Not-So-Safe-Deposit Boxes: States Seize Citizens’ Property to Balance Their Budgets

Not-So-Safe-Deposit Boxes: States Seize Citizens’ Property to Balance Their Budgets

May 12, 2008. Elisabeth Leamy. abcnews

The 50 U.S. states are holding more than $32 billion worth of unclaimed property that they’re supposed to safeguard for their citizens. But a “Good Morning America” investigation found some states aggressively seize property that isn’t really unclaimed and then use the money — your money — to balance their budgets.

Unclaimed property consists of things like forgotten apartment security deposits, uncashed dividend checks and safe-deposit boxes abandoned when an elderly relative dies.

Banks and other businesses are required to turn that property over to the state for safekeeping. The problem is that the states return less than a quarter of unclaimed property to the rightful owners.

Not-So-Safe-Deposit Boxes

San Francisco resident Carla Ruff’s safe-deposit box was drilled, seized, and turned over to the state of California, marked “owner unknown.”

“I was appalled,” Ruff said. “I felt violated.”

Unknown? Carla’s name was right on documents in the box at the Noe Valley Bank of America location. So was her address — a house about six blocks from the bank. Carla had a checking account at the bank, too — still does — and receives regular statements. Plus, she has receipts showing she’s the kind of person who paid her box rental fee. And yet, she says nobody ever notified her.

“They are zealously uncovering accounts that are not unclaimed,” Ruff said.

To make matters worse, Ruff discovered the loss when she went to her box to retrieve important paperwork she needed because her husband was dying. Those papers had been shredded.

And that’s not all. Her great-grandmother’s precious natural pearls and other jewelry had been auctioned off. They were sold for just $1,800, even though they were appraised for $82,500.

“These things were things that she gave to me,” Ruff said. “I valued them because I loved her.”

Bank of America told ABC News it deeply regrets the situation and appreciates the difficulty of what Mrs. Ruff was going through. The bank has reached a settlement with Ruff and continues to update its unclaimed property procedures as laws change.

California’s Class Action Lawsuit

Ruff is not alone. Attorney Bill Palmer represents her and countless other citizens in a class action lawsuit against the state of California.

“They figured the safety-deposit box was safer than keeping it under the mattress,” Palmer said. “In the case of a lot of citizens, they were wrong, weren’t they?”

California law used to say property was unclaimed if the rightful owner had had no contact with the business for 15 years. But during various state budget crises, the waiting period was reduced to seven years, and then five, and then three. Legislators even tried for one year. Why? Because the state wanted to use that free money.

“That’s absolutely correct,” said California State Controller John Chiang, who inherited the situation when he came into office. “What we’ve done here over the last two decades has been dead wrong. We’ve kept the property and not provided owners with the opportunities — the best opportunities — to get their property back.”

Chiang now faces the daunting task of returning $5.1 billion worth of unclaimed property to people. Some states keep their unclaimed property in a special trust fund and only tap into the interest they earn on it. But California dumps the money into the general fund — and spends it.

“It’s supposed to be segregated and protected,” Palmer said. “California has taken all of that $5.1 billion and has used it as a massive loan.”

California became so addicted to spending people’s money, that, for years, it simply stopped sending notices to the rightful owners. ABC News obtained a 1996 internal memo in which the lawyer for the Bureau of Unclaimed Property argued against expanding programs to notify rightful owners. He wrote, “It could well result in additional claims of monies that would otherwise flow into the general fund.”

Seizing More Than Safe-Deposit Boxes

It’s not just safe-deposit boxes. A British man went to retire and discovered the $4 million in U.S. stock he had been counting on had been seized and sold for $200,000 years earlier — even though he was in touch with the company about other matters.

A Sacramento family lost out on railroad land rights their ancestors had owned for generations — also sold off as unclaimed property.

“If I had hung onto it, I would be a millionaire, multimillionaire,” said John Whitley. “But that didn’t happen because we didn’t get to hold it.”

State Reforms

California’s unclaimed property program was so out of control that, last year, the courts issued injunctions barring the state from seizing any more property until it made reforms. Since then, Chiang has taken several steps to try to clean up the program.

For example, the state now sends notices alerting citizens about unclaimed property before it is handed over to the state — the only state to do so. Once unclaimed property is delivered to the state, it is now held for several months while the state tries to contact the owners, rather than it being immediately sold off or destroyed.

Which raises the question, in the Internet era, is anybody really lost anymore? California and other states are just beginning to make use of modern databases that can find most anyone in minutes. Unfortunately, California only uses those databases to search after it has already seized a citizen’s property.

If California does get better at locating people, that could present another challenge. Remember, right now, the state spends the money.

“It’s like the last guy in line at a pizza parlor,” Palmer criticized. “There is only so much pizza. At the end, when I get up to the counter to claim my pizza, there may be no pizza for me.”

California’s fiscal problems are legendary and once again in the news, so it’s reasonable to question whether the state can afford to repay its citizens if a bunch of them surface at once.

“There is always going to be money to give the owners when they make their claim, ” Chiang insisted. “I don’t want my legacy to say I continued a broken program. I want my legacy to be ‘this guy was the guy who truly cared about the people and returned their money.'”

California is not the only state to come under fire for its handling of unclaimed property. In Delaware, unclaimed property is the third largest source of state revenue. Idaho recently passed an unprecedented law that says the state gets to keep unclaimed property permanently if the rightful owners don’t claim it within 10 short years. And all 50 states pay private contractors 10 to 12 percent commissions to locate and seize accounts for them. It’s an inherent conflict of interest: the more rightful owners are found, the less money the contractors make.

Of course, there are some states who handle their people’s property with respect. Oregon never takes title to unclaimed property. Instead, it holds it in a perpetual trust fund.

Colorado uses the interest on its unclaimed property fund to pay for some state programs, but leaves the principal untouched.

Missouri, Iowa and Kansas make extra efforts to reunite people with their property even setting up booths at state fairs to get the word out. The State of Maryland actively compares the names on unclaimed accounts with state income tax records. If it finds a match, the state simply cuts a check and sends it to the citizen.

Protecting Your Property

So, the question for citizens is, how do you protect yourself?

Make contact with your bank, your brokerage firm, etc. at least once a year, in a way that creates a paper trail. Make sure they have your current address.

If you own stock, occasionally vote your proxies or take other steps to keep your stock ownership active. Stay in touch with your broker.

Write a list of all your accounts and keep it with your will, so your heirs will know where to look.

Consider insuring valuables even if you keep them in your safe-deposit box. That way, you’re covered financially if the bank or state makes a mistake and empties your box. Plus, safe-deposit contents have been known to be destroyed by fire or flooding.

If you want to search for unclaimed property in your name, you do not need to pay other people to do it for you. Check out the following links for more information:

National Association of Unclaimed Property Administrators

www.missingmoney.com

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Credit Card Debt

May 1, 2008 U.S. Credit Card Debt Soars to Unprecedented Heights http://en.epochtimes.com/news/8-4-28/69849.html

Studies indicate that credit card defaults and related write-offs increased drastically since 2006. Today, lenders write off 33 percent more in credit card debt than they did two years ago. Statistics show that about 35 percent of all credit card holders are already exhibiting signs of possible default. Late credit card payments result in fees many consumers can’t afford.

Credit card debt accelerated to unprecedented heights since bank loans began to dry up due to mortgage defaults. Total U.S. credit card debt reached almost $800 billion in November 2007, up from around $680 billion in March of last year, according to the latest available government statistics. In the aftermath of the U.S. mortgage crisis, the credit card bubble may be next to burst. In the past few years, banks have aggressively marketed credit card ownership and usage to consumers with limited income and low credit scores.

Credit card standards remain lax, while loan standards have tightened to a degree. More than 50 percent of senior loan officers said in a January 2008 Federal Reserve survey that they performed a more rigorous analysis before approving a mortgage or car loan over the prior three months. Only 14 percent said so in a mid-2007 survey of the same nature. Banks and lenders have tightened their lending standards following the collapse of the subprime market.

With borrowing venues drying up, American consumers may be drawn to credit card debt, creating defaults similar to those in the mortgage market. Credit card debt—much like mortgages—are bundled and sold by investment banks as asset-backed securities. “Rising credit card debt since April 2006 amid the decrease in the mortgage expansion rate resulted in a substantial shift to credit card borrowing from mortgage debt,” according to a recent report titled “House of Cards: Consumers Turn to Credit Cards Amid the Mortgage Crisis, Delaying Inevitable Defaults.” The report was published by the Center for American Progress (CAP), a nonpartisan Washington, D.C.-based research institute.

The rules of the credit card game usually aren’t transparent and are difficult to follow even by many sophisticated consumers. Just take any credit card agreement: Caveats are written in difficult-to-understand “legalese.” Words like “late fees, annual fees, over-limit fees, cash-advance fees, balance-transfer fees, annul fees, setup fees, fees to pay balance by telephone,” and so on, are confusingly sprinkled throughout the contract.

“Credit card debt tends to carry substantially higher costs than other forms of credit, due to myriad fees in addition to high interest rates. The result is that many borrowers unwittingly slide deeper and deeper into debt as they fall prey to the lack of transparency in credit cards,” said CAP staff.

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Credit Default Swaps & CDO’s

Why Wall St. Needed Credit Default Swaps

http://seekingalpha.com/article/73060-why-wall-st-needed-credit-default-swaps

Take a CDO with a 50 basis point spread over US Treasures. Banks will buy credit default swaps costing them 20 basis points, but by doing so, even they seem to make less profit (50 vs. now only 30 bp spread), banks can actually book the difference in spread for the whole life of this CDO instantly, something called negative-basis trade.

If this CDO life is 10 years, banks can book the whole 10 years of phantom profits this year, even if this CDO defaults sometime in next 10 years. And I don’t need to mention its implications for the bonuses of the structured product groups at Wall St firms, or hedge funds with 2/20 fee structure.

In other words, who cares whether this CDO defaults next year, let us just realize the next 10 years of bonuses today! There is a common secret at Wall St. – it doesn’t matter whether a product is good or bad, the only thing matters is how you structure it. As former Secretary of the Treasury, John Connely, said to European central banks in 1970s’ “It might be our currency (US dollar), but it is your problem”. Same thing here. If CDO defaults, they have already bumped up the stock price, cashed out the stock options and their vested shares, collected the yearend bonuses, now it is investors’ problem.

This kind of accounting manipulation can fool people for a few years, but not forever, since the well of CDOs gets sucked dry very quickly when every single firm on Wall St. has found out about this and is doing it. Any firm owning a mortgage originator has a competitive “advantage” since it guarantees the source for the well. Now you know why Stanley O’Neal at Merrill Lynch wanted to buy First Franklin (a mortgage loan originator) so badly, because for every loan First Franklin originates, Merrill Lynch executives and their structured product groups will advance 10 years of their firm’s earnings and future bonuses today.

Now you understand why Wall St wants to package and collateralize everything from residential to commercial, from mortgage to credit card to auto loan. Now you also realize what is behind the major shift and increase from traditional M&A fees in the good old days to the so-called trading “profit” in recent years “earned” by investment banks.

But at the same time, this raises a lot of questions about how real are the past earnings reported by both Wall St firms and hedge funds with large CDO profits. For example, if a hedge fund manager can trade minor reduction of profit (from 50 to 30 bps) with an immediate bonus of 10 times (1 vs. 10 years) paid today, what would he choose?

He would be nuts for not using credit default swaps to “structure” his CDO holdings. If the CDO defaults next year and take his fund under the watermark, it’s no a big deal. He already collected 20% money from the “profit” the year before. He can just close the fund and open another new one, raising money probably from the same sucker pool of investors. If you want to see a pyramid scheme, there is nothing more live and vivid than this.

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2nd largest oil field in the world, Mexico’s Cantarell, declining rapidly

Mexican oil exports: start saying adios!

by Martin Payne, 19 Mar 2008. Energy Bulletin.

1)      This story illustrates the problem of RATE of production – you might have a lot of oil, but if you can only produce it at x barrels per day, then you have x barrels and no more

2)      We get 10% of our oil from Mexico, and Cantarell rate of production has gone down 29% since 2004!

Cantarell Field is a “poster child” for Peak Oil. In my opinion, Cantarell/Mexico may be one of the most poignant, and easiest to grasp examples of what Peak Oil is all about.

Most folks are surprised to learn that the world’s 2nd largest oil field is not located in Saudi Arabia. Nor even in the Middle East. In fact, it is located offshore Mexico, in the Bay of Campeche, Gulf of Mexico.

Cantarell Field, as it turns out, is a real freak of geology. The porosity – or holes in the rock where the oil is located – is believed to be the result of a rubble pile from an asteroid strike which took place some 65 million years ago! And not just any asteroid strike: The asteroid which caused what has become known as the Chicxulub Crater, on the Yucatan Peninsula, is thought to have been 6 miles in diameter, and many scientists attribute this particular asteroid strike as being the “extinction event” that took out the dinosaurs!

Cantarell was put on production in 1979. Production was 1.16 million barrels per day (1.16 MMBO/D) in 1981, and in 1995 production was still 1 MMBO/D.

In 2000, PEMEX installed the world’s largest nitrogen injection project on Cantarell. In this process, nitrogen is stripped from air and injected into the upper parts of the reservoir in order to maintain reservoir pressure, and thus to increase or maintain production. Production increased to 1.6 MMBO/D in 2001, then to 1.9 MMBO/D in 2002, and then to 2.1 MMBO/D in 2003. By the end of 2005, however, production had returned to 1.9 MMBO/D.

In January, 2006, a PEMEX press release unveiled their conclusion that Cantarell had peaked, and would decline down to a rate between 1.5 MMBO/D and .5 MMBO/D by the end of 2008.

As of the end of 2007, Cantarell was said to be producing 1.4 MMBO/D, or down some 600,000 BO/D (or 29%) from its peak rate in 2004!

Why is this important? Well, Mexico is the 3rd largest exporter of oil to the United States. Out of about 21 MMBO/D of total consumption we import some 60%, or around 12 MMBO/D.

Mexico makes up some 1.4 MMBO/D of that 12 MMBO/D, about 10 % of our total imports.

So, if Mexico can’t supply that oil – just get it somewhere else, right? Well it appears that there is little or no “spare” capacity in oil production RATE, worldwide. So, if we need 1.4 MMBO/D from Mexico but they can’t supply it, we either have to get that oil instead of someone else, or do without [2014 comment: we’ve been doing without, the financial crash has lowered demand to 16 MMBO/D due to the high levels of unemployment and poverty].

To put the ultimate loss of 1.5 MMBO/D out of Cantarell into perspective, consider the massive tar sands in Canada. Even though these tar sand RESERVES are huge, their production RATE is limited by the QUALITY of these deposits. Namely, one has to shovel, melt or dissolve this tar out of the ground. Today’s total production RATE from these tar sands, after huge efforts and investments of billions of dollars, only totals about 1.1 MMBO/D. And, with billions more invested, by 2015 they believe the rate can be increased by an additional 1.9 MMBO/D. If there weren’t any other RATE declines going on around the world, and if demand was not increasing, then the Canadian tar sands might be able to compensate for the loss of Cantarell.

Put another way, if other declines ARE present around the world, and if there are not many provinces where the RATE is significantly increasing (such as with the Canadian tar sands), and if the increases from the tar sands can barely make up for Cantarell declines, then what significant capacity increases are available to make up for the other declines?

So, Cantarell Field is a “poster child” for Peak Oil concerns.

Mr. Payne is an “upstream oil and gas professional with over 25 years of experience. Past Chairman, Houston Chapter of the American Petroleum Institute (API). Member of American Society of Mechanical Engineers (ASME), Society of Petroleum Engineers (SPE), American Solar Energy Society (ASES).”

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Richard Heinberg We need 50 million farmers

Fifty Million Farmers

by Richard Heinberg, originally published by Energy Bulletin  | Nov 17, 2006

(Note: This is the abbreviated text of a lecture by Richard Heinberg delivered to the E. F. Schumacher Society in Stockbridge, Massachusetts on October 28, 2006)

There was a time not so long ago when famine was an expected, if not accepted, part of life. Until the 19th century—whether in China, France, India or Britain—food came almost entirely from local sources and harvests were variable. In good years, there was plenty—enough for seasonal feasts and for storage in anticipation of winter and hard times to come; in bad years, starvation cut down the poorest and the weakest—the very young, the old, and the sickly. Sometimes bad years followed one upon another, reducing the size of the population by several percent. This was the normal condition of life in pre-industrial societies, and it persisted for thousands of years.

Today, in America, such a state of affairs is hard to imagine. Food is so cheap and plentiful that obesity is a far more widespread concern than hunger. The average mega-supermarket stocks an impressive array of exotic foods from across the globe, and even staples are typically trucked from hundreds of miles away. Many people in America did go hungry during the Great Depression, but those were times that only the elderly can recall. In the current regime, the desperately poor may experience chronic malnutrition and may miss meals, but for most the dilemma is finding time in the day’s hectic schedule to go to the grocery store or to cook. As a result, fast-food restaurants proliferate: the fare may not be particularly nutritious, but even an hour’s earnings at minimum wage will buy a meal or two. The average American family spent 20 percent of its income on food in 1950; today the figure is 10 percent.

This is an extraordinary situation; but because it is the only one that most Americans alive today have ever experienced, we tend to assume that it will continue indefinitely. However there are reasons to think that our current anomalous abundance of inexpensive food may be only temporary; if so, present and future generations may become acquainted with that old, formerly familiar but unwelcome houseguest—famine.

The following are four principal bases (there are others) for this gloomy forecast.

The first has to with looming fuel shortages. This is a subject I have written about extensively elsewhere, so I shall not repeat myself in any detail. Suffice it to say that the era of cheap oil and natural gas is coming to a crashing end, with global oil production projected to peak in 2010 and North American natural gas extraction rates already in decline. These events will have enormous implications for America’s petroleum-dependent food system.

Modern industrial agriculture has been described as a method of using soil to turn petroleum and gas into food. We use natural gas to make fertilizer, and oil to fuel farm machinery and power irrigation pumps, as a feedstock for pesticides and herbicides, in the maintenance of animal operations, in crop storage and drying, and for transportation of farm inputs and outputs. Agriculture accounts for about 17 percent of the U.S. annual energy budget; this makes it the single largest consumer of petroleum products as compared to other industries. By comparison, the U.S. military, in all of its operations, uses only about half that amount. About 350 gallons (1,500 liters) of oil equivalents are required to feed each American each year, and every calorie of food produced requires, on average, ten calories of fossil-fuel inputs. This is a food system profoundly vulnerable, at every level, to fuel shortages and skyrocketing prices. And both are inevitable.

An attempt to make up for fuel shortfalls by producing more biofuels—ethanol, butanol, and biodiesel—will put even more pressure on the food system, and will likely result in a competition between food and fuel uses of land and other resources needed for agricultural production. Already 14 percent of the U.S. corn crop is devoted to making ethanol, and that proportion is expected to rise to one quarter, based solely on existing projects-in-development and government mandates.

The second factor potentially leading to famine is a shortage of farmers. Much of the success of industrial agriculture lies in its labor efficiency: far less human work is required to produce a given amount of food today than was the case decades ago (the actual fraction, comparing the year 2000 with 1900, is about one seventh). But that very success implies a growing vulnerability. We don’t need as many farmers, as a percentage of the population, as we used to; so, throughout the past century, most farming families—including hundreds of thousands and perhaps millions that would have preferred to maintain their rural, self-sufficient way of life—were economically forced to move to cities and find jobs. Today so few people farm that vital knowledge of how to farm is disappearing. The average age of American farmers is over 55 and approaching 60. The proportion of principal farm operators younger than 35 has dropped from 15.9 percent in 1982 to 5.8 percent in 2002. Of all the dismal statistics I know, these are surely among the most frightening. Who will be growing our food twenty years from now? With less oil and gas available, we will need far more knowledge and muscle power devoted to food production, and thus far more people on the farm, than we have currently.

The third worrisome trend is an increasing scarcity of fresh water. Sixty percent of water used nationally goes toward agriculture. California’s Central Valley, which produces the substantial bulk of the nation’s fruits, nuts, and vegetables, receives virtually no rainfall during summer months and relies overwhelmingly on irrigation. But the snowpack on the Sierras, which provides much of that irrigation water, is declining, and the aquifer that supplies much of the rest is being drawn down at many times its recharge rate. If these trends continue, the Central Valley may be incapable of producing food in any substantial quantities within two or three decades. Other parts of the country are similarly overspending their water budgets, and very little is being done to deal with this looming catastrophe.

Fourth and finally, there is the problem of global climate change. Often the phrase used for this is “global warming,” which implies only the fact that the world’s average temperature will be increasing by a couple of degrees or more over the next few decades. The much greater problem for farmers is destabilization of weather patterns. We face not just a warmer climate, but climate chaos: droughts, floods, and stronger storms in general (hurricanes, cyclones, tornadoes, hail storms)—in short, unpredictable weather of all kinds. Farmers depend on relatively consistent seasonal patterns of rain and sun, cold and heat; a climate shift can spell the end of farmers’ ability to grow a crop in a given region, and even a single freak storm can destroy an entire year’s production. Given the fact that modern American agriculture has become highly centralized due to cheap transport and economies of scale (almost the entire national spinach crop, for example, comes from a single valley in California), the damage from that freak storm is today potentially continental or even global in scale. We have embarked on a century in which, increasingly, freakish weather is normal.

I am not pointing out these problems, and their likely consequences, in order to cause panic. As I propose below, there is a solution to at least two of these dilemmas, one that may also help us address the remaining ones. It is not a simple or easy strategy and it will require a coordinated and sustained national effort. But in addition to averting famine, this strategy may permit us to solve a host of other, seemingly unrelated social and environmental problems.

Intensifying Food Production

In order to get a better grasp of the problems and the solution being proposed, it is essential that we understand how our present exceptional situation of cheap abundance came about. In order to do that, we must go back not just a few decades, but at least ten thousand years.

The origins of agriculture are shrouded in mystery, though archaeologists have been whittling away at that mystery for decades. We know that horticulture (gardening) began at somewhat different periods, independently, in at least three regions—the Middle East, Southeast Asia, and Central America. Following the end of the last Ice Age, roughly 12,000 years ago, much of humanity was experiencing a centuries-long food crisis brought on by the over-hunting of the megafauna that had previously been at the center of the human diet. The subsequent domestication of plants and animals brought relative food security, as well as the ability to support larger and more sedentary populations.

As compared to hunting and gathering, horticulture intensified the process of obtaining food. Intensification (because it led to increased population density—i.e., more mouths to feed), then led to the need for even more intensification: thus horticulture (gardening) eventually led to agriculture (field cropping). The latter produced more food per unit of land, which enabled more population growth, which meant still more demand for food. We are describing a classic self-reinforcing feedback loop.

As a social regime, horticulture did not represent a decisive break with hunting and gathering. Just as women had previously participated in essential productive activities by foraging for plants and hunting small animals, they now played a prominent role in planting, tending, and harvesting the garden—activities that were all compatible with the care of infants and small children. Thus women’s status remained relatively high in most horticultural societies. Seasonal surpluses were relatively small and there was no full-time division of labor.

But as agriculture developed—with field crops, plows, and draft animals—societies inevitably mutated in response. Plowing fields was men’s work; women were forced to stay at home and lost social power. Larger seasonal surpluses required management as well as protection from raiders; full-time managers and specialists in violence proliferated as a result. Societies became multi-layered: wealthy ruling classes (which had never existed among hunter-gatherers, and were rare among gardeners) sat atop an economic pyramid that came to include scribes, soldiers, and religious functionaries, and that was supported at its base by the vastly more numerous peasants—who produced all the food for themselves and everyone else as well. Writing, mathematics, metallurgy, and, ultimately, the trappings of modern life as we know it thus followed not so much from planting in general, as from agriculture in particular.

As important an instance of intensification as agriculture was, in many respects it pales in comparison with what has occurred within the past century or so, with the application of fossil fuels to farming. Petroleum-fed tractors replaced horses and oxen, freeing up more land to grow food for far more people. The Haber-Bosch process for synthesizing ammonia from fossil fuels, invented just prior to World War I, has doubled the amount of nitrogen available to green nature—with nearly all of that increase going directly to food crops. New hybrid plant varieties led to higher yields. Technologies for food storage improved radically. And fuel-fed transport systems enabled local surpluses to be sold not just regionally, but nationally and even globally. Through all of these strategies, we have developed the wherewithal to feed seven times the population that existed at the beginning of the Industrial Revolution. And, in the process, we have made farming uneconomical and unattractive to all but a few.

That’s the broad, global overview. In America, whose history as an independent nation begins at the dawn of the industrial era, the story of agriculture comprises three distinct periods:

The Expansion Period (1600 to 1920): Increases in food production during these three centuries came simply from putting more land into production; technological change played only a minor role.

The Mechanization Period (1920 to 1970): In this half-century, technological advances issuing from cheap, abundant fossil-fuel energy resulted in a dramatic increase in productivity (output per worker hour). Meanwhile, farm machinery, pesticides, herbicides, irrigation, new hybrid crops, and synthetic fertilizers allowed for the doubling and tripling of crop production. Also during this time, U.S. Department of Agriculture policy began favoring larger farms (the average U.S. farm size grew from 100 acres in 1930 to almost 500 acres by 1990), and production for export.

The Saturation Period (1970-present): In recent decades, the application of still greater amounts of energy have produced smaller relative increases in crop yields; meanwhile an ever-growing amount of energy is being expended to maintain the functioning of the overall system. For example, about ten percent of the energy in agriculture is used just to offset the negative effects of soil erosion, while increasing amounts of pesticides must be sprayed each year as pests develop resistances. In short, strategies that had recently produced dramatic increases in productivity became subject to the law of diminishing returns.

While we were achieving miracles of productivity, agriculture’s impact on the natural world was also growing; indeed it is now the single greatest source of human damage to the global environment. That damage takes a number of forms: erosion and salinization of soils; deforestation (a strategy for bringing more land into cultivation); fertilizer runoff (which ultimately creates enormous “dead zones” around the mouths of many rivers); loss of biodiversity; fresh water scarcity; and agrochemical pollution of water and soil.

In short, we created unprecedented abundance while ignoring the long-term consequences of our actions. This is more than a little reminiscent of how some previous agricultural societies—the Greeks, Babylonians, and Romans—destroyed soil and habitat in their mania to feed growing urban populations, and collapsed as a result.

Fortunately, during the past century or two we have also developed the disciplines of archaeology and ecology, which teach us how and why those ancient societies failed, and how the diversity of the web of life sustains us. Thus, in principle, if we avail ourselves of this knowledge, we need not mindlessly repeat yet again the time-worn tale of catastrophic civilizational collapse.

The 21st Century: De-Industrialization

How might we avoid such a fate?

Surely the dilemmas we have outlined above are understood by the managers of the current industrial food system. They must have some solutions in mind.

Indeed they do, and, predictably perhaps, those solutions involve a further intensification of the food production process. Since we cannot achieve much by applying more energy directly to that process, the most promising strategy on the horizon seems to be the genetic engineering of new crop varieties. If, for example, we could design crops to grow with less water, or in unfavorable climate and soil conditions, we could perhaps find our way out of the current mess.

Unfortunately, there are some flaws with this plan. Our collective experience with genetically modifying crops so far shows that glowing promises of higher yields, or of the reduced need for herbicides, have seldom been fulfilled. At the same time, new genetic technologies carry with them the potential for horrific unintended consequences in the forms of negative impacts on human health and the integrity of ecosystems. We have been gradually modifying plants and animals through selective breeding for millennia, but new gene-splicing techniques enable the re-mixing of genomes in ways and to degrees impossible heretofore. One serious error could result in biological tragedy on an unprecedented scale.

Yet even if future genetically modified commercial crops prove to be much more successful than past ones, and even if we manage to avert a genetic apocalypse, the means of producing and distributing genetically engineered seeds is itself reliant on the very fuel-fed industrial system that is in question.

Is it possible, then, that a solution lies in another direction altogether—perhaps in deliberately de-industrializing production, but doing so intelligently, using information we have gained from the science of ecology, as well as from traditional and indigenous farming methods, in order to reduce environmental impacts while maintaining total yields at a level high enough to avert widespread famine?

This is not an entirely new idea (as you all well know, the organic and ecological farming movements have been around for decades), but up to this point the managers of the current system have resisted it. This is no doubt largely because those managers are heavily influenced by giant corporations that profit from centralized industrial production for distant markets. Nevertheless, the fact that we have reached the end of the era of cheap oil and gas demands that we re-examine the potential costs and benefits of our current trajectory and its alternatives.

I believe we must and can de-industrialize agriculture. The general outline of what I mean by de-industrialization is simple enough: this would imply a radical reduction of fossil fuel inputs to agriculture, accompanied by an increase in labor inputs and a reduction of transport, with production being devoted primarily to local consumption.

Once again, fossil fuel depletion almost ensures that this will happen. But at the same time, it is fairly obvious that if we don’t plan for de-industrialization, the result could be catastrophic. It’s worth taking a moment to think about how events might unfold if the process occurs without intelligent management, driven simply by oil and gas depletion.

Facing high fuel prices, family farms would declare bankruptcy in record numbers. Older farmers (the majority, in other words) would probably choose simply to retire, whether they could afford to or not. However, giant corporate farms would also confront rising costs—which they would pass along to consumers by way of dramatically higher food prices.

Yields would begin to decline—in fits and starts—as weather anomalies and water shortages affected one crop after another.

Meanwhile, people in the cities would also feel the effects of skyrocketing energy prices. Entire industries would falter, precipitating a general economic collapse. Massive unemployment would lead to unprecedented levels of homelessness and hunger.

Many people would leave cities looking for places to live where they could grow some food. Yet they might find all of the available land already owned by banks or the government. Without experience of farming, even those who succeeded in gaining access to acreage would fail to produce much food and would ruin large tracts of land in the process.

Eventually these problems would sort themselves out; people and social systems would adapt—but probably not before an immense human and environmental tragedy had ensued.

I wish I could say that this forecast is exaggerated for effect. Yet the actual events could be far more violent and disruptive than it is possible to suggest in so short a summary.

Examples and Strategies

Things don’t have to turn out that way. As I have already said, I believe that the de-industrialization of agriculture could be carried out in a way that is not catastrophic and that in fact substantially benefits society and the environment in the long run. But to be convinced of the thesis we need more than promises—we need historic examples and proven strategies. Fortunately, we have two of each.

In some respects the most relevant example is that of Cuba’s Special Period. In the early 1990s, with the collapse of the Soviet Union, Cuba lost its source of cheap oil. Its industrialized agricultural system, which was heavily fuel-dependent, immediately faltered. Very quickly, Cuban leaders abandoned the Soviet industrial model of production, changing from a fuel- and petrochemical-intensive farming method to a more localized, labor-intensive, organic mode of production.

How they did this is itself an interesting story. Eco-agronomists at Cuban universities had already been advocating a transition somewhat along these lines. However, they were making little or no headway. When the crisis hit, they were given free rein to, in effect, redesign the entire Cuban food system. Had these academics not had a plan waiting in the wings, the nation’s fate might have been sealed.

Heeding their advice, the Cuban government broke up large, state-owned farms and introduced private farms, farmer co-ops, and farmer markets. Cuban farmers began breeding oxen for animal traction. The Cuban people adopted a mainly vegetarian diet, mostly involuntarily (Meat eating went from twice a day to twice a week). They increased their intake of vegetable sources of protein and farmers decreased the growing of wheat and rice (Green Revolution crops that required too many inputs). Urban gardens (including rooftop gardens) were encouraged, and today they produce 50 to 80 percent of vegetables consumed in cities.

Early on, it was realized that more farmers were needed, and that this would require education. All of the nation’s colleges and universities quickly added courses on agronomy. At the same time, wages for farmers were raised to be at parity with those for engineers and doctors. Many people moved from the cities to the country; in some cases there were incentives, in others the move was forced.

The result was survival. The average Cuban lost 20 pounds of body weight, but in the long run the overall health of the nation’s people actually improved as a consequence. Today, Cuba has a stable, slowly growing economy. There are few if any luxuries, but everyone has enough to eat. Having seen the benefit of smaller-scale organic production, Cuba’s leaders have decided that even if they find another source of cheap oil, they will maintain a commitment to their new, decentralized, low-energy methods.

I don’t want to give the impression that Cubans sailed through the Special Period unscathed. Cuba was a grim place during these years, and to this day food is far from plentiful there by American standards. My point is not that Cuba is some sort of paradise, but simply that matters could have been far worse.

It could be objected that Cuba’s experience holds few lessons for our own nation. Since Cuba has a very different government and climate, we might question whether its experience can be extrapolated to the U.S.

Let us, then, consider an indigenous historical example. During both World Wars, Americans planted Victory Gardens. During both periods, gardening became a sort of spontaneous popular movement, which (at least during World War II) the USDA initially tried to suppress, believing that it would compromise the industrialization of agriculture. It wasn’t until Eleanor Roosevelt planted a Victory Garden in the White House lawn that agriculture secretary Claude Wickard relented; his agency then began to promote Victory Gardens and to take credit for them. At the height of the movement, Victory Gardens were producing roughly 40 percent of America’s vegetables, an extraordinary achievement in so short a time.

In addition to these historical precedents, we have new techniques developed with the coming agricultural crisis in mind; two of the most significant are Permaculture and Biointensive farming (there are others—such as efforts by Wes Jackson of The Land Institute to breed perennial grain crops—but limitations of time and space require me to pick and choose).

Permaculture was developed in the late 1970s by Australian ecologists Bill Mollison and David Holmgren in anticipation of exactly the problem we see unfolding before us. Holmgren defines Permaculture as “consciously designed landscapes that mimic the patterns and relationships found in nature, while yielding an abundance of food, fiber, and energy for provision of local needs.” Common Permaculture strategies include mulching, rainwater capture using earthworks such as swales, composting, and the harmonious integration of aquaculture, horticulture, and small-scale animal operations. A typical Permaculture farm may produce a small cash crop but concentrates largely on self-sufficiency and soil building. Significantly, Permaculture has played an important role in Cuba’s adaptation to a low-energy food regime.

Biointensive farming has been developed primarily by Californian John Jeavons, author of How to Grow More Vegetables. Like Permaculture, Biointensive is a product of research begun in the 1970s. Jeavons defines Biointensive (now trademarked as “Grow Biointensive”) farming as

. . . an organic agricultural system that focuses on maximum yields from the minimum area of land, while simultaneously improving the soil. The goal of the method is long-term sustainability on a closed-system basis. Because biointensive is practiced on a relatively small scale, it is well suited to anything from personal or family to community gardens, market gardens, or minifarms. It has also been used successfully on small-scale commercial farms.

Like Homgren and Mollison, Jeavons has worked for the past three decades in anticipation of the need for the de-industrialization of food production due to accumulating environmental damage and fossil fuel depletion. Currently Biointensive farming is being taught extensively in Africa and South America as a sustainable alternative to the globalized monocropping. The term “biointensive” suggests that what we are discussing here is not a de-intensification of food production, but rather the development of production along entirely different lines. While both Permaculture and Biointensive have been shown to be capable of dramatically improving yields-per-acre, their developers clearly understand that even these methods will eventually fail us unless we also limit demand for food by gradually and humanely limiting the size of the human population.

In short, it is possible in principle for industrial nations like the U.S. to make the transition to smaller-scale, non-petroleum food production, given certain conditions. There are both precedents and models.

However, all of them imply more farmers. Here’s the catch—and here’s where the ancillary benefits kick in.

The Key: More Farmers!

One way or another, re-ruralization will be the dominant social trend of the 21st century. Thirty or forty years from now—again, one way or another—we will see a more historically normal ratio of rural to urban population, with the majority once again living in small, farming communities. More food will be produced in cities than is the case today, but cities will be smaller. Millions more people than today will be in the countryside growing food.

They won’t be doing so the way farmers do it today, and perhaps not the way farmers did it in 1900.

Indeed, we need perhaps to redefine the term farmer. We have come to think of a farmer as someone with 500 acres and a big tractor and other expensive machinery. But this is not what farmers looked like a hundred years ago, and it’s not an accurate picture of most current farmers in less-industrialized countries. Nor does it coincide with what will be needed in the coming decades. We should perhaps start thinking of a farmer as someone with 3 to 50 acres, who uses mostly hand labor and twice a year borrows a small tractor that she or he fuels with ethanol or biodiesel produced on-site.

How many more farmers are we talking about? Currently the U.S. has three or four million of them, depending on how we define the term.

Let’s again consider Cuba’s experience: in its transition away from fossil-fueled agriculture, that nation found that it required 15 to 25 percent of its population to become involved in food production. In America in 1900, nearly 40 percent of the population farmed; the current proportion is close to one percent.

Do the math for yourself. Extrapolated to this country’s future requirements, this implies the need for a minimum of 40 to 50 million additional farmers as oil and gas availability declines. How soon will the need arise? Assuming that the peak of global oil production occurs within the next five years, and that North American natural gas is already in decline, we are looking at a transition that must occur over the next 20 to 30 years, and that must begin approximately now.

Fortunately there are some hopeful existing trends to point to. The stereotypical American farmer is a middle-aged, Euro-American male, but the millions of new farmers in our future will have to include a broad mix of people, reflecting America’s increasing diversity. Already the fastest growth in farm operators in America is among female full-time farmers, as well as Hispanic, Asian, and Native American farm operators.

Another positive trend worth noting: Here in the Northeast, where the soil is acidic and giant agribusiness has not established as much of a foothold as elsewhere, the number of small farms is increasing. Young adults—not in the millions, but at least in the hundreds—are aspiring to become Permaculture or organic or Biointensive farmers. Farmers markets and CSAs are established or springing up throughout the region. This is somewhat the case also on the Pacific coast, much less so in the Midwest and South.

What will it take to make these tentative trends the predominant ones? Among other things we will need good and helpful policies. The USDA will need to cease supporting and encouraging industrial monocropping for export, and begin supporting smaller farms, rewarding those that make the effort to reduce inputs and to grow for local consumption. In the absence of USDA policy along these lines, we need to pursue state, county, and municipal efforts to support small farms in various ways, through favorable zoning, by purchasing local food for school lunches, and so on.

We will also require land reform. Those millions of new farmers will need access to the soil, and there must be some means for assisting in making land available for this purpose. Conservation land trusts may be useful in this regard, and we might take inspiration from Indian Line Farm, here in the northeast.

Since so few people currently know much about farming, education will be essential. Universities and community colleges have both the opportunity and responsibility to quickly develop programs in small-scale ecological farming methods—programs that also include training in other skills that farmers will need, such as in marketing and formulating business plans.

Since few if any farms are financially successful the first year or even the second or third, loans and grants will also be necessary to help farmers get started.

These new farmers will need higher and stabilized food prices. As difficult as it may be even to imagine this situation now, food rationing may be required at some point in the next two or three decades. That quota system needs to be organized in such a way as to make sure everyone has the bare essentials, and to support the people at the base of the food system—the farmers.

Finally, we need a revitalization of farming communities and farming culture. A century ago, even in the absence of the air and auto transport systems we now take for granted, small towns across this land strove to provide their citizens with lectures, concerts, libraries, and yearly chautauquas. Over the past decades these same towns have seen their best and brightest young people flee first to distant colleges and then to the cities. The folks left behind have done their best to maintain a cultural environment, but in all too many cases that now consists merely of a movie theater and a couple of video rental stores. Farming communities must be interesting, attractive places if we expect people to inhabit them and for children to want to stay there.

If We Do This Well

We have been trained to admire the benefits of intensification and industrialization. But, as I’ve already indicated, we have paid an enormous price for these benefits—a price that includes alienation from nature, loss of community and tradition, and the acceptance of the anonymity and loss of autonomy implied by mass society. In essence, this tradeoff has its origins in the beginnings of urbanization and agriculture.

Could we actually regain much of what we have lost? Yes, perhaps by going back, at least in large part, to horticulture. Recall that the shift from horticulture to agriculture was, as best we can tell, a fateful turning point in cultural history. It represented the beginning of full-time division of labor, hierarchy, and patriarchy.

Biointensive farming and Permaculture are primarily horticultural rather than agricultural systems. These new, intelligent forms of horticulture could, then, offer an alternative to a new feudalism with a new peasantry. In addition, they emphasize biodiversity, averting many of the environmental impacts of field cropping. They use various strategies to make hand labor as efficient as possible, minimizing toil and drudgery. And they typically slash water requirements for crops grown in arid regions.

We have gotten used to a situation where most farmers rely on non-farm income. As of 2002 only a bit less than 60 percent of farm operators reported that their primary work is on the farm. Only 9 percent of primary operators on farms with one operator, and 10 percent on farms with multiple operators, report all of their income as coming from the farm.

The bad side of this is that it means it’s hard to make a living farming these days. The good side is that we don’t have to think of farming as an exclusive occupation. As people return to small communities and to farming, they could bring with them other interests. Rather than a new peasantry that spends all of its time in drudgery, we could look forward to a new population of producers who maintain interests in the arts and sciences, in history, philosophy, spirituality, and psychology—in short, the whole range of pursuits that make modern urban life interesting and worthwhile.

Moreover, the re-ruralization program I am describing could be a springboard for the rebirth of democracy in this nation. I do not have to tell this audience how, over the past few years, democracy in America has become little more than a slogan. In fact this erosion of our democratic traditions has been going on for some time. As Kirkpatrick Sale showed in his wonderful book Human Scale, as communities grow in size, individuals’ ability to influence public affairs tends to shrink. Sociological research now shows that people who have the ability to influence policy in their communities show a much higher sense of satisfaction with life in general. In short, the re-ruralization of America could represent the fulfillment of Thomas Jefferson’s vision of an agrarian democracy—but without the slaves.

If we do this well, it could mean the revitalization not only of democracy, but of the family and of authentic, place-based culture. It could also serve as the basis for a new, genuine conservatism to replace the ersatz conservatism of the current ruling political elites.

What I am proposing is nothing less than a new alliance among environmental organizations, farmers, gardeners, organizations promoting economic justice, the anti-globalization movement, universities and colleges, local businesses, churches, and other social organizations. Moreover, the efforts of this alliance would have to be coordinated at the national, state, and local level. This is clearly a tall order. However, we are not talking about merely a good idea. This is a survival strategy.

It may seem that I am describing and advocating a reversion to the world of 1800, or even that of 8,000 BC. This is not really the case. We will of course need to relearn much of what our ancestors knew. But we have discovered a great deal about biology, geology, hydrology, and other relevant subjects in recent decades, and we should be applying that knowledge—as Holmgren, Mollison, Jeavons, and others have done—to the project of producing food for ourselves.

Cultural anthropology teaches us that the way people get their food is the most reliable determinant of virtually all other social characteristics. Thus, as we build a different food system we will inevitably be building a new kind of culture, certainly very different from industrial urbanism but probably also from what preceded it. As always before in human history, we will make it up as we go along, in response to necessity and opportunity.

Perhaps these great changes won’t take place until the need is obvious and irresistibly pressing. Maybe gasoline needs to get to $10 a gallon. Perhaps unemployment will have to rise to ten or twenty or forty percent, with families begging for food in the streets, before embattled policy makers begin to reconsider their commitment to industrial agriculture.

But even in that case, as in Cuba, all may depend upon having another option already articulated. Without that, we will be left to the worst possible outcome.

Rather than consigning ourselves to that fate, let us accept the current challenge—the next great energy transition—as an opportunity not to vainly try to preserve business as usual, the American Way of Life that, we are told, is not up for negotiation, but rather to re-imagine human culture from the ground up.

(This lecture drew on certain ideas earlier put forward by Knox, New York farmer Sharon Astyk in her remarks at the 2006 Peak Oil and Community Solutions conference in Yellow Springs, Ohio, and on others that emerged in conversation with Pat Murphy of Community Service and Julian Darley of the Post Carbon Institute.)

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We’ll need more Farmers

Energy Descent and Agricultural Population

Jason Bradford on March 11, 2009

Some excerpts of this article below:

Among the cadre of folks who think about food systems and sustainability in the U.S., there’s a concern about the number of farmers and their age. Only about two percent (5,802,000 / 295,410,000 in 2004) of the U.S. population is part of a farm family, and the average age of principal operators of farms is nearing 60 years (See the recent release of the 2007 Ag Census for details). Since mechanization and the fuels that power machines are what enable such a small agricultural labor force, is it reasonable to assume that a decline in fossil fuels will require more farmers?

Others, such as peak oil educators Richard Heinberg and Sharon Astyk, have suggested this will indeed be the case, even going so far as to put a rough number on the future farmers of America. Their estimates are partly based on looking at the proportion of farmers in an early to pre-industrial economic system in the United States, when about a third of the population engaged in agriculture and at societal differences today. They then adjust for current population size to arrive at the admittedly tentative figure of 50 to 100 million farmers (or members of farming families) needed to feed a population of 300 million.

As these authors point out, not only is the absolute number very large compared to today, but given the age of the current crop of farmers it implies that a rapid education of youth will be required to keep bread on the table. Given the importance of this topic, I wanted to take a look myself. Just as we use multiple lines of evidence to understand the evolution of life, oil depletion, and climate change, we need to look for confirmation from as many angles as possible. Furthermore, better knowledge potentially gets us closer to grasping the scale and rate of change required to cope with the problem in the same way that depletion rates in existing fields and net exports analyses do in the oil situation, or the timing and consequences of melting ice sheets and release of methane from warming permafrost do in the climate system.

Perhaps we can validate or refute this scenario by further use of the comparative method–for example, we may compare a future scenario to a potentially analogous historic past. In the analysis presented here, I take as a given that the United States (and other high energy consuming industrial countries) will have less energy available in the future, at least of the type currently used in mechanized agriculture. The comparison I use is not historic, but contemporary. I know that today some nations have much less energy consumption than others and anecdotally I am aware that poorer countries tend to be more agrarian. If nations with less energy consumption have more farmers, it would support the notion that a reduction in energy consumption in the U.S. (and other industrialized countries) will lead to an increase in farmers.

Is there a discernable inverse relationship between energy consumption and agricultural populations among nations?

Let’s take a look. First, I had to find total population by nation and agricultural population (which I believe means farmers and their immediate dependents) by nation. These data can be downloaded from the United Nations Food and Agriculture Organization (FAO) (http://faostat.fao.org/site/550/default.aspx).

Simply dividing the agricultural population by the total population gives the percentage that live an agricultural life. The range of this figure is huge, from essentially zero for places like Singapore to over 90% for places like Bhutan. I really don’t know how accurate censuses data are from the 205 countries used (not all places are fully independent nations, e.g., Puerto Rico is separated from the U.S. in these data sets), but assume figures are in the ballpark. Certainly citizens of Bhutan and Singapore have vastly different livelihoods. According to 2004 FAO data, overall about 41% of the world’s people still live in families who work in agriculture (2.6 billion out of 6.4 billion).

Most nations (about 70%) have 40% or less of their population in agriculture. This means that the fewer countries with high percentages of agricultural workers have large populations, e.g., China and India are 64% and 52% respectively and equal about a third of the total world population. In all likelihood, large populations correlate with high population density. As a 1997 paper by Conforti and Giampietro showed, economic forces in poorer nations with dense populations tend to retain farmers.

Second, I had to find energy consumption data. It is difficult to locate data on use of wood, animal dung, etc., but for commercial energy such as oil, natural gas, coal, and electricity the Energy Information Administration (EIA) of the U.S. Department of Energy has available spreadsheets for download (see table E.1 at http://www.eia.doe.gov/iea/wecbtu.html). While this doesn’t include all forms of energy, it does cover the forms most readily usable in an industrial agricultural system.

As expected, nations with relatively little commercial energy consumption tend to have lots of farmers

To harmonize the two data sets I used 2004 data and limited the analysis to 205 nations—which I figure is fairly complete. The figure below shows the results, plotting the percent agricultural population as a potential response to per capita energy consumption.Ag Popu and energy consumption 205 countries

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Though I may have just done so, I am mistrustful of studying this issue in isolation. Nagging at me is the question of whether the globalized industrial system is inherently unstable in the face of multiple challenges, including energy scarcity but also the converging crises spawned by the surging weight of humanity. Climate change, financial wobbles, violent conflicts and related spin-offs can unpredictably disrupt the vast system of trade that moves fertilizers, seeds and replacement parts that keep industrial agriculture humming. I think we are already seeing hints of this scenario in the U.S., as farmers run short of diesel fuel during harvest season and end up leaving crops in the ground.

Some of Jason’s replies in the COMMENTS section:

Having a farming system that includes long rotations in pasture or other deep rooted perennials is very important. Must go through cycles of fungal dominance to bring deep soil layers into the mix, add the minerals to the top soil, which basically get mined by the annuals. If I was head of the USDA I would have the U.S. make a strategic goal of LOWERING its grain production by 50% so that the feedlots go out of business, land is pastured, and meat is once again grass fed and local. Do this slowly and strategically and nobody needs to starve. In fact, it would likely prevent starvation by keeping the soils from being continually pushed beyond their limits.

————–

I was looking at the work ahead of me at my little farm and thinking…it would be so much easier if I was primarily just trying to grow for my family. I could readily cover most of our vegetable food needs by hand without a whole lot of aggravation. For grains and legumes a drill seeder and small combine or at least a quality stationary thresher and seed cleaner would certainly be a great tool set. But instead I am trying to grow for other people, and they don’t pay very much. At least in my situation I don’t pay property taxes because it is public property, but what if I did? There’s no way this would be worth it.

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Softer landing if we can keep the Combines going

Save it for the Combine

August 24, 2010. Jason Bradford

Excerpts from this article:

The combine performs tasks that replace an enormous amount of labor in a reliable and timely fashion.  It cuts the stalks of seed crops, threshes the heads to dislodge the seeds, and then separates the seeds from the straw and chaff.  Without the combine (and a series of intermediate technologies), harvesting grains involves manually cutting stalks, bundling them, transporting the bundle to storage, threshing and winnowing.

The labor efficiency of the combine is extreme.  Over the course of a long and somewhat boring 12 hour day in his air conditioned cab (made a little better by listening to audio books on an iPod), Clint can harvest about 25 acres of wheat.  We visited while he was in a field with a hard red variety that yields about 2400 lbs per acre (soft white yields are 2-3 times higher).  In one day, Clint and his machine will collect 60,000 lbs of hard red wheat, or 1000 bushels.

Each pound of wheat contains about 1500 food calories (i.e., kilo calories), and a person needs about 2500 calories per day.  A year’s supply of calories for a person is in the neighborhood of 900,000, which in wheat units is 600 lbs.  In simple terms, during a day of work Clint can supply the annual food needs of 100 people.  Of course he and his dad Mike also spent days prepping and sowing the field, and there are hours planning, maintaining equipment, and marketing, etc., but in total the amount of time actually spent with machines on that 25 acres is probably only a week or so.  And since Clint and his family manage to farm several hundred acres it all works out to about 100 people fed by one guy like Clint, which is typical for the US food system.

I propose that the main enabler of a demographic shift away from rural-agrarian populations to an urban-industrial one is the combine.  The combine removes most labor from agriculture for the most critical crops:  edible grains, legumes and oil seeds.  Seeds are a highly portable, storable and versatile class of food, allowing civilizations to trade and buffer against shortages.  Most calories now consumed derive directly or indirectly from seeds.

It seems plausible that in the US we could do away with 3/4 of our per capita energy and, if we allocate smartly, keep the combines running and continue to feed everybody with little extra labor (and assuming climate change doesn’t bite too sharply into yields).

I  have mixed feelings about how the historical shift into cities and away from farms has impacted our culture.  On the one hand, surplus food has permitted our society to specialize greatly, developing technologies, arts and forms of entertainment that I truly enjoy.  Material abundance may also have led to cultural openness and flexibility, or what may be called liberalism, as opposed to the rigidity, isolation and xenophobia common to many pre-industrial societies.

On the other hand, I am certainly no fan of the over-consumptive lifestyles and the disconnection from nature endemic to highly industrialized cultures.  However, one possible future entails a larger agrarian population as industrialized countries lose access to abundant fossil fuels.  For example, even if we manage to save fuel for the combines, more labor will still be needed for plenty of other tasks.  While this is likely to be a painful process, what could emerge is greater ecological awareness—the understanding that our livelihoods are deeply connected and dependent upon natural processes.  Such a path is described in some detail by David Holmgren in Future Scenarios.

If energy descent is slow enough, our economy will have hybrid characteristics—leveraging the value of existing infrastructure and machinery as long as possible while learning how to adapt to natural rhythms.  Keeping such a transition as benign as feasible requires food supply stability. Maintaining social cohesion gives the population time to adjust to the new normal.  Combines, I would argue, are a fantastic tool for obtaining surplus food.  We should keep them running during any potential phase of “scarcity industrialism.”

Energy Returned

Obviously, combines are entirely reliant on barrels and barrels of liquid fuel.  Clint told me he uses about 50 gallons of fuel for every 8-9 hours harvesting wheat, which would cover about 17 acres.  This means it takes around three gallons of diesel fuel per acre, just for the harvest. In standard energy terms three gallons of diesel contains 0.44 Giga Joules (GJ).  For comparison, 2400 lbs of wheat contains just over 15 GJ of edible energy.  Ignoring all the other energy needed to deliver the fuel to the farm, and get the crop to maturity, the harvest-only EROI is a highly profitable 34:1.

Liquid fuels are absolutely essential for industrial farming systems.  I worry less about nitrogen fertilizer inputs, herbicides and pesticides, as these can be dramatically reduced using organic and agroecological methods.  It is much more difficult to substantially decrease liquid fuel usage.  Even with no-till methods, tractors make passes to sow seeds, and they make passes to harvest.

Unless you relish the idea of your descendants living a life akin to Little House on the Prairie, it may be prudent to cut back a bit on oil consumption today and extend the reserves of fossil fuels as long as possible.  Time is second to oil on my list of most precious resources.  A slowing down today, when we have so much excess, potentially buys a lot of time for tomorrow.  I don’t know if we will use this time to develop liquid fuel substitutes for fossil fuels to run combines, or manufacture millions of scythes and train a whole generation to use them.

 

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Energy in the Food System uses 19% of all energy consumed in the USA. Pimentel 2008

Pimentel David, et. al. 2008.  Reducing Energy Inputs in the US Food System.  Human Ecology 36:459–471

[ Here are some excerpts from this paper. I don’t list many of the ideas in the article on how to do this though, read it if you’d like to know more]

Abstract Petroleum and natural gas are the primary fuels in the US food system. Both fuels are now in short supply and significant quantities are being imported into the USA from various nations. An investigation documented that fossil energy use in the food system could be reduced by about 50% by appropriate technology changes in food production, processing, packaging, transportation, and consumption. The results suggest that overall, farmers benefit as well as consumers.

Introduction  Petroleum, natural gas, coal, and other mined fuels currently provide the USA with nearly all of its diverse energy needs at a cost $700 billion/year (USCB 2007). Given that more than 90% of US oil deposits have been depleted, the country now imports over 65% of its oil at an annual cost of $200 billion (USCB 2004–2005; Deffeyes 2001). These figures indicate the magnitude of the economic and energy challenges associated with supplying food for the US population.

Further, the usage of oil and natural gas has peaked at a time when oil and gas reserves are predicted to last only 40 to 50 more years (Duncan and Youngquist 1999; Deffeyes 2001). As oil and natural gas supplies decline, the USA will have to depend on coal and a variety of renewable energy technologies. Best estimates are that coal supplies are only capable of providing the USAwith 50 to 100 years of energy (USCB 2007). With the US population continuing to grow close to its current rate, it is projected to increase from 317 million to one billion in about 100 years, further exacerbating strains on coal and oil supplies (Abernethy 2006). However, it is unlikely that such a population could be sustained with the diminishing availability of fossil fuels. The American food supply is driven almost entirely by non-renewable energy sources. In total, each American requires approximately 2,000 l/year in oil equivalents to supply their food, which accounts for about 19% of the total energy use in the USA. Agricultural production, plus food processing and packaging, consumes 14%, while transportation and preparation use 5% of total energy in the USA (Pimentel et al. 2007).

Food Consumed by Americans The fossil energy required to produce the relatively high level of animal products consumed in the average American diet are estimated to be 50% of the total energy inputs, while to produce staple foods such as potatoes, rice, common fruits and vegetables, uses about 20% of the fossil energy inputs.  The average American consumes 1,000 kg (2,200 lb) of food per year containing an estimated 3,747 kcal per day (Table 1). A vegetarian diet of an equivalent 3,747 kcal per day requires 33% less fossil energy than the average American diet (Pimentel and Pimentel 1996). The Food and Drug Administration (FDA 2007) recommends an average daily consumption of 2,000 to 2,500 kcal a day, much less than provided by the typical American diet (Vaclavik et al. 2006). Reducing the calorie intake to a lower level would significantly reduce the energy used in food production.

Renewable Energy Supplies The production of 46 quads per year from renewable energy technologies would require at least 17% of total land area not counting cropland in the USA (Pimentel et al. 2002a).

The renewable energy systems that are projected to provide the most energy in the future are photovoltaics, biomass (thermal), and hydroelectric power (Pimentel et al. 2002a). None of these renewable energy sources produce liquid fuels [which is a big problem – tractors, trucks, cars, ships, trains, mass transit, and other essential agricultural and transportation machinery runs on liquid fuels 97% of them oil].

The decline of fossil energy reserves will force the USA to rely on various renewable energy technologies to maintain a viable food supply. These include: hydroelectric, biomass (wood), wind power, solar thermal systems, photovoltaics, passive energy systems, geothermal, biogas, and methanol (Hayden 2001; Pimentel et al. 2002a; Pimentel 2008). Ethanol is not included in this study because it fails to provide renewable energy (Pimentel and Patzek 2005). Together, these systems could provide the USA with an estimated 46 of the 103 quads (quad=1015 BTU) of energy currently used per year (Pimentel 2008; USCB 2004– 2005). The renewable energy systems that are projected to provide the most energy in the future are photovoltaics, biomass (thermal), and hydroelectric power (Pimentel et al. 2002a).

Hydroelectric power already supplies the USA with 269 billion kWh or 7% of the nation’s electricity at a cost of $0.02 per kWh (USCB 2007). One drawback to hydroelectric plants is the substantial land requirement for water reservoirs; 75,000 ha of reservoir land and 14 trillion liters of water are needed to produce 1 billion kWh per year (Pimentel et al. 2002a; Sims et al. 2003).

Land Availability Land is a major concern when attempting to modify fossil energy usage as land provides 99.9% of the human food supply (measured in calories; FAOSTAT 2004). As the population expands, more land is needed to meet nutritional needs, yet the per capita availability of world cropland has declined by 20% in the past decade (Worldwatch Institute 2001). This decrease is due in part to the loss of viable cropland caused by wind and water erosion at a rate of ten million hectares per year (Preiser 2005). In addition, another ten million hectares are abandoned annually worldwide due to severe salinization as a result of irrigation (FAO 2006).

Loss of soil is insidious; one rain or wind storm can remove 1 mm of topsoil and nearly 14 tons of total soil per hectare. This 1 mm of erosion can easily go unnoticed by farmers. Soil erosion occurs at rates ranging from 10 t ha-1 year-1 in the USA and Europe to 30 t ha-1 year-1 in Africa, South America and Asia. Approximately 75 billion tons of topsoil is lost each year worldwide (Pimentel 2006a; Wilkinson and McElroy 2007). Additionally, rapid deforestation (at a rate of 11.2 million ha/year) is occurring as more forest is claimed to replace lost and degraded cropland (Pimentel et al. 2005).

Cropland now occupies 17% of the total land area in the USA, but little additional land is available or even suitable for future agricultural expansion (USDA 2004).

At present, the global availability of land per capita is 0.23 ha for cropland and 0.5 ha for pastureland (Pimentel and Pimentel 2006). However, the USA and Europe have 0.5 ha of cropland and 0.81 ha of pasture available per capita, which is the minimum amount of land required to support their diverse food systems (Pimentel and Wilson 2004; USDA 2004).

As the US population increases to a projected 1 billion people (120 years), US fossil energy resources will run out and reduce per capita land area to only 0.17 ha of cropland and 0.3 ha of pasture land, both values below current global land availability.

There are several different conservation technologies that help control soil erosion, including: crop rotations, cover crops, contour planting, ridge till, mulch, terraces, grass strips, and no-till. Some investigators claim that no-till saves energy but this is usually only accounted for in tractor fuel reductions. These investigations seldom account for the added nitrogen, added corn seed, plus the added pesticides required in no-till production (Pimentel and Ali 1998; Williams et al. 2000; Parsch et al. 2001; Epplin et al. 2005).

In 100 years time, world population is projected to be more than twice as the number is today (6.5 billion)—about 13 billion. A World Health Organization report states that worldwide there are currently more than 3.7 billion malnourished humans, the largest number of malnourished people ever in the history of the Earth (WHO 2005). In light of this report, we should expect food shortage problems to continually worsen.

While the number of malnourished people increased worldwide over the past two decades, per capita grain production simultaneously declined (FAOSTAT 1961– 2005). There are many factors that contributed to this decline, including: a rapidly growing world population (PRB 2006), a 20% decline in cropland per capita in the last decade (Pimentel and Wilson 2004), a 10% decline in irrigated land per capita (Postel 1997) and a 17% decrease in per capita fertilizer use (Pimentel and Wilson 2004). It should be noted that cereal grains make up 80% of the world’s food supply.

Irrigation and Energy Provided there is ample of irrigation water, crop production can be increased significantly in arid regions. Approximately 80% of water used in the USA is solely for irrigation to increase crop production, particularly in arid regions (Pimentel et al. 2004). Plants consume about twothirds of this water while one-third is non-recoverable (Postel 1997). Irrigated corn requires about 14 million liters of water per hectare (500,000 gallons per acre) and uses about three times more energy than rain-fed corn to produce the same yield (Pimentel et al. 2004). Irrigation tends to be expensive both energetically and economically, costing more than $1,200 per hectare when pumping from a depth of only 100 m (Pimentel et al. 2004).

Reducing irrigation dependence in the USA would save significant amounts of energy, but probably require that crop production shift from the dry and arid western and southern regions to the more agriculturally suitable Midwest and Northeast. Also, as noted above, soil salinization due to irrigation causes the abandonment of ten million hectares each year worldwide (FAO 2006). The leaching of salts from the soil into rivers poses another major problem. For example, where the Colorado River flows through the Grand River Valley in Colorado, water returned to the river from irrigated cropland contains an estimated 18 t/ha of salts leached from the soil (EPA 1976), resulting in high salt concentrations in the river.

Conserving Essential Nutrients As fossil fuels become scarce, costs for the production of synthetic fertilizers will rise. This economic pressure will force farmers to seek alternative sources to meet their nitrogen, phosphorus, and potassium demands. Nitrogen is the most vital nutrient in agricultural production and is applied at a rate of 12 million tons of commercial or synthetic nitrogen per year in the USA (GAO 2003; USDA 2004). Although 18 million tons of nitrogen were applied in 1995 in the USA, a 300% increase in the price of nitrogen fertilizer over the past decade has resulted in fewer N applications, highlighting the need to explore alternative nutrient sources. It is of equal commercial importance to provide adequate amounts of phosphorus and potassium, the other essential macro-elements needed by plants to grow well and produce high yields. As will be shown below, leguminous cover crops, manure, and other organic inputs can meet the N, P, and K demands of food production in the USA (Funderberg 2001; Schmalshof 2005).

Cover Crops Conserving soil nutrients is a priority in agricultural production because it reduces the demand for fertilizers and produces high crop yields. A crucial aspect of soil nutrient conservation is the prevention of soil erosion. Cultivation practices that build soil organic matter (SOM) and prevent the exposure of bare soil are a key part of preventing soil erosion. Cover crops help protect the exposed soil from erosion after the main crop is harvested (Troeh et al. 2004). Compared with conventional farming systems, which traditionally leave the soil bare, the use of cover crops significantly reduces soil erosion. Leguminous cover crops also add nutrients to the soil (Drinkwater et al. 1998; Weinert et al. 2002). For example, vetch, a legume cover crop grown during the fall and spring months (non-growing season), can add about 70 kg/ha of nitrogen (Pimentel et al. 2005; Henao and Baanante 2006). Cover crops further aid in agriculture by collecting about 1.8 times more solar energy than conventional farming systems (Pimentel 2006b). Growing cover crops on land before and after a primary crop nearly doubles the amount of solar energy that is harvested per hectare per year. This increased solar energy capture provides extra organic matter which improves soil quality.

Soil Organic Matter Maintaining high levels of soil organic matter (SOM) is beneficial for all agriculture and crucial to improving soil quality. Carter (2002) has shown aggregated SOM to have “major implications for the functioning of soil in regulating air and water infiltration, conserving nutrients, and influencing soil permeability and erodibility” by improving the soil’s water infiltration, structure, and reducing erosion. Maintaining high levels of SOM is a primary focus of organic farming. On average, the amount of SOM is significantly higher in organic production systems than in conventional systems. Typical conventional farming systems with satisfactory soil generally have 3% to 4% SOM, whereas organic systems soil average from 5% to 5.5% SOM (Troeh et al. 2004). Soil carbon increased about 28% in organic animal systems and 15% in organic legume systems, but only 9% in conventional farming systems (Pimentel et al. 2005). This high level of SOM provides many advantages. Increased SOM also provides soil with an increased capacity to retain water. Sullivan (2002) reported that approximately 41% of the volume of organic matter in the organic systems consisted of water, compared with only 35% in conventional systems. The large amount of soil organic matter and water present in organic systems is the major factor in making these systems more drought resistant. Furthermore, 110,000 kg/ha of soil organic matter in an organic corn system could sequester 190,000 kg/ha of carbon dioxide. This is 67,000 kg/ha more carbon dioxide sequestered than in conventional corn systems, and equals the amount of carbon dioxide emitted by ten cars that averaged 20 miles per gallon and traveled 12,000 miles per year (USCB 2004–2005). The added carbon sequestration benefits of organic systems clearly have beneficial implications for reducing global warming.

Manure In 2005, the 100 million cattle, 60 million hogs, and nine billion chickens maintained in the USA produced an estimated 20.5 million metric tons of nitrogen. This nitrogen, most of which is produced by cattle, could potentially be used in crop production. The collection and management of this nitrogen requires special attention. Approximately 50% of the nitrogen is lost as ammonia within 24 to 48 h after defecation, if the animal waste is not immediately buried in the soil or placed in a lagoon under anaerobic conditions (Troeh et al. 2004). The liquid nutrient material in the lagoon must be buried in the soil immediately after it is applied to the land, or again the nitrogen will be lost to the atmosphere. We estimate 70% of cattle manure is dropped in pasture or rangeland and is not included in the total nitrogen estimate, reducing the amount of nitrogen theoretically collected for use per year to 18 million metric tons (Pimentel et al., unpublished data). Because cow manure is 80% water, this manure can only be transported a distance of about eight miles before the energy return is negative. Conserving nutrients will be crucial to farmers in a world of high fertilizer costs. In addition, practices that center on building and conserving soil integrity can greatly improve energy efficiency in food production systems. The use of manure, cover crops, composting, and conservation tillage can contribute to such energy reductions and allow farmers to produce food sustainably.

Reducing energy use in the farm system

Reduced Pesticide Use Currently, more than one billion pounds of pesticides are applied annually to US agriculture (USDA 2004). Certified organic farming systems do not apply synthetic pesticides. Weed control is, instead, achieved through crop rotations, cover crops, and mechanical cultivation (Pimentel et al. 2005). Avoiding the use of herbicides and insecticides improves energy efficiency in corn/soybean production systems. For example, in organic farming, one pass of a cultivator and one pass of a rotary hoe use approximately 300,000 kcal/ha of fossil energy. Herbicide weed control (including 6.2 kg of herbicide per hectare plus sprayer application) requires about 720,000 kcal/ha or about twice the amount of energy used for mechanical weed control in organic farming (Pimentel et al. 2005). In addition, there are a reported 300,000 non-fatal pesticide poisonings (EPA 1992) per year in the USA, and pesticides in the diet have been shown to increase the odds of developing cancer (Horrigan et al. 2002).

Moving Livestock Back to the Grain Farms Another factor in energy usage in farming is the recent proliferation of monocultures, or farms devoting large tracts of land to one crop. The movement of livestock frommixed farming systems was encouraged by the US Government as it began to provide price supports for farmers (NAS 1989). As a result, livestock were moved to concentrated animal feeding operations (CAFOs) where they could be raised in large numbers. This shift resulted in an increase in commercial fertilizer and pesticide use in crop production, plus a significant increase in soil erosion (NAS 1989). It has also raised concern that 76 million hospital cases and 5,000 human deaths may be attributable to pollution associated with CAFOs and poor waste management (CDC 2002).

Crop Rotations Crop rotations are beneficial to all agricultural production systems because they help control soil erosion (Troeh et al. 2004; Delgado et al. 2005). They also help control pests such as insects, plant pathogens and weeds (Pimentel et al. 1993; Troeh et al. 2004). In addition, when legume cover crops are used, essential nitrogen is added to the soil when they are plowed under. As mentioned above, in the Rodale study soil nitrogen levels in organic farming systems were 43% compared with only 17% in conventional systems (Pimentel et al. 2005). Regulatory actions and market-based incentives could encourage the movement of livestock manure away from pollution causing CAFOs and back to the mixed farms where it can be incorporated into the soil. They could also encourage the agricultural practice of crop rotation, the use of cover crops, and reduced pesticide applications, all of which would result in increased energy savings and reduced hazards to human health.

Labor and Mechanization

Raising corn and most other crops by hand requires about 1,200 h of labor per hectare (nearly 500 h per acre; Feeding the World 2002). Modern mechanization allows farmers to raise a hectare of corn with a time input of only 11 h, or 110 times less than required for hand-produced crops (Pimentel et al. 2007). Mechanization requires significant energy for both the production and repair of machinery (about 333,000 kcal/ha) and diesel and gasoline fuel (1.4 million kcal/ha; Table 4). About one-third of the energy required to produce a hectare of crops is invested in machine operation (Pimentel and Patzek 2005). Mechanization decreases labor significantly, but does not contribute to increased crop yields. Organic corn production requires mechanization. Economies of scale are still possible with more labor and the use of smaller tractors and other implements. Reports suggest that equipment quantity and size is often in excess of requirements for the tasks. Reducing the number and size of tractors will help increase efficiency and conserve energy (Grisso and Pitman 2001).

Return to Horses and Mules

A horse can contribute to the management of 10 ha (25 acres) per year (Morrison 1946). Each horse requires one acre of pasture and about 225 kg of corn grain. Another 1.5 acres of hayland is necessary to produce the roughly 800 lbs of hay needed to sustain each animal. In addition to the manpower required to care for the horses, labor is required to drive the horses during tilling and other farm operations. The farm labor required per hectare would probably increase from 11 hours to between 30 and 40 h per hectare using draft animal power. Nevertheless, an increase in human and animal labor as well as a decrease in fuel-powered machinery is necessary to decrease fossil fuel use in the US food system.

Energy Inputs in Meat, Poultry and Dairy Production

Each year an estimated 45 million tons of plant protein are fed to US livestock producing approximately 7.5 million tons of animal protein (meat, milk, and eggs) for human consumption (Pimentel 2004). The livestock feed is comprised of about 28 million tons of plant protein from grains and 17 million tons from forage. In the USA, the average protein yield of the five major grains (corn, rice, wheat, sorghum, and barley, plus soybeans) fed to livestock is about 700 kg/ha. For every kilogram of high quality animal protein produced, livestock are fed nearly 6 kg of plant protein (Pimentel 2004). Major differences exist in the inputs of feed and forage between animal products. For example, production of 1 kg of beef requires 13 kg of grain and 30 kg of forage (fossil energy input 40 kcal per 1 kcal beef protein), 1 kg of pork requires 5.9 kg of grain (14:1 kcal), and 1 kg of broiler chicken requires only 2.3 kg of grain (4:1 kcal). A kilogram of conventional milk produced in the USA requires 0.7 kg of grain and 1 kg of hay (14:1 kcal; Pimentel 2006b). In Norway, organic milk production was reported to be 43% more energy efficient (Refsgaar et al. 1998), since the cattle were grazed on pasture land.

When converting plant protein into animal protein, there are two principal categories of energy and economic costs:
(1) the direct production costs of the harvested animal including the grain and forage fed; and (2) the indirect costs of maintaining the breeding herd. Diverse combinations of grains, forages, and legumes (including soybeans) are fed to livestock to produce meat, milk, and eggs. The major fossil energy inputs required to produce grain and forage for animals includes fertilizers, farm machinery, fuel, irrigation, and pesticides. The energy inputs vary according to the particular grain or forage being grown and fed to livestock. On average producing one kcal of plant protein for livestock feed requires about 10 kcal of fossil energy (Pimentel 2004). Of the livestock systems evaluated, broiler-chicken production is the most energy efficient, with 1 kcal of broiler protein produced with an input of 4 kcal of fossil energy (Pimentel 2006b). Broilers are a grain-only livestock system. Turkey production is also a grain-only system and is next in efficiency with a 1:10 ratio. In addition, conventional milk production, based on a mixture of grain and forage feed, is also relatively efficient, with 1 kcal of milk protein requiring 14 kcal of fossil energy (Pimentel 2006b). Nearly all the feed protein consumed by broilers is from grain, while milk production uses about two-thirds grain and one-third forage. Of course, 100% of milk production could be achieved using hay and/or pasture as feed.

Food Processing and Packaging

In the USA, processed foods account for 82% to 92% of food sales (Murray 2005; Putman et al. 2002; SixWise 2006). Of the energy used for the total food system, 16% is used in processing and 7% is used in packaging.  [Pimentel then has a long list of how to use less energy]

Transport of Food

In the US food travels an average of 2,400 km (1,500 miles) before it is consumed, a practice which is obviously energy intensive.  A very energy intensive part of the American diet is the large quantity of fruits and vegetables that are transported by aircraft. The amount of energy required to ship 1 kg of food by aircraft is 6.63 kcal/km. On the other hand, shipping by rail is only 0.12 kcal/kg/km (Pimentel 1980).

Conclusion and References: see the original paper

 

 

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Energy in Food System. March 2010. USDA

Canning, P. 2010. Energy Use in the U.S. Food System.  USDA Economic Research Report Number 94

Another great review of this article is Beyond Food Miles by Michael Bomford, a research scientist and extension specialist at Kentucky State University, an adjunct faculty member in the University of Kentucky Department of Horticulture

Food system energy USDA 2002

 

 

 

 

 

 

In 2007 the U.S. The United States economy used 100 quadrillion Btu of energy: 85% from fossil fuels, 8% nuclear fuel, 6% hydroelectric, 1% biomass, geothermal, solar, and wind.

Pimentel et al., 2008, “Reducing Energy Inputs in the US Food System,” Human Ecology 36., reported that food used 19% of the  national energy budget.  Other researchers come up with different figures, because calculating energy use is complicated.  This report concluded 14.4% [my summary below makes it clear why every report comes up with a different number, it’s an insanely complex system with so many components and variables to include or exclude, that no report will have the same figure].

Energy is used throughout the U.S. food supply chain, from the manufacture and application of agricultural inputs, such as fertilizers and irrigation; through crop and livestock production, processing, and packaging; distribution services, such as shipping and cold storage; the running of refrigeration, preparation, and disposal equipment in food retailing and food service establishments; and in home kitchens.

In addition, life cycle analyses were also done on the energy

  • imported food (energy used by ships, barges, trains, trucks, fertilizers, etc)
  • municipal waste disposal
  • Water required: sewage systems and water services

The energy used to EXPORT food was NOT CONSIDERED IN THIS STUDY.

Energy used in a salad mix bought on the East Coast grown in California

The lettuce mix is just one of the 45,000 items sold in 140,000 supermarkets and 537,000 food and beverage service establishments in the USA in 2007. nationwide.  Each of these purchased,
stored, prepared, cleaned, and disposed of food items.

  1. The farm California used a precision seed planter months before attached to a gas-powered farm tractor.
  2. Fertilizers and pesticides were trucked to wholesalers by diesel powered trucks.
  3. Local farmers drove in gas-fueled trucks to buy these fertilizers and pesticides.
  4. A diesel-powered broadcast spreader applied fertilizers, pesticides, and herbicides to the lettuce
  5. These nitrogen-based fertilizers, pesticides, and herbicides, were all made with natural gas and electricity
  6. The farms used electric-powered irrigation equipment throughout much of the growing period
  7. At harvest, field workers packed harvested vegetables in boxes produced at a paper mill
  8. The boxes were in gas-powered trucks to ship to a regional processing plant, where specialized machinery cleaned, cut, mixed, and packaged the salad mixes.
  9. Utility services at the paper mill, plastic packaging manufacturers, and salad mix plants use energy to produce the boxes used at harvest and the packaging used at the processing plant, and for processing and packaging the fresh produce.
  10. The packaged salad mix was shipped in refrigerated containers by a combination of rail and truck to an East Coast grocery store
  11. The grocery store kept the lettuce under constant refrigeration.
  12. To purchase this packaged salad mix, a consumer probably got there by car or mass transit.
  13. At home, the consumer refrigerated the salad mix a while before eating it.
  14. Dishes and utensils used to eat the salad may be placed in a dishwasher for cleaning and reuse—adding to the electricity use of the consumer’s household.
  15. Leftover salad may be ground in a garbage disposal and washed away to a wastewater treatment facility, or disposed, collected, and hauled to a landfill

Household measurements

26.7%: Electricity for cooking, cleaning, and food storage, 6.6% cooking (i.e. electric range, oven, microwave, toaster oven, and coffee makers), 14% refrigeration,  3.6 freezers; 2.5% dishwashers,

3% (in 2001) Cooking heat other than electricity (natural gas and liquid petroleum gas (LPG)

2% roughly Auto fuel for food-related personal transportation

Embodied energy in purchases of food storage, preparation, and serving equipment

Part of the embodied energy in purchases of automobiles, parts, and auto services (insurance and accessories were not included)

Table 5: Freight industry 

Average miles 2007    Commodity

  • 374 Fresh produce, oilseeds, and other horticulture
  • 243 Meat, fish, and preparations
  • 262 Milled grain products and preparations, and bakery products
  • 230 Other prepared foodstuffs and fats and oils

Freight mode:
BTU’s 2007 Energy use by freight mode

23,260    Energy use per truck mile
14,990    Energy use per freight car rail mile
Sources: USDA, Economic Research Service using data from the U.S. Department of
Transportation (www.bts.gov), and U.S. Department of Energy (http://cta.ornl.gov/cta/).

Agriculture mechanization grew 10%, labor declined 30% between 1996 – 2006

With farm machinery use on the rise and use of agricultural chemicals roughly constant, energy services for the production of farm inputs may have increased steadily over the past decade.

References

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Cutler, D.M., E.L. Glaeser, and J.M. Shaprio. 2003. “Why Have Americans Become More Obese?” Journal of Economic Perspectives 17, No. 3: pp. 93-118.
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Pimentel, D., S. Williamson, C. Alexander, O. Gonzalez-Pagan, C. Kontak, and S. Mulkey. 2008. “Reducing Energy Inputs in the US Food System,” Human Ecology 36, pp. 459-471.

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Posted in Agriculture Infrastructure | Comments Off on Energy in Food System. March 2010. USDA

Articles about the Stages of Collapse

Complexity, Problem Solving, and Sustainable Societies

1996. Joseph A. Tainter

from GETTING DOWN TO EARTH: Practical Applications of Ecological Economics, Island Press, 1996; ISBN 1-55963-503-7 http://www.amazon.com/exec/obidos/ASIN/1559635037

OVERVIEW   Historical knowledge is essential to practical applications of ecological economics. Systems of problem solving develop greater complexity and higher costs over long periods. In time such systems either require increasing energy subsidies or they collapse. Diminishing returns to complexity in problem solving limited the abilities of earlier societies to respond sustainably to challenges, and will shape contemporary responses to global change. To confront this dilemma we must understand both the role of energy in sustaining problem solving, and our historical position in systems of increasing complexity.

INTRODUCTION In our quest to understand sustainability we have rushed to comprehend such factors as energy transformations, biophysical constraints, and environmental deterioration, as well as the human characteristics that drive production and consumption, and the assumptions of neoclassical economics. As our knowledge of these matters increases, practical applications of ecological economics are emerging. Yet amidst these advances something important is missing. Any human problem is but a moment of reaction to prior events and processes. Historical patterns develop over generations or even centuries. Rarely will the experience of a lifetime disclose fully the origin of an event or a process. Employment levels in natural resource production, for example, may respond to a capital investment cycle with a lag time of several decades (Watt 1992). The factors that cause societies to collapse take centuries to develop (Tainter 1988). To design policies for today and the future we need to understand social and economic processes at all temporal scales, and comprehend where we are in historical patterns. Historical knowledge is essential to sustainability (Tainter 1995a). No program to enhance sustainability can be considered practical if it does not incorporate such fundamental knowledge.

In this era of global environmental change we face what may be humanity’s greatest crisis. The cluster of transformations labeled global change dwarfs all previous experiences in its speed. in the geographical scale of its consequences, and in the numbers of people who will be affected (Norgaard 1994). Yet many times past human populations faced extraordinary challenges, and the difference between their problems and ours is only one of degree. One might expect that in a rational, problem-solving society, we would eagerly seek to understand historical experiences. In actuality, our approaches to education and our impatience for innovation have made us averse to historical knowledge (Tainter 1995a). In ignorance, policy makers tend to look for the causes of events only in the recent past (Watt 1992). As a result, while we have a greater opportunity than the people of any previous era to understand the long-term reasons for our problems, that opportunity is largely ignored. Not only do we not know where we are in history, most of our citizens and policy makers are not aware that we ought to.

A recurring constraint faced by previous societies has been complexity in problem solving. It is a constraint that is usually unrecognized in contemporary economic analyses. For the past 12,000 years human societies have seemed almost inexorably to grow more complex. For the most part this has been successful: complexity confers advantages, and one of the reasons for our success as a species has been our ability to ‘Increase rapidly the complexity of our behavior (Tainter 1992, 1995b). Yet complexity can also be detrimental to sustainability. Since our approach to resolving our problems has been to develop the most complex society and economy of human history, it is important to understand how previous societies fared when they pursued analogous strategies. In this chapter I will discuss the factors that caused previous societies to collapse, the economics of complexity in problem solving, and some implications of historical patterns for our efforts at problem solving today. This discussion indicates that part of our response to global change must be to understand the long-term evolution of problem-solving systems.

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Tainter’s law: where is the physics?

March 27, 2011. Ugo Bardi.  cassandralegacy.blogspot.com

Joseph Tainter has written a fascinating interpretation of the collapse of human civilisations in his book “The Collapse of Complex Societies” (1988) (see also his 1996 paper) Collapse is a common event: it is the stuff history books are made of. The mighty empires of the past; from Sumeria to the Soviet Union, have all collapsed at some point. Yet, we don’t seem to be able to understand the reasons why collapse is so common.

In his book, Tainter examines previous studies and lists at least eleven causes (or “concauses”) of collapse that have been proposed by historians. Resource depletion, catastrophes, intruders, social conflict, and others. But is there a single cause of collapse? Or are there several? Tainter looks for a single, common root of the problem and finds it in what he calls “the decreasing returns of complexity”.

Bardi proposes a model that can be viewed here: “Physics of Collapse

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