2011-05-19_Shareholder_Advocates_Declare_Fracking_Not_Sustainable_For_Enviro_or_Invest.pdf (application/pdf Object)

2011-05-19_Shareholder_Advocates_Declare_Fracking_Not_Sustainable_For_Enviro_or_Invest.pdf (application/pdf Object).

FOR IMMEDIATE RELEASE CONTACT: Glenn Turner, 917]817]3396
May 19, 2011 glenn@ripplestrategies.com
or Shayna Samuels, 718]541]4785
shayna@ripplestrategies.com
Shareholder Advocates Declare eFrackingf
Not Sustainable for Environment or Investment
Upcoming Shareholder Resolutions Examine Failures of Chevron, ExxonMobil,
and Ultra Petroleum to Disclose Environmental and Investment Risks of Fracking;
Urge Transparency and Accountability to Ensure Financial Sustainability
On Wednesday, May 25th resolutions filed by the shareholder advocacy group As You Sow will
be voted on by investors at the annual meetings of three U.S. energy corporations: Chevron,
ExxonMobil, and Ultra Petroleum. The resolutions ask for a report on the environmental and financial
risks of hydraulic fracturing (commonly referred to as gfrackingh) in natural gas drilling. Fracking is a
process of injecting a mixture of water, chemicals, and particles underground to create fractures
through which gas can flow for collection.
The shareholder votes will be taking place on May 25 at Chevron in San Ramon, California;
ExxonMobil in Dallas, Texas; and Ultra Petroleum in Calgary, Alberta. Resolution proponents filed
shareholder rebuttals with the SEC and produced investor fact sheets which are available for
ExxonMobil, Ultra Petroleum, and Chevron.
In the past year, thousands of documents obtained from the Environmental Protection Agency
(EPA) have revealed that the threats of fracking to the environment and public health are greater than
anticipated. The two critical issues.toxic chemicals used in fracking fluid and the disposal of
wastewater.have the most potential to limit expansion of this practice.
gHydraulic fracturing of each well requires moving millions of gallons of water, chemicals, and
wastewater,h says Michael Passoff, Senior Strategist with As You Sow. gFracking poses environmental
and health hazards at every step in its lifecycle and these impacts can result in very substantial business
risks as well. These shareholder resolutions are asking some of the leading energy corporations to report
on the real risks and costs of fracking.h
Shareholders are concerned that these potential environmental and health impacts will result in
regulatory, legal, financial, and reputational risks to the companies and want to know how the
companies intend to mitigate the risks associated with fracking.
In most cases, the EPA regulates chemicals used in underground injection under the Safe
Drinking Water Act. However, the 2005 Energy Policy Act stripped the EPA of its authority to monitor
hydraulic fracturing. It is the only industry to benefit from such an exemption. The New York Times
dubbed this the gHalliburton loophole,h alleging that former Vice President Dick Cheney shepherded this
provision through Congress. Dick Cheney was also formerly CEO of Halliburton, one of the companies
which pioneered fracking.
gFracking fluids typically contain known hazardous chemicals, including benzene and other
carcinogens, which can contaminate nearby water supplies,h says Sister Nora Nash of the Sisters of St.
Francis of Philadelphia, lead filer of the Chevron resolution. gTreatment plants in Pennsylvania have
accepted more than a billion gallons of toxic wastewater over the last few years and most of this went
to sewage plants that were not equipped to handle it.h The Chevron resolution was co]filed by As You
Sow, the Park Foundation, and 16 other members of the Interfaith Center on Corporate Responsibility.
gAs the use of hydraulic fracturing skyrockets, communities, regulators, and investors are
growing increasingly concerned about the environmental impacts of this process,h says Jon Jensen of
the Park Foundation in Ithaca, N.Y. and one of the co]filers of the ExxonMobil resolution. gShareholders
need assurance that companies are candidly disclosing these risks and are adopting best management
practices to minimize them.h The ExxonMobil resolution was co]filed by As You Sow and the Unitarian
Universalist Service Committee.
The shareholder resolutions contend that disclosure by Chevron, ExxonMobil, and Ultra
Petroleum are inadequate to enable investors to determine if the companies are taking the steps
necessary to reduce the financial risks associated with hydraulic fracturing operations. The same
resolution was co]filed by As You Sow and Trillium Asset Management at Anadarko Petroleum, but was
withdrawn when the company agreed to provide investors with the requested information.
gIn the absence of meaningful disclosure, investors have no way of fully assessing the risks and
rewards from investing in various companies in the energy sector, and are concerned about unpleasant
shocks to shareholder value,h says Larisa Ruoff of Green Century Capital Management. The Ultra
Petroleum resolution was co]filed by As You Sow and Green Century Capital Management.
# # #
As You Sow is a nonprofit organization that promotes corporate responsibility through shareholder
advocacy, coalition building, and innovative legal strategies. For more information visit
http://www.asyousow.org.

ISS – A REGULATORY DISASTER

ISS – A REGULATORY DISASTER.

A REGULATORY DISASTER

Following the BP oil disaster, federal agencies took steps that may have further compromised the health of cleanup workers and Gulf Coast residents.

A special Facing South investigation by Sue Sturgis and Chris Kromm

Riki-Ott_small.jpgWhen BP’s Deepwater Horizon oil rig blew up a year ago in the Gulf of Mexico, triggering the largest oil spill in U.S. history, Riki Ott — a marine toxicologist from Alaska — had a sinking feeling: Here we go again.

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Ott (photo at right) was touring the United States to promote her book Not One Drop, the story of what until then was the nation’s worst oil spill — the 1989 Exxon Valdez disaster, which spilled up to 32 million gallons of crude oil into Alaska’s Prince William Sound after a tanker ran aground.

Back then, Ott was working as a commercial salmon fisher in the area. She wrote extensively about the environmental and social fallout from Exxon Valdez, and founded several nonprofits to help Alaskan communities deal with the impact.

When BP’s failed rig began gushing oil into the Gulf, Ott’s first instinct was to turn away. “I didn’t want to go,” Ott told Facing South. “It hurt too much.”

But Ott managed to stay away for only 10 days. From news reports, she became convinced that many of the post-spill mistakes made in Alaska were being repeated in the Gulf — and putting the health of thousands of Gulf Coast residents in serious jeopardy.

Over the last year, Ott has been crisscrossing Gulf communities from Louisiana to Florida, collecting stories from hundreds of people. What she has learned has led her to believe there is an environmental health crisis unfolding in the Gulf that was exacerbated by the federal government’s failure to take appropriate action to protect cleanup workers and coastal residents.

“There are a lot of sick people in the Gulf, with reports of respiratory problems, skin rashes and other issues that won’t go away,” she says. “The federal government has done a huge disservice by pretending this isn’t a problem.”

exxonvaldez_cleanup_workers.jpgLacking a plan

Exhibit A of the government’s failure to address the BP disaster’s public health aftermath, Ott and others contend, are the medical problems now afflicting many of the workers mobilized to clean up the spill.

There are a potentially large number of people affected, as about 100,000 people went through cleanup worker safety training, according to the National Institute of Environmental Health Sciences.

The National Institutes of Health is currently undertaking a study looking at impacts of the BP spill on cleanup workers. But that research is geared toward helping prepare for future incidents that put workers at risk and not to helping those affected by the BP disaster.

The reported illnesses should have come as no surprise: People who were involved in the Exxon Valdez cleanup two decades ago (photo above) reported a flu-like respiratory illness that was dubbed “Valdez Crud,” the symptoms of which — coughing, burning eyes, chest pain, etc. — are consistent with exposure to toxic chemicals found in crude oil.

Over time, the acute health problems suffered by Exxon Valdez cleanup workers morphed into more chronic conditions including memory loss and cancer, which are long-term consequences of toxic chemical exposure.

Though there were no published, peer-reviewed studies conducted on Exxon Valdez cleanup workers, an unpublished pilot study done by a Yale graduate student in 2003 included a phone survey of 169 workers that found those with significant oil exposure or exposure to oil fumes were more likely to report symptoms of chronic airway disease than those with less exposure. Based on that finding, Ott told Congress that she estimates as many as 3,000 former Exxon Valdez cleanup workers suffer from spill-related health problems.

More recently, a study by Spanish scientists published last August in the Annals of Internal Medicine looking at fishermen who responded to the 2002 spill of 20 million gallons of oil from the Prestige tanker off the northwestern coast of Spain found that participation in the cleanup was associated with persistent respiratory problems such as coughing and shortness of breath.

The Spanish cleanup workers also showed chromosomal abnormalities in their white blood cells that increased with intensity of exposure.

The U.S. Agency for Toxic Substances and Disease Registry, a division of the Centers for Disease Control and Prevention, reports that exposure to benzene, a component of crude oil, causes damage to the blood, immune system and reproductive organs, and can lead to leukemia.

The Occupational Safety and Health Administration (OSHA), the federal agency in charge of protecting workers from on-the-job hazards, deployed personnel to the Gulf the week after the rig exploded. But even at the height of the cleanup effort, the cash-strapped agency had at most only 50 personnel assigned solely to the oil cleanup — far too few to comprehensively monitor the massive effort that stretched from Texas to Florida.

OSHA also worked with the National Institute on Occupational Safety and Health (NIOSH), a division of the Centers for Disease Control and Prevention, to establish rules regarding protective equipment and training for cleanup workers. But those rules were not always followed. Last July, for example, OSHA sounded an alarm over shortcuts in the required 40-hour training for cleanup supervisors.

“We have received reports that some are offering this training in significantly less than 40 hours, showing video presentations and offering only limited instruction,” U.S. Assistant Secretary of Labor for Occupational Safety and Health Dr. David Michaels announced last July.

A report [pdf] released last year by the Center for Progressive Reform (CPR), a nonprofit public and environmental health watchdog group, identified the “original sin” behind the compromise of cleanup workers’ health and safety as the limited role that OSHA and NIOSH played in the oil spill planning process laid out under the Oil Pollution Act of 1990.

Passed by Congress in the wake of the Exxon Valdez disaster, the act creates a National Contingency Plan that gives OSHA inspection authority after a spill and a role on national and regional response teams. However, the plan simply states that response actions should comply with OSHA standards but doesn’t set out any clear compliance mechanism. As a consequence, CPR found, too few cleanup workers were given adequate training on the use of personal protective equipment such as respirators.

“When cleanup crews first got to work on the beaches and on the water, there was no carefully considered plan for what protections they needed for the oil fumes and heat,” says CPR President Rena Steinzor, a professor at the University of Maryland School of Law.

But a lack of training about how to use protective gear wasn’t the only problem: In some cases, BP failed to even make gear available.

Kellie Fellows was one of hundreds of workers hired by BP to help clean up beaches in Mississippi last summer, and she later shared the story about her experience with the Louisiana Environmental Action Network (LEAN). During training Fellows and her co-workers were told that safety was a priority and that they would be provided with respirators and other protective gear.

But when it was time to go to work, there were no respirators provided — even though there was a strong smell of oil on the beach. Initially they were given Tyvek protective suits to wear but were instructed to pull them up only partway and to tie the arms around their waists; eventually they were told there was no danger and sent out without the suits. They were given only straw hats, safety glasses and gloves and sent to work.

Fellows’ job was to hold a trash bag while two men shoveled in tar balls. Once they collected about 20 pounds of tar balls, her assignment was to tie off the bag in a knot. But in order to do that, her bare arms repeatedly touched the oil-smeared bag. Eventually her arms became covered with oil, which also worked its way down inside her gloves. Her skin began burning.

“I wanted to be in a Tyvek [suit]. And they refused.”

When she reported the contamination to her superiors, no one seemed to know what to do. They ended up washing her hands with soap and bottled water, rubbing on a couple packets of burn cream, and sending her home for the rest of the day.

Fellows has been left with lingering headaches she attributes to the toxic exposures, and she believes many others are still experiencing health-damaging consequences — even though the managers denied the clean-up had anything to do with it.

“Everyone was given excuses,” Fellows says, “Oh, you have the flu, it’s going around, that kind of thing. Bronchial issues? Oh, well, it’s allergies. Every excuse known to man was given except for them to actually say this is coming from the oil.”

Louis Bayhi, a Louisiana charter boat captain, heard the same story after he was hired by BP to shuttle divers and scientists to the spill site, and later worked for BP’s Vessels of Opportunity program in direct cleanup.

Bayhi says he was told he didn’t have to wear a respirator since he wouldn’t be directly touching the oil, though he says the fumes still sickened him and his crew. Two co-workers passed out on his boat, were taken for emergency treatment, and never returned. He still doesn’t know what happened to them.

When crews would arrive back at shore, Bayhi says, BP medical staff would ask them how they were feeling. When they described headaches and other problems, they were told it was seasickness.

“I’ve been offshore pretty much all my life and I got sick one time because I ate Froot Loops and beer for breakfast. Other than that, I really don’t remember a time I got seasick.”

Plus, seasickness doesn’t continue onshore for months on end — but Bayhi’s symptoms have. Earlier this month, he spent five days in the hospital with severe abdominal pain. The doctors couldn’t figure out what’s wrong with him, but he suspects it’s related to his oil exposure.

Environmental health advocates say the kind of exposures cleanup workers suffered is unthinkable in this day and age.

“The workplace environment cleanup people were put in was totally unacceptable for 2010,” Wilma Subra, an environmental chemist who works with LEAN, told Facing South. “You had a responsible party with resources, and it should not have happened.”

chemical_dispersant_spraying.jpg‘Human health hazards: acute’

Adding to the toxic stew in the Gulf — and the health risks to cleanup workers and coastal residents — was the approach BP used, with government approval, to disperse the massive oil slicks stemming from the disaster.

Oil dispersants are a mix of surfactants and industrial solvents that cause oil to form into droplets and fall to the ocean floor. Less than a month after the Deepwater Horizon explosion, BP reported spraying more than 400,000 gallons of dispersant on the slick and wellhead itself — primarily two versions of Corexit, manufactured by Illinois-based Nalco.

Corexit EC9500A and Corexit EC9527A were both on the list of 18 dispersants approved for use on oil spills by the Environmental Protection Agency. However, as The New York Times reported, the EPA’s own data showed that Corexit was far more toxic — and far less effective — than other alternatives in handling southern Louisiana crude:

Of 18 dispersants whose use EPA has approved, 12 were found to be more effective on southern Louisiana crude than Corexit, EPA data show. Two of the 12 were found to be 100 percent effective on Gulf of Mexico crude, while the two Corexit products rated 56 percent and 63 percent effective, respectively. The toxicity of the 12 was shown to be either comparable to the Corexit line or, in some cases, 10 or 20 times less, according to EPA.

Considered a trade secret, the precise contents of dispersants like Corexit were initially hidden from public view and revealed to the Environmental Protection Agency last June only after extensive negotiations. However, OSHA requires that any ingredients which may be harmful to exposed workers be listed on readily available Material Safety Data Sheets. For both forms of Corexit used by BP — Corexit EC9500A and EC9527A — the data sheets include this warning: “Human health hazards: acute.”

OSHA’s data sheet for Corexit EC9527A [pdf] details the potential health consequences: “[E]xcessive exposure may cause central nervous system effects, nausea, vomiting, anesthetic or narcotic effects.” It also notes that this version of Corexit includes 2-butoxyethanol, stating that “repeated or excessive exposure to butoxyethanol may cause injury to red blood cells (hemolysis), kidney or the liver … Prolonged and/or repeated exposure through inhalation or extensive skin contact with EGBE [butoxyethanol] may result in damage to the blood and kidneys.”

By September 2010, BP reported spraying about 2 million gallons of dispersants for the spill — an unprecedented amount. And some Gulf scientists believe there is already evidence that it’s having adverse health impacts.

In July 2010, Dr. Susan Shaw — founder and director of the Marine Environmental Research Institute — told CNN about a shrimper who had water splash onto his skin:

…[H]e got a headache that lasted for three weeks. He had heart palpitations. He had muscle spasms and … bleeding from the rectum.

And that’s what Corexit does. It ruptures red blood cells, causes internal bleeding, and liver and kidney damage.

This stuff is so toxic combined [with oil] … it goes right through skin.

As with the risks to cleanup workers, the hazards posed by Corexit were already known. The United Kingdom had famously banned the used of the dispersant. A version of Corexit was also used after the Exxon Valdez disaster and implicated by cleanup workers and environmental advocates for the health problems they suffered after that disaster.

Even when faced with growing criticism about the use of such toxic elements on such an untested scale — especially near cleanup workers and coastal communities — government regulators appeared slow to address the hazards.

On May 26, the EPA and U.S. Coast Guard issued a directive telling BP to stop using surface dispersants — except in “rare cases where there may have to be an exception.” Yet as Rep. Edward Markey (D-Mass.) noted in a strongly worded letter sent to Adm. Thad Allen, the spill recovery commander, on July 30, exemptions were being routinely granted:

An analysis of the exemption request letters submitted by both the BP and Houma Unified Command, as well as other documents provided to me by the USCG, reveals that since the Directive was issued on May 26th, more than 74 exemption requests have been submitted and, usually within the same day, approved by the USCG. On 5 separate occasions BP submitted requests for pre-authorized exemptions to deviate from EPA and USCG instructions by applying 6,000 gallons of dispersant per day to the ocean surface for an entire week … In every instance this weekly request was approved by the USCG, and on many of these days, BP still used more than double its new 6,000 gallon limit.

The result? Dispersant use declined only 9 percent — even after federal officials had formally directed BP to stop using them in all but the most extreme circumstances.

Aside from the threats posed by immediate exposure, there’s concern about how long Corexit will linger. Dr. Shaw warns that such chemicals readily bioaccumulate — meaning they get stored in the fat tissue of marine organisms and get passed up the food chain, including to humans who eat fish.

And there were reports that dispersants were still being used and posing a health threat long after the spraying was supposed to have stopped. “I have received hundreds of reports about improper spraying,” says Subra with the group LEAN. “It was ongoing, and people are being made very, very sick.”

In August 2010, a month after the Joint Command for the oil spill says the spraying was supposed to have ended, Rocky Kistner with the Natural Resources Defense Council documented the presence of of large tanks of Corexit on Gulf beaches. Earlier this year, MSNBC also detailed accounts of Gulf residents who maintain the dispersant spraying continued long after July, with C-130s spraying within sight of beaches at night.

Subra says she has passed the reports she’s received about the spraying to the EPA. However, the agency has refused to discuss the matter with her, saying only that it’s part of an ongoing criminal investigation.

lmrk_seafood_sampling.pngJust four jumbo shrimp a week

Another potential health risk for people in the Gulf Coast and beyond is the safety of the region’s seafood.

At a press conference held last September, National Oceanic and Atmospheric Administrator Jane Lubchenco declared that seafood from the Gulf was “free of contamination.” NOAA echoed the sentiment earlier this month, when it led reporters on a tour of testing facilities in Mississippi and declared that “not one piece of tainted seafood has entered the market” due to the BP spill.

But as Subra points out, test data from the federal government and state agencies contradicted at least the earlier assertions. Twenty-four percent of all Gulf seafood and 43 percent of all Gulf oysters sampled through August 2010 contained polycyclic aromatic hydrocarbons (PAHs), a natural constituent of crude oil and a byproduct of burning fuel. The ATSDR reports that PAHs are known to cause cancer as well as birth defects and damage to the skin and immune system.

While the concentrations detected fell far below the levels of concern established by the Food and Drug Administration, those levels are another source of controversy.

To set its safe consumption levels for Gulf seafood in the wake of the BP oil spill, the FDA measured the levels of PAHs in the seafood against the national average of seafood consumption — about 3 ounces a week. That’s the equivalent of four jumbo shrimp.

But the typical Gulf Coast family — especially in fishing communities — eats much more seafood than that. A survey in late 2010 by the Natural Resources Defense Council of 547 seafood eaters in the Gulf found the median consumption was about 20 seafood meals a month. Those at the higher end consumed up to 60 seafood meals a month. And their portions were bigger than just four jumbo shrimp.

“Those levels are clearly not designed to deal with the situation on the Gulf Coast,” says Subra. “It’s not protective enough.”

What’s more, the estimate is based on the person eating the seafood weighing an average of 176 pounds. What about children? People who weigh less? Pregnant women and their developing fetuses? Yet federal and state health officials insist their measures are conservative and adequate to protect the public.

LEAN has been conducting its own tests of seafood from the Gulf, looking at PAHs as well as total petroleum hydrocarbons, which the FDA is not testing for. It tested only seafood that appeared pristine and neither looked nor smelled suspicious.

LEAN found that levels of total petroleum hydrocarbons in flounder and speckled trout caught in Louisiana’s St. Bernard Parish last August were 21,575 milligrams per kilogram, while oysters caught in Plaquemines Parish showed levels of 12,500 mg/kg. Petroleum levels found in fiddler crabs and periwinkles harvested from Terrebonne Parish on Aug. 19 were 6,916 mg/kg. LEAN notes that there shouldn’t be any detectable levels of petroleum hydrocarbons in seafood.

The prospect of contaminated seafood continues today: At a public meeting held late last month in Grand Isle, La. as part of the Natural Resource Damage Assessment process that’s now underway, shrimpers reported pulling up nets full of oil from the seafloor and facing the decision of whether to report the oil to the Coast Guard, which would mean throwing away the day’s catch, or keeping quiet.

Subra is among those who aren’t taking any chances.

“I don’t eat seafood now from the Gulf or from coastal areas,” she confesses. “I still eat crawfish, but that’s freshwater.”

* * *

TOMORROW: BP’s spill is not the oil industry’s only threat to the health of Gulf Coast residents.

* * *

Sue Sturgis is an investigative reporter and editorial director of Facing South, and Chris Kromm is Facing South’s publisher. This piece is the second installment in an in-depth, week-long series by Sturgis and Kromm on the growing health crisis in the Gulf in the wake of the BP disaster and the government’s failure to respond adequately. To read the first piece, click here.

* * *
(PHOTOS: From top, Riki Ott from www.rikiott.com; Exxon Valdez cleanup workers from NOAA via Wikimedia Commons; C-130 spraying chemical dispersants on BP spill from U.S. Air Force; Gulf seafood being sampled by Jeffrey Dubinsky for the Lower Mississippi Riverkeeper.)
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EnerSol Technologies, Inc.   PEPS® and PEGS™ Plasma Enhanced Systems

EnerSol Technologies, Inc.   PEPS® and PEGS™ Plasma Enhanced Systems.

Daily Kos: Leaked Congressional Report: Even ‘Fracking’ Companies Can’t Identify All the Chemicals They Use

Daily Kos: Leaked Congressional Report: Even ‘Fracking’ Companies Can’t Identify All the Chemicals They Use.

Vote Solar – New York Solar Jobs Act of 2011

Vote Solar – New York Solar Jobs Act of 2011.

New York Solar Jobs Act of 2011

Take ActionNYStickerRoundv2Help New York go solar! Tell your state lawmakers that you support the Solar Jobs Act today — S.4178 & A.5713 (View bill text here)

With rising electricity needs, plenty of sunshine, and a local workforce primed for green jobs, New York has what it takes to lead the new solar economy. But the state has a policy structure that’s supported less than 54 MW of installed solar to date. That’s not even 0.1% of New York’s electricity mix. New Jersey installed more than twice that much solar in 2010 alone.

The Empire State is missing a tremendous opportunity to invest its energy dollars in local jobs, economic opportunity and a brighter future for the state. New York can and should use smart solar policies to go further.

The Solar Industry Development & Jobs Act of 2011 provides a much-needed blueprint for solar leadership by:

  • SolarWorkersSetting a strong solar target of 5,000 MW – enough to power 500,000 average households and equivalent to 3% of the state’s total electric load.
  • Establishing annual interim targets that ramp up to meet that impressive solar end goal at minimum cost and maximum benefit to New York ratepayers.
  • Supporting a broad spectrum of business models and technologies to serve the residential, commercial and utility sectors. This design feature enables diverse participation and supports a strong, competitive local solar market.

Altogether it’s a recipe for creating tens of thousands of new local jobs and billions in economic output – all while reducing harmful emissions and reliance on fossil-fuels.

•Create tens of thousands of new high quality jobs, from manufacturing and design to construction and operation.
•Generate a multi-billion dollar boost in wages and economic output that could be reinvested in New York’s economy.
•Deliver maximum solar benefits at minimum cost to New York electricity consumers.
•Decrease the state’s production of harmful emissions by reducing the need for fossil fuel based electricity generation, especially at times of peak energy dema

Additional Resources:

Fact Sheets:

Press Highlights:

Press Releases:

Blogs to Watch:

Partner Resources:

The New York Solar Industry Development and Jobs Act of 2011 is supported by a broad coalition of industry, environmental and public health organizations, including:

Alliance for Clean Energy New York (ACE NY), the American Lung Association in New York, Citizens Campaign for the Environment, Environmental Advocates of New York, Environment New York, New York Interfaith Power and Light, New York League of Conservation Voters, New York Solar Energy Industries Association, Natural Resources Defense Council, Pace Climate and Energy Center, Physicians for Social Responsibility – New York Chapter, Renewable Energy Long Island, Solar Alliance, and the Vote Solar Initiative. 

Waste2Energy

Waste2Energy.

Plasma arc waste disposal – Wikipedia, the free encyclopedia

Plasma arc waste disposal – Wikipedia, the free encyclopedia.

Biomass Power and Thermal | Biomassmagazine.com

Biomass Power and Thermal | Biomassmagazine.com.

Landfill Eliminators

The process is called plasma gasification and the technology for creating and harnessing plasma has been around for decades. However, plasma gasification technology is now being used for a new purpose-the conversion of municipal solid waste-to-energy.
By Jessica Ebert

Plants that use extremely high temperatures to turn municipal solid waste (MSW) into electricity are springing from the soils of countries around the globe including Canada, Spain, the United States and Japan. Although the process technologies and temperature ranges employed at these facilities vary, the basic concept is the same: MSW goes in, electricity comes out. In addition, unlike incineration few, if any, emissions are produced and little, if any, of the remaining material needs to be landfilled.

As farfetched as it may sound, the technology for producing plasmas dates back nearly a century. Plasmas are gases that have been heated to the point of ionization-meaning they are composed of charged particles such as electrons that can conduct electricity and generate tremendous amounts of heat. Lightning is an example of naturally occurring plasma. Since the early 1900s, plasmas have been used to melt metals and to make acetylene fuel from natural gas. In the 1960s, NASA developed plasma technology to simulate the intense heat of re-entry for testing the durability of certain pieces of shuttle equipment. The technology continues to be used in the metal and chemical industries and has now begun to filter into waste management.

In the latter case, the scenario goes something like this: MSW is shredded into one- to two-inch waste strips, which are dumped into a steel cylinder. This cupola is typically equipped with two torches near the bottom or top, which protrude like perches in a canary cage. These torches house electrodes, and when a continuous flow of electricity is applied, an arc forms between them. The air in the torch pushes this extremely hot artificial bolt of lightning into a furnace, where the MSW enters. The torrid temperatures generated by this process, which can be hotter than the surface of the sun, rip apart compounds and convert inorganic solids into a glassy obsidian-like rock that can be used in road construction. The process also transforms organic materials into syngas that can be used to make electricity and liquid fuels. Since the entire process is closed to the atmosphere, no emissions are released during the conversion of MSW to syngas and slag. “Plasma processing of MSW has unique treatment capabilities unequaled by existing technologies,” says Lou Circeo, director of plasma applications research at Georgia Tech Research Institute. “Plasma gasification could revolutionize the whole field of waste management.”

That’s certainly the hope of city planners, county commissioners and their comrades worldwide who feel the crunch of ever diminishing landfill space. The city of Ottawa for instance, has partnered with Plasco Energy Group Inc., a private high-technology company based in Canada, to process 85 tons of MSW per day over the next two years. The company holds 19 patents for its process technologies including one for the overall plasma gasification system, explains Rod Bryden, president and CEO of the company. Bryden, who owned Ottawa’s National Hockey League team from the time it was an expansion franchise until about two years ago, has been building businesses since 1974. “Plasma-based technologies have been around for some time but I saw the opportunity to create a conversion business that would deliver environmental quality while creating net energy for sale,” he says.

Plasco broke ground for the new demonstration facility in September 2006. Construction was completed in June and the plant, which covers three acres of grassland across the road from the Trail Road Landfill southwest of Ottawa, started in July. The plant began receiving waste from city trucks in late September.

Process Variation
The Plasco plasma gasification process differs from the general scheme previously described. Instead of directly dumping the shredded MSW into a plasma torch chamber, Plasco’s process uses a separate gasification chamber to heat the strips of waste to about 700 degrees Celsius (1,292 degrees Fahrenheit). In this step, some components of the MSW such as water are converted into gas while everything else is transformed to ash. The gas rises to a vertical chamber that holds two plasma torches, which blast the gas into its basic elements. Some of these elements reform into syngas, a mixture of carbon monoxide and hydrogen. Before the syngas can be scrubbed of heavy metals such as mercury, cadmium and lead as well as other undesirable chemicals like chlorine and sulfur, the syngas is cooled. Some of the heat released during this cooling is shuttled back to the initial chamber. This is the only process that recycles heat to convert waste into syngas, Bryden explains. “We don’t use these plasma torches to generate gas,” Bryden explains. “We use these plasma torches to refine the gases that have already been released from the waste.” Refining gases rather than whole MSW requires less heat from the torches, which saves energy. “This is one of the reasons our system produces so much more power than it consumes.”

The ash from that first gasification chamber is transferred to a separate plasma torch compartment where it is converted into syngas and a hard glass-like material that is broken into pieces and sold for use as a construction aggregate. All the syngas that’s produced is collected and piped to a bank of generators that converts it into electricity. In the end, out of 100 tons of MSW that enters the system, 4 megawatts (MW) of electricity are sold to the grid and used to power about 3,600 homes, 1 MW of electricity is used to power the plant, 15 tons of slag aggregate is produced and sold, and 500 kilograms (kg) of sulfur is sold as fertilizer. In addition, 1 kg of ash-made up of heavy metals-is landfilled. “You could fit a day’s disposal requirement in the glove compartment of your car,” Bryden says.

The plant in Ottawa will run for two years at which time the city will either dismantle the facility, continue to use it for MSW treatment or operate the plant as a development facility for the processing of other energetic materials that pose disposal challenges such as paper mill waste and the sludge from sewage treatment. In addition, Plasco has a memorandum of understanding with a waste management company in Spain to build a plant in Barcelona that will process 200 tons of MSW per day and two other contracts are in the works for plants in Canada. “We expect that by October we’ll be moving forward with commercial plants in a number of places,” Bryden says.

Growing in Popularity
Over the past several years, about 12 commercial plasma waste processing facilities have been operating in Europe and North America, and about 10 in Asia. The waste processed at these facilities varies and ranges from MSW to medical waste, catalytic converters, asbestos and ammunition.

The largest facility in the world to date is slated for start up in 2010. The plant will be built in St. Lucie County, a beach destination along Florida’s south-central Atlantic coast. On April 10, Geoplasma LLC, an energy developer based in Atlanta, Ga., signed an agreement with the county. The company will finance, permit, construct, own and operate the $425 million MSW-to-energy plant for 20 years.

The new plant will be constructed in two stages. The first will likely start up in the winter of 2010 and will process at least 1,000 tons of MSW each day and produce enough electricity to power about 25,000 homes. Each gasifier unit will house up to six plasma torches and will process between 500 to 750 tons of waste. Within five years, Geoplasma intends to scale-up the plant by adding more gasifier reactors. At this time, the plant, which will stand on about eight acres, will process 3,000 tons of MSW per day, two-thirds of which will come from the existing landfill. “We’ll be able to consume the landfill within our 20-year contract. This will be the first time that a landfill like this has been recovered to our knowledge,” explains Hilburn Hillestad, president of Geoplasma.

The plasma torches and gasification reactors for the modules will be supplied by Westinghouse Plasma Corp., the technology developer Geoplasma has teamed with. Westinghouse has been in the plasma gasification business since the 1960s. The company’s technology is being used in two waste processing facilities in Japan and in a General Motors Corp. plant in Definance, Ohio, for scrap metal melting. The torches in the latter plant have been in use for 17 years and the electrodes have been in use for more than 500,000 hours. Westinghouse was recently acquired by Alter Nrg Corp. of Canada and Geoplasma will be the exclusive marketer for the Westinghouse technology in Canada and the United States, Hillestad explains.

“The technology is proven and reliable,” says Shyam Dighe, president and chief technology officer for Westinghouse Plasma Corp. Although the technology has been around for a while, “now, several factors have come together to make plasma gasification like a perfect storm,” he adds.

Hillestad agrees with Dighe and adds that “over the past few years we’ve seen a steep increase in energy prices in this country and worldwide. Before those energy prices spiked the natural gas community generated a lot of power with natural gas and we couldn’t compete with that. Now, however, our syngas can compete with natural gas to generate electricity. It’s the most sustainable alternative technology for disposing of MSW that we know of at a time when we critically need alternative energy supplies.”

Jessica Ebert is a Biomass Magazine staff writer. She can be reached at jebert@bbibiofuels.com or (701) 746-8385.

1 Responses

  1. Pier

    2011-01-20

    1

    I introduces plasma waste Italy,but many universities professor like inceneritors and petrol companies like conventional or pyrolisis gasification.For me landfills eliminator is only plasma waste 7°generation cool plasma modular systems. Cost:for me a plasma plant 4000 t/day cost 500 millions dollar. 40 plasma plant cost 20 billions to recycle 160.000 tons day and produce 40.000 MW or 7,6 billions plasmafuel via syngas. I search a Us-Canada Company to confirm and building this plasma gasification Italian project.Pier caffit@alice.it

Cortland Homer Preble Sole-Source Aquifer System

Water | Region 2 | US EPA.

Cortland Homer Preble Sole-Source Aquifer System

Support Document

  Cortland and Onondaga Counties New York

June 1988

I. Introduction

A. Statement of Section 1424 (e)

The Safe Drinking Water Act (SDWA), Public Law 93-523, of December 16, 1974 contains a provision in Section 1424(e), which states that:

If the Administrator determines, on his own initiative or upon petition, that an area has an aquifer which is the sole or principal drinking water source for the area and which, if contaminated, would create significant hazard to public health, he shall publish notice of that determination in the Federal Register. After the publication of any such notice, no commitment for Federal financial assistance (through a grant, contract, loan guarantee, or otherwise) may be entered into for any project which the Administrator determines may contaminate such aquifer through a recharge zone so as to create a significant hazard to public health, but a commitment for Federal financial assistance may, if authorized under another provision of law, be entered into to plan or design the project to assure that it will not so contaminate the aquifer.

This section allows for the specific designation of areas which are dependent upon ground water supplies. Following designation, the review process will ensure that federal agencies will not commit funds toward projects which may contaminate these ground water supplies.

B. Receipt of Petition

On September 15, 1987 the Cortland County Legislature petitioned the U.S. Environmental Protection Agency (EPA) Administrator to declare the Cortland-Homer-Preble Aquifer System, as defined in the petition (Appendix A), a sole source aquifer (SSA) under the provisions of the SDWA.

C. Area of Consideration

The boundary of the area specified in the petition submitted by the Cortland County Legislature was defined as portions of five valleys that meet in the vicinity of the City of Cortland. The entire petitioned area is within Cortland County, New York. However, based on EPA’s review of the hydrogeologic information, the final SSA designation area has been extended into Onondaga County. The Agency has amended the area for designation because the aquifer extends into Onondaga County. It has beenAgency policy to designate sole source aquifers based on hydrogeologic criteria rather than political boundaries whenever possible, because contamination of a portion of the aquifer can affect the down gradient portion of the aquifer.

D. Topography

The Cortland-Homer-Preble area is located within the Allegheny Plateaus Province of central New York State (Miller, 1982). Altitudes range from approximately 1,100 to 2,000 feet above sea level.

The entire area was affected by the Wisconsin Stage glaciation (Buller et.al., 1978), ending approximately ten-thousand years (10,000 yrs.) ago (Muller, 1965). The glaciers altered the existing topography and surface water drainage patterns. The resulting terrain consists of relatively flat, sedimentfilled valleys bounded by tillmantled bedrock hills that rise up to nine-hundred (900) feet above the valley floors (Buller et.al., 1978; Miller, 1982).

E. Climate

Precipitation in the Cortland-Homer-Preble area averages approximately forty inches (40″) per year (Buller et.al., 1978), evenly distributed throughout the year (McFarlandJohnson Engineers, Inc., 1982). Winters are harsh, with an average temperature of approximately twenty-four degrees degrees Fahrenheit (McFarlandJohnson Engineers, Inc., 1982) and average snowfall of sixty inches (60″) (Buller et.al., 1978). Temperatures in summer average approximately sixty-six degrees Fahrenheit (McFarland Johnson Engineers, Inc., 1982).

II. Hydrogeology

A. Geologic Framework

The bedrock of the Cortland-Homer-Preble area is predominantly shale, with minor siltstone and fine grained sandstone (Corner and Harsh, 1978; Miller, 1982). These rocks are part of the Genesee Group (Reynolds, 1985) and are Upper Devonian in age (Buller et.al., 1978). The beds are nearly flatlying, with a less than one degree to the southsouthwest (Bul..al.. 1978).

Depth to bedrock ranges from zero to five-hundred feet (0-500′) below the land surface (Corner and Harsh, 1978; Miller, 1982). The bedrock is nearest the surface in the hills and deepest in the valleys. When exposed at the surface, the shale is weathered and jointed (Corner and Harsh, 1978). Joints and bedding planes provide the only storage areas for significant amounts of water in the bedrock. Because the size and number of joints decrease with depth (Corner and Harsh, 1978) and are open to depths less than one-hundred feet (100′) below land surface (McFarlandJohnson Engineers, Inc., 1982), wells drilled into the bedrock are lowyielding (generally ten to fifty gallons per minute (Buller, 1978: McFarlandJohnson Engineers, Inc., 1985)).

B. Geologic Setting

The area was subjected to glaciation to glaciation during the Wisconsin Stage Pleistocene Epoch. Much of the bedrock is concealed under the glacial deposits. These deposits are thickest in the valleys.

Several types of deposits were left by the glaciers. Each is described below (descriptions from McFarlandJohnson Engineers, Inc., 1982):

Stratified Drift: The aquifers that can support public water supply wells are composed of stratified drift and outwash deposits. Stratified drift is the fairly wellsorted sand and gravel found along the valley walls. It was deposited by streams flowing between the glacier and the bedrock hills.
Outwash Deposits: Outwash is sand and gravel deposited by streams flowing from the face of the melting glacier. It is extensive in the Cortland-Homer-Preble area, filling the valleys with continuous deposits up to two-hundred feet (240′) thick. Outwash deposits comprise the most productive aquifers in the area.
Till: The most widespread glacial deposit is till, an unsorted mixture of silt, clay, sand, gravel, and rock fragments. In Cortland County, the till is mainly silt and clay, and has low permeability. The till therefore enhances runoff from the upland areas and limits recharge to the bedrock. Till is exposed in the uplands portion of the area.
Moraine: Material pushed in front, or to the side of the advancing glacier forms a moraine. Moraines generally represent the furthest advance of a glacier. In the Cortland-Homer-Preble area, moraines are found at valley heads. They are comprised of the redeposited material left by previous glacialactivity, and consist of stratified sand and gravel interbedded with poorly sorted silt and clay. Because of low permeability, the moraines act as ground water divides.
Glacial Lake: Glacial lakes were formed in the valleys as the glacier retreated, because the existing drainage outlet had become closed by moraine deposition. Lake sediments, consisting of finegrained sand, silt and clay were deposited. These sediments, which range from ten to three-hundred feet (10-300′) thick, have low permeability and act as a confining unit between aquifers.

C. Ground Water Hydrology

Ground water moves through inter-granular openings in the unconsolidated deposits and through cleavage planes, joints and fractures in the consolidated rocks of the area. As stated above, the yield from bedrock wells in the Cortland-HomerPreble area is low. However, the yield is sufficient for domestic supplies and upland wells are completed into bedrock (Buller, 1978).

The most productive aquifers in the area are the outwash sands and gravels found in the major stream valleys. In the HomerPreble valley, it is the surficial outwash aquifer that provides the majority of drinking water. Its saturated thickness averages fifty-five feet (55′) (Buller et.al., 1978) and yields may exceed one-thousand gallons per minute (1,000 gpd) (Miller, 1982). The base of the aquifer is defined by a lacustrine clay layer at a depth of approximately sixty feet (60′) below the land surface (Buller, 1978). There is a thin layer of sand between the clay and bedrock; its potential as a source of water is unknown (Miller, 1982).

In the southern portion of the area, there is a confined outwash aquifer as well as a surficial outwash aquifer. Both are present within the City of Cortland and the valleys of the East and Main Branches of the Tioughnioga River (Reynolds, 1987). Current well yields are as high as four-hundred gallons per minute (400 gpm) (McFarlandJohnson Engineers, Inc., 1985).

Southwest of the City of Cortland, the sands and gravel of the aquifer have been interpreted to represent kame terraces and icedisintegration deposits (Miller, 1982).

The water table in the Cortland-Homer-Preble area generally occurs at depths less than twenty-five feet (25′) below the land surface in the major stream valleys (Buller, 1978; Buller et.al., 1978; Miller, 1982; McFarlandJohnson Engineers, Inc. 1985). In the upland areas, the water table may be as deep as one-hundred feet (100′) below the land surface (McFarlandJohnson Engineers, Inc., 1985), although this is still well above the valley floors.

Although the relatively impermeable till limits infiltration, recharge to the upland ground water system is derived from precipitation (McFarland-Johnson Engineers, Inc, 1985). In the valleys, the surficial aquifer is recharged by infiltration of precipitation, infiltration from losing streams, and upland sources (Buller et.al., 1978), such as runoff and streams from the hills (McFarlandJohnson Engineers, Inc., 1985; Reynolds, 1987) and very minor recharge from the bedrock (Buller et.al., 1978; Miller, 1982. According to Reynolds (1987), the confined aquifer (where present) is recharged by the surficial aquifer wherever they are in hydraulic contact. This occurs through the stratified drift deposits along the valley walls, which connect the two aquifers, and wherever the confining lacustrine unit is absent.

In the upland areas, the ground water flow is toward and into the streams (Buller et.al., 1978; McFarlandJohnson Engineers, Inc., 1985). Upland streams are gaining (i.e., they act as ground water sinks) (McFarland-Johnson Engineers, Inc., 1985). Once they reach the valley floors, however, some of the water recharges the aquifer (Buller et.al., 1978).

In the major valleys, ground water flows toward the center from the valley walls (Buller et.al., 1978). There is also flow in the river’s downstream direction (Buller et.al., , 1978; 1978; Corner and Harsh Inc., 1985; Reynolds, 1987). After the valleys meet near the City of Cortland, flow is southeast, following the Tioughnioga River valley out of the area (Buller et.al., 1978).

1. Recharge
The recharge area is delineated by the designated valleys and the upland area which drain into them. All precipitation within these boundaries has the possibility of recharging the aquifer system.

2. Discharge

Discharge from the aquifer system is by seepage into gaining reaches of streams, evapotranspiration, flow to pumping the area wells and flow out of the area (Buller et.al., 1978; McFarlandJohnson Engineers, Inc., 1985; Reynolds, 1987).
3. Streamflow Source Zone
The streamflow source zone is the upstream area of losing streams which flow into the recharge area. For the Cortland-Homer-Preble Aquifer System, this area is defined as the portion of the Tioughnioga River basin upstream of the southeastern end of the designated area (near Blodgett Mills), as shown on Figure 1. The project review area is coincident with the designated aquifer area, its recharge area, and streamflow source zone.
D. Ground Water Quality

Data provided by the Cortland County Health Department (CCDH) in the petition indicate that all of the ground water in the area contains less than three-hundred milligrams per liter (300 mg/l) total dissolved solids and ranges in temperature from three to nine degrees Centigrade. The pH ranges from slightly acidic to slightly alkaline water varies from moderately to very hard (6.5 to 8.0). The water varies from moderately to very hard (85 to 250 mg/l).

The overall quality of the ground water is good, although there has been contamination of several private wells in the southwestern portion of the area by organic solvents (up to (200 parts per billion). All public water supply wells meet or exceed the appropriate State and Federal drinking water standards.

E. Designated Areas

The area that has been designated as the Sole Source Aquifer is defined as the stratified drift and glacial outwash within the valleys. This area is coincident with that identified as a Primary Water Supply Aquifer by New York State Department of Health (1981) and New York State Department of Environmental Conservation (1987). The aquifer service area is the same as the aquifer area. Figure 1 shows the location and boundaries of the designated area.

F. Ground Water Use

Table 1 shows the population served and the amount of water withdrawn by public water suppliers within the Aquifer Service Area (ASA). Table 2 shows the estimated population within the ASA relying on private wells. Water use for the population using private wells is estimated based on one hundred gallons per day per person. All information was provided by the Cortland County Health Department.

Table 3 highlights the dependence of the SSA on the petitioned aquifer system. As shown, the area obtains 100% of its drinking water (5,599,813 gallons per day) from the Cortland-Homer-Preble Aquifer System.

III. Susceptibility to Contamination

The Cortland-Homer-Preble Aquifer System is highly vulnerable to contamination, due to highly soil permeability and shallow depth to ground water. The following is a discussion of potential sources of contamination, many of which may receive Federal financial assistance through agencies such as the Federal Highway Administration and the Department of Housing and Urban Development.

Transportation Routes and Facilities

A major interstate highway runs through the proposed designation area. The potential exists for accidental spills on the land overlying the aquifer which could result in serious contamination of the water supply.

On-site Septic Disposal

There are many areas that depend upon on-site septic-systems for waste disposal. These systems, depending on design and soil conditions, may lead to the contamination of the ground water.

Storm Water Runoff

Rain and snowmelt runoff can carry potential contaminants as it enters the aquifer. These include deicing salts, animal excrement, pesticides, fertilizers, petroleum products, bacteria and particulates from air pollutants.

Commercial and Industrial Facilities

There are various commercial and industrial facilities located within the aquifer system borders. Several of these facilities make, use or store chemicals and substances that could be hazardous if allowed to enter the ground water system. A common example is the storage of heating oil and gasoline, often in underground tanks. Leakage and/or accidental spills from tanks is not uncommon. Dense commercial, industrial, or residential development may also present a potential source of contamination to the aquifer.

Agricultural Practices

Much of the land in the designated area is used for agricultural purposes. Agricultural practices, such as chemical fertilizer application, pesticide and herbicide use, and disposal of animal wastes, can contribute to ground water contamination. This can occur through direct recharge or surface runoff.

Future Development

Future commercial, industrial, and residential development is also a potential source of contamination to the aquifer. The Cortland-Homer-Preble area is under intensive development pressure. It is unlikely to ease in the future. Therefore, projects should be designed to avoid significant increases in contaminant loading to the aquifer system.

IV. Alternative Sources of Drinking Water

There are no alternate sources that can provide the same quantity of drinking water as the Cortland-Homer-Preble Aquifer System at a reasonable cost. Nearby surface water sources are the Tioughnioga River System (including several lakes north of the Town of Preble) and Skaneateles Lake. The Tioughnioga River System is hydraulically connected to Cortland-Homer-Preble Aquifer System, and therefore is not a potential alternate source.

According to a letter received from the City Engineer of Syracuse, the City of Syracuse has the legal authority to use Skaneateles Lake as a water supply. During critical dry periods the lake is not able to meet the needs of Syracuse. Due to these institutional and capacity restrictions, Skaneateles Lake cannot be considered an alternate source of drinking water to the petitioned aquifer system.

There are four community water supply systems within Cortland County that are outside the petitioned area. Each uses ground water. Capacity (McFarlandJohnson Engineers, Inc., 1982) and current use information were used to determine the quantity of water potentially available from each. This is shown in Table 4. As seen, the total excess capacity of these systems (622,700 gpd) is inadequate to replace the water supplied by the petitioned aquifer (approximately 5.6 Mgpd).

In addition, there are two public water suppliers west of the petitioned area in Tompkins County that can be considered potential alternate sources. The Village of Dryden obtains drinking water from ground water and the Village of Groton utilizes both ground water and surface water. Data supplied by John Anderson of the Tompkins County Department of Health (shown in Table 5) indicate that the excess capacity of these systems (330,000 gpd) is also inadequate to replace the water from the petitioned aquifer system.

To summarize, the total excess capacity of nearby public water supply systems is approximately 950,000 gpd. This volume is insufficient to supply drinking water for the ASA should the Cortland-Homer-Preble Aquifer System become contaminated.

V. Summary

Based upon the information presented, the Cortland-Homer-Preble Aquifer System meets the technical requirements for SSA designation. More than fifty percent (50%) of the drinking water for the aquifer service area is supplied by the Cortland-Homer-Preble Aquifer System. In addition, there are no economically feasible alternative drinking water sources which could replace the Cortland-Homer-Preble Aquifer System. It is therefore recommended that the Cortland-Homer-Preble Aquifer System be designated a SSA. Designation will provide an additional review of those projects for which Federal financial assistance is requested, and will ensure ground water protection measures, incorporating state and local measures whenever possible, are built into the projects.

VI. Selected References

1. Buller, W. (1978). Hydrologic Appraisal of the Water Resources of the HomerPreble Valley, New York. U.S. Geological Survey Water Resource Investigation OpenFile Report 7894. 31 pp.

2. Buller, W., W.J. Nichols and J.F. Harsh (1978). Quality and Movement of Ground Water in Otter Creek-Dry Creek Basin, Cortland County, New York. U.S. Geological Survey Water Investigation Open-File Report 78-3. 63pp.

3. Corner, Oliver J. and J.F. Harsh (1978). Digital-model Simulation of the Glacial Outwash Basin, Cortland County, New York. U.S. Geological Survey Water Resource Investigation Open-File Report 78-71. 34 pp.

4. McFarlandJohnson Engineers, Inc. (1982). Central New York Ground Water Management Program for Cortland County – Task I Report on Ground Water Resources. 99 pp.

5. Milller, Todd S. (1982). CortlandHomerPreble Area, in Atlas of Eleven Selected Aquifers in New York State (R. Waller and A. Finch, compilers). U.S. Geological Survey Water Resource Investigation OpenFile Report 82553. pp. 149172.

6. Milller, Ernest (1965). Quaternary Geology of New York, in Quaternary Geology of the United States (H.E. Wright and E.G. Frey, eds.). Princeton University Press, Princeton, New Jersey. 922 pp.

7. New York State Department of Environmental Conservation (1987). Upstate Ground Water Management Program. 232 pp.

8. New York State Department of Health (1981). Report of Ground Water Dependence in New York State. 49 pp.

9. Reynolds, Richard J. (1987). Hydrogeology of the Surficial Outwash Aquifer at Cortland, Cortland County, New York. U.S. Geological Survey Water Resource Investigation Report 85-4090. 43 pp.

VII. Tables

Table 1. Community Water Suppliers Within Cortland-Homer-Preble Aquifer System

Supply Population
Served
Water Usage
(gallons per day)
City of Cortland 20,100 3,792,000
Cortlandville 2,700 413,600
Homer 4,250 717,800
McGraw 1,300 87,900
Scott 154 9,341
Preble 51 3,200
Green Acres MHP 32 2,000
McBride MHP 54 3,400
Mountainview MHP 86 5,400
Parker Manor MHP 64 4,000
Pine Hill MHP 253 16,000
Ripley Hill MHP 64 4,000
Tully MHP 333 13,672
TOTAL 29,441 5,072,313

MPH = Mobil Home Park
Source: Cortland County Health Department.

Table 2. Private Well Information within Cortland-Homer-Preble Aquifer System

Town Estimated
Population
Estimated Water
Usage (gal/day)
Cortlandville 2,700 270,000
Homer 1,575 157,500
Preble 860 86,000
Scott 140 14,000
TOTAL 5,275 527,500

Estimate of water usage based on 100 gallons per day per person.
Source: Cortland County Health Department.

Table 3. Current Drinking Water Sources for the Cortland-Homer-Preble Aquifer System Service Area and Percentage of Water Obtained from Each Source

Source \ Use Public
Water
Supply
Private
and
Other
Total
Petitioned Aquifer System 90.4 9.6 100%
Other Aquifers —- —- —-
Surface Water — —- —-
Transported from the Outside —- —- —-
Total 90.4 9.6 100%

Table 4. Alternate Water Sources within Cortland County

(All volumes are gallons per day)
Supplier Capacity * Current Usage # Excess Capacity
Cincinnatus 270,000 189,500 80,500
Harford 100,000 4,000 96,000
Marathon 490,000 203,800 286,200
Greek Peak 170,000 10,000 160,000
TOTAL 1,030,000 407,300 622,700

* McFarland-Johnson Engineers, Inc., 1982, Table 6-6.
# Source: Cortland County Health Department.

Table 5. Alternate Water Sources within Tompkins County

(All volumes are gallons per day)
Supplier Capacity Current Usage Excess Capacity
Dryden 300,000 200,000 100,000
Groton 610,000 380,000 230,000
TOTAL 910,000 580,000 330,000

Source: John Andersson, Tompkins County Department of Health.

VIII. Figure

Figure 1. Cortland-Homer-Preble Aquifer System Designated Area

(Displayed USGS 7.5 Minute Quadrangle Sheets)

USGS Quads


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