The pipe ran into the leachate sump because that was the nearest wet well, and for six years nobody thought about it. Then the site started solidifying sump contents for off-site disposal, and the first three loads came back from the receiving facility with a pH of 3.9 and a solvent smell that the inspector wrote up twice.
Landfill gas condensate is the stream that gets absorbed into leachate accounting and then surprises everyone. It is small in volume, usually one to five cubic metres a day on a medium site, and it is chemically nothing like the liquid it joins.
Condensate forms when warm, saturated landfill gas cools in the collection pipework. What drops out is a dilute aqueous mixture of volatile fatty acids, alcohols, ketones, aromatic hydrocarbons and ammonia, typically with a pH between 3.5 and 5.5, a COD that can run from 1,000 to 15,000 mg/L depending on waste age, and a distinct solvent odour. It carries almost no suspended solids and almost no hardness.
That last point is the one that matters for solidification. Leachate gel dosing is built around a liquid with a high dissolved load competing for water. Condensate has very little competition, so a dose calculated by mass or by COD will over-absorb, produce a stiff, poorly mixed mass, and leave free liquid trapped in pockets. Operators describe it as “the batch that goes crumbly”.
Polyacrylate swells best in the neutral to mildly alkaline range. Below about pH 5 the carboxylate groups protonate, the polymer network collapses, and absorption capacity falls steeply. A condensate at pH 4.0 blended into a sump at pH 7.8 does not simply dilute; where the two meet, locally low pH can suppress swelling in a way that a bulk pH reading never shows.
In practice the fix is either to neutralise the condensate before it enters the batch, or to keep it out of solidification batches entirely and route it to the treatment plant’s biological stage, which handles volatile acids well. Both are legitimate. Mixing it in and hoping is the option that fails.
Three cubic metres a day is roughly one tanker load a month. That is small enough that a site can handle it with a dedicated 5 m3 tank and a batch protocol, and large enough that ignoring it will change the character of every batch it touches.
The protocol that works: collect condensate separately, equalise for at least 24 hours because flow is bursty and composition swings with gas temperature, neutralise to pH 6.5 to 7.5 with a measured alkali dose, then either send it to the biological plant or solidify it as its own batch with a dose set by trial rather than by analogy to leachate.
Watch the odour at the point of handling. Condensate in an open tank releases volatiles fast, and a batch that is mechanically agitated in an enclosed shed will put those volatiles into the working atmosphere. Forced ventilation and closed transfer are not optional extras on this stream.
Sites that co-mingle condensate and then solidify report three symptoms in a recognisable order. First, gel consumption per cubic metre rises without explanation. Second, batches occasionally set unevenly, with a wet pocket at the bottom of the drum that shows up as a paint filter failure. Third, the receiving facility starts asking about odour and about a low pH reading on the acceptance test.
Each symptom gets treated separately, which is why the root cause takes months to find. The cheap diagnostic is to sample the sump twice: once before the condensate line discharges and once two hours after. If pH and conductivity shift measurably across that window, the condensate is running the batch, not the leachate.
For a site that has never separated the streams, the first practical step is a five-day logging exercise: measure condensate volume daily and pH and conductivity at the sump inlet. That data decides whether separation is worth piping. Where the condensate is routed to its own batch, a grade with a wider working pH band reduces the neutralisation burden, and the product data sheets state the pH window for each type.
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