCl)  if  compaCble.   •  Dilute  with  compaCble  soluCon  but  not  causing  problems  with   ICP  analysis  
  • 28. Impact of High HCl Matrix on ICP-OES Analysis • High  concentraCon  of  acids  etc.   •  Many  types  of  geological  and  environmental  samples  require   digesCon  by  acid.    High  HCl  can  cause  down-­‐dri_  dramaCcally   over  Cme.   •  High  TDS   0   5   10   15   20   25   0   10   20   30   40   Conc.,  ppm   Time,  min   Long  Cme  rinse  to  bring  reading   back  on  ICP-­‐OES   Al3092   Ba2335   0   5   10   15   20   25   0   55   Conc,  ppm   Time,  min   QC  dropped  a_er  1  hrs  run.   Begin 48  min.   later   •  25%  of  concentrate  HCl.   •  Almost  no  elements  detecCble.   •  Take  about  30  min.  rinsing  to  bring  the   signal  back.  
  • 29. Solution for High Matrix Samples 15   16   17   18   19   20   21   22   23   24   25   0   50   100   150   200   250   300   Conc,  ppm   Time,  min   QC  monitoring  a1er  dilu5ng  acid   concentra5on  to  5%  with  DI  water   Al   Ba  
  • 30. Case Study: Plasma Shut- down • Causes:  carbonate  extracted  samples   • Na2CO3/NaHCO3  is  used  to  extract  P  in  soil   samples     • CO2  was  produced  during  rinsing  with  3%   nitric  acid  and  sample  flushing   • Produced  CO2  either  shutdown  plasma  if  the   concentraCon  is  high  or  cause  bad  precision   when  it  is  low  
  • 31. Solutions for Plasma Shut- down 9   9.2   9.4   9.6   9.8   10   10.2   10.4   10.6   10.8   11   0   50   100   150   200   250   Conc,  ppm   Time,  min   QC  monitoring  a1er  pre-­‐acidified   carbonate  solu5on   P   •  SoluCons:   •  Pre-­‐acidify  the  samples   to  release  the  CO2  from   soluCon.   •  Take  over  night  to   complete  the  CO2   release.  
  • 32. Case Study: Precipitation Clogging•  Causes:   •  Buffer  or  soluCon  reacts  with   the  rinse  soluCon,  then  forms   precipitate  to  clog  the   nebulizer  and  tubing   •  Examples:   •  Sodium  dithionate  extraxcCon   •  Humic  acid  samples   •  DNA  soluCon   •  Oxalate  extracCon   •  PIPES   •  SoluCons:   •  Switching  rinse   soluCon  to  water,  or   other  dilute  acid,  or   with  extra  cleaning   soluCon  
  • 33. 1. Samples of Sodium Dithionite Extraction •  Sodium  Dithionite  is  used  with   citrate  and  bicarbonate  to  extract   crystalline  Fe  in  environmental   research     •  Problems:   •  High  sodium  and  sulfur  contents   •  Elemental  sulfur  was  formed  during   rinsing  and  sample  flushing   •  PrecipitaCon  of  sulfur  compounds   •  Clogging  nebulizer  or  line     •  Not  possible  to  run  samples   •  How  to  deal  with  it:   •  DiluCon  with  DI  water   •  Switching  rinse  soluCon  from  3%   nitric  acid  to  DI  water,  it  minimized   the  reacCon/decomposiCon  of   NaS2O4   0   1   2   3   4   5   6   0   50   100   150   200   250   Conc.  ppb   Time,  min.   Dithionite    with  DI  water  rinse   Al   As   B   Ca   Fe   K   Mg   Mn   P   Si   QC  varia5on  a1er  dilu5on   and  switching  rinse  solu5on    
  • 34. 2. Humic Acid Samples on ICP-MS 90   95   100   105   110   115   120   125   130   135   140   0   50   100   150   200   250   300   350   Conc,  ppb   Time,  min.   Dri_  Using  3%  Nitric  Acid  as   Rinse   Na   Fe   U   •  Humic  acid  can   precipitate  in   acidic  condiCon   •  If  dilute  acid  is   used  as  rinse   soluCon,  ppt   will  be  formed   either  in   sample  tubes   or  line     •  Nebulizer  and   tubing  get   clogged   •  NebulizaCon   gets  impacted     90   95   100   105   110   115   120   125   0   50   100   150   200   250   300   350   Conc,  ppb   Time,  min.   Water  rinse   Na   Fe   stdev                          1.6                                          1.2                                     1.3   QC  monitoring  a1er  switching  rinse     to  DI  water  
  • 35. 3. DNA Solution on ICP-MS 70   90   110   130   150   170   190   0   50   100   150   200   250   300   350   Conc,  ppb   Time,  min.   Dri_  of  DNA  soluCon  over  5.5  hrs  with  3%  Nitric   Acid     Li   Na   P   Br   Rb   Rb   stdev      13.4                      16.6                  15.4                    8.1                5.3                        5.2   •  DNA  was  used  in  drug   development  research     •  DNA  can  precipitate  in   acidic  condiCon   •  If  dilute  acid  is  used  as   rinse  soluCon,  ppt  will  be   formed  either  in  sample   tubes  or  line     •  Nebulizer  and  tubing  get   clogged.   •  NebulizaCon  gets  impacted    
  • 36. QC Variation of DNA Samples after Switching to DI Water Rinse on ICP-MS 90   95   100   105   110   115   120   125   0   50   100   150   200   250   300   350   Conc,  ppb     Time,  min.   Li   Na   P   Br   Rb   Stdev                      1.5                            1.2                                        1.1                          1.0                            0.8  
  • 37. QC after Switching Rinse with Extra Cleaning of 5% of NH4OH 90   95   100   105   110   115   120   125   0   50   100   150   200   250   300   350   400   Conc.  ppb   Time,  min.   Na   P   As   Br   Cs   Stdev                        0.61                0.68                    1.21                    1.32                    0.76    
  • 38. 4. Oxalate Extraction on ICP- OES 4   4.2   4.4   4.6   4.8   5   5.2   5.4   5.6   5.8   0   100   200   300   400   Conc,  ppm   Time,  min.   Al   Ca   •   3%  nitric  acid   as  rinse   •   Oxalate   extracCon   soluCon   caused  back   pressure  of   nebulizer   increase   •   Results   started   fluctuaCng  or   dri_ing       4   4.2   4.4   4.6   4.8   5   5.2   5.4   5.6   5.8   0   50   100   150   200   250   Conc,  ppm   Time,  min.   Al   Ca   Fe   K   Mg   Mn  
  • 39. Improvement of Standard Deviation After Switching Rinse Solution on ICP-OES Rinse Solution Al3961 Al3961 Ca3179 Fe2599 Fe2599 K_7664 Mg2852 Mn2576 Mo2020 P_2136 Si2516  3%  Acid 0.28 0.27 0.03 0.28 0.23 0.06 0.03 0.02 0.01 0.02 0.08 1%   Oxalic   Acid 0.07 0.05 0.01 0.05 0.05 0.00 0.01 0.00 0.00 0.01 0.02
  • 40. 5. PIPES Samples on ICP-OES •  PIPES  is  used  as  biological  buffer   •  PIPES  can  precipitate  in  acidic  condiCon   •  If  dilute  acid  is  used  as  rinse  soluCon,  precipitate   will  be  formed  either  in  sample  tubes  or  line     •  Nebulizer  and  tubing  get  clogged   •  NebulizaCon  gets  impacted     •  What  we  did:     •  We  pre-­‐acidified  samples  with  dilute  acid   and  stored  samples  in  fridge  overnight  to   help  with  the  precipitaCon  of  PIPES   •  Make  sure  precipitate  seTle  to  boTom  
  • 41. QC Monitoring before and after Precipitating PIPES 0   5   10   15   20   25   30   35   0   50   100   150   200   Conc.  ppm   Time,  Min   Ca   Fe   U   0.000   1.000   2.000   3.000   4.000   5.000   6.000   0   50   100   150   200   250   300   350   Conc,  ppm   Time,  min.   PIPES  Samples  with  3%  nitric   acid  on  ICP-­‐OES  
  • 42. Our Findings •  DiluCon   •  Dilute  with  dilute  acid,  nitric  or  HCl,  preferred  acid  is  nitric  acid   •  Dilute  with  water  or  compaCble  soluCon  if  any  matrix  could  precipitate  in   acidic  condiCon.   •  Pre-­‐acidificaCon   •  PIPES  samples  -­‐  pre-­‐acidify  the  samples  with  dilute  acid  to  precipitate   PIPES   •  Carbonate  extracCon  samples  -­‐  should  be  pre-­‐acidified  and  let  CO2  escape   •  Customizing  rinse  soluCons  based  on  the  matrix  and  compaCbility   •  Oxalate  matrix  should  use  dilute  oxalic  acid   •  Samples  with  humic  acid  matrix  should  use  water  and  diluCon   •  Samples  with  protein/DNA  should  use  water   •  ...   •  Clean  nebulizer  and  spray  chamber  with  both  acid  and  base   soluCons  
  • 43. Take-home Message • Sample  prep:  DiluCon  is  a  very  effecCve  way  to  improve   the  precision  during  sample  prep,  but  error  introducCon   can  impact  the  precision.  So,  make  decision  based  on   your  precision  requirement  of  research  project   • Pre-­‐treat  samples  if  needed  to  eliminate  problems   • Customize  rinse  soluCon  to  prevent  precipitaCon  
  • 44. Guangchao  Li   Environmental  Measurements  Facility(EMF)   School  of  Earth,  Energy,  and  Environmental  Sciences   Stanford  University