For decades, sewage sludge has been dumped into the ocean as a means of recycling the water used and so that people did not have to find a way to store it safely. Sewage sludge is defined as “a mixture of water, inorganic, and organic solids removed from municipal wastewater by physical, biological, and/or chemical treatment and it and liquid effluent are the two products resulting from municipal wastewater treatment” (Guisti 1). The Ocean Dumping Ban, signed into law in 1988, prohibited ocean dumping after December 31, 1991. Dumping is currently banned in the United States, Sweden, Switzerland, and many other countries, but it is still done illegally in many places, including the United States. Many companies dump sewage sludge legally on land as a fertilizer once it has been properly treated. Until 1992, two dumpsites, one 106 nautical miles southeast of New York Harbor and one 12 miles southeast, were used for sludge disposal. Because legal sludge dumping was banned, the two sites provide researchers with a large study area to determine the effects that sludge has had on the aquatic environment.
There
are three levels of sewage treatment, with tertiary being the most effective
form of treatment. Most cities in the US used a combination of primary and
secondary treatments because tertiary is too costly. The cost per month per
resident for treatment up to the secondary stage is $18, where as for tertiary
treatment it is $46, which is quite a significant increase (Hartman 9). Primary
treatment includes the settling of sludge to remove the oil and grease that
remain at the top of the liquid. Secondary treatment occurs when the settled
sewage liquor is consumes using aerobic biological processes, mainly bacteria
and protozoa that consume biodegradable soluble organic contaminants and bind
to less soluble fractions, which are then filtered out. Tertiary treatment
includes sand filtration, lagooning of the liquid to cause more settlement, and
removal of nutrients such as nitrogen and phosphorus. After this process
occurs, the liquid water is returned to the environment and the solid sludge is
further treated, sometimes being dehydrated and turned into fertilizer pellets.
During
the dumping period, researchers found elevated levels of benthic communities,
including sea urchins, sea cucumbers, and star fish, which are able to make use
of the organic material in the sludge. There were also increased levels of
silver found in the sediment was “20 times higher at the site relative to an
unaffected reference area” (NOAA Research). While these numbers decreased once
dumping was stopped, elevated levels of silver and sediment-dwelling organisms
were found 50 nautical miles south of the dumpsite, indicating that the sludge
materials suspended in the water were transported south by the ocean currents.
This also indicated that the sludge affected not only the dumpsite, but also
many areas near the zone. Also, elevated levels of organic contaminants,
including PCBs, used as a dielectric and coolant fluid, PAHs, occur in oil, coal, and tar deposits, in
surface sediments around the dumpsite could still be detected. These pollutants
have “been associated with mortality, malformation, abnormal chromosome
division, and higher frequencies of mitotic abnormality in adult fish from
polluted areas compared with those from less polluted regions of the northwest
Atlantic Ocean” (Johnson 5). This can be seen in the lobsters in the 12-mile
site, which developed a shell disease that erodes the carapace that covers their
cephalothorax, as well as in “larval deformities in haddock reduced hatching
success and increased larval mortality in winter flounder, skeletal deformities
in Atlantic cod inhibited gamete production and maturation in sea scallops, and
reproductive impairment in Atlantic cod” (Johnson 5). This research should be a
obvious wake up call to most people, demonstrating the effect that treated
sewage has on our environment.
Once
the Ocean Dumping Ban was put in effect, people tried to find new ways to dispose
of sewage sludge. One of the most prevalent ways to do it is to use the sludge
in agriculture for a fertilizer. This form of disposal is not a tightly
regulated as it should be, because the run off from agriculture is bringing the
pollutants back to waterways after storms or the land being watered. If the
treated sludge that was dumped into the ocean is causing so many biodiversity
problems in the sea, why should we be using them on land? In order to properly
use treated sludge as fertilizer, one would need to know where it’s from, how
it was treated, and what it’s made of, so as not to cause contamination from
other sources. Often times sludge is brought to different places from other
places around the US, increasing the potential for contamination because sewage
sludge is treated differently in different cities. This potentially
contaminated sludge is what we’re using to grow our food supply with.
Often times the run off from these farms using treated sludge
finds it way back into the aquatic environment causing harmful algae blooms
that contribute to the eutrophication of submerged aquatic vegetation.
Chesapeake Bay is a great example of the effect of fertilizer and sewage
treatment run off. It was found by Short and Burdick that “eelgrass losses in Waquoit
Bay, MA with anthropogenic nutrient loading primarily as a result of increased
number of septic systems from housing developments in the watershed” (Short and
Burdick). Eutrophication of seabeds causes decreased “shoot density and blade
stature, [decreased] the size and depths of beds, and [stimulates] excessive
growth of macroalgae (Johnson 8). If eutrophication occurs, the amount of
dissolved oxygen in the water is significantly reduced, causing a reduction in
primary producers, such as eelgrass in Chesapeake Bay. The loss of primary
producers reduces the amount of secondary consumers that feed off of primary
producers, as well as tertiary consumers. The increase in algae blooms blocks
the primary producers’ food source, the sun, which in turn decreases the amount
of dissolved oxygen in the water, decreasing the secondary and tertiary
consumers ability to live.
We need to find different ways of
disposing of sewage that does not affect ocean biodiversity or our food supply.
There are many countries, such as Sweden, Egypt, and Germany, who are using
sewage sludge in novel ways. One country to look to for solutions is Sweden.
They have engineered a way to convert their sewage into sustainable gas and
power that they use to power about a thousand cars on the road, by upgrading
the sewage and injecting it into their gas lines that support eighteen filling
stations. They have created three ways of dealing with the sludge: “organic
sludge with a high dry solids (DS) content, which can be used as a biofuel; inorganic
sludge with a high phosphorus content, which can be used for agricultural
fertilizer; and liquid-containing soluble organic matter and the precipitation
chemical used in phosphorus removal” (International 1). The left over liquid is
returned to the treatment plant where its organic content provides a carbon
denitrification source, and its precipitation chemicals are reused during the
phosphorous removal process. Because the project eliminates the cost of sludge
disposal, it practically pays for itself. It also provides an energy surplus,
because the biofuel's energy value exceeds the energy consumed during the
process. If the United States and other countries could adapt their
Sweden’s sludge disposal methods, we could end the current degradation of our
waterways.
Works
Cited
Collie, Marcia, and Julie Russo. "Deep-Sea Biodiversity
and the Impacts of Ocean Dumping." Deep-Sea Biodiversity and the Impacts of
Ocean Dumping. N.p., 30 June
2000. Web. 29 May 2013.
Gina L. Giusti and Nancy J. Grasso, Alternatives to Ocean
Dumping: A Municipal Dilemma,
6 Pace Envtl. L. Rev. 157 (1988)
Hartman, Pamela, and Joshua Cleland. "WASTEWATER
TREATMENT PERFORMANCE
AND COST DATA TO SUPPORT AN AFFORDABILITY ANALYSIS
FOR WATER QUALITY STANDARDS." IFC International, 31 May
2007. Web. 12 June 2013.
"International: Sweden Creates Sludge
Products." Waste360 Home Page.
N.p., n.d. Web. 12
June 2013.
Johnson, Michael. "Impacts to Marine Fisheries Habitat
from Nonfishing Activities in the Northeastern
United States." NOAA Tech Memo.
N.p., 29 Oct. 2008. Web. 28 May
2013.
Short FT, Burdick DM. 1996. Quantifying, eelgrass habitat
loss in relation to housing development
and nitrogen loading in Waquoit Bay, Massachusetts. Estuaries 19(3):730-9
Is there any further reading you would recommend on this?
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