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Andjelkovic et al. J Environ Expo Assess 2024;3:23  https://dx.doi.org/10.20517/jeea.2024.22  Page 11 of 20

               Table 2. Concentrations (ng/g lw) of OCPs in human milk from various countries
                                           β-HCH  β-HCH  p,p’-DDE  p,p’-DDE  p,p’-DDT  p,p’-DDT  HCB  HCB
                Country         Sampling year                                                    Ref.
                                           mean  median mean   median  mean   median  Mean median
                                                                                                         *
                Belgium         2014       2.91  2.40  52.2    37.0   4.40    2.80   5.57  5.50  current study
                France          2011-2014        15.0          60.1           2.2         10.3   [35]
                the Netherlands  2011-2014             69.2    49.4   2.0     1.5    6.5  6.2    [36]
                Israel (1 pooled sample) 2012  10.8    147            4.3                        [40]
                Slovakia        2010-2012              266     167    10.6    18.7   13.3  12.9  [36]
                Tunisia         2010       28.1        371            271            203         [38]
                Croatia         2011       1.7         14.2           8.1            3           [37]
                Croatia (Zadar)  2009-2011       2.3           23.5           1.9         2.0    [37]
                Croatia (Zagreb)  2009-2011      3.1           21.0           1.5         2.5    [37]
                Belgium (rural Flanders) 2009-2010  6.1        56.9           2.6         6.4    [34]
                Turkey          2009       36.3        325.1          10.5           5.4         [39]
                Belgium         2006             nd            95.9           nd          15.5   [15]
                Norway          Birth cohort  4.70  4.32  66.0  53.5  2.65    2.11   11.1  10.5  [41]
               *
                For current study: medians and means = medium bound results. OCPs: Organochlorine pesticides; HCH: hexachlorocyclohexane isomer; DDE:
               dichloro-diphenyl-dichloroethane; DDT: dichloro-diphenyl-trichloroethane; HCB: hexachlorobenzene; nd: not determined.

               Table 3. PBDE levels (ng/g lw) in human milk from Europe
                Country     Sampling year  BDE-28 BDE-47 BDE-99 BDE-100  BDE-153  BDE-154  BDE-183  Ref.
                Belgium     2014         0.06   0.24   0.10    0.09    0.46    0.13    < LOQ   Current study *
                France      2011-2014    0.04   0.43   0.10    0.10    0.54    0.03    0.05    [35]
                the Netherlands  2011-2014  0.02  0.20  0.08   0.06    0.48            0.04    [36]
                Slovakia    2011-2012           0.17   0.07    0.04    0.12                    [36]
                UK          2011-2012    0.09   1.92   0.88    0.64    1.01    0.07    0.05    [44]
                UK
                            2010                2.80   0.69    0.38    0.91    0.21            [45]
                Belgium     2009-2010    < LOQ  0.16   0.06    0.06    0.29    0.07    < LOQ   [34]
                Germany     2009                0.24   0.08    0.08    0.47                    [46]
                Norway      2003-2006    0.08   1.10   0.10    0.10    0.25                    [36]
                Greece      2004-2005    < 0.10  0.48  0.27    0.19    0.30    < 0.10  < 0.10  [20]
                Denmark     1997-2002    0.19   1.99   0.76    0.45    1.20    0.07    0.07    [35]
                Finland     1997-2001    0.33   3.12   0.54    0.42    0.77    0.05    0.03    [35]
                Norway      Birth cohort  0.16  1.10   0.26    0.26    0.50    0.03            [40]
               *
                Mean MB values. PBDE: Polybrominated diphenyl ether; BDE: brominated diphenyl ether; LOQ: limit of quantification; MB: medium bound.

               POP levels in regional pooled samples
               The analyses of the mixed samples per each Belgian region (n = 10) did not reveal the presence of
               hexachlorobutadiene (LOQ = 50 pg/mL), chlordecone (LOQ = 10 pg/mL), dieldrin (LOQ = 5 pg/mL), cis-
               heptachlor (LOQ = 5 pg/mL), trans-heptachlor epoxide (LOQ = 5 pg/mL), or heptachlor (LOQ = 4 pg/mL).
               However, heptachlor was detected in the pooled Belgian sample at 3.5 ng/g lw [Supplementary Table 5].
               Only α-HBCD could be quantified in comparable levels as in the pooled Belgian sample (0.9 to 4.97 ng/g
               lw). Despite α-HBCD’s minor contribution to global HBCD production (technical mixture: α-HBCD of
               around 10% vs. γ-HBCD of > 70%), it is the dominant congener found in most biotic samples worldwide. Its
                                                                                                       [48]
               predominance is hypothesized by the different toxicokinetics and persistency of the HBCD stereoisomers .

               The results for HBCDs in regional samples are comparable to those reported by Roosens et al., who also
               detected HBCDs in samples from Flanders, Belgium (0.6-5.7 ng/g lw) . Several studies in Flanders have
                                                                           [47]
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