Persistent pollutant concentrations in salmon

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Benefit-risk assessment on farmed salmon: To the assessment page | To the Analytica model
Decision variables:

Variable:Recommendation for consumption of farmed salmon | Variable:Pollutant concentration limits for fish feed

Indicators:

Variable:Pollutant health risk due to the consumption of salmon | Variable:Net health effects due to the consumption of salmon

Other variables:

Variable:Persistent pollutant concentrations in fish feed | Variable:Persistent pollutant concentrations in salmon | Variable:Salmon intake in the population of the Western Europe | Variable:Exposure to persistent pollutants due to salmon in the population of the Western Europe | Variable:Dose-response function of persistent pollutants | Variable:Omega-3 content in salmon | Variable:Omega-3 intake due to salmon in the population of the Western Europe | Variable:Dose-response function of cardiovascular effects of omega-3 fatty acids | Variable:Total mortality in the Western Europe | Variable:Cardiovascular mortality in the Western Europe | Variable:Cardiovascular effects of omega-3 in salmon in the Western Europe


Scope

Persistent pollutant concentrations in salmon describes concentrations of several pollutants in salmon.

Definition

Data

Dieldrin, toxaphene, PCB, and dioxin concentrations in farmed, wild, and market salmon. Triangular probability distribution is used for each pollutant and salmon type. Estimates are based on data from Hites [1]. Parameters min, mode, and max are the minimum, average, and maximum of Hites' data, respectively.

Table. Concentrations (µg/kg) of several pollutants from different sources in salmon.

Location Dieldrin Toxaphene Dioxin PCB
Scotland 5.61 160.01 2.94E-003 50.9
Faroe Islands 5.61 190.01 2.57E-003 48.18
Frankfurt 6.81 136.67 2.52E-003 47.27
Edinburgh 3.74 126.67 2.31E-003 50
Norway 4.54 113.34 2.31E-003 41.81
Paris 4.94 150.01 2.00E-003 37.27
London 3.6 93.34 2.52E-003 46.36
Oslo 4.41 153.34 2.10E-003 34.54
East Canada 3.2 66.67 1.73E-003 39.09
Boston 2.54 43.34 1.89E-003 34.18
Maine 3.34 70 1.42E-003 30
San Francisco 2.8 43.34 1.45E-003 34.54
West Canada 2.54 36.67 1.52E-003 34.54
Toronto 2.4 36.67 1.35E-003 32.72
Los Angeles 2 30 1.55E-003 26.36
Vancouver 1.74 32 1.10E-003 21.82
Washington DC 2 58.67 8.40E-004 12.73
Seattle 1.2 23.33 1.34E-003 22.73
Chicago 1.2 23.33 9.45E-004 18.18
New York 1.2 26.67 7.88E-004 15.45
Washington St 0.93 14.67 1.34E-003 21.82
Chile 1.07 18.67 8.93E-004 21.82
SE AK Chinook 1.2 53.34 1.58E-003 7.27
Denver 0.8 18.67 1.16E-003 14.54
BC Chinook 0.53 20.67 4.31E-004 15.45
BC Sockeye 0.67 23.33 3.15E-004 7.27
Oregon Chinook 0.53 26.67 2.84E-004 8.18
SE AK Sockeye 0.48 20 3.15E-004 6.36
New Orleans 0.48 13.33 7.35E-004 9.09
BC Coho 0.4 16.67 1.79E-004 4.55
Kodiak AK Sockeye 0.27 13.33 2.10E-004 3.64
SE AK Coho 0.4 14 1.05E-004 3.64
Kodiak AK Coho 0.4 15.33 1.05E-004 3.64
BC Pink 0.4 12 1.26E-004 3.64
Kodiak AK Pink 0.4 10 1.05E-004 2.73
SE AK Pink 0.4 10 1.05E-004 1.82
SE AK Chum 0.27 6.67 1.05E-004 1.82
BC Chum 0.27 6.67 1.05E-004 1.82
Kodiak AK Chum 0.27 6.67 1.05E-004 1.82

Causality

Upstream variables

Unit

µg/kg

Formula

<anacode>Poll_i_types*Feed_poll</anacode>

Result

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Statistics or fractile BAU BAU BAU Stricter rules for feed Stricter rules for feed Stricter rules for feed
Dieldrin Toxaphene PCB Dieldrin Toxaphene PCB
Mean 3.3 96.14 36.25 2.2 64.02 24.17
SD 0.95 36.06 5.94 1.03 34.05 9.53
0.01 1.27 25.69 23.85 0.28 7.41 3.43
0.025 1.47 32.08 25.03 0.45 11.39 5.48
0.05 1.69 39.28 26.36 0.62 16.11 7.65
0.25 2.62 69.7 31.98 1.41 37.63 17.42
0.5 (Median) 3.31 93.49 36.19 2.13 60.06 24.57
0.75 3.98 121.76 40.5 2.91 85.93 31.13
0.95 4.88 159.48 46.25 4.01 127.78 39.41
0.975 5.09 168.42 47.61 4.33 140.35 41.76
0.99 5.28 176.34 48.82 4.69 153.1 44

References

  1. R. A. Hites et al. Global assessment of organic contaminants in farmed salmon. Science, 9 Jan. 2004, p. 226