EU-kalat: Difference between revisions
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indices <- list( | indices <- list( | ||
Compound.TEQ2 = c(" | Compound.TEQ2 = c("PCDDF", "PCB"), | ||
Compound.PCDDF14 = as.character(unique(euRaw@data$POP)[c(1:12, 14, 15)]), # 7 OCDD should be removed | Compound.PCDDF14 = as.character(unique(euRaw@data$POP)[c(1:12, 14, 15)]), # 7 OCDD should be removed | ||
Fish.Fish14 = as.character(unique(euRaw@data$Fish_species)[c(1:4, 6:14, 17)]) | Fish.Fish14 = as.character(unique(euRaw@data$Fish_species)[c(1:4, 6:14, 17)]) | ||
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* Model run 22.5.2017 with TEQdx and TEQpcb as the only Compounds [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=2vTgALXXTzLgd4l1] | * Model run 22.5.2017 with TEQdx and TEQpcb as the only Compounds [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=2vTgALXXTzLgd4l1] | ||
* Model run 23.5.2017 debugged [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=rMSAZy6PSKzKhHwp] [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=1P7ZPBbghEfisEcH] [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=BcZDhfjpv3fa4IRU] | * Model run 23.5.2017 debugged [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=rMSAZy6PSKzKhHwp] [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=1P7ZPBbghEfisEcH] [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=BcZDhfjpv3fa4IRU] | ||
* Model run 24.5.2017 TEQdx, TECpcb -> PCDDF, PCB [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=kNNzEMTSD4N2f0Yy] | |||
<rcode name="bayes" label="Sample Bayes model (for developers only)" graphics=1> | <rcode name="bayes" label="Sample Bayes model (for developers only)" graphics=1> | ||
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replaces <- list( | replaces <- list( | ||
c("Chlorinated dibenzo-p-dioxins", " | c("Chlorinated dibenzo-p-dioxins", "PCDDF"), | ||
c("Chlorinated dibenzofurans", " | c("Chlorinated dibenzofurans", "PCDDF"), | ||
c("Mono-ortho-substituted PCBs", " | c("Mono-ortho-substituted PCBs", "PCB"), | ||
c("Non-ortho-substituted PCBs", " | c("Non-ortho-substituted PCBs", "PCB") | ||
) | ) | ||
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# PCDD/F concentrations in fish. | # PCDD/F concentrations in fish. | ||
# It uses the TEQ sum of PCDD/F ( | # It uses the TEQ sum of PCDD/F (PCDDF) as the total concentration | ||
# of dioxin and | # of dioxin and PCB respectively for PCB in fish. | ||
# | # PCDDF depends on age of fish, fish species and catchment area, | ||
# but we only have species now so other variables are omitted. | # but we only have species now so other variables are omitted. | ||
# cong depends on fish species. | # cong depends on fish species. | ||
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#> colnames(eu3) | #> colnames(eu3) | ||
#[1] "THLcode" "Fish" "euResult. | #[1] "THLcode" "Fish" "euResult.PCDDF" "euResult.PCB" | ||
# Find the level of quantification for dinterval function | # Find the level of quantification for dinterval function | ||
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## scatterplotMatrix(t(samps.j$mu1[,,1]), main = "Means for all compounds of the generic fish") | ## scatterplotMatrix(t(samps.j$mu1[,,1]), main = "Means for all compounds of the generic fish") | ||
scatterplotMatrix(t(samps.j$pred1[,,1]), main = "Prediction for all compounds of the generic fish") | scatterplotMatrix(t(samps.j$pred1[,,1]), main = "Prediction for all compounds of the generic fish") | ||
scatterplotMatrix(t(samps.j$pred[,1,,1]), main = "Predictions for all fish species for | scatterplotMatrix(t(samps.j$pred[,1,,1]), main = "Predictions for all fish species for PCDDF") | ||
scatterplotMatrix(t(samps.j$Omega[6,2,,,1]), main = "Predictions of Omega for pike and | scatterplotMatrix(t(samps.j$Omega[6,2,,,1]), main = "Predictions of Omega for pike and PCB") | ||
coda.j <- coda.samples( | coda.j <- coda.samples( | ||
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formula = function(...) { | formula = function(...) { | ||
require(MASS) | require(MASS) | ||
require(reshape2) | |||
jsp <- lapply(1:length(conc.param$mu[, 1]), FUN = function(x) { | jsp <- lapply(1:length(conc.param$mu[, 1]), FUN = function(x) { | ||
temp <- exp(mvrnorm( | temp <- exp(mvrnorm( |
Revision as of 11:53, 24 May 2017
[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 the Run code 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 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]
Bayes model for dioxin concentrations
- Model run 28.2.2017 [8]
- Model run 28.2.2017 with corrected survey model [9]
- Model run 28.2.2017 with Mu estimates [10]
- Model run 1.3.2017 [11]
- Model run 23.4.2017 [12] produces list conc.param and ovariable concentration
- Model run 24.4.2017 [13]
- Model run 19.5.2017 without ovariable concentration [14] ⇤--#: . 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 [15]
- Model run 23.5.2017 debugged [16] [17] [18]
- Model run 24.5.2017 TEQdx, TECpcb -> PCDDF, PCB [19]
Initiate concentration
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]