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Method Summary

Method Source U.S. EPA Office of Ground Water and Drinking Water/Technical Support Center
Method Number300.1
Revision InformationRevision 1.0, 1997
Method NameDescriptive Name: Anions in Water by IC

Official Name: Determination of Inorganic Anions in Drinking Water by Ion Chromatography

MediaMedia: WATER
SubcategoryInorganic
Citation Methods for the Determination of Organic and Inorganic Compounds in Drinking Water, Volume 1 (EPA/815-R-00-014)
Method Download Adobe Acrobat (pdf) icon Download full method now (PDF file)
Summary of MethodThe concentration of anions in a 10-uL (for common anions) or 50-uL (for disinfection byproducts) sample are determined using an ion chromatography (IC) system equipped with a conductivity detector (CD).
Scope and ApplicationThis method determines certain inorganic anions (both common and disinfection byproducts) in reagent water, surface water, ground water, and finished drinking water. Methyl fluoroacetate is measured using the fluoride ion.
Applicable Concentration RangeLinear calibration range (LCR) should be established by the analyst.
Interferences

(A) Co-elution: Modifying the eluent with organic solvents, changing the detection system, or pretreating the sample can reduce co-elution.

(B) Pretreatment cartridges: Use of a pretreatment cartridge can lead to artifacts in the sample; use with caution.

(C) Turbidity: Remove turbidity using filtration.

(D) Weakly-bound anions: Anions which are weakly retained by the column interfere with fluoride determination at > 1.5 mg/L.

(E) Carryover effects: There are some compounds in ozonated and chlorine dioxide matrices which will elute well after sulfate. These may carry over in later runs.

(F) Chlorine dioxide. Chlorine dioxide can form chlorite. Remove chlorine dioxide by purging the sample with inert gas.

QC RequirementsInitial demonstration of laboratory performance and subsequent analysis in each analysis batch of a Laboratory Reagent Blank (LRB), Laboratory Fortified Blank (LFB), Instrument Performance Check Standard (IPC), Calibration Check Standards, Laboratory Fortified Sample Matrices (LFM), and either Field, Laboratory or LFM duplicate sample analyses.
Sample HandlingSamples should be collected in plastic or glass bottles that have been thoroughly cleaned and rinsed with reagent water. Sample bottles used for chlorite analysis must be opaque or amber. Preserve samples to be analyzed for bromate, chlorate, and chlorite with 50 mg/L of ethylene diamine (EDA). Samples analyzed for nitrate-N, nitrite-N, ortho-Phosphate-P, sulfate, and chlorite should be stored at < 4oC. When collecting a field sample from a treatment plant employing chlorine dioxide, the field sample must be sparged with an inert gas (helium, argon, nitrogen) prior to the addition of EDA preservative.
Max Holding Time28 days for bromide, chloride, fluoride, bromate, and chlorate
14 days for chlorite
48 hours for Nitrate-N, Nitrite-N, and ortho-Phosphate-P
Relative Cost/Effort$51 to $200
Sample Prep Method(s) 
 

Method Anions in Water by IC has 12 analytes associated with it.

Analyte


Detection
Level


Bias Precision Pct False
Positive
Methyl fluoroacetate
(453-18-9)
N/AN/AN/A 
Nitrate/nitrite
(E-10128)
N/AN/AN/A 
Sulfate
(14808-79-8)
.019 mg/L89.5 % Rec (SL).11 % RSD (SL)50 mg/L
Phosphate
(14265-44-2)
.019 mg/L96.2 % Rec (SL).14 % RSD (SL)10 mg/L
Nitrate
(14797-55-8)
.008 mg/L95 % Rec (SL).14 % RSD (SL)10 mg/L
Bromide
(24959-67-9)
.014 mg/L96.1 % Rec (SL).92 % RSD (SL).5 mg/L
Nitrite
(14797-65-0)
.001 mg/L85.1 % Rec (SL).51 % RSD (SL)1 mg/L
Chloride
(16887-00-6)
.004 mg/L98.7 % Rec (SL).1 % RSD (SL)50 mg/L
Fluoride
(16984-48-8)
.009 mg/L89.7 % Rec (SL)1.18 % RSD (SL)2 mg/L
Chlorate
(14866-68-3)
1.31 ug/L98.3 % Rec (SL).82 % RSD (SL)100 ug/L
Chlorite
(14998-27-7)
.89 ug/L96.2 % Rec (SL).99 % RSD (SL)100 ug/L
Bromate
(15541-45-4)
1.44 ug/L101 % Rec (SL)8.86 % RSD (SL)5 ug/L
export_analytes
Precision Descriptor NotesPrecision and accuracy values were calculated using data from nine replicate analyses of a fortified reagent water sample. Additional precision and accuracy data, including data from different matrices, are available in the method.
Detection Level NoteMDL procedure is equivalent to the procedure at 40 CFR part 136, Appendix B. MDLs were determined using the standard deviation of 7 replicate analyses of an analyte-fortified reagent water sample multiplied by the t-value for 6 degrees of freedom at the 99% confidence level (3.14). Detailed instructions for how MDLs are determined are found in Section 9.2.4 of the Method.
 
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