Landfills and waste water treatment plants as sources of ... - GKSS
Landfills and waste water treatment plants as sources of ... - GKSS
Landfills and waste water treatment plants as sources of ... - GKSS
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INTRODUCTION<br />
Chen et al. 2007a; Hart et al. 2008; Löfstr<strong>and</strong> et al. 2008; Ahrens et al. 2009d; Hutter et al.<br />
2009; Kelly et al. 2009). However, for musk fragrances the availability <strong>of</strong> biomonitoring data<br />
is rather limited compared to the other substance cl<strong>as</strong>ses.<br />
Bioaccumulation <strong>and</strong> bioconcentration <strong>of</strong> PFCs are directly connected to the carbon chain<br />
length <strong>and</strong> incre<strong>as</strong>e with incre<strong>as</strong>ing number <strong>of</strong> fluorinated carbons (Conder et al. 2008).<br />
PFSAs are more bioaccumulative than its corresponding PFCAs <strong>of</strong> same chain length (Houde<br />
et al. 2006) PFCAs with chain length shorter than eight carbons are reported not to be<br />
bioaccumulative according to current regulatory criteria (Conder et al. 2008). The potential<br />
for bioaccumulation <strong>of</strong> PBDEs is directly linked to the size <strong>of</strong> the molecule. Therefore, lower<br />
brominated congeners (four to seven bromines) are more bioaccumulative with<br />
bioconcentration factors <strong>of</strong> higher than 5000 (Birnbaum <strong>and</strong> St<strong>as</strong>kal 2004). BDE209 h<strong>as</strong> only<br />
limited bioavailability (De Wit 2002).<br />
Where<strong>as</strong>, PBDEs <strong>and</strong> musk fragrances accumulate primarily in fatty tissues <strong>of</strong> animals <strong>and</strong><br />
humans, PFCs are stored in protein-rich repositories such <strong>as</strong> liver, gall bladder <strong>and</strong> blood<br />
proteins (Hites 2004; Conder et al. 2008). For example, concentrations <strong>of</strong> PFOS <strong>and</strong> PFOA in<br />
liver from Artic polar bears ranged from 263-6340 <strong>and</strong> 2-9 ng g -1 , respectively (Smithwick et<br />
al. 2005). PBDEs were recently detected in adipose tissue <strong>of</strong> polar bears from various arctic<br />
locations <strong>and</strong> ranged from 2.91-132 ng g -1 dominated by BDE47 (Muir et al. 2005). Kannan et<br />
al. (2005) observed polycyclic musk HHCB between 4 <strong>and</strong> 25 ng g -1 in the blubbers <strong>of</strong><br />
dolphins <strong>and</strong> whales.<br />
Half-life time <strong>of</strong> PFOS in monkeys is reported to be 150 days, where<strong>as</strong> that <strong>of</strong> PFOA w<strong>as</strong> 30<br />
<strong>and</strong> 21 days for female <strong>and</strong> male, respectively (Lau et al. 2007). Half-lives in rats <strong>of</strong><br />
commercial pentaBDE congeners were determined between 19-105 days <strong>and</strong> were incre<strong>as</strong>ing<br />
with incre<strong>as</strong>ed degree <strong>of</strong> bromination (Birnbaum <strong>and</strong> Cohen Hubal 2006). MX h<strong>as</strong> a<br />
calculated half-life time in humans <strong>of</strong> 100 days (Kokot-Helbling et al. 1995). In fish they are<br />
rather short (3 d for MX <strong>and</strong> MK) (T<strong>as</strong> et al. 1997).<br />
Furthermore, PFCs <strong>and</strong> PBDEs were reported to accumulate in the marine food web with<br />
significant incre<strong>as</strong>es towards higher trophic levels (Sørmo et al. 2006; Kelly et al. 2009). In<br />
contr<strong>as</strong>t, biomagnification <strong>of</strong> musk fragrances to higher trophic levels w<strong>as</strong> less pronounced<br />
(Kannan et al. 2005; Nakata 2005).<br />
1.4.3 Toxicity<br />
PFCs, PBDEs <strong>and</strong> musk fragrances are subject to various toxicologically effects in humans<br />
<strong>and</strong> animals. In general, acute toxicities <strong>of</strong> PFCs are moderate but incre<strong>as</strong>e with chain-length<br />
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