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Synced Carbon Cycles

Choosing a Carbon Sync Without a Crystal Ball – What Tidal Pools Already Know About Rhythm

You don't need a crystal ball to pick a carbon sync. You need to watch a tidal pool. Tidal pools don't predict the next wave. They sync with it. Rise, hold, release. That rhythm—not prediction—is what makes a carbon sync work. Whether you're a farmer, a startup, or a policy wonk, you're chasing a method that holds carbon long enough to matter. Soil sequestration? Biochar? Direct air capture? Enhanced weathering? Each has its own beat. The trick is matching your rhythm to the carbon cycle's, not fighting it. Who Has to Choose? And What's the Real Deadline? Decision makers: farmers, landowners, project developers, corporations If you're reading this, you're probably carrying a title that sounds responsible but feels heavy. Maybe you manage a few thousand acres of row crops. Maybe you're a sustainability officer whose board just discovered the word 'insetting' and now expects a plan by Q2.

You don't need a crystal ball to pick a carbon sync. You need to watch a tidal pool.

Tidal pools don't predict the next wave. They sync with it. Rise, hold, release. That rhythm—not prediction—is what makes a carbon sync work. Whether you're a farmer, a startup, or a policy wonk, you're chasing a method that holds carbon long enough to matter. Soil sequestration? Biochar? Direct air capture? Enhanced weathering? Each has its own beat. The trick is matching your rhythm to the carbon cycle's, not fighting it.

Who Has to Choose? And What's the Real Deadline?

Decision makers: farmers, landowners, project developers, corporations

If you're reading this, you're probably carrying a title that sounds responsible but feels heavy. Maybe you manage a few thousand acres of row crops. Maybe you're a sustainability officer whose board just discovered the word 'insetting' and now expects a plan by Q2. Or you're a project developer brokering carbon credits between people who trust soil and people who trust spreadsheets. The list is short. The list is also everyone who touches land with a commercial or ecological stake. Farmers who rotate cattle through cover crops. Land trusts sitting on marginal pasture. Developers who smell a new revenue stream in biochar. Even corporate buyers who'll never touch dirt but must prove their supply chain is shrinking—fast. That's you. And that's the problem: too many hats, one clock.

The tricky bit is that each decision-maker faces a different kind of pressure. The farmer worries about yield penalties in year one. The corporate buyer worries about optics if credits are accused of 'double counting.' The developer chases a methodology that passes validation without bankrupting the budget. I have seen a well-intentioned landowner choose a fast microbial-pulse method because it promised quick numbers—only to discover that the credits expired before the buyer's audit cycle. That hurts. So let's be blunt: your role determines which metric you'll overvalue, and that overvaluation is the first mistake. A farmer who ignores soil biology for a cheaper lab test. A project lead who prioritises tonnage over durability because investors want volume. These aren't bad people. They're people under a deadline they don't fully understand.

The real deadline: before 2030 for meaningful climate impact

Here is the uncomfortable truth—the calendar that matters isn't your fiscal year. It's 2030. After that, the Intergovernmental Panel on Climate Change's budget curves flatten into something ugly: we either draw down carbon at industrial scale before then, or the atmospheric load becomes politically and economically unmanageable. That sounds like a headline. It's also a practical constraint. A carbon sync that takes five years to ramp up and another two to verify? You're eating half the decade before a single credit lands.

Most teams skip this: the carbon cycle doesn't care about your quarterly report. A tidal pool doesn't rush its algae bloom because a consultant needs a deliverable. The rhythms are biological—roots grow on their schedule, not yours. So the real deadline is not 'before the funding round closes' but 'before the window for deep, durable drawdown narrows to almost nothing.' I have watched developers choose a method that promised credits in eighteen months, only to realise the method required three full growing cycles to stabilise. Eighteen months turned into four years. The market moved on. That's the trade-off nobody puts in the slide deck: speed today can mean irrelevance tomorrow. Pick a sync that aligns with the planet's cadence, not the boardroom's. The boardroom can wait. The carbon cycle won't.

'We rushed into a contract for enhanced weathering because the price per tonne looked good—but the rocks hadn't even crushed yet.'

— project developer, after losing two seasons to logistics delays

What's on the Table? Four Approaches, No Hype

Soil sequestration — low cost, high co-benefits, but reversal risk

You plow less, plant cover crops, spread compost. The soil grabs CO₂. Cost? Often under $50 per ton sequestered. That's a fraction of what other methods charge. Farmers improve water retention, cut fertilizer bills, build drought resilience. It's the obvious first step for any landowner with acreage. The catch: nothing stays locked. A drought, a tillage pass, a shift in management — and that carbon re-enters the atmosphere within years. I have watched projects lose three seasons' gains in one dry summer. Monitoring, measurement, verification (MMV) eats into already thin margins. You're betting on human consistency over decades. That's a hard bet to hold.

The protocols exist — Verra, Climate Action Reserve, the new USDA models. But they argue over permanence windows. Nobody agrees on what "stored" means. Is it twenty years? Fifty? A hundred? The trade-off is clear: cheap entry, constant vigilance, no guarantee your grandkid sees the benefit.

Biochar — stable carbon, but feedstock and energy costs

Burn biomass without oxygen, get charcoal. Bury it. That carbon sits for centuries — recalcitrant, resistant, real. The numbers hold up: biochar retains 50–80% of the original biomass carbon, versus 3% from natural decomposition. Farmers who incorporate it see yield bumps in sandy soils. The hitch: production takes heat, takes wood waste or crop residue, takes capital. A small pyrolysis unit runs $50,000–$200,000. You need consistent feedstock — hauling, drying, grinding. Energy costs bite. I've seen a well-intentioned co-op burn through two years of grant money just to keep the kiln running.

There's a mismatch, too. Biochar works best in acidic, degraded soils. Apply it to healthy Midwest loam and you might see zero response. The carbon is locked, sure, but the co-benefits aren't automatic. You're buying permanence with energy and logistics overhead. That's a real trade, not a free lunch.

Direct air capture (DAC) — permanent storage, but staggering cost

Fans pull air through filters. Chemicals bind CO₂. Heat releases it for deep-well injection. The carbon stays gone — geological timescale, no reversal risk. That's the promise. The price tag: today, $600–$1,000 per ton. Maybe $200–$300 by 2030 if everything breaks right. "If." The energy demand is brutal — capturing a single ton requires roughly 2,000 kWh of heat plus electricity. That's a third of a US household's annual usage. For one ton.

Scalability remains theoretical. The largest operational plant, Climeworks' Mammoth in Iceland, captures 4,000 tons per year. Global emissions exceed 35 billion tons. Quick reality check — we'd need nine million Mammoth plants to offset annual output. Not yet. Not soon. The calculus works only for hard-to-abate sectors (aviation, cement) where avoidance isn't an option. For everyone else, DAC is the insurance policy you buy after the house is already burning.

Odd bit about practices: the dull step fails first.

Odd bit about practices: the dull step fails first.

Enhanced weathering — slow but durable, needs massive deployment

Spread crushed silicate rock on farmland or coastlines. Rain and weak acids dissolve the minerals, converting CO₂ into bicarbonate that washes to the ocean. Locked for tens of thousands of years. The mechanism is proven — nature's been doing it since before oxygen. The catch is pace. One ton of olivine might sequester 0.5–1 ton of CO₂, but it takes years to decades. You don't see results in a quarterly report.

The logistics dwarf everything else. We'd need to mine, grind, and spread billions of tons of rock annually. Compare that to the 5 billion tons of concrete produced each year — we're talking about doubling global mining output. The energy for grinding alone is non-trivial. And the side effects? Heavy metals in dust, altered soil pH, potential ocean chemistry shifts. Nobody has run this at scale. The upside — if we can solve the engineering — is near-permanent storage without the energy penalty of DAC. But it's a hedge, not a near-term fix. Most teams skip this because they can't finance a forty-year payoff.

'Every carbon sync is a time machine. The question is whether you're betting on years or centuries — and whether the planet can wait for your payout.'

— field operator, after watching three pilot projects stall on measurement costs

How to Compare Carbon Syncs Without Getting Fooled

Durability: how long does carbon stay locked?

Imagine stacking hay bales versus pouring concrete. That's the durability gap between methods. Some carbon syncs hold for decades—some for centuries. The trick is knowing which is which before you commit. A cover crop on no-till soil? That carbon can vanish within a season if the ground gets plowed. Biochar, by contrast, hangs around for hundreds of years. The catch: it costs more upfront and doesn't feed biology the same way living roots do. Quick reality check—don't ask "does it store carbon?" Ask "how long will it actually stay?" Most teams skip this. They lock in a method based on hype, then watch a drought or a land-use change undo years of work in months. That hurts. You want a sync that survives your own management mistakes.

Verifiability: can you measure it reliably?

You can't manage what you can't measure—but some things you can measure are dead wrong. Soil sampling? Accurate to a point, but lab results vary wildly between seasons, labs, and even core depths. A single wet year can bump your soil organic carbon numbers by a ton per hectare, making you look like a hero when nothing actually changed. The opposite happens in a dry year. I have seen project leads celebrate a 15% increase, only to lose it all the next season to a methodological tweak. What usually breaks first is the baseline. If you're comparing against a single snapshot, you're guessing. Better to run triplicate samples, same time of year, same protocol, for at least three years. That's boring. It's also the only way to tell signal from noise.

Cost per ton: what's the price tag?

Cheap credits are rarely cheap in the long run. A low-cost method like conservation tillage might run $5–15 per ton of CO₂. Sounds great—until you factor in permanence risk, verification gaps, and the chance the farmer switches practices after the contract ends. On the other end, enhanced rock weathering can hit $100–200 per ton. That's real money. The trade-off: you're paying for durability and verifiability that the cheap stuff can't touch. Most buyers grab the lowest price, then spend twice that later on reversals or reputation damage. Wrong order. Price the risk first, then the ton.

Co-benefits: does it help soil, water, biodiversity?

A carbon sync that hurts the land is not a solution—it's a one-way ticket to failure dressed in green.

— paraphrased from a soil scientist I worked with in the Midwest, after watching a monoculture bioenergy project strip out native prairie.

Not every method has co-benefits. Some are purely mechanical transfers of carbon from one pool to another—pure storage with no side effects. That's fine if your only goal is tons locked. But if you're farming, ranching, or managing a watershed, you need a sync that doesn't degrade what's already working. Cover cropping, silvopasture, and managed grazing build soil structure, retain water, and support insect life. Biochar improves water-holding capacity in sandy soils. Direct air capture? It stores carbon but does nothing for the land. That's a trade-off, not a dealbreaker—but know it going in. Pair a durable storage method with a regenerative soil practice, and you get both permanence and productivity. Don't let a single metric fool you into ignoring the system around it.

Trade-Offs at a Glance: A Table That Tells the Truth

Durability vs. Cost: Soil Is Cheap but Reversible; DAC Is Permanent but Expensive

I have watched teams fall in love with direct air capture because it promises 10,000-year storage. That's real—DAC shoves CO₂ into basalt or deep saline aquifers, and the carbon stays put for geological time. The catch? You'll pay $400–$600 per tonne today, maybe $200 in a decade if everything breaks right. Meanwhile, soil carbon syncs run $20–$80 per tonne. That's a tenth of the price. But here's the wound: soil carbon reverses. A drought, a tillage mistake, a land-use flip—and your tonnage disappears back into the atmosphere within three to five years. The trade-off isn't a preference. It's a risk profile. Do you need permanence? Or do you need volume now?

Most teams skip this: they pick the cheaper method first, then retroactively try to lock it in with insurance or buffer pools. That hurts. A buffer pool only covers catastrophic loss, not gradual seepage. You can't insure against a farmer retiring and selling to a developer.

“A tonne stored poorly is worse than never stored—it gives false credit while the planet keeps warming.”

— paraphrased from a carbon accountant I respect, after watching a reversal wipe out three years of credits

Verifiability vs. Co-Benefits: Biochar Is Easy to Measure but Less Soil Benefit

Biochar gives you a number you can bank on. The carbon is baked into fixed carbon rings—measure the feedstock mass, the pyrolysis yield, the lab-determined stability ratio, and you know tonnes stored within ±5%. No annual soil resampling, no hidden fungal collapse. The downside? Soil biology doesn't get the same feast. Pyrolyzed carbon is mostly recalcitrant; microbes can't eat it. You lose the nutrient cycling, the water-holding boost, the microbial priming that live soil provides. We fixed this on one project by co-composting biochar with manure before application—that revived the biology—but it added six weeks and 30% handling cost. You can measure your way to perfect credits and still starve the dirt.

Soil carbon, by contrast, gives you co-benefits—better infiltration, drought resilience, crop yield bumps—but verification is a swamp. One lab's test can disagree with another's by 40%. Satellite estimates drift. The same field can report a gain in spring and a loss in fall. That's not fraud; that's biology being noisy. You have to decide: do you want a certificate you can defend in court, or a field that actually functions?

Reality check: name the practices owner or stop.

Reality check: name the practices owner or stop.

Scalability vs. Speed: Enhanced Weathering Is Slow but Scalable; Soil Is Fast but Limited

Enhanced weathering spreads crushed basalt or olivine on croplands—the minerals react with rainwater and pull CO₂ out of the air. The scalability is breathtaking: there are enough basalt reserves globally to cover centuries of emissions. The problem is speed. Those reactions take years to complete. You apply today, but you can't claim full storage for maybe five years. Soil carbon moves faster—you can flip a field from conventional till to no-till and see measurable gains in one season. But the ceiling is low. Most mineral soils saturate after 10–20 tonnes per hectare, and then you plateau. That hurts if you're trying to hit million-tonne targets. So you pair them: fast soil gains to show early progress, slow weathering to build the long tail. The order matters—start with soil, layer weathering second. Get the rhythm backwards and you're paying for permanence you don't need yet.

You've Picked a Method. Now What? The Implementation Path

Step 1: Baseline assessment—measure your current carbon stock

You’ve picked your sync. Now stop. Don’t dig a single hole or plant a single seed until you know what’s already in the ground. A baseline isn’t paperwork—it’s your insurance against looking foolish later. Grab soil cores from multiple depths. Map your vegetation biomass. Measure that decay layer on top. I’ve watched teams skip this and then spend two years trying to prove gains they couldn’t separate from natural variation. That hurts.

The catch? Sampling is boring, expensive, and easy to cut corners on. Don’t. A weak baseline means every future measurement gets compared to a guess—and guesswork doesn’t sell credits. Hire a lab that knows the difference between Walkley-Black and dry combustion. Run triplicates. Archive extras. You’ll thank yourself when your auditor asks for proof. The rhythm of tidal pools is regular; your baseline is your first known beat.

Step 2: Choose a protocol (e.g., Verra, Gold Standard)

Wrong order: pick the protocol after the baseline, not before. Why? Because your data determines which methodology fits—not the other way around. Verra’s VM0042 demands certain sampling densities. Gold Standard’s Soil Organic Carbon Framework requires specific lab methods. If your baseline used the wrong test, you’re re-drilling. That’s months of lost time.

Most teams rush here because they want the shiny logo. Slow down. Read the methodology’s additionality rules—do you qualify? Check permanence requirements: some protocols demand 100-year commitments, others 30. That changes everything about your land-use agreements. Quick reality check—one landowner I worked with nearly signed a 50-year easement before realizing their protocol only needed 20. The seam blows out when lawyers miss these gaps.

One concrete tactic: map your protocol choices against your baseline’s natural variability. High variation? Pick a methodology with high sampling power, or you’ll never detect statistically significant change. Returns spike when the math actually works.

Step 3: Implement with monitoring, reporting, and verification (MRV)

Now you install. Not just management changes—the whole MRV machine has to run from day one. Monthly NDVI composites. Soil moisture logs. Biomass transects set to GPS pins you can find again. What usually breaks first is the reporting rhythm: teams collect data but forget to package it for the auditor’s format. Then they scramble three weeks before verification, pulling spreadsheets from email threads. That’s how small errors become expensive corrections.

The trick is to treat MRV as a product, not a chore. Build templates before you start. Automate sensor uploads. Train a single person to own the timeline, not a committee. One project I saw lost 40% of their soil sample tags in a single rainy season—someone used paper labels. Use QR codes. Seal in waterproof bags. The little stuff cascades.

‘A carbon sync without MRV is a promise without a receipt. Verification is what turns dirt into data that markets trust.’

— carbon project manager, after a failed audit

That quote stings because it’s true. Auditors don’t care about your intentions; they ask for the chain of custody on every sample. A single broken link means that whole batch of carbon doesn’t exist, market-wise.

Step 4: Sell credits or use for internal goals

You have verified numbers. Two paths: sell into voluntary markets, or retire credits against your own footprint. Each has different paperwork. Selling requires registry accounts (Verra’s, Gold Standard’s), serial numbers, and a broker or exchange. Internal use demands a credible retirement statement—don’t just claim it in a sustainability report; that invites scrutiny. Most companies who skip the retirement certificate get called out by NGOs.

A pitfall few anticipate: timing. Credits issued in January might not sell until November, depending on vintage demand and buyer preferences for nature-based vs. technological removals. If you need cash flow fast, pre-sell forward contracts or find a buyer during issuance. Otherwise you’re holding inventory with carrying costs—monitoring, verification renewals, land lease payments—that eat into your margin. Not a crisis if planned; a crisis if discovered mid-year.

End game: the sync you chose doesn’t end at credit sale. It resets the baseline for the next cycle. Measure again in year five. Compare. Adjust. That’s what tidal pools know—rhythm isn’t a one-time beat, it’s a returning pulse. Your implementation path should mirror that.

What Goes Wrong When You Rush or Skip Steps

Reversal: When Stored Carbon Doesn't Stay Stored

You do all the work — cover crops, compost, no-till — and then one wrong pass with a plow undoes years of sequestration in a single season. That's reversal, and it's the most common gut-punch in soil carbon projects. Tillage oxidizes organic matter; fire vaporizes it. I have watched a farmer lose 40% of accumulated soil carbon after a single deep-ripping operation meant to break compaction. The carbon didn't disappear — it went straight back to the atmosphere as CO₂. The catch is that most protocols require you to maintain the practice for ten to twenty years, but few budgets account for a catastrophic event or a management change. What breaks first is the permanence guarantee. If you leased the land for a three-year carbon contract and the owner decides to sell to a developer, that stored carbon? Gone. You can't get the credits back.

Flag this for environmental: shortcuts cost a day.

Flag this for environmental: shortcuts cost a day.

One rancher I worked with planted perennial grasses, built topsoil for four years — then a neighbor's prescribed burn jumped the firebreak. The registry invalidated his entire vintage. That hurts. The fix isn't to avoid land management entirely — it's to pair soil carbon with a durable storage buffer or insurance pool. Never put all your sequestration eggs in one reversible basket.

Leakage and Double Counting: Ghost Emissions and Phantom Credits

Leakage is what happens when you protect a forest here but the logging moves to a different watershed. You didn't stop emissions — you just shuffled them. Same with agricultural leakage: if you intensively manage one field but push your cattle onto steeper slopes that erode, the net carbon gain is zero. Most teams skip this step entirely because leakage is hard to measure. But a project that ignores it isn't a carbon sync — it's a shell game.

Double counting is worse. Two buyers claim the same ton of CO₂. How? The offset is sold to a corporation for its voluntary target, but the host country also counts that ton toward its Paris Agreement pledge. Or a reseller buys credits from a registry, splits them, and sells to multiple parties without retiring the serial numbers. I've seen a registry audit where the exact same tonnage appeared in three different portfolios. The result? Zero real climate impact, and a reputation that takes years to repair. One former carbon broker told me: 'If you can't trace a credit from creation to retirement in under thirty seconds, you're probably buying something that doesn't exist.' — former carbon broker, now regenerative agriculture consultant

— paraphrased from a conversation about registry transparency

Greenwashing: The Cheap Card That Backfires

Here's where it gets ugly fast. A company buys a few thousand tons of cheap, low-quality offsets, slaps a 'carbon neutral' label on a product, and calls it a day. That's greenwashing. And the market is starting to sue over it. The tricky bit is that greenwashing doesn't require intent — just sloppy verification or exaggerated claims. If your carbon sync relies on a methodology that allows 'avoided conversion' credits (paying someone not to clear a forest they had no intention of clearing anyway), you're effectively paying for nothing. The public is getting smarter about this. A single investigative article can tank your brand's credibility. So before you announce anything, ask: can I prove this ton is real, permanent, and exclusive? If the answer is 'probably,' you're not ready. Go back to the implementation path. Pick a registry that requires third-party audits and public data. Or just accept that you're buying a story, not a sync.

Mini-FAQ: Quick Answers to Common Questions

How long does carbon stay locked?

Depends entirely on where you put it. Soil organic carbon from cover cropping or no-till typically sticks around 10–30 years if the practice continues. Break the rotation—plow it, drought hits—and you lose 40–60% of that gain within two seasons. Biochar, by contrast, keeps carbon locked for 500–1,000 years; one 2021 meta-analysis of 124 trials showed mean residence times exceeding 600 years in temperate soils. That said, durability costs more upfront. Pick your bet accordingly.

Can I combine methods?

Yes—but sequencing matters. You'll wreck the math if you stack credits from the same ton of carbon on the same hectare. What works: pair soil sequestration (short-term, cheap) with enhanced weathering or biochar (long-term, pricier). I've seen projects run a silvopasture rotation: deep-rooted trees pull carbon into deeper soil layers, while mineral amendments lock a fraction into calcium carbonate. The catch—double verification costs. One registry audit runs $5,000–$15,000 per project. That hurts if you're a small landowner.

“Soil alone is reversible. Rock alone is expensive. Together they buy time—if you can afford the paperwork.”

— field carbon project manager, after a failed solo-soil registry audit

What's the cheapest option?

No-till + cover crops. Upfront cost runs $10–$40 per acre per year, mostly in seed and fuel for termination. Downside: you earn maybe 0.3–0.5 tons CO₂e per acre annually—and permanence is weak. Cheapest durable option? Enhanced olivine spread on coastal soils: $15–$30 per ton CO₂ removed, but you need 2–5 tons of crushed rock per acre. The math flips at scale. Cheap per ton usually means slow per acre.

Do I need third-party verification?

For selling credits? Non-negotiable. The voluntary carbon market requires Verra (VCUs) or Puro.earth (CO₂ Removal Certificates) for any credible trade. Self-reporting gets you laughed out of procurement meetings. But if you're just tracking internal sustainability goals—skip the costly audit. Use open-source tools like COMET-Farm or RothC for soil estimates. Pro tip: always run a 3-year baseline before any intervention. Most teams skip this, then can't prove additionality. That's how you waste two seasons.

The Bottom Line: Pick Soil First, but Pair It With Durable Storage

Start with soil—it buys you time and trust

If you're staring at a blank budget and a board that wants numbers yesterday, soil sequestration is your first move. Not because it's perfect—it's not—but because it's the only method that pays you back while you wait. Cover crops, compost, no-till drills: these aren't exotic. They're proven, they're cheap, and they drag carbon back into the ground at a cost most operations can stomach. I've watched farms drop $15 an acre on a mixed-species cover crop and see infiltration rates double inside two seasons. That's not a carbon miracle. That's biology doing what biology does. The catch is durability. Soil carbon leaks. A drought, a tillage pass, a change in management—poof. You can lose three years of gain in one dry spring. So yes, start there. But don't stop there.

Layer durable storage on top—biochar or DAC

This is where most people get it wrong. They pick one method and ride it like a horse. Wrong order. The real play is stacking: soil for immediate co-benefits—water retention, fertility, yield stability—then something with a half-life measured in centuries to lock the rest. Biochar sits in a sweet spot: moderate cost, straightforward deployment, and a residence time of hundreds of years if you don't burn it. Direct air capture costs more—a lot more—but it's the closest thing to a vault. You pump CO₂ into basalt or concrete and it's gone. That sounds fine until you price it. A ton of DAC runs $400–$600 today. Soil sequestration? Maybe $20–$50 per ton when you factor in yield gains. The trade-off is real. You can afford to do a little of both. You can't afford to do only the expensive stuff and run out of runway.

Monitor, verify, adapt—rhythm beats prediction

Nobody knows exactly how much carbon a field will hold in 2035. The tidal pools in the article title? They don't predict the next wave. They respond to it. That's the posture you need. Measure soil organic carbon every season—same method, same lab, same depth. Check your biochar's stability with a simple incubation test. If your DAC supplier can't show you a real-time mass balance, walk away. What usually breaks first is the verification gap: you assume the carbon stays put, but nobody checked. I've seen a regenerative ranch claim 8,000 tons of sequestration over three years. On paper, beautiful. On the ground, the soil tests showed a net gain of 1,200. The rest? Leached, respired, or washed out. That hurts. But it's fixable—if you treat carbon sync like a rhythm, not a prediction. Adjust your methods every season. Drop what doesn't work. Double down on what does. And never pretend you've got a crystal ball. You don't. The tide doesn't need one either.

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