01How to read these comparisons
Every product on these six pages does real work somewhere in a wastewater system. Bacteria additives, enzyme products, iron salts, nitrate products, aeration, and scrubbers and masking agents all have a job they do well, and we say so on each page before we say anything about our own program. We are not trying to sell against any of them. We sell a different point of intervention: usable oxygen delivered to the bacteria already living in the water, dosed as far upstream as we can reach water and power. Read these pages for what each option adds, when it acts relative to the moment hydrogen sulfide forms, and what it leaves behind once it has done its job. The right choice depends on the problem in front of you, not on which page you read first.
The one difference that matters
Across all six categories, the pattern repeats: something is added, and either it stays in the water after it has done its job, or it acts on hydrogen sulfide only after the gas already exists. Bacteria additives and enzyme products introduce organisms or proteins that were not there before. Iron salts bind sulfide into a compound that has to be settled or hauled out. Nitrate products add nitrogen to the water. Aeration and scrubbers manage the air, not the water where the gas is made. Our approach is different in kind, not just in name: we supply usable oxygen to the bacteria already living in the wastewater. The bacteria consume that oxygen as they use it, so nothing of the accelerator is left downstream. Because the bacteria have oxygen before they would otherwise strip it from sulfate, hydrogen sulfide is never formed in the first place, not captured or treated after the fact.
What we do not claim
A fair comparison also states its own limits. Our program does not dissolve sand or grit; that is a physical removal problem, not a biological one. It does not replace aeration at the treatment plant: aeration keeps running, and our program simply gives it less organic load to work through by the time the water arrives. It does not replace gas monitors or confined-space procedures at a lift station or a wet well; those stay in place regardless of what our readings show. And we do not promise a result before we measure one. Every system differs in flow, temperature, grease load and how long the water sits, so we set a baseline before the first dose and report the trend against that baseline, case by case, rather than quoting a number from someone else's system.
Six options side by side
| Option |
What it adds |
Acts before or after H2S forms |
What stays downstream |
Works on FOG and sludge |
Best fit |
| Bacteria additives |
An outside bacterial culture |
After: needs oxygen or a niche to establish before it works |
The added culture, competing with the native population |
Some formulations, if they establish |
A system with little native biological activity to start from |
| Enzyme products |
Manufactured enzymes |
After: breaks down existing material, does not stop sulfide from forming |
Spent enzyme residue |
FOG mostly; limited effect on the gas |
A grease-heavy line where gas is not yet the main complaint |
| Iron salts |
An iron compound |
After: binds sulfide once it exists |
Iron compound requiring removal or settling |
No, gas only |
A site that needs a fast odor knockdown while a longer fix is arranged |
| Nitrate products |
Nitrogen compound |
Before: gives bacteria an alternate oxygen source to sulfate |
Added nitrogen |
No, gas only |
A force main with the flow and dosing access to sustain nitrate addition |
| Aeration |
Air (dissolved oxygen) |
Before, where it physically reaches |
Nothing added, but ongoing blower and energy cost |
At the plant, not upstream |
A treatment plant with the blower capacity and access aeration needs |
| Scrubbers and masking agents |
Chemical scrubbing media or fragrance |
After: treats the gas or the smell once it is in the air |
Spent scrubbing media or fragrance residue |
No |
An enclosed space where the air, not the water, is the problem |
| DRP Accelerator |
Usable oxygen for native bacteria |
Before: hydrogen sulfide is not formed |
Nothing; the accelerator is consumed as bacteria use it |
Yes, both |
A collection system or lagoon with a dosing point that can reach water and power upstream |
No single row on this table is wrong for every site. A lift station with an active complaint today may still need an iron drum on order while a dosing point for the accelerator is surveyed. A plant with room in its aeration basins may only need help upstream, where blowers cannot go. Read the table for where each option sits, then read the page for the category closest to your problem.
Read the full comparisons
- Bacteria additives: where an added culture helps, and where the native population already doing the work is enough on its own.
- Enzyme products: what enzymes break down well, and why they do not touch the gas.
- Iron salts: fast odor knockdown, and what has to be removed once the iron has done its job.
- Nitrate products: another oxygen source ahead of formation, and what it adds to the water.
- Aeration: where blowers do their best work, and why they cannot reach a force main.
- Scrubbers and masking agents: treating the air instead of the water, and when that is the right target.
Named suppliers, one page each
The companies below add bacteria to wastewater, and each is an established supplier. Every page describes the company in its own terms, as its website puts it, says where that company is the better fit before saying where we are, and ends with the question to ask about your own system. Start with the side-by-side page if you want all of them at once.
COMMON QUESTIONS
Straight answers.
Which of these options actually stops hydrogen sulfide from forming?+
Only two of the six options act before hydrogen sulfide forms: nitrate products and DRP Accelerator, both of which give bacteria an oxygen source before they turn to sulfate. Bacteria additives, enzyme products, iron salts and scrubbers and masking agents all act after the gas or the material they target already exists. Acting earlier does not make an option better for every site; it means the two groups solve different moments in the same problem.
Is DRP Accelerator a bacteria additive?+
No, DRP Accelerator is not a bacteria additive. It is an inorganic compound that carries usable oxygen to the bacteria already living in the wastewater; we add no bacteria and no enzymes. The full comparison to bacteria additives, including where an additive is the better fit, is on its own page.
Can iron salts and DRP Accelerator be used at the same site?+
Iron salts and DRP Accelerator can run at the same site, though many operators move away from iron once the accelerator program is established. Iron salts bind sulfide after it forms and can serve as a fast, temporary response while a dosing point for the accelerator is surveyed and set up. Once hydrogen sulfide is prevented at the source, the ongoing need for iron typically drops.
Does DRP Accelerator replace aeration at the treatment plant?+
DRP Accelerator does not replace aeration at the treatment plant. Aeration keeps running there; the accelerator's job is upstream, in the collection system, force mains and lagoons that plant aeration cannot reach. The two work at different points in the same system rather than competing for the same job.
What does acting before or after H2S forms mean in the comparison table?+
It describes the moment in the process when an option does its work. An option that acts before formation gives bacteria an oxygen source so they never strip it from sulfate, which is how hydrogen sulfide is normally made. An option that acts after formation treats, binds or masks the gas once it already exists, whether that gas is dissolved in the water or already in the air above it.
Which option is the best fit for a lift station with an odor complaint today?+
For an immediate odor complaint, iron salts or a scrubber can knock the gas down fastest while a longer-term fix is arranged. DRP Accelerator is not an instant fix; it is dosed upstream and works as the native bacteria population adjusts to the oxygen it supplies over the following weeks. Many sites use a fast response for the complaint in front of them and prevention for the complaints still ahead.