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Table 8.2 Concentrations of PCBs and DDTs in waters from remote sites (mean ±
standard deviation). (From Vilanova et al . 2001a; Fernandez et al . 2005.)
PCBs (pg l −1 )
DDTs (pg l −1 )
Location
Total
Particulate
Dissolved
% in SPM
Total
Ladove Lake Sept.
2000
64 ± 30
33 ± 8
31 ± 31
59 ± 19
12 ± 3
Lake Redon Nov.
2000
79
53
26
67
9.6
Lake Redon May
2000
56 ± 11
28 ± 8
29 ± 8
7.1 ± 2.9
Lake Redon
(1996-8)
62 ± 44
16 ± 28
Lake Gossenkölle
(1996-7)
110 ± 64
14 ± 6.3
Øvre Neådalsvatn
(1998)
26 ± 5.4
0.59 ± 0.40
Amituk Lake
(1994, Arctic)
372
27
Arctic Ocean
(1990, 1992-4)
1.0 ± 0.30*
Easthwaite Water
Lake (1996-7)
680 ± 190
Lakes in southern
Sweden (1997)
8-144
* Only dissolved phase.
Sum of 61 PCBs.
Sum of 49 PCBs.
rather, it is general to the entire planet. These compounds pose a new toxic
threat. Humans are exposed to small doses starting in the womb and continuing
throughout life. The consequences of the combined long-term effects of such
exposure must be evaluated. Health problems due to exposure in the developmental
phase may not appear until a much later age. For example, links between oncogene
mutation and higher blood concentrations of some of these compounds in
patients with colon cancer (Howsam et al . 2004) or exocrine pancreatic cancer
have been observed (Porta et al . 1999). These compounds may even cause
problems in the earliest stages of life. Indeed, decreases in cognitive ability have
been correlated with intrauterine exposure to DDT (Ribas-Fito et al . 2006).
Wheezing at age 6 has been reported in association with prenatal exposure to
DDE (Sunyer et al . 2005, 2006) and increases in attention deficit and hyperactivity
disorders in young children have been attributed to high exposure to HCB during
the neonatal period (Ribas-Fito et al . 2007). An increase in global temperature
will lead to greater volatilization and, consequently, to higher concentrations of
these compounds in the atmosphere and in aquatic systems and ultimately in the
human body.
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