What does it actually cost to throw away the future? For a retired solar panel in the United States, the answer is surprisingly small, and that small number is deciding where the panel ends up.

The National Renewable Energy Laboratory (NREL) estimates it costs roughly $1 to $5 to landfill a silicon module and $15 to $45 to recycle one. Faced with that spread, most panel owners do the obvious thing. Fewer than 10% of decommissioned US panels are recycled.

That gap is worth naming, because it isn’t really about whether recycling is possible. It plainly is. The gap is about who pays, and when, and that turns out to be a very different kind of problem.

Why the cheap option keeps winning

A solar panel is not a mysterious object. Roughly 75% of a crystalline silicon panel by weight is glass, with an aluminum frame, a junction box, silicon cells, and small amounts of copper and silver threaded through it. The trouble is that the parts worth money are the parts hardest to get at, and the part that’s easy to handle, the glass, is worth almost nothing on its own.

So the economics run backwards from what you’d hope. NREL’s own behavioral modeling of US modules through 2050 found that, under baseline conditions, about 80% end up landfilled, 1% reused, and 10% recycled. Landfilling wins not because anyone prefers it, but because it’s the option that clears at the lowest price on the day the panel comes down.

Contrast that with the European Union, where producer-responsibility mandates fold the cost of end-of-life handling into the product from the start. Under those rules, recycling a panel has been put at about $0.75 per panel, and EU recycling rates reach 95%. Same physics, same materials, wildly different outcome. The variable is policy, not chemistry.

What actually costs money when you take a panel apart

Pulling the aluminum frame and the junction box off a panel is straightforward. The expensive step is what comes after: cleanly separating the glass from the silicon cells, then extracting the tiny quantities of silver and copper that sit inside. Those metals are where the recoverable value lives, and they are present in vanishingly small amounts. Silver sits at well under a tenth of a percent of a panel’s weight, yet it drives the recycling math.

Because clean separation is hard, many operations skip it. They shred the whole panel and sell the low-value glass cullet, capturing a fraction of what’s there. And the prize for doing the harder work isn’t large: an electrical engineer writing in The Conversation estimates the recoverable silver and copper in a single panel are worth only about $10 to $12, which is why recycling loses money under current processes. Layers glued together make the glass reclamation harder still.

The field’s own practitioners have been candid about the limits. As of 2022, Arizona State University’s Meng Tao, who works on PV recycling, told Chemical & Engineering News that “The recycling technologies we have today are still rudimentary.” That was an assessment of a young field, and the field has moved since. The same Conversation piece notes that advanced methods like salt etching can now recover over 99% of silver and 98% of silicon at high purity. The capability is arriving. Whether the economics arrive with it is the open question.

The Georgia plant’s bet

Which brings us to Cedartown. On January 29, 2026, SOLARCYCLE began commercial operations at a 255,000-square-foot plant that the company says recovers 96% of a panel’s material value and achieves 100% landfill diversion. According to CEO Suvi Sharma, the ” recycling facility in Cedartown represents a step-change in how we’re delivering end-of-life infrastructure.”

The more interesting move, to our eye, is what’s planned next door. SOLARCYCLE intends to feed the recovered glass into an adjacent solar-glass factory, with more than 80% of that plant’s planned 5 GW capacity already committed and first glass production slated for 2028. That vertical integration matters because it changes the value of the least-valuable material. If the glass has a buyer waiting rather than a landfill, the whole equation shifts. Sharma frames the ambition plainly: “The next phase of our growth is all about bringing solar recycling to industrial scale and delivering winning economics for our customers.” That’s a stated aim, not a demonstrated result, but it names the actual barrier: scale.

Not everyone is sold on the crush-and-separate approach. Terry Ko, chief operating officer of PV Circonomy, whose company markets a layer-by-layer alternative, has argued that “Once glass, silicon, metals, and polymers are reduced into mixed particles, contamination becomes a significant challenge regardless of the subsequent separation technology employed.” Ko has a commercial stake in that critique, and the trade coverage it appeared in noted the absence of industry-wide purity standards. Worth hearing, not yet settled.

The retirement wave that’s already loading

All of this would be an academic argument if the panels weren’t coming. They are.

NREL’s Garvin Heath put the timing plainly: “Installations two decades ago are nearing their end of life, and that becomes a challenge for the waste industry.” Roughly one million tons of US panel waste is expected by 2030, and NREL’s global assessment projects the volume of retired modules could reach up to 80 million metric tons by 2050. That’s a forecast, not a certainty, but the trend line under it is firm: US utility-scale solar is set to add 70 GW of new solar capacity across 2026 and 2027. Every panel installed is a panel that will one day retire.

There’s also a supply-chain angle that reframes the whole thing. Several of the metals inside panels appear on US critical-minerals lists and are largely imported. Recovered silver, copper, and silicon are not just waste avoided; they’re domestic material that didn’t have to be dug up or shipped in. Heath’s argument is that the lead time here is long, so the work has to start early: “Because it takes a long time to develop technology and policy and solutions to dealing with end-of-life products, this is something we need to start to address today.”

Incentive, not inevitability

The technology to recover most of a panel exists, salt etching hits high-purity numbers, and a plant in Georgia is now claiming near-total value recovery. What keeps most panels in the ground is that landfilling is cheap on the day the decision gets made, and the cost of recycling lands on whoever is holding the panel at end of life rather than on whoever profited from it at the start.

The EU’s $0.75-per-panel figure is the tell. When the cost is built in early and the value chain is closed, the same object that looks like expensive waste in one system looks like feedstock in another. Cedartown’s bet on selling its recovered glass next door is a private-sector version of the same logic: make the low-value material worth something, and the math stops fighting you.

The $1-to-$5 number isn’t telling us that recycling is too hard. It’s telling us who currently pays for the easy way out. Change that, through mandates, through scale, or through a buyer waiting on the other side of the shredder, and the cheap option stops being the only rational one.

The post Dropping a dead solar panel into a U.S. landfill costs $1 to $5, while recycling the same panel has been estimated at $15 to $45. That gap helps explain why most go into the ground, even though a plant that opened in Georgia this year says it recovers 96 percent of a panel’s material value. appeared first on Space Daily.

Bar soap moved a lighthouse. Crews smeared ordinary Ivory soap along the steel beams the tower rode across, because it turned out to be the ideal lubricant for a job involving thousands of tons of creeping brick, a detail recorded at the time by the Lighthouse Directory.

Everything else about the job was considerably less homely.

Why a lighthouse ends up in the surf

When Cape Hatteras Lighthouse was finished in 1870, it stood a comfortable 1,500 feet from the Atlantic. Then Hatteras Island did what barrier islands do, which is travel. Storm tides strip sand off the ocean side and dump it on the sound side, and the whole island shuffles westward, a process the National Park Service traces back at least 10,000 years.

The island moved. The lighthouse stayed exactly where the builders left it.

Underneath sat yellow pine timbers resting in fresh water on compacted sand, a floating foundation improvised because pilings could not be driven through hard sand barely eight feet down. Ingenious for 1870, and considerably less reassuring once the surf reached the door. By the late 1990s the ocean had closed to within 60 feet of the base, per the park service’s account of the light station, and decades of groins and sandbags had mostly made the erosion worse.

How to move five thousand tons of brick

Very slowly, and with an enormous amount of hydraulics.

Crews cut the tower free of its foundation, all 4,830 tons of it by the park service’s own retrospective, and replaced it with a grid of seven main beams, each 70 feet long and weighing 11 tons, fitted with 100 hydraulic jacks, as documented by Island Free Press. Those jacks raised the lighthouse 5.34 feet, just enough to slide roll beams underneath and give it a road. Horizontal push jacks then nudged the tower forward about five feet, backed off, shifted position along the beams, and pushed again, a sequence the park service sets out in its move FAQs. Each shove took about a minute, in coverage by the National Parks Conservation Association, and beams the tower had already passed over were carried round to the front to extend the track.

Progress ran to roughly 100 feet a day, with crowds cheering pushes that were barely visible to the naked eye, as Our State magazine later described the scene.

Twenty-three days, 2,900 feet, $11.8 million, and one American Society of Civil Engineers award the following year. International Chimney Corp of Buffalo held the contract. Expert House Movers of Maryland did the shoving.

The argument that came first

None of this was settled quietly. Relocation had been on the table since the National Academy of Sciences recommended it in the late 1980s, and North Carolina State University reached the same conclusion in a review published in January 1997, as Coastal Review later recounted, but plenty of locals were convinced the tower would shake itself to rubble halfway down the track. Congress funded the move anyway in 1998. The lawsuit that followed now sits in an administrative record held by the State Archives of North Carolina, a tidy paper monument to a very loud argument.

What the ocean has done since

The tower now stands about 1,500 feet from the water, the same margin it enjoyed in 1870, and should not be threatened again for something like a century, according to the State Library of North Carolina’s history project on the relocation.

Nearby property has fared worse. At least 32 privately owned beach homes have collapsed onto Cape Hatteras National Seashore since 2020, most of them at Rodanthe and Buxton, with the latest counted by National Parks Traveler in June. Each one brings a notice from Cape Hatteras National Seashore warning visitors about nail-studded debris drifting for miles down the beach. Superintendent David Hallac has pointed out that earlier generations built smaller and shifted buildings when the surf came for them, which is a polite way of saying the island never agreed to stay still.

Cracks the sea did not cause

Scaffolding went up in 2024 for what was meant to be an 18-month restoration costing $19.2 million, and the work has turned up something awkward. Crews expected 30 to 40 cracks in the cast-iron brackets carrying the gallery deck near the top. They found 116, spread across all 16 brackets, Stone & Lime superintendent Josh Brundige told a media tour in July, in reporting by Outer Banks Insider. Most were hidden under seven layers of brick, and the documentation of them predates the 1999 move.

Nobody can say what caused the cracking. Brundige offered thermal expansion and water damage as candidates, with generations of whale oil flame heating the lantern room and winter cooling it down again.

So the lantern room is currently missing from the tower altogether, a temporary beacon is doing the work, and the repair has added about a year and $10 million, taking the project to roughly $30 million. Moving a lighthouse five feet at a time was, in the end, the easy part. Whatever quietly split the ironwork at the gallery deck was already there, decades before anyone thought to look.

The post When Cape Hatteras Lighthouse was built in 1870, the Atlantic sat about 1,500 feet away, but by 1999 the ocean had crept to within 60 feet — engineers lifted the entire lighthouse and moved it 2,900 feet inland, five feet at a time appeared first on Space Daily.

Concrete is the second most-used substance on Earth after water, and the cement that holds it together is one of the biggest headaches in climate policy.

Making cement means heating limestone until it breaks down, a process that accounts for around 8 percent of global CO2 emissions. And we are not slowing down. Concrete production is projected to climb from roughly 14 billion cubic metres a year toward 20 billion by mid-century. So anything that lets you use less cement per wall, without the wall getting weaker, is worth a close look.

That is the claim in a new paper out of India, and it comes with an unusual ingredient: human waste. A team turned treated sewage sludge into a fine black powder, swapped it in for a tenth of the cement, and got concrete that ended up harder to crush, not softer.

It’s one study, and an early-access version still subject to edits, so treat what follows as a promising result, not a settled fact.

Why cement is the part worth fixing

The problem with concrete is not the gravel or the sand or the water. It is the cement paste that binds them together. Estimates of cement’s climate footprint vary a bit depending on how you count, landing somewhere between 5 and 8 percent of global human-caused CO2 emissions each year. Most of that comes from the chemistry of making cement, not the fuel in the furnace. That is why switching to cleaner energy alone will not fix it.

One line of research has spent years asking whether you can replace some of that cement with biochar. Biochar is a carbon-rich char made by heating organic matter with very little oxygen. The appeal is twofold: you use less cement, and the carbon in the char, which the original plant or waste pulled out of the air, gets locked inside the building instead of released. The open question has always been whether the concrete survives the swap.

What the Warangal team actually did

The material here started at a sewage-sludge treatment plant in Warangal, in the Indian state of Telangana, a facility set up as a public-private partnership to tackle the city’s sewage problem. Human solid waste that would otherwise be dumped or burned gets processed there.

V Srinivas Chary, whose institution is a partner on the project, praised the operation, saying that “From the toilet to the final conversion of the biochar, the process is scientific and comprehensive.” 

The research team, led by civil engineer Raghuvesh Tiwari of Manipal University Jaipur with colleagues at Louisiana Tech University, took that sludge, dried it, and heated it to between 350 and 450 degrees Celsius with very little oxygen. That heating step drives off gases and leaves char behind. They ground the char into a powder, then replaced 5, 10, and 15 percent of the cement in test concrete with it and ran the usual checks: how well it resisted crushing and bending, how much it shrank, how much water it soaked up, how many gaps it had inside.

Dumped waste versus a carbon sink in the wall

The study sets up a pointed contrast. Normally a city’s sewage sludge is a liability to be disposed of, and a builder’s cement is a material whose production loads the atmosphere. Both are problems flowing toward waste and emissions. The first is bigger than you might think: a single person produces up to around 400 grams of faeces a day, which across a city becomes a constant stream that has to go somewhere.

The idea here is to route that stream into the wall. The waste replaces some of the cement, and the carbon in the char stays put instead of being burned off. It is a tidy story on paper: two problems that might cancel out a slice of each other. The caveat is that this study did not actually measure the carbon side of that ledger, so the climate benefit is still an argument rather than a number the paper delivered.

Why it got stronger, not weaker

The surprise is that adding a char to concrete made it tougher. The study reports this clearly for the middle dose. As the authors put it, “After a 91-day curing period, concrete with a 10% biochar substitution demonstrated a 21% increase in compressive strength and a 42% increase in flexural strength.” The 5 percent mix was close behind, gaining about 20 percent in crushing strength and 36 percent in bending strength over the same period. Those gains are measured against this study’s own plain concrete, not a universal benchmark.

There is a limit, though, and the study found it. The 15 percent mix did worse. Past a certain point, the char stops helping and simply dilutes the cement, a useful reminder that the good result here depends on getting the dose right. The authors’ own summary is careful: the results indicate that biochar at the 5 and 10 percent levels “yields significant improvements in concrete properties.”

The catch, and what still has to be proven

A strong lab result is not a paving slab. Several things stand between this and a real building site, and the paper is upfront about the biggest one. Sewage sludge can carry heavy metals, and whether those slowly leak out of the finished concrete over time is an open question. That is not something you can wave away when the material might end up in a school foundation or a water channel.

How long it lasts is the other unknown. The tests ran to 91 days in controlled conditions. Real structures face decades of freezing and thawing, wetting and drying, weight and vibration, and nobody has shown yet how this concrete holds up over that span. The researchers say themselves that more work is needed to assess how it performs under real-world conditions such as freeze-thaw cycles and extreme temperatures. 

What the study earns, we think, is attention rather than adoption. The explanation is plausible, the numbers are real for the mix that was tested, and the idea that a waste stream and a carbon-heavy material might each solve part of the other’s problem is worth chasing. 

The post Researchers took biochar made from human waste at a treatment plant in Warangal, India, ground it into a fine black powder and mixed it into concrete in place of a tenth of the cement. After 91 days the concrete was 21 percent harder to crush. appeared first on Space Daily.