PD ISO/TR 18105:2014
Current
The latest, up-to-date edition.
Soil quality. Detection of water soluble chromium(VI) using a ready-to-use test-kit method
Hardcopy , PDF
English
30-09-2014
Foreword
Introduction
1 Scope
2 References
3 Terms and definitions
4 Principle
5 Reagents
6 Interferences
7 Apparatus
8 Procedure
9 Quality assurance (QA) and quality control (QC)
10 Test report
Annex A (informative) - Extraction of Cr(VI) from
soil CRMs
Annex B (informative) - Comparison of Cr(VI) results
obtained with commercially available
test-kits
Annex C (informative) - Simulation of mapping
distributions of Cr(VI) contaminating
potential land
Bibliography
Specifies the procedure to screen soil samples to detect Cr(VI) using test-kits based on water extraction of Cr(VI) in soil.
Committee |
EH/4
|
DocumentType |
Standard
|
Pages |
26
|
PublisherName |
British Standards Institution
|
Status |
Current
|
This Technical Report describes the procedure to screen soil samples to detect Cr(VI) using test-kits based on water extraction of Cr(VI) in soil. The test-kit approach in this method is designed to quickly screen soil samples using calibration to indicate the concentration level. A batch test at a liquid to solid ratio of 10l/kg, designated by ISO/TS21268-2, has been used in Japan for over 30years to evaluate the risk of Cr(VI) contamination in soil. The Cr(VI) detection by a ready-to-use test-kit method follows ISO/TS21268-2.
This screening technique is applicable in laboratories but can also be applied for site screening in the field. The standard system detection covers the range mg/kg to % for Cr(VI).
This method is expected as a screening technique because of the significant colour change given by 1,5-diphenylcarbazide in the existence of Cr(VI). The method may be especially useful in quickly detecting Cr(VI) where a site is assumed to have no Cr(VI) contamination. As with other screening techniques, it is advisable to confirm a certain percentage of both positive and negative test results in another technique, especially when the detected level is near or above a regulatory action limit or when the presence of background or interfering materials is suspected.
Basically, laboratory analysis requires longer time and higher costs than those of test-kit detection. If the same survey time and the costs are allowed with test-kit screening work and conventional investigation methods including laboratory analysis, the former way can work on more inspection spots than the latter. However, test-kit detection should carefully be adopted for site investigation because the recovery of Cr(VI) from soil into water dependent on soil matrices changes the performance of test-kit detection.
Standards | Relationship |
ISO/TR 18105:2014 | Identical |
ISO 12404:2011 | Soil quality Guidance on the selection and application of screening methods |
ISO 11074:2015 | Soil quality — Vocabulary |
ISO 11083:1994 | Water quality — Determination of chromium(VI) — Spectrometric method using 1,5-diphenylcarbazide |
ISO 11464:2006 | Soil quality Pretreatment of samples for physico-chemical analysis |
ISO 17381:2003 | Water quality — Selection and application of ready-to-use test kit methods in water analysis |
ISO 15192:2010 | Soil quality Determination of chromium(VI) in solid material by alkaline digestion and ion chromatography with spectrophotometric detection |
ISO 10381-5:2005 | Soil quality Sampling Part 5: Guidance on the procedure for the investigation of urban and industrial sites with regard to soil contamination |
ISO/TS 21268-2:2007 | Soil quality Leaching procedures for subsequent chemical and ecotoxicological testing of soil and soil materials Part 2: Batch test using a liquid to solid ratio of 10 l/kg dry matter |
ISO/IEC Guide 98-3:2008 | Uncertainty of measurement — Part 3: Guide to the expression of uncertainty in measurement (GUM:1995) |
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