EU-kalat: Difference between revisions
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== Answer == | == Answer == | ||
[[File:Dioxin concentrations in Baltic herring.png|thumb|400px|Dioxin concentrations in Baltic herring.]] | |||
The original sample results can be acquired from [http://en.opasnet.org/w/Special:Opasnet_Base?id=Op_en3104 Opasnet base]. The study showed that levels of PCDD/Fs and PCBs depends especially on the fish species. Highest levels were on salmon and large sized herring. Levels of PCDD/Fs exceeded maximum level of 4 pg TEQ/g fw multiple times. Levels of PCDD/Fs were correlated positively with age of the fish. | The original sample results can be acquired from [http://en.opasnet.org/w/Special:Opasnet_Base?id=Op_en3104 Opasnet base]. The study showed that levels of PCDD/Fs and PCBs depends especially on the fish species. Highest levels were on salmon and large sized herring. Levels of PCDD/Fs exceeded maximum level of 4 pg TEQ/g fw multiple times. Levels of PCDD/Fs were correlated positively with age of the fish. | ||
Mean congener concentrations as WHO2005-TEQ in Baltic herring can be printed out with the | Mean congener concentrations as WHO2005-TEQ in Baltic herring can be [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=9Q7skOCFyPfpJbmg printed out with this link] or by running the codel below. | ||
<rcode | <rcode graphics=1> | ||
# This code is Op_en on page [[EU-kalat]]. | # This code is Op_en on page [[EU-kalat]]. | ||
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ggplot(temp, aes(x = Congener, y = Result, fill = Congener)) + geom_bar(stat = "identity") + facet_wrap(~ Catch_location) + | ggplot(temp, aes(x = Congener, y = Result, fill = Congener)) + geom_bar(stat = "identity") + facet_wrap(~ Catch_location) + | ||
labs(x = "Congener", y = "TEQ concentration (pg/g fat)") + theme_gray(base_size = 18) + coord_flip() | labs(x = "Congener", y = "TEQ concentration (pg/g fat)") + theme_gray(base_size = 18) + coord_flip() | ||
temp2 <- temp[temp$Congener %in% levels(temp$Congener)[1:17],] | |||
ggplot(temp2, aes(x = Congener, y = Result, fill = Congener)) + geom_bar(stat = "identity") + facet_wrap(~ Catch_location) + | |||
labs( | |||
title="Dioxin concentrations in Baltic herring", | |||
x = "Congener", | |||
y = "TEQ concentration (pg/g fat)" | |||
) + theme_gray(base_size = 18) + coord_flip() | |||
</rcode> | </rcode> | ||
Revision as of 08:53, 30 January 2018
[show] This page is a study.
The page identifier is Op_en3104 |
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EU-kalat is a study, where concentrations of PCDD/Fs, PCBs, PBDEs and heavy metals have been measured from fish
Question
The scope of EU-kalat study was to measure concentrations of persistent organic pollutants (POPs) including dioxin (PCDD/F), PCB and BDE in fish from Baltic sea and Finnish inland lakes and rivers. [1] [2] [3].
Answer

The original sample results can be acquired from Opasnet base. The study showed that levels of PCDD/Fs and PCBs depends especially on the fish species. Highest levels were on salmon and large sized herring. Levels of PCDD/Fs exceeded maximum level of 4 pg TEQ/g fw multiple times. Levels of PCDD/Fs were correlated positively with age of the fish.
Mean congener concentrations as WHO2005-TEQ in Baltic herring can be printed out with this link or by running the codel below.
Rationale
Data
Data was collected between 2009-2010. The study contains years, tissue type, fish species, and fat content for each concentration measurement. Number of observations is 285.
There is a new study EU-kalat 3, which will produce results in 2016.
Calculations
Preprocess
- Preprocess model 22.2.2017 [4]
- Objects used in Benefit-risk assessment of Baltic herring and salmon intake
- Model run 25.1.2017 [5]
- Model run 22.5.2017 with new ovariables euRaw, euAll, euMain, and euRatio [6]
- Model run 23.5.2017 with adjusted ovariables euRaw, eu, euRatio [7]
- Model run 11.10.2017: Small herring and Large herring added as new species [8]
- Model rerun 15.11.2017 because the previous stored run was lost in update [9]
Bayes model for dioxin concentrations
- Model run 28.2.2017 [10]
- Model run 28.2.2017 with corrected survey model [11]
- Model run 28.2.2017 with Mu estimates [12]
- Model run 1.3.2017 [13]
- Model run 23.4.2017 [14] produces list conc.param and ovariable concentration
- Model run 24.4.2017 [15]
- Model run 19.5.2017 without ovariable concentration [16] ⇤--#: . The model does not mix well, so the results should not be used for final results. --Jouni (talk) 19:37, 19 May 2017 (UTC) (type: truth; paradigms: science: attack)
- Model run 22.5.2017 with TEQdx and TEQpcb as the only Compounds [17]
- Model run 23.5.2017 debugged [18] [19] [20]
- Model run 24.5.2017 TEQdx, TECpcb -> PCDDF, PCB [21]
- Model run 11.10.2017 with small and large herring [22] (removed in update)
Initiate conc_pcddf
- Model run 19.5.2017 [23]
- Model run 23.5.2017 with bugs fixed [24]
- Model run 12.10.2017: TEQ calculation added [25]
- Model rerun 15.11.2017 because the previous stored run was lost in update [26]
⇤--#: . These codes should be coherent with POPs in Baltic herring. --Jouni (talk) 12:14, 7 June 2017 (UTC) (type: truth; paradigms: science: attack)
See also
References
- ↑ A. Hallikainen, H. Kiviranta, P. Isosaari, T. Vartiainen, R. Parmanne, P.J. Vuorinen: Kotimaisen järvi- ja merikalan dioksiinien, furaanien, dioksiinien kaltaisten PCB-yhdisteiden ja polybromattujen difenyylieettereiden pitoisuudet. Elintarvikeviraston julkaisuja 1/2004. [1]
- ↑ E-R.Venäläinen, A. Hallikainen, R. Parmanne, P.J. Vuorinen: Kotimaisen järvi- ja merikalan raskasmetallipitoisuudet. Elintarvikeviraston julkaisuja 3/2004. [2]
- ↑ Anja Hallikainen, Riikka Airaksinen, Panu Rantakokko, Jani Koponen, Jaakko Mannio, Pekka J. Vuorinen, Timo Jääskeläinen, Hannu Kiviranta. Itämeren kalan ja muun kotimaisen kalan ympäristömyrkyt: PCDD/F-, PCB-, PBDE-, PFC- ja OT-yhdisteet. Eviran tutkimuksia 2/2011. ISSN 1797-2981 ISBN 978-952-225-083-4 [3]