Proficiency Test SYKE 2/2013
|
|
|
- Heli Kouki
- 9 vuotta sitten
- Katselukertoja:
Transkriptio
1 REPORTS OF FINNISH ENVIRONMENT INSTITUTE 13 Proficiency Test SYKE 2/13 Chlorophyll a, colour, conductivity, nutrients, ph and turbidity in natural waters Kaija Korhonen-Ylönen, Teemu Näykki, Mirja Leivuori, Keijo Tervonen, Sari Lanteri and Markku Ilmakunnas Finnish Environment Institute
2
3 SUOMEN YMPÄRISTÖKESKUKSEN RAPORTTEJA 13 Proficiency Test SYKE 2/13 Chlorophyll a, colour, conductivity, nutrients, ph and turbidity in natural waters Kaija Korhonen-Ylönen, Teemu Näykki, Mirja Leivuori, Keijo Tervonen, Sari Lanteri and Markku Ilmakunnas SYKE Helsinki 13 Suomen ympäristökeskus
4 REPORTS OF FINNISH ENVIRONMENT INSTITUTE 13 Finnish Environment Institute SYKE The proficiency test provider: Proftest SYKE, Finnish Environment Institute (SYKE), Laboratory Centre Hakuninmaantie 6, 004 Helsinki Publication is available only on the internet : / helda.helsinki.fi/syke ISBN (PDF) ISSN (Online)
5 CONTENT 3 ALKUSANAT/PREFACE 4 1 INTRODUCTION 2 ORGANIZING THE PROFICIENCY TEST 2.1 Responsibilities 2.2 Participants 2.3 Samples and delivery 2.4 Homogeneity and stability studies 6 2. Feedback from the pro ciency test Processing of the data Pretesting of the data Assigned value Standard deviation for pro ciency assessment and z score 8 3 RESULTS AND CONCLUSIONS Results Analytical methods and status to the results Uncertainties of the results 11 4 EVALUATION OF PERFORMANCE 12 SUMMARY 13 6 YHTEENVETO 14 REFERENCES 14 APPENDICES Appendix 1 Participants Appendix 2 Preparation of the samples 16 Appendix 3 Testing of homogeneity 18 Appendix 4 Testing of stability 19 Appendix Feedback from the pro ciency test Appendix 6 Evaluation of the assigned values 21 Appendix 7 Terms in the result tables 23 Appendix 8 Results of each participant 24 Appendix 9 Results and their uncertainties Appendix Summary of the z scores 1 Appendix 11.1 Analytical methods 3 Appendix 11.2 Results grouped according to the measurement methods 4 Appendix 12 Examples of the reported measurement uncertainties 6 DOCUMENTATION PAGE 69 KUVAILULEHTI 70 PRESENTATIONS BLAD 71
6 ALKUSANAT 4 Suomen ympäristökeskus (SYKE) on toiminut ympäristöalan kansallisena vertailulaboratoriona vuodesta 01 lähtien. Toiminta perustuu ympäristöministeriön määräykseen, mikä on annettu ympäristönsuojelulain (86/00) nojalla. Vertailulaboratorion tarjoamista palveluista yksi tärkeimmistä on pätevyyskokeiden ja muiden vertailumittausten järjestäminen. SYKEn laboratoriot on FINAS-akkreditointipalvelun akkreditoima testauslaboratorio T003 ja kalibrointilaboratorio K04 (SFS-EN ISO/IEC 1702) sekä vertailumittausten järjestäjä Pro!est SYKE PT01 (SFS-EN ISO/IEC 17043, www. nas. ). Tämä pätevyyskoe on toteutettu SYKEn vertailulaboratorion pätevyysalueella ja se antaa tietoa osallistujien pätevyyden lisäksi tulosten vertailukelpoisuudesta myös yleisemmällä tasolla. Pätevyyskokeen onnistumisen edellytys on järjestäjän ja osallistujien välinen luottamuksellinen yhteistyö. Parhaat kiitokset yhteistyöstä kaikille osallistujille! PREFACE Finnish Environment Institute (SYKE) is appointed National Reference Laboratory in the environmental sector by the Ministry of the Environment according to section 24 of the Environment Protection Act (86/00) since 01. "e duties of the reference laboratory service include providing pro ciency tests and other interlaboratory comparisons for analytical laboratories and other producers of environmental information. SYKE laboratories has been accredited by the Finnish Accreditation service as the testing laboratory T003 and the calibration laboratory K04 (EN ISO/IEC 1702) and as the pro ciency testing provider Pro!est SYKE PT01 (EN ISO/IEC 17043, www. nas. ). "is pro ciency test has been carried out under the scope of the SYKE reference laboratory and it provides information about performance of the participants as well as comparability of the results at a more general level. "e success of the pro ciency test requires con dential co-operation between the provider and participants. "ank you for your co-operation, Helsingissä 12 kesäkuuta 13 / Helsinki 12 June 13 Laboratorionjohtaja / Chief of Laboratory
7 1 Introduction Pro est SYKE carried out the pro!ciency test (PT) for analysis of a chlorophyll, colour, conductivity, nutrients (ammonium nitrogen, nitrate+nitrite nitrogen, total nitrogen, phosphate phosphorus, total phosphorus), ph and turbidity in surface and coastal waters in February 13. A total of 44 laboratories participated in the PT. In the PT the results of Finnish laboratories providing environmental data for Finnish environmental authorities were evaluated. Additionally, other water and environmental laboratories were welcomed in the pro!ciency test. "e test was carried out in accordance with the international guidelines, ISO/IEC [1], ISO 1328 [2] and IUPAC Technical Report [3]. "e SYKE laboratory has been accredited by the Finnish Accreditation Service as a pro!ciency testing provider (PT01, ISO/IEC 17043, SYKE is the accredited pro!ciency test provider on the!eld of the present test. 2 Organizing the pro ciency test 2.1 Responsibilities Organizing laboratory: Pro est SYKE, Finnish Environment Institute (SYKE), Laboratory Centre, Hakuninmaantie 6, 004 Helsinki, Finland, Phone: +38 6#123, Fax: "e responsibilities in organizing the pro!ciency test were as follows: Kaija Korhonen-Ylönen, coordinator Mirja Leivuori, substitute of coordinator Keijo Tervonen, technical assistant Sari Lanteri, technical assistant Ritva Väisänen, technical assistant Markku Ilmakunnas, technical assistant and lay-out of the report "e analytical expert for all measurements was Teemu Näykki (SYKE). 2.2 Participants In total, 44 laboratories from Finland, Denmark, Estonia, Georgia, Kyrgyztan, Norway and Sweden participated in the PT (Appendix 1). One laboratory reported two results measured with two di$erent methods. 26 of the Finnish participating laboratories provide data for use of the Finnish environmental authorities. About 69 % of the participating laboratories used accredited analytical methods for at least a part of the measurements. "e organizing laboratory (SYKE) has the code 12 in the result tables. 2.3 Samples and delivery "e arti!cial samples A1H, A1J, A1N and A1P were prepared by diluting from the NIST traceable certi!ed reference materials produced by Merck KGaA or by AccuStandard, Inc. NIST traceable certi!cated reference materials were not available for a chlorophyll, turbidity and colour determination. "e arti!cial sample A1K for a chlorophyll determination was prepared using green pigment (Sigma-Aldrich) by dissolving the weighted pigment in ethanol. "e arti!cial sample A1S for turbidity determination was prepared by diluting Hach Formatzin Turbidity Standard produced by Hach Company. "e arti!cial sample A1V for colour measurement was prepared according to the standard EN ISO 7887 using potassium hexachloroplatinate produced by Sigma-Aldrich and cobalt chloride hexahydrate produced by Merck KGaA. "e preparation of
8 6 the samples is presented in more detail in Appendix 2. e coastal water samples B2H, B2N, B2P and B2S were collected o! shore Helsinki the Gulf of Finland. e natural water samples N3H, N3N, N3P and N3S were from the River Ilolanjoki, the southern Finland. e purity of the laboratory and the used sample vessels was checked. According to the test the all used vessels ful"lled the purity requirements. e samples were delivered 12 February 13. To Kyrgyzstan the samples were sent a week earlier using special transport services. Chlorophyll a, conductivity, colour, turbidity, ph, N NH4, N NO2+NO3 and P PO4 were requested to be measured 14 February 13. N tot and P tot were requested to be analysed by 22 February 13. All results were requested to be reported by 2 February 13 and all participants reported their results on time. 2.4 Homogeneity an stability studies e homogeneity of the coastal and river water samples was studied by measuring N NH4, N tot, P tot and turbidity. According to the homogeneity test results the samples were considered to be homogenous. More detailed information of homogeneity studies is shown in Appendix 3. e homogeneity tests showed that the preparation of coastal and river water samples for a chlorophyll measurement was unsuccessful and so these samples were not delivered to the participants. e stability of the samples was carried out by measuring a chlorophyll, N NH4, ph and P Po4 from the samples, which were stored at the room temperature during one day. e measured values were checked against the results of the samples stored in cool. According to the test the concentration of N NH4 in the sample A1N could decrease, if the the samples warmed during the distribution. is was taken into account in performance evaluation (Chapter 4). 2. Feedback from the pro ciency test e feedbacks from the pro"ciency test are shown in Appendix. e comments from the participants mainly dealt with their reporting errors with the samples. e comments from the provider are mainly focused to the lacking conversancy to the given information with the samples. 2.6 Processing of the data Pretesting of the data Before the statistical treatment, the data was tested according to the Kolmogorov-Smirnov normality test and the possible extreme values were rejected as the outliers according to the Hampel test (H in the results sheets). Also before the robust calculation some extreme outliers were rejected in case that the results deviated from the robust mean more than 0 % or in case that the result was reported erroneously (e.g. wrong unit). More detailed information of the testing and statistical treatment of the PT data is available on the internet in the guide for participating laboratories in SYKE pro"ciency testing schemes ( Assigned value e assigned values and their uncertainties are presented in Appendix 6. e NIST traceable calculated concentrations were used as the assigned values for measurements of N NO2+NO3, N tot, P PO4 and P tot in the arti"cial samples. e calculated concentration was used as the assigned value also
9 7 for the measurement of colour value although the value was not NIST traceable. For the calculated assigned values the expanded measurement uncertainty (k=2) was estimated using standard uncertainties associated with individual operations involved in the preparation of the sample. e main individual source of the uncertainty was the uncertainty of the concentration in the stock solution. For the other samples and measurements the robust means or means of the results reported by the participants were used as the assigned value. e uncertainty of the assigned value was calculated using the robust standard deviation (or the standard deviation) of the reported results using the formula presented in Appendix 6. e uncertainty of the calculated assigned values was less than 1 %. When using the robust mean of the participant results as the assigned value, the uncertainties of the assigned values varied between 0.9 % and 19 % (Appendix 6). $#er reporting of the preliminary results the assigned values was recalculated a#er rejecting erroneously reported results. Following changes to the assigned values have been done: Sample Measurement Change Impact on performance evaluation B2S Colour mg/l, Pt Questionable result Satisfactory result (Lab 8). N3N N NO2+NO mg/l No impact on performance evaluation. N3P P PO4.0.2 µg/l No impact on performance evaluation. e reliability of the assigned value was tested according to the criterion: u/s p %& 0.3, where u = the standard uncertainty of the assigned value (the expanded uncertainty of the assigned value divided by 2) s p = the standard deviation for pro"ciency assessment (total standard deviation divided by 2). In the testing of the reliability of the assigned value the criterion was not met in every case, which is indicated by the high uncertainty of the assigned values in the following cases: Sample B2S N3N N3P Measurement Colour-1 N NH4 P PO4 In the above cases the standard deviations of the reported results were high for the reliable performance evaluation (Table 1). Due to low number of results the evaluation of performance is only approximate for the Colour-2 results from the samples B2S and N3S.
10 Standard deviation for pro ciency assessment and z score "e performance evaluation was carried out by using z scores (Appendix 7). "e total standard deviation for pro!ciency assessment used for calculation of the z scores was estimated on basis of the type of the sample, the concentration of the element, the results of homogeneity testing, the uncertainties of the assigned values and the long-term variation in former pro!ciency tests. A er the preliminary performance evaluation the total standard deviations were changed as follows: Sample Measurement Change of 2 s p Impact on performance evaluation A1N N NH4 % % Labs, 18, 24, 2, 44: Questionable result Satisfactory result. Lab 31: Unsatisfactory results Questionable result. N3N N NH4 % % Labs, 7, 17, 23, 24 2, 28, 29: Questionable result Satisfactory result. Labs 2, 16, 21, 34, 3, 37, 44: Unsatisfactory results Questionable result. "e performance evaluation of the participants using calculated z scores is presented in Appendix 8.!e reliability of the target value for total deviation and the reliability of the corresponding z score were estimated by comparing the deviation for pro!ciency assessment (s p ) with the robust standard deviation of the reported results (s rob ). "e criterion s rob /s p < 1.2 was met in most cases. "is criterion was not met in the case Colour-1 results from the sample B2S, which weakened the evaluation of performance. 3 Results and conclusions 3.1 Results "e results and the performance of each laboratory are presented in Appendix 8 and the summary of the results in Table 1. "e reported results with their expanded uncertainties (k = 2) are presented in Appendix 9. "e summary of z-scores is shown in Appendix. "e robust standard deviations in the Colour results varied from 0 to 41.4 % and in the other results from 1 % to 13.2 % (Table 1)."e robust standard deviation of results was lower than 3 % for the conductivity and ph results from all samples and for the results of a chlorophyll from the synthetic sample A1K. "e robust standard deviation of the results was lower than % for 77 % of the results and lower than % for 90 % of the results (Table 1). Robust standard deviations higher than % apply to the Colour-2 measurement with a low number of participants and Colour-1 measurement from the sample B2S. Except for Colour determination they were approximately in the same range as in the previous pro!ciency test PK SYKE 1/11 [4], where the deviations varied from 1.0 % to 23.3 %.
11 9 Table 1. Summary of the results in the pro!ciency test 2/13. Ass. val. -the assigned value, Mean- the mean value, Mean rob- the robust mean, Md- the median value, SD rob- the robust standard deviation, SD rob % - the robust standard deviation as percents, Num of Labs- the number of the participants, 2*Targ. SD%- the total standard deviation for pro!ciency assessment at the 9% con!dence interval (=2*s p ), Accepted z-val% - the satisfactory z values: the results (%), where z Analytical methods and status to the results It was allowed to use di$erent analytical methods for the measurements in the PT. "e used analytical methods of the participants are shown in more detail in Appendix Statiscal comparison of the analytical methods has been done only on data, in which the number of the results for each method was ( 3. Colour Colour determination was grouped to two groups: visual method using a comparator (Colour-1) and spectrophotometric method (Colour-2). Depending on the sample 19 or 22 laboratories used visual method and 6 or 7 laboratories spectrophotometric method. Statistical comparison was carried out between visual and spectrophotometric methods and no signi!cant di$erence was observed between the methods. Conductivity Most participants measured conductivity using the standard method EN Only one laboratory used an unspeci!ed other method. Statistical comparison between the methods was not possible carried out due to low number of the results.
12 Phosphate phosphorus About % of the participants determined phosphate phosphorus using the standard method EN 681. Nearly as common method (28 %) was withdrawn Finnish standard method 36. e standard method EN ISO 6878 (manual spectrophotometric method) was used by 14 % of the participants. e ammonium molybdate spectrophotometric method modi!ed for Aquachem technique was used by 4 laboratories. Two laboratories used some other method. In statistical method comparison no signi!cant di"erence was observed between the methods. Total phosphorus About % of the participants determined total phosphorus using the standard method EN ISO 681 as common was the withdrawn standard method SFS 26. e manual standard method EN ISO 6878 was used by % of the participants. Ammonium molybdate method modi!ed for Aquachem technique was used by 4 participants and ICP-MS technique by 2 participants. Two laboratories used some other method. In statistical comparison between the methods the following statistically signi!cant di"erences were observed: Mean ± standard deviation, µg/l Sample / Analyte Method n = number of the results Method 1 (EN ISO 6878) 64.0 ± 14.8, n = 4 N3P / P tot Method 2 (SFS 26) 77.4 ± 4.9, n = 9 Conclusion: The significant difference was observed between the methods 1 and 2. There was one deviating small value (42.1 µg/l) measured with the method 1, which explained the difference. Ammonium nitrogen Most participants (4 %) determined ammonium nitrogen using the standard method SFS 32 (manual indophenol blue spectrophotometric method) and 29 % of the participants used the corresponding automatic standard method EN ISO Depending on the sample 3 or 4 participants used the spectrophotometric salicylate method modi!ed for Aquachem technique and 1 participants used some other method. In statistical comparison between the methods the following statistically signi!cant di"erences were observed: Sample / Analyte Method Method 1 (SFS 32) A1N / N NH4 Method 3 (Aquachem) Method 1 (SFS 32) N3N / N NH4 Mean ± standard deviation, µg/l n = number of the results 60.7 ± 2.9, n = ± 46, n = ±.1, n = 92.9 ± 4. n = 4 Method 3 (Aquachem) Conclusion: Sample A1N: The differences between both the means and the standard deviations were significant. Two of three results measured with the Method 3 were greatly higher than the assigned value. Sample N3N: The difference between the means was significant, but low number of the results with the method 3 weakened the reliability of the method comparison.
13 11 Nitrate + nitrite nitrogen Nitrate+ nitrite nitrogen was determined using several methods. Half of the participants used the standard method EN ISO e standard method EN ISO 4 and the sulfanilamide spectrophotometric method a#er hydrazine reduction modi!ed for Aquachem technique were used by 4 laboratories. e standard method was used by 3 participants and depending of the sample some other method was used by 3 or 8 participants. In statistical comparison between the methods the following statistically signi!cant di"erences were observed: Mean ± standard deviation, µg/l Sample / Analyte Method n = number of the results Method 2 (EN ISO 1339) 76.2 ± 2.6, n = 19 A1N / N NO2+NO3 Method 4 (Aquachem) 79.4 ± 1.8, n = 4 Conclusion: Although the difference between the means was statistically significant it was smaller than the standard uncertainty of the analytical methods. The means of both methods deviated less than 3 % from the NIST traceable assigned value (77.4 µg/l). Low number of the results with the method 4 weakened the reliability of the method comparison. Total nitrogen Most participants (68 %) determined total nitrogen according to the standard method EN ISO About 26 % of the participants used modi!ed Kjeldahl method (e.g. SFS 0) and depending of the sample 1 or 2 laboratories used other methods. In statistical method comparison no signi!cant di"erence was observed between the methods. ph About 60 % of the participants measured ph using universal electrode and 33 % of the participants used an electrode for low ionic waters. a speci!c electrode was used by 1 or two participant. In statistical method comparison no signi!cant di"erence was observed between the electrodes. Turbidity Most participants measured turbidity with an apparatus based on di"used radiation measurement. Two participants used an apparatus based attenuated radiation. Statistical comparison between the methods was not possible carried out due to low number of the results. 3.3 Uncertainties of the results At maximum about 84 % of participants reported the expanded uncertainties (k=2) with their results for some measurements (Table 2, Appendix 12). e range of the reported uncertainties varied between the measurements and the sample types. e measure uncertainty is a part of all measured results and it is a measure for the accuracy of the result. It is misleading to report that the uncertainty is 0 % as two laboratories had reported in the case of turbinity results. Several approaches were used for estimating of measurement uncertainty (Appendix 12). The most used approach based on data of the internal quality data (Meth 3 and Meth 4). Generally, the approach for estimating measurement uncertainty has not made a de nite impact on the uncertainty estimates. Thus, harmonization in the estimating of uncertainties should be continued.
14 Table e range of the expanded measurement uncertainties (k=2) as per cent reported with the results by the participants in the PT 2/13. Analyte Coastal water River water Colour Colour Conductivity N NH N NO2+NO3 N tot 6 6 ph P PO4 9 2 P tot Turbidity Evaluation of performance e total number of laboratories participating in this PT was 44. based on z scores and they were interpreted as follows: e evaluation of performance is Criteria Performance z 2 Satisfactory 2 < z < 3 Questionable z 3 Unsatisfactory In total, 8 % of the results in this pro!ciency test were satisfactory. About 69 % of the participants used accredited methods and 87 % of their results were satisfactory. About 72 % of the results measured using non-accredited methods were satisfactory. Pro#est SYKE arranged a similar pro!ciency test in 11 and then 91 % of the results were satisfactory [4]. Similar test arranged also in 12 and then 81 % of the results were satisfactory []. e calculated z scores are presented with the results of each participant in Appendix 8 and the summary of z scores is presented in Appendix. e summary of the performance evaluation is shown in Table 3.
15 13 Table 3. Summary of the performance evaluation in the pro!ciency test 2/13. 2 s Analyte p, Satisfactory results, Assessment % % a chlorophyll 92 Good performance. In % of the results were satisfactory [4]. Colour n % of the results were satisfactory. Colour The evaluation for the results of the samples B2S and N3S is only approximate due to the low number of the results. In 11 evaluation was not carried out due to the low number of the results. Conductivity 8 In % of the results and in % of the results were satisfactory [, 4]. N NH4 7 In % of the results and in % of the results were satisfactory [, 4]. N NO2+NO In % of the results and in % of the results were satisfactory [, 4]. N tot 9 Good performance. In % of the results and in % of the results were satisfactory [, 4]. ph Good performance. In % of the results and in % of the results were satisfactory [, 4]. P PO4 79 In % of the results were satisfactory []. P tot 86 In % of the results and in % of the results were satisfactory [, 4]. Turbidity 89 In % of the results were satisfactory [4]. According the stability test the concentration of ammonium nitrogen in the sample A1N could decrease, if the temperature increased up to C during the transport. Several laboratories (16) reported the received temperature of the samples from to 21 C and 14 of these laboratories analysed ammonium nitrogen. Most of these laboratories reported satisfactory ammonium nitrogen results for the sample A1N. Two laboratories reported ammonium nitrogen results below the quanti!cation limit and one laboratory too high result from the sample A1N. e provider concluded that in this case the stability of the sample A1N was not reason for the unsatisfactory ammonium nitrogen results. SUMMARY Pro#est SYKE carried out the pro!ciency test for analysis of a chlorophyll, colour, conductivity, nutriens, ph and turbidity February 13. A total of 44 laboratories participated in the PT. e sample types were: arti!cial water, coastal water and river water. e calculated concentrations, the robust mean or mean of the results reported by the participants were used as the assigned values for measurements. e uncertainties of the calculated assigned values were 1 % or less. e uncertainties of the consensus assigned values (the robust mean) varied from 0.9 % to 19 %. e evaluation of the performance of the participants was carried out using z scores. In some cases the evaluation of the performance was not possible e.g. due to the low number of participants. In total, 8 % of the results in this pro!ciency test were satisfactory when deviations of % from the assigned values were accepted. About 69 % of the participants used accredited methods and 87 % of their results were satisfactory.
16 6 YHTEENVETO REFERENCES 14 Pro est SYKE järjesti pätevyyskokeen ympäristönäytteitä analysoiville laboratorioille helmikuussa 13. Pätevyyskokeessa määritettiin synteettisistä näytteistä, rannikkovedestä ja jokivedestä a-klorofylli, fosfaattifosfori, kokonaisfosfori, ammoniumtyppi, nitraatti+nitriitti-typpi, kokonaistyppi, ph, sameus, sähkönjohtavuus ja väri. Pätevyyskokeeseen osallistui yhteensä 44 laboratoriota. Laboratorioiden pätevyyden arviointi tehtiin z-arvon avulla ja sen laskemisessa käytetyn kokonaishajonnan tavoitearvot olivat välillä 2,4 3 %. Mittaussuureen vertailuarvona käytettiin pääsääntöisesti laskennallista pitoisuutta tai osallistujien ilmoittamien tulosten robustia keskiarvoa. Pinta- ja rannikkovesinäytteiden värin vertailuarvona käytettiin keskiarvoa. Kun tavoitearvona käytettiin laskennallsita pitoisuutta, sen epävarmuus oli pienempi kuin 1 % ja robustia keskiarvoa käytettäessä tavoitearvon epävarmuus vaihteli 0,9 % ja 19 % välillä. Pienestä tulosmäärästä johtuen spektrifotometrisesti määritetyn värin vertailuarvon epävarmuutta ei voinut määrittää. Eri analyysimenetelmillä saaduissa tuloksissa todettiin jonkin verran merkitseviä eroja. Menetelmävertailun luotettavuutta heikensi, jos toisella vertailtavalla menetelmällä oli vähän tuloksia. Koko tulosaineistossa hyväksyttäviä tuloksia oli 8 %, kun vertailuarvosta sallittiin 2,4 3 %:n poikkeama. Noin 69 % osallistujista käytti akkreditoituja määritysmenetelmiä ja näistä tuloksista oli hyväksyttäviä 87 %. 1. ISO/IEC 17043,. Conformity assessment General requirements for pro!ciency testing. 2. ISO 1328, 0. Statistical methods for use in pro!ciency testing by interlaboratory comparisons. 3. "ompson, M., Ellison, S.L. R., Wood, R., 06. "e International Harmonized Protocol for the Pro!ciency Testing of Analytical Chemistry laboratories (IUPAC Technical report). Pure Appl. Chem. 78: ( 4 Korhonen-Ylönen, K., Näykki, T., Järvinen, O., Leivuori, M., Tervonen, K., Lanteri, S., Ilmakunnas, M. ja Väisänen, R., 11. Laboratorioiden välinen pätevyyskoe 1/11 a-klorofylli, ph, ravinteet, sameus, sähkönjohtavuus ja väri luonnonvesistä. Suomen ympäristökeskus. Suomen ympäristökeskuksen raportteja 13 / 11. ISBN (PDF), 67 s. est > Raportoidut pätevyyskokeet.. Korhonen-Ylönen, K., Leivuori, M., Näykki, T., Järvinen, O., Tervonen, K., Lanteri, S., Ilmakunnas, M. ja Väisänen, R., 12. Laboratorioiden välinen pätevyyskoe 1/12 Alkaliniteetti, ph, ravinteet ja sähkönjohtavuus luonnonvesistä. Suomen ympäristökeskus. Suomen ympäristökeskuksen raportteja / 12. ISBN (PDF), 67 s. est > Raportoidut pätevyyskokeet.
17 PARTICIPANTS APPENDIX 1 Country Denmark Estonia Finland Georgia Kyrgyzstan Name of participant Eurofins Miljø A/S, Vejen Estonian Marine Institute of Tartu university, Tallinn Ahma ymparistö Oy, Rovaniemi Almalab/Ympäristötieteiden laitos/hy, Lahti Etelä-Pohjanmaan Vesitutkijat Oy, Ilmajoki Haapaveden kaupungin ympäristölaboratorio, Haapavesi HSY/Vedenpuhdistus, käyttölaboratorio, Helsinki Jyväskylän yliopisto, Ympäristöntutkimuskeskus, Jyväskylä KCL Kymen Laboratorio Oy, Kuusankoski Kokemäenjoen vesistön vesiensuojeluyhdistys ry, Tampere Labtium Oy, Espoo Lounais-Suomen vesi- ja ympäristötutkimus Oy, Turku Länsi-Uudenmaan vesi ja ympäristö ry, Lohja Metsäntutkimuslaitos, Rovaniemi Metsäntutkimuslaitos, Vantaa MetropoliLab, Helsinki Nab Labs Oy, Oulu Neste Oil Oyj, Tutkimus ja kehitys, vesilaboratorio, Kulloo Novalab Oy, Karkkila Ramboll Analytics, Lahti Rauman Vesi, Rauma Saimaan Vesi- ja Ympäristötutkimus Oy, Lappeenranta Savo-Karjalan Ympäristötutkimus Oy, Joensuu Savo-Karjalan Ympäristötutkimus Oy, Kuopio SGS Inspection Services Oy, Kotka Suomen Ympäristöpalvelut Oy, Oulu SYKE Laboratory Centre, Helsinki SYKE Laboratory Centre, Joensuu SYKE Laboratory Centre, Oulu SYKE, Marine Research Centre, Helsinki Tampereen Vesi, Viemärilaitoksen laboratorio, Tampere Tvärminnen eläintieteellinen asema, Hanko Vaasan kaupungin ympäristölaboratorio, Vaasa Viljavuuspalvelu Oy, Mikkeli Yara Suomi Oy, Uusikaupunki ÅMHM laboratoriet, Jomala The Department of the Environmental Pollution Monitoring, Tbilisi Ecological Monitoring Administration (Laboratory) the State Agency of Environment Protection and Forestry under government of Kyrgyz Rebublic, SAEPF, Bishkek Division of Surface Water Pollution Observation (Laboratory) of Environmental Pollution Observation Administration, the State Agency on Hydrometeorology under the Ministry of Emergency Situations of the KR (Kyrgyzhydromet), Bishkek Division of Ecological Monitoring and the State Ecological Expertise (Laboratory), Issyk-Kul-Naryn Territorial Administration of Environment Protection, SAEPF, Cholpon-Ata City Division of Ecological Monitoring and the State Ecological Expertise (Laboratory), Djalal-Abad Territorial Administration of Environment Protection, SAEPF, Djalal- Abad City Norway Sweden Division of Ecological Monitoring and the State Ecological Expertise (Laboratory), Osh-Batken Territorial Administration of Environment Protection, SAEPF, Osh City Eurofins Environmental Testing Norway AS, Moss ITM, Stockholm University, Stockholm
18 APPENDIX 2/1 16 PREPARATION OF THE SAMPLES Sample 2 ph Chlorophyll a P PO4 P tot A1J KCl Addition, ms/m 6 Assigned value, ms/ 7.7 A1H Addition Na 2 HPO 4 / KH 2 PO Assigned value 7,2 B2H Original concentration ms/m or ph unit Assigned value ms/m or ph unit N3H Original concentration ms/m or ph unit Assigned value ms/m or ph unit A1K Addition, abs/cm a chlorophyll 3 mg / 1.l l ethanol 0.12 Assigned value, abs/cm A1P Addition KH 2 PO 4 KH 2 PO Assigned value, µg/l B2P Original concentration, µg/l Assigned value, µg/l N3P Original concentration, µg/l Assigned value, µg/l
19 17 APPENDIX PREPARATION OF THE SAMPLES 2/2 Sample N NO2+NO3 N NH4 N tot Colour-1 / Colour-2 A1N Addition, µg/l NaNO 3 NH 4 Cl NaNO NH 4 Cl CH 2 CH 2 COOH 171 Assigned value, µg/l Turbidity B2N Original concentration, µg/l Addition, µg/l 26 Assigned value, µg/l N3N Original concentration, µg/l Addition, µg/l 2 Assigned value, µg/l A1V Additon, mg/l Pt K 2 PtCl 6 CoCl 2 3 Assigned value, mg/l Pt 3/3 A1S Addition, FNU HACH Formazin Turbidity Standard 4 Assigned value, FNU 3.9 B2S Original concentration, mg/l Pt or FNU 0.13 Addition, FNU 2 N3S Assigned value, mg/l Pt or FNU Original concentration, mg/l Pt or FNU Assigned value mg/l Pt or FNU 19/ /
20 APPENDIX 3 TESTING OF HOMOGENEITY 18 Homogeneity of the coastal and river water samples was tested by analysing the concentration of the analyte from 8 subsamples. Criteria for homogeinity: s a /s p <0. and s bb 2 <c, where s p % = standard deviation for proficiency assessment s a = analytical deviation, standard deviation of the results within sub samples s bb = between-sample deviation, standard deviation of the results between sub samples c = F1 x s all 2 + F2 x s a 2, where s all 2 = (0.3 x s p ) 2 F1 = 2.01 and F2 = 1.2, when the number of sub samples is 8 Measurement / Sample Concentration µg/l or FNU s p s p s a s a /s p s a /s p <0,? s bb s bb 2 c s bb 2 <c? % N NH4 /B2N 2, Yes Yes N NH4 /N3N 97, Yes Yes N tot /B2N Yes Yes N tot /N3N Yes Yes P tot /B2P 33, Yes ,97 Yes P tot /N3P 71, Yes ,6 Yes Turbidity/B2S 2, Yes ,011 Yes Turbidity/N3S 11, Yes ,14 Yes Conclusion: All criterions for homogeneity fulfilled. The samples could be regarded as homogenous. Homogeneity of the ph samples was tested by measuring ph value from subsamples. Criteria for homogeinity: s bb < 0. s p s p % = standard deviation for proficiency assessment s bb = standard deviation of the results between sub samples Measurement / Sample Concentration Stanadard deviation s p 0. s p s (s bb ) bb < 0. s p? ph/ B2H Yes ph/ N3H Yes Conclusion: The criteria for homogeneity fulfilled. The samples could be regarded as homogenous.
21 TESTING OF STABILITY 19 APPENDIX 4 The samples were distributed 11 February 13 and they were mainly received during the next day. The time table for analysing of the samples was as follows: Chlorophyll a 14 February 13 ph, conductivity 14 February 13 N NH4, N NO3+NO2, P PO4 14 February 13 Turbidity, colour 14 February 13 N tot, P tot Before 22 February 13 Stability of ph, N NH4, P PO4 and a chlorophyll was tested by analysing the samples stored at the temperatures 4 C and C. Criteria for stability: D < 0.3 s p, where D = the difference of results measured from the samples stored at the temperatures 4 C and C s p = standard deviation for proficiency assessment ph Sample Result Sample Result Sample Result Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) A1H B2H N3H D s p D <0.3 s p Yes D < 0.3 s p Yes D < 0.3 s p Yes N NH4 Sample Result, µg/l Sample Result, µg/l Sample Result, µg/l Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) Date 12 Feb. 14 Feb ( ºC) 14 Feb (4 ºC) Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) A1N N3N D s p D <0.3 s p No D < 0.3 s p Yes D < 0.3 s p Yes P PO4 Sample Result, µg/l Sample Result, µg/l Sample Result, µg/l Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) A1P B2P N3P D ) ) s p D <0.3 s p No D < 0.3 s p No D < 0.3 s p Yes 1) The difference depended on the analytical deviation. It was not obvious that the concentration of P PO4 could increase in the sample A1P. The NIST traceable assigned value for the concentration of P PO4 was 16.3 µg/l. 2) The difference depended on the analytical deviation. The difference of the results measured 12 February and 23 February ( C) was -0.16, which was smaller than 0.3 s p. Chlorophyll a Sample Result, abs/cm Date 12 Feb 14 Feb ( ºC) 14 Feb (4 ºC) A1K D 0.0 0,3 s p D <0,3 s p Yes Conclusion: According the test the concentration of N NH4 in the sample A1N could decrease, if the temperature of the samples increased during the distribution. This was taken into account in performance evaluation (Chapter 4). All other analytes could be regarded stable enough for the proficiency test.
22 APPENDIX FEEDBACK FROM THE PROFICIENCT TEST Feedback from the participants Laboratory Comments on samples Action / SYKE 11 The participant informed that several sample bottles had the same sample number. 18 The sample letter was not included in the sample packace. The participant analysed the samples according to the guidelines given for the previous corresponding proficiency test. Laboratory Comments on results Action / SYKE 7, 16, 22, 34 The participant received also in reanalysis significantly too high ammonium nitrogen results from the sample A1N. 9 The participant had informed with reporting of the results that N and P species had been reported as anions because the guidelines were not clear enough. 18 The participant filtered the samples for phosphate phosphorus determination (pore size 0.4 µm). 37 The participant had reported the colour and conductivity results on the erroneous rows. The correct results were: Conductivity A1J 7.3 ms/m, B2H 76 ms/m, N3H.4 ms/m. Colour-1 A1V 3 mg/l Pt, B2S mg/l Pt, N3S 70 mg/l Pt. Feedback to the participants Laboratory Comments from the provider The sample numbers are given according to the filling order. The samples to the participant are collected randomly. It is possible that the sample bottles for different measurements have the same bottle number. Proftest SYKE regrets for the lack of the letter. The PT letters and other documents are available on Proftest web site ( On request the documents will be sent by . Proftest SYKE asked the samples to send back to SYKE for check analysis. At SYKE the ammonium concentration was measured by manual indophenol blue method (Method 1) and by FIA (Method 2). The results were: Method 1: 62,1 µg/l, SD = 3 % Method 2: 63,1 µg/l, SD = % According to these results the ammonium concentration was not changed significantly. Glycine (Amino acetic acid) was used as organic nitrogen compound in the preparation of the sample A1N (Appendix 2) and it was possible that it interfered the determination of ammonium nitrogen in some cases. The results were corrected by the provider. The results were not included in the calculation of the assigned value. The results were treated as outliers. The results should have been satisfactory, if they had been reported correctly. 4 Probably the turbidity results of the samples B2S and N3S have been reported on the erroneous rows. The results were not included for the calculation of the assigned value. 4 The results of N NH4 were reported as accredited, but without measurement uncertainties. 11, 32 It is misleading to report uncertainties 0 %, if any uncertainty has not been estimated. The results were reported as accredited, but without measurement uncertainties.
23 21 APPENDIX EVALUATION OF THE ASSIGNED VALUES Evaluation of U % u/s Measurement Sample Assigned value Unit p the assigned value Chloropfyll a A1K abs/cm Robust mean Colour-1 Colour-2 Conductivity A1V 3 mg/l, Pt Calculated B2S 16 mg/l, Pt Mean N3S 72 mg/l, Pt Mean A1V 3 mg/l, Pt Calculated B2S 19 1) mg/l, Pt Mean - - N3S 76 1) mg/l, Pt Mean - - A1J 7.7 ms/m Robust mean B2H 70 ms/m Robust mean N3H.4 ms/m Robust mean N NH4 B2N 48.1 µg/l Robust mean A1N 9.1 µg/l Robust mean N3N 84.6 µg/l Robust mean N NO2+NO3 B2N 20 µg/l Robust mean A1N 2) 77.4 µg/l Calculated 0.4 <0.1 N3N 23 µg/l Robust mean N tot B2N 46 µg/l Robust mean A1N 2) 4 µg/l Calculated 0.4 <0.1 ph N3N 11 µg/l Robust mean A1H 7.2 Robust mean B2H 7.79 Robust mean N3H 7.19 Robust mean P PO4 B2P 23.1 µg/l Robust mean A1P 2) 16.3 µg/l Robust mean 0.3 <0.1 N3P.0 µg/l Robust mean 3,7 0.4 P tot B2P 29.3 µg/l Robust mean A1P 2) 16.3 µg/l Calculated 0.3 <0.1 Turbidity N3P 73.7 µg/l Robust mean A1S 3.9 FNU Robust mean B2S 1.98 FNU Robust mean N3S 11.3 FNU Robust mean /1 1) 2) The evaluation of the assigned value for Colour-2 was not carried out due to low number of the results. The performance evaluation of these results is only approximate. NIST traceable assigned value. The uncertainty of the calculated assigned value was estimated on the basis of the sample preparation. Other measurements the uncertainty was estimated using the data of the results as follows:
24 APPENDIX 6/2 22 EVALUATION OF THE ASSIGNED VALUES U% n AV s rob, where U% = the expanded uncertainty of the assigned value n = the number of the results s rob = the robust standard deviation (for the robust mean) or the standard deviation (for the mean) AV = the assigned value Criterion for realibility of the assigned value: u/s p 0.3 u = Standard uncertainty of the assigned value s p = Target value of the standard deviation for proficiency assessment Conclusion: Performance evaluation could be regarded reliable except for the Colour-2 results from the samples B2S and N3S and the Colour-1 results from the sample B2S.
25 TERMS IN THE RESULT TABLES 23 APPENDIX 7 Results of each participants Sample the code of the sample z-graphics z score - the graphical presentation z value calculated as follows: z = (x i - X)/s p, where x i = the result of the individual laboratory X = the reference value (the assigned value) s p = the target value of the standard deviation for proficiency assessment Outl test OK yes - the result passed the outlier test H = Hampel test (test for the mean value) C = Cochran test (replicate test) Assigned value the reference value 2* Targ SD % the target value of total standard deviation for proficiency assessment (s p ) at the 9 % confidence level, equal 2 s p Lab s result the result reported by the participant (the mean value of the replicates) Md. Median Mean Mean SD Standard deviation SD% Standard deviation, % Passed The results passed the outlier test Outl. failed The results not passed the outlier test Missing i.e. < DL Num of labs the total number of the participants Summary on the z scores S satisfactory ( -2 z 2) Q questionable ( 2< z < 3), positive error, the result deviates more than 2 s p from the assigned value q questionable ( -3 > z< -2), negative error, the result deviates more than 2 s p from the assigned value U unsatisfactory (z 3), positive error, the result deviates more than 3 s p from the assigned value u unsatisfactory (z -3), negative error, the result deviates more than 3 s p from the assigned value Robust analysis The data items are sorted in increasing order: x 1, x 2,, x i,,x p. Initial values for x * and s * are calculated as follows: x* = median of x i (i = 1, 2,...,p) s* = 1,483 median of x i x* (i = 1, 2,...,p) The mean x* and s* are updated as follows: Calculate = 1. s*. A new value is then calculated for each result x i (i = 1, 2 p): { x* -, if x i < x* - x i * = { x* +, if x i > x* + { x i otherwise The new values of x * and s * are calculated as follows: * x xi / p * s * p i 1 ( x * i x * ) 2 /( p 1) Ref: Statistical methods for use in proficiency testing by inter laboratory comparisons, Annex C [3].
26 24 LIITE APPENDIX 8 / 1 LIITE 8. RESULTS OF EACH PARTICIPANT APPENDIX 8. Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 1 a-chlorophyll abs/cm A1K 0,000 yes 0,117 0,117 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S 0,741 yes ,76 11,2, conductivity ms/m A1J -0,476 yes 7,7 7,48 7,6 7,84 0,1671 2, ms/m B2H -0,33 yes ,1 17,84 2, ms/m N3H -1,4 yes,4,1,4,4 0,2988 2, ,971 H 9,1 90,0 9, 8,,022 8, ,328 yes 48,1 6, 47,6 48,27 3, ,324 yes 84,6 93,0 87,1 84,66 9,996 11, ,711 yes 77,4 8 79,6 76,9 77,2 4,393, ,390 yes , ,8 8,223 3, ,44 yes , 22 23,2 17,27 3, Ntot µg/l A1N 1,246 yes 4 332,4 6, 6,21 6, ,291 yes 46 34, ,6,0, ,096 yes ,02, P-PO4 µg/l A1P 0,24 yes 16,3 16,,8,84 0, ,19 yes 23,1 22, 22,7 22,9 1,193, ,20 H, 39,9,28 2,71 6, ph A1H -0,493 yes 7,2 2,8 7,2 7,2 7,241 0,0961 1, B2H 1,086 yes 7,79 2,6 7,9 7,8 7,798 0, , N3H 0,099 yes 7,19 2,8 7,2 7,19 7,19 0,82 1, Ptot µg/l A1P -1,9 yes 16,3,0 16,9 0,9672 6, ,819 yes 29,3, 29 29,08 1,67, ,217 yes 73,7 74, 74 74,14 4,491 6, Turbidity FNU A1S -0,334 yes 3,9 3, 3,62 3,616 0,3878, FNU B2S 0,606 yes 1,98 2,1 2 1,983 0, , FNU N3S -0,90 yes 11,3,8 11,3 11,31 0,887 7, Laboratory 2 a-chlorophyll abs/cm A1K 77,6 H 0,117 0,71 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S -1,111 yes ,76 11,2, conductivity ms/m A1J 1,849 yes 7,7 7,92 7,6 7,84 0,1671 2, ms/m B2H 1,499 yes , ,1 17,84 2, ms/m N3H 1,962 yes,4,91,4,4 0,2988 2, ,80 yes 9,1 61,67 9, 8,,022 8, ,391 yes 48,1 46,69 47,6 48,27 3, ,11 yes 84,6 68,67 87,1 84,66 9,996 11, ,28 yes 77,4 8 76,6 76,9 77,2 4,393, ,0 yes ,8 8,223 3, ,669 yes ,2 17,27 3, Ntot µg/l A1N 0,132 yes 4 7 6, 6,21 6, ,464 yes ,6,0, ,060 yes ,02, P-PO4 µg/l A1P -1,9 yes 16,3,0,8,84 0, ,38 yes 23,1 21, 22,7 22,9 1,193, ,0 yes,4 39,9,28 2,71 6, ph A1H -0,788 yes 7,2 2,8 7,17 7,2 7,241 0,0961 1, B2H 0,099 yes 7,79 2,6 7,80 7,8 7,798 0, , N3H -0,099 yes 7,19 2,8 7,18 7,19 7,19 0,82 1, Ptot µg/l A1P -1,4 yes 16,3,4 16,9 0,9672 6, ,02 yes 29,3 27, ,08 1,67, ,678 yes 73,7 71, ,14 4,491 6, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
27 LIITE 8 / 2 2 APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 3 a-chlorophyll abs/cm A1K -0,8 yes 0,117 0,112 0,117 0,1169 0, , ,78 yes 9,1 6,4 9, 8,,022 8, ,71 yes 48,1 4,39 47,6 48,27 3, ,908 yes 77,4 8 89,0 76,9 77,2 4,393, ,006 yes , ,8 8,223 3, Ntot µg/l A1N 0,879 yes 4 324,04 6, 6,21 6, ,031 yes 46 47, ,6,0, P-PO4 µg/l A1P 0,233 yes 16,3 16,49,8,84 0, ,6 yes 23,1 23,28 22,7 22,9 1,193, ph A1H 2,660 yes 7,2 2,8 7,2 7,2 7,241 0,0961 1, B2H -1,284 yes 7,79 2,6 7,66 7,8 7,798 0, , Ptot µg/l A1P -0,344 yes 16,3 16,02 16,9 0,9672 6, ,0 yes 29,3, ,08 1,67, Laboratory 4 Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S 0,741 yes ,76 11,2, conductivity ms/m A1J 0,81 yes 7,7 7,68 7,6 7,84 0,1671 2, ms/m B2H 0,000 yes ,1 17,84 2, ms/m N3H 0,64 yes,4,7,4,4 0,2988 2, ,474 yes 9,1 61,2 9, 8,,022 8, ,333 yes 48,1 46,9 47,6 48,27 3, ,214 yes 84,6 76,9 87,1 84,66 9,996 11, H 77,4 8 <0 76,9 77,2 4,393, H 20 8 < ,8 8,223 3, ,3 H ,2 17,27 3, ph A1H 0,690 yes 7,2 2,8 7,32 7,2 7,241 0,0961 1, B2H 2,074 yes 7,79 2,6 8,00 7,8 7,798 0, , N3H 2,83 yes 7,19 2,8 7,4 7,19 7,19 0,82 1, Turbidity FNU A1S 1,23 yes 3,9 4,00 3,62 3,616 0,3878, FNU B2S 49,600 H 1,98 11,8 2 1,983 0, , FNU N3S -,7 H 11,3 2,22 11,3 11,31 0,887 7, Laboratory a-chlorophyll abs/cm A1K 0,000 yes 0,117 0,117 0,117 0,1169 0, , Colour-2 mg/l, Pt A1V -0,14 yes 3 34,62 34,16 33,96 1, mg/l, Pt B2S -0,7 yes ,64 17,8 19,01,929 31, mg/l, Pt N3S -1,72 yes 76 6,33 64,4 7,64 27,6 36, conductivity ms/m A1J -0,370 yes 7,7 7, 7,6 7,84 0,1671 2, ms/m B2H 0,000 yes 70 70, ,1 17,84 2, ms/m N3H -0,192 yes,4,3,4,4 0,2988 2, ,984 yes 9,1 63,46 9, 8,,022 8, ,132 yes 48,1,79 47,6 48,27 3, ,8 yes 84,6 96,37 87,1 84,66 9,996 11, ,06 yes 77,4 8 77,2 76,9 77,2 4,393, ,9 yes , ,8 8,223 3, ,684 yes , ,2 17,27 3, Ntot µg/l A1N 0,000 yes 4 4 6, 6,21 6, ,342 yes ,6,0, , yes ,02, P-PO4 µg/l A1P 0,614 yes 16,3 16,8,8,84 0, ,693 yes 23,1 23,9 22,7 22,9 1,193, ,0 yes 44,6 39,9,28 2,71 6, ph A1H 0,296 yes 7,2 2,8 7,28 7,2 7,241 0,0961 1, B2H 0,889 yes 7,79 2,6 7,88 7,8 7,798 0, , N3H 0,199 yes 7,19 2,8 7,21 7,19 7,19 0,82 1, Ptot µg/l A1P 0,89 yes 16,3 17,0 16,9 0,9672 6, ,160 yes 29,3 27, ,08 1,67, ,248 yes 73,7 78, ,14 4,491 6, Turbidity FNU A1S 0,111 yes 3,9 3,62 3,62 3,616 0,3878, FNU B2S -0,4 yes 1,98 1,90 2 1,983 0, , FNU N3S 0,90 yes 11,3 11,80 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
28 26 LIITE APPENDIX 8 / 3 Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 6 conductivity ms/m A1J -13,690 H 7,7 4,98 7,6 7,84 0,1671 2, ms/m N3H -14,080 H,4 6,74,4,4 0,2988 2, ,60 H 9,1 2 9, 8,,022 8, ,000 H 84, ,1 84,66 9,996 11, ,790 H 77, ,9 77,2 4,393, ,8 H ,2 17,27 3, P-PO4 µg/l A1P -7,7 H 16,3,8,84 0, ,000 H ,9,28 2,71 6, ph A1H -0,296 yes 7,2 2,8 7,22 7,2 7,241 0,0961 1, N3H -2,980 yes 7,19 2,8 6,89 7,19 7,19 0,82 1, Laboratory 7 14,190 H 9, , 8,,022 8, ,028 yes 48,1 48,2 47,6 48,27 3, ,371 yes 84,6 7,9 87,1 84,66 9,996 11, ,42 yes 77,4 8 78,8 76,9 77,2 4,393, ,700 yes ,8 8,223 3, ,000 yes ,2 17,27 3, Ntot µg/l A1N -0,132 yes 4 1 6, 6,21 6, ,391 yes ,6,0, ,297 yes ,02, P-PO4 µg/l A1P -0,614 yes 16,3,8,8,84 0, ,693 yes 23,1 22,3 22,7 22,9 1,193, ,00 yes 41,0 39,9,28 2,71 6, Laboratory 8 a-chlorophyll abs/cm A1K 0,000 yes 0,117 0,117 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V -0,762 yes ,71 4,314 12, mg/l, Pt B2S -1,429 yes ,89,121 32, mg/l, Pt N3S -0,370 yes ,76 11,2, conductivity ms/m A1J -0,370 yes 7,7 7,0 7,6 7,84 0,1671 2, ,7 H 9,1 1 9, 8,,022 8, ,4 yes 84, ,1 84,66 9,996 11, ,77 yes 77, ,9 77,2 4,393, ,071 H ,2 17,27 3, Ntot µg/l A1N -0,614 yes , 6,21 6, ,1 yes ,02, P-PO4 µg/l A1P -,276 H 16,3 12,8,84 0, ,00 H 13 39,9,28 2,71 6, ph A1H -1,478 yes 7,2 2,8 7,1 7,2 7,241 0,0961 1, B2H 0,099 yes 7,79 2,6 7,8 7,8 7,798 0, , N3H -0,894 yes 7,19 2,8 7,1 7,19 7,19 0,82 1, Ptot µg/l A1P 2,086 yes 16, ,9 0,9672 6, ,090 yes 73, ,14 4,491 6, Turbidity FNU A1S -0,334 yes 3,9 3, 3,62 3,616 0,3878, Laboratory 9 Colour-1 mg/l, Pt A1V,714 yes ,71 4,314 12, mg/l, Pt B2S -3,929 yes 16 3,89,121 32, mg/l, Pt N3S 2,93 yes ,76 11,2, conductivity ms/m A1J 0,687 yes 7,7 7,70 7,6 7,84 0,1671 2, ms/m B2H 0,373 yes ,1 17,84 2, ms/m N3H 0,38 yes,4,,4,4 0,2988 2, ,238 H 77, ,9 77,2 4,393, ,00 yes ,8 8,223 3, ,717 yes ,2 17,27 3, P-PO4 µg/l A1P -0,368 yes 16,3 16,8,84 0, ,260 yes 23,1 22,8 22,7 22,9 1,193, ,0 yes 39,8 39,9,28 2,71 6, ph A1H -0,493 yes 7,2 2,8 7,2 7,2 7,241 0,0961 1, B2H 0,099 yes 7,79 2,6 7,8 7,8 7,798 0, , N3H 0,099 yes 7,19 2,8 7,2 7,19 7,19 0,82 1, Ptot µg/l A1P H 16,3 <0 16,9 0,9672 6, H 29,3 < ,08 1,67, H 73,7 < ,14 4,491 6, Turbidity FNU A1S 1,23 yes 3,9 4,00 3,62 3,616 0,3878, FNU B2S -0,1 yes 1,98 1,9 2 1,983 0, , FNU N3S -0,34 yes 11,3 11,0 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
29 LIITE 8 / 4 27 APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory conductivity ms/m A1J 0,03 yes 7,7 7,8 7,6 7,84 0,1671 2, ms/m N3H -0,38 yes,4,3,4,4 0,2988 2, ,827 yes 9,1 1 9, 8,,022 8, ,36 yes 84, ,1 84,66 9,996 11, ,42 yes 77, ,9 77,2 4,393, ,000 yes ,2 17,27 3, Ntot µg/l A1N -0,31 yes , 6,21 6, ,601 yes ,02, P-PO4 µg/l A1P -1,9 yes 16,3,0,8,84 0, ,000 yes 38,0 39,9,28 2,71 6, ph A1H -0,296 yes 7,2 2,8 7,22 7,2 7,241 0,0961 1, N3H -1,987 yes 7,19 2,8 6,99 7,19 7,19 0,82 1, Ptot µg/l A1P 0,000 yes 16,3 16,3 16,9 0,9672 6, ,7 yes 73,7 72, ,14 4,491 6, Turbidity FNU A1S 0,8 yes 3,9 3,70 3,62 3,616 0,3878, FNU N3S -1,003 yes 11,3,4 11,3 11,31 0,887 7, Laboratory 11 a-chlorophyll abs/cm A1K 0,137 yes 0,117 0,1178 0,117 0,1169 0, , conductivity ms/m A1J -0,03 yes 7,7 7,6 7,6 7,84 0,1671 2, ms/m B2H 0,480 yes ,1 17,84 2, ms/m N3H 0,000 yes,4,4,4,4 0,2988 2, ,64 yes 9,1 6,2 9, 8,,022 8, ,444 yes 48,1 49,7 47,6 48,27 3, ,72 yes 84,6 89,2 87,1 84,66 9,996 11, ,42 yes 77,4 8 76,0 76,9 77,2 4,393, ,600 yes ,8 8,223 3, ,717 yes ,2 17,27 3, Ntot µg/l A1N -0,7 yes , 6,21 6, ,294 yes ,6,0, ,216 yes ,02, P-PO4 µg/l A1P 0,491 yes 16,3 16,7,8,84 0, ,433 yes 23,1 22,6 22,7 22,9 1,193, ,20 yes 39, 39,9,28 2,71 6, ph A1H -0,394 yes 7,2 2,8 7,21 7,2 7,241 0,0961 1, B2H -0,889 yes 7,79 2,6 7,70 7,8 7,798 0, , N3H 2,83 yes 7,19 2,8 7,4 7,19 7,19 0,82 1, Ptot µg/l A1P -1,718 yes 16,3 14,9 16,9 0,9672 6, ,4 yes 29,3 29, ,08 1,67, ,062 yes 73,7 81, ,14 4,491 6, Turbidity FNU A1S -1,931 yes 3,9 3,07 3,62 3,616 0,3878, FNU B2S -3,384 yes 1,98 1,31 2 1,983 0, , FNU N3S -2,442 yes 11,3 9,23 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
30 28 LIITE APPENDIX 8 / Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 12 a-chlorophyll abs/cm A1K 0,342 yes 0,117 0,119 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 1,90 yes 3 3 3,71 4,314 12, mg/l, Pt B2S 1,429 yes 16 3,89,121 32, mg/l, Pt N3S 2,93 yes ,76 11,2, conductivity ms/m A1J -0,169 yes 7,7 7,38 7,6 7,84 0,1671 2, ms/m B2H -0,272 yes , ,1 17,84 2, ms/m N3H 1,00 yes,4,79,4,4 0,2988 2, ,090 yes 9,1 9, 9, 8,,022 8, ,719 yes 48,1 41,9 47,6 48,27 3, ,81 yes 84,6 79,2 87,1 84,66 9,996 11, ,129 yes 77,4 8 77,0 76,9 77,2 4,393, ,0 yes ,8 8,223 3, ,96 yes ,2 17,27 3, Ntot µg/l A1N 1,4 yes , 6,21 6, ,684 yes ,6,0, ,000 yes ,02, P-PO4 µg/l A1P -0,89 yes 16,3,6,8,84 0, ,346 yes 23,1 22,7 22,7 22,9 1,193, ,0 yes 3,7 39,9,28 2,71 6, ph A1H 0,099 yes 7,2 2,8 7,26 7,2 7,241 0,0961 1, B2H 0,988 yes 7,79 2,6 7,89 7,8 7,798 0, , N3H 0,298 yes 7,19 2,8 7,22 7,19 7,19 0,82 1, Ptot µg/l A1P -0,24 yes 16,3 16,1 16,9 0,9672 6, ,02 yes 29,3 31, 29 29,08 1,67, ,7 yes 73,7 72, ,14 4,491 6, Turbidity FNU A1S -0,780 yes 3,9 3,38 3,62 3,616 0,3878, FNU B2S 2,424 yes 1,98 2,46 2 1,983 0, , FNU N3S 0,118 yes 11,3 11,4 11,3 11,31 0,887 7, Laboratory 13 a-chlorophyll abs/cm A1K 0,171 yes 0,117 0,118 0,117 0,1169 0, , ,69 yes 9,1 62,02 9, 8,,022 8, ,294 yes 48,1 47,04 47,6 48,27 3, ,743 yes 77,4 8 79,7 76,9 77,2 4,393, ,026 yes , ,8 8,223 3, Ntot -0,068 yes 46 43, ,6,0, P-PO4 µg/l A1P -2,94 yes 16,3 13,9,8,84 0, ,30 H 23,1 46,61 22,7 22,9 1,193, ph B2H -,826 H 7,79 2,6 7, 7,8 7,798 0, , Laboratory 14 Ptot µg/l A1P -1,963 yes 16,3 14,7 16,9 0,9672 6, ,90 yes 73,7 77, ,14 4,491 6, Laboratory a-chlorophyll abs/cm A1K -0,017 yes 0,117 0,1169 0,117 0,1169 0, , Colour-2 mg/l, Pt A1V -1,160 yes 3 31,96 34,16 33,96 1, mg/l, Pt B2S 2,49 yes ,29 17,8 19,01,929 31, N-NH4-0,048 yes 48,1 47, ,6 48,27 3, N-NO2+NO3-0,291 yes , ,8 8,223 3, Ntot -13,3 H 46 0, ,6,0, P-PO4-0,121 yes 23,1 22,960 22,7 22,9 1,193, Ptot 0,701 yes 29,3, ,08 1,67, Turbidity FNU A1S -1,8 yes 3,9 3,1 3,62 3,616 0,3878, FNU B2S 0,2 yes 1,98 2,02 2 1,983 0, , Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
31 LIITE 8 / 6 29 APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 16 a-chlorophyll abs/cm A1K 0,684 yes 0,117 0,121 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S 0,741 yes ,76 11,2, conductivity ms/m A1J 0,28 yes 7,7 7,67 7,6 7,84 0,1671 2, ms/m B2H -1,013 yes ,1 17,84 2, ms/m N3H 2,231 yes,4,98,4,4 0,2988 2, N-NH4 0,804 yes 48,1 1 47,6 48,27 3, ,112 yes 84, ,1 84,66 9,996 11, ,163 yes 77, ,9 77,2 4,393, ,0 yes ,8 8,223 3, ,434 yes ,2 17,27 3, Ntot µg/l A1N 0,088 yes 4 6 6, 6,21 6, ,270 yes ,6,0, ,4 yes ,02, P-PO4 µg/l A1P -0,982 yes 16,3,,8,84 0, ,606 yes 23,1 22,4 22,7 22,9 1,193, ,80 yes 38,3 39,9,28 2,71 6, ph A1H 0,690 yes 7,2 2,8 7,32 7,2 7,241 0,0961 1, B2H -0,988 yes 7,79 2,6 7,69 7,8 7,798 0, , N3H 0,894 yes 7,19 2,8 7,28 7,19 7,19 0,82 1, Ptot µg/l A1P 1,472 yes 16,3 17, 16,9 0,9672 6, ,683 yes 29,3 28, ,08 1,67, ,791 yes 73,7 67, ,14 4,491 6, Turbidity FNU A1S -1,003 yes 3,9 3,32 3,62 3,616 0,3878, FNU B2S -1,66 yes 1,98 1,67 2 1,983 0, , FNU N3S -0,236 yes 11,3 11,1 11,3 11,31 0,887 7, Laboratory 17 a-chlorophyll abs/cm A1K -0,81 yes 0,117 0,1136 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,762 yes ,71 4,314 12, mg/l, Pt B2S -0,714 yes ,89,121 32, mg/l, Pt N3S -0,370 yes ,76 11,2, conductivity ms/m A1J -0,476 yes 7,7 7,48 7,6 7,84 0,1671 2, ms/m B2H 0,800 yes ,1 17,84 2, ms/m N3H -1,4 yes,4,1,4,4 0,2988 2, ,3 yes 9,1 60 9, 8,,022 8, ,804 yes 48,1 1 47,6 48,27 3, ,481 yes 84, ,1 84,66 9,996 11, ,8 yes 77, ,9 77,2 4,393, ,00 yes ,8 8,223 3, ,143 yes ,2 17,27 3, Ntot µg/l A1N -0,614 yes , 6,21 6, ,342 yes ,6,0, ,360 yes ,02, P-PO4 µg/l A1P -0,982 yes 16,3,,8,84 0, ,779 yes 23,1 22,2 22,7 22,9 1,193, ,00 yes,1 39,9,28 2,71 6, ph A1H -0,099 yes 7,2 2,8 7,24 7,2 7,241 0,0961 1, B2H 0,691 yes 7,79 2,6 7,86 7,8 7,798 0, , N3H 0,993 yes 7,19 2,8 7,29 7,19 7,19 0,82 1, Ptot µg/l A1P -0,736 yes 16,3,7 16,9 0,9672 6, ,478 yes 29,3, ,08 1,67, ,61 yes 73,7 76, ,14 4,491 6, Turbidity FNU A1S -0,706 yes 3,9 3,4 3,62 3,616 0,3878, FNU B2S 0,1 yes 1,98 2,0 2 1,983 0, , FNU N3S -0,236 yes 11,3 11,1 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
32 LIITE APPENDIX 8 / 7 Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 18 a-chlorophyll abs/cm A1K 0,342 yes 0,117 0,119 0,117 0,1169 0, , Colour-2 mg/l, Pt A1V -0,49 yes 3 33,7 34,16 33,96 1, mg/l, Pt B2S -2,6 yes 19 3, 17,8 19,01,929 31, mg/l, Pt N3S -1,18 yes 76 8,7 64,4 7,64 27,6 36, conductivity ms/m A1J 0,81 yes 7,7 7,68 7,6 7,84 0,1671 2, ms/m B2H -2,60 yes ,1 17,84 2, ms/m N3H -2,962 yes,4 9,63,4,4 0,2988 2, ,782 yes 9,1 1,2 9, 8,,022 8, ,913 yes 48,1 41,2 47,6 48,27 3, ,6 yes 84,6 80,7 87,1 84,66 9,996 11, ,098 yes 77,4 8 74,0 76,9 77,2 4,393, ,0 yes ,8 8,223 3, ,382 yes ,2 17,27 3, Ntot µg/l A1N 0,833 yes , 6,21 6, ,342 yes ,6,0, ,721 yes ,02, P-PO4 µg/l A1P 1,4 yes 16,3 17,2,8,84 0, ,606 yes 23,1 22,4 22,7 22,9 1,193, ,30 H 19,3 39,9,28 2,71 6, ph A1H 0,000 yes 7,2 2,8 7,2 7,2 7,241 0,0961 1, B2H 0,198 yes 7,79 2,6 7,81 7,8 7,798 0, , N3H -0,79 yes 7,19 2,8 7,11 7,19 7,19 0,82 1, Ptot µg/l A1P 0,491 yes 16,3 16,7 16,9 0,9672 6, ,819 yes 29,3 28, ,08 1,67, ,461 yes 73,7 7, ,14 4,491 6, Turbidity FNU A1S 0,817 yes 3,9 3,81 3,62 3,616 0,3878, FNU B2S 0,606 yes 1,98 2, 2 1,983 0, , FNU N3S 0,472 yes 11,3 11,7 11,3 11,31 0,887 7, Laboratory 19 a-chlorophyll abs/cm A1K -0,342 yes 0,117 0,1 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 1,90 yes 3 3 3,71 4,314 12, mg/l, Pt B2S 1,429 yes 16 3,89,121 32, mg/l, Pt N3S 0,741 yes ,76 11,2, conductivity ms/m A1J -0,211 yes 7,7 7, 7,6 7,84 0,1671 2, ms/m B2H 0,427 yes ,1 17,84 2, ms/m N3H -0,64 yes,4,23,4,4 0,2988 2, ,023 yes 9,1 9,0 9, 8,,022 8, , H 48,1 60,8 47,6 48,27 3, ,3 yes 84,6 77,6 87,1 84,66 9,996 11, ,162 yes 77,4 8 76,9 76,9 77,2 4,393, ,00 yes ,8 8,223 3, ,048 yes ,2 17,27 3, Ntot µg/l A1N 0,702 yes 4 3 6, 6,21 6, ,69 yes ,6,0, ,096 yes ,02, P-PO4 µg/l A1P 0,89 yes 16,3 17,0,8,84 0, ,126 yes 23,1 24,4 22,7 22,9 1,193, ,00 yes 42,1 39,9,28 2,71 6, ph A1H 0,197 yes 7,2 2,8 7,27 7,2 7,241 0,0961 1, B2H -0,198 yes 7,79 2,6 7,77 7,8 7,798 0, , N3H -0,099 yes 7,19 2,8 7,18 7,19 7,19 0,82 1, Ptot µg/l A1P 1,227 yes 16,3 17,3 16,9 0,9672 6, ,02 yes 29,3 31, 29 29,08 1,67, ,764 yes 73,7 80, ,14 4,491 6, Turbidity FNU A1S 0,94 yes 3,9 3,7 3,62 3,616 0,3878, FNU B2S 0,2 yes 1,98 2,02 2 1,983 0, , FNU N3S 0,236 yes 11,3 11, 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
33 LIITE 8 / 8 31 APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory a-chlorophyll abs/cm A1K 0, yes 0,117 0,1182 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V -1,90 yes 3 3 3,71 4,314 12, mg/l, Pt B2S -2,143 yes 16 3,89,121 32, mg/l, Pt N3S -1,111 yes ,76 11,2, conductivity ms/m A1J -0,03 yes 7,7 7,6 7,6 7,84 0,1671 2, ms/m B2H 0,213 yes ,1 17,84 2, ms/m N3H -0,346 yes,4,31,4,4 0,2988 2, ,338 yes 9,1 60,6 9, 8,,022 8, ,000 yes 48,1 48,1 47,6 48,27 3, ,04 yes 84,6 87,8 87,1 84,66 9,996 11, ,614 yes 77,4 8 79,3 76,9 77,2 4,393, ,0 yes ,8 8,223 3, ,62 yes ,2 17,27 3, Ntot µg/l A1N 0,31 yes , 6,21 6, ,049 yes ,6,0, ,601 yes ,02, P-PO4 µg/l A1P -1,8 yes 16,3 14,8,8,84 0, ,472 yes 23,1 21,4 22,7 22,9 1,193, ,60 yes 38,7 39,9,28 2,71 6, ph A1H 0,493 yes 7,2 2,8 7, 7,2 7,241 0,0961 1, B2H 0,889 yes 7,79 2,6 7,88 7,8 7,798 0, , N3H 0,298 yes 7,19 2,8 7,22 7,19 7,19 0,82 1, Ptot µg/l A1P -0,24 yes 16,3 16,1 16,9 0,9672 6, ,819 yes 29,3 28, ,08 1,67, ,217 yes 73,7 74, 74 74,14 4,491 6, Turbidity FNU A1S -1,97 yes 3,9 3,16 3,62 3,616 0,3878, FNU B2S -0,1 yes 1,98 1,96 2 1,983 0, , FNU N3S -1,062 yes 11,3,4 11,3 11,31 0,887 7, Laboratory 21 a-chlorophyll abs/cm A1K -0,171 yes 0,117 0,116 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S 0,278 yes ,76 11,2, conductivity ms/m A1J 0,317 yes 7,7 7,63 7,6 7,84 0,1671 2, ms/m B2H -39,600 H 70 7, ,1 17,84 2, ms/m N3H 0,64 yes,4,7,4,4 0,2988 2, ,113 yes 9,1 9,6 9, 8,,022 8, ,277 yes 48,1 49,1 47,6 48,27 3, ,033 yes 84,6 71,7 87,1 84,66 9,996 11, ,872 yes 77,4 8 80,1 76,9 77,2 4,393, ,000 H ,8 8,223 3, ,000 yes ,2 17,27 3, Ntot µg/l A1N 0,17 yes 4 8 6, 6,21 6, ,293 yes ,6,0, ,360 yes ,02, P-PO4 µg/l A1P -0,442 yes 16,3,94,8,84 0, ,117 yes 23,1 24,39 22,7 22,9 1,193, ,08 yes 44,17 39,9,28 2,71 6, ph A1H -0,197 yes 7,2 2,8 7,23 7,2 7,241 0,0961 1, B2H 0,691 yes 7,79 2,6 7,86 7,8 7,798 0, , N3H 0,397 yes 7,19 2,8 7,23 7,19 7,19 0,82 1, Ptot µg/l A1P -0,478 yes 16,3,91 16,9 0,9672 6, ,01 yes 29,3, ,08 1,67, ,434 yes 73,7 82, ,14 4,491 6, Turbidity FNU A1S -1,077 yes 3,9 3,3 3,62 3,616 0,3878, FNU B2S -0,909 yes 1,98 1,8 2 1,983 0, , FNU N3S 1,34 yes 11,3 12,6 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
34 32 LIITE APPENDIX 8 / 9 Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 22 a-chlorophyll abs/cm A1K 0,342 yes 0,117 0,119 0,117 0,1169 0, , Colour-2 mg/l, Pt A1V 0,267 yes 3 3,7 34,16 33,96 1, mg/l, Pt B2S -0,1 yes ,6 17,8 19,01,929 31, mg/l, Pt N3S 1,96 yes 76 98,3 64,4 7,64 27,6 36, conductivity ms/m A1J 0,476 yes 7,7 7,66 7,6 7,84 0,1671 2, ms/m B2H 0,213 yes ,1 17,84 2, ms/m N3H 0,38 yes,4,,4,4 0,2988 2, ,480 H 9, , 8,,022 8, ,99 H 48,1 27,9 47,6 48,27 3, ,229 yes 84,6 92,4 87,1 84,66 9,996 11, ,969 yes 77,4 8 74,4 76,9 77,2 4,393, ,00 yes ,8 8,223 3, ,621 yes ,2 17,27 3, Ntot µg/l A1N 0,31 yes , 6,21 6, ,19 yes ,6,0, ,601 yes ,02, P-PO4 µg/l A1P -0,982 yes 16,3,,8,84 0, ,87 yes 23,1 19,8 22,7 22,9 1,193, ,80 yes 38,3 39,9,28 2,71 6, ph A1H -0,394 yes 7,2 2,8 7,21 7,2 7,241 0,0961 1, B2H -0,988 yes 7,79 2,6 7,69 7,8 7,798 0, , N3H 0,199 yes 7,19 2,8 7,21 7,19 7,19 0,82 1, Ptot µg/l A1P -3,804 yes 16,3 13,2 16,9 0,9672 6, ,072 yes 29,3 24, ,08 1,67, ,841 yes 73,7 70, ,14 4,491 6, Turbidity FNU A1S -0,260 yes 3,9 3,2 3,62 3,616 0,3878, FNU B2S -0,89 yes 1,98 1,81 2 1,983 0, , FNU N3S -1,971 yes 11,3 9,63 11,3 11,31 0,887 7, Laboratory 23 a-chlorophyll abs/cm A1K -0,171 yes 0,117 0,116 0,117 0,1169 0, , Colour-2 mg/l, Pt A1V 7,238 H ,16 33,96 1, mg/l, Pt B2S 1,04 yes ,8 19,01,929 31, mg/l, Pt N3S 3,860 yes ,4 7,64 27,6 36, conductivity ms/m A1J 0,211 yes 7,7 7,61 7,6 7,84 0,1671 2, ms/m B2H 0,693 yes ,1 17,84 2, ms/m N3H 0,38 yes,4,,4,4 0,2988 2, ,090 yes 9,1 9, 9, 8,,022 8, ,139 yes 48,1 47,6 47,6 48,27 3, ,812 yes 84,6 73,1 87,1 84,66 9,996 11, ,293 yes 77,4 8 84, 76,9 77,2 4,393, ,0 H ,8 8,223 3, ,721 yes ,2 17,27 3, Ntot µg/l A1N -0,31 yes , 6,21 6, ,77 yes ,6,0, ,417 yes ,02, P-PO4 µg/l A1P 0,982 yes 16,3 17,1,8,84 0, ,329 H 23,1 28,1 22,7 22,9 1,193, ,0 H 3,1 39,9,28 2,71 6, ph A1H -0,296 yes 7,2 2,8 7,22 7,2 7,241 0,0961 1, B2H -0,099 yes 7,79 2,6 7,78 7,8 7,798 0, , N3H -0,298 yes 7,19 2,8 7,16 7,19 7,19 0,82 1, Ptot µg/l A1P 0,123 yes 16,3 16,4 16,9 0,9672 6, ,341 yes 29,3 29, ,08 1,67, ,79 yes 73,7 84, ,14 4,491 6, Turbidity FNU A1S 4,160 yes 3,9 4,71 3,62 3,616 0,3878, FNU B2S 0,0 yes 1,98 2,08 2 1,983 0, , FNU N3S 1,180 yes 11,3 12,3 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
35 LIITE 8 / 33 APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 24 a-chlorophyll abs/cm A1K 0,171 yes 0,117 0,118 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S -1,111 yes ,76 11,2, conductivity ms/m A1J -1,744 yes 7,7 7,24 7,6 7,84 0,1671 2, ms/m B2H -0,160 yes ,1 17,84 2, ms/m N3H -0,769 yes,4,2,4,4 0,2988 2, ,737 yes 9,1 66,8 9, 8,,022 8, ,832 yes 48,1 4,1 47,6 48,27 3, ,371 yes 84,6 7,9 87,1 84,66 9,996 11, ,226 yes 77,4 8 76,7 76,9 77,2 4,393, ,000 yes ,8 8,223 3, ,33 yes ,2 17,27 3, Ntot µg/l A1N -1,1 yes , 6,21 6, ,636 yes ,6,0, ,961 yes ,02, P-PO4 µg/l A1P -1,8 yes 16,3 14,8,8,84 0, ,866 yes 23,1 22,1 22,7 22,9 1,193, ,20 yes, 39,9,28 2,71 6, ph A1H 0,000 yes 7,2 2,8 7,2 7,2 7,241 0,0961 1, B2H 0,099 yes 7,79 2,6 7,80 7,8 7,798 0, , N3H -0,199 yes 7,19 2,8 7,17 7,19 7,19 0,82 1, Ptot µg/l A1P -0,491 yes 16,3,9 16,9 0,9672 6, , yes 29,3 29, ,08 1,67, ,081 yes 73,7 74, ,14 4,491 6, Turbidity FNU A1S -1,634 yes 3,9 3, 3,62 3,616 0,3878, FNU B2S -3,0 H 1,98 1,38 2 1,983 0, , FNU N3S -1,416 yes 11,3,1 11,3 11,31 0,887 7, Laboratory 2 a-chlorophyll abs/cm A1K -0,171 yes 0,117 0,116 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S,000 yes 16 3,89,121 32, mg/l, Pt N3S 0,741 yes ,76 11,2, conductivity ms/m A1J 0,7 yes 7,7 7,71 7,6 7,84 0,1671 2, ms/m B2H -0,160 yes ,1 17,84 2, ms/m N3H 0,000 yes,4,4,4,4 0,2988 2, ,444 yes 9,1 6, 9, 8,,022 8, ,222 yes 48,1 48,9 47,6 48,27 3, ,371 yes 84,6 7,9 87,1 84,66 9,996 11, ,28 yes 77,4 8 76,6 76,9 77,2 4,393, ,900 yes ,8 8,223 3, ,478 yes ,2 17,27 3, Ntot µg/l A1N -0,39 yes , 6,21 6, ,366 yes ,6,0, ,2 yes ,02, P-PO4 µg/l A1P 0,000 yes 16,3 16,3,8,84 0, ,90 yes 23,1 2,3 22,7 22,9 1,193, ,900 yes 4,8 39,9,28 2,71 6, ph A1H 0,394 yes 7,2 2,8 7,29 7,2 7,241 0,0961 1, B2H -1,481 yes 7,79 2,6 7,64 7,8 7,798 0, , N3H 1,490 yes 7,19 2,8 7,34 7,19 7,19 0,82 1, Ptot µg/l A1P 0,368 yes 16,3 16,6 16,9 0,9672 6, ,706 yes 29,3 26, ,08 1,67, ,33 yes 73,7 72, ,14 4,491 6, Turbidity FNU A1S -0,706 yes 3,9 3, 3,62 3,616 0,3878, FNU B2S -0,6 yes 1,98 1,87 2 1,983 0, , FNU N3S -0,90 yes 11,3,8 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
36 34 LIITE APPENDIX 8 / 11 Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 26 a-chlorophyll abs/cm A1K 0,171 yes 0,117 0,118 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 1,90 yes 3 3 3,71 4,314 12, mg/l, Pt B2S 1,429 yes 16 3,89,121 32, mg/l, Pt N3S -0,18 yes ,76 11,2, Colour-2 mg/l, Pt A1V -0,076 yes 3 34,8 34,16 33,96 1, mg/l, Pt B2S -0,602 yes ,8 19,01,929 31, mg/l, Pt N3S -0,17 yes 76 70,1 64,4 7,64 27,6 36, conductivity ms/m A1J -0,28 yes 7,7 7,47 7,6 7,84 0,1671 2, ms/m B2H -0,267 yes ,1 17,84 2, ms/m N3H -0,769 yes,4,2,4,4 0,2988 2, ,64 yes 9,1 61,6 9, 8,,022 8, ,638 yes 48,1 4,8 47,6 48,27 3, ,741 yes 84,6 89,3 87,1 84,66 9,996 11, ,42 yes 77, ,9 77,2 4,393, ,900 yes ,8 8,223 3, ,33 yes ,2 17,27 3, Ntot µg/l A1N 0,789 yes , 6,21 6, ,269 yes ,6,0, ,841 yes ,02, P-PO4 µg/l A1P -0,89 yes 16,3,6,8,84 0, ,173 yes 23,1 23,3 22,7 22,9 1,193, ,700 yes 38,6 39,9,28 2,71 6, ph A1H 0,296 yes 7,2 2,8 7,28 7,2 7,241 0,0961 1, B2H -0,198 yes 7,79 2,6 7,77 7,8 7,798 0, , N3H 0,96 yes 7,19 2,8 7,2 7,19 7,19 0,82 1, Ptot µg/l A1P -0,736 yes 16,3,7 16,9 0,9672 6, ,36 yes 29,3 27, ,08 1,67, ,221 yes 73,7 69, ,14 4,491 6, Turbidity FNU A1S 1,671 yes 3,9 4,04 3,62 3,616 0,3878, FNU B2S -0,67 yes 1,98 1,8 2 1,983 0, , FNU N3S 0,944 yes 11,3 12,1 11,3 11,31 0,887 7, Laboratory 27 a-chlorophyll abs/cm A1K -0,13 yes 0,117 0,114 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V -1,90 yes 3 3 3,71 4,314 12, mg/l, Pt N3S -0,18 yes ,76 11,2, conductivity ms/m A1J -0,7 yes 7,7 7,43 7,6 7,84 0,1671 2, ms/m N3H -0,769 yes,4,2,4,4 0,2988 2, ,70 H 9, , 8,,022 8, ,394 yes 84,6 87,1 87,1 84,66 9,996 11, ,807 yes 77,4 8 79,9 76,9 77,2 4,393, ,314 H ,2 17,27 3, Ntot µg/l A1N 0,31 yes , 6,21 6, ,276 yes ,02, P-PO4 µg/l A1P -0,614 yes 16,3,8,8,84 0, ,80 yes 43,7 39,9,28 2,71 6, ph A1H 0,91 yes 7,2 2,8 7,31 7,2 7,241 0,0961 1, N3H 0,099 yes 7,19 2,8 7, 7,19 7,19 0,82 1, Ptot µg/l A1P -0,89 yes 16,3,6 16,9 0,9672 6, ,380 yes 73,7 7, ,14 4,491 6, Turbidity FNU A1S 0,780 yes 3,9 3,80 3,62 3,616 0,3878, FNU N3S 0,90 yes 11,3 11,8 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
37 LIITE 8 / 12 3 APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 28 a-chlorophyll abs/cm A1K,6 H 0,117 0,1791 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V -1,90 yes 3 3 3,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S -0,18 yes ,76 11,2, conductivity ms/m A1J -1,374 yes 7,7 7,31 7,6 7,84 0,1671 2, ms/m B2H -1,600 yes ,1 17,84 2, ms/m N3H 16,9 H,4 14,8,4,4 0,2988 2, ,248 yes 9,1 8 9, 8,,022 8, ,89 yes 48,1 4 47,6 48,27 3, ,986 yes 84, ,1 84,66 9,996 11, ,129 yes 77, ,9 77,2 4,393, ,000 yes ,8 8,223 3, ,33 yes ,2 17,27 3, Ntot µg/l A1N 0,263 yes 4 3 6, 6,21 6, ,342 yes ,6,0, ,081 yes ,02, P-PO4 µg/l A1P -1,9 yes 16,3,8,84 0, ,087 yes 23, ,7 22,9 1,193, ,000 yes 42 39,9,28 2,71 6, ph A1H 0,788 yes 7,2 2,8 7,33 7,2 7,241 0,0961 1, B2H -1,086 yes 7,79 2,6 7,68 7,8 7,798 0, , N3H 0,099 yes 7,19 2,8 7, 7,19 7,19 0,82 1, Ptot µg/l A1P -0,368 yes 16, ,9 0,9672 6, , yes 29, ,08 1,67, ,33 yes 73, ,14 4,491 6, Turbidity FNU A1S -0,94 yes 3,9 3,43 3,62 3,616 0,3878, FNU B2S 1, yes 1,98 2,28 2 1,983 0, , FNU N3S 1,888 yes 11,3 12,9 11,3 11,31 0,887 7, Laboratory 29 a-chlorophyll abs/cm A1K 0,171 yes 0,117 0,118 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S 0,278 yes ,76 11,2, conductivity ms/m A1J 0,317 yes 7,7 7,63 7,6 7,84 0,1671 2, ms/m B2H 0,9 yes 70 7, ,1 17,84 2, ms/m N3H 0,00 yes,4,3,4,4 0,2988 2, ,293 yes 9,1 60,4 9, 8,,022 8, ,82 yes 48,1 46,0 47,6 48,27 3, ,6 yes 84,6 74,1 87,1 84,66 9,996 11, ,226 yes 77,4 8 76,7 76,9 77,2 4,393, ,600 yes ,8 8,223 3, ,4 yes ,2 17,27 3, Ntot µg/l A1N -0,439 yes , 6,21 6, ,62 yes ,6,0, ,480 yes ,02, P-PO4 µg/l A1P -0,123 yes 16,3 16,2,8,84 0, ,472 yes 23,1 24,8 22,7 22,9 1,193, ,0 yes,4 39,9,28 2,71 6, ph A1H -0,099 yes 7,2 2,8 7,24 7,2 7,241 0,0961 1, B2H 0,198 yes 7,79 2,6 7,81 7,8 7,798 0, , N3H -0,199 yes 7,19 2,8 7,17 7,19 7,19 0,82 1, Ptot µg/l A1P -1,718 yes 16,3 14,9 16,9 0,9672 6, ,068 yes 29,3 29, ,08 1,67, ,081 yes 73,7 74, ,14 4,491 6, Turbidity FNU A1S 0,149 yes 3,9 3,63 3,62 3,616 0,3878, FNU B2S 1, yes 1,98 2,28 2 1,983 0, , FNU N3S 0,472 yes 11,3 11,7 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
38 36 LIITE APPENDIX 8 / 13 Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory conductivity ms/m A1J 0,449 yes 7,7 7,6 7,6 7,84 0,1671 2, ms/m B2H -1,67 yes , ,1 17,84 2, ms/m N3H 0,192 yes,4,4,4,4 0,2988 2, Ntot µg/l A1N 2,46 yes , 6,21 6, ,074 yes ,6,0, ,1 yes ,02, ph A1H 0,91 yes 7,2 2,8 7,31 7,2 7,241 0,0961 1, B2H 1,679 yes 7,79 2,6 7,96 7,8 7,798 0, , N3H 1,391 yes 7,19 2,8 7,33 7,19 7,19 0,82 1, Ptot µg/l A1P 0,89 yes 16, ,9 0,9672 6, ,478 yes 29, ,08 1,67, ,27 yes 73, ,14 4,491 6, Laboratory 31 conductivity ms/m A1J -3,118 H 7,7 6,98 7,6 7,84 0,1671 2, ms/m B2H 0,987 yes , ,1 17,84 2, ,098 yes 9,1 49,8 9, 8,,022 8, ,416 yes 48,1 46,6 47,6 48,27 3, ,970 yes 77,4 8 71,3 76,9 77,2 4,393, ,2 yes , ,8 8,223 3, Ntot µg/l A1N -1,009 yes , 6,21 6, ,62 yes ,6,0, P-PO4 µg/l A1P -7,7 H 16,3,8,84 0, ,974 H 23,1 22,7 22,9 1,193, ph A1H -1,872 yes 7,2 2,8 7,06 7,2 7,241 0,0961 1, B2H -0,198 yes 7,79 2,6 7,77 7,8 7,798 0, , Ptot µg/l A1P -0,123 yes 16,3 16,2 16,9 0,9672 6, ,706 yes 29,3 31, ,08 1,67, Laboratory 32 a-chlorophyll abs/cm A1K -0,222 yes 0,117 0,17 0,117 0,1169 0, , ,8 yes 77, ,9 77,2 4,393, ,191 yes ,2 17,27 3, Turbidity FNU A1S 0,446 yes 3,9 3,71 3,62 3,616 0,3878, FNU N3S -0,90 yes 11,3,8 11,3 11,31 0,887 7, Laboratory 33 N-NH4 0,969 yes 84,6 90,7 87,1 84,66 9,996 11, N-NO2+NO3 1,907 yes , ,2 17,27 3, ph N3H 0,000 yes 7,19 2,8 7,19 7,19 7,19 0,82 1, Turbidity FNU A1S 1,374 yes 3,9 3,96 3,62 3,616 0,3878, FNU N3S -0,319 yes 11,3 11,03 11,3 11,31 0,887 7, Laboratory 34 conductivity ms/m A1J -0,03 yes 7,7 7,6 7,6 7,84 0,1671 2, ms/m N3H 0,769 yes,4,6,4,4 0,2988 2, ,870 H 9,1 12 9, 8,,022 8, ,238 yes 84,6 98,8 87,1 84,66 9,996 11, ph A1H 0,394 yes 7,2 2,8 7,29 7,2 7,241 0,0961 1, N3H -0,497 yes 7,19 2,8 7,14 7,19 7,19 0,82 1, Turbidity FNU A1S 1,1 yes 3,9 3,90 3,62 3,616 0,3878, FNU N3S 0,118 yes 11,3 11,4 11,3 11,31 0,887 7, Laboratory 3 Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt N3S 0,278 yes ,76 11,2, conductivity ms/m A1J -0,03 yes 7,7 7,6 7,6 7,84 0,1671 2, ms/m N3H 0,000 yes,4,4,4,4 0,2988 2, ,023 yes 9,1 9,0 9, 8,,022 8, ,049 yes 84,6 71,6 87,1 84,66 9,996 11, Ntot µg/l A1N H 4 <0, 6, 6,21 6, ,3 H 11 0, ,02, ph A1H 0,000 yes 7,2 2,8 7,2 7,2 7,241 0,0961 1, N3H -0,96 yes 7,19 2,8 7,13 7,19 7,19 0,82 1, Ptot µg/l A1P 3,436 H 16,3 19,1 16,9 0,9672 6, ,7 H 73,7 42, ,14 4,491 6, Turbidity FNU A1S 1,0 yes 3,9 3,87 3,62 3,616 0,3878, FNU N3S 0,944 yes 11,3 12,1 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
39 LIITE 8 / APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 36 Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt N3S -1,296 yes ,76 11,2, Colour-2 mg/l, Pt A1V -0,762 yes 3 33,0 34,16 33,96 1, mg/l, Pt N3S -2,246 yes 76 0,4 64,4 7,64 27,6 36, conductivity ms/m A1J -0,7 yes 7,7 7,43 7,6 7,84 0,1671 2, ms/m N3H -2,038 yes,4 9,87,4,4 0,2988 2, ,632 yes 9,1 6,3 9, 8,,022 8, ,072 yes 84,6 77,8 87,1 84,66 9,996 11, ,907 yes 77,4 8 68,4 76,9 77,2 4,393, ,048 yes ,2 17,27 3, ph A1H -0,296 yes 7,2 2,8 7,22 7,2 7,241 0,0961 1, N3H -0,099 yes 7,19 2,8 7,18 7,19 7,19 0,82 1, Ptot µg/l A1P -1,9 yes 16,3,0 16,9 0,9672 6, ,706 yes 73,7 76, ,14 4,491 6, Turbidity FNU A1S -0,706 yes 3,9 3,4 3,62 3,616 0,3878, FNU N3S -0,34 yes 11, ,3 11,31 0,887 7, Laboratory 37 a-chlorophyll abs/cm A1K 0,000 yes 0,117 0,117 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V -7,619 M 3 3 3,71 4,314 12, mg/l, Pt B2S 19,290 M ,89,121 32, mg/l, Pt N3S -3,426 M ,76 11,2, conductivity ms/m A1J 02,00 H 7,7 76 7,6 7,84 0,1671 2, ms/m B2H -39, H 70, ,1 17,84 2, ms/m N3H -11,0 H,4 7,3,4,4 0,2988 2, ,6 yes 9,1 60,9 9, 8,,022 8, ,03 yes 48,1 1,9 47,6 48,27 3, ,742 yes 84,6 2 87,1 84,66 9,996 11, ,196 yes 77,4 8 70,6 76,9 77,2 4,393, ,0 yes ,8 8,223 3, ,291 yes ,2 17,27 3, Ntot µg/l A1N 0,132 yes 4 7 6, 6,21 6, ,63 yes ,6,0, ,961 yes ,02, P-PO4 µg/l A1P -0,123 yes 16,3 16,2,8,84 0, ,087 yes 23,1 23,0 22,7 22,9 1,193, ,0 yes 36,9 39,9,28 2,71 6, ph A1H 0,000 yes 7,2 2,8 7,2 7,2 7,241 0,0961 1, B2H -0,099 yes 7,79 2,6 7,78 7,8 7,798 0, , N3H -0,894 yes 7,19 2,8 7, 7,19 7,19 0,82 1, Ptot µg/l A1P -0,24 yes 16,3 16,1 16,9 0,9672 6, ,160 yes 29,3 27, ,08 1,67, ,16 yes 73,7 71, ,14 4,491 6, Turbidity FNU A1S 2,934 yes 3,9 4,38 3,62 3,616 0,3878, FNU B2S 1,061 yes 1,98 2,19 2 1,983 0, , FNU N3S 1,888 yes 11,3 12,9 11,3 11,31 0,887 7, Laboratory 38-3,181 yes 9,1 4 9, 8,,022 8, ,0 H 77, ,9 77,2 4,393, ph A1H -2,463 yes 7,2 2,8 7,0 7,2 7,241 0,0961 1, Laboratory 39 H 9,1 <0,000 9, 8,,022 8, ,600 H 77,4 8 76,9 77,2 4,393, ph A1H -1,478 yes 7,2 2,8 7,1 7,2 7,241 0,0961 1, Laboratory H 9,1 <0,000 9, 8,,022 8, ,0 H 77, ,9 77,2 4,393, Ntot µg/l A1N -2,46 yes , 6,21 6, ph A1H 0,98 yes 7,2 2,8 7,3 7,2 7,241 0,0961 1, Laboratory 41-8,370 H 9,1 22 9, 8,,022 8, ,61 H 77, ,9 77,2 4,393, ph A1H -2,266 yes 7,2 2,8 7,02 7,2 7,241 0,0961 1, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
40 38 LIITE APPENDIX 8 / Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 42-1,1 yes 9,1 4,0 9, 8,,022 8, ,23 H 77,4 8,0 76,9 77,2 4,393, P-PO4 µg/l A1P -1,9 yes 16,3,0,8,84 0, ph A1H 1,478 yes 7,2 2,8 7, 7,2 7,241 0,0961 1, Laboratory 43 Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S -0,37 yes 16 3,89,121 32, mg/l, Pt N3S -0,18 yes ,76 11,2, conductivity ms/m A1J -0,211 yes 7,7 7,3 7,6 7,84 0,1671 2, ms/m B2H 0,7 yes ,1 17,84 2, ms/m N3H 0,38 yes,4,,4,4 0,2988 2, ,1 yes 9,1 4 9, 8,,022 8, ,34 H 48, ,6 48,27 3, ,166 yes 84, ,1 84,66 9,996 11, ,486 yes 77, ,9 77,2 4,393, ,000 yes ,8 8,223 3, ,74 yes ,2 17,27 3, Ntot µg/l A1N -0,39 yes , 6,21 6, ,63 yes ,6,0, ,721 yes ,02, P-PO4 µg/l A1P -0,368 yes 16,3 16,0,8,84 0, ,19 yes 23,1 22, 22,7 22,9 1,193, ,70 yes 38, 39,9,28 2,71 6, ph A1H 0,394 yes 7,2 2,8 7,29 7,2 7,241 0,0961 1, B2H 0,889 yes 7,79 2,6 7,88 7,8 7,798 0, , N3H 0,000 yes 7,19 2,8 7,19 7,19 7,19 0,82 1, Ptot µg/l A1P -0,368 yes 16, ,9 0,9672 6, , yes 29, ,08 1,67, ,733 yes 73, ,14 4,491 6, Turbidity FNU A1S 0,223 yes 3,9 3,6 3,62 3,616 0,3878, FNU B2S 0,01 yes 1,98 1,99 2 1,983 0, , FNU N3S -0,118 yes 11,3 11,2 11,3 11,31 0,887 7, Laboratory 44 1,484 yes 9,1 6,68 9, 8,,022 8, ,231 yes 48,1 6, 47,6 48,27 3, ,917 yes 84,6 3,11 87,1 84,66 9,996 11, ,174 yes 77,4 8 76,86 76,9 77,2 4,393, ,312 yes , ,8 8,223 3, ,1 yes , ,2 17,27 3, Ntot µg/l A1N 0,623 yes 4 318, 6, 6,21 6, ,811 yes 46 79, 48 44,6,0, ,622 yes , ,02, P-PO4 µg/l A1P -0,699 yes 16,3,73,8,84 0, ,02 yes 23,1 22,2 22,7 22,9 1,193, ,770 H 28,46 39,9,28 2,71 6, ph A1H -0,42 yes 7,2 2,8 7,19 7,2 7,241 0,0961 1, B2H -0,148 yes 7,79 2,6 7,77 7,8 7,798 0, , N3H -1,03 yes 7,19 2,8 7,084 7,19 7,19 0,82 1, Ptot µg/l A1P -4,44 H 16,3 12,67 16,9 0,9672 6, ,724 H 29,3 39, 29 29,08 1,67, ,763 H 73,7 48, ,14 4,491 6, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
41 LIITE 8 / APPENDIX Analyte Unit Sample z-graphics Z- value Outl Assigned test OK value 2* Targ SD% Lab's result Md. Mean SD SD% Passed Outl. failed Missing Num of labs Laboratory 4 a-chlorophyll abs/cm A1K -0, yes 0,117 0,18 0,117 0,1169 0, , Colour-1 mg/l, Pt A1V 0,000 yes ,71 4,314 12, mg/l, Pt B2S 1,429 yes 16 3,89,121 32, mg/l, Pt N3S -0,18 yes ,76 11,2, conductivity ms/m A1J 2,99 yes 7,7 8,13 7,6 7,84 0,1671 2, ms/m B2H -1,397 yes , ,1 17,84 2, ms/m N3H 1,692 yes,4,84,4,4 0,2988 2, ,6 yes 9,1 60,9 9, 8,,022 8, ,222 yes 48,1 47,3 47,6 48,27 3, ,804 yes 84,6 89,7 87,1 84,66 9,996 11, ,327 yes 77,4 8 67,1 76,9 77,2 4,393, ,2 H , ,8 8,223 3, ,666 H , ,2 17,27 3, Ntot µg/l A1N 0,013 yes 4 4,3 6, 6,21 6, ,222 yes 46 36, ,6,0, ,8 yes ,02, P-PO4 µg/l A1P 0,24 yes 16,3 16,,8,84 0, ,212 yes 23,1 24, 22,7 22,9 1,193, ,0 yes 39,2 39,9,28 2,71 6, ph A1H -0,099 yes 7,2 2,8 7,24 7,2 7,241 0,0961 1, B2H -0,790 yes 7,79 2,6 7,71 7,8 7,798 0, , N3H 0,000 yes 7,19 2,8 7,19 7,19 7,19 0,82 1, Ptot µg/l A1P -1,227 yes 16,3,3 16,9 0,9672 6, ,4 yes 29,3 28, ,08 1,67, ,89 yes 73,7 70, ,14 4,491 6, Turbidity FNU A1S -2,377 yes 3,9 2,9 3,62 3,616 0,3878, FNU B2S 0,1 yes 1,98 2,00 2 1,983 0, , FNU N3S 0,472 yes 11,3 11,7 11,3 11,31 0,887 7, Outlier test failed: C - Cohcran, G1 - Grubbs(1-outlier algorithm), G2 - Grubbs(2-outliers algorithm), H - Hampel, M - manual SYKE - Interlaboratory comparison test 2/13
42 LIITE 9. RESULTS AND THEIR UNCERTAINTY ESTIMATES APPENDIX 9. LIITE APPENDIX 9 / 1 a-chlorophyll A1K 0,14 0,14 0,13 0,13 0,12 abs/cm 0,12 0,1 0,11 0, 0,1 0,09 0,09 2 Laboratory 3 4 Colour-1 A1V mg/l, Pt Laboratory 3 4 Colour-1 B2S 2 mg/l, Pt 2 Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
43 LIITE APPENDIX 9 / 2 41 Colour-1 N3S mg/l, Pt Laboratory 3 4 Colour-2 A1V mg/l, Pt Laboratory 2 3 Colour-2 B2S 3 2 mg/l, Pt Laboratory 2 SYKE - Interlaboratory comparison test 2/13
44 42 LIITE APPENDIX 9 / 3 Colour-2 N3S mg/l, Pt Laboratory 2 3 conductivity A1J 8,4 8,2 8 7,8 ms/m 7,6 7,4 7,2 7 6,8 2 Laboratory 3 4 conductivity B2H ms/m Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
45 LIITE APPENDIX 9 / 4 43 conductivity N3H ms/m 11,6 11,4 11,2 11,8,6,4,2 9,8 9,6 9,4 9,2 2 Laboratory 3 4 N-NH4 A1N µg/l Laboratory 3 4 N-NH4 B2N 6 60 µg/l Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
46 44 LIITE APPENDIX 9 / N-NH4 N3N µg/l Laboratory 3 4 N-NO2+NO3 A1N µg/l Laboratory 3 4 N-NO2+NO3 B2N µg/l Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
47 LIITE APPENDIX 9 / 6 4 N-NO2+NO3 N3N µg/l Laboratory 3 4 Ntot A1N µg/l Laboratory 3 4 Ntot B2N µg/l Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
48 46 LIITE APPENDIX 9 / 7 Ntot N3N µg/l Laboratory 3 4 P-PO4 A1P µg/l Laboratory 3 4 P-PO4 B2P µg/l Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
49 LIITE APPENDIX 9 / 8 47 P-PO4 N3P µg/l Laboratory 3 4 ph A1H 7,7 7,6 7, 7,4 7,3 7,2 7,1 7 6,9 6,8 2 Laboratory 3 4 ph B2H 8,2 8,1 8 7,9 7,8 7,7 7,6 7, 7,4 7,3 2 Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
50 48 LIITE APPENDIX 9 / 9 ph N3H 7,6 7, 7,4 7,3 7,2 7,1 7 6,9 6,8 6,7 2 Laboratory 3 4 Ptot A1P µg/l Laboratory 3 4 Ptot B2P µg/l Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
51 LIITE APPENDIX 9 / 49 Ptot N3P µg/l Laboratory 3 4 Turbidity A1S FNU 4,8 4,6 4,4 4,2 4 3,8 3,6 3,4 3,2 3 2,8 2,6 2,4 2 Laboratory 3 4 Turbidity B2S 2,8 2,6 2,4 2,2 FNU 2 1,8 1,6 1,4 1,2 1 2 Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
52 0 LIITE APPENDIX 9 / 11 Turbidity N3S FNU Laboratory 3 4 SYKE - Interlaboratory comparison test 2/13
53 1 LIITE APPENDIX / 1 LIITE. SUMMARY OF THE z SCORES APPENDIX. Analyte Sample\Lab a-chlorophyll A1K S U S. S.. S.. S S S. S S S S S S S S S Colour-1 A1V S S. S... S U.. S... S S. S S S.. B2S S S. S... S u.. S... S S. S q S.. N3S S S. S... S Q.. Q... S S. S S S.. Colour-2 A1V.... S S.. S... S U B2S.... S Q.. q... S S N3S.... S S... S U conductivity A1J S S. S S u. S S S S S... S S S S S S S S B2H S S. S S... S. S S... S S q S S u S S N3H S S. S S u.. S S S S... Q S q S S S S S N-NH4 A1N U S S S S U U U. S S S S... S S S S S U S B2N Q S S S Q. S... S S S. S S S S U S S u S N3N S q. S S U S S. S S S... Q S S S S q S S N-NO2+NO3 A1N S S U. S U S S U S S S S.. S S S S S S S Q B2N S S Q. S. S. S. S S S. S S S S S S U S u N3N S S. U S u S U S S S S... S S S S S S S S Ntot A1N S S S. S. S S. S S S... S S S S S S S S B2N S S S. S. S... S S S. u S S S S S S S S N3N S S.. S. S S. S S S... S S S S S S S S P-PO4 A1P S S S. S u S u S S S S q.. S S S S S S S S B2P S S S. S. S. S. S S U. S S S S S S S q U N3P u S.. Q U S u S S S q... S S u S S Q S U ph A1H S S Q S S S. S S S S S... S S S S S S S S B2H S S S Q S.. S S. S S u.. S S S S S S S S N3H S S. Q S q. S S S Q S... S S S S S S S S Ptot A1P S S S. S.. Q. S S S. S. S S S S S S u S B2P S S S. S..... S S.. S S S S S S S u S N3P S S.. S.. q. S Q S. S. S S S S S Q S Q Turbidity A1S S.. S S.. S S S S S.. S S S S S S S S U B2S S.. U S... S. u Q.. S S S S S S S S S N3S S.. u S... S S q S... S S S S S S S S % Accredited yes yes yes yes yes yes yes yes yes yes yes yes yes yes yes yes yes yes Analyte Sample\Lab % a-chlorophyll A1K S S S S U S.. S.... S S 92 Colour-1 A1V S S S S S S..... S S u..... S. S 91 B2S S U S. S S U..... S. S 79 N3S S S S S S S..... S S u..... S. S 86 Colour-2 A1V.. S S B2S.. S N3S.. S q conductivity A1J S S S S S S S u.. S S S U..... S. Q 88 B2H S S S. S S S S..... u..... S. S 88 N3H S S S S U S S... S S q u..... S. S 80 N-NH4 A1N S S S U S S. q.. U S S S u.. u S S S S 72 B2N S S S. S S. S..... S..... u Q S 79 N3N S S S S S S... S Q q S Q..... S Q S 7 N-NO2+NO3 A1N S S S S S S. S S... q q U U U U u S S u 68 B2N S S S. S S. S..... q..... S S u 82 N3N S S S u S S.. S S.. S S..... S S u 84 Ntot A1N S S S S S S Q S..... S.. q.. S S S 93 B2N S S S. S S S S..... S..... S S S 96 N3N S S S S S S S.... u. S..... S S S 96 P-PO4 A1P S S S S S S. u..... S.... S S S S 88 B2P S S S. S S. U..... S..... S S S 86 N3P S Q S S S S S..... S u S 64 ph A1H S S S S S S S S.. S S S S q S S q S S S S 92 B2H S S S. S S S S..... S..... S S S 93 N3H S S S S S S S.. S S S S S..... S S S 91 Ptot A1P S S S S S S S S... U S S..... S u S 87 B2P S S S. S S S S..... S..... S U S 92 N3P S S S S S S S.... u S S..... S u S 79 Turbidity A1S S S S S S S.. S S S S S Q..... S. q 90 B2S u S S. S S S..... S. S 83 N3S S S S S S S.. S S S S S S..... S. S 93 % Accredited yes yes yes yes yes yes yes yes yes yes yes yes yes yes SYKE - Interlaboratory comparison test 2/13
54 LIITE APPENDIX / 2 2 Analyte Sample\Lab % %* - percentage of satisfactory results Totally satisfactory, % In all: 8 In accredited: 87 In non-accredited: 72 SYKE - Interlaboratory comparison test 2/13
55 ANALYTICAL METHODS 3 APPENDIX 11.1 Analyte Code Method Chlorophyll a 1 SFS 772 or similar (ethanol extraction + spectrophotometric measurement) 2 Other method ph 1 Electrode for low ionic waters 2 Universal electrode 3 Other electrode Conductivity 1 EN Other method N NH4 1 SFS 32 or similar indophenol blue method manual measurement 2 EN ISO or similar CFA- or FIA-method 3 Salicylate method application for Aquachem tecnique 4 Other method N NO3+NO2 1 SFS or similar spectrophotometric measurement 2 EN ISO 1339 or similar FIA or CFA- method 3 Cd-reduction, Aquachem technique based with sulfanilamide method 4 Hydrazine reduction, Aquachem technique based with sulfanilamide method EN ISO 4 or similar IC- or HPLC-method 6 Other method N tot 1 EN ISO SFS 0 or comparable modified Kjeldahl method 3 Other method P PO4 1 EN ISO 6878 (replaced EN 1189) 2 SFS 2 (withdrawn) 3 EN ISO 681 or similar automatic ammonium molybdate method (FIA, CFA) 4 Ammonium molybdate method with Aquachem technique Other method P tot 1 EN ISO 6878 (replaced EN 1189) 2 SFS 26 (withdrawn) 3 EN ISO 681 or comparable automatic ammonium molybdate method (FIA, CFA) 4 Ammonium molybdate method with Aquachem technique Tube method (e.g Hach, Lange) 6 EN ISO 1188 ICP-MS-method 7 Other method Turbidity 1 EN ISO 7027 or similar diffused radiation measurement, unit FNU 2 EN ISO 7027 or similar attenuation or a radiant flux measurement, unit FAU 3 Other method Colour-1 1 EN ISO 7887 or similar visual comparator method 2 Other method Colour-2 1 EN ISO 7887 or similar spectrophotometric method 2 Other method
56 LIITE APPENDIX 11.2 / 1 4 LIITE RESULTS GROUPED ACCORDING TO THE MEASUREMENT METHODS APPENDIX 11.2.Method code - see Appendix 11.1 a-chlorophyll A1K abs/cm 0,14 0,14 0,13 0,13 0,12 0,12 0,1 0,11 0, 0,1 0,09 0,09 Meth 1 Meth 2 Colour-1 A1V mg/l, Pt Meth 1 Colour-1 B2S mg/l, Pt Meth 1 SYKE - Interlaboratory comparison test 2/13
57 LIITE APPENDIX 11.2 / 2 Colour-1 N3S mg/l, Pt Meth 1 Colour-2 A1V mg/l, Pt Meth 1 Colour-2 B2S 3 2 mg/l, Pt Meth 1 SYKE - Interlaboratory comparison test 2/13
58 LIITE APPENDIX 11.2 / 3 6 Colour-2 N3S mg/l, Pt Meth 1 conductivity A1J 8,4 8,2 8 7,8 ms/m 7,6 7,4 7,2 7 6,8 Meth 1 Meth 2 conductivity B2H ms/m Meth 1 SYKE - Interlaboratory comparison test 2/13
59 7 LIITE APPENDIX 11.2 / 4 conductivity N3H ms/m 11,6 11,4 11,2 11,8,6,4,2 9,8 9,6 9,4 9,2 Meth 1 Meth 2 N-NH4 A1N µg/l Meth 1 Meth 2 Meth 3 Meth 4 N-NH4 B2N 6 60 µg/l Meth 1 Meth 2 Meth 3 Meth 4 SYKE - Interlaboratory comparison test 2/13
60 LIITE APPENDIX 11.2 / 8 N-NH4 N3N 1 1 µg/l Meth 1 Meth 2 Meth 3 Meth 4 N-NO2+NO3 A1N µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth Meth 6 N-NO2+NO3 B2N µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth Meth 6 SYKE - Interlaboratory comparison test 2/13
61 9 LIITE APPENDIX 11.2 / 6 N-NO2+NO3 N3N µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth Meth 6 Ntot A1N µg/l Meth 1 Meth 3 Meth Meth 6 Ntot B2N µg/l Meth 1 Meth 3 Meth SYKE - Interlaboratory comparison test 2/13
62 LIITE APPENDIX 11.2 / 7 60 Ntot N3N µg/l Meth 1 Meth 3 Meth P-PO4 A1P µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth P-PO4 B2P µg/l Meth 1 Meth 2 Meth 3 Meth 4 SYKE - Interlaboratory comparison test 2/13
63 61 LIITE APPENDIX 11.2 / 8 P-PO4 N3P µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth ph A1H 7,7 7,6 7, 7,4 7,3 7,2 7,1 7 6,9 6,8 Meth 1 Meth 2 Meth 3 ph B2H 8,2 8,1 8 7,9 7,8 7,7 7,6 7, 7,4 7,3 Meth 1 Meth 2 Meth 3 SYKE - Interlaboratory comparison test 2/13
64 LIITE APPENDIX 11.2 / 9 62 ph N3H 7,6 7, 7,4 7,3 7,2 7,1 7 6,9 6,8 6,7 Meth 1 Meth 2 Ptot A1P µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth 6 Meth 7 Ptot B2P µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth 6 Meth 7 SYKE - Interlaboratory comparison test 2/13
65 63 LIITE APPENDIX 11.2 / Ptot N3P µg/l Meth 1 Meth 2 Meth 3 Meth 4 Meth 6 Meth 7 Turbidity A1S FNU 4,8 4,6 4,4 4,2 4 3,8 3,6 3,4 3,2 3 2,8 2,6 2,4 Meth 1 Meth 2 Meth 3 Turbidity B2S 2,8 2,6 2,4 2,2 FNU 2 1,8 1,6 1,4 1,2 1 Meth 1 Meth 3 SYKE - Interlaboratory comparison test 2/13
66 LIITE APPENDIX 11.2 / Turbidity N3S FNU Meth 1 Meth 2 Meth 3 SYKE - Interlaboratory comparison test 2/13
67 6 APPENDIX 12 EXAMPLES OF THE REPORTED MEASURENT UNCERTAINTIES UC No: the procedure used for the estimation of the expanded measurement uncertainty at 9 % confidence level (IQC = internal quality control) 1. Using the IQC data only from synthetic control sample and/or CRM (X-chart), see e.g. NORDTEST TR 37 1). Using MUkit measurement uncertainty software 3). - 4 laboratories 2. Using the IQC data only from synthetic control sample and/or CRM (X-chart), see e.g. NORDTEST TR 37 1). Without MUkit measurement uncertainty software 3). - 6 laboratories 3. Using the IQC data from synthetic sample (X-chart) together with the IQC data from routine sample replicates (R-chart or r%-chart), see e.g. NORDTEST TR 37 1). Using MUkit software 3). - 4 laboratories 4. Using the IQC data from synthetic sample (X-chart) together with the IQC data from routine sample replicates (R-chart or r%-chart), see e.g. NORDTEST TR 37 1). Without MUkit software 3). - laboratories. Using the IQC data and the results obtained in proficiency tests, see e.g. NORDTEST TR 37 1). Using MUkit software 3) Using the IQC data and the results obtained in proficiency tests, see e.g. NORDTEST TR 37 1). Without MUkit software 3). - laboratories 7. Using the data obtained in method validation. Using MUkit software 3) Using the data obtained in method validation. Without MUkit software 3). - 7 laboratories 9. Using the "modeling approach" (GUM Guide or EURACHEM Guide Quantifying Uncertainty in Analytical Measurement) 2) - -. Other procedure, please specify - 2 laboratories 11. No uncertainty estimation - 1) 2) 3) The software is freely downloadable on SYKE calibration and contract laboratory website: Data/Calibration_services_and_contract_laboratory
68 66 LIITE APPENDIX 12 / 1 LIITE 12. APPENDIX 12. conductivity B2H Uncertainty, % Meth2 Meth3 Meth4 Meth Meth6 Meth8 N-NH4 N3N 3 Uncertainty, % 2 Meth1 Meth2 Meth3 Meth4 Meth Meth6 Meth8 N-NO2+NO3 N3N 2 Meth1 Meth2 Meth3 Meth4 Meth Uncertainty, % Meth6 Meth8 SYKE - Interlaboratory comparison test 2/13
69 LIITE APPENDIX 12 / 2 67 Ntot B2N Uncertainty, % Meth2 Meth3 Meth4 Meth Meth6 Meth8 ph N3H Uncertainty, % Meth1 Meth2 Meth3 Meth4 Meth Meth6 Meth8 Meth P-PO4 N3P 2 Meth1 Meth2 Meth3 Meth4 Meth Uncertainty, % Meth6 Meth8 SYKE - Interlaboratory comparison test 2/13
70 68 LIITE APPENDIX 12 / 3 Ptot N3P Uncertainty, % Meth1 Meth2 Meth3 Meth4 Meth Meth6 Meth8 Turbidity B2S 3 Meth2 Meth3 Meth4 Meth6 Meth8 Uncertainty, % Meth Meth11 2 SYKE - Interlaboratory comparison test 2/13
71 Documentation page 69 Publisher Finnish Environment Institute (SYKE) Date June 13 Author(s) Kaija Korhonen-Ylönen, Teemu Näykki, Mirja Leivuori, Keijo Tervonen, Sari Lanteri and Markku Ilmakunnas Title of publication Proficiency test SYKE 2/13 Chlorophyll a, colour, conductivity, nutrients, ph and turbidity in natural waters Parts of publication/ other project publications Abstract Proftest SYKE carried out the proficiency test for analysis of chlorophyll, colour, conductivity, nutrients, ph and turbidity in natural waters in February 13. In total 44 laboratories participated in this proficiency test. The sample types were: artificial water sample, coastal water and natural water. Calculated concentrations or the robust mean of the results reported by the participant were used as the assigned values for measurements. The evaluation of the performance of the participants was carried out using z score. In some cases the evaluation of the performance was not possible e.g. due to the low number of the participants. In total, 8 % of the total data in this proficiency test were satisfactory when the deviations of % from the assigned values were accepted. Keywords Publication series and number Theme of publication water analysis, nutrients, ph, conductivity, colour, turbidity, water, environmental laboratories, proficiency test, interlaboratory comparisons Reports of Finnish Environment Institute /13 Project name and number, if any Financier/ commissioner Project organization ISSN ISBN (online) (PDF) No. of pages Language 71 English Restrictions Public Price For sale at/ distributor Financier of publication Printing place and year Helsinki 13 Other information The publication is available only on the internet: / helda.helsinki.fi/syke Finnish Environment Institute, P.O. Box 1, FI-0021 Helsinki, Finland
72 Kuvailulehti Julkaisija Suomen ympäristökeskus (SYKE) Julkaisuaika Kesäkuu Tekijä(t) Kaija Korhonen-Ylönen, Teemu Näykki, Mirja Leivuori, Keijo Tervonen, Sari Lanteri ja Markku Ilmakunnas Julkaisun nimi Proficiency test SYKE 2/13 Chlorophyll a, colour, conductivity, nutrients, ph and turbidity in natural waters Julkaisun osat/ muut saman projektin tuottamat julkaisut Tiivistelmä Proftest SYKE järjesti pätevyyskokeen luonnonvesiä analysoiville laboratorioille helmikuussa 13. Testattavina suureina olivat a-klorofylli, ravinteet, ph sameus, sähkönjohtavuus ja väri. Näytteenä olivat synteettinen vesinäyte, rannikkovesi ja jokivesi. Pätevyyskokeeseen osallistui yhteensä 44 laboratoriota. Mittaussuureen vertailuarvona käytettiin laskennallista arvoa tai osallistujien tulosten robustia keskiarvoa. Pätevyyden arvioimisessa käytettiin z-arvoa. Kokonaisuudessaan hyväksyttäviä tuloksia oli 8 %, kun tulosten sallittiin poiketa 2,6 3 % vertailuarvosta. Asiasanat Julkaisusarjan nimi ja numero Julkaisun teema vesianalyysi, ravinteet, a-klorofylli, väri, sähkönjohtavuus, ph, sameus, vesi- ja ympäristölaboratoriot, pätevyyskoe, laboratorioiden välinen vertailumittaus Reports of Finnish Environment Institute /13 Projektihankkeen nimi ja projektinumero Rahoittaja/ toimeksiantaja Projektiryhmään kuuluvat organisaatiot ISSN ISBN (verkkoj.) (PDF) Sivuja Kieli 71 Englanti Luottamuksellisuus Julkinen Hinta Julkaisun myynti/ jakaja Julkaisun kustantaja Julkaisu on saatavana vain internetistä: / helda.helsinki.fi/syke Suomen ympäristökeskus, PL 1, 0021 Helsinki Painopaikka ja -aika Helsinki 13 Muut tiedot
73 Presentationsblad 71 Utgivare Finlands Miljöcentral (SYKE) Datum Juni 13 Författare Kaija Korhonen-Ylönen, Teemu Näykki, Mirja Leivuori, Keijo Tervonen, Sari Lanteri och Markku Ilmakunnas Publikationens titel Proficiency test SYKE 2/13 Chlorophyll a, colour, conductivity, nutrients, ph and turbidity in natural waters Publikationens delar/ andra publikationer inom samma projekt Sammandrag Under februari 13 genomförde Proftest SYKE en provningsjämförelse, som omfattade bestämningen av a-klorofyll, näringsämnen (N NH4, N NO3+NO2, N tot, P PO4, P tot ), ph, ledningsförmåga, grumlighet och färg i naturvatten. Proven sändes ut till 44 laboratorier. Som referensvärde av analytens koncentration användes det teoretiska värdet eller robust medelvärdet av deltagarnas resultat. Resultaten värderades med hjälp av z-värden. I jämförelsen var 8 % av alla resultaten tillfredsställande, när 2,6 3 % totalavvikelsen från referensvärdet accepterades. Nyckelord vattenanalyser, grumlighet, näringsämne, N NH4, N NO3+NO2, N tot, P PO4, P tot, ph, ledningsförmåga, a- klorofyll, provningsjämförelse, vatten- och miljölaboratorier Reports of Finnish Environment Institute /13 Publikationsserie och nummer Publikationens tema Projektets namn och nummer Finansiär/ uppdragsgivare Organisationer i projektgruppen ISSN ISBN (online) (PDF) Sidantal Språk 71 Engelska Offentlighet Offentlig Pris Beställningar/ distribution Förläggare Tryckeri/ tryckningsort och år Publicationen finns tillgänglig på internet / helda.helsinki.fi/syke Finlands Miljöcentral, PB 1, 0021 Helsingfors Helsingfors 13 Övriga uppgifter
74 PROFICIENCY TEST SYKE 2/13 ISBN (PDF) ISSN (online) SYKE FINNISH ENVIRONMENT INSTITUTE
Interlaboratory Proficiency Test 03/2018
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 11 218 Interlaboratory Proficiency Test 3/218 Alkalinity, ph, nutrients and conductivity in natural waters Mirja Leivuori, Riitta Koivikko, Mika Sarkkinen,
Interlaboratory Proficiency Test 03/2016
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 18 2016 Interlaboratory Proficiency Test 03/2016 Alkalinity, ph, nutrients and conductivity in natural waters Mirja Leivuori, Riitta Koivikko, Teemu Näykki,
Interlaboratory Proficiency Test 02/2017
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 4 7 Interlaboratory Proficiency Test /7 Chlorophyll a, colour, conductivity, nutrients, ph and turbidity in natural waters Mirja Leivuori, Riitta Koivikko,
Interlaboratory Proficiency Test 02/2019
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 23 2019 Interlaboratory Proficiency Test 02/2019 Chlorophyll a, colour, conductivity, nutrients, ph and turbidity in natural waters Riitta Koivikko, Mirja Leivuori,
Proficiency Test SYKE 10/2011
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 11 12 Proficiency Test SYKE /11 Heavy metals in surface waters Mirja Leivuori, Kaija KorhonenYlönen, Timo SaraAho, Teemu Näykki, Keijo Tervonen, Sari Lanteri and
Interlaboratory Proficiency Test 07/2016
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 36 016 Interlaboratory Proficiency Test 07/016 Chlorophyll a, oxygen, salinity, SiO, TIC and TOC in natural waters Riitta Koivikko, Mirja Leivuori, Teemu Näykki,
Interlaboratory Proficiency Test NW 4/2014
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 6 014 Interlaboratory Proficiency Test NW 4/014 Oxygen, a-chlorophyll, salinity, SiO, TIC and TOC in natural waters Mirja Leivuori, Teemu Näykki, Mika Sarkkinen,
Interlaboratory Proficiency Test 01/2017
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 11 2017 Interlaboratory Proficiency Test 01/2017 Swimming pool water analysis Mirja Leivuori, Sami Tyrväinen, Mika Sarkkinen, Riitta Koivikko, Keijo Tervonen,
Interlaboratory Proficiency Test 09/2014
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 5 2015 Interlaboratory Proficiency Test 09/2014 Oil hydrocarbons in water and soil Jari Nuutinen, Riitta Koivikko, Mirja Leivuori and Markku Ilmakunnas Finnish
Interlaboratory Proficiency Test 01/2018
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 10 2018 Interlaboratory Proficiency Test 01/2018 Swimming pool water analysis Mirja Leivuori, Sami Tyrväinen, Mika Sarkkinen, Riitta Koivikko, Keijo Tervonen,
Proficiency Test SYKE 9/2012
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 8 2013 Proficiency Test SYKE 9/2012 Oil hydrocarbons in water and soil Kaija Korhonen-Ylönen, Jari Nuutinen, Mirja Leivuori and Markku Ilmakunnas Finnish Environment
MIKES, Julkaisu J3/2000 MASS COMPARISON M3. Comparison of 1 kg and 10 kg weights between MIKES and three FINAS accredited calibration laboratories
MITTATEKNIIKAN KESKUS CENTRE FOR METROLOGY AND ACCREDITATION Julkaisu J3/2000 MASS COMPARISON M3 Comparison of 1 kg and 10 kg weights between MIKES and three FINAS accredited calibration laboratories Kari
Interlaboratory Proficiency Test 08/2014
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 7 5 Interlaboratory Proficiency Test 8/ Metals and mercury in waters Mirja Leivuori, Riitta Koivikko, Timo SaraAho, Teemu Näykki, Katarina Björklöf, Keijo Tervonen,
Proficiency Test SYKE 8a/2010
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 0 Proficiency Test SYKE a/0 Volatile organic compounds in water and soil Kaija Korhonen-Ylönen, Jari Nuutinen, Mirja Leivuori and Markku Ilmakunnas Finnish Environment
Proficiency Test SYKE 8/2013
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 4 2014 Proficiency Test SYKE 8/2013 Radon in ground water Katarina Björklöf, Reko Simola, Kaija Korhonen-Ylönen, Keijo Tervonen, Sari Lanteri and Markku Ilmakunnas
Interlaboratory Proficiency Test 08/2017
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 6 17 Interlaboratory Proficiency Test 8/17 Domestic water measurements Katarina Björklöf, Mirja Leivuori, Mika Sarkkinen, Timo Sara-Aho, Keijo Tervonen, Sari
Interlaboratory Proficiency Test 08/2015
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 6 Interlaboratory Proficiency Test 8/5 Metals in waste water and sludge Riitta Koivikko, Mirja Leivuori, Teemu Näykki, Timo SaraAho, Keijo Tervonen, Sari Lanteri,
Interlaboratory Proficiency Test 04/2019
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 5 9 Interlaboratory Proficiency Test /9 Metals in natural water and sediment Mirja Leivuori, Riitta Koivikko, Timo Sara-Aho, Teemu Näykki, Keijo Tervonen, Sari
Interlaboratory Proficiency Test 6/2014
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 1 2015 Interlaboratory Proficiency Test 6/2014 Gross and net calorific values in fuels Mirja Leivuori, Minna Rantanen, Katarina Björklöf, Keijo Tervonen, Sari Lanteri
Interlaboratory Proficiency Test 06/2015
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 37 2015 Interlaboratory Proficiency Test 06/2015 Gross and net calorific values in fuels Mirja Leivuori, Minna Rantanen, Katarina Björklöf, Keijo Tervonen,
Interlaboratory Proficiency Test 10/2016
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 8 7 Interlaboratory Proficiency Test /6 Metals in waste water and recycled material Mirja Leivuori, Riitta Koivikko, Timo SaraAho, Teemu Näykki, Keijo Tervonen,
Interlaboratory Proficiency Test 10/2018
REPORTS OF THE FINNISH ENVIRONMENT INSTITUTE 9 Interlaboratory Proficiency Test /8 Metals in waste water and compost Mirja Leivuori, Riitta Koivikko, Timo SaraAho, Teemu Näykki, Aija Pelkonen, Keijo Tervonen,
SYKE Proficiency Test 3/2010
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 1 11 SYKE Proficiency Test 3/ Metals in waters and sediment Mirja Leivuori, Kaija Korhonen,Timo SaraAho, Teemu Näykki, Olli Järvinen, Keijo Tervonen, Sari Lanteri
SYKE Proficiency Test 5/2009
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 2 2010 SYKE Proficiency Test /2009 Gross and net calorific value in fuels Mirja Leivuori, Irma Mäkinen, Minna Rantanen, Minna Salonen, Kaija Korhonen and Markku
SYKE Proficiency Test 6/2012
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 4 2013 SYKE Proficiency Test 6/2012 Gross and net calorific values in fuels Mirja Leivuori, Minna Rantanen, Katarina Björklöf, Keijo Tervonen, Sari Lanteri and
Capacity Utilization
Capacity Utilization Tim Schöneberg 28th November Agenda Introduction Fixed and variable input ressources Technical capacity utilization Price based capacity utilization measure Long run and short run
SYKE Proficiency Test 4/2009
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 28 2009 SYKE Proficiency Test 4/2009 Metals in waters and soils Mirja Leivuori, Kaija Korhonen, Olli Järvinen, Teemu Näykki, Timo SaraAho, Keijo Tervonen, Sari
Proficiency Test SYKE 3/2011
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 22 2011 Proficiency Test SYKE 3/2011 Metals in water and sludge Mirja Leivuori, Kaija KorhonenYlönen, Timo SaraAho, Teemu Näykki, Keijo Tervonen, Sari Lanteri and
AKKREDITOITU TESTAUSLABORATORIO ACCREDITED TESTING LABORATORY LUONNONVARAKESKUS VANTAA, ROVANIEMI
T203/M13/2014 Liite 1 / Appendix 1 Sivu / Page 1(5) AKKREDITOITU TESTAUSLABORATORIO ACCREDITED TESTING LABORATORY LUONNONVARAKESKUS VANTAA, ROVANIEMI NATURAL RESOURCES INSTITUTE FINLAND VANTAA, ROVANIEMI
TEST REPORT Nro VTT-S Air tightness and strength tests for Furanflex exhaust air ducts
TEST REPORT Nro VTT-S-04515-08 19.5.008 Air tightness and strength tests for Furanflex exhaust air ducts Requested by: Hormex Oy TEST REPORT NRO VTT-S-04515-08 1 () Requested by Order Hormex Oy Linnanherrankuja
Efficiency change over time
Efficiency change over time Heikki Tikanmäki Optimointiopin seminaari 14.11.2007 Contents Introduction (11.1) Window analysis (11.2) Example, application, analysis Malmquist index (11.3) Dealing with panel
SYKE Proficiency Test 5/2010
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 4 2011 SYKE Proficiency Test 5/2010 Gross and net calorific values in flues Mirja Leivuori, Minna Rantanen, Kaija Korhonen-Ylönen and Markku Ilmakunnas Finnish
Asiakaspalautteen merkitys laboratoriovirheiden paljastamisessa. Taustaa
Asiakaspalautteen merkitys laboratoriovirheiden paljastamisessa Paula Oja, TtT Laboratorio, Oulun yliopistollinen sairaala Potilasturvallisuustutkimuksen päivät 26. 27.1.2011 1 Taustaa Laboratorion tulee
16. Allocation Models
16. Allocation Models Juha Saloheimo 17.1.27 S steemianalsin Optimointiopin seminaari - Sks 27 Content Introduction Overall Efficienc with common prices and costs Cost Efficienc S steemianalsin Revenue
Laboratorioiden välinen pätevyyskoe 6/2011
SUOMEN YMPÄRISTÖKESKUKSEN RAPORTTEJA 1 2012 Laboratorioiden välinen pätevyyskoe 6/2011 Radon pohjavedestä Kaija Korhonen-Ylönen, Ulla-Maija Hanste, Mirja Leivuori ja Markku Ilmakunnas Suomen ympäristökeskus
Laboratorioiden välinen pätevyyskoe 3/2013
SUOMEN YMPÄRISTÖKESKUKSEN RAPORTTEJA 23 13 Laboratorioiden välinen pätevyyskoe 3/13 BOD 7, COD Cr, COD Mn, kiintoaine, Na ja TOC jätevesistä Katarina Björklöf, Kaija Korhonen-Ylönen, Teemu Näykki, Marketta
AKKREDITOITU TESTAUSLABORATORIO ACCREDITED TESTING LABORATORY
T032/M27/2019 Liite 1 / Appendix 1 Sivu / Page 1(5) AKKREDITOITU TESTAUSLABORATORIO ACCREDITED TESTING LABORATORY SAIMAAN VESI- JA YMPÄRISTÖTUTKIMUS OY WATER AND ENVIRONMENT RESEARCH OF SAIMAA Tunnus Code
LYTH-CONS CONSISTENCY TRANSMITTER
LYTH-CONS CONSISTENCY TRANSMITTER LYTH-INSTRUMENT OY has generate new consistency transmitter with blade-system to meet high technical requirements in Pulp&Paper industries. Insurmountable advantages are
Laboratorioiden välinen vertailumittaus
SUOMEN YMPÄRISTÖKESKUKSEN RAPORTTEJA 14 2011 Laboratorioiden välinen vertailumittaus AOX-määritys Kaija Korhonen-Ylönen, Mirja Leivuori, Olli Järvinen, Keijo Tervonen, Sari Lanteri, Markku Ilmakunnas ja
Proficiency Test SYKE 10/2012
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 19 2013 Proficiency Test SYKE 10/2012 Leaching testing of solid waste sample Katarina Björklöf, Kaija Korhonen-Ylönen, Marika Kaasalainen, Mirja Leivuori, Sirpa
Information on preparing Presentation
Information on preparing Presentation Seminar on big data management Lecturer: Spring 2017 20.1.2017 1 Agenda Hints and tips on giving a good presentation Watch two videos and discussion 22.1.2017 2 Goals
Results on the new polydrug use questions in the Finnish TDI data
Results on the new polydrug use questions in the Finnish TDI data Multi-drug use, polydrug use and problematic polydrug use Martta Forsell, Finnish Focal Point 28/09/2015 Martta Forsell 1 28/09/2015 Esityksen
The CCR Model and Production Correspondence
The CCR Model and Production Correspondence Tim Schöneberg The 19th of September Agenda Introduction Definitions Production Possiblity Set CCR Model and the Dual Problem Input excesses and output shortfalls
Digitally signed by Hans Vadbäck DN: cn=hans Vadbäck, o, ou=fcg Suunnittelu ja Tekniikka Oy, [email protected], c=fi Date: 2016.12.20 15:45:35 +02'00' Jakob Kjellman Digitally signed by Jakob Kjellman
AKKREDITOITU TESTAUSLABORATORIO ACCREDITED TESTING LABORATORY
T073/A16/2016 Liite 1 / Appendix 1 Sivu / Page 1(6) AKKREDITOITU TESTAUSLABORATORIO ACCREDITED TESTING LABORATORY KEMIALLISEN ASEEN KIELTOSOPIMUKSEN INSTITUUTTI FINNISH INSTITUTE FOR VERIFICATION OF THE
Other approaches to restrict multipliers
Other approaches to restrict multipliers Heikki Tikanmäki Optimointiopin seminaari 10.10.2007 Contents Short revision (6.2) Another Assurance Region Model (6.3) Cone-Ratio Method (6.4) An Application of
TIEKE Verkottaja Service Tools for electronic data interchange utilizers. Heikki Laaksamo
TIEKE Verkottaja Service Tools for electronic data interchange utilizers Heikki Laaksamo TIEKE Finnish Information Society Development Centre (TIEKE Tietoyhteiskunnan kehittämiskeskus ry) TIEKE is a neutral,
Accommodation statistics
Transport and Tourism 2013 Accommodation statistics 2013, February Nights spent by foreign tourists in Finland down by 2.5 per cent in February 2013 The number of recorded nights spent by foreign tourists
Accommodation statistics
Transport and Tourism 2011 Accommodation statistics 2011, January Nights spent by foreign tourists in Finland increased by per cent in January The number of recorded nights spent by foreign tourists at
Proficiency Test on soil improver maturity tests
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 7 0 Proficiency Test on soil improver maturity tests Liisa Maunuksela, Katarina Björklöf, Leena Kaarla, Mirja Kartio and Mirja Leivuori Finnish Environment Institute
Laboratorioiden välinen pätevyyskoe 4/2012
SUOMEN YMPÄRISTÖKESKUKSEN RAPORTTEJA 22 2012 Laboratorioiden välinen pätevyyskoe 4/2012 Happi, a-klorofylli, saliniteetti, SiO 2, TIC ja TOC luonnonvesistä Kaija Korhonen-Ylönen, Mirja Leivuori, Marketta
On instrument costs in decentralized macroeconomic decision making (Helsingin Kauppakorkeakoulun julkaisuja ; D-31)
On instrument costs in decentralized macroeconomic decision making (Helsingin Kauppakorkeakoulun julkaisuja ; D-31) Juha Kahkonen Click here if your download doesn"t start automatically On instrument costs
WindPRO version joulu 2012 Printed/Page :47 / 1. SHADOW - Main Result
SHADOW - Main Result Assumptions for shadow calculations Maximum distance for influence Calculate only when more than 20 % of sun is covered by the blade Please look in WTG table WindPRO version 2.8.579
ELEMET- MOCASTRO. Effect of grain size on A 3 temperatures in C-Mn and low alloyed steels - Gleeble tests and predictions. Period
1 ELEMET- MOCASTRO Effect of grain size on A 3 temperatures in C-Mn and low alloyed steels - Gleeble tests and predictions Period 20.02-25.05.2012 Diaarinumero Rahoituspäätöksen numero 1114/31/2010 502/10
Satelliittikuvat osana öljypäästövalvontaa
Öljypäästövalvonta Euroopan meriturvallisuusviraston (EMSA) satelliittikuvilta Kati Tahvonen Suomen ympäristökeskus Kaukokartoituspäivät 2007 Helsinki, 8.11.2007 Satelliittikuvat osana öljypäästövalvontaa
Sisällysluettelo Table of contents
Sisällysluettelo Table of contents OTC:n Moodlen käyttöohje suomeksi... 1 Kirjautuminen Moodleen... 2 Ensimmäinen kirjautuminen Moodleen... 2 Salasanan vaihto... 2 Oma käyttäjäprofiili... 3 Työskentely
,0 Yes ,0 120, ,8
SHADOW - Main Result Calculation: Alue 2 ( x 9 x HH120) TuuliSaimaa kaavaluonnos Assumptions for shadow calculations Maximum distance for influence Calculate only when more than 20 % of sun is covered
SELL Student Games kansainvälinen opiskelijaurheilutapahtuma
SELL Student Games kansainvälinen opiskelijaurheilutapahtuma Painonnosto 13.5.2016 (kansallinen, CUP) Below in English Paikka: Nääshalli Näsijärvenkatu 8 33210 Tampere Alustava aikataulu: Punnitus 12:00-13:00
Gap-filling methods for CH 4 data
Gap-filling methods for CH 4 data Sigrid Dengel University of Helsinki Outline - Ecosystems known for CH 4 emissions; - Why is gap-filling of CH 4 data not as easy and straight forward as CO 2 ; - Gap-filling
Bounds on non-surjective cellular automata
Bounds on non-surjective cellular automata Jarkko Kari Pascal Vanier Thomas Zeume University of Turku LIF Marseille Universität Hannover 27 august 2009 J. Kari, P. Vanier, T. Zeume (UTU) Bounds on non-surjective
Field measurement intercomparison
REPORTS OF FINNISH ENVIRONMENT INSTITUTE 24 2014 Field measurement intercomparison Field measurements of dissolved oxygen concentration Mirja Leivuori, Teemu Näykki, Ivo Leito, Irja Helm, Lauri Jalukse,
Laboratorioiden välinen pätevyyskoe 1/2008
SUOMEN YMPÄRISTÖKESKUKSEN RAPORTTEJA 08 Laboratorioiden välinen pätevyyskoe 1/08 Ravinteet, ph ja sähkönjohtavuus luonnonvesistä Kaija Korhonen, Teemu Näykki, Olli Järvinen, Tero Eklin, Keijo Tervonen
