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Water Quality Monitoring Report - Noosa Civic - November 2009-2010 - Eenie Creek Rd NOOSAVILLE · 132002.220285
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Page 7of8
Work Order EB1003890
Client DUKE ENVIRONMENTAL
Project DE0923
Reactive Phosphorus as P-By Discrete EK071G WATER APHA 21st ed., 4500-P F Ammonium molybdate and potassium antimonyl tartrate reacts in acid medium with
Analyser othophosphate to form a heteropoly acid -phosphomolybdic acid - which is reduced to intensely coloured
molybdenum blue by ascorbic acid. Quantification is by Discrete Analyser. This method is compliant with NEPM
(1999) Schedule B(3) (Appdx. 2)
Dissolved Organic Carbon EP002 WATER APHA 21st ed., 5310 B. This method is compliant with NEPM (1999) Schedule B(3) (Appdx. 2)
TPH - Semivolatile Fraction EP071 WATER USEPA SW 846 - 8015A The sample extract is analysed by Capillary GC/FID and quantification is by comparison
against an established 5 point calibration curve of n-Alkane standards. This method is compliant with NEPM
(1999) Schedule B(3) (Appdx. 2)
TPH Volatiles/BTEX EP080 WATER USEPA SW 846 - 8260B Water samples are directly purged prior to analysis by Capillary GC/MS and
quantification is by comparison against an established 5 point calibration curve. This method is compliant with
NEPM (1999) Schedule B(3) (Appdx. 2)
TKN/TP Digestion EK0611EK067 WATER APHA 21st ed., 4500 Norg - D; APHA 21st ed., 4500 P - H. This method is compliant with NEPM (1999) Schedule
B(3) (Appdx. 2)
USEPA SW 846 - 35108 500 mL to 1L of sample is transferred to a separatory funnel and serially extracted three
times using 60mL DCM for each extract. The resultant extracts are combined, dehydrated and concentrated for
analysis. This method is compliant with NEPM (1999) Schedule B(3) (Appdx. 2). ALS default excludes sediment
which may be resident in the container _
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