# BS ISO 13292-2006 (2008)

BRITISH STANDARD BS ISO 132922006 Copper, lead, zinc and nickel concentrates Experimental s for checking the bias of sampling ICS 73.060.99 BS ISO 132922006 This British Standard was published under the authority of the Standards Policy and Strategy Committee on 30 April 2008 BSI 2008 ISBN 978 0 580 55515 2 National foreword This British Standard is the UK implementation of ISO 132922006. The UK participation in its preparation was entrusted to Technical Committee NFE/36, Copper, lead and zinc ores and concentrates. A list of organizations represented on this committee can be obtained on request to its secretary. This publication does not purport to include all the necessary provisions of a contract. Users are responsible for its correct application. Compliance with a British Standard cannot confer immunity from legal obligations. Amendments/corrigenda issued since publication Date Comments Reference number ISO 132922006EINTERNATIONAL STANDARD ISO 13292 Second edition 2006-03-15 Copper, lead, zinc and nickel concentrates Experimental s for checking the bias of sampling Concentrs de cuivre, de plomb, de zinc et de nickel Mthodes exprimentales de contrle de lerreur systmatique dchantillonnage BS ISO 132922006ii iii Sommaire Page Foreword iv 1 Scope . 1 2 Normative references . 1 3 General requirements and recommendations . 1 4 Sampling and sample processing s 2 4.1 Sampling 2 4.1.1 General. 2 4.1.2 Checking bias in mechanical sampling 3 4.1.3 Checking difference between sampling at different locations 3 4.2 Sample processing and analysis 3 5 Analysis of experimental data . 3 5.1 Statistical basis. 3 5.2 Determination of the mean difference and its standard deviation 4 5.3 Determination of the required number of data sets 4 5.4 Statistical test 6 Annex A inative Numerical examples of determining the bias of sampling 7 Bibliography . 11 BS ISO 132922006iv Foreword ISO the International Organization for Standardization is a worldwide federation of national standards bodies ISO member bodies. The work of preparing International Standards is normally carried out through ISO technical committees. Each member body interested in a subject for which a technical committee has been established has the right to be represented on that committee. International organizations, governmental and non-governmental, in liaison with ISO, also take part in the work. ISO collaborates closely with the International Electrotechnical Commission IEC on all matters of electrotechnical standardization. International Standards are drafted in accordance with the rules given in the ISO/IEC Directives, Part 2. The main task of technical committees is to prepare International Standards. Draft International Standards adopted by the technical committees are circulated to the member bodies for voting. Publication as an International Standard requires approval by at least 75 of the member bodies casting a vote. Attention is drawn to the possibility that some of the elements of this document may be the subject of patent rights. ISO shall not be held responsible for identifying any or all such patent rights. ISO 13292 was prepared by Technical Committee ISO/TC 183, Copper, lead, zinc and nickel ores and concentrates. This second edition cancels and replaces the first edition ISO 132921997, which has been technically revised. BS ISO 132922006 1 Copper, lead, zinc and nickel concentrates Experimental s for checking the bias of sampling WARNING This International Standard may involve hazardous materials, operations and equipment. It is the responsibility of the user of this International Standard to establish appropriate health and safety practices and determine the applicability of regulatory limitations prior to use. 1 Scope This International Standard specifies s for checking whether there is any bias in the sampling of copper, lead, zinc and nickel concentrates, where the sampling is carried out in accordance with the s specified in ISO 12743. These s can also be used for comparing alternative sampling regimes, checking whether there is any bias in sample processing and for checking possible significant differences in sampling at different places, e.g. at loading and discharge points, or the analysis of exchange samples. Numerical examples are given in Annex A. 2 Normative references The following referenced documents are indispensable for the application of this document. For dated references, only the edition cited applies. For undated references, the latest edition of the referenced document including any amendments applies. ISO 12743, Copper, lead, zinc and nickel concentrates Sampling procedures for determination of metal and moisture content 3 General requirements and recommendations The procedures specified in this International Standard are applicable to paired data only. The results obtained from the to be checked for bias referred to as B are compared with the results for a reference referred to as A, which is considered to produce unbiased results from technical and empirical viewpoints. If there is no significant difference between the results obtained using B and A, then B may be adopted as a routine . While the procedures specified in Clause 5 are principally designed for checking bias against a reference , separate measurements of quality characteristics, e.g. using different sampling regimes, sampling at loading A and discharge B, or analyses of exchange samples, may also be compared to check whether there is a statistically significant difference between the results. Mechanical sampling systems, or manual sampling s, are tested for bias by comparing the test results for final system or manually collected samples B with the test results for reference increments collected from a stopped conveyor belt A. Analytical s or test procedures are checked against certified reference materials. The standard of taking reference increments from a stopped conveyor belt presents operational difficulties, even if the handling system is capable of being restarted with a fully loaded belt. The main problems are losses in production tonnage and the difficulty experienced in the sequence of starting the handling system. During a ships loading or unloading operation, this can cause delays in the turnaround time of the ship. BS ISO 1329220062 Alternative reference s, which are also expensive, divert the ore flow onto a transfer conveyor belt to produce a material bed section identical to that from the main belt on which the mechanical primary sampler B is installed. Stopped-belt sampling is then carried out on the transfer belt to collect reference increments A. The transfer conveyor belt should be of sufficient length to allow the establishment of a material bed section that is not influenced by any longitudinal segregation introduced by the diversion plate. The primary sampler and the point of diversion to the transfer belt should be as close as possible. Sampling and sample processing procedures are more prone to bias than analytical techniques and test s. As system samples and reference increments are progressively reduced in mass and particle size, lot samples, subsamples and test samples become increasingly vulnerable to sample loss and contamination. Therefore, systematic errors occur more frequently during sample processing than during sampling, so different stages of the sample processing procedure may require testing for bias. Where testing for bias, the number of paired sets of measurements data sets shall be not less than 20. The number of data sets required depends on the variance of the differences between the two s and on the value of the bias, , to be detected. Any chemical or physical characteristic may be used to check whether any bias is present, e.g. copper, lead, zinc, nickel or moisture content. Bias may not always be present for just one parameter. Therefore, several parameters to reduce the effect of short-term variations in quality, preferably including all those that are likely to be of interest, should be examined to determine whether bias exists. Characteristics to be tested for the presence of bias need to be decided before the test work begins. If the purpose of the bias check is to assess the perance of the sampling equipment, it is recommended that increments for A and B be taken from closely adjacent portions of the concentrate to reduce the effect of short-term variations in quality, and that sample processing and analysis be carried out on each increment individually. This is likely to reduce the number of data sets required to detect a given bias in the sampling equipment. On the other hand, if the purpose of the bias check is to determine whether the selected sampling regime is biased, e.g. due to the presence of periodic variations in quality, it is recommended that increments for A and B be taken completely independently. Even after a bias check has been conducted, further checks should be carried out at regular intervals. Bias checks should also be carried out when sampling equipment is changed. 4 Sampling and sample processing s 4.1 Sampling 4.1.1 General The to be checked B shall be compared with a designated reference A using the same type of concentrate. A may also be an alternative that is being compared with B. As specified in Clause 3, at least 20 pairs of samples shall be collected following the procedures detailed in ISO 12743. BS ISO 132922006 3 4.1.2 Checking bias in mechanical sampling A Reference increments are taken by stopped-belt sampling. B System increments are taken from a moving stream with a mechanical sampler. 4.1.3 Checking difference between sampling at different locations A Increments are taken from a moving stream with a mechanical sampler at a loading location. B Increments are taken from a moving stream with a mechanical sampler at a discharge location. 4.2 Sample processing and analysis The procedure for constituting pairs of samples and carrying out the subsequent sample processing and analysis shall be as follows. a Constitute two samples sample A and sample B, consisting of one or a number of individual increments obtained in accordance with A and B. b Subject sample A and sample B to similar sample processing and analysis procedures, as specified in ISO 12743 and other relevant International Standards, to obtain sets of measurements for the characteristics of interest. It is recommended that analyses of paired samples be carried out under repeatability conditions, to decrease the analytical variance. 5 Analysis of experimental data 5.1 Statistical basis It is helpful at this point to review the definitions of Type I and Type II risks in bias testing. Consider the null hypothesis, H 0 , that there is no positive or negative bias in B compared with A. The alternative hypothesis, H 1 , is that there is either positive or negative bias. A Type I error occurs if H 0is rejected on the basis of the sample data falling into the critical region of a statistical test when, in reality, H 0is true. A Type II error occurs if H 0is accepted on the basis of the statistical test on the sample data when, in reality, H 1is true. In this International Standard, the statistical test for accepting H 0is that the absolute value of the difference between the mean of the quality characteristics for the reference or alternative set of increments A and the mean for the corresponding set of system increments B is smaller than a specified bias detection limit, BDL. A bias can be either positive or negative, so for a positive bias BAB D L xx 1 while for a negative bias BAB D L xx 2 where x A and x B are the means for the reference or alternative set of increments A and the system set of increments B, respectively. The bias detection limit is defined as the minimum bias that can be detected at the 95 confidence level using the data available. It is calculated using the described in 5.3. BS ISO 1329220064 By convention, a symmetrical, two-sided 5 probability 0,05 is assigned to the risk Type I of rejecting the null hypothesis, H 0 , when in fact it is true see 1 and 2 in the Bibliography. In addition, an asymmetrical 10 probability 0,10 is assigned to the risk of accepting the null hypothesis, H 0 , when in fact it is not true. Thus, sufficient data sets shall be collected to ensure that there is a small risk 0,05 of concluding that there is a statistical difference between A and B when none exists Type I risk, and a small risk 0,10 of concluding that there is no statistical difference when a bias is present Type II risk. A Students t-test two-sided shall then be applied at the 5 level of significance. If the result is significant, it is concluded that a bias exists. However, if the result is not significant, it is concluded that no bias as large as exists. 5.2 Determination of the mean difference and its standard deviation Determine the standard deviation of the differences between A and B using the following procedure. a Denote individual measurements for the ith sample pair using A and B as x A iand x B i , respectively. b Calculate the difference, d i, between x Biand x Ai , i.e. d i x B i- x A i 3 where i 1, 2, , k k is the the number of paired sets of measurements. c Calculate the mean, , d of the differences using the following equation A k i i d dxx k 1 B 4 d Calculate the sum of the squares, SS d , and the standard deviation, s d , of the difference using the following equations, where summations are over i 1,2,., k 2 SS ii dd k 2 d 15 SS 1 s k d d6 5.3 Determination of the required number of data sets a Specify the magnitude of the bias or difference, , to be detected. b Calculate the bias detection limit for the combined risk of Type I and Type II errors using the following equation ;kk s tt k d 0,05 1 0,10; 1 BDL 7 BS ISO 132922006 5 where t 0,05;k 1and t 0,10;k 1are the tabulated Students t-values for k 1 degrees of freedom corresponding to 0,05 and 0,10 as given in Table 1. The bias detection limit, BDL, is the minimum bias that can be detected using the data available. c If BDL u , the number of data sets is sufficient and the statistical test in 5.4 can be applied. d If BDL , calculate the standardized difference, D, and the required number of data sets, n r , corresponding to th