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Week 3 - Puget Sound Biophysical Connections to Salmon
Si Simenstad, Alan Mearns, Steve Jeffries
January 20, 1999
Estuarine, Nearshore - Si Simenstad
Contaminants and Pollution - Mearns
Predators - Steve Jeffries
Contaminants in the Puget Sound
Alan Mearns
Senior Staff Scientist
and Leader of the Biological Assessment Team at NOAA's HazMat
Division, SeattleOffice of Response and Restoration
National Ocean Service
National Oceanic and Atmospheric Administration
7600 Sand Point Way NE
Seattle, WA 98115
Pollution in the Puget Sound Basin as it Relates to Salmon
Outline, Viewgraphs and References
A Lecture Presented for Fish 497U
Questions Addressed (Outline)
- Overview: Response and Restoration
What is pollution?
What are the contaminants of concern ?
Where are they/what are the sources ?
Is contamination getting better or worse?
What is pollution?
To what extent are or were salmon exposed ?
- Are or did salmon experiencing effects ?
Evidence from the field
Evidence from laboratory and exposure studies
- Are the effects significant in terms of risk (to the stocks) and
if so...
- What actions will reduce the risk?
Summary
This is a very brief overview of pollution studies and highlights
in Puget Sound, but it includes some recent important trend information.
Pollution is a damaging excess of contaminants. Contaminants are
any biological, physical or chemical agents that occur in excess
of the their natural range. Human bacteria, light, noise, suspended
particulate material, and various chemicals are contaminants.
This summary focuses on chemical contaminants. Federal, state
and local agencies conduct monitoring and assessment surveys to
map and document contamination and effects of contaminants on
marine and aquatic biota. Materials which we consider contaminants
can enter the Sound from a wide range of sources including transport
from the ocean (advection), rivers and streams, shoreline erosion,
urban runoff, permitted industrial and municipal discharges, combined
serer overflows and atmospheric fallout. Water, sediment and marine
life in large areas of the greater Puget Sound area are clean
or slightly contaminated and do not harbor marine life injured
by contaminants. However, most urban and rural bays contain water,
sediments and/or biota with low levels of various chemical contaminants.
In some areas, such as urban waterways, concentrations of contaminants
are high enough to injure marine life, shellfish and fish, including
juvenile salmon.
In past decades Puget Sound sediments, water and biota were considerably
more contaminated, and over a larger area, than they are today.
Dated sediment cores reveal that the bottom of Puget Sound was
clean until just after the turn of the century. The most contaminated
period was between World War II and about 1960 when many kinds
of metals and organic chemicals were discharged and spread through
the shallow and deep waters of the Main Basin. Laws and enforcement
actions during the 1960's began to reverse this trend. Pulp mills
reduced their waste inputs by factors of 10 or more. During the
1970's pre-treatment, source controls and bans on chemicals such
as DDT , PCB's and leaded gasoline caused further and dramatic
reductions in the amounts of contaminants entering the Sound.
Actions during the 1980's and 1990's help control contaminant
inputs from old plumbing, hazardous waste sites and other hot
spots. During the late 1980's and into the 1990's increased levels
of wastewater treatment were implemented.
Challenges for the future include completing cleanup of hotspots,
improving prevention and/or cleanup of oil and chemical spills,
reducing inputs from combustion and understanding and, if necessary,
controlling contamination of rivers, lakes and streams.
VIEWGRAPHS
1. OVERVIEW : RESPONSE AND RESTORATION
2. HAZMAT APPROACH AND RESPONSE QUESTIONS
What got spilled?
Where is it going?
Who gets hit?
How does it hurt?
So what and how should we respond?
The goal of response, clean-up, pollution control should be to
make things better , improve the chance for natural restoration,
etc. Over-reacting can make things worse.
1. An effective response requires good knowledge about hazardous
materials. What chemical form? Are they biologically reactive,
available? How toxic are they? Do they change, weather, over time?
2. Resources are not affected unless they are exposed, in the
path of contamination. Either monitoring or modeling is needed
to mount an effective response.
3. To what extent are plankton, bottom-dwelling biota, shoreline
biota, surface dwellers exposed. Knowing this sets even better
priorities on response and control.
4. What is the mode of action of the material? Acutely toxic,
chronically toxic? Does it bioaccumulate? Biomagnify?
5. What type of response would do the most good and cause the
least harm? Alternatives include: no action, collection and removal,
in place treatment (chemicals, bioremediation) and/or dispersion
and dilution.
3. PUGET SOUND BASIN POLLUTION QUESTIONS
o What are the contaminants of concern ?
o Where are they/what are the sources ?
o Is contamination getting better or worse?
o Are salmon exposed ?
o Are salmon experiencing effects ?
o Are the effects significant ?
o What actions will reduce the risk?
4. CONTAMINANTS OF CONCERN
There are dozens of biological, physical and chemical materials
that could impact salmon
- Biological Materials (Non-native)
Viruses (Norwalk, polio-,)
Bacteria (and coprostanol)
Non-indigenous biota (green crab larvae)
- Physical Materials
Water, Radionulcides, Debris, Solid Waste
Settleable and/or Suspended solids
Organic Matter, Food wastes, Oxygen Demanding (BOD)
- Chemical Materials
Conventional
Nutrients (nitrate, nitrite, phosphate), Ammonia, Urea
Cyanide, Chlorine (Disinfectants)
Acids and Bases (inorganic and organic)
- Metals
Trace Elements (arsenic, cadmium, mercury, etc)
Organic Metals (organo-tins, organic mercury)
Major elements
Volatile Organics (carbon tetrachloride)
Semi-Volatile Organics (phenols)
- Petroleum Hydrocarbons
- Aromatic Hydrocarbons
Monocyclic, volatile (benzene, xylene, toluene)
Polycyclic (PAH's) - (naphthalenes, benzo-(a)-pyrene)
Alkanes, Waxes, Asphaltenes
- Synthetic Hydrocarbons
Organochlorine pesticides (DDT, Mirex, Toxaphene, Dieldrin)
Other Chlorinateds (Dioxin, Polychlorinated Biphenyls (PCB's))
Organophosphate pesticides, Phthalates
Other petrochemicals (butadienes, styrenes)
- Etc (the list goes on....)
-
5. DEFINITION
- Contamination is an excess
Pollution is a damaging excess
6. OVERVIEW OF PUGET SOUND STUDIES
Many lines of investigation since the 1960's. Important outcomes:
New "discoveries" occur as a result of first time monitoring/research
(they may have been there years ago, maybe even worse; Studies
have been leading to National recognition; decisions have to be
made, meanwhile science goes on, exploding past myths, producing
new information, ideas, priorities.
1950's 1960's 1970's 1980's 1990's
Anecdotal xxxxxxxxxxxxxxxx x x x x x x x x x x x
Oyster Treatment xxxxxxxxxxxxx
Pulp Mill Pollution xxxxxxxxxxxxxxxxxx
Outfall Monitoring xxxxxxxxxxxxxxx x x x x x
Water Quality Monitoring xxxxxxxxxxxxxx x x x x X
Bioaccumulation x x x xxxxxxxxxxxx
Fish Diseases x x x x xxxxxxxx
Sediment Contamination x x x xxxxxxx
Shellfish bacteria x x x xxxxxxx
Sediment Toxicity x x x xxx
"Mussel Watch" x x xxxxxxxx
"Superfund" Site Invest. xxxxxxx
Historical Sediment Cores x x
7. Puget Sound in national perspective: Map of PAH's in US Mussels
and Oysters

NOAA's National Status and Trends Program uses shellfish to monitor
contaminant trends at over 250 sites around the US. Puget Sound
contains mussels with a wide range of levels of PAH contamination,
comparable to other larger major urban areas. Dominant sources
apprea to be combustion, spills, urban runoff. For other contaminants,
such as heavy metals, the Sound is relatively clean compared to
other urban coastal areas.
8. Sources of Contaminants: Example -NPDES Sites.
The National Pollutant Discharge Elimination System permits over
100 municipal and industrial discharges into waters of the basin.
They have to meet many criteria. Source: US EPA GIS data base
(see references)

9. Sources of Contamination: Example - Superfund Sites
Over a dozen sites, mainly in the southern half of the basin and
many are military and most are inland, away from the shoreline
(but possibly in the path of salmon). Source: US EPA GIS data
base (see references)

10. Sources of Contaminants: Example - Map of Oil Spills, 1991-92
Map of amounts of oil spilled during one year (1991-92); This
was a particularly bad time for spills in Puget Sound and adjacent
waters. Commencement Bay topped the list but others occurred in
Seattle, Everett, Kitsap Peninsula and offshore in the ocean.
Source: Figure 2.4, page 20, State of the Sound 1992 Report, Puget
Sound Water Quality Authority, Olympia.

STATUS OF EFFECTS ON FISH
Few studies have demonstrated large-scale effects of chemical
contaminants on fishery populations. One of the few is by Prager
and MacCall (1993). They found evidence that DDT may have contributed
to the demise of the Pacific sardine in California ("Cannery Row"
days). It has since recovered. Salmon present a different challenge.
11. What kinds of effects should we look for in salmon?
Physiology, growth, reproduction, disease, contamination, are
all responses of fish to pollutants.

12. Where should we look for effects of contaminants on salmon?
The bigger the "X" the higher the chance for exposure and effects.
The places to look for effects of pollutants on salmon are where
the salmon go. Most critical may be the vegetated urban shorelines
and upstream.
13. Slow growth of juvenile salmon in the Duwamish Waterway.
Slower here than in less contaminated Nisqually River tidal area.
This and related impacts (immunosuppression, enzyme alterations,
etc) summarized in Casillas et al., 1995 (See 1995 Puget Sound
Research Conference papers ).
14. Tissue contamination: PCB's in adult salmon.
Concentrations have been higher than in resident species such
as English sole. May be do to biomagnification and their higher
position on the food chain than English sole, and/or to higher
lipid content of salmon? Source: O'Neill et al., 1995 (below).TRENDS

With notable exceptions Puget Sound chemical contamination is
decreasing and has been doing so for several decades. I prepared
the accompanying viewgraphs from data on concentrations of contaminants
in one of six dated cores taken in 1991 as reported by Lefkovitz
et al (1995 and 1997 and as summarized in Crecilius et al., 1995;
see references, below). "Core 3" was taken from a point in the
deep basin of Puget Sound located several miles due east of downtown
Seattle and within several miles of the West Point Outfall. It
was cut into 25 sections and each section dated using special
radiochemistry methods. The oldest date is about 1890 (with an
error of plus or minus 3-4 years).
15. and 16. Metal Contamination History
Metals are natural constituents of sediments. Contamination by
seven metals (silver, arsenic, copper, mercury, lead, antimony
and zinc) began around the turn of the century, reached a maximum
in the mid-1900's and have been decreasing since. Concentrations
of copper, lead, antimony and zinc declined significantly in the
past 20 years. When "normalized" 1890 concentrations, only five
showed levels of contamination more than twice background; all
the others varied within the natural range.


17. PCB's and Pesticides
Polychlorinated biphenyls (PCB's) are a group of over 200 synthetic
compounds, some mutagenic and carcinogenic (cancer promoting).
Although their used was banned in the 1970's they are persistent
and remain contaminants of concern. PCB contamination in the bottom
of Puget Sound peaked during the early 1960's and have declined
since; levels are about what they were at the onset of World War
II.
DDT and other related persistent pesticides experienced a similar
rise and fall, with the peak period of contamination occurring
before 1960. Levels are about what they were in the 1930's.

18. PAH's and Marker Chemicals
Polycyclic aromatic hydrocarbons (PAH's) include over 40 chemical
compounds many of which are toxic and some of which are carcinogenic.
They occur in coal, oil and fuel and certain kinds increase greatly
during combustion. PAH concentrations in the Sound peaked during
World War II and then decreased. Today levels are about what they
were in the 1920's. However, the sources may be different (for
example combustion runoff vs coal).

Terpenes, also natural chemicals, mark contamination from forest
industries. Again, concentrations peaked during 1940 to 1960 and
have slowly decreased since.
Hopane is a natural non-degradable chemical in oil and fuel and
may mark the cumulative history of oil and fuel spills, again
peaking in the 1940-60 era and declining slowly since.
LAB's - linear alkyl benzenes - are chemicals in modern laundry
detergent. Thus, their recent rise indicates increasing detergent
use.
19. Trends for nitrogen (N), phosphorus (P) and total organic
carbon (TOC)
Throughout the course of urban development of the Basin there
has surprisingly been no dramatic increase in N , P or TOC. However,
there is a "statistically significant" increase of a few percent
in recent decades, yet concentrations are far below what has been
observed elsewhere in eutrophic and sewage-polluted situations.

20. How Clean is Clean??
This plot of recent trends in deep basin sediment copper offer
some suggestions. Since 1960 concentrations have been decreasing
from about 50 parts per million (ppm) toward a natural background
of 35 ppm. The lowest concentration (Effects Range-Low, ER-L)
in sediments that might elicit a toxic response (10% of the time
or less) is about 75. The level of more considerable concern (Effects
Range-Median, ER-M) is about 350 ppm. From this view, copper is
a non-problem and moving further away from one as well. With no
further action, it may approach "background" within the next decade.
Similar guidelines occur for many other chemicals and are being
used to set clean-up goals in more contaminated (inshore) sites.
21. How Effective Have We Been ?
Actions and legislation during the past 20 years probably helped,
but recovery was indeed started earlier.
22. Future: Report Outline Challenge
Much more work is needed to asses the extent to which salmon may
be, or have been impacted by pollution. This outline represents
topics that need to be addressed.
References
Cassillas, E., M.A. Arkoosh, E. Clemons, T. Hom, D. Misitano,
T.K. Collier, J.E. Stein and U. Varanasi. 1995. Chemical contaminant
exposure and physiological effects in outmigrant juvenile chinook
salmon from urban estuaries of Puget Sound. 657-677 In Volume
2, Puget Sound Research '95 Proceedings, Puget Sound Water Quality
Authority, Olympia.
Crecilius, E.A., V.I. Cullinan, L.F. Lefkovitz and C. Peden. 1995.
Historical trends in the accumulation of chemicals in Puget Sound.
825-831 In Volume 2, Puget Sound Research '95 Proceedings, Puget
Sound Water Quality Authority, Olympia.
Dexter, R.N., D.E. Anderson, E.A. Quinlan, L.S. Goldstein, R.M.
Strickland, S.P. Pavlou, J.R. Clayton, Jr., R.M. Kocan and M.
Landolt. 1981. A Summary of Knowledge of Puget Sound related to
Chemical Contaminants. NOAA Technical Memorandum OMPA-13. National
Oceanic and Atmospheric Administration, Boulder, CO. 435 pp.
Edmondson, W.T. 1991. The Uses of Ecology: Lake Washington and
Beyond. University of Washington Press. 329 pp.
(Read Chapters 1-4).
Lefkovitz, L.F., V.I. Cullinan and E.A. Crecilius. 1997. Historical
Trends in the Accumulation of Chemicals in Puget Sound. NOAA Technical
Memorandum NOS ORCA 111. National Oceanic and Atmospheric Administration,
Silver Spring, MD.
Llanso, R.J., S. Aasen and K. Welch. 1998. Marine Sediment Monitoring
Program 1. Chemistry and Toxicity Testing, 1989 - 1995. Publication
No. 98-323. Washington State Department of Ecology, Environmental
Investigations and Laboratory Services Program, Olympia. 101 pp
+ Append.
O'Neill, S.M., J.E. West and S. Quinnell. 1995. Contaminant monitoring
in fish: overview of the Puget Sound Ambient Monitoring Program
Fish Task. 35-50 In Volume 1, Puget Sound Research '95 Proceedings,
Puget Sound Water Quality Authority, Olympia.
Prager, M.D. and A.D. MacCall. 1993. Detection of contaminant
and climate effects on spawning success of three pelagic fish
stocks off Southern California: Northern anchovy Engraulis mordax,
Pacific sardine Sardinops sagax, and chub mackerel Scomber japonicus.
Fishery Bulletin (U.S.) 91: 310-327.
Puget Sound Water Quality Authority, Olympia, WA
o Annual Updates (including 1998)
o Puget Sound Research. Proceedings from Conferences (1988, 1991,
1995, 1998 (in prep)
US EPA GIS data base, Puget Sound Basin, from the Coastal Resources
Coordination Divsion, Office of Response and Restoration, National
Oceanic and Atmospheric Administration, Seattle.
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