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Sampling of Nutrients in the Environment a QA/QC perspective
Dan Wruck Supervisor, Nutrients & Environmental Waters Queensland Health Scientific Services Manilla, Philippines, October 2006
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Australia Brisbane Sydney Melbourne
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Queensland Health Scientific Services
National Research Centre for Environmental Toxicology (EnTox)
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South of the Great Divide Where?
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Nutrients Lab Leading Australian Lab - analysing approx 20,000 samples annually Accredited to ISO/IEC 17025 Samples sourced from: pristine freshwater water storages estuaries seawater effluent monitoring compliance monitoring
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Nutrients Lab Accredited Proficiency Testing Provider
Accredited to ILAC Guide 13:2000 based on ISO guide 43-1 and relevant elements of ISO/IEC 17025 Manages and Coordinates National Low Level Nutrient Collaborative Trials (NLLNCT) More than 60 Australian & overseas labs participate trials evaluate & provides feedback through Summary Reports, Workshops
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Nutrients Lab Certified Reference Material Producer
Accredited to ILAC Guide 12:2000 based on ISO guide 34:1996 (quality system guidelines for the production of reference materials) Certified Reference Materials in natural freshwaters and seawaters Suitable for: method development quality control samples
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Conductivity (µS/cm at 25oC)
pH Conductivity (µS/cm at 25oC) Turbidity (NTU) TSS (mg/L) 7.4 140 875 600 Hello… any crocs around???
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Certified Values and Ranges for Dawson River
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NLLNCT Round 9 Pristine Freshwater Site
Somerset Dam Potable water source for Brisbane population. Bloody good fishing spot Conductivity Turbidity Total Suspended Solids ( m S/cm ) NTU mg/L 300 5 6
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NLLNCT Round 9 Pristine Seawater
Pumicestone Passage Pristine estuary Can be good fishing
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Impacted seawater Prawn Farm 40,000 28 150 Conductivity Turbidity
Total Suspended Solids ( m S/cm ) NTU mg/L 40,000 28 150 Prawn Farm
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QHSS Nutrient’s Laboratory
Gary with 5 channel FIA automated analyser Tuyet preparing samples for Kjeldahl analysis
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Conceptual Model
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Sampling and Analysis Design Framework (1)
Problem/Question William Maher (1993) Cost Effectiveness Objectives Model ??????? Sampling Indicators Hypotheses QUALITY QA/QC Laboratory Measurement Interpretation
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Sampling and Analysis Design Framework (2)
William Maher (1993) Site selection Sampling Scheme frequency QUALITY QA/QC replication Field Collection Storage / transport Collection Device
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QA Requirements (1) contamination sources effecting nutrient samples
“May” QA Requirements (1) contamination sources effecting nutrient samples Filters Filtration Preservation Digestion Storage Sampling Chemistry Contamination Water Body Analytical Result Sample Containers Hygiene
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COMPARATIVE FINGER TEST AMMONIA
0.100 0.090 0.080 0.070 0.060 Concentration (mgN/L) 0.050 0.040 0.030 0.020 0.010 0.000 A B C D Control Participant
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COMPARATIVE FINGER TEST FRP
0.000 0.005 0.010 0.015 0.020 0.025 0.030 Concentration (mgP/L) Participant Control A B C D
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COMPARATIVE FINGER TEST OXN
0.000 0.005 0.010 0.015 0.020 0.025 0.030 0.035 0.040 Participant Concentration (mgN/L) Control A B C D
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QA Requirements How to effectively monitor QA for sampling
Some Examples Audit sample bottles before use field blanks - take through whole sampling process transport blank - background check control sites replicate samples
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WHY DO WE COLLECT SAMPLES?
In-situ Techniques or Field Instruments Not Robust site access & location equipment fouling Quality assurance difficult to incorporate Inadequate detection Limits Matrix correction
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Monitoring Techniques
ü Key Processes – Water quality – Phytoplankton bioassays – Sediment nutrient fluxes ü Human Impacts Sewage plume mapping N signatures of N signatures of mangroves ü Critical Habitat – Seagrass distribution and depth range
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PRESERVATION & STORAGE
NO universal procedure will satisfy all requirements WHY All water bodies contain particulate matter the nature of the particulate matter determines how a sample behaves Any procedure WILL require validation
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Some factors which may effect the recovery of nutrients from a sample
Bioassimilation Desorption from particulate Volatilisation Nutrient Sample Adsorption onto container walls Absorption by particulates Cell destruction with freezing Desorption from container walls Contamination
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Framework for Collecting Nutrient Samples
TN TKN TP Unfiltered Sample -18°C HDPE containers Water Body NH3 NO2 NO3 TDN TDP 0.45µm cellulose acetate Filtered Sample
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Sample Storage
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Some Common Sampling Devices & Situations
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“GRAB” - Stream Sample into the flow Face neck of bottle down Invert bottle at depth of 150 mm
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Do not disturb bottom sediments
“GRAB” - Pond Do not disturb bottom sediments Beaker with telescopic pole for “inspector gadget” situations
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“GRAB” - Sample away from boat slick
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Automatic Samplers Install in secure environment
Sampling MUST take account of preservation requirements
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Multi-parameter Probe
pH conductivity DO salinity temperature
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Van Veen Depth Sampling Van Dorn
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Vacum Filtration Metals Chlorophyll
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Sampling Techniques The bucket MUST be inserted upside down and NOT inverted until below the surface of the water
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Sampling Techniques Total Nutrients
The water sample MUST be dispensed into the container ASAP after collection to minimise the effects of sedimentation occurring
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Sampling Techniques The bucket MUST be inserted upside down and NOT inverted until below the surface of the water
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Sampling Techniques Total Nutrients
The water sample MUST be dispensed into the container ASAP after collection to minimise the effects of sedimentation occurring
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Sampling Techniques Filtration occurs within a “closed system” minimising the risk of contamination
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FILTRATION ??? WHY
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Frozen Kept on ice Frozen Kept on ice
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PRESSURE - PROCEDURE ROBUST PRACTICAL SMALL VOLUMES/BOTTLES
MINIMAL CONTAMINATION (procedure is performed in a “closed environment”) REPRODUCIBLE HIGH ACCEPTANCE AMONG FIELD OFFICERS MEETS REQUIREMENTS OF AS/NZS & ISO :2003)
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??? FILTRATION WHY Impossible to model
Impact assessments - meaningless Potential high costs incorrect decisions on treatment processes legal implications Professional reputation
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Sampling Scenarios - Ammonia
AS/NZS :1998 ISO :2003 Standard Methods 20th Edition Refrigerate (6hrs) Filter on site then acidify to pH <2 with sulfuric acid and refrigerate (21 days) Unfiltered sample to be refrigerated (24hrs) Filter on site and refrigerate (24 hrs) Unfiltered sample to be acidified to pH <2 and refrigerate (1 month) Filter on site and freeze (1 month) Unfiltered sample to be frozen (1 month)
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Sampling Scenarios - Nitrate
AS/NZS :1998 ISO :2003 Standard Methods 20th Edition Refrigerate (24 hrs) Unfiltered sample to be refrigerated (24hrs) Unfiltered sample to be refrigerated (48hrs) Unfiltered sample to be acidified to pH <2 and refrigerate (1 month) Filter on site and freeze (1 month) Unfiltered sample to be frozen (1 month)
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Sampling Scenarios – Total Nitrogen
AS/NZS :1998 ISO :2003 Standard Methods 20th Edition Refrigerate (24hrs) Acidify to pH <2 with sulphuric acid (1 month) Not discussed Freeze (1 month)
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Sampling Scenarios – Total Kjeldahl Nitrogen
AS/NZS :1998 ISO :2003 Standard Methods 20th Edition Refrigerate (24hrs) Acidify to pH <2 with sulphuric acid and refrigerate (24 hrs) Analyse immediately Acidify to pH <2 with sulphuric acid and refrigerate Freeze (1 month)
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Sampling Scenarios – Filtered Reactive Phosphorus
AS/NZS :1998 ISO :2003 Standard Methods 20th Edition Filter on site and refrigerate (24 hrs) Filter on site and refrigerate (1 month) Filter on site and freeze (not specified) Filter on site and freeze (1 month)
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Sampling Scenarios – Total Phosphorus
AS/NZS :1998 ISO :2003 Standard Methods 20th Edition Refrigerate (1 month) Acidify to pH <2 with sulphuric acid and refrigerate (1 month) Acidify to pH <2 with sulphuric acid and refrigerate (not specified) Freeze (1 month) Freeze (not specified)
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Sampling Scenarios – Silica
AS/NZS :1998 ISO :2003 Standard Methods 20th Edition Refrigerate (24 hours) Filter on site and refrigerate (1 month) Collect in plastic containers (not specified) DO NOT FREEZE SAMPLES DO NOT ACIDIFY SAMPLES
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Farmer Danny
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