evaluation of sensors and analysers

45
7th 7th Anque’s Anque’s international Congress international Congress Water in industry Water in industry AquaFit4Use SP2 : Waste water treatment AquaFit4Use SP2 : Waste water treatment EVALUATION OF SENSORS EVALUATION OF SENSORS AND ANALYSERS AND ANALYSERS Marie MAUREL Marie MAUREL Yannik LADEGAILLERIE Yannik LADEGAILLERIE VEOLIA ENVIRONNEMENT VEOLIA ENVIRONNEMENT SP2 meeting SP2 meeting – Oviedo Oviedo 14.06.2010 14.06.2010 AND ANALYSERS AND ANALYSERS

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Sensors and Analysers for Wastewater treatment.

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Page 1: Evaluation of Sensors and Analysers

7th 7th Anque’sAnque’s international Congressinternational Congress

Water in industryWater in industryAquaFit4Use SP2 : Waste water treatmentAquaFit4Use SP2 : Waste water treatment

EVALUATION OF SENSORS EVALUATION OF SENSORS

AND ANALYSERSAND ANALYSERS

Marie MAURELMarie MAUREL

Yannik LADEGAILLERIEYannik LADEGAILLERIE

VEOLIA ENVIRONNEMENTVEOLIA ENVIRONNEMENT

SP2 meeting SP2 meeting –– OviedoOviedo

14.06.201014.06.2010

AND ANALYSERSAND ANALYSERS

Page 2: Evaluation of Sensors and Analysers

AgendaAgenda

�� Task 2.1.1 Evaluation of Sensors and AnalysersTask 2.1.1 Evaluation of Sensors and Analysers

�� Context and ObjectivesContext and Objectives

�� Material and MethodsMaterial and Methods

�� Results about CODResults about COD

OnOn--going and future workgoing and future work�� OnOn--going and future workgoing and future work

Page 3: Evaluation of Sensors and Analysers

Context & ObjectivesContext & Objectives

Task 2.1.1 Task 2.1.1 -- EVALUATION OF SENSORS AND ANALYSERSEVALUATION OF SENSORS AND ANALYSERS

Context & ObjectivesContext & Objectives

Page 4: Evaluation of Sensors and Analysers

Context & General objectivesContext & General objectives

�� ContextContext

�� Process modelling and control needs adequate measurementsProcess modelling and control needs adequate measurements

�� Parameters must be chosen among the list set by WP 1.1Parameters must be chosen among the list set by WP 1.1

�� ObjectivesObjectives

�� Define sensors benchmark and criteria of comparison Define sensors benchmark and criteria of comparison

�� Execute labExecute lab--scale tests for sensor evaluationscale tests for sensor evaluation

�� Execute test for sensor evaluation on real industrial waste water Execute test for sensor evaluation on real industrial waste water samplessamples

Page 5: Evaluation of Sensors and Analysers

Main Parameter chosen: Main Parameter chosen:

the Chemical Oxygen Demand (COD)the Chemical Oxygen Demand (COD)

�� Definition:Definition:�� Indirect measurement of organic compounds in waterIndirect measurement of organic compounds in water�� Mass of oxygen consumed to oxidize one litter of solutionMass of oxygen consumed to oxidize one litter of solution

�� Interest:Interest:�� Good indicator of the efficiency of a process Good indicator of the efficiency of a process �� This parameter is interesting at all stages of all processesThis parameter is interesting at all stages of all processes�� This parameter is interesting at all stages of all processesThis parameter is interesting at all stages of all processes

�� Concentrations:Concentrations:�� Pure water:Pure water: 00�� Potable water:Potable water: < 2 mgO2/L (~TOC)< 2 mgO2/L (~TOC)�� Surface water:Surface water: 20 mgO2/L (~TOC)20 mgO2/L (~TOC)�� Raw Waste water:Raw Waste water: 1000 mgO2/L1000 mgO2/L�� Outlet of industrial waste water plant: Outlet of industrial waste water plant: < 150 mgO2/L< 150 mgO2/L

Page 6: Evaluation of Sensors and Analysers

Secondary Parameters chosen: Secondary Parameters chosen:

Total Nitrogen (N), Calcium (Ca), Lead (Pb)Total Nitrogen (N), Calcium (Ca), Lead (Pb)

�� Definition:Definition:�� Total N = NH4 + organic N + NOTotal N = NH4 + organic N + NO33 + NO+ NO22

�� Interest:Interest:�� Total N: salt, able to inhibit biological activity, necessary control of N to Total N: salt, able to inhibit biological activity, necessary control of N to

avoid eutrophisation in case of dischargeavoid eutrophisation in case of discharge�� Ca: indicator of water hardness, source of depositsCa: indicator of water hardness, source of deposits�� Ca: indicator of water hardness, source of depositsCa: indicator of water hardness, source of deposits�� Pb: example of heavy metal Pb: example of heavy metal

�� Concentrations for Total N:Concentrations for Total N:�� Potable waterPotable water < 50 mgN/L< 50 mgN/L

�� Raw Waste water :Raw Waste water : 100 mgN/L100 mgN/L

�� Outlet of waste water plant: Outlet of waste water plant: < 10< 10--15 mgN/L15 mgN/L

�� Industrial waste water:Industrial waste water: > 1000 mgN/L> 1000 mgN/L

Page 7: Evaluation of Sensors and Analysers

Material & MethodMaterial & Method

Task 2.1.1 Task 2.1.1 -- EVALUATION OF SENSORS AND ANALYSERSEVALUATION OF SENSORS AND ANALYSERS

Material & MethodMaterial & Method

Page 8: Evaluation of Sensors and Analysers

�� Analyse of the absorption for the whole Analyse of the absorption for the whole spectrum:spectrum:�� Spectro::Lyser (S::CAN)Spectro::Lyser (S::CAN)

�� Carbovis (WTW)Carbovis (WTW)

�� Analyse of absorption for only 1 or 2 Analyse of absorption for only 1 or 2

Instruments tested for CODInstruments tested for COD

�� Analyse of absorption for only 1 or 2 Analyse of absorption for only 1 or 2 wavelengths:wavelengths:�� Uvas (HachUvas (Hach--Lange)Lange)

�� Trescon SAC Module (WTW)Trescon SAC Module (WTW)

�� Oxidation with UV activated TiO2 photoOxidation with UV activated TiO2 photo--catalyst:catalyst:�� PeCOD P100 (AquaDiagnostic)PeCOD P100 (AquaDiagnostic)

Page 9: Evaluation of Sensors and Analysers

Absorption Absorption -- Measurement principleMeasurement principle

�� The COD can be correlated with the UVThe COD can be correlated with the UV--VIS measurement (254 nm).VIS measurement (254 nm).

�� This measurement must be compensated with turbidity (visible wave This measurement must be compensated with turbidity (visible wave length)length)

Page 10: Evaluation of Sensors and Analysers

PeCOD PeCOD –– Measurement principleMeasurement principle

Page 11: Evaluation of Sensors and Analysers

�� Analyse of gas from thermal oxidation Analyse of gas from thermal oxidation (total Nitrogen):(total Nitrogen):

�� QuickTONb (ANAEL) QuickTONb (ANAEL)

�� Selective electrodes for Calcium (Ca):Selective electrodes for Calcium (Ca):

�� Orion (Thermo)Orion (Thermo)

Instruments tested for Total N, Ca and PbInstruments tested for Total N, Ca and Pb

�� Orion (Thermo)Orion (Thermo)

�� MetrohmMetrohm

�� Schott (WTW)Schott (WTW)

�� Selective electrodes for Lead (Pb):Selective electrodes for Lead (Pb):

�� Orion (Thermo)Orion (Thermo)

�� MetrohmMetrohm

�� Schott (WTW)Schott (WTW)

Page 12: Evaluation of Sensors and Analysers

�� Full combustion and thermal oxidation of the sample at 1200Full combustion and thermal oxidation of the sample at 1200°°CC

�� Condensation of the gas at 4Condensation of the gas at 4°°CC

�� Use of specific sensorUse of specific sensor

Thermal oxidation Thermal oxidation –– Measurement principleMeasurement principle

Selective electrodes Selective electrodes –– Measurement principleMeasurement principleSelective electrodes Selective electrodes –– Measurement principleMeasurement principle

�� Measurement of electrical potential for a targeted ionMeasurement of electrical potential for a targeted ion

�� Comparison with a reference electrodeComparison with a reference electrode

Page 13: Evaluation of Sensors and Analysers

Reference Measurement for CODReference Measurement for COD

�� Based on ISO 15705Based on ISO 15705

�� Measurement of the mass of potassium dichromate that reacts with the Measurement of the mass of potassium dichromate that reacts with the oxidizable substances in sample under the working conditions of the method.oxidizable substances in sample under the working conditions of the method.

�� Reaction time of 2 hours at 148 Reaction time of 2 hours at 148 °°C. C.

Page 14: Evaluation of Sensors and Analysers

Test protocolTest protocol

�� Protocol developed:Protocol developed:

�� Laboratory tests (on synthetic samples)Laboratory tests (on synthetic samples)

�� Evaluation of sensor performances (static, dynamic)Evaluation of sensor performances (static, dynamic)

�� Pilot tests (on real water)Pilot tests (on real water)

�� Evaluation of maintenance costsEvaluation of maintenance costs�� Evaluation of maintenance costsEvaluation of maintenance costs

�� Evaluation of interferencesEvaluation of interferences

LOD

SDC20

SDC80B20

B80

0

10

20

30

40

50

60

70

80

90

100

110

120

130

X - Time

Y -

Re

sp

on

se

in

%

Delay Time Response Time

Fall TimeRiseTime

Page 15: Evaluation of Sensors and Analysers

Choice of a synthetic sample for CODChoice of a synthetic sample for COD

�� Choice between 3 existing synthetic samples:Choice between 3 existing synthetic samples:�� Brenntaplus (Brenntag GmbH):Brenntaplus (Brenntag GmbH):

�� Acetic acid (25 % Acetic acid (25 % -- 50 %),50 %),�� Dark brown liquid Dark brown liquid �� COD ~ 1000 gOCOD ~ 1000 gO22/L/L

�� Canadian formula:Canadian formula:�� Potassium Biphtalate, phosphatePotassium Biphtalate, phosphate�� Potassium Biphtalate, phosphatePotassium Biphtalate, phosphate�� COD ~ 1 gOCOD ~ 1 gO22/L /L

�� OCDE:OCDE:�� Main compound : Viandox (Main compound : Viandox (salty sauce with a little meat extract and salty sauce with a little meat extract and

flavored)flavored)�� Dark brown liquidDark brown liquid�� COD ~ 79 gOCOD ~ 79 gO22/L/L

�� OCDE was chosen due to similarity with urban waste waterOCDE was chosen due to similarity with urban waste water

Page 16: Evaluation of Sensors and Analysers

Choice of a synthetic sample for CODChoice of a synthetic sample for COD

Absorption spectra of synthetic samples of COD = 1000 mg/L

2

2,5

Ab

so

rpti

on

(1/m

)

OCDE

Canadian receip

BrenntaPlus

Urban Waste Water

0

0,5

1

1,5

150 200 250 300 350 400 450 500

Wavelength (nm)

Ab

so

rpti

on

(1/m

)

Page 17: Evaluation of Sensors and Analysers

Results about CODResults about COD

Task 2.1.1 Task 2.1.1 -- EVALUATION OF SENSORS AND ANALYSERSEVALUATION OF SENSORS AND ANALYSERS

Results about CODResults about COD

Page 18: Evaluation of Sensors and Analysers

Results about CODResults about COD

�� Tests performed for 5 devices:Tests performed for 5 devices:�� Use of OCDEUse of OCDE�� Scale: Scale: 0 mgO2/L < COD < 1000 mgO2/L0 mgO2/L < COD < 1000 mgO2/L

�� Interpretation of results needs to be completed in Interpretation of results needs to be completed in collaboration with the supplierscollaboration with the supplierscollaboration with the supplierscollaboration with the suppliers

Page 19: Evaluation of Sensors and Analysers

Results about COD:Results about COD:

Carbovis (WTW) Carbovis (WTW) –– AccuracyAccuracy

550

600

650

700

750

800

850

900

Carbovis WTW Reference

-50

0

50

100

150

200

250

300

350

400

450

500

11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30

Time (hour:minute)

CO

D (

mg

/L)

Page 20: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Carbovis (WTW) Carbovis (WTW) –– DynamicsDynamics

550

600

650

700

750

800

850

900

Carbovis WTW Reference

-50

0

50

100

150

200

250

300

350

400

450

500

550

11:31 12:01 12:31 13:01 13:31 14:01 14:31 15:01 15:31 16:01 16:31 17:01 17:31 18:01

Time (hour:minute)

CO

D (

mg

/L)

Page 21: Evaluation of Sensors and Analysers

Results for COD: Results for COD:

Trescon (WTW) Trescon (WTW) –– AccuracyAccuracy

550

600

650

700

750

800

850

900

TresCon WTW Reference

-50

0

50

100

150

200

250

300

350

400

450

500

11:53 12:23 12:53 13:23 13:53 14:23 14:53 15:23 15:53 16:23 16:53 17:23 17:53

Time (hour:minute)

CO

D (

mg

/L)

Page 22: Evaluation of Sensors and Analysers

Results for COD: Results for COD:

Trescon (WTW) Trescon (WTW) –– DynamicsDynamics

550

600

650

700

750

800

850

900

-50

0

50

100

150

200

250

300

350

400

450

500

550

11:45 12:15 12:45 13:15 13:45 14:15 14:45 15:15 15:45 16:15 16:45 17:15 17:45 18:15

Time (hour:minute)

CO

D (

mg

/L)

Reference TresCon WTW

Page 23: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Spectro::Lyser (S::CAN) Spectro::Lyser (S::CAN) –– AccuracyAccuracy

550

600

650

700

750

800

850

900

Spectrolyser SCAN Reference

-50

0

50

100

150

200

250

300

350

400

450

500

550

10:52 11:22 11:52 12:22 12:52 13:22 13:52 14:22 14:52 15:22 15:52 16:22 16:52 17:22

Time (hour:minute)

CO

D (

mg

/L)

Page 24: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Spectro::Lyser (S::CAN) Spectro::Lyser (S::CAN) –– DynamicsDynamics

550

600

650

700

750

800

850

900

SpectroLyser SCAN Reference

-50

0

50

100

150

200

250

300

350

400

450

500

09:00 09:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30

Time (hour:minute)

CO

D (

mg

/L)

Page 25: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Spectro::Lyser (S::CAN) Spectro::Lyser (S::CAN) –– LinearityLinearity

500

550

600

650

700

750

800

850

Spectrolyser SCAN Reference

-50

0

50

100

150

200

250

300

350

400

450

500

11:18 11:48 12:18 12:48 13:18 13:48 14:18 14:48 15:18

Time (hour:minute)

CO

D (

mg

/L)

Page 26: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Uvas (HachUvas (Hach--Lange) Lange) –– LinearityLinearity

550

600

650

700

750

800

850

900

Uvas LANGE Reference

-50

0

50

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300

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400

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550

11:43 12:13 12:43 13:13 13:43 14:13 14:43 15:13 15:43

Time (hour:minute)

CO

D (

mg

/L)

Page 27: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

All devices: table of main evaluation criteriaAll devices: table of main evaluation criteria

Trescon (WTW)Trescon (WTW)Carbovis Carbovis

(WTW)(WTW)

Uvas (HachUvas (Hach--

Lange)Lange)

Spectro::Lyser Spectro::Lyser

(S::CAN)(S::CAN)

Response time (minutes)Response time (minutes) 77 33 22 11

OffsetOffset 1010 9292 2525 99

Limit of detection (LOD)Limit of detection (LOD) 1313 00 1212 1111Limit of detection (LOD)Limit of detection (LOD) 1313 00 1212 1111

Bias at 20%Bias at 20%

(B20)(B20)1212 8181 --112112 --77

Bias at 20%Bias at 20%

(B80)(B80)2020 8787 --102102 2323

Smallest detectable change at 20%Smallest detectable change at 20%

(SDC20)(SDC20)22 104104 3434 7575

Smallest detectable change at 80%Smallest detectable change at 80%

(SDC80)(SDC80)1111 123123 3131 102102

mg

(Om

g(O

22)/

L)/

L

Page 28: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

All devices: comparison radar diagramAll devices: comparison radar diagram

-4

-2

0

2

4

6

8

Response time

OffsetSDC80

Trescon (WTW)

-10

-8

-6

-4

LOD

B20B80

SDC20

Carbovis (WTW)

Uvas (Hach-Lange)

Spectro::Lyser (S::CAN)

Page 29: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

All devices: preconisationsAll devices: preconisations

Trescon Trescon

(WTW)(WTW)

Carbovis Carbovis

(WTW)(WTW)

Uvas (HachUvas (Hach--

Lange)Lange)

Spectro::Lyser Spectro::Lyser

(S::CAN)(S::CAN)

Price (per unit)Price (per unit) 7 000 7 000 €€ 13 000 13 000 €€ 6 000 6 000 €€ 23 000 23 000 €€

�� Which sensor should you choose ?Which sensor should you choose ?�� Which sensor should you choose ?Which sensor should you choose ?

�� Choice depends on the requirements for the applicationChoice depends on the requirements for the application

�� What specifications are needed ?What specifications are needed ?

�� Tests have to be achieved on real industrial waste water Tests have to be achieved on real industrial waste water samples to complete the evaluationsamples to complete the evaluation

Page 30: Evaluation of Sensors and Analysers

OnOn--going & future workgoing & future work

Task 2.1.1 Task 2.1.1 -- EVALUATION OF SENSORS AND ANALYSERSEVALUATION OF SENSORS AND ANALYSERS

OnOn--going & future workgoing & future work

Page 31: Evaluation of Sensors and Analysers

OnOn--going an future workgoing an future work

�� OnOn--going work:going work:

�� Final interpretation of the results about CODFinal interpretation of the results about COD

�� Evaluation of Total N analyser and Ca and Pb sensorsEvaluation of Total N analyser and Ca and Pb sensors

�� Future work:Future work:�� Future work:Future work:

�� Evaluation of COD sensors on real industrial waste Evaluation of COD sensors on real industrial waste water sampleswater samples

Page 32: Evaluation of Sensors and Analysers

Thank you Thank you

for your attentionfor your attention

☺☺

Merci pour votre attentionMerci pour votre attention

Gracias por su atención Gracias por su atención

Danke für Ihre AufmerksamkeitDanke für Ihre Aufmerksamkeit

Grazie per la vostra attenzione Grazie per la vostra attenzione

Dank u voor uw aandachtDank u voor uw aandacht

Page 33: Evaluation of Sensors and Analysers

Early results for CODEarly results for COD

�� Issue: comparison of different physical quantities for CODIssue: comparison of different physical quantities for COD

�� Absorption: mAbsorption: m--11 �� Trescon SAC Module (WTW), UVAS (Lange)Trescon SAC Module (WTW), UVAS (Lange)

SensorSensor ComputerComputer

Absorption Absorption [m[m--11]]

COD COD [mgO[mgO22/L]/L]SampleSample

�� COD: mgOCOD: mgO22/L/L

Measurement of Measurement of absorptionabsorption

External offline conversion: External offline conversion: specific to each sensorspecific to each sensor

SensorSensor

Measurement and Measurement and internal online calculationinternal online calculation

COD COD [mgO[mgO22/L]/L]SampleSample

Page 34: Evaluation of Sensors and Analysers

Tasks / Deliverables and StatusTasks / Deliverables and Status�� Selection of sensors and definition of the test protocolSelection of sensors and definition of the test protocol

�� Internal report (2.1.1.1) finalizedInternal report (2.1.1.1) finalized

�� Evaluation of sensorsEvaluation of sensors�� Completed: COD analysers tests on synthetic samplesCompleted: COD analysers tests on synthetic samples

�� In progress: In progress: �� In progress: In progress: �� Completion of COD analysers tests on real industrial water samples Completion of COD analysers tests on real industrial water samples

(June 2010)(June 2010)

�� Total N analyser, Ca and Pb sensors evaluation (July 2010)Total N analyser, Ca and Pb sensors evaluation (July 2010)

�� Internal report (2.1.1.2) due month 28 (September 2010)Internal report (2.1.1.2) due month 28 (September 2010)

�� Interactions with other WPsInteractions with other WPs�� Samples received form ATM (food industry waste water)Samples received form ATM (food industry waste water)

Page 35: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Carbovis (WTW) Carbovis (WTW) –– LinearityLinearity

600

700

800

900

CO

D (

mg

/L)

Carbovis WTW Reference

0

100

200

300

400

500

11:13 11:43 12:13 12:43 13:13 13:43 14:13 14:43 15:13 15:43 16:13

Time (hour:minute)

CO

D (

mg

/L)

Page 36: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Uvas (HachUvas (Hach--Lange) Lange) –– AccuracyAccuracy

50

55

60

65

70

75

80

CO

D (

mg

/L)

Uvas LANGE Reference

0

5

10

15

20

25

30

35

40

45

11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30

Time (hour:minute)

CO

D (

mg

/L)

Page 37: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Uvas (HachUvas (Hach--Lange) Lange) –– DynamicsDynamics

600

700

800

900

1000

CO

D (

mg

/L)

Uvas LANGE Reference

0

100

200

300

400

500

600

12:02 12:32 13:02 13:32 14:02 14:32 15:02 15:32 16:02 16:32 17:02 17:32 18:02 18:32

Time (hour:minute)

CO

D (

mg

/L)

Page 38: Evaluation of Sensors and Analysers

Results for COD: Results for COD:

Trescon (WTW) Trescon (WTW) –– LinearityLinearity

600

700

800

900

TresCon WTW Reference

0

100

200

300

400

500

11:14 11:44 12:14 12:44 13:14 13:44 14:14 14:44 15:14

Time (hour:minute)

CO

D (

mg

/L)

Page 39: Evaluation of Sensors and Analysers

Results about COD:Results about COD:

Carbovis (WTW) Carbovis (WTW) –– AccuracyAccuracy

35

45

55

65

CO

D (

mg

/L)

Carbovis WTW Reference

-5

5

15

25

35

11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30

Time (hour:minute)

CO

D (

mg

/L)

Page 40: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Carbovis (WTW) Carbovis (WTW) –– DynamicsDynamics

550

650

750

850

950

Carbovis WTW Reference

-50

50

150

250

350

450

550

11:31 12:01 12:31 13:01 13:31 14:01 14:31 15:01 15:31 16:01 16:31 17:01 17:31 18:01

Time (hour:minute)

CO

D (

mg

/L)

Page 41: Evaluation of Sensors and Analysers

Results for COD: Results for COD:

Trescon (WTW) Trescon (WTW) –– AccuracyAccuracy

35

40

45

50

55

60TresCon WTW Reference

-10

-5

0

5

10

15

20

25

30

11:53 12:23 12:53 13:23 13:53 14:23 14:53 15:23 15:53 16:23 16:53 17:23 17:53

Time (hour:minute)

CO

D (

mg

/L)

Page 42: Evaluation of Sensors and Analysers

Results for COD: Results for COD:

Trescon (WTW) Trescon (WTW) –– DynamicsDynamics

600

700

800

900

Reference TresCon WTW

0

100

200

300

400

500

11:45 12:15 12:45 13:15 13:45 14:15 14:45 15:15 15:45 16:15 16:45 17:15 17:45 18:15

Time (hour:minute)

CO

D (

mg

/L)

Page 43: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Spectro::Lyser (S::CAN) Spectro::Lyser (S::CAN) –– AccuracyAccuracy

200

250

300

350

Spectrolyser SCAN Reference

-50

0

50

100

150

200

10:52 11:22 11:52 12:22 12:52 13:22 13:52 14:22 14:52 15:22 15:52 16:22 16:52 17:22

Time (hour:minute)

CO

D (

mg

/L)

Page 44: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Spectro::Lyser (S::CAN) Spectro::Lyser (S::CAN) –– DynamicsDynamics

600

700

800

900

SpectroLyser SCAN Reference

0

100

200

300

400

500

09:00 09:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30

Time (hour:minute)

CO

D (

mg

/L)

Page 45: Evaluation of Sensors and Analysers

Results for COD:Results for COD:

Spectro::Lyser (S::CAN) Spectro::Lyser (S::CAN) –– LinearityLinearity

600

700

800

900

Spectrolyser SCAN Reference

0

100

200

300

400

500

11:18 11:48 12:18 12:48 13:18 13:48 14:18 14:48 15:18

Time (hour:minute)

CO

D (

mg

/L)