persistent organic pollutants (pops) in marine mammals ... › ... › s6-1115-ross.pdf · harmless...
TRANSCRIPT
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Persistent Organic Pollutants (POPs) in marine mammals: harmless chemicals or lingering poisons?
Peter S. RossFisheries and Oceans Canada
Institute of Ocean Sciences, Sidney BC
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Marine mammals can serve as integrated indicators of marine pollution
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But only when we understand biology and ecology (~confounding factors)
• Age• Sex• Feeding ecology• Habitat use• Biomagnification: trophic
level, metabolism
• Physico‐chemical properties of pollutant• Complex pollutant mixtures
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Marine mammals are not good sentinels for all pollutants, but can be for those contaminants considered to be:
• Persistent (do not break down in environment)• Bioaccumulative
(are not metabolized and amplify in
food webs)• Toxic (endocrine‐disrupting)• Subject to long‐range transport (trans‐Pacific!)• E.g. PCBs, DDT, dioxins, PBDEs, etc
– (i.e. pollutants considered by Stockholm Convention)
Clx
Clx
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Age and sex: PCBs increase with age in male killer whales (circles), but decrease in reproductively active
females (triangles)
(Ross et al., 2000)
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femalesmales
Northernresidents
PCB
(ppm
)
0
100
200
300
Feeding ecology: PCBs are higher in marine mammal‐ eating Transient killer whales than in salmon‐eating Resident killer whales
Southernresidents
Transients
(Ross et al., 2000)
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Trophic
level: total PCBs
biomagnify
in harbour seal food web
• PCB concentration in lipid increases with
trophic
level in food web
• PCBs are persistent• Fat soluble• Recalcitrant • Stable isotopes of
nitrogen (15N: 14N) provide measure of trophic
level
(Cullon et al., 2012)
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Metabolism: individual PCBs
behave differently in marine food webs
• Influence of log Kow• Influence of
metabolism on different congeners
– Black circles: recalcitrant
– Open circles: metabolizable
(Cullon et al., 2012)
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Brown et al. 2009, ES&T; Kuzyk
et al. 2005, Sci. Tot. Environ
Habitat use: Local PCB releases can contaminate local marine mammal food webs
Satellite tracks reveal local movement of resident seal in Saglek
Bay
Contaminated sediments deliver PCBsto ringed seal food web
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Habitat use: some individuals move hundreds of kilometers, and may be more exposed to global PCB
‘background’, while others are more localized and can be exposed to contaminated sites
Saglek Fjord
Saglek
‘resident’
sealMigratory seal
Saglek Fjord
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Complex mixtures: which pollutant poses the greatest risk? Comparative risk approaches
POP concentrationHendrickson beluga
sHCHPCB
sCHLsDDT
sCBdieldrin
Con
cent
ratio
n ug
/kg
ww
0
1000
2000
3000
4000
sHCHPCB
sCHLsDDT
sCBdieldrinC
RQ (P
OP
conc
entr
atio
n / T
RV a
tsdr
)
0
10
20
30
40
50Comparative Risk Quotient (CRQ)
Hendrickson beluga
POPs in Beaufort Sea beluga whales:1) Concentration vs 2) Relative risk basedon relative toxicity in rodent studies
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When we address such factors, marine mammals
provide integrated information of PCB trends in
the NE Pacific
• Same age harbour seals (4 weeks old);
• Live captured in good condition;
• Feeding ecology is documented.
(Ross et al., 2013)
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Flame retardant PBDEs
were going up,
but they were banned starting in 2004
(Ross et al., 2013)
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PCB-related health effects in harbour seals: effects on thyroid and vitamin A physiology and immune
function
(Tabuchi et al., 2007; Mos et al. 2007)
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PCB-related health effects in wild killer whales: Gene expression profiles (PCA) in biopsies correlate with PCBs (33%) and age (19%)
t1 (32.93%)-2.0 -1.0 0.0 1.0 2.0 3.0
t2 (1
9.36
%
-3.0
-2.0
-1.0
0.0
1.0
2.0
3.0A
Log10ΣPCB (mg/kg, lw)0.0 0.5 1.0 1.5 2.0 2.5 3.0
Fact
or 1
-3.0
-2.0
-1.0
0.0
1.0
2.0
3.0
4.0 C
y = 1.86x - 2.64r2 = 0.84p < 0.001
Log10Age0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 1.8
Fact
or 2
-3.0
-2.0
-1.0
0.0
1.0
2.0
3.0D
y = -2.24x - 2.39r2 = 0.50p < 0.001
p1 (32.93%)-0.6 -0.4 -0.2 0.0 0.2 0.4 0.6 0.8
p2 (1
9.36
%)
-0.2
-0.1
0.0
0.1
0.2
0.3
0.4
0.5
0.6GAPDH
ILGF-1ADP
PPARγ TRβGRLEP
VDRCβA
HSP70RXRα
AhR
TRαMT1
IL-10
ERα
B
(Buckman et al, 2011)
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Health effects in killer whales: Five gene transcripts were strongly correlated with PCBs, including the
thyroid hormone receptor (TRa), the estrogen
receptor (Era) and the Aryl hydrocarbon receptor (AhR)
Log10 Total PCBs (mg/kg, lipid)
Gen
e Ex
pres
sion
(R
elat
ive
Fold
Cha
nge)
0
1
2
3 AhR
y = 1.05x - 0.44r2 = 0.85p < 0.001
TRα
y = 0.85x - 0.17r2 = 0.69p < 0.001
ERα
y = 0.72x - 0.17r2 = 0.74p < 0.001
0.0 0.5 1.0 1.5 2.0 2.5 3.0
TRβ r2 = 0.02p = 0.47
0.0 0.5 1.0 1.5 2.0 2.5 3.0
MT1
y = 0.87x - 0.13r2 = 0.64p < 0.001
0.0 0.5 1.0 1.5 2.0 2.5 3.0
0
1
2
3 IL-10
yfemale
= 0.67x - 0.74
r2= 0.66p < 0.001
ymalel
= 0.87x - 0.63r2 = 0.73p < 0.001
(Buckman et al, 2011)
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Marine mammals can serve as useful sentinels of marine food web contamination, but only when we understand the biology and ecology of the
study animals, and incorporate these into study design and interpretation
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Thank you
• Species at Risk Act Science Fund (DFO), Ecosystem Research Fund (DFO), Federal Contaminated Sites Action Plan, Northern Contaminants Program (AANDC), Washington Department of Fish and Wildlife
• Neil Dangerfield, Graeme Ellis, John Ford, Graeme Ellis, Lance Barrett‐Lennard
• Andrea Buckman, Donna Cullon, Maki Tabuchi
Lizzy
Mos• Photo credits Graeme Ellis, Brian Gisborne, Peter S. Ross, John
K.B. Ford
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Martin Fortier
Habitat use:
Local PCB contamination: Saglek Bay military radar site 1950‐70s
(Labrador, eastern Canada)
After Excavation 1999
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PCDEs are going down
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Lag time between regulations and response
PCBs are declining very slowly in most ecosystems (environmental half‐life ~20 to >40 years).
Projected times for 95% of population members to fall below the least protective 17 mg/kg effects threshold (t½
=
30 yrs):
Northern Residents ~ 2030
Southern Residents ~2089
(Hickie et al., 2007)
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We have been evaluating ocean disposal practices to determine if sediment PCB ‘reservoirs’
might be a concern
to killer whales or their Critical habitat
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Every thing is connected
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Almost all Southern Resident killer whales still exceed health effects thresholds for marine mammals: higher risk of endocrine, immune,
developmental effects
0
20
40
60
80
100
1 10 100 1000PCB concentration (mg/kg lipid)
Cum
ulat
ive
% o
f pop
ulat
ion
(Hickie
et al 2007)
Threshold effects
levels
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Killer whale food web modelling reveals failure of SQGs
to protect killer whales (these scenarios reflect theoretical
implications of a killer whale living ‘above’
the stated guideline)
Test scenario
Actual SRKW
LEACA DL
CCME ISQGEC DL
CEPA ALSoG
Burrard I
Victoria Hrbr
Puget Sd
Pred
icte
d P
CB
con
cent
ratio
n in
mal
e so
uthe
rn re
side
nt k
iller
wha
les
(μg/
kg L
W)
and
fold
incr
ease
ove
r cur
rent
0
10000000
20000000
30000000
40000000
50000000
60000000
70000000
1.0x
.01x
17x 32x81x
.8x 25x
300x
759x
Evaluating guidelines, laboratory practices and habitat quality.
We used the model to predictwhat the PCB burden in a hypothetical killer whale would become
if it lived in an environment where the sediments had PCB concentrations equivalent to one of eight scenarios.Numbers above each bar represent the fold‐difference over the actual SRKW predicted value.
(Lachmuth
et al 2010; Alava et al 2012)
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• 12,000 back trajectories calculated: Prevailing air mass
movement supports notion of trans‐Pacific delivery of PBDEs
to coastal British Columbia
• PCBs and PBDEs
travel across the Pacific from the west in 5‐10
days;• 42% of back trajectories
originate over Asia, consistent with our 40% of background
PBDEs
levels estimated for Strait of Georgia;
• These pollutants fall out and become incorporated into
aquatic food webs.
(Noel et al, 2009: 10‐day back trajectories, 4x per day, three elevations, two sites)
Marine mammals in the North Pacific are subject to both local POP sources and a common ‘global background’
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“Is it safe to eat traditional seafoods...?”
‐Vancouver Island Region Wildlife Management Society letter to HC, DFO and INAC in 2005
• Concerns expressed by numerous communities about PCBs, dioxins, mercury, biological
pollution and toxic algal blooms in the ocean;• However, concern also about the loss of
connection with nature’s bounty as people shift towards supermarket foods;
• Can we do a better job of balancing health risks with health benefits?
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We posed three research questions:
2) How contaminated are traditional seafoods?
1) How much traditional seafoods are consumed by Vancouver Island First Nations?
3) Is it safe to eat traditional seafoods? (Questions 1 and 2 combined)
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PCNs are going down
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‘Structural pollutants’
present a visible and obvious threat to marine wildlife
(Mapoon Aboriginal Shire Council, 2006)
(Beach Envtal Awareness Campaign Hawaii)
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Most pollutants are invisible but can cause acute or chronic effects