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Drinking water news – Bottled water

Drinking water news Bottled water courtesy of  Amelia Wade  NZHerald.co.nz

Is bottled water a case of money down the drain?

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Article courtesy of Amelia Wade / www.NZHerald.co.nz / Monday Jun 10, 2013

Kiwis spend millions of dollars buying bottles of water – but their use raises recycling issues and concerns about potentially harmful chemicals such as Bisphenol-A leaching from the polycarbonate plastic containers.

New Zealanders spent a staggering $60.4 million on bottled water at petrol stations and supermarkets last year but health experts question whether it’s any better for us than tap water. Nielsen research showed the value of the water category at supermarkets and petrol stations was $60.4 million last year. That figure does not include dairy sales. The figure was down 5.8 per cent on 2011, but bottled water sales were up 25.7 per cent for the first quarter of this year. Nielsen said this showed weather had a major impact on water sales.

“Therefore, it is fair to say 2012 wasn’t such a good year for water because of the poor summer but the strong summer this year has put water back in positive value growth.” The New Zealand water industry is dominated by two companies – Coca-Cola Amatil, which owns brands like Pump and Kiwi Blue and sources its water from the Blue Spring in Putaruru, and Frucor, which does not reveal its source but owns H2Go.

Rob Bree, a marketing strategy consultant who has worked extensively in the food and beverage industry, said that since the 1990s there had been extraordinary growth in bottled water sales. Explanations include the launch of the sipper bottle, concerns about chlorination and fluoridation, globalisation, a boom in the fitness industry and people leading generally healthier lifestyles. “There’s a convenience to it … People don’t generally tend to plan ahead, unless you have children. You don’t often take a bottle of water around with you so end up just buying it from a dairy.”

Mr Bree said that if people were thirsty, they’d buy water over a sugary drink because it was healthier. A 2002 international study of 122 countries found the quality of New Zealand water was the third-best in the world. But University of Canterbury toxicology professor Ian Shaw said that in his opinion there were no health benefits in drinking bottled water over tap. In fact, the chemicals that leaked into bottled water from the plastic could be damaging. Professor Shaw said the problem with studies on the effects of chemicals in plastic was that they did not look at the impact of the tiny amount that leached into the liquid combined with other enzymes people consumed from other plastics, such as cling film or containers.

“Why on Earth buy water when there’s perfectly good stuff coming out of the tap?”

Much debate has surrounded the concern about Bisphenol-A or BPA in the manufacture of polycarbonate plastic drink bottles and packaging and in the lacquer that lines food and drink cans. Tiny amounts of BPA end up in humans and tests have consistently found the chemical in blood, urine, umbilical-cord blood and in the amniotic fluid protecting a fetus. The New Zealand Food Standards Authority says BPA is safe as long as no one exceeds the “Tolerable Daily Intake” level of 0.05mg per kilogram of bodyweight per day. Professor Shaw says the thin and flexible plastic used to make most single-use water bottles doesn’t contain BPA, but the hard plastic lids do.

“The marketing around it is excellent. People think that they’re getting something that’s really good for them, but it’s just water.”

A master’s thesis by former Massey University student Ruta Svagzdiene examined the debate on whether bottled water was safe from a microbiological point of view. The 2010 study found three out of 39 brands tested did not comply with the New Zealand Microbiological Reference Criteria for Food and the Australia and New Zealand Food Standards Code. Ms Svagzdiene said the public perception was that bottled water was safer than municipal water. “This master’s research study demonstrated that New Zealanders should not assume that all batches of bottled water brands sold in New Zealand is of a satisfactory drinking water standard,” she said in her conclusion.

New Zealand’s standards and practices for monitoring the microbiological quality of mineral water needed to be revised.

The New Zealand Juice and Beverage Association executive director, Kerry Tyack, said it wasn’t a matter of “tap versus bottle”, as bottled water had its benefits. “There’s many reasons why people might purchase a bottle of water – they might be travelling in a car and it’s convenient, to buy a bottle and use it later.”

Bottled water also often tasted better than municipal water.

In a Herald blind taste test, food writers and chefs Nici Wickes and Nadia Lim could tell which cup had tap water in it. Both said the flavour of tap water varied around the country and rated Christchurch’s water as the best. “It’s honestly just as good as bottled water – I don’t know why you would buy water in Christchurch,” said Ms Lim. Mr Tyack said beverage companies were working to find ways of making their packaging more sustainable and that the industry urged people to recycle their bottles.

Over three years, 31,130 plastic bottles were picked up from the country’s beaches, said Sam Judd, chief executive of the Sustainable Coastlines Charitable Trust. “[A water bottle] is an item you don’t really need – it’s an unnecessary product.” Mr Judd urged people to buy a reusable bottle. Two Californian scientists estimated in 2008 that just producing the plastic bottles for bottled-water consumption worldwide used 50 million barrels of oil annually – enough to supply total United States oil demand for 2.5 days.

Some companies are now using PLA plastic bottles that are completely biodegradable.

A 2009 study by Dr Steve Bowden and Dr Eva Collins of the University of Waikato Management School and Dr Kate Kearins and Dr Helen Tregidga of Auckland University found not enough of the PLA plastic was used in New Zealand at the time and it was not seen as economic to separate and recycle.

H20 for young and hip

A majority of daily bottled water drinkers (60 per cent) are aged between 10 and 39. They are most likely to be female, and 83 per cent live in the North Island. Nielsen research has found the attitudes of daily bottled water drinkers reflect a youthful, modern and social group. They are more likely than the total population to have the latest gadgets and spend lots of money on clothes and fine food. They like to dine out and go shopping.

Bottled water drinkers are also a health-conscious group as they like to follow a low-carbohydrate diet and are more likely to go to the gym or exercise regularly than the total population. Fitness activities such as running, walking and swimming are also popular. They are more likely to visit the cinema, read magazines and spend a lot of time on the internet than the average Kiwi. The research company says bottled water drinkers have plenty of opportunities to see outdoor advertising.

Expensive thirst

*$60.4m spent on bottled water at supermarkets and petrol stations in 2012
*5.8 per cent drop in sales in 2012 compared to 2011
*15-17 litres per person – estimate of how much bottled water New Zealanders drink on average a year
*54c more a litre for mid-range bottled water than petrol – $2.65 for h2go vs $2.11 for 91 Octane

Foregoing article was written by Amelia Wade Email Amelia

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The real story behind Bisphenol A

David Case  February 1 2009  Fast Company featured article

Bottled water information│BPA facts.

BY David Case | February 1, 2009 / Fast Company featured article.

The real story behind Bisphenol A

How a handful of consultants used Big Tobacco’s tactics to sow doubt about science and hold off regulation of BPA, a chemical in hundreds of products that could be harming an entire generation.


Surely you’ve heard about BPA by now. It’s everywhere. Some 7 billion pounds of it were produced in 2007. It’s in adhesives, dental fillings, and the linings of food and drink cans. It’s a building block for polycarbonate, a near-shatterproof plastic used in cell phones, computers, eyeglasses, drinking bottles, medical devices, and CDs and DVDs. It’s also in infant-formula cans and many clear plastic baby bottles. Studies have shown that it can leach into food and drink, especially when containers are heated or damaged. More than 90% of Americans have some in their bodies.

BPA is dangerous to human health. Or it is not. That’s according to two government reports in recent months that came to opposite conclusions. The National Toxicology Program (NTP), which is part of the National Institutes of Health, reported in September 2008 “some concern” that BPA harms the human brain and reproductive system, especially in babies and fetuses. Yet less than a month earlier, the U.S. Food and Drug Administration declared that “at current levels of exposure” BPA is safe. Even after the FDA’s own science board questioned the rigor of this analysis in late October, the agency didn’t change its position.

Let’s take a moment to ponder this absurd dichotomy. How could our nation’s health watchdogs reach such divergent conclusions? Are we being unnecessarily scared by the NTP? Or could the FDA be sugarcoating things? What exactly is going on?

We went on a journey to find out. What we learned was shocking. To some degree, the BPA controversy is a story about a scientific dispute. But even more, it’s about a battle to protect a multibillion-dollar market from regulation. In the United States, industrial chemicals are presumed safe until proven otherwise. As a result, the vast majority of the 80,000 chemicals registered to be used in products have never undergone a government safety review. Companies are left largely to police themselves.

Just five companies make BPA in the United States: Bayer, Dow, Hexion Specialty Chemicals, SABIC Innovative Plastics (formerly GE Plastics), and Sunoco. Together, they bring in more than $6 billion a year from the compound. Each of them referred questions about BPA’s safety to their Arlington, Virginia — based trade association, the American Chemistry Council. “Our view would be, Well, no, there isn’t anything to be concerned about,” says Steve Hentges, the council’s point person on BPA. “In a sense, you could have ‘some concern’ about just about anything.”

Of the more than 100 independently funded experiments on BPA, about 90% have found evidence of adverse health effects. On the other hand, every single industry-funded study ever conducted — 14 in all — has found no such effects.

It is the industry-funded studies that have held sway among regulators. This is thanks largely to a small group of “product defense” consultants — also funded by the chemical industry — who have worked to sow doubt about negative effects of BPA by using a playbook that borrows from the wars over tobacco, asbestos, and other public-health controversies. A secretive Beltway public-relations consultant. A government contractor funded by the industries it was hired to assess. A Harvard research center with a history of conflicts of interest. These have been the key actors in how the science of BPA has been interpreted by the government. And it is their work, as much as the science itself, that has stymied regulation.

Raging Hormones

There are a few facts about BPA that everyone agrees on. One is that people are constantly exposed to the compound. Babies — particularly those fed canned formula via polycarbonate bottles — are at the highest risk from BPA; their undeveloped digestive systems metabolize it poorly. It’s also undisputed that BPA mimics the female sex hormone estrogen, and that some synthetic estrogens can cause infertility and cancer.

What is in dispute is whether the tiny doses of BPA we’re exposed to are enough to trigger such hormonal effects. For decades, the assumption was that they didn’t. This was based on traditional toxicology, which holds that “the dose makes the poison.” In other words, a threshold exists below which a compound is harmless. This makes intuitive sense. Consider alcohol: The more you drink, the drunker you get; but if you drink just a little — below the threshold — you may not feel anything. In the 1970s and 1980s, government scientists used standard toxicology to test BPA. They concluded that, at doses far higher than those found in humans, it may cause organ failure, leukemia, and severe weight loss. Yet as BPA products have made their way into every part of our lives, biologists have discovered evidence that very low doses may have a completely different set of effects — on the endocrine system, which influences human development, metabolism, and behavior.

At first, these discoveries emerged by accident, when test tubes and petri dishes in laboratories were switched from glass to plastic. A group of Stanford researchers in 1993 found that breast-cancer cells it was studying reacted with a mysterious estrogen, which it traced to polycarbonate lab flasks. A few years later, Patricia Hunt, a geneticist at Case Western Reserve University, discovered abnormalities in the chromosomes of her lab mice. She eventually concluded that damaged polycarbonate cages were at fault.

In 1995, a developmental biologist named Frederick vom Saal stepped into the picture. A tenured professor at the University of Missouri — Columbia, with funding from the National Institutes of Health, vom Saal tested BPA to see how it interacted with samples of human blood. He found that, because it bypassed mechanisms that control the dose of hormones in the body, its estrogenic effects were magnified. “We said, ‘Wow, that’s bad. This stuff should be considered a lot more potent than it is,’ ” vom Saal recalls. He then fed small amounts of BPA — 25,000 times lower than the EPA’s toxic threshold — to pregnant mice. He discovered that the compound enlarged the prostates of the male offspring, signaling potentially serious developmental disorders. His study was published in 1997 in the peer-reviewed journal Environmental Health Perspectives.

In the years since, more than 100 experiments have shown BPA to cause permanent harm in lab animals at the low exposure levels found in humans. In 2000, Chandra Gupta, a biologist at the University of Pittsburgh, replicated vom Saal’s prostate study. Hunt, the geneticist, replicated under controlled conditions her findings of damage to mouse chromosomes. Others have found impacts on sperm production, testes development, and mammary-gland tissue, as well as behavioral disorders including hyperactivity, aggressiveness, and impaired learning. Most recently, scientists found a correlation (though it’s impossible to determine causation) between BPA levels and heart disease and diabetes in humans.

If these low-dose findings were counterintuitive to toxicologists, they made perfect sense to developmental biologists. After all, BPA is a synthetic hormone. Any physician knows that at small doses, most hormones are extremely powerful in stimulating their target organs, while at higher doses — above a certain threshold — they can paralyze these same organs. (Testosterone powers the male sex drive, for instance, but at high doses causes impotence.)

What’s more, BPA is hardly the only chemical to be identified as an “endocrine disrupter.” To date, more than 50 such compounds have been identified. Dioxins, PCBs, and DDT are some of the more infamous examples. Some cosmetics and soft plastic toys contain one or more phthalates — a group of chemicals that interfere with testosterone and have been shown to lead to infertility and cancer. But because BPA is used in so many common products and has shown effects at such low doses, Hunt says, it quickly became the “poster-child chemical for these endocrine disrupters.”

Rats in the Lab

As the evidence against BPA has mounted, some 29 studies have found the opposite: that the compound is safe. While these experiments have been fewer in number, many of them have the advantage of being far larger in sample size — and thus, their backers say, more statistically significant. Yet the largest of these studies also have another thing in common: They have been funded by BPA’s manufacturers. Sample size, of course, isn’t the only criterion for judging a study. There’s also methodology, lab procedures, and interpretation of data. And a close look at the big industry-funded studies indicates significant flaws.

One of the first such studies, paid for by the trade group Society of the Plastics Industry, was directed by Stuart Cagen of Shell Chemical Co.; another was conducted by John Ashby, at the AstraZeneca lab in the U.K. Both were attempts to replicate vom Saal’s experiment. Published in 1999, the Cagen and Ashby studies gave BPA a clean bill of health. Independent scientists, though, questioned the findings. In addition to testing BPA, Cagen and Ashby had tested the chemical DES as a “positive control” — a lab procedure to determine if a study is conducted properly. Although DES is known to harm mice, neither study found any effects from it. By the definition of a positive control, this indicates the experiments were flawed. (Cagen declined comment; Ashby has retired and could not be reached.)

The largest and most influential industry studies have been conducted by Rochelle Tyl of the Research Triangle Institute, a private lab in North Carolina. Tyl’s first BPA study, published in 2002 at a cost that Tyl puts at around $2 million (also funded by the Society of the Plastics Industry), examined three generations of rats and found no adverse effects at low doses. Yet here, too, there are questions of protocol. The study used a rat strain called the CD Sprague-Dawley, which has been shown to be insensitive to synthetic estrogens like BPA. (A Japanese study found that the CD Sprague-Dawley rat can withstand a dose of synthetic estrogen more than 100 times greater than what a female human can tolerate.) As of early 2007, of the 29 studies that have shown no harm due to BPA, 13 have used the CD Sprague-Dawley rat. Nonetheless, when the FDA declared BPA “safe” this fall, it relied almost exclusively on Tyl’s work — a shortcoming that the agency’s science board publicly criticized in October.

To address criticisms of her first study, Tyl recently completed a follow-up, this time with funding from the American Chemistry Council. “It doesn’t matter who pays for my studies,” says Tyl, who denies there has been any industry influence over her experiments. “It offends the living bejesus out of me, that I’m going to alter a study design or a result.” The follow-up used mice instead of the CD Sprague-Dawley rat and also found no adverse effects from low-dose BPA. However, the study’s details indicate that the mice were fed a type of animal chow that has been shown to mask the effects of estrogens like BPA. Moreover, according to Tyl’s own data, the prostates in both her experimental and her control mice were enormous, suggesting that her study had, in fact, shown effects from BPA, or that there were significant flaws in her team’s lab practices.

Harvard to the Rescue

With two pools of warring studies, BPA regulation has hinged on scientific reviews that assess and pass judgment on the overall body of research. In April 2001, a select group of scientists received a letter emblazoned with the Harvard University crest inviting them to sit on the first such BPA panel. The Harvard Center for Risk Analysis (HCRA), a program under the Harvard School of Public Health, would assume “much of the technical writing responsibilities,” the letter explained. In exchange for attending three two-day meetings and reviewing drafts of the panel’s report, the scientists would be paid $12,000 apiece plus expenses. The letter noted that the Society of the Plastics Industry had commissioned the study and that the panel’s deliberations would be private. The letter concluded, “I assure you it will be a stimulating and productive experience.”

“I said, ‘Great! This is a Harvard center. They’re obviously an honorable bunch,’ ” recalls one accomplished biologist on the panel, who spoke on condition of anonymity. What he didn’t know at the time, he says, was that the center has a history of conflicts of interest. Under founder John D. Graham, a Harvard professor and later administrator of the Office of Information and Regulatory Affairs in the George W. Bush White House, the center had solicited funding from companies whose business might be affected by its research. HCRA’s donors have included more than 100 corporations, including BPA producers Dow, Shell, and Germany-based BASF, as well as industry associations such as the American Chemistry Council.

“In the past, HCRA has acted very much like a product-defense group,” says David Michaels, a Clinton-era Energy Department official and author of the book Doubt Is Their Product. “In a 2000 study, paid for by AT&T Wireless, HCRA justified letting motorists talk on their cell phones by arguing that the added productivity outweighs the cost of accidents. Three years later, in a Harvard-funded study, the same researchers found that not to be true.” A more recent example: In 2005, the center published a study concluding that “government advisories on fish consumption and mercury may do more harm than good”; the lead researcher didn’t disclose that most of the study’s $500,000 in funding was underwritten by the United States Tuna Foundation.

Back in October 1991, in a letter to Philip Morris (obtained through the archives of tobacco-industry files released during litigation and maintained by the University of California, San Francisco), Graham demonstrated how HCRA could recast opposition to regulation as concern for the greater good. In the D.C. debate on fuel-efficiency standards, he noted, “We have urged consideration of the safety risks associated with smaller vehicles.” The letter concluded with an appeal for money and an offer of assistance. In an internal memo, a Philip Morris executive noted, “Depending on the ‘vibes’ you guys get when you meet Graham, I would also be in favor of PM becoming a contributor to the center.”

When it came to its BPA review, the Harvard center held several meetings of its panel between summer 2001 and 2002. But then the report languished for two years, during which time dozens of studies were released that strengthened the case against BPA, including a human study that linked the compound to ovarian cysts (a cause of infertility). None of those findings made it into the final report. Instead, the review, published in the journal Human and Ecological Risk Assessment in 2004, focused on Tyl’s research and a few other industry studies that downplayed BPA’s health concerns. The review concluded that there is “no consistent affirmative evidence of low-dose BPA effects.”

Several members of the 12-person panel didn’t feel comfortable with the conclusions. Four removed their names from the study. One of those scientists, Marvin Meistrich, says, “I disagreed with the way the final report was prepared.” After the panel’s last meeting, the Harvard center selected additional studies to include in its review — “ones that tended to demonstrate no effects,” says Meistrich. One panel member who did sign the report, Claude Hughes, turned around and less than a year later published a paper with vom Saal in Environmental Health Perspectives (the NIH’s premier journal) that refuted the Harvard center’s conclusions.

In the end, HCRA paid even the scientists who pulled their names from the review. The published paper’s acknowledgments thank them by name for their “helpful comments and guidance.” That, in itself, is a score for BPA’s defenders: These scientists have rare specialties that would be vitally important if BPA were to wind up in court. A judge could rule that they had a conflict of interest. “It’s fairly commonplace for companies facing tort suits to corner the market on experts, making it more difficult for the plaintiff to hire witnesses,” says Peter Nordberg, a toxic-tort lawyer at Berger & Montague in Philadelphia.

Through a spokesperson, George Gray, the acting director of the Harvard center at the time, declined to comment on the study. (Shortly after the HCRA review appeared, President George W. Bush appointed him assistant administrator of the EPA.) For its part, the Harvard School of Public Health distances itself from the center’s controversial past. “HCRA is a much different place since John Graham left [in 2001],” says assistant dean Robin Herman. Graham says that industry-funded studies at the center have always been subject to “rigorous quality-control procedures.”

You might expect that a compromised review like this would wither away. Yet the opposite is true. The plastics industry still uses it as evidence that BPA is safe. Journalists and consumers who visit bisphenol-a.org, a site created by the American Chemistry Council, can see that none other than Harvard University has weighed in and pronounced BPA harmless.

For a Few Dollars More

In December 2005, another review of BPA began, this one spurred by the federal government, not industry. The National Institutes of Health had started the Center for the Evaluation of Risks to Human Reproduction (CERHR), an arm of the National Toxicology Program, in 1998 to study chemicals that might be contributing to alarming trends in the developmental health of Americans. Infertility and birth defects are up. Sperm counts are down. Girls reach puberty earlier. Breast cancer, prostate cancer, and neurobehavioral conditions such as attention-deficit disorder are mounting. Soon after the center’s inception, however, its operations were outsourced to a Beltway consultancy called Sciences International. For a fee of about $1 million a year, Sciences ran the evaluation of roughly 20 chemicals in an eight-year period.

On the surface, Sciences International appeared highly qualified for the task. Its president and founder was Dr. Elizabeth Anderson, a former government toxicologist who had helped establish the EPA. She conducted the EPA’s first studies on carcinogens and later spearheaded its Office of Health and Environmental Assessment. A 10-person firm, launched in 1993, Sciences had analyzed the toxicity of dozens of chemicals for the EPA, the FDA, and other government agencies.

Sciences had also built a robust practice helping corporations grapple with lawsuits and regulation. Among its clients were law firms, trade associations, and oil-, tobacco-, and chemical-industry giants. Until 2006, Sciences reported on its Web site that it had defended MTBE (a gasoline additive since banned in 25 states), TCE (an industrial solvent in drinking water found highly likely to cause childhood cancer and birth defects), and perchlorate (another toxin in drinking water that California has deemed “a serious threat to human health”). Tools of the trade included providing expert testimony in lawsuits and producing scientific papers for publication.

A 2005 investigation in Environmental Health Perspectives raised questions about the boundaries that Anderson and her firm were willing to cross in service of their clients. The journal focused on Sciences’ defense of the pesticide phosphine. In the late 1990s, the EPA proposed stricter standards for phosphine after several people died near fumigated warehouses. The tobacco industry determined that the restrictions would cost millions and turned to Sciences for help. Correspondence between Anderson and R.J. Reynolds, obtained from the UC San Francisco tobacco archives, reveals that Anderson lobbied her former colleagues at the EPA to reconsider. Then, with input from her clients, she drafted a report arguing for the old standards and offered to get it published in a peer-reviewed journal. “My experience is that consultant reports funded by those being regulated, and written expressly for the EPA, are easily and frequently ignored,” she wrote in a memo to Joel Seckar, a toxicologist at R.J. Reynolds. “Since I am currently editor-in-chief of the international journal Risk Analysis, perhaps the peer-review process could be expedited.” For this, “Sciences would need an additional $35,000 over and above the $50,000 provided by the original contract,” the letter concluded. When the EPA eventually decided not to change the exposure standard for phosphine, the agency cited the review by Sciences International as justification. (Risk Analysis‘s board — which included HCRA’s George Gray — later tightened its conflict-of-interest standards, after examining the Sciences-phospine episode, but allowed Anderson to remain editor. Anderson declined to talk with Fast Company about the matter.)

Among the first tasks in Sciences’ examination of BPA was to draft a review of previous studies. That draft would serve as a foundation for a panel of scientists who would judge the compound. According to biologist Pete Myers, chief scientist of the nonprofit Environmental Health Sciences, who analyzed the 330-page report, it shared flaws with the discredited Harvard review. “They contained similar biases, both giving undue weight to flawed industry studies and dismissing a wealth of research funded by the National Institutes of Health,” he says. In its own investigation, the Environmental Working Group, a D.C.-based consumer advocate, found that the Sciences draft failed to note which studies were industry funded and ignored details such as Tyl’s use of the estrogen-resistant CD Sprague-Dawley rat.

A further complication was that the panel of experts brought in to conduct the review itself — while all highly accomplished in their own specialties — included only one person with any experience in BPA research. Unfamiliar with the thousands of pages of literature, the panel was heavily dependent on the Sciences draft review, says Myers. In November 2007, the panel issued a weak warning on BPA: that the research merits “minimal concern” for most of the effects studied.

The fact that the National Toxicology Program eventually overruled the panel — strengthening the warning to “some concern” — has much to do with outrage in Congress over revelations that Sciences International had a significant conflict of interest. In February 2007, another investigation by the Environmental Working Group had revealed that Anthony Scialli, a top Sciences employee whose title was “principal investigator” under the 2005 CERHR contract, had coauthored a 2004 study on birth defects from chemicals with a toxicologist from Dow, a manufacturer of BPA. In response, Senator Barbara Boxer and Representative Henry Waxman, both of California, wrote letters upbraiding NIH brass and vowing to keep a close eye on the BPA panel. The NIH requested an explanation from Sciences, which denied that any conflicts had “impaired its judgment or objectivity.”

But Fast Company has learned that Sciences’ conflicts of interest went even deeper. The firm had passed its verdict on BPA, under oath, even before it began the government review. In 2003, Sciences provided expert testimony for the defense in a lawsuit over BPA. On an archived page of the firm’s Web site, the company bragged that, for a private client, it had acted as an expert witness “challenging the validity” of the science on BPA’s health risks. “The case was decided in favor of the defendants,” the site said. (Anderson, who sold Sciences for $5.1 million in 2001 and left for rival Exponent in 2006, confirmed by email that the testimony happened but declined to provide details. Herman Gibb, who took over as president of Sciences, says the staff working on the CERHR contract was not aware of the testimony.)

The NIH terminated the Sciences contract in April 2007, and the firm is now down to four employees. The Environmental Working Group has since reported that Sciences had client relationships with the makers of nearly every chemical it reviewed under the CERHR contract.

Echoes of Agent Orange

As the Sciences International scandal broke, John D. Dingell, Michigan congressman and then-chair of the House Committee on Energy and Commerce, launched an investigation into the product-defense industry. “I have grave concerns that science may be for sale at these consulting firms,” Dingell told Fast Company. “If supposedly reputable scientists are paid to cast doubt on valid scientific data that raise public-health concerns about everyday products, then the public’s health and safety are being endangered.”

Science may be for sale at these consulting firms,” says Congressman Dingell. “If supposedly reputable scientists are paid to cast doubt on valid data, the public’s health and safety are being endangered.”

Dingell’s probe zeroed in on a 75-employee Beltway firm called the Weinberg Group (tagline: “Science minds over business matters”). The firm got started in the 1980s defending the carcinogenic defoliant Agent Orange. According to documents from the tobacco archives, founder Myron Weinberg was a major player in Philip Morris’s infamous “whitecoat” project, under which the company secretly paid dozens of PhDs to challenge the findings that secondhand smoke caused cancer. More recently, the firm has fought restrictions on drugs such as ephedra and Fen-phen — both since pulled from the market. On its site, it has noted that when the FDA proposed canceling an unspecified client’s drug, the Weinberg Group launched a lengthy appeal process that led “to 10 additional years of sales prior to the ultimate cancellation.”

An April 2003 marketing letter written by Weinberg vice president P. Terrence Gaffney provides insight into the services the firm offers. The letter offered DuPont help in defending PFOA, a component of Teflon that has been the subject of lawsuits and EPA enforcement costing the company more than $100 million. “Manufacturers must be the aggressors,” the letter urged. “We must implement a strategy at the outset which discourages government agencies, the plaintiff’s bar, and misguided environmental groups from pursuing this matter.” Specifically, Gaffney offered to facilitate “the publication of papers and articles dispelling the alleged … harm.” He promised, “We will harness, focus, and involve the scientific and intellectual capital of our company with one goal in mind — creating the outcome our client desires.”

According to Dingell’s investigation, Sunoco is among the manufacturers that hired the Weinberg Group to defend its BPA business. A spokesperson for Sunoco confirms the company hired Weinberg but says it was only to analyze BPA science. Weinberg also downplays its role. “The Weinberg Group certainly has been involved,” says spokesman John Kyte, managing director of PR giant Burson-Marsteller. “But critics want to attribute to the Weinberg Group this exorbitant influence and this cloak-and-dagger kind of thing. In the big picture, it’s not the reason the product is in widespread use.”

James Lamb, a lawyer and toxicologist, has been a prominent advocate for BPA’s safety, both as a Weinberg vice president and an independent contractor. In 1998, when BPA became a major issue at a scientific conference in Kyoto, Japan, Lamb led press conferences attacking vom Saal’s studies. In a 2001 press release publicizing Tyl’s study using the CD Sprague-Dawley rats, Lamb — identified only as a former NIH scientist, not a consultant to BPA manufacturers — declared that “the concerns raised by sketchy or incomplete data have now been conclusively addressed. The results indicate very clearly that there is no risk to human health from these low-dose exposures.”

The Weinberg Group also sponsors the journal Regulatory Toxicology and Pharmacology, which has published much of the industry-backed science on BPA. It published one of Cagen’s BPA studies, as well as the Ashby experiment that cast doubt on vom Saal’s prostate findings. George Gray, formerly of HCRA, is a regular contributor, and many of the studies the Harvard center sent to its expert panel were published here.

Reg Tox Pharm, as the journal is known, is published by the International Society of Regulatory Toxicology and Pharmacology. That may sound like a weighty organization, but its annual budget is about $50,000, according to its nonprofit tax return. The society was headed by its founder, C. Jelleff Carr, until he passed away in 2005 at age 94. It is now managed by his wife from her suburban Columbia, Maryland, home.

Every year, the society presents an International Achievement Award, for which “there are no specific criteria … however, international scientific developments in toxicology are of special interest,” according to the society’s Web site. The 2004 award went to Dr. Lester M. Crawford, who later was appointed FDA commissioner by President Bush but resigned after two months. The following year, he pleaded guilty to conflict-of-interest charges. In 2005, the award went to Jerome H. Heckman, general counsel to the Society of the Plastics Industry since 1954. And the 2006 honoree was Elizabeth Anderson of Sciences International.

Watchdogs and Canaries

Where the BPA saga goes from here is unclear.

The dueling government reports’ effect on business began rippling out as early as last April, when a draft version of the National Toxicology Program decision was made public. Outraged activists accused the chemical industry of poisoning infants for profit. Trial lawyers filed class-action suits against bottle manufacturers. Senator Charles Schumer of New York proposed banning the suspect baby bottles outright. Wal-Mart, Toys “R” Us, and CVS all announced plans to phase out polycarbonate bottles. Some companies, such as bottle maker Nalgene, have adopted BPA-free plastic. Yet most businesses stuck with BPA products — at least partly because they don’t have a good substitute. Nearly all of the 130 billion food and beverage cans made in the United States each year are still lined with a BPA resin, for example. There is an alternative called Oleoresin, but it’s more expensive, has a shorter shelf life, and can’t be used for acidic foods like tomatoes.

You might expect the government to start controlling the use of BPA, but the track record suggests otherwise. The United States has a long tradition of keeping harmful substances — lead, DDT, tobacco, PCBs — on the market for decades after scientists find adverse effects. The National Toxicology Program report citing “some concern” has no regulatory impact, and the FDA has repeatedly deemed BPA “safe,” even in the face of criticism. Senator Charles Grassley of Iowa, who has launched numerous investigations into the agency, contends, “The FDA has got to be a watchdog, not a business partner with industry.” (The agency owes a substantial portion of its budget to fees it collects from companies registering new products.) What’s more, the Milwaukee Journal Sentinel reported that the outside scientist supervising the FDA’s latest review, Martin Philbert of the University of Michigan Risk Science Center, failed to disclose a $5 million donation from a man named Charles Gelman — a retired medical-device executive and an opponent of BPA regulation.

The government is unlikely to start controlling the use of BPA. The United States has a long tradition of keeping harmful substances — lead, DDT, tobacco, PCBs — on the market for decades after scientists find adverse effects.

The EPA could theoretically step in, but that’s unlikely too. The agency “has no real program to regulate industrial chemicals, as a result of deep flaws in the 1976 Toxic Substances Control Act,” says Andy Igrejas, environmental-health campaign director for the Pew Charitable Trusts. Under the act, the EPA needs to show “substantial evidence” that a chemical is harmful, and must weigh the costs of restrictions against the economic benefits of keeping the chemical in commerce. That’s a byzantine chore and helps explain why the agency has managed to restrict only five chemicals in the law’s 33-year history. Under the 1996 Food Quality Protection Act, Congress ordered the agency to screen industrial chemicals to determine if they interfere with the endocrine system, a program that might have flagged BPA. Nine years after the 1999 deadline, the agency has yet to screen a single chemical.

Senator Frank Lautenberg of New Jersey has proposed an overhaul of the whole system. In May, he introduced the Kid-Safe Chemical Act of 2008, which would reverse the burden of proof on chemicals, requiring manufacturers to demonstrate their safety in order to keep them in commerce. The E.U. passed a similar law in 2006, as did Canada in 1999. (Canada has banned BPA in baby bottles.) Still, even if Lautenberg’s bill passes, the question remains whether it would be any less vulnerable to product-defense firms gaming the science.

In the meantime, consumers and concerned producers and retailers of BPA products are left with two options: Trust that the chemical industry has their best interests at heart, or take precautions. In its report, the NIH’s National Toxicology Program advised “concerned parents” to reduce their use of canned foods; use BPA-free baby bottles; and opt for glass, porcelain, or stainless-steel containers, particularly for hot foods and liquids. Independent scientists applauded, though many of them contend that the advice should have been even more strongly worded — and would have been, were the agency not constrained by the industry-funded science.

“The U.S. has this disjointed approach to chemicals management that doesn’t focus on the inherent hazard of the chemical,” says Joel Tickner, project director at the Center for Sustainable Production at the University of Massachusetts Lowell. BPA is far from the only modern-age substance whose effects we don’t fully understand, and isn’t the only product whose safety record has been twisted. In that way, perhaps, it may be the canary in the coal mine. And so the question looms: In our quest for progress — and profit — are we putting our future at risk?

David Case interviewed unlikely wind-power tycoon T. Boone Pickens in the June 2008 issue. He is an editor of the Global

FDA Public health report:

Bisphenol A (BPA): Use in Food Contact Application

Update on Bisphenol A (BPA) for Use in Food Contact Applications

January 2010; Updated March 30, 2012


Overview

Bisphenol A (BPA) is an industrial chemical that has been present in many hard plastic bottles and metal-based food and beverage cans since the 1960s.

Studies employing standardized toxicity tests have thus far supported the safety of current low levels of human exposure to BPA. However, on the basis of results from recent studies using novel approaches to test for subtle effects, both the National Toxicology Program at the National Institutes of Health and FDA have some concern about the potential effects of BPA on the brain, behavior, and prostate gland in fetuses, infants, and young children. In cooperation with the National Toxicology Program, FDA’s National Center for Toxicological Research is carrying out in-depth studies to answer key questions and clarify uncertainties about the risks of BPA.

In the interim:

  • FDA is taking reasonable steps to reduce human exposure to BPA in the food supply. These steps include:
    • supporting the industry’s actions to stop producing BPA-containing baby bottles and infant feeding cups for the U.S. market;
    • facilitating the development of alternatives to BPA for the linings of infant formula cans; and
    • supporting efforts to replace BPA or minimize BPA levels in other food can linings.
  • FDA is supporting a shift to a more robust regulatory framework for oversight of BPA.
  • FDA is seeking further public comment and external input on the science surrounding BPA.

FDA is also supporting recommendations from the Department of Health and Human Services for infant feeding and food preparation to reduce exposure to BPA.

FDA is not recommending that families change the use of infant formula or foods, as the benefit of a stable source of good nutrition outweighs the potential risk from BPA exposure.


Background

BPA is an industrial chemical used to make a hard, clear plastic known as polycarbonate, which has been used in many consumer products, including reusable water bottles. BPA is also found in epoxy resins, which act as a protective lining on the inside of metal-based food and beverage cans. These uses of BPA are subject to premarket approval by FDA as indirect food additives or food contact substances. The original approvals were issued under FDA’s food additive regulations and date from the 1960s.

Studies employing standardized toxicity tests used globally for regulatory decision making thus far have supported the safety of current low levels of human exposure to BPA.[1] However, results of recent studies using novel approaches and different endpoints describe BPA effects in laboratory animals at very low doses corresponding to some estimated human exposures.[2] Many of these new studies evaluated developmental or behavioral effects that are not typically assessed in standardized tests.

The National Toxicology Program Center for the Evaluation of Risks to Human Reproduction, part of the National Institutes of Health, completed a review of BPA in September 2008.[3] The National Toxicology Program uses five different terms to describe its level of concern about the different effects of chemicals: negligible concern, minimal concern, some concern, concern, and serious concern.[4]

In its report on BPA, the National Toxicology Program expressed “some concern for effects on the brain, behavior, and prostate gland in fetuses, infants, and children at current human exposures to bisphenol A.”[5] The Program also expressed “minimal concern for effects on the mammary gland and an earlier age for puberty for females in fetuses, infants, and children at current human exposures to bisphenol A” and “negligible concern” for other outcomes.[6]

The National Toxicology Program does not make regulatory recommendations. With respect to neurological and developmental outcomes of BPA, the Program stated that “additional research is needed to more fully assess the functional, long-term impacts of exposures to bisphenol A on the developing brain and behavior.”[7] The Program also stated:

Overall, the current literature cannot yet be fully interpreted for biological or experimental consistency or for relevance to human health. Part of the difficulty for evaluating consistency lies in reconciling findings of different studies that use different experimental designs and different specific behavioral tests to measure the same dimension of behavior.[8]

In August 2008, prior to the release of the final National Toxicology Program report, FDA released a document entitled Draft Assessment of Bisphenol A for Use in Food Contact Applications.[9] This draft assessment was then reviewed by a Subcommittee of FDA’s Science Board, which released its report at the end of October 2008.[10]

Since that time, the Center for Food Safety and Applied Nutrition (CFSAN) within FDA has reviewed additional studies of low-dose toxicity cited by the National Toxicology Program and the Science Board Subcommittee as well as other such studies that have become available. The Center then prepared a document entitled Bisphenol A (CAS RN. 80-05): Review of Low Dose Studies,dated August 31, 2009. In the fall of 2009, FDA’s Acting Chief Scientist asked five expert scientists from across the federal government to provide independent scientific evaluations of this document. In April 2010, FDA made the CFSAN documents available for public comment, and also made public the independent scientific evaluations.

FDA is continuing to consider the low dose toxicity studies of BPA as well as other recent peer-reviewed studies related to BPA. At this stage, FDA is explaining its current perspective on BPA, its support for further studies, its establishment of a public docket for its assessment of BPA use in food contact applications, its interim public health recommendations, its view of the appropriate regulatory framework for BPA use in food contact applications, and our collaborations with international partners.


FDA’s Current Perspective on BPA

At this interim stage, FDA shares the perspective of the National Toxicology Program that recent studies provide reason for some concern about the potential effects of BPA on the brain, behavior, and prostate gland of fetuses, infants and children. FDA also recognizes substantial uncertainties with respect to the overall interpretation of these studies and their potential implications for human health effects of BPA exposure. These uncertainties relate to issues such as the routes of exposure employed, the lack of consistency among some of the measured endpoints or results between studies, the relevance of some animal models to human health, differences in the metabolism (and detoxification) of and responses to BPA both at different ages and in different species, and limited or absent dose response information for some studies.

FDA is pursuing additional studies to address the uncertainties in the findings, seeking public input and input from other expert agencies, and supporting a shift to a more robust regulatory framework for oversight of BPA to be able to respond quickly, if necessary, to protect the public.

In addition, FDA is supporting reasonable steps to reduce human exposure to BPA, including actions by industry and recommendations to consumers on food preparation. At this time, FDA is not recommending that families change the use of infant formula or foods, as the benefit of a stable source of good nutrition outweighs the potential risk of BPA exposure.


Additional Studies

FDA supports additional studies, by both governmental and non-governmental entities, to provide additional information and address uncertainties about the safety of BPA.

FDA’s Studies. FDA’s CFSAN and FDA’s National Center for Toxicological Research has been and continues to pursue a set of studies on the exposure to dietary BPA and the safety of low doses of BPA, including assessment of the novel endpoints where concerns have been raised. These include studies pursued in collaboration with the National Toxicology Program and with support and input from the National Institute for Environmental Health Sciences.

Recent evaluation by the FDA’s CFSAN has:

  • Determined that exposure to dietary BPA for infants, the population of most potential concern, is less than previously estimated. The initial FDA exposure estimates were 0.185 micrograms/kg-bw/day for adults and 2.42 micrograms/kg bw/day for infants. The new estimate of average dietary exposure, based on increased data collection, is 0.2-0.4 micrograms/kw-bw/day for infants and 0.1-0.2 micrograms/kg-bw/day for children and adults.

Recent research studies pursued by FDA’s National Center for Toxicological Research have[11-17]:

  • Found evidence in rodent studies that the level of the active form of BPA passed from expectant mothers to their unborn offspring, following oral exposure, is so low it could not be measured. The study orally dosed pregnant rodents with 100-1000 times more BPA than people are exposed to through food, and could not detect the active form of BPA in the fetus 8 hours after the mother’s exposure.
  • Demonstrated that oral BPA administration results in rapid metabolism of BPA to an inactive form. This results in much lower internal exposure of aglycone BPA (i.e., the active form) than what occurs from other routes of exposure such as injection. Primates of all ages were also found to effectively metabolize BPA to its inactive form and excrete it much more rapidly and efficiently than rodents, thus reducing concerns about results from some rodent studies using oral and, particularly, non-oral exposures which result in higher actual internal exposures of rodents than of primates, including humans, exposed to the same dose.
  • Developed a physiologically based pharmacokinetic model which can be used to predict the level of internal exposure to the active and inactive forms of BPA. This model allows comparisons of internal exposure across different ages and routes of exposure (e.g., oral and intravenous routes). Based on the effects of metabolism, internal exposures to aglycone BPA following oral administration are predicted to be below 1% or less of the total BPA level administered.

The FDA’s National Center for Toxicological Research is continuing with additional studies, including:

  • Rodent subchronic studies which are in progress to characterize potential effects, and, where observed, the dose-response relationship in the prostate and mammary glands for orally administered BPA. In addition, these studies will explore other issues including potential effects of BPA on metabolic changes and cardiovascular endpoints. These studies will include an in utero phase, mimic bottle feeding in neonates, and employ a dose range that will cover the low doses where effects have been previously reported in some animal studies, as well as higher doses where estrogenic effects have been measured in guideline oral studies. Results from this study are expected to be available to FDA to inform the agency’s decision making starting in 2012.
  • Rodent behavioral/neuroanatomical pilot studies which are also already in progress as part of the sub-chronic study to characterize dose levels at which behavioral, neuroanatomical, neurochemical and hormonal endpoints may be affected by developmental exposure to BPA. These data are intended to evaluate possible effects of exposure to BPA during development that have been reported in some published studies on sexually dimorphic behavioral endpoints such as anxiety, as well as on standard developmental neurotoxicity tests. Results from these studies are expected to be available to FDA to inform the agency’s decision making starting in 2012.

Other Studies. Other studies on the safety of BPA are also underway. For example, the National Toxicology Program/Food and Drug Administration (NTP/FDA) will conduct a long-term toxicity study of BPA in rodents to assess a variety of endpoints including novel endpoints where concerns have been raised. NTP/FDA will collaborate with the National Institute of Environmental Health Sciences by providing animals and tissues to a consortium of researchers with interest in studying a variety of additional toxicological areas.


Public Comment and Next Steps for FDA’s Assessment of BPA

On April 5, 2010 the FDA opened a public docket (FDA-2010-N-0100) for comment on BPA. The docket contains the Center for Food Safety and Applied Nutrition’s review of the low dose toxicity studies and recently published studies, the five expert reviews, other relevant material, and public comments.

FDA will also continue to consult with other expert agencies in the federal government, including the National Institutes of Health (and National Toxicology Program), Environmental Protection Agency, Consumer Product Safety Commission, and the Centers for Disease Control and Prevention.

Based on this outside input and the results of new studies, FDA will update its assessment of BPA and will be prepared to take additional action if warranted. As the scientific field is evolving rapidly, FDA anticipates providing further updates on BPA to the public as significant new information becomes available.


Interim Public Health Recommendations

At this interim stage, FDA supports reasonable steps to reduce exposure of infants to BPA in the food supply. In addition, FDA will work with industry to support and evaluate manufacturing practices and alternative substances that could reduce exposure to other populations.

Given that these are preliminary steps being taken as a precaution, it is important that no harmful changes be made in food packaging or consumption, whether by industry or consumers, that could jeopardize either food safety or reduce access to and intake of food needed to provide good nutrition, particularly for infants.

Infants. Infants are a potentially sensitive population for BPA because (1) their neurological and endocrine systems are developing; and (2) their hepatic system for detoxification and elimination of such substances as BPA may be immature.

  • FDA is supporting the industry’s actions to stop producing BPA-containing bottles and infant feeding cups for the U.S. market. FDA understands that the major manufacturers of these products have stopped selling new BPA-containing bottles and infant feeding cups for the U.S. market. Glass and polypropylene bottles and plastic disposable “bag” liners have long been alternatives to polycarbonate nursing bottles.
  • FDA is facilitating the development of alternatives to BPA for the linings of infant formula cans. FDA has already noted increased interest on the part of infant formula manufacturers to explore alternatives to BPA-containing can linings, and has received notifications for alternative packaging. The agency is supporting efforts to develop and use alternatives by (1) working with manufacturers regarding the regulatory status and safety of alternative liners; (2) giving technical assistance to those wishing to prepare applications for approval of alternatives; and (3) expeditiously reviewing any such new applications for alternatives. Because reliable can lining materials are a critical factor in ensuring the quality of heat processed liquid infant formula, safe replacement of such materials requires not only that they both be safe for food contact but also allow for processing that is fully functional in protecting the safety and quality of the infant formula itself.

The American Academy of Pediatrics and other health authorities recommend breastfeeding as the optimal nutrition for infants. Infant formula, including infant formula packaged in cans, is a safe and acceptable alternative that provides known nutritional benefits and prevents life-threatening nutritional deficiencies.

FDA is not recommending that families change the use of infant formula or foods, as the benefit of a stable source of good nutrition outweighs the potential risk of BPA exposure.

Other Populations. With respect to uses of BPA in packaging of food intended for other populations, FDA will support changes in food can linings and manufacturing to replace BPA or minimize BPA levels where the changes can be accomplished while still protecting food safety and quality. FDA will support efforts to develop alternatives for other can lining applications similar to those which are already being tested for liquid infant formula packaging. Reliable can lining materials are a critical factor in ensuring the quality of heat processed foods. Therefore, FDA will work to encourage and facilitate changes that minimize exposure to BPA and avoid other adverse impacts on food safety or quality.

Other Advice. FDA is supporting recommendations by the Department of Health and Human Services for infant feeding and food preparation to reduce exposure to BPA.


The Regulatory Framework for BPA

Current BPA food contact uses were approved under food additive regulations issued more than 40 years ago. This regulatory structure limits the oversight and flexibility of FDA. Once a food additive is approved, any manufacturer of food or food packaging may use the food additive in accordance with the regulation. There is no requirement to notify FDA of that use. For example, today there exist hundreds of different formulations for BPA-containing epoxy linings, which have varying characteristics. As currently regulated, manufacturers are not required to disclose to FDA the existence or nature of these formulations. Furthermore, if FDA were to decide to revoke one or more approved uses, FDA would need to undertake what could be a lengthy process of rulemaking to accomplish this goal.

Since 2000, FDA has regulated new food contact substances through the Food Contact Notification Program. Under this program:

  • FDA receives notification from each manufacturer of the basis for the safe use of a food contact substance, detailing the conditions of the substance’s use, allowing the agency and public to know how much is being used, and for what applications;
  • FDA can work with individual manufacturers to minimize exposure if a potential or actual safety concern is identified after approval;
  • FDA can require the submission of additional safety and exposure data from individual manufacturers to address a significant safety concern;
  • FDA can require additional studies by individual manufacturers to address a significant safety concern; and
  • If FDA were to reach a conclusion that revocation of one or more approved uses is justified, FDA could quickly protect the public by revoking the use through a notice published in the Federal Register.

Given concern about BPA, and the ongoing evaluation of and studies on its safety, FDA believes that the more modern framework is more robust and appropriate for oversight of BPA than the current one.

FDA will encourage manufacturers to voluntarily submit a food contact notification for their currently marketed uses of BPA-containing materials.

In addition, FDA will explore additional options to regulate BPA under the more modern framework.


Collaboration with International Partners

FDA will continue to participate in discussions with our international regulatory and public health counterparts who have also been engaged in assessing the safety of BPA.

For example, FDA has participated with Health Canada in encouraging industry efforts to refine their manufacturing methods for the production of infant formula can linings to minimize migration of BPA into the formula.

In addition, FDA actively supported and participated in the Expert Consultation on BPA convened by World Health Organization and the Food and Agriculture Organization of the United Nations on November 2-5, 2010, in Ottawa, Canada. Information about this expert consultation and the report of the meeting is available from the WHO web site disclaimer icon.


[1]See, e.g., European Food Safety Authority. Toxicokinetics of Bisphenol A, Scientific Opinion of the Panel on Food additives, Flavourings, Processing aids and Materials in Contact with Food, Adopted 9 July 2008 disclaimer icon, The EFSA Journal 2008.

[2]See, e.g. vom Saal FS, Akingbemi BT, Belcher SM et al. Chapel Hill bisphenol A expert panel consensus statement: integration of mechanisms, effects in animals and potential to impact human health at current levels of exposure, Reproductive Toxicology 2007;24:131-8.

[3]NTP-CERHR Monograph on the Potential Human Reproductive and Developmental Effects of Bisphenol A, NIH Publication No. 08-5994, September 2008.

[4]Ibid, page 6.

[5]Ibid.

[6]Ibid.

[7]Ibid, page 20.

[8]Ibid.

[9]U.S. Food and Drug Administration, Draft Assessment of Bisphenol A for Use in Food Contact Applications, 14 August 2008.

[10]FDA Science Board Subcommittee on Bisphenol A. Scientific Peer-Review of the Draft Assessment of Bisphenol A for Use in Food Contact Applications, 31 October 2008.

[11]Doerge D.R., Twaddle N.C., Woodling K.A., Fisher J.W. Pharmacokinetics of bisphenol A in neonatal and adult rhesus monkeys, Toxicology and Applied Pharmacology 2010; 248: 1–11.

[12]Doerge D.R., Twaddle N.C., Vanlandingham M., Fisher J.W. Pharmacokinetics of Bisphenol A in neonatal and adult CD-1 mice: Inter-species comparisons with Sprague-Dawley rats and rhesus monkeys, Toxicology Letters 2011; 207: 298– 305.

[13]Doerge D.R., Twaddle N.C., Vanlandingham M., Brown R.P., Fisher J.W. Distribution of bisphenol A into tissues of adult, neonatal, and fetal Sprague–Dawley rats, Toxicology and Applied Pharmacology 2011; 255: 261–270.

[14]Doerge D.R., Vanlandingham M., Twaddle N.C., Delclos K.B. Lactational transfer of bisphenol A in Sprague–Dawley rats, Toxicology Letters 2010; 199: 372–376.

[15]Twaddle N.C., Churchwell M.I., Vanlandingham M., Doerge D.R. Quantification of deuterated bisphenol A in serum, tissues, and excreta from adult Sprague Dawley rats using liquid chromatography with tandem mass spectrometry, Rapid Communications in Mass Spectrometry 2010; 24: 3011–3020.

[16]Doerge D.R., Twaddle N.C., Vanlandingham M., Fisher J.W. Pharmacokinetics of bisphenol A in neonatal and adult Sprague-Dawley rats, Toxicology and Applied Pharmacology 2010; 247: 158–165.

[17]Fisher J.W., Twaddle N.C., Vanlandingham M., Doerge D.R. Pharmacokinetic Modeling: Prediction and Evaluation of Route Dependent Dosimetry of Bisphenol A in Monkeys with Extrapolation to Humans, Toxicology and Applied Pharmacology 2011; 257; 122-136.

EPA Action plan on BPA 2012:

Bisphenol A (BPA) Action plan summary

Announcements

New! July 31, 2012 – Through its DfE program, EPA has released for comment the draft alternatives assessment “Bisphenol A (BPA) Alternatives in Thermal Paper” (PDF) (492 pp., 6.1 mb.) About PDF). Read more about the BPA Alternatives in Thermal Paper Partnership. The draft report is available for comment until October 1, 2012. Please send comments to Cal Baier-Anderson


In an advance notice of proposed rulemaking (ANPRM) (PDF) (13 pp. 266 kb, About PDF) EPA asked for comment on requiring toxicity testing and environmental sampling and monitoring to help the Agency better understand and address the potential environmental effects of Bisphenol A (BPA). Read more and read the press release.

What chemical is addressed in the action plan?

This action plan addresses EPA’s review of Bisphenol A (BPA), CASRN 80-05-7.

Why is EPA concerned about this chemical?

BPA is a high production volume (HPV) chemical widely used in manufacturing polycarbonate plastics and epoxy resins used in nearly every industry. Humans appear to be exposed primarily through food packaging manufactured using BPA, although those products account for less than 5 percent of the BPA used in this country. Food packaging is under the jurisdiction of the Food and Drug Administration (FDA), not EPA. FDA recently explained the steps it is taking to address BPA. Releases of BPA to the environment exceed 1 million pounds per year.

Because BPA is a reproductive, developmental, and systemic toxicant in animal studies and is weakly estrogenic, there are questions about its potential impact particularly on children’s health and the environment. Studies employing standardized toxicity tests used globally for regulatory decision-making indicate that the levels of BPA in humans and the environment are below levels of potential concern for adverse effects. However, results of some recent studies using novel low-dose approaches and examining different endpoints describe subtle effects in laboratory animals at very low concentrations. Some of these low-dose studies are potentially of concern for the environment because the concentration levels identified with effects are similar to some current environmental levels to which sensitive aquatic organisms may be exposed.

Regulatory authorities around the world reviewing these low-dose studies have generally concluded that they are insufficient for use in risk assessment because of a variety of flaws in some of the study designs, scientific uncertainty concerning the relevance to health of the reported effects, and the inability of other researchers to reproduce the effects in standardized studies. However, since the low-dose studies do raise questions and concerns, some authorities have taken action to protect sensitive populations, particularly infants and young children. For example, while acknowledging that science indicates exposure levels are below potential health effects levels, Canada is taking steps to ban BPA in baby bottles as a precautionary measure. On January 15, 2010, the U.S. Department of Health and Human Services (HHS) provided interim recommendations on how parents and families can reduce exposures to BPA while additional studies are underway.

What action is EPA taking?

Based on EPA’s screening-level review of hazard and exposure information, including the uncertainties surrounding the low-dose studies, EPA’s action plan called for EPA to:

  1. Consider initiating rulemaking under section 5(b)(4) of the Toxic Substances Control Act (TSCA) to identify BPA on the Concern List as a substance that may present an unreasonable risk of injury to the environment on the basis of its potential for long-term adverse effects on growth, reproduction and development in aquatic species at concentrations similar to those found in the environment. A notice of proposed rulemaking is currently pending interagency review at the Office of Management and Budget (OMB).
  1. Consider initiating rulemaking under section 4(a) of TSCA to develop data with respect to environmental effects relevant to a further determination that BPA either does or does not present an unreasonable risk of injury to the environment. This may include testing or monitoring data in the vicinity of landfills, manufacturing facilities, or similar locations to determine the potential for BPA to enter the environment, including surface water, ground water, and drinking water, at levels of potential concern particularly for environmental organisms, pregnant women, and children. EPA released this advance notice of proposed rulemaking (ANPRM)(PDF) (13 pp. 266 kb, About PDF) on July 26, 2011. Read more about the ANPRM on environmental testing of BPA.
  1. Initiate collaborative alternatives assessment activities under its Design for the Environment (DfE) program to encourage reductions in BPA releases and exposures. One of these activities, initiated in April 2010, will address thermal paper coatings used in such applications as cash register receipts, a use where preferable alternatives to BPA may be readily available. This DfE environmental and health assessment is expected to be completed in the latter half of 2011. Additionally, EPA intends to initiate alternatives analyses for BPA used in foundry castings since foundries are accountable for large releases of BPA as reported under the Toxic Release Inventory (TRI), and for BPA-based materials lining water and waste water pipes since this application may have a potential for human and environmental exposure.

EPA does not intend to initiate regulatory action under TSCA at this time on the basis of risks to human health. EPA remains committed to protecting human health and will continue to consult and coordinate closely with FDA, the Centers for Disease Control and Prevention (CDC), and the National Institute of Environmental Health Sciences (NIEHS) to better determine and evaluate the potential health consequences of BPA. The results of this assessment work will factor significantly in any future EPA decisions to address potential risks to human health resulting from uses within EPA’s jurisdiction.

As part of the Agency’s efforts to address BPA, EPA also intends to evaluate the potential for disproportionate impact on children and other sub-populations through exposure from TSCA uses.

Download the complete Bisphenol A (BPA) Action Plan (PDF), (22 pp., 202 KB, About PDF)

Access the public comment docket for the Bisphenol A (BPA) Action Plan (Docket ID EPA-HQ-OPPT-2010-0348) on Regulations.gov.

Access the American Chemistry Council’s request for correction of the BPA Action Plan and the EPA responses to that request.

Access information on the Design for the Environment (DfE) BPA Alternatives In Thermal Paper Partnership.

Track the progress of the TSCA section 4 test rule development activity on the EPA’s Rulemaking Gateway.

Access information on the Environmental Testing of Bisphenol A.

Access the public comment docket for the Testing of Bisphenol A Advance Notice of Proposed Rulemaking (Docket ID EPA-HQ-OPPT-2010-0812) at regulations.gov.

Wikipedia: BPA History/production/use/health effects:

Bisphenol A

From Wikipedia, the free encyclopedia
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Bisphenol A
Identifiers
CAS number 80-05-7 Yes
PubChem 6623
ChemSpider 6371 Yes
UNII MLT3645I99 Yes
EC number 201-245-8
UN number 2430
DrugBank DB06973
KEGG C13624 Yes
ChEBI CHEBI:33216 Yes
ChEMBL CHEMBL418971 Yes
RTECS number SL6300000
Jmol-3D images Image 1
Image 2
Properties
Molecular formula C15H16O2
Molar mass 228.29 g mol−1
Appearance White solid
Density 1.20 g/cm³
Melting point 158-159 °C, 431-432 K, 316-318 °F
Boiling point 220 °C, 493 K, 428 °F (4 mmHg)
Solubility in water 120–300 ppm (21.5 °C)
Hazards
R-phrases R36 R37 R38 R43
S-phrases S24 S26 S37
NFPA 704
NFPA 704.svg
0
3
0
Flash point 227 °C (441 °F)
Related compounds
Related compounds phenols
Bisphenol S
Yes (verify) (what is: Yes/?)
Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa)
Infobox references

Bisphenol A (BPA) is an organic compound with the chemical formula (CH3)2C(C6H4OH)2. It is a colorless solid that is soluble in organic solvents, but poorly soluble in water. Having two phenol functional groups, it is used to make polycarbonate polymers and epoxy resins, along with other materials used to make plastics. Bisphenol A has a vapor pressure of 5*10-6 Pa.[1]

BPA is controversial because it exerts detectable hormone-like properties, raising concerns about its presence in consumer products and foods contained in such products. Starting in 2008, several governments questioned its safety, prompting some retailers to withdraw polycarbonate products. A 2010 report from the United States Food and Drug Administration (FDA) raised further concerns regarding exposure to fetuses, infants, and young children.[2] In September 2010, Canada became the first country to declare BPA a toxic substance.[3][4] The European Union, Canada, and recently the United States have banned BPA use in baby bottles.[5][6]

Production:

World production capacity of this compound was 1 million tons in the 80s,[7] and more than 2.2 million tons in 2009.[8] In 2003, U.S. consumption was 856,000 tons, 72% of which was used to make polycarbonate plastic and 21% going into epoxy resins.[9] In the U.S., less than 5% of the BPA produced is used in food contact applications,[10] but remains in the canned food industry and printing applications such as sales receipts.[11][12]

Bisphenol A was first synthesized by the Russian chemist A.P. Dianin in 1891.[13][14] This compound is synthesized by the condensation of acetone (hence the suffix A in the name)[15] with two equivalents of phenol. The reaction is catalyzed by a strong acid, such as hydrochloric acid (HCl) or a sulfonated polystyrene resin. Industrially, a large excess of phenol is used to ensure full condensation; the product mixture of the cumene process (acetone and phenol) may also be used as starting material:[7]

Synthesis of bisphenol A from phenol and acetone

A large number of ketones undergo analogous condensation reactions. Commercial production of BPA requires distillation – either extraction of BPA from many resinous byproducts under high vacuum, or solvent-based extraction using additional phenol followed by distillation.[7]

Use:

Further information: Polycarbonate

Bisphenol A is used primarily to make plastics, and products using bisphenol A-based plastics have been in commercial use since 1957.[16] At least 3.6 million tonnes (8 billion pounds) of BPA are used by manufacturers yearly.[17] It is a key monomer in production of epoxy resins[18][19] and in the most common form of polycarbonate plastic.[7][20][21] Bisphenol A and phosgene react to give polycarbonate under biphasic conditions; the hydrochloric acid is scavenged with aqueous base:

Polycarbonatsynthese.svg

Diphenyl carbonate may be used in place of phosgene. Phenol is eliminated instead of hydrochloric acid. This transesterification process avoids the toxicity and handling of phosgene.[22]

Polycarbonate plastic, which is clear and nearly shatter-proof, is used to make a variety of common products including baby and water bottles, sports equipment, medical and dental devices, dental fillings and sealants, CDs and DVDs, household electronics, and eyeglass lenses.[7] BPA is also used in the synthesis of polysulfones and polyether ketones, as an antioxidant in some plasticizers, and as a polymerization inhibitor in PVC. Epoxy resins containing bisphenol A are used as coatings on the inside of almost all food and beverage cans,[23] however, due to BPA health concerns, in Japan epoxy coating was mostly replaced by PET film.[24]

Bisphenol A is also a precursor to the flame retardant tetrabromobisphenol A, and formerly was used as a fungicide.[25] Bisphenol A is a preferred color developer in carbonless copy paper and thermal paper,[26] with the most common public exposure coming from some[27] thermal point of sale receipt paper.[28][29] BPA-based products are also used in foundry castings and for lining water pipes.[10]

Identification in plastics:

Some flexible type 3 plastics may leak bisphenol A

Some flexible type 3 plastics may leak bisphenol A

BPA LABEL

Some type 7 plastics may leak bisphenol A

There are seven classes of plastics used in packaging applications. Currently there are no BPA labeling requirements for plastics.

“In general, plastics that are marked with recycle codes 1, 2, 4, 5, and 6 are very unlikely to contain BPA. Some, but not all, plastics that are marked with recycle codes 3 or 7 may be made with BPA.”[30]

Type 7 is the catch-all “other” class, and some type 7 plastics, such as polycarbonate (sometimes identified with the letters “PC” near the recycling symbol) and epoxy resins, are made from bisphenol A monomer.[7][31]

Type 3 (PVC) also may contain bisphenol A as an antioxidant in plasticizers.[7] This refers to “flexible PVC”, but not for rigids such as pipe, windows, and siding.

History:

Bisphenol A was discovered in 1891 by Russian chemist Aleksandr Dianin. In the early 1930s the British chemist Charles Edward Dodds recognized BPA as an artificial estrogen.[32] During that time BPA had two initial uses. The first use of BPA was to enhance the growth of cattle and poultry. The second use of BPA in the mid 1930s was as an estrogen replacement for women. BPA was only briefly used as an estrogen replacement and was replaced by diethylstilbestrol (DES).[33] Based on research by chemists at Bayer and General Electric, BPA has been used since the 1950s to harden polycarbonate plastics and make epoxy resin, and in the lining of food and beverage containers.[34][35] The first evidence of the estrogenicity of bisphenol A came from experiments on rats conducted in the 1930s,[36][37] but it was not until 1997 that adverse effects of low-dose exposure on laboratory animals were first proposed (hormesis).[23] Modern studies began finding possible connections to health issues caused by exposure to BPA during pregnancy and during development. See Government and industry response. Research is ongoing and the debate continues as to whether BPA should be banned or not, and to what extent, all over the world. In 2010 Canada’s department of the environment declared BPA to be a “toxic substance”.[38]

Health effects:

Bisphenol A is a weak endocrine disruptor, which can mimic estrogen and may lead to negative health effects.[39][40][41][42] Early developmental stages appear to be the period of greatest sensitivity to its effects,[43] and some studies have linked prenatal exposure to later physical and neurological difficulties. Regulatory bodies have determined safety levels for humans, but those safety levels are currently being questioned or are under review as a result of new scientific studies.[44][45] A 2011 study that investigated the number of chemicals pregnant women are exposed to in the U.S. found BPA in 96% of women.[46]

In 2009, The Endocrine Society released a statement citing the adverse effects of endocrine-disrupting chemicals, and the controversy surrounding BPA.[47]

In 2011, the chief scientist of the United Kingdom’s Food Standards Agency commented on a study on dietary exposure of adult humans to BPA performed by the EPA,[48] saying, “This corroborates other independent studies and adds to the evidence that BPA is rapidly absorbed, detoxified, and eliminated from humans – therefore is not a health concern.”[49] In the study 20 subjects were tested for BPA every hour for twenty-four hours while consuming three meals consisting of canned food.[48]

In 2012 a paper was written in response to this study, however, criticizing the study as lacking data and having flawed assumptions.[50]

Overall, empirical evidence supporting the negative health effects of BPA varies significantly across studies. Opinions vary greatly about the health effects of BPA. Some studies conclude that BPA poses no health risks while others state that BPA causes a number of adverse health effects. In general, the European’s Scientific Committee on Food, the EUs European Chemicals Bureau, the European Food Safety Authority, and the US Food and Drug Administration have concluded that current levels of BPA present no risk to the general population. However, experts in the field of endocrine disruptors have stated that the entire population may suffer adverse health effects from current BPA levels.[51] Experts advise readers of scientific studies to consider who conducted the study, what their affiliations are, and what the purpose of the study was.

Expert panel conclusions:

In 2006, the US Government sponsored an assessment of the scientific literature on BPA. 38 opponents of bisphenol A gathered in Chapel Hill, North Carolina to review several hundred studies on BPA, many conducted by members of the group. At the end of the meeting, the group issued the Chapel Hill Consensus Statement, which stated “BPA at concentrations found in the human body is associated with organizational changes in the prostate, breast, testis, mammary glands, body size, brain structure and chemistry, and behavior of laboratory animals.”[52]

The Chapel Hill Consensus Statement claimed that average levels in people are above those that cause harm to many animals in laboratory experiments. They noted that while BPA is not persistent in the environment or in humans, biomonitoring surveys indicate that exposure is continuous, however, which is problematic because acute animal exposure studies are used to estimate daily human exposure to BPA, and no studies that had examined BPA pharmacokinetics in animal models had followed continuous low-level exposures. They added that measurement of BPA levels in serum and other body fluids suggests the possibilities that BPA intake is much higher than accounted for, and/or that BPA can bioaccumulate in some conditions (such as pregnancy).[53] A 2011 study, the first to examine BPA in a continuous low-level exposure throughout the day, did find an increased absorption and accumulation of BPA in the blood of mice.[54]

In 2007 studies indicating harm reported a variety of deleterious effects in rodent offspring exposed in the uterus: abnormal weight gain, insulin resistance, prostate cancer, and excessive mammary gland development.[55]

A panel convened by the U.S. National Institutes of Health in 2007 noted that many of the studies referenced by the Chapel Hill group had methodological problems. This panel could not rule out “some concern” about BPA’s effects on fetal and infant brain development and behavior.[9] The concern over the effect of BPA on infants was also heightened by the fact that infants and children are estimated to have the highest daily intake of BPA.[56] A 2008 report by the U.S. National Toxicology Program (NTP) later agreed with the panel, expressing “some concern for effects on the brain, behavior, and prostate gland in fetuses, infants, and children at current human exposures to bisphenol A,” and “minimal concern for effects on the mammary gland and an earlier age for puberty for females in fetuses, infants, and children at current human exposures to bisphenol A.” The NTP had “negligible concern that exposure of pregnant women to bisphenol A will result in fetal or neonatal mortality, birth defects, or reduced birth weight and growth in their offspring.”[57]

External links:

Look up bisphenol a in Wiktionary, the free dictionary.

Richard Branson – Water crisis – How do we save the water?

“Richard Branson – Water crisis – How do we save the water?”

WHOLE WORLD Water seeks to prove that economic, social, and environmental progress are not mutually exclusive. Developed to end the global water and sanitation crisis, WHOLE WORLD Water works to engage the hospitality and tourism industry to filter, bottle, and sell its own water, and contribute 10% of the proceeds to the WHOLE WORLD Water Fund. 100% of the proceeds will go directly to clean and safe water initiatives worldwide.
We believe that everyone should have access to clean and safe water. Visit Sir Richard Branson

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Water contamination news: USA – Fracking – Investigation reveals fracking fluids were illegally dumped – STEM water education – Why dumping chemicals and waste endangers our water supply.

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Water contamination news: USA – Fracking

Water contamination news USA -  Fracking- Investigation reveals fracking fluids were illegally dumped - STEM water education - Why dumping chemicals and waste endangers our water supply.

Investigation reveals fracking fluids were illegally dumped

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Save the Water™ / Water Research / Water Education / Global Water News ©2013
Article and video courtesy of www.KGET.com

After a video posted to YouTube sparked an investigation the state’s water watchdog says fluids containing chemicals from an oil well were illegally dumped into the ground.

The Vintage Oil Company well was drilled and fracked, a controversial process of extracting oil from dense rock. Although the Central Valley Regional Water Quality Control Board said its investigation isn’t complete but board officials say they know already something illegal was done. “Nobody is protecting us,” said almond farmer Tom Frantz.

We first showed you video last February of an Vintage Oil Company well being drilled near an almond orchard in Shafter. “Ten yards away a farmer was flood irrigating his almonds at about the same time,” said Frantz. Frantz captured the video back in October. At first he thought it was the release of fracking fluids, chemicals pumped into the ground to make oil flow. “It turns out they weren’t fracking until the next day they were just getting ready to frack,” said Frantz.

Documents released by Vintage reveal this was the release of what the oil company calls drilling and formation fluids. “We do not believe it was in compliance with the conditional waiver,” said Clay Rodgers, Executive Officer for the Central Valley Regional Water Quality Control Board.

However the documents reveal fracking fluids were released at that site at a later date. A letter says on October 7th and 8th fracking fluids “estimated to be five barrels or less on each date” were discharged into an unlined pond. According to the Rodgers, that is illegal. Tom Frantz thinks it’s happening often.

“I wasn’t that lucky to get there on the only day the only time they did something illegal. If I’m that lucky I should get a lottery ticket,” said Frantz. Vintage said in the documents they do not believe “drilling operations…contaminated soil, creeks, wetlands.” Vintage did say however the company is making progress toward “ceasing the use of unlined sumps” near farmland. “We think that is a promising solution that they are not going to use the unlined ponds,” said Rodgers.

But Tom Frantz said it’s too little late. “We already see when no one is watching, they do something illegal and this is the tip of the iceberg,” said Frantz. A Vintage spokesperson would not comment saying it was “premature.” Once Central Valley Water Board completes their investigation the company could face fines and a possible drilling moratorium. According to vintage, 83 percent of what was released was water, 8 percent was sand and the rest were chemicals like methanol, known as wood alcohol, potassium hydroxide, a corrosive substance and sodium hydroxide, also known as lye. There are a small percentage of chemicals not disclosed, which the company calls “trade secrets.” According to Vintage documents these chemicals were kept from ground water.

But Frantz who took video that lead to the investigation of the fracked well thinks otherwise. “It may not be a hazardous substance but do you want to drink it do you want it in your water no,” said Frantz.

Why dumping chemicals and waste endangers our water supply

Save the Water™ Education Dept. Groundwater can become contaminated in many ways. If rain water or surface water comes into contact with contaminated soil while seeping into the ground, it can become polluted and can carry the pollution from the soil to the groundwater.

Groundwater can also become contaminated when liquid hazardous substances themselves soak down through the soil or rock into the groundwater. Some liquid hazardous substances do not mix with the groundwater but remain pooled within the soil or bedrock. These pooled substances can act as long-term sources of groundwater contamination as the groundwater flows through the soil or rock and comes into contact with them.

Right click on image and view image to enlarge Groundwater can become contaminated in many ways. If rain water or surface water comes into contact with contaminated soil while seeping into the ground, it can become polluted and can carry the pollution from the soil to the groundwater. Groundwater can also become contaminated when liquid hazardous substances themselves soak down through the soil or rock into the groundwater. Some liquid hazardous substances do not mix with the groundwater but remain pooled within the soil or bedrock. These pooled substances can act as long-term sources of groundwater contamination as the groundwater flows through the soil or rock and comes into contact with them.
The dangers of fracking

Fracking dangers

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Richard Branson – Water crisis – How do we save the water?

“Richard Branson – Water crisis – How do we save the water?”

WHOLE WORLD Water seeks to prove that economic, social, and environmental progress are not mutually exclusive. Developed to end the global water and sanitation crisis, WHOLE WORLD Water works to engage the hospitality and tourism industry to filter, bottle, and sell its own water, and contribute 10% of the proceeds to the WHOLE WORLD Water Fund. 100% of the proceeds will go directly to clean and safe water initiatives worldwide.
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Drinking water news: Can bottled water ever really be sustainable? – Why you should not drink bottled water infographic.

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Drinking water news – bottled water

bottled water

Can bottled water ever really be sustainable?

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By Luke Upchurch /Guardian Professional

BawellRight click on image and click view to enlarge

True water sustainability is providing safe drinking water for the one billion without access, not about bottle design and CSR.

Bottled water companies can have all the sustainable credentials in the world, but they are part of the problem.

Business leaders often lay responsibility for the failure of sustainable consumption to go mainstream at the feet of consumers: “They don’t understand what it means.” Well, they’re wrong. The world’s consumers do understand what it means; it’s just not what many in business understand it to be.

If we’re going to get the paradigm shift that everyone is so eager to see, we need to start by focusing on the things that really matter. To understand what I mean, let me tell you the story of Icelandic Glacial.

Icelandic Glacial is a bottled water available in the UK, US, Canada and several other countries. It markets itself as the world’s first carbon-neutral bottled water. Its processing plant, situated on Iceland’s Olfus spring, runs on hydroelectric and geothermal energy. Its packaging is 100% recyclable and, to reduce CO2, it’s even shipped from Iceland in the unused space of cargo ships that would have otherwise remained empty.

Icelandic Glacial has received sustainable certification for both the product and its processing. In 2007, it won the Bottle Water World design award for sustainability. It’s even been certified by the Carbon Neutral company – the seal of approval for which takes centre stage on the bottle’s label.

Many of you reading this will already be pondering the irony of a sustainable bottled water company tapping the very glaciers we need to preserve to survive – but give Icelandic Glacial some credit. In every sense this can be recognised as a sustainable product: it’s recyclable, third-party certified, and CO2 neutral.

Yet this is not a sustainable solution. This is not what sustainability means to the consumer movement. Unfortunately for Icelandic Glacial – which appears genuine in its efforts – this bottled water represents the very antithesis of what sustainability means.

Meaningful sustainability for consumers cannot be captured on a label or celebrated with an industry award. Meaningful sustainability – the type of stuff that spurs paradigm shifts and reverses global trajectories – is about how we provide safe and sustainable drinking water for all, including the one billion consumers who currently have no access to it.

We cannot seriously talk about consumers not understanding or caring about sustainability and not consider the millions of consumers in the developing world without piped water, who are given no choice but to buy bottled alternatives at up to 10 times the price. That is what unsustainable consumption looks like.

The challenge is how we meet this consumer right to the satisfaction of basic needs in a sustainable way – in terms of access, quality, and affordability – as well as environmental impact. This is what the overwhelming majority of the world’s consumers understand sustainability to be about.

Icelandic Glacial may have all the sustainability credentials the company could think of. It may well be a sustainable product in its own right. But it embodies the problem, not the solution, when it comes to sustainable living.

Sustainable consumption is about much more than marketing: much more than niche product lines, and, indeed, the polar opposite of fresh water bottled and sold at a huge mark up.

It’s about creating accessible and stable markets that offer low-environmental impact, good quality products at a fair price, whether it is water, healthcare, food, financial services, or even access to the internet. Some pioneers in industry get that, but most can’t see beyond the label.

So, how do we make the paradigm shift? Put bluntly, stop obsessing about the marketing strategy and CSR brochure and focus on the big meaningful changes that create a sustainable business regardless of consumer demand.

After all, sustainability is about meeting consumer needs, not creating consumer wants.

Luke Upchurch is head of communications and stakeholder relations at Consumers International, the global federation of consumer groups.

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“Richard Branson – Water crisis – How do we save the water?”

WHOLE WORLD Water seeks to prove that economic, social, and environmental progress are not mutually exclusive. Developed to end the global water and sanitation crisis, WHOLE WORLD Water works to engage the hospitality and tourism industry to filter, bottle, and sell its own water, and contribute 10% of the proceeds to the WHOLE WORLD Water Fund. 100% of the proceeds will go directly to clean and safe water initiatives worldwide.
We believe that everyone should have access to clean and safe water. Visit Sir Richard Branson

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Millions of celebrities have joined Matt Damon’s “Toilet Strike” protesting the lack of access to safe water and adequate sanitation for billions. Just today, innovative entrepreneur Richard Branson, rockstar-philanthropist Bono, and actress Olivia Wilde have made their own support public.


Water news directory – 750 articles-March 2012~June 2013: updated daily – click here
Support Save the Water™ click here.

Any donation no matter how small assists Save the Water™ in researching and publishing water education articles such as this. Your support is appreciated as STW™ relies on your assistance to continue each day providing you this information. Click here to help support Save the Water™
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Vol. V
652
June 9 2013

Water
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Daily News
DILOS Program DILOS PROGRAM a day in the life of a scientist water education A day in the life of a scientist DILOS program: youth education principles.Sponsor a program today. Save the water before its too lateMicrosope Videos STEM WATER INFOGRAPHICS


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Present and future generations must be educated in water sustainability issues. With proper funding Save the Water™ will provide that extensive instruction.

We respect the right of every individual to have access to safe and clean drinking water. Your financial support and generosity is needed help support our mission.

 

 help support STW save the water Paypal
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Global water news: India water crisis – Liquid gold: A polluted harvest – A regulatory black hole – Why its ‘no’ to tap water.

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Global water news – India water crisis

Liquid gold: A polluted harvest – A regulatory black hole – Why its no to tap water.

Liquid gold: A polluted harvest.

Girija Shivakumar /thehindu.com

Chronic water scarcity has gripped India as the groundwater table continues to fall at an alarming rate. The current crisis is not just about the disturbed demand-supply curve but mismanagement of resources. Most water sources are contaminated by sewage and agricultural run-off.

Rising population, sprawling cities, and an enormous and thirsty farm belt have jeopardized a feeble, ill-kept public water and sanitation network.

Water problems are endemic, mainly because system maintenance is almost non-existent. As India celebrates ‘water conservation year,’ a faulty municipal system is reinforcing several stark inequalities. There has been a rapid decline of water levels in Delhi and Andhra Pradesh, with 85 and 74 per cent of wells respectively registering a fall in the water level during 2007-2012.

Sunita Narain, director-general of the Centre for Science and Environment, says municipal supply is caught up in a problem resulting in rising cost of supply and an increasing number of people who need the water.

“Most cities are caught in a very vicious cycle as costs are rising, sourcing the water is taking up a huge amount of energy, the distribution network requires longer and longer pipelines. Municipal agencies spend all their time extending the length of the pipelines rather than repairing them. They are not able to supply water to people at affordable prices,” Ms. Narain told The Hindu.

She suggests that we need a different way to reform the municipal supply systems because today it is the poor in India who are the worst-affected. The rich virtually exit the municipal system and often do not pay water or sewage charges. For example, New Delhi has the lowest water and sewage charges in the country.

Ms. Narain warns that the rich have the option of bottled water, leaving the poor to drink what is polluted. This has huge health costs and social implications. She reiterates that water is an issue of need. “Today, the challenge in India is to fix the municipal supply not to get everyone to drink bottled water.”

Companies that use the natural resource for profit pay no charge or royalty for the raw water they use — only a nominal ‘cess’ varying from State to State (a few paise per kilolitre).

There are no credible data available in the country on the quantum of the groundwater, surface or spring water that is being extracted and used by the bottled water and beverages industry, even in the authorised sector.

A regulatory black hole

Gargi Parsai / thehindu.com

Officials admit to proliferation of unauthorised manufacturers who are selling “just about any water — be it rainwater, river or nallah water” as ‘treated’ bottled water under different brand names.

The Water Resources Ministry puts the onus of ensuring quality (including display of composition of the packaged natural mineral or drinking water) and quantity on the Bureau of Indian Standards (BIS), which comes the Department of Consumer Affairs. Sources in the Ministry also point out that although “municipal water is cheapest and assured in quality” water pipelines cannot be laid in all nooks and corners of the country. Places devoid of municipal water supply are increasingly getting dependent on water tankers or bottled water for drinking purposes. The situation worsens during drought months.

Of the 5,842 blocks assessed in the country in 2009, 802 were over-exploited for groundwater; 169 blocks were critical; 523 were semi-critical; and 4,277 were safe.

Central Ground Water Board (CGWB) Chairman Sushil Gupta says the Board does not give permission for groundwater extraction in over-exploited zones. In critical areas, permission is given for extracting 50 per cent of the water the company can recharge; in semi-critical, excavation can be done equivalent to 100 per cent rechargeable water; and in safe zones 200 per cent of rechargeable water can be extracted.

The BIS has to ensure that any company or individual seeking quality certification for using groundwater as raw material has a no-objection certificate (NOC) from the CGWB. It also has to ensure compliance with physical, chemical and microbiological standards. But there is no systematic monitoring to ensure that excess quantities are not extracted and standards are being maintained as is obvious from the numerous brand names flooding the markets. The BIS could not be reached for comment.

The 14 States that have adopted the Central Model Ground Water Regulation Bill are free to give permission to beverages and bottled water companies for extraction of groundwater and more often than not, with little monitoring. For the States that do not have the Act in place, permission is taken from the Centre. Again, no permission is required or taken for drawing river, canal or natural spring water for bottling or use in soft drinks.

Union Secretary for Water Resources S.K. Sarkar feels the problem should have a long-term solution like mapping of aquifers to set limits on how much water can be extracted, at what place, with what recharge, at what distance between wells and at what depth.

The 12th Five-Year Plan will see three-dimensional aquifer mapping and participatory management to decide how much water can be allocated to various users, including industry.

Why its ‘no’ to tap water

Smriti Kak Ramachandran / thehindu.com

In 2002, the Delhi Jal Board that supplies water in the capital set up its own bottling plant; this, by its own admission, was done to address “quantity, not quality,” issues. Bottled water packaged as ‘Jal’ from the plant, the Board claims, was used to make up for deficit supply in several tail-end areas.

The plant continues to produce water, though supply to most targeted areas has improved with the commissioning of the Sonia Vihar Water Treatment Plant that brings Ganga water to the city.

“Bottled water from the plant is for bridging the gap in demand and supply, not because we are not providing clean water. The water that leaves our treatment plants is fit to drink straight from the tap; contamination occurs as the water travels from the plants to individual connections. We adhere to the WHO and BIS norms, and the water we produce is absolutely safe for potable use,” says Debashree Mukherjee, chief executive officer of the utility.

Priced at Rs. 45 a jar of 20 litres, ‘Jal’ has already found a niche in the bottled water market that continues to grow; efforts are under way to increase its reach. A new bottling plant is being commissioned at Savda Gevra, (a resettlement area for the weaker sections), which does not have piped supply.

So if the Board provides clean water, what explains the presence of impurities, bacteria, particle matter that lead to discoloured, smelly and, in a few cases, totally unfit-for-consumption supply? And why is the market for water purifying devices and bottled water growing?

“The pipelines are not pressurised always because of intermittent system of supply. The risk of contamination increases in depressurised systems; it gets worse when water carrying pipelines are laid close to sewerage systems and consumers use online boosters to draw water,” Ms. Mukherjee says.

Uncared for storage systems at the consumer end, poor maintenance of service pipelines and poor planning of cities — development and infrastructure follow occupation — are some other reasons for poor quality, the Board claims.

In 2012, the Union Urban Development Ministry issued an advisory to all the States, asking for water supply and sanitation services to be recognised as ‘basic services.’ Recognising the need for reliability, sustainability and quality and their linkage to social and economic development, the Ministry stressed that “in order to contribute effectively to economic development, these basic services need to be structured as ‘economic services,’ working on principles such as universal access and self-sustainability.”

To improve water supply, the Ministry suggested increasing autonomy of urban local bodies, evaluating the performance of service-providers and making them accountable.

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Water news: Florida – Miami-Dade agrees to $1.6 billion upgrade of its sewer system to eliminate sewage overflows.

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Miami-Dade agrees to $1.6 billion upgrade of its sewer system to eliminate sewage overflows.

Contact: Davina Marraccini, 404-562-8293 (direct), 404-562-8400 (main), marraccini.davina@epa.gov

ATLANTA – Under a settlement with the U.S. Department of Justice and the U.S Environmental Protection Agency (EPA) announced today, Miami-Dade County in Florida has agreed to invest in major upgrades to its wastewater treatment plants and wastewater collection and transmission systems in order to eliminate sanitary sewer overflows. The state of Florida and the Florida Department of Environmental Protection (FDEP) are co-plaintiffs with the United States in this action.

Under the terms of the consent decree, Miami-Dade will rehabilitate its wastewater treatment plants and its wastewater collection and transmission system within 15 years. The county will also develop and implement management operation and maintenance programs to help ensure the sewer system is properly operated and maintained in the future. By implementing these measures, Miami-Dade is expected to eliminate sanitary sewer overflows from its wastewater collection and transmission system and achieve compliance with its National Pollutant Discharge Elimination System (NPDES) permits.

“Sewage overflows are a significant problem in the Southeast because of inadequate and aging infrastructure,” said Stan Meiburg, Acting Regional Administrator of EPA’s Southeastern office. “This agreement demonstrates the county’s commitment to address its sewage problems. Eliminating overflows of raw sewage will comply with the Clean Water Act and benefit the Miami-Dade community by providing a cleaner and healthier environment.”

“Miami-Dade County is one of the world’s premier resort destinations and is home to America’s Everglades, two aquatic preserves as well as Bill Baggs Cape Florida, Oleta River and The Barnacle Historic state parks,” said Florida Department of Environmental Protection Secretary Herschel T. Vinyard Jr. “This agreement will bring lasting environmental and recreational benefits to the citizens and visitors of Miami-Dade County by reducing the threats posed by untreated sewage overflows that degrade water quality and contribute to beach closures,”

Between January 2007 and May 2013, Miami-Dade reported 211 sanitary sewer overflows totaling more than 51 million gallons. Such overflows included a number of large volume overflows from ruptured force mains. At least 84 overflows, totaling over 29 million gallons of raw sewage, reached navigable waters of the United States. Miami-Dade’s Central District wastewater treatment plant (WWTP) also experienced several violations of the effluent limits contained in its NPDES permit. EPA also documented numerous operation and maintenance violations at this same WWTP during inspections in September 2011, April 2012 and April 2013.

Miami-Dade estimates it will spend approximately $1.6 billion to complete the upgrades required by the consent decree and come into compliance with the Clean Water Act. Under the settlement, Miami-Dade will also pay a civil penalty of $978,100 ($511,800 to be paid to the United States and $466,300 to FDEP) and complete a supplemental environmental project costing $2,047,200.

Miami-Dade’s supplemental environmental project involves the installation of approximately 7,660 linear feet of gravity sewer mains through the Green Technology Corridor, an area that is currently using septic tanks. Businesses in the area have been unable to connect to the sewer system because sewer lines are lacking. Disconnecting industrial users from septic tanks will improve water quality in the Biscayne aquifer and nearby surface waters and prevent future contamination.

The terms and conditions of the settlement announced today will update, replace and supersede two existing consent decrees between the United States and the county, the 1994 First Partial Consent Decree and the 1995 Second and Final Partial Consent Decree. Both of these existing consent decrees will be terminated upon entry of the new, proposed consent decree. The parties to this settlement recognized that since entry of the previous consent decrees, conditions within and circumstances surrounding Miami-Dade’s sewer system have changed over the last 18 years, including the causes and locations of sanitary sewer overflows. As a result, appropriate modifications and updates to the previous settlements are included in the new settlement.

Today’s announcement is the latest in a series of Clean Water Act settlements, including sanitary sewer overflow remediation and combined sewer overflow control plans that will reduce the discharge of raw sewage and contaminated stormwater into U.S. rivers, streams and lakes. It is part of EPA’s national enforcement initiative to keep raw sewage and contaminated stormwater out of the nation’s waterways. Reductions in sanitary sewer overflows are accomplished by obtaining municipal utilities’ commitments to implement timely, affordable solutions to these problems.

The settlement, lodged today in the U.S. District Court for the Southern District of Florida, is subject to a 30-day public comment period and approval by the federal court. The settlement will be available for viewing at www.justice.gov/enrd/Consent_Decrees.html

More information about EPA’s national enforcement initiative: http://www.epa.gov/compliance/data/planning/initiatives/2011sewagestormwater.html

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WHOLE WORLD Water seeks to prove that economic, social, and environmental progress are not mutually exclusive. Developed to end the global water and sanitation crisis, WHOLE WORLD Water works to engage the hospitality and tourism industry to filter, bottle, and sell its own water, and contribute 10% of the proceeds to the WHOLE WORLD Water Fund. 100% of the proceeds will go directly to clean and safe water initiatives worldwide.
We believe that everyone should have access to clean and safe water. Visit Sir Richard Branson

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Millions of celebrities have joined Matt Damon’s “Toilet Strike” protesting the lack of access to safe water and adequate sanitation for billions. Just today, innovative entrepreneur Richard Branson, rockstar-philanthropist Bono, and actress Olivia Wilde have made their own support public.

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Water contamination education news: Fracking – Fracking defined – Fracking infographics – Water education resources.

Water contamination news: Fracking

Fracking education update

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Hydraulic fracturing is the propagation of fractures in a rock layer by a pressurized fluid. Some hydraulic fractures form naturally certain veins or dikes are examples—and can create conduits along which gas and petroleum from source rocks may migrate to reservoir rocks. Induced hydraulic fracturing or hydrofracturing, commonly known as fracing, fraccing, or fracking, is a technique used to release petroleum, natural gas (including shale gas, tight gas, and coal seam gas), or other substances for extraction. This type of fracturing creates fractures from a wellbore drilled into reservoir rock formations.

The first use of hydraulic fracturing was in 1947. However, it was only in 1998 that modern fracturing technology, referred to as horizontal slickwater fracturing, made possible the economical extraction of shale gas; this new technology was first used in the Barnett Shale in Texas. The energy from the injection of a highly pressurized hydraulic fracturing fluid creates new channels in the rock, which can increase the extraction rates and ultimate recovery of hydrocarbons.

Proponents of hydraulic fracturing point to the economic benefits from vast amounts of formerly inaccessible hydrocarbons the process can extract. Opponents point to potential environmental impacts, including contamination of ground water, risks to air quality, the migration of gases and hydraulic fracturing chemicals to the surface, surface contamination from spills and flowback and the health effects of these. For these reasons hydraulic fracturing has come under scrutiny internationally, with some countries suspending or banning it.

History

Fracturing as a method to stimulate shallow, hard rock oil wells dates back to the 1860s. It was applied by oil producers in the US states of Pennsylvania, New York, Kentucky, and West Virginia by using liquid and later also solidified nitroglycerin. Later, the same method was applied to water and gas wells. The idea to use acid as a nonexplosive fluid for well stimulation was introduced in the 1930s. Due to acid etching, fractures would not close completely and therefore productivity was enhanced. The same phenomenon was discovered with water injection and squeeze cementing operations.

The relationship between well performance and treatment pressures was studied by Floyd Farris of Stanolind Oil and Gas Corporation. This study became a basis of the first hydraulic fracturing experiment, which was conducted in 1947 at the Hugoton gas field in Grant County of southwestern Kansas by Stanolind. For the well treatment 1,000 US gallons (3,800 l; 830 imp gal) of gelled gasoline and sand from the Arkansas River was injected into the gas-producing limestone formation at 2,400 feet (730 m).

The experiment was not very successful as deliverability of the well did not change appreciably. The process was further described by J.B. Clark of Stanolind in his paper published in 1948. A patent on this process was issued in 1949 and an exclusive license was granted to the Halliburton Oil Well Cementing Company. On March 17, 1949, Halliburton performed the first two commercial hydraulic fracturing treatments in Stephens County, Oklahoma, and Archer County, Texas.[15] Since then, hydraulic fracturing has been used to stimulate approximately a million oil and gas wells.

In the Soviet Union, the first hydraulic proppant fracturing was carried out in 1952. In Western Europe in 1977–1985, hydraulic fracturing was conducted at Rotliegend and Carboniferous gas-bearing sandstones in Germany, Netherlands onshore and offshore gas fields, and the United Kingdoms sector of the North Sea. Other countries in Europe and Northern Africa included Norway, the Soviet Union, Poland, Czechoslovakia, Yugoslavia, Hungary, Austria, France, Italy, Bulgaria, Romania, Turkey, Tunisia, and Algeria.

Due to shale’s high porosity and low permeability, technology research, development and demonstration were necessary before hydraulic fracturing could be commercially applied to shale gas deposits. In the 1970s the United States government initiated the Eastern Gas Shales Project, a set of dozens of public-private hydraulic fracturing pilot demonstration projects. During the same period, the Gas Research Institute, a gas industry research consortium, received approval for research and funding from the Federal Energy Regulatory Commission.

In 1977, the Department of Energy pioneered massive hydraulic fracturing in tight sandstone formations. In 1997, based on earlier techniques used by Union Pacific Resources, now part of Anadarko Petroleum Corporation, Mitchell Energy, now part of Devon Energy, developed the hydraulic fracturing technique known as “slickwater fracturing” which involves adding chemicals to water to increase the fluid flow, that made the shale gas extraction economical.

Method A hydraulic fracture is formed by pumping the fracturing fluid into the wellbore at a rate sufficient to increase pressure downhole to exceed that of the fracture gradient (pressure gradient) of the rock. The fracture gradient is defined as the pressure increase per unit of the depth due to its density and it is usually measured in pounds per square inch per foot or bars per meter. The rock cracks and the fracture fluid continues further into the rock, extending the crack still further, and so on.

Operators typically try to maintain “fracture width”, or slow its decline, following treatment by introducing into the injected fluid a proppant – a material such as grains of sand, ceramic, or other particulates, that prevent the fractures from closing when the injection is stopped and the pressure of the fluid is reduced. Consideration of proppant strengths and prevention of proppant failure becomes more important at greater depths where pressure and stresses on fractures are higher. The propped fracture is permeable enough to allow the flow of formation fluids to the well. Formation fluids include gas, oil, salt water, fresh water and fluids introduced to the formation during completion of the well during fracturing.

During the process fracturing fluid leakoff, loss of fracturing fluid from the fracture channel into the surrounding permeable rock occurs. If not controlled properly, it can exceed 70% of the injected volume. This may result in formation matrix damage, adverse formation fluid interactions, or altered fracture geometry and thereby decreased production efficiency.

The location of one or more fractures along the length of the borehole is strictly controlled by various methods that create or seal off holes in the side of the wellbore. Typically, hydraulic fracturing is performed in cased wellbores and the zones to be fractured are accessed by perforating the casing at those locations.

Hydraulic-fracturing equipment used in oil and natural gas fields usually consists of a slurry blender, one or more high-pressure, high-volume fracturing pumps (typically powerful triplex or quintuplex pumps) and a monitoring unit. Associated equipment includes fracturing tanks, one or more units for storage and handling of proppant, high-pressure treating iron, a chemical additive unit (used to accurately monitor chemical addition), low-pressure flexible hoses, and many gauges and meters for flow rate, fluid density, and treating pressure. Fracturing equipment operates over a range of pressures and injection rates, and can reach up to 100 megapascals (15,000 psi) and 265 litres per second (9.4 cu ft/s) (100 barrels per minute).

Fracturing fluids.

Proppants and fracking fluids and List of additives for hydraulic fracturing

High-pressure fracture fluid is injected into the wellbore, with the pressure above the fracture gradient of the rock. The two main purposes of fracturing fluid is to extend fractures and to carry proppant into the formation, the purpose of which is to stay there without damaging the formation or production of the well. Two methods of transporting the proppant in the fluid are used – high-rate and high-viscosity. High-viscosity fracturing tends to cause large dominant fractures, while high-rate (slickwater) fracturing causes small spread-out micro-fractures.

This fracture fluid contains water-soluble gelling agents (such as guar gum) which increase viscosity and efficiently deliver the proppant into the formation.

The fluid injected into the rock is typically a slurry of water, proppants, and chemical  additives. Additionally, gels, foams, and compressed gases, including nitrogen, carbon dioxide and air can be injected. Typically, of the fracturing fluid 90% is water and 9.5% is sand with the chemical additives accounting to about 0.5%.

A proppant is a material that will keep an induced hydraulic fracture open, during or following a fracturing treatment, and can be gel, foam, or slickwater-based. Fluids make tradeoffs in such material properties as viscosity, where more viscous fluids can carry more concentrated proppant; the energy or pressure demands to maintain a certain flux pump rate (flow velocity) that will conduct the proppant appropriately; pH, various rheological factors, among others. Types of proppant include silica sand, resin-coated sand, and man-made ceramics.

These vary depending on the type of permeability or grain strength needed. The most commonly used proppant is silica sand, though proppants of uniform size and shape, such as a ceramic proppant, is believed to be more effective. Due to a higher porosity within the fracture, a greater amount of oil and natural gas is liberated.

The fracturing fluid varies in composition depending on the type of fracturing used, the conditions of the specific well being fractured, and the water characteristics. A typical fracture treatment uses between 3 and 12 additive chemicals. Although there may be unconventional fracturing fluids, the typical used chemical additives are:

•Acids—hydrochloric acid (usually 28%-5%), or acetic acid is used in the pre-fracturing stage for cleaning the perforations and initiating fissure in the near-wellbore rock.

•Sodium chloride (salt)—delays breakdown of the gel polymer chains.

•Polyacrylamide and other friction reducers—minimizes the friction between fluid and pipe, thus allowing the pumps to pump at a higher rate without having greater pressure on the surface. Polyacrylamide are good suspension agents ensuring the proppant does not fall out.

• Ethylene glycol—prevents formation of scale deposits in the pipe.

•Borate salts—used for maintaining fluid viscosity during the temperature increase.

•Sodium and potassium carbonates—used for maintaining effectiveness of crosslinkers.

•Glutaraldehyde—used as disinfectant of the water (bacteria elimination).

•Guar gum and other water-soluble gelling agents—increases viscosity of the fracturing fluid to deliver more efficiently the proppant into the formation.

•Citric acid—used for corrosion prevention.

•Isopropanol—increases the viscosity of the fracture fluid.

The most common chemical used for hydraulic fracturing in the United States in 2005–2009 was methanol, while some other most widely used chemicals were isopropyl alcohol, 2-butoxyethanol, and ethylene glycol.

Typical fluid types.

• Conventional linear gels. These gels are cellulose derivatives (carboxymethyl cellulose, hydroxyethyl cellulose, carboxymethyl hydroxyethyl cellulose, hydroxypropyl cellulose, methyl hydroxyl ethyl cellulose), guar or its derivatives (hydroxypropyl guar, carboxymethyl hydroxypropyl guar) based, with other chemicals providing the necessary chemistry for the desired results.

•Borate-crosslinked fluids. These are guar-based fluids cross-linked with boron ions (from aqueous borax/boric acid solution). These gels have higher viscosity at pH 9 onwards and are used to carry proppants. After the fracturing job the pH is reduced to 3–4 so that the cross-links are broken and the gel is less viscous and can be pumped out.

•Organometallic-crosslinked fluids zirconium, chromium, antimony, titanium salts are known to crosslink the guar based gels. The crosslinking mechanism is not reversible. So once the proppant is pumped down along with the cross-linked gel, the fracturing part is done. The gels are broken down with appropriate breakers.

•Aluminium phosphate-ester oil gels. Aluminium phosphate and ester oils are slurried to form cross-linked gel. These are one of the first known gelling systems.

For slickwater it is common to include sweeps or a reduction in the proppant concentration temporarily to ensure the well is not overwhelmed with proppant causing a screen-off. As the fracturing process proceeds, viscosity reducing agents such as oxidizers and enzyme breakers are sometimes then added to the fracturing fluid to deactivate the gelling agents and encourage flowback. The oxidizer reacts with the gel to break it down, reducing the fluid’s viscosity and ensuring that no proppant is pulled from the formation.

An enzyme acts as a catalyst for the breaking down of the gel. Sometimes pH modifiers are used to break down the crosslink at the end of a hydraulic fracturing job, since many require a pH buffer system to stay viscous.  At the end of the job the well is commonly flushed with water (sometimes blended with a friction reducing chemical) under pressure.

Injected fluid is to some degree recovered and is managed by several methods, such as underground injection control, treatment and discharge, recycling, or temporary storage in pits or containers while new technology is being continually being developed and improved to better handle waste water and improve re-usability.

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Water education: Chlorine – Chlorine Dioxide – Chloramine – What are the differences? STEM – Water education research report part 3 of 3.

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Water education news: Chlorine – chlorine dioxide – chloramine – what are the differences?

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Chloramine facts: Shocking but true.

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This article is courtesy of Citizens Concerned About Chloramine (CCAC), a nonprofit organization based in the San Francisco Bay Area, California.

…. Summary statement from a recent study at a major U.S. University and as reported in Science News, vol. 130.

Diagram adapted from the Weekly Newsmagazine of Science, SCIENCE NEWS.Chemistry VOL 130 no. 12 Pages 177-192
"You Get More Toxic Exposure From Taking A Shower Than From Drinking The Same Water."

In a new study, researcher Julian Andelman, of the University of Pittsburgh Graduate School of Public Health, the National Academy of Sciences has shown that volatile chemicals present in many municipal drinking water supplies are especially toxic to people when they are exposed to them when bathing or showering. “. . .the major health threat posed by these water pollutants is far more likely to be from their inhalation as air pollutants in the home, according to preliminary data from a study Andelman and his colleagues have just reported.”

“In the past, he says, inhalation exposure to water pollutants has largely been ignored.” His data indicates that hot showers can liberate between 50 to 80 percent of the dissolved chemicals into the air. Emissions from hot baths are half as high. “(One reason, explains Andelman, is that because water droplets dispersed by a shower head have a larger surface-to volume ratio than water streaming into a bath, more of the volatiles can vaporize out).”

It is interesting to note that chloramine actually exists in three forms: monochloramine, dichloramine, and trichloramine. The three forms constantly and rapidly shift from one form to another. “The different volatilities of the chloramines result in substantial differences in the rates of release from water: di- and tri-chloramine are released ~3 and 300 times faster than monochloramine, respectively.” (See page 3 of Chemicals in Drinking Water: Chloramine (PDF, 178 KB), by Scottish Centre for Infection and Environmental Health. Alternate source: click here.) These chemicals vaporize easily out of the water that is heated and aerosolized. All three forms are respiratory irritants, with trichloramine being the most toxic.

Andelman points out that.. . “Although showering can be an intense source of residential exposure to water pollutants, . . . it is far from the only important source. Andelman notes that only about 5 of the 50 to 70 gallons of water used daily by the average American goes for showers. Much of the rest is used by dishwashing and laundering. “

“Though actual doses will depend on many factors–especially the level of water contamination–the study does offer clues for limiting exposure. Cold showers can reduce the vaporization of dissolved volatile chemicals by 50 percent, Andelman says. And short showers help, since each doubling in shower time quadruples the dose from accumulating gases. Finally, to limit the spread of released gases into the rest of the home, he suggests closing the bathroom door while bathing and exhausting the room air outdoors.

“Science News, Vol. 130 no. 12, pgs. 177-192, cited by CCAC in this report.

Citizens Concerned About Chloramine (CCAC) 408 227-5767 Send an email to CCAC http://www.chloramine.org

 

Research in this issue

EPA data base for chloramines in drinking water
Basic information about chloramines and drinking water disinfection
Water systems, disinfection byproducts, and the use of monochloramine
Chloramines-related research
Common health questions related to monochloramine
More information about your drinking water
More information about chloramines and disinfection byproducts
Chloramine data by Wikipedia
Uses and chemical reactions
Reduction of organic chloramines
Uses in water treatment
Health risks
Removing chloramine from water
Situations where monochloramine is removed from water supplies
Organic chloramines

Part one and two of series

Water education research report: Chlorine-part 1 of 3
Water education research report: Chlorine dioxide-part 2 of 3.

Save the Water™© 2013/ 06/5/2013 / Anthony Kozuh / Research – Education .

In this last of our three part water education series: “Chlorine – Chlorine Dioxide – Chloramine – What are the differences?“, the chemical treatment chloramine is looked at. This article is not an opinion of STW™. It is shocking scientific fact. We recommend the video and first toggle be reviewed before going further. At the end of the article we have provided a complete education and news article directory of everything Save the Water™ has published over the past year.”Water education resource and news article directory with 5,450 links“. Water educators are welcome to utilize this information under Creative Commons Attribution-ShareAlike License with proper credit given.

EPA data base for chloramines in drinking water:

Chloramines are disinfectants used to treat drinking water. Chloramines are most commonly formed when ammonia is added to chlorine to treat drinking water. The typical purpose of chloramines is to provide longer-lasting water treatment as the water moves through pipes to consumers. This type of disinfection is known as secondary disinfection. Chloramines have been used by water utilities for almost 90 years, and their use is closely regulated. More than one in five Americans uses drinking water treated with chloramines. Water that contains chloramines and meets EPA regulatory standards is safe to use for drinking, cooking, bathing and other household uses.

Many utilities use chlorine as their secondary disinfectant; however, in recent years, some of them changed their secondary disinfectant to chloramines to meet disinfection byproduct regulations. In order to address questions that have been raised by consumers about this switch, EPA scientists and experts have answered 29 of the most frequently asked questions about chloramines. We have also worked with a risk communication expert to help us organize complex information and make it easier for us to express current knowledge.

The question and answer format takes a step-wise approach to communicate complex information to a wide variety of consumers who may have different educational backgrounds or interest in this topic. Each question is answered by three key responses, which are written at an approximately sixth grade reading level. In turn, each key response is supported by three more detailed pieces of information, which are written at an approximately 12th grade reading level. More complex information is provided in the Additional Supporting Information section, which includes links to documents and resources that provide additional technical information.

EPA continues to research drinking water disinfectants and expects to periodically evaluate and possibly update the questions and answers about chloramines when new information becomes available.

You may wish to view each question separately by clicking on the highlighted questions below or may wish to view them as one document.


Basic information about chloramines and drinking water disinfection


Water systems, disinfection byproducts, and the use of monochloramine


Chloramines-related research


Common health questions related to monochloramine

More information about your drinking water


More information about your drinking water

EPA strongly encourages people to learn more about their drinking water. Your water bill or telephone book’s government listings are a good starting point for local information. Water systems have several different choices when it comes to disinfection. To find out if chloramines are used in your community, contact your local water system.

EPA requires all community water systems to prepare an annual consumer confidence report (CCR) (sometimes called a water quality report) for their customers. The CCR lists the level of contaminants that have been detected over a certain period of time and shows how these levels compare with EPA’s drinking water regulations. Some water suppliers have posted their annual reports on EPA’s Website. If you have not received this annual report, and it is not posted on EPA’s Website, you may request it by calling your water system.

More information about chloramines and disinfection byproducts

More information about health effects and drinking water disinfection from EPA is available in the following locations:


2007 Version of Chloramines Q&A’s

EPA has updated the previous version of the Chloramines Q&A’s in order to better communicate complex issues to a wider audience. EPA expects to continue to review and possiblyupdate the Q&A’s on a periodic basis or as new information becomes available

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Chloramine data by Wikipedia

Text is available under the Creative Commons Attribution-ShareAlike License; additional terms may apply. See Wikipedia terms of use. Wikipedia® is a registered trademark of the Wikimedia Foundation, Inc.

Chloramines are derivatives of ammonia by substitution of one, two or three hydrogen atoms with chlorine atoms.[1] Monochloramine is an inorganic compound with the formula NH2Cl. It is an unstable colourless liquid at its melting point of -66° temperature, but it is usually handled as a dilute aqueous solution where it is used as a disinfectant. The term chloramine also refers to a family of organic compounds with the formulas R2NCl and RNCl2 (R is an organic group). Dichloramine, NHCl2, and nitrogen trichloride, NCl3, are also well known.

Uses and chemical reactions

NH2Cl is a key intermediate in the traditional synthesis of hydrazine.

Monochloramine oxidizes sulfhydryls and disulfides in the same manner as HClO,[4] but only possesses 0.4% of the biocidal effect of HClO.[5]

Reduction of organic chloramines

Chloramines are often an unwanted side product of oxidation reactions of organic compounds (with amino groups) with bleach. The reduction of chloramines back into amines can be carried out through a mild hydride donor. Sodium borohydride will reduce chloramines, but this reaction is greatly sped up with acid catalysis.

Uses in water treatment

See also: Chloramination

NH2Cl is commonly used in low concentrations as a secondary disinfectant in municipal water distribution systems as an alternative to chlorination. This application is increasing. Chlorine (sometimes referred to as free chlorine) is being displaced by chloramine, which is much more stable and does not dissipate from the water before it reaches consumers. NH2Cl also has a very much lower, however still present, tendency than free chlorine to convert organic materials into chlorocarbons such as chloroform and carbon tetrachloride. Such compounds have been identified as carcinogens and in 1979 the United States Environmental Protection Agency‎ began regulating their levels in U.S. drinking water. Furthermore, water treated with chloramine lacks the distinct chlorine odour of the gaseous treatment and so has improved taste. In swimming pools, chloramines are formed by the reaction of free chlorine with organic substances. Chloramines, compared to free chlorine, are both less effective as a sanitizer and more irritating to the eyes of swimmers. When swimmers complain of eye irritation from “too much chlorine” in a pool, the problem is typically a high level of chloramines.[citation needed] Pool test kits designed for use by homeowners are sensitive to both free chlorine and chloramines, which can be misleading.[citation needed]

Chloramine-treated water has a greenish cast; the source of the colour is uncertain. Pure water by contrast normally is blue.[citation needed] This greenish color may be observed by filling a white polyethylene bucket with chloraminated tap water and comparing it to chloramine-free water such as distilled water or a sample from a swimming pool.

Health risks

Adding chloramine to the water supply can increase exposure to lead in drinking water, especially in areas with older housing; this exposure can result in increased lead levels in the bloodstream and can pose a significant health risk.[6]

There is also evidence that exposure to chloramine can contribute to respiratory problems, including asthma, among swimmers.[7] Respiratory problems related to chloramine exposure are common and prevalent among competitive swimmers.[8]

Chloramine use, together with chlorine dioxide, ozone, and ultraviolet, have been described as public health concerns and an example of the outcome of poorly implemented environmental regulation.[citation needed] These methods of disinfection decrease the formation of regulated byproducts such as alkyl chloroforms, which has led to their widespread adoption. However, they can increase the formation of a number of less regulated cytotoxic and genotoxic byproducts, some of which pose greater health risks than the regulated chemicals,[9] causing such diseases as cancer, kidney disease, thyroid damage,[10] and birth defects.[11]

Removing chloramine from water

Chloramine can be removed from tap water by treatment with superchlorination (10 ppm or more of free chlorine, such as from a dose of sodium hypochlorite bleach or pool sanitizer) while maintaining a pH of about 7 (such as from a dose of hydrochloric acid). Hypochlorous acid from the free chlorine strips the ammonia from the chloramine, and the ammonia outgasses from the surface of the bulk water. This process takes about 24 hours for normal tap water concentrations of a few ppm of chloramine. Residual free chlorine can then be removed by exposure to bright sunlight for about 4 hours.

Boiling the water for 20 minutes will remove chloramine and ammonia. Additionally, many foods and drinks rapidly neutralize chloramine without the necessity of boiling (e.g., tea, coffee, chicken stock, orange juice, etc.). SFPUC determined that 1000 mg of Vitamin C (tablets purchased in a grocery store, crushed and mixed in with the bath water) remove chloramine completely in a medium size bathtub without significantly depressing pH. Shower attachments containing Vitamin C can be purchased on the Internet, as well as effervescent Vitamin C bath tablets. [12]

Situations where monochloramine is removed from water supplies

Many animals are sensitive to chloramine and it must be removed from water given to many animals in zoos. Aquarium owners remove the chloramine from their tap water because it is toxic to fish. Aging the water for a few days removes chlorine but not the more stable chloramine, which can be neutralised using products available at pet stores.

Chloramine must also be removed from the water prior to use in kidney dialysis machines, as it would come in contact with the bloodstream across a permeable membrane. However, since chloramine is neutralized by the digestive process, kidney dialysis patients can still safely drink chloramine-treated water.

Home brewers use reducing agents such as sodium metabisulfite or potassium metabisulfite to remove chloramine from brewing fermented beverages. Chloramine, like chlorine, can be removed by boiling. However the boiling time required to remove the chloramine is much longer than that of chlorine.[13] Residual sodium can cause off flavors in beer (See Brewing, Michael Lewis) so potassium metabisulfite is preferred.

Chloramine can be removed from bathwater and birthing tubs by adding 1000 mg of vitamin C (as the ascorbic acid form) to a medium size bathtub (about 40 gallons of water).[14]

Organic chloramines

A variety of organic chloramines are known and proven useful in organic synthesis. One example is N-chloromorpholine ClN(CH2CH2)2O, N-chloropiperidine, and N-chloroquinuclidinium chloride.[15]

Safety

US EPA regulations limit chloramine concentration to 4 parts per million (ppm). A typical target level in US public water supplies is 3 ppm. In order to meet EPA regulated limits on halogenated disinfection by-products, many utilities are switching from chlorination to chloramination. While chloramination produces fewer total halogenated disinfection by-products, it produces greater concentrations of unregulated iodinated disinfection by-products and N-nitrosodimethylamine.[16][17] Both iodinated disinfection by-products and N-nitrosodimethylamine have been shown to be genotoxic.[17]
Research references

Richard Branson – Water crisis – How do we save the water?

“Richard Branson – Water crisis – How do we save the water?”

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Water education news: Chlorine – Chlorine Dioxide – Chloramine – What are the differences?

Chlorine dioxide
Save the Water™ © 2013 Special Education Issue / June 4, 2013 / Anthony Kozuh / Research – Education Dept.

Chlorine dioxide – part two of three

Research in this issue

Historical Background
Differentiating Factors
Molecular Properties & Oxidation
Effective Biocide
Applications
Define chlorine dioxide
Uses
Bleaching
Water chlorination
Other disinfection uses
Safety issues in water and supplements

Research report part 1 of 3.
Research report part 3 of 3.

Historical Background

Following education material is courtesy of The Sabre Companies.

The discovery of chlorine dioxide has largely been credited to Sir Humphrey Davy, who, in 1814, created the compound by mixing sulfuric acid with potassium chlorate. Since its discovery, researchers have found that chlorine dioxide shares some common characteristics with chlorine. Specifically, chlorine dioxide is a greenish-yellowish gas with a chlorine-like odor that is irritating to the eyes, nose, and throat. Apart from these very limited similarities, however, it has been learned that chlorine dioxide exhibits physical and chemical properties that are dramatically different from those of chlorine, even though it contains a chlorine atom in its molecular structure.

Differentiating Factors

One of the most important properties of chlorine dioxide that sets it apart from chlorine is its behavior when placed in water. Not only is chlorine dioxide 10 times more soluble in water than chlorine (3.01 grams/liter at 25 degrees C), it doesn’t hydrolyze when placed in solution. It remains as a “true” dissolved gas that retains its useful oxidative and biocidal properties throughout the entire 2 to 10 pH range. By way of contrast, chlorine dissociates when placed in water to form hypochlorous and hydrochloric acids. Hypochlorous acid is the primary biocide in solution, which dissociates to form hypochlorite ion with increasing pH. Hypochlorite ion is only from 1/20 to 1/300 as effective in controlling microbes as hypochlorous acid. Thus, chlorine can only be an effective biocide in systems with low pH. The high degree of solubility exhibited by chlorine dioxide in water has also been observed in a variety of organic materials, such as oils and solvents, thereby allowing for utilization of its unique oxidative and biocidal properties in a wide range of potential applications.

Molecular Properties & Oxidation

Chlorine dioxide is a small, volatile, and very strong molecule that reacts with other substances by way of oxidation rather than by substitution (i.e., chlorination). chlorine dioxide has lower oxidation strength than chlorine, but more than twice the oxidative capacity. Oxidation strength describes how strongly an oxidizer will react with an “oxidizable” substance. The higher its oxidation strength, the more substances the oxidant compound will react with. chlorine dioxide is comparatively weak, and has a lower oxidation potential than ozone, chlorine or even hypochlorous acid. Oxidation capacity refers to the number of electrons transferred during an oxidation or reduction reaction. The chlorine atom in the ClO2 molecule has an oxidation number of +4. For this reason ClO2 accepts 5 electrons when reduced to chloride ion. By way of comparison, ClO2 contains 263 percent ‘available chlorine,’ which is more than 2.5 times the oxidation capacity of chlorine.The Sabre Companies Chlorine Dioxide (ClO2) Animation

Because chlorine dioxide has lower oxidation strength, it is more selective in its reactions. Typically, chlorine dioxide will only react with compounds that have activated carbon bonds such as phenols, or with other active compounds like sulfides, cyanides, and reduced iron and manganese compounds. Chlorine is a more powerful oxidizer than chlorine dioxide, and will react with a wider variety of chemicals, including ammonia. This property limits its overall effectiveness as a biocide. Conversely, because chlorine dioxide has more oxidative capacity compared to ozone or chlorine, less chlorine dioxide is required to obtain an active residual concentration of the material when used as a disinfectant.

An Effective Biocide

The propensity of chlorine dioxide to react by oxidation rather than substitution makes it a useful alternative to chlorine in drinking water disinfection applications where the formation of potentially carcinogenic halogenated disinfection byproducts, such as trihalomethanes and halogenated acidic acids, is of concern. Additionally, chlorine dioxide does not produce significant amounts of aldehydes, ketons, keton acids, or other disinfection byproducts that originate from ozonation of water containing organic substances.

The reaction of ClO2 with microorganisms or other oxidizable substances takes place in two steps. In the first stage of the reaction, the ClO2 molecule accepts an electron and chlorite ion is formed (ClO2-). In the second stage, ClO2 accepts 4 electrons and chloride ion (Cl-) is formed.

The mechanism of action by which chlorine dioxide inactivates microorganisms is not entirely well understood. As a general matter, however, it is known that chlorine dioxide destroys microbes by attacking their cell walls (or viral envelopes) and interfering with essential protein formation. It is also known that chlorine dioxide is more effective against viruses than either chlorine or ozone. Furthermore, chlorine dioxide is known to be effective against hearty waterborne protozoans such as Giardia Lambia and Cryptosporidium, the causative agents of giardiasis and cryptosporidiosis, respectively. Since chlorine dioxide is an oxidative biocide, microorganisms cannot build up a resistance to it.

Applications

Because chlorine dioxide always exists as a true gas under standard conditions of temperature and pressure, whether in open air or dissolved in solution, its antimicrobial properties can be harnessed for either liquid or gaseous application. The “free radical” property of chlorine dioxide makes it particularly useful for addressing structural microbial contamination problems. Liquid chlorine dioxide solution can be applied directly to known areas of microbial contamination, or entire contaminated structures can be fumigated with the gas by simply stripping it back out of solution at the point of application. Once applied, chlorine dioxide quickly decays on its own to invisible, harmless concentrations of various sodium salts including chlorite, chlorate, and chloride ion.

Foregoing education material is courtesy of Copyright ©2010 The Sabre Companies LLC, All rights reserved. to learn more click here

Accepted definition of chlorine dioxide

Wikimedia Foundation, Inc. Chlorine dioxide is a chemical compound with the formula ClO2. This yellowish-green gas crystallizes as bright orange crystals at −59 °C. As one of several oxides of chlorine, it is a potent and useful oxidizing agent used in water treatment and in bleaching.[2]

Uses

Chlorine dioxide is used primarily (>95%) for bleaching of wood pulp, and for the disinfection (called chlorination) of municipal drinking water.[10][11]:4-1[12]

Bleaching

Chlorine dioxide is sometimes used for bleaching of wood pulp in combination with chlorine, but it is used alone in ECF (elemental chlorine-free) bleaching sequences. It is used at moderately acidic pH (3.5 to 6). The use of chlorine dioxide minimizes the amount of organochlorine compounds produced.[13] Chlorine dioxide (ECF technology) currently is the most important bleaching method world wide. About 95% of all bleached Kraft pulp is made using chlorine dioxide in ECF bleaching sequences.[14]

Chlorine dioxide is also used for the bleaching of flour.

Water chlorination

The Niagara Falls, New York water treatment plant first used chlorine dioxide for drinking water treatment in 1944 for phenol destruction.[11]:4-17[12] Chlorine dioxide was introduced as a drinking water disinfectant on a large scale in 1956, when Brussels, Belgium, changed from chlorine to chlorine dioxide.[12] Its most common use in water treatment is as a pre-oxidant prior to chlorination of drinking water to destroy natural water impurities that produce trihalomethanes on exposure to free chlorine.[15][16][17] Trihalomethanes are suspect carcinogenic disinfection by-products[18] associated with chlorination of naturally occurring organics in the raw water.[17] Chlorine dioxide is also superior to chlorine when operating above pH 7,[11]:4-33 in the presence of ammonia and amines[citation needed] and/or for the control of biofilms in water distribution systems.[17] Chlorine dioxide is used in many industrial water treatment applications as a biocide including cooling towers, process water, and food processing.[19]

Chlorine dioxide is less corrosive than chlorine and superior for the control of legionella bacteria.[12][20] Chlorine dioxide is superior to some other secondary water disinfection methods in that chlorine dioxide: 1) is an EPA registered biocide, 2) is not negatively impacted by pH 3) does not lose efficacy over time (the bacteria will not grow resistant to it) and 4) is not negatively impacted by silica and phosphate, which are commonly used potable water corrosion inhibitors. Some unscrupulous biocide manufacturers will state that their product is EPA registered as a biocide. All EPA registered biocides must have a product label that is supplied with the product. This label will contain specifications as far as the product’s EPA registration. EPA will register certain products as a general biocide, but others will have specifications for what bacteria the product can protect against. For instance, although chlorine dioxide is a registered biocide, it is not registered to protect against Legionella. If a biocide is sold without an EPA approved biocide label that is because the product is not registered as an EPA approved biocide.

It is more effective as a disinfectant than chlorine in most circumstances against water borne pathogenic microbes such as viruses,[21] bacteria and protozoa – including the cysts of Giardia and the oocysts of Cryptosporidium.[11]:4-20–4-21

The use of chlorine dioxide in water treatment leads to the formation of the by-product chlorite, which is currently limited to a maximum of 1 ppm in drinking water in the USA.[11]:4-33 This EPA standard limits the use of chlorine dioxide in the USA to relatively high quality water or water, which is to be treated with iron based coagulants (Iron can reduce chlorite to chloride).[citation needed]

Other disinfection uses

It can also be used for air disinfection,[22] and was the principal agent used in the decontamination of buildings in the United States after the 2001 anthrax attacks.[23] After the disaster of Hurricane Katrina in New Orleans, Louisiana and the surrounding Gulf Coast, chlorine dioxide has been used to eradicate dangerous mold from houses inundated by the flood-water.[24] Sometimes it is used as a fumigant treatment to ‘sanitize’ fruits such as blueberries, raspberries, and strawberries that develop molds and yeast.

Chlorine dioxide is used for the disinfection of endoscopes, such as, under the trade name Tristel.[25] It is also available in a “trio” consisting of a preceding “pre-clean” with surfactant and a succeeding “rinse” with deionised water and low-level antioxidant.[26]

Chlorine dioxide also is used for control of zebra and quagga mussels in water intakes.[11]:4-34

Chlorine dioxide also was shown to be effective in bedbug eradication.[27]

Chlorine dioxide is used as an oxidant for phenol destruction in waste water streams and for odor control in the air scrubbers of animal byproduct (rendering) plants.[11]:4-34

Safety issues in water and supplements

Chlorine dioxide is toxic, hence limits on exposure to it are needed to ensure its safe use. The United States Environmental Protection Agency has set a maximum level of 0.8 mg/L for chlorine dioxide in drinking water.[28] Occupational Safety and Health Administration, OSHA, an agency of the United States Department of Labor has set a 8 hour permissible exposure limit of 0.1 ppm in air (0.3 milligrams per cubic meter (mg/m(3))) for people working with chlorine dioxide.[29]

On July 30, 2010 and again on October 1, 2010, the United States Food and Drug Administration, FDA, warned against the use of the product “Miracle Mineral Supplement” or “MMS”, which when made up according to instructions produces chlorine dioxide. MMS has been marketed as a treatment for a variety of conditions, including HIV, cancer, and acne. The FDA warnings informed consumers that MMS can cause serious harm to health, and stated that it has received numerous reports of nausea, severe vomiting, and life-threatening low blood pressure caused by dehydration,[30][31] among other symptoms, such as diarrhea.

Text is available under the Creative Commons Attribution-ShareAlike License; additional terms may apply. By using this site, you agree to the Terms of Use and Privacy Policy. Wikipedia® is a registered trademark of the Wikimedia Foundation, Inc., a non-profit organization.

Research references

Richard Branson – Water crisis – How do we save the water?

WHOLE WORLD Water seeks to prove that economic, social, and environmental progress are not mutually exclusive. Developed to end the global water and sanitation crisis, WHOLE WORLD Water works to engage the hospitality and tourism industry to filter, bottle, and sell its own water, and contribute 10% of the proceeds to the WHOLE WORLD Water Fund. 100% of the proceeds will go directly to clean and safe water initiatives worldwide.
We believe that everyone should have access to clean and safe water. Visit Sir Richard Branson

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Save the Water™ (STW™) wish to thank our friends, supporters and those who work to educate in regards to the current global water crisis.
STW™ Research and education department wish to thank you and provide water fact banners for your site. You will find thirty water fact banners herein this post (One month). These banner facts are for you to utilize in any way that you deem will help educate your readers in regards to our global water crisis.
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648
June 4, 2013

Water
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    Water education: Chlorine – Chlorine Dioxide – Chloramine – What are the differences? STEM – Water education research report part 1 of 3.

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    Water education news: Chlorine – Chlorine Dioxide – Chloramine – What are the differences?

    chlorine definition
    Save the Water™ © 2013 Special Education Issue / June 3, 2013 / Anthony Kozuh / Research – Education Dept.

    Chlorine – part one of three

    Research in this issue

    EPA Defines chlorine
    History of chlorine
    Scientific definition
    Health Hazard Information
    Acute Effects
    Chronic Effects (Noncancer)
    Reproductive/Developmental Effects
    Cancer Risk
    Science research material
    Physical characteristics of chlorine and its compounds
    Chemical characteristics
    Isotopes

    Research report part 2 of 3.
    Research report part 3 of 3.

    EPA Defines chlorine

    Chlorine is a strong oxidant commonly used in water treatment for oxidation and disinfection. As an oxidant, chlorine is applied to control biological growth and to remove color, taste and odor compounds, iron and manganese, and other dissolved inorganic contaminants such as arsenic. As a primary disinfectant, chlorine is applied to disinfect and to control microbial activity in the distribution system. It is also used as a secondary disinfectant after chlorine, ozone, UV irradiation, or chlorine dioxide. Chlorine is commonly applied at one or two points during treatment. Downstream residual chlorine concentrations make chlorination concurrent with other treatment processes. Figure 1 shows multiple possible chlorine (Cl2) application points during conventional treatment. Chlorine residuals are common during filtration to inhibit microbial (biofilm) growth on filter media that could increase filter head loss (pressure) build up.

    Chlorine is available as compressed elemental gas, sodium hypochlorite solution (NaOCl) or solid calcium hypochlorite (Ca(OCl)2). All forms of chlorine, when applied to water, form hypochlorous acid (HOCl). Gaseous chlorine acidifies the water and reduces the alkalinity, whereas the liquid and solid forms of chlorine increase the pH and the alkalinity at the application point. The pH of the water will affect the dominating chlorine species such that HOCl dominates at lower pH, while the hypochlorite ion (OCl-) dominates at higher pH. Of the two species, HOCl is the stronger oxidant. Therefore, chlorine is more effective as an oxidant and a disinfectant at lower pH. Both forms, HOCl and OCl-, are referred to as free chlorine.

    The concentration (C), contact time (T), pH and temperature affect the effectiveness of chlorine application.  CHLORINEThe product of concentration and time (CT) is the most important operational parameter in disinfection and inactivation. Although increasing the dose increases the ability of chlorine to oxidize and disinfect, it may also lead to taste and odor issues and to the formation of disinfection byproducts (DBPs) by chlorine’s reaction with natural organic matter (NOM). The dose is also affected by the application point, chlorine demand of the water, and desired residual concentration. Total organic carbon (TOC) and ultraviolet absorbance (UV) are two measures of DBP-reactive NOM and of chlorine demand. Information courtesy of EPA Drinking Water Treatability Database

    EPA Contaminants treated by chlorine

    EPA Research references

    History

    Wikimedia Foundation, Inc. The most common compound of chlorine, sodium chloride, has been known since ancient times; archaeologists have found evidence that rock salt was used as early as 3000 BC and brine as early as 6000 BC.[21] Around 1630, chlorine was recognized as a gas by the Belgian chemist and physician Jan Baptist van Helmont.[22]

    Elemental chlorine was first prepared and studied in 1774 by Swedish chemist Carl Wilhelm Scheele, and, therefore, he is credited for its discovery.[23] He called it “dephlogisticated muriatic acid air” since it is a gas (then called “airs”) and it came from hydrochloric acid (then known as “muriatic acid”).[23] However, he failed to establish chlorine as an element, mistakenly thinking that it was the oxide obtained from the hydrochloric acid (see phlogiston theory).[23] He named the new element within this oxide as muriaticum.[23] Regardless of what he thought, Scheele did isolate chlorine by reacting MnO2 (as the mineral pyrolusite) with HCl:[22]

    4 HCl + MnO2 → MnCl2 + 2 H2O + Cl2

    Scheele observed several of the properties of chlorine: the bleaching effect on litmus, the deadly effect on insects, the yellow green color, and the smell similar to aqua regia.[24]

    At the time, common chemical theory was: any acid is a compound that contains oxygen (still sounding in the German and Dutch names of oxygen: sauerstoff or zuurstof, both translating into English as acid stuff), so a number of chemists, including Claude Berthollet, suggested that Scheele’s dephlogisticated muriatic acid air must be a combination of oxygen and the yet undiscovered element, muriaticum.[25][26][27]

    In 1809, Joseph Louis Gay-Lussac and Louis-Jacques Thénard tried to decompose dephlogisticated muriatic acid air by reacting it with charcoal to release the free element muriaticum (and carbon dioxide).[23] They did not succeed and published a report in which they considered the possibility that dephlogisticated muriatic acid air is an element, but were not convinced.[28]

    In 1810, Sir Humphry Davy tried the same experiment again, and concluded that it is an element, and not a compound.[23] He named this new element as chlorine, from the Greek word χλωρος (chlōros), meaning green-yellow.[29] The name halogen, meaning “salt producer,” was originally used for chlorine in 1811 by Johann Salomo Christoph Schweigger. However, this term was later used as a generic term to describe all the elements in the chlorine family (fluorine, bromine, iodine), after a suggestion by Jöns Jakob Berzelius in 1842.[30][31] In 1823, Michael Faraday liquefied chlorine for the first time,[32][33] and demonstrated that what was then known as “solid chlorine” had a structure of chlorine hydrate (Cl2•H2O).[22]

    Chlorine gas was first used by French chemist Claude Berthollet to bleach textiles in 1785.[34][35] Modern bleaches resulted from further work by Berthollet, who first produced sodium hypochlorite in 1789 in his laboratory in the town of Javel (now part of Paris, France), by passing chlorine gas through a solution of sodium carbonate. The resulting liquid, known as “Eau de Javel” (“Javel water“), was a weak solution of sodium hypochlorite. However, this process was not very efficient, and alternative production methods were sought. Scottish chemist and industrialist Charles Tennant first produced a solution of calcium hypochlorite (“chlorinated lime”), then solid calcium hypochlorite (bleaching powder).[34] These compounds produced low levels of elemental chlorine, and could be more efficiently transported than sodium hypochlorite, which remained as dilute solutions because when purified to eliminate water, it became a dangerously powerful and unstable oxidizer. Near the end of the nineteenth century, E. S. Smith patented a method of sodium hypochlorite production involving electrolysis of brine to produce sodium hydroxide and chlorine gas, which then mixed to form sodium hypochlorite.[36] This is known as the chloralkali process, first introduced on an industrial scale in 1892, and now the source of essentially all modern elemental chlorine and sodium hydroxide production (a related low-temperature electrolysis reaction, the Hooker process, is now responsible for bleach and sodium hypochlorite production).

    Elemental chlorine solutions dissolved in chemically basic water (sodium and calcium hypochlorite) were first used as anti-putrification agents and disinfectants in the 1820s, in France, long before the establishment of the germ theory of disease. This work is mainly due to Antoine-Germain Labarraque, who adapted Berthollet’s “Javel water” bleach and other chlorine preparations for the purpose (see a more complete history, see below). Elemental chlorine has since served a continuous function in topical antisepsis (wound irrigation solutions and the like) as well as public sanitation (especially of swimming and drinking water). In 1826, silver chloride was used to produce photographic images for the first time.[37] Chloroform was first used as an anesthetic in 1847.[37]

    Polyvinyl chloride (PVC) was invented in 1912, initially without a purpose.[37]Chlorine gas was first introduced as a weapon on April 22, 1915, at Ypres by the German Army,[38][39] and the results of this weapon were disastrous because gas masks had not been mass distributed and were tricky to get on quickly.

    Chlorine definition as accepted today

    Wikimedia Foundation, Inc. Chlorine is a chemical element with symbol Cl and atomic number 17. Chlorine is in the halogen group (17) and is the second lightest halogen after fluorine. The element is a yellow-green gas under standard conditions, where it forms diatomic molecules. It has the highest electron affinity and the third highest electronegativity of all the elements; for this reason, chlorine is a strong oxidizing agent. Free chlorine is rare on Earth, and is usually a result of direct or indirect oxidation by oxygen.

    The most common compound of chlorine, sodium chloride, has been known since ancient times. Around 1630 chlorine gas was first synthesized in a chemical reaction, but not recognized as a fundamentally important substance. Characterization of chlorine gas was made in 1774 by Carl Wilhelm Scheele, who supposed it an oxide of a new element. In 1809 chemists suggested that the gas might be a pure element, and this was confirmed by Sir Humphry Davy in 1810, who named it from Ancient Greek: χλωρóς khlôros “pale green”.

    Nearly all chlorine in the Earth’s crust occurs as chloride in various ionic compounds, including table salt. It is the second most abundant halogen and 21st most abundant chemical element in Earth’s crust. Elemental chlorine is commercially produced from brine by electrolysis. The high oxidizing potential of elemental chlorine led commercially to free chlorine’s bleaching and disinfectant uses, as well as its many uses of an essential reagent in the chemical industry. Chlorine is used in the manufacture of a wide range of consumer products, about two-thirds of them organic chemicals such as polyvinyl chloride, as well as many intermediates for production of plastics and other end products which do not contain the element. As a common disinfectant, elemental chlorine and chlorine-generating compounds are used more directly in swimming pools to keep them clean and sanitary.

    In the form of chloride ions, chlorine is necessary to all known species of life. Other types of chlorine compounds are rare in living organisms, and artificially produced chlorinated organics range from inert to toxic. In the upper atmosphere, chlorine-containing organic molecules such as chlorofluorocarbons have been implicated in ozone depletion. Small quantities of elemental chlorine are generated by oxidation of chloride to hypochlorite in neutrophils, as part of the immune response against bacteria. Elemental chlorine at high concentrations is extremely dangerous and poisonous for all living organisms, and was historically used in World War I as the first gaseous chemical warfare agent.

    Wikipedia research references to forgoing history and current definition

    Text is available under the Creative Commons Attribution-ShareAlike License; additional terms may apply. By using this information, you agree to the Terms of Use and Privacy Policy. Wikipedia® is a registered trademark of the Wikimedia Foundation, Inc., a non-profit organization.

    Health Hazard Information

    Acute Effects:

    • Chlorine is a potent irritant in humans to the eyes, the upper respiratory tract, and the lungs. Several acute (short-term) studies have reported the following effects: tickling of the nose at 0.014 to 0.054 parts per million (ppm); tickling of the throat at 0.04 to 0.097 ppm; itching of the nose and cough, stinging, or dryness of the nose and throat at 0.06 to 0.3 ppm; burning of the conjunctiva and pain after 15 minutes at 0.35 to 0.72 ppm; and discomfort ranging from ocular and respiratory irritation to coughing, shortness of breath, and headaches above 1.0 ppm. (4)
    • Higher levels of chlorine have resulted in the following effects in humans: mild mucous membrane irritation at 1 to 3 ppm; chest pain, vomiting, dypsnea, and cough at 30 ppm; and toxic pneumonitis and pulmonary edema at 46 to 60 ppm. (3)
    • Chlorine is extremely irritating to the skin and can cause severe burns in humans. (3)
    • Acute animal tests in rats and mice have shown chlorine to have high acute toxicity via inhalation. (6)

    Chronic Effects (Noncancer):

    • Workers chronically exposed to chlorine gas have exhibited respiratory effects, such as eye and throat irritation, and airflow obstruction. (8)
    • Animal studies have reported decreased body weight gain, eye and nose irritation, and nonneoplastic lesions and respiratory epithelial hyperplasia from chronic inhalation exposure to chlorine. (4,8)
    • The Reference Dose (RfD) for chlorine is 0.1 milligrams per kilogram body weight per day (mg/kg/d) based on no observed adverse effects in rats. The RfD is an estimate (with uncertainty spanning perhaps an order of magnitude) of a daily oral exposure to the human population (including sensitive subgroups) that is likely to be without appreciable risk of deleterious noncancer effects during a lifetime. It is not a direct estimator of risk but rather a reference point to gauge the potential effects. At exposures increasingly greater than the RfD, the potential for adverse health effects increases. Lifetime exposure above the RfD does not imply that an adverse health effect would necessarily occur. (2)
    • EPA has medium confidence in the RfD based on (1) medium to high confidence in the principal study because relevant endpoints in two animal species were examined after prolonged exposure by an appropriate route, but an effect level was not observed in this study and higher levels may not be practicable due to taste aversion, and (2) medium confidence in the database because information is available for rats and mice on the noncarcinogenic toxicity of oral exposure to chlorine for subchronic periods. Developmental and reproductive toxicity of chlorine have been examined in rats and mice, but with suboptimal studies; due to the chemical relationship between chlorine and monochloramine, reproductive and developmental studies for monochloramine may be used to satisfy data gaps for chlorine. (2)
    • EPA has not established a Reference Concentration (RfC) for chlorine. (2)
    • CalEPA has established a chronic reference exposure level of 0.00006 milligrams per cubic meter (mg/m3) based on respiratory epithelial lesions in rats. The CalEPA reference exposure level is a concentration at or below which adverse health effects are not likely to occur. (8)

    Reproductive/Developmental Effects:

    • No information is available on the developmental or reproductive effects of chlorine in humans or animals via inhalation exposure.
    • Animal studies have demonstrated no evidence of reproductive or developmental effects from ingestion exposure to chlorine. (2)
    • Since chlorine is highly reactive, uptake at sites such as the ovaries and testes which are remote from the respiratory tract, is anticipated to be minimal. (2)

    Cancer Risk:

    • No information is available on the carcinogenic effects of chlorine in humans from inhalation exposure.
    • Several human studies have investigated the relationship between exposure to chlorinated drinking water and cancer. These studies were not designed to assess whether chlorine itself causes cancer, but whether trihalomethanes or other organic compounds occurring in drinking water as a result of chlorination are associated with an increased risk of cancer. These studies show an association between bladder and rectal cancer and chlorination byproducts in drinking water. (5)
    • An NTP study reported no evidence of carcinogenic activity in male rats or male and female mice, and equivocal evidence, based on an increase in mononuclear cell leukemia, in female rats, from ingestion of chlorinated or chloraminated water. (9)
    • EPA has not classified chlorine for carcinogenicity. (2)

    EPA research reference

    Chlorine: Further science research material

    Chlorine
    17Cl
    F

    Cl

    Br
    sulfurchlorineargon
    Appearance
    pale yellow-green gas
    General properties
    Name, symbol, number chlorine, Cl, 17
    Pronunciation /ˈklɔərn/ KLOHR-een
    or /ˈklɔərɨ