EU-kalat: Difference between revisions

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* Model run 2021-03-08 [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=ZvJDOo7xL8d7x7EI]
* Model run 2021-03-08 [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=ZvJDOo7xL8d7x7EI]
* Model run 2021-03-08 [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=VpSUS4pfGavspLG9] with the fish needed in PFAS assessment
* Model run 2021-03-08 [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=VpSUS4pfGavspLG9] with the fish needed in PFAS assessment
* Model run 2021-03-12 [http://en.opasnet.org/en-opwiki/index.php?title=Special:RTools&id=SYJXm55OtbqdjDK6] using euw


<rcode name="pollutant_bayes" label="Initiate conc_pcddf with PFAS, OT (for developers only)" embed=0 graphics=1>
<rcode name="pollutant_bayes" label="Initiate conc_param with PCDDF, PFAS, OT (for developers only)" embed=0 graphics=1>
# This is code Op_en3104/pollutant_bayes on page [[EU-kalat]]
# This is code Op_en3104/pollutant_bayes on page [[EU-kalat]]
# The code is also available at https://github.com/jtuomist/pfas/blob/main/conc_pcddf_preprocess.R
# The code is also available at https://github.com/jtuomist/pfas/blob/main/conc_pcddf_preprocess.R
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#' @param df data.frame
#' @param df data.frame
#' @return data.matrix
#' @return data.matrix
add_loq <- function(df) {
add_loq <- function(df) { # This should reflect the fraction of observations below LOQ.
   LOQ <- unlist(lapply(df, FUN = function(x) min(x[x!=0], na.rm=TRUE)))  
   LOQ <- unlist(lapply(df, FUN = function(x) min(x[x!=0], na.rm=TRUE)))  
   out <- sapply(
   out <- sapply(
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#size <- Ovariable("size", ddata="Op_en7748", subset="Size distribution of fish species")
#size <- Ovariable("size", ddata="Op_en7748", subset="Size distribution of fish species")
#time <- Ovariable("time", data = data.frame(Result=2015))
#time <- Ovariable("time", data = data.frame(Result=2015))
#conc_pcddf <- EvalOutput(conc_pcddf,verbose=TRUE)
#View(conc_pcddf@output)


objects.latest("Op_en3104", code_name = "preprocess") # [[EU-kalat]] eu, eu2, euRatio, indices
objects.latest("Op_en3104", code_name = "preprocess2") # [[EU-kalat]] euw
 
eu2 <- EvalOutput(eu2)


# Hierarchical Bayes model.
# Hierarchical Bayes model.
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# Catchment year affects all species similarly.  
# Catchment year affects all species similarly.  


eu2 <- eu2[!eu2$Compound %in% c("MPhT","DOT","BDE138"),] # No values > 0
euw <- euw[!colnames(euw) %in% c("MPhT","DOT","BDE138")] # No values > 0


eu3 <- eu2[eu2$Matrix == "Muscle" , ]@output
eu3 <- euw[euw$Matrix == "Muscle" , ]
eu3 <- reshape(
  eu3,
  v.names = "eu2Result",
  idvar = c("THLcode", "Fish"),
  timevar = "Compound",
  drop = c("Matrix","eu2Source"),
  direction = "wide"
)
colnames(eu3) <- gsub("eu2Result\\.","",colnames(eu3))
eu3$TEQ <- eu3$PCDDF + eu3$PCB
eu3$PFAS <- eu3$PFOA + eu3$PFOS


#conl_nd <- c("PFAS","PFOA","PFOS","DBT","MBT","TBT","DPhT","TPhT")
#conl_nd <- c("PFAS","PFOA","PFOS","DBT","MBT","TBT","DPhT","TPhT")
Line 764: Line 750:


objects.store(conc_param)
objects.store(conc_param)
cat("Data frame conc_params stored.\n")
cat("Ovariable conc_param stored.\n")


######################3
######################3
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#))
#))


tmp <- eu2[eu2$Compound %in% c("PCDDF","PCB","BDE153","PBB153","PFOA","PFOS","DBT","MBT","TBT"),]@output
#tmp <- euw[euw$Compound %in% c("PCDDF","PCB","BDE153","PBB153","PFOA","PFOS","DBT","MBT","TBT"),]
ggplot(tmp, aes(x = eu2Result, colour=Fish))+stat_ecdf()+
#ggplot(tmp, aes(x = eu2Result, colour=Fish))+stat_ecdf()+
  facet_wrap( ~ Compound, scales="free_x")+scale_x_log10()
facet_wrap( ~ Compound, scales="free_x")+scale_x_log10()


scatterplotMatrix(t(exp(samps.j$pred[2,,,1])), main = paste("Predictions for several compounds for",
scatterplotMatrix(t(exp(samps.j$pred[2,,,1])), main = paste("Predictions for several compounds for",

Revision as of 05:25, 12 March 2021


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

Dioxin concentrations in Baltic herring.

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.

+ Show code

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]
  • 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]
  • Model run 21.3.2018: Small and large herring replaced by actual fish length [10]
  • Model run 26.3.2018 eu2 moved here [11]

See an updated version of preprocess code for eu on Health effects of Baltic herring and salmon: a benefit-risk assessment#Code for estimating TEQ from chinese PCB7

+ Show code

Bayes model for dioxin concentrations

  • Model run 28.2.2017 [12]
  • Model run 28.2.2017 with corrected survey model [13]
  • Model run 28.2.2017 with Mu estimates [14]
  • Model run 1.3.2017 [15]
  • Model run 23.4.2017 [16] produces list conc.param and ovariable concentration
  • Model run 24.4.2017 [17]
  • Model run 19.5.2017 without ovariable concentration [18] ⇤--#: . 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)
----#: . Maybe we should just estimate TEQs until the problem is fixed. --Jouni (talk) 19:37, 19 May 2017 (UTC) (type: truth; paradigms: science: comment)
  • Model run 22.5.2017 with TEQdx and TEQpcb as the only Compounds [19]
  • Model run 23.5.2017 debugged [20] [21] [22]
  • Model run 24.5.2017 TEQdx, TECpcb -> PCDDF, PCB [23]
  • Model run 11.10.2017 with small and large herring [24] (removed in update)
  • Model run 12.3.2018: bugs fixed with data used in Bayes. In addition, redundant fish species removed and Omega assumed to be the same for herring and salmon. [25]
  • Model run 22.3.2018 [26] Model does not mix well. Thinning gives little help?
  • Model run 25.3.2018 with conc.param as ovariable [27]

+ Show code

Initiate conc_pcddf for PFAS disease burden study

This code is similar to preprocess but is better and includes PFAS concentrations from op_fi:PFAS-yhdisteiden tautitaakka. It produces data.frame euw that is the EU-kalat + PFAS data in wide format and, for PFAS but not EU-kalat, a sampled value for measurements below the level of quantification.

+ Show code

Bayesian approach for PCDDF, PCB, OT, PFAS.

  • Model run 2021-03-08 [28]
  • Model run 2021-03-08 [29] with the fish needed in PFAS assessment
  • Model run 2021-03-12 [30] using euw

+ Show code

+ Show code

NOTE! This is not a probabilistic approach. Species and area-specific distributions should be created.

+ Show code

Initiate conc_pcddf for Goherr

  • Model run 19.5.2017 [31]
  • Model run 23.5.2017 with bugs fixed [32]
  • Model run 12.10.2017: TEQ calculation added [33]
  • Model rerun 15.11.2017 because the previous stored run was lost in update [34]
  • 12.3.2018 adjusted to match the same Omega for all fish species [35]
  • 26.3.2018 includes length and time as parameters, lengt ovariable initiated here [36]

+ Show code

⇤--#: . 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

  1. 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]
  2. E-R.Venäläinen, A. Hallikainen, R. Parmanne, P.J. Vuorinen: Kotimaisen järvi- ja merikalan raskasmetallipitoisuudet. Elintarvikeviraston julkaisuja 3/2004. [2]
  3. 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]