སྒྱུ་རྩལ
མཛེས་སྡུག་དང་བདེ་ཐང
བཟོ་རིག
རིག་གནས་དང་ལོ་རྒྱུས
དགའ་སྟོན
ཁོར་ཡུག
ཟས་དང་བཏུང་རྫས
ཕྱིར་འཕྲུལ་རིག
ཚན་རིག
རྩེད་འགྲན
རིག་རྩལ
གྱོན་རུང

Activated Sludge
People had been blowing air through sewage since the 1880s. It worked, slowly, and it took weeks — long enough that nobody could build a works around it. The organisms doing the job were being washed out as fast as they grew.
Edward Ardern and William Lockett, working at the Davyhulme works in Manchester, published the answer in April 1914 in a paper with a deliberately dull title: Experiments on the Oxidation of Sewage without the Aid of Filters. They aerated sewage in a bottle until it was clean, then poured off the clear liquid and KEPT the sludge at the bottom. Then they filled the bottle again with fresh sewage onto that same sludge. And again. Each cycle got faster. By the time they had accumulated enough sludge, sewage that once took five weeks was treated in about six hours.
They called the retained sludge activated, borrowing the word from activated carbon, and the name stuck to the whole process. What they had actually invented was the decoupling of two times that everyone had assumed were one. The water passes through in hours. The organisms stay for days. Once you can set those two independently you can grow a dense population of exactly the organisms that eat your waste, and keep them.
Everything else in the process follows from that. You need a settling tank, because the only way to hold the sludge back is to let it settle and pump it forward. You need the sludge to settle well, which turns out to be a biological property you can lose. And you need to waste some sludge deliberately every day, because the population grows, and how much you waste sets how long an organism stays — the sludge age — which is the single control knob over what kind of community you get.
You will build a bench reactor with a settler, grow a culture, measure its density and its settling behaviour, and deliberately push it into the failure that plagues every real works: bulking.
མཐོ་རིམ
6 hours to build, 6 weeks to a stable culture
ལམ་སྟོན
1
1
Build the reactor and the settler as one loop
Build the reactor and the settler as one loop
The plant is two vessels and a return, and the return is what makes it a process rather than a bucket of aerated sewage.
The aeration tank: a 10 litre clear container, tall rather than wide, with an air stone on the floor fed from an aquarium air pump. Tall matters — a bubble rising through 400 mm of liquid has roughly twice the contact time of one rising through 200 mm, and contact time is what transfers oxygen. Run enough air to keep the whole contents visibly rolling; you are mixing as well as aerating, and settled solids in the corner of an aeration tank go anaerobic and start making the smell that gets works closed.
The settler: a cone-bottomed vessel of about 3 litres hung immediately after it. A cone, not a flat bottom, and a steep one — 60 degrees — so sludge slides to the point instead of sitting on a shelf. Feed it from the aeration tank near mid-depth, take clear effluent off a weir at the top, and take sludge from the very bottom of the cone.
The return: a small peristaltic pump or an air lift moving settled sludge from the cone bottom back to the aeration tank. Set it initially at about the same rate as the feed — a 1:1 return ratio — which is ordinary practice. The return must run continuously. Sludge that sits in a cone for more than about half an hour goes anaerobic, releases the phosphorus it has taken up, and floats back to the surface in a mat, which people misread as bulking. It is not bulking, it is a stopped return.
Feed with the same defined synthetic wastewater as the rest of this batch — per 10 litres, 1.5 g glucose, 1.5 g peptone, 0.5 g ammonium chloride, 0.2 g potassium dihydrogen phosphate, 0.5 g sodium bicarbonate — at roughly 40 litres per day, giving about six hours of hydraulic detention. Use a peristaltic pump on a timer, or a levelled constant-head bottle with a needle valve.
Seed with two litres of return sludge from a working municipal plant if you can get it. If not, settled effluent from a septic tank will populate the reactor eventually, but expect to spend six weeks rather than two getting to a stable, well-settling culture.
གོམ་པ་འདིའི་རྫས་རིགས:
Acrylic Tube (100mm, Clear)1 དུམ་བུ།
Acrylic Sheet (5mm, Clear)1 square metre
Air Pump1 དུམ་བུ།
Air Stone2 དུམ་བུ།
Laboratory Peristaltic Pump2 དུམ་བུ།
Activated Sludge Seed2 ལི་ཊར།ལག་ཆས་དགོས་མཁོ:
Hacksaw
Acrylic Strip Heater
Digital Calipers - 152.4 mm
Bucket (10L, Graduated)
Stopwatch2
2
Measure the culture: MLSS, the settled volume, and the index that joins them
Measure the culture: MLSS, the settled volume, and the index that joins them
Three measurements run this process. Take all three daily; they take twenty minutes together and nothing else tells you what the culture is doing.
Mixed liquor suspended solids, MLSS, is how much biomass you are carrying. Filter a known volume of well-mixed aeration-tank contents through a dried, pre-weighed glass-fibre filter, dry it at 105 degrees Celsius to constant mass, and weigh again. Milligrams of solids per litre. Conventional plants run 1500 to 4000 mg/l. Below about 1000 you have too few organisms to do the work in the time available; above about 5000 the settler cannot cope with the solids loading and you lose sludge over the weir.
The thirty-minute settled volume is the crude, fast one and it is the one operators actually watch. Fill a one litre measuring cylinder with mixed liquor, leave it thirty minutes, read the millilitres the sludge blanket occupies. It takes no equipment and it shows you the answer directly: a good sludge falls to a compact 200 to 300 ml with a sharp interface and clear water above. A bad one hangs.
The sludge volume index joins them and is the number that means something: SVI is the volume in millilitres that one gram of sludge occupies after thirty minutes of settling.
SVI = settled volume (ml/l) x 1000 / MLSS (mg/l)
An SVI under 100 is a good, dense, well-settling sludge. Between 100 and 150 is workable. Over 150 the sludge is bulking — it occupies too much volume for its mass, the blanket in the settler rises, and eventually it goes over the weir and the plant fails visibly.
The reason SVI is the right number rather than either input alone: a plant can carry 4000 mg/l of excellent sludge or 1500 mg/l of terrible sludge, and the settled volume alone cannot tell them apart. Normalising by mass can.
While you have the cylinder in front of you, look at the water above the blanket. Crisp and clear with a sharp interface is a healthy sludge with protozoa grazing the free bacteria. Cloudy with fine particles that never settle is a young sludge, too low a sludge age, dispersed growth. Learn to read those two before you trust any instrument.
གོམ་པ་འདིའི་རྫས་རིགས:
Glass Fibre Filter Papers (1.2 micron)100 དུམ་བུ།
Distilled Water5 ལི་ཊར།ལག་ཆས་དགོས་མཁོ:
Graduated Cylinder (100 ml)
Measuring Cylinder
Precision Digital Scale (0.01g)
Buchner Funnel (Porcelain)
Stopwatch3
3
Sludge age, oxygen demand, and the two times you get to set separately
Sludge age, oxygen demand, and the two times you get to set separately
Loading Jupyter Notebook...
ལག་ཆས་དགོས་མཁོ:
Desktop Computer
Notebook and Pencil4
4
Log dissolved oxygen continuously — the one variable that changes faster than you can watch
Log dissolved oxygen continuously — the one variable that changes faster than you can watch
Dissolved oxygen is the variable that moves on a timescale of minutes and decides everything. Below about 0.5 mg/l the floc goes anaerobic at its centre and filamentous organisms — which tolerate low oxygen better than floc-formers — take over, and you get bulking. Above about 3 mg/l you are simply wasting electricity, and on a real works aeration is most of the energy bill.
A spot reading once a day tells you almost nothing, because DO swings with every feed dose. Log it.
This sketch runs on an ESP32 with an analogue dissolved-oxygen probe and a DS18B20 temperature sensor, because DO saturation is strongly temperature-dependent and an uncompensated reading is not a measurement. It logs to an SD card every thirty seconds and prints to serial, and it computes percent saturation as well as milligrams per litre so you can see how hard the aeration is actually working.
Calibrate before you trust it. Two points: zero, in a fresh solution of sodium sulfite which strips oxygen out of water completely; and saturation, in water vigorously aerated for twenty minutes at a known temperature. The saturation table is in the sketch.
Run the logger through a feed dose and look at the trace. You should see DO drop sharply as the organisms get their food, then climb back as it is consumed. The depth of that dip is a direct measure of the culture's respiration rate, and watching it recover — or fail to — is the earliest warning you will get of a plant in trouble.
do_logger.inocpp
གོམ་པ་འདིའི་རྫས་རིགས:
ESP32 Development Board1 དུམ་བུ།
Dissolved Oxygen Probe (Analogue)1 དུམ་བུ།
DS18B20 Temperature Sensor (Waterproof)1 དུམ་བུ།
MicroSD Card Module1 དུམ་བུ།
Sodium Sulfite100 gramལག་ཆས་དགོས་མཁོ:
Soldering Station (Temperature-Controlled)
Digital Multimeter (Lab Grade)
Dissolved Oxygen Meter
Desktop Computer5
5
Break it deliberately: cause bulking, then cure it
Break it deliberately: cause bulking, then cure it
Bulking is the characteristic failure of activated sludge, it is biological rather than mechanical, and the fastest way to understand it is to cause it on purpose in a system you can afford to lose.
What it is: filamentous bacteria growing long threads that bridge between flocs and hold them apart. The sludge stops being a collection of dense compact particles and becomes an open lattice that traps water. It occupies far more volume for the same mass — SVI climbs past 150, then past 250 — the blanket in the settler rises steadily day after day, and finally solids go over the weir and the effluent is worse than the influent. The reactor is still eating the food perfectly well. It simply cannot separate itself from the water any more, and separation is half the process.
To cause it, take away the thing floc-formers need and filaments do not. Filaments have a high surface-to-volume ratio, so they are better at scavenging when something is scarce. Any of these three will do it within one to two weeks: throttle the air until DO sits below 0.5 mg/l; drop the feed so F/M falls under about 0.05 with a very long sludge age; or leave out the potassium dihydrogen phosphate so nitrogen and phosphorus become limiting.
Pick one, log MLSS and SVI daily, and plot SVI against time. You will see it climb before you see anything wrong in the settler — which is the point of measuring it. Look at a drop under a microscope at 100x if you have one: the threads are unmistakable, running between and through the flocs.
Then cure it, and cure it by reversing the specific cause rather than by reaching for chemicals. Restore the DO to 2 mg/l, or restore the nutrient, or increase the feed. Recovery takes one to three sludge ages — a week or two — because you are not killing the filaments, you are letting the floc-formers out-grow them. There is no fast fix, which is exactly why operators watch SVI daily instead of waiting for the settler to tell them.
Chlorinating the return sludge is the emergency measure a real works uses when the blanket is about to go over the weir. It damages filaments more than flocs because filaments have more surface exposed. It is a tourniquet, not a treatment: it buys days while you fix whatever caused it, and it harms the culture. Do not reach for it first.
Record the whole excursion — cause, daily SVI, cure, days to recover. That record is worth more than the plant working perfectly for a month, because a process you have only ever seen working is a process you cannot yet run.
གོམ་པ་འདིའི་རྫས་རིགས:
Glass Fibre Filter Papers (1.2 micron)50 དུམ་བུ།
Potassium Dihydrogen Phosphate100 gramལག་ཆས་དགོས་མཁོ:
Measuring Cylinder
Precision Digital Scale (0.01g)
Compound Microscope
Dissolved Oxygen Meter
Notebook and Pencilརྫས་རིགས
15- 1 དུམ་བུ།ས་ཆ་འཛིན
- 1 square metreས་ཆ་འཛིན
- Laboratory Peristaltic Pumpཁེ་ཕོགས 10%2 དུམ་བུ།ས་ཆ་འཛིན
- 4 metreས་ཆ་འཛིན
- Activated Sludge Seedཁེ་ཕོགས 100%2 ལི་ཊར།ས་ཆ་འཛིན
- 150 དུམ་བུ།ས་ཆ་འཛིན
- 5 ལི་ཊར།ས་ཆ་འཛིན
- ESP32 Development Boardཁེ་ཕོགས 10%1 དུམ་བུ།ས་ཆ་འཛིན
- Dissolved Oxygen Probe (Analogue)ཁེ་ཕོགས 100%1 དུམ་བུ།ས་ཆ་འཛིན
- DS18B20 Temperature Sensor (Waterproof)ཁེ་ཕོགས 100%1 དུམ་བུ།ས་ཆ་འཛིན
- MicroSD Card Moduleཁེ་ཕོགས 100%1 དུམ་བུ།ས་ཆ་འཛིན
- Sodium Sulfiteཁེ་ཕོགས 100%100 gramས་ཆ་འཛིན
- Potassium Dihydrogen Phosphateཁེ་ཕོགས 100%100 gramས་ཆ་འཛིན
ལག་ཆས་དགོས་མཁོ
15- Acrylic Strip Heaterཁེ་ཕོགས 10%ས་ཆ་འཛིན
- Digital Calipers - 152.4 mmཁེ་ཕོགས 10%$14.00
- ས་ཆ་འཛིན
- Measuring Cylinderཁེ་ཕོགས 10%ས་ཆ་འཛིན
- Buchner Funnel (Porcelain)ཁེ་ཕོགས 10%ས་ཆ་འཛིན
- Desktop Computerཁེ་ཕོགས 100%ས་ཆ་འཛིན
- Notebook and Pencilཁེ་ཕོགས 10%ས་ཆ་འཛིན
- Soldering Station (Temperature-Controlled)ཁེ་ཕོགས 10%ས་ཆ་འཛིན
- Digital Multimeter - Lab Gradeཁེ་ཕོགས 10%ས་ཆ་འཛིན
- Dissolved Oxygen Meterཁེ་ཕོགས 10%ས་ཆ་འཛིན
- Student Compound Microscope (40x-1000x)ཁེ་ཕོགས 10%ས་ཆ་འཛིན
འབྲེལ་ཡོད་བིལུ་པིརིན་ཊི
བིལུ་པིརིན་ཊི་འདི་ཚུ་ཐབས་ལམ་དང་རྫས་རིགས། སྤྱི་ཆོས་བགོ་བཤའ་བྱེད
CC0 སྤྱི་དབང
བིལུ་པིརིན་ཊི་འདི་CC0 འོག་བཀྲམས་ཡོད། ཁྱེད་རང་གིས་ཆོག་མཆན་མ་བཞེས་པར་ཕབ་ལེན་དང་བཟོ་བཅོས། བགོ་བཤའ། དགོས་མཁོ་གང་ལའང་བཀོལ་སྤྱོད་བྱས་ཆོག
བཟོ་མཁན་ལ་རྒྱབ་སྐྱོར་བྱེད་པའི་ཆེད་ཁོང་ཚོའི་བིལུ་པིརིན་ཊི་བརྒྱུད་ཐོན་སྐྱེད་ཉོ། བཟོ་མཁན་གྱིས བཟོ་མཁན་གྱི་ཁེ་ཕོགས ཚོང་པས་གཏན་འཁེལ་བྱས་པ། ཡང་ན་བིལུ་པིརིན་ཊི་འདིའི་པར་གསར་བཟོས་ཏེ་ཁྱེད་རང་གི་བིལུ་པིརིན་ཊི་ནང་མཐུད་སྦྲེལ་བྱས་ཏེ་ཡོང་སྒོ་བགོ་བཤའ་བྱེད།


