calibration and inter-comparisons between instruments ... · detected by users via telemetry....
TRANSCRIPT
Calibration and inter-comparisons between instruments – WQM FLNTU’s
National Reference Stations – time series dataSensors and Sampling
Key* - long term site# - infrastructure deployed+ - Telemetry^ BGC sampling
QC sensors vs. BGC water samplingCombine for cross validation
Sensors• 9 QC tests• Scientist per site• Matlab toolbox• Methods papers• NATA cal lab
BGC• 4 central processing laboratories
• Scientist per lab• Training• Sampling/lab guides• Taxonomic guides
NRS design– Many FLNTUs
CSIRO. Insert presentation title, do not remove CSIRO from start of footer
FLNTU – Fluorometer and backscatter
Lesson Learnt – Bio-fouling of sensors after 6 monthsDetected by users via telemetry
Quality Control – Fuzzy logic – look at the other sensor – take photograph of the sensor
Perform a detailed characterization to determine the actual zero point and scale factor
Determine accurate blank, equivalent phytoplankton types and similar physiological conditions for calculating the scale factor
FLNTU – owners manual
Occurs singly, groups and embedded in a gelatinous matrix
Used in aquaculture
Asexual phase involves cell division with each of the new individuals receiving one of the valves. This means that the offspring are of unequal sizes and successive generations tend to decrease in size.
Large individuals can also reproduce sexually
Thalassiosira weissflogii - factory set scale factorSingle point solid standard – factory set calibration
Key lesson learnt for sustained observing QC – inter sensor comparability
• Spiking (physicists vs. biologists)• Change of calibration method from
single to multiple point
• Changing of sensors replacedduring servicing of instrument
y = 0.6506x + 0.3566R² = 0.8285
0
0.5
1
1.5
2
2.5
3
0 0.5 1 1.5 2 2.5 3
WQ
M
Bottle sample
Comparisons sensor to bottle @ 20 m
mean CPHL
Linear (mean CPHL)
Cross validation of sensor to monthly BGC samples – Chlorophyll 20m Maria Island NRS
Chlorophyll 80m Maria Island NRS
y = 1.1654x + 0.0824R² = 0.8994
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
0 0.2 0.4 0.6 0.8 1
WQ
M
Bottle sample
Comparisons sensor to bottle @ 80 m
mean CPHL
Linear (mean CPHL)
y = 0.3618x + 0.0431R² = 0.9782
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0 0.5 1 1.5 2 2.5
Mea
n on
WQ
M 3
nea
rest
bur
sts
Bottle sample
Comparisons sensor to bottle @ 25m
Chlorophyll 25m Port Hacking NRS –mean of 3 bursts
Back to the lab
NATA Certified Calibration lab
Australian Algae collection
Many FLNTUs on hand
Highly skilled staff (not me!)
Compare multiple algal mono-cultures to one FLNTU
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
0 10 20 30 40 50 60 70
Wet
labs
Chl
Time (sec)
WQM-040 (Chl scale factor 0.007)
#1 Thalassiosira oceanica #2 Tetraselmis sp. #3 Hetrocapsa niei#4 Synechococcus sp. #5 Ditylum brightwelli #6 Nannochloropsis
Bio-optical instrument characterization HPLC vs. single FLNTU across 3 x 3 replicates of representative algae
0
1
2
3
4
5
6
7
8
chl-a
(ug/
L)
Instrument and algae type and replication
0
2
4
6
8
10
12
1 11 21 31 41 51 61 71 81
WQM chl‐a (u
g/L)
Reading number
Nannochloropsis oculata Wetlabs
129#6_rep1
127#6_rep1
96#6_rep1
41#6_rep1
40#6_rep1
Compare multiple instruments – factory settingsRandom design
Move to a new calibration standard
Factory WQM - Single solid standard
CSIRO - Multipoint Fluorescein calibration
0
5
10
15
20
25
30
35
1 11 21 31 41 51 61 71 81
WQ
M c
hl-a
(ug\
L)
Reading number
Nannochloropsis oculata CMAR
129#6_rep3
127#6_rep3 CMAR
96#6_end run CMAR
41#6_rep3CMAR
40#6_rep3CMAR
New multi-point fluorescence calibration – notescale change, as not scaled to Thalassiosira weissflogii
y = 0.0216x - 3.3255R² = 0.9802
0
10
20
30
40
50
60
70
80
90
100
0 500 1000 1500 2000 2500 3000 3500 4000 4500
Raw
Chl
Cou
nts
Concentration (μg/L)
WQM Chl-a Calibration Curve Using Fluorescein:
WQM 127 Fluroescein calibration
y = 0.0243x - 0.8938R² = 0.9999
0
10
20
30
40
50
60
70
80
90
100
0 500 1000 1500 2000 2500 3000 3500 4000
Raw
Chl
Cou
nts
Concentration (μg/L)
WQM Chl-a Calibration Curve Using Fluorescein:
WQM 41 Fluorescein calibration
0
5
10
15
20
25
30
1 11 21 31 41 51 61 71 81
WQ
M c
hl-a
(ug\
L)
Reading Number
Nannochloropsis oculata CMAR remove WQM 127 and 96
129#6_rep1 CMAR
41#6_rep2CMAR
40#6_rep3CMAR
Remove the bogus instruments – starting to get repeatable
0
5
10
15
20
25
30
HPLC output WQM CMAR HPLC WQM Wetlabs Wetlabs WQM CMAR None
Ave
rage
with
SD
Chl
a (u
g/L)
Sensor, Calibration and Characterisations type
Nannochloropsis #6 (high)
Tetraselmis sp. #2 (medium)
Synechoccoccus sp. # 4 (low)
Characterize against the HPLC standard and nowboth precise and accurate across 3 species of algae
Esperance
peridinin = dinoflagellatesalloxanthin = chryptophytes19 but ~ pelagophytesfucoxanthin ~ diatoms19 hex ~ coccolithophoridszeaxanthin ~ SynechococcusDV chla = ProchlorococcusChlb ~ greensneoxanthin ~ greensprasinoxanthin ~ greens
Rottnest IslandNingaloo
Yongala
North Stradbroke Island
Port Hacking
Maria Island
Kangaroo Island
Darwin
Across the system now need to recalibrate instruments, characterize against the HPLC results and reprocess
History of FLNTUSB Loggers at AIMS• Purchased first 3 instruments in 2006• Routine use started Oct 2007 at 14 sites deployed on inshore reefs• Problems with negative Chl values - 2006• Logger step changes noticed and discussions with company in ~2008• Internal calibrations developed:
• Pontoon deployments with regular direct water sampling (since August 2010) - natural water
• Tank deployments with plankton bloom initiated by nutrient addition• Tank deployments with plankton culture added
• After discussions with WET Labs loggers sequentially sent to WET Labs for Uranine cal as they were retrieved from the field for recalibration
• Meeting with WET Labs after ICRS (mid July) and discussed multiplication by a ratio: Uranine pre-cal / old-cal as easiest adjustment solution.
• Adjustment results showing varied success• Solution still required for problem loggers and those with negative
values
AIMS pontoon co-deploymentsfor chlorophyll QC 2010
Chlorophyll (µg L-1):•High inter-logger variability apparent, range ~0.5 µg L-1•Only instrument 816 shows good agreement with results from water sampling for chlorophyll.
AIMS pontoon co-deployments for turbidity QC 2010
Turbidity (NTU):•Good agreement between loggers, apart from a few spikes
•Suspended solids data from water sampling (mg L-1) included for reference,.
Test deployment with ratio adjustment applied
Ratio adjustment with ref samples
Performance of new uranine cal
Conclusions
•Some FLNTUs produce poor quality data
•FLNTU’s can return good field data
•FLNTU’s need categorisation
•FLNTU’s require multi-point calibrations
Authors:Tim Lynch, Lesley Clementson, Robert Kay, Guillaume Galibert, Irena Zagorskis
NRS teams:Anthony Richardson and his team
Pru Bonham and Peter Thompson
John Middleton and Charles James
Ming Feng and Liejun Zhong
Craig Steinberg, Vittorio Brando, Martina Doblin
Brad Morris, Moninya Roughan
Ken Ridgeway, Darren Moore
Acknowledgements
Contact UsPhone: 1300 363 400 or +61 3 9545 2176
Email: [email protected] Web: www.csiro.au
Thank you