ORP Redox Potential ???

fullmonti

now is the time
I had ask a question about UV sterilizers & was given a link to an article about them. Among other things it spoke about Redox Potential & ORP, ORP I had heard of but no one around here really understood it well enough to explain it, Redox never heard of before. The article had obviously been written by a scientist who knew what he was talking about. BUT could some one please explain these things in a way that some one who is NOT a scientist, biologist or chemist could understand? Thank You in advance
 
The term Redox is a shortcut for the work Reduction. ORP stands for Oxidation Reduction Potential.

Some say ORP is an indicator of the balance of oxidation and reduction reactions taking place in seawater.

Others say that ORP measures the tanks ability to process decaying organic material which requires oxygen to process. The more oxidative power the water has, the better it will be able to deal with organic material.

Either way, in this day and age, it appears the only benefit to using ozone is water clarity. And to use ozone, you should monitor ORP.

Due to the advent of super skimmers and all that good stuff, not much of a benefit does running ozone give to the aquarist other than that.

That's pretty simple huh ? :)
 
OK if this was covered in high school science class I must have been sleeping. So forgive the dumb questions pls. I know when aluminum oxidizes it gets a chalky film on it. When you refer to oxidation in a tank what are you referring to? And reduction reaction???

Sorry I'm playing catchup on the tech end of reefing

And I almost forgot the original question was about UV sterilizers, & how effective they might be in helping rid a tank of algae, & would they zap good stuff in the process? Though this might not be the time to get into that?
 
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I doubt a UV has too much impact on ORP.

Here's a description of what ORP is, both simplified and technical:

ORP and the Reef Aquarium
http://reefkeeping.com/issues/2003-12/rhf/feature/index.php

the simplified one:

Simplified ORP

Imagine a reef aquarium as a vast battlefield. No, more vast. Much, much more. OK, that's ORP. That is, ORP is a measure of who is winning and who is losing the battle. The battle is never won by one side or the other. As an aquarist, you do not want it to be, or else everything in the tank would be dead. In other situations, such as the purification of tap water for drinking, allowing the oxidizers to win is fine. A high enough ORP (650+ mv) can kill most bacteria in a few seconds.

On one side of this aquarium battle there are the oxidizers. They all want to get electrons, and they rip them off of the bodies of the enemy. The foot soldiers of the oxidizers are oxygen molecules (O2). Did I say the battle is vast? On one day last week, there were 342,418,226,849,748,675,496,726 of these little guys roaming my aquarium, looking for action. Some of these are paratroopers, arriving at the aquarium out of the air. Others are made in secret labs, otherwise known as photosynthetic organisms such as many corals and algae.

Unfortunately, despite their vast numbers, the oxygen molecules are not very effective fighters. In many cases, they can swarm all over the enemy and still not prevail. The true leaders of the oxidizers are far less numerous, but considerably more potent fighters. These include ozone (O3), hydrogen peroxide (H2O2), triplet oxygen (3O2), and a variety of oxygen radicals, some with such inspiring names such as superoxide radical (O2-). They also include chlorine (Cl2) and chloramine (NH2Cl). It turns out that oxygen molecules (O2) can occasionally morph into some of these better fighters (such as hydrogen peroxide), sometimes all on their own, but most frequently when they get blasted with UV light.

The oxidizers also have other types of fighters. Some are present at very low concentration, but are so sensitive to the state of the battle, that one can gauge the battle by how many of them are left standing at any given point in time. Metals, for example, such as iron (as ferric ion, Fe+++) can serve this purpose. The other oxidizers also include anions such as hypochlorite (ClO-), iodate (IO3-) and nitrate (NO3-), among a host of others.

On the other side are the reducers. The reducers all want to get rid of electrons, and they virtually throw them at the oxidizers. Many of these are organic molecules. They are not as numerous as the oxidizers, but many are much larger. Some are more than 10,000 times as large as an oxygen molecule. So they can make up for low numbers with pure brawn. That is not to say that the reducers do not have small but potent soldiers. The antioxidant vitamins, like vitamin C, for example, are small but extremely potent reducing agents. The reducers also number on their side some inorganic compounds, such as ammonia, iodide, and a really nasty fellow, sulfide.

The reducers come from fish food, metabolic waste products, the breakdown of dead organisms, and certain additives put into the aquarium (e.g., iron supplements that contain ferrous ion). The surfaces of most organisms themselves enter the fray as reducers, waiting to be oxidized by the enemy.

Interestingly, most soldiers on both sides are suicide attackers. Oxygen, ozone, and hydrogen peroxide are all destroyed when they react with a reducer. While not strictly suicidal, most organics are heavily damaged by oxidizer attacks, and are slowly degraded, eventually ending up as carbon dioxide if oxidized enough. They tend to be found in areas that the oxidizers hate; that is, in areas of low oxygen. Yet, the reducers are also sneaky, and even manage to get their hands inside cells (even finding positions in photosynthesis itself).

So Where Does ORP Fit Into All This?

ORP is a measure of the relative fighting ability of the oxidizers and the reducers. Think of the surface of the ORP electrode as a surface that these various fighters are hurling themselves against for practice. If there are lots of potent oxidizers around, and not so many reducers, ORP rises because the electrode senses more oxidizing "power" in solution. Likewise, ORP drops if it senses more reducing power in solution.

The exact value reported by an ORP electrode is, consequently, a constantly varying number that represents the ebb and flow of the battle. If you add oxidizers to the aquarium (ozone, permanganate, hydrogen peroxide, etc.) then the ORP rises. Alternatively, if you add a lot of organic molecules to the solution, or restrict the oxygen supply, the ORP drops.

What about pH? pH can impact the ORP readings in aquaria. Often, ORP goes down as pH rises. A typical aquarium ORP reading will change on the order of 59 mv/pH unit. The easiest way to understand this is to simply think of pH as a measure of hydrogen ions (H+) in solution, and to think of H+ as being on the side of the oxidizers. In reality, H+ doesn't usually oxidize things itself (though it can), but more typically it can hype up other oxidizers, like oxygen, making them much more potent. So during the course of a 24-hour day in a reef aquarium, ORP will vary as pH and O2 also vary.

Is ORP a useful measure? That is, should aquarists really care how this incredible battle is going? To some extent, yes. If the oxidizers carry the day, the ORP would rise to the point where the organic molecules that represent the bodies of organisms would be burned away. If the reducers won outright, the ORP would drop below 0 mv. In that case, there would be little oxygen left, and toxic hydrogen sulfide would rule the aquarium. In either case, the aquarium would be a disaster.

So aquarists have to hope for, and to some extent maintain, this battle in a sort of middle ground. That middle ground is typically described as being between 200 and 500 mv. Most aquarium authors have recommended a range of 300-450 mV. Why? Mostly because the ocean often has ORP in this range, and because these authors have successfully operated aquaria in this range.

HOWEVER, there is a significant potential to misunderstand cause and effect with ORP. If a crappy looking tank that is overrun by algae has a low ORP, is the low ORP the cause of the algae, or is the algae the cause of the low ORP? Or are both simply the byproduct of some other process? Does artificially raising ORP by adding an oxidizer like ozone actually improve anything? The answers are not obvious. These and other related questions will be addressed in greater detail in subsequent sections of this article that go into the scientific details surrounding ORP in aquaria.

Most reef aquarists, aside from those that use ozone and must therefore monitor ORP to prevent overdosing, use ORP to monitor if anything unusual happens in the aquarium. A sudden drop in ORP, for example, suggests that the reducers are suddenly gaining ground. That might be because a gush of organic molecules has been released from a dead organism, or because the oxygen supply is not keeping up with demand for some reason. Aquarists might use such information like an alarm suggesting the tank needs to be looked at closely. Most aquarists do not target any specific ORP value as being optimal, in part because ORP measurement is subject to considerable potential error.

So is ORP measurement and control recommended for nonscientists who also happen to be reef aquarists? My suggestion is no. There are interesting things to learn by measuring ORP, and I recommend that everyone with any interest read the following sections to better understand it and decide for themselves if it is worth doing or not. Nevertheless, I have not measured ORP in my aquarium for years, despite having the tools at hand. It is simply not very high on the list of things that one can usefully do to maintain a high quality reef aquarium, in my opinion.
 
WOW
That was a really long answer, BUT it did explain what goes on very well. Thank YOU!!!

One part of keeping a reef tank has been like going to photo school. When I started out I thought I knew a little some thing about it. Then the more I learned, the more I realize I had a lot more to learn.

A little peace ocean in your living room is a wonderful & beautiful thing. While it didn't appear a simple thing to do, it is proving to be a very complex system to fully understand.
Working on it!

Thanks again
 
I had ask a question about UV sterilizers & was given a link to an article about them. Among other things it spoke about Redox Potential & ORP, ORP I had heard of but no one around here really understood it well enough to explain it, Redox never heard of before. The article had obviously been written by a scientist who knew what he was talking about. BUT could some one please explain these things in a way that some one who is NOT a scientist, biologist or chemist could understand? Thank You in advance

When a chemical species accepts electron, it is reduced. The species that donates the electron is oxidized.

An oxidizing agent is itself reduced.

ORP is the aggregate prevailing "tendency" for oxidation or reduction of all species in solution.

Oxygen is the most common oxidizing agent, so the degree of oxygenation has a profound influence on ORP.
 
Either way, in this day and age, it appears the only benefit to using ozone is water clarity.
Can you explain what that statement is based on?


I review the effects of ozone here, and IMO, the only one most reefers experiences is less yellowing of the water. That's the only reason I use it.

Ozone and the Reef Aquarium, Part 1: Chemistry and Biochemistry
http://reefkeeping.com/issues/2006-03/rhf/index.php

Ozone and the Reef Aquarium, Part 2: Equipment and Safety
http://reefkeeping.com/issues/2006-04/rhf/index.php

Ozone and the Reef Aquarium, Part 3: Changes in a Reef Aquarium upon Initiating Ozone
http://reefkeeping.com/issues/2006-05/rhf/index.php
 
Randy I assume those were your articles, well done but on first blush what I see as possible flaw is your section on ORP.

Using ozone thru a skimmer is not as efficient as a reactor.

That could have been done.

Your level of 300-330 was a bit low to fully asertain the effects of ozone.

Was it not possible with the equip you used to reach those levels?

Only one brand American Marine was used along with one probe, hardly enough of a control.

Ozone used correctly does a hech of a lot more than clear the water, IMO
 
Ozone used correctly does a hech of a lot more than clear the water, IMO

FWIW, the sections on what it can do were not primarily from my experiences, but rather from the literature and what levels and times it takes to do certain things.

Obviously it CAN do more, with enough ozone and a long enough contact time. Like sterilize the water passing through a good reactor. But very, very few reefers have long enough contact times for that.

Any other effect you think reefers experience?
 
Why didn't you say that to begin with, you throw a lot of people off to the use of ozone with your other post.
 
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The use of ozone has long been a standard practice in industrial and public water purification plants, and large scale public aquarium filtration, as one of the best and most efficient means to increase water quality.
One of the biggest problems to overcome in these closed water systems is the accumulation of dissolved organic waste from various biological sources such as animal waste and decomposing food and plant material.

Ozone helps in the eliminations of wastes that the aquatic inhabitants will produce. It oxidizes the pollutants in the tank and brings them to a form from which they can be discarded properly.

Ozone is also a disinfecting agent. Since it can combat with most pathogens,

Ozone enhances the quality of the water. Ozone is a fresh gas, present in the higher realms of the atmosphere where it is purer. The same kind of purity is brought into the reef tank when ozone is used in it. Ozonized water is odorless, colorless and tasteless.

Ozone does not leave chemical wastes in the water when it is passed through it. That means, when water is ozonized, there will be effectively less amount of wastes and chemical discharges into the water.

Ask the curators of public aquariums what they use.


Shall I continue?
 
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Why didn't you say that to begin with, you throw a lot of people off to the use of ozone with your other post.

Not sure what you mean. I posted the effect that most reefers can expect from ozone, and not other effects (good or bad) that I do not believe they will experience. The only reason to use it in a reef, IMO, is to keep the water from yellowing. If you have a different opinion on why to use it, just post it. :)
 
The use of ozone has long been a standard practice in industrial and public water purification plants, and large scale public aquarium filtration, as one of the best and most efficient means to increase water quality.

Absolutely it works welll in those settings with different systems than reefers use to kill bacteria, which is hugely important in many seetings.

One of the biggest problems to overcome in these closed water systems is the accumulation of dissolved organic waste from various biological sources such as animal waste and decomposing food and plant material.

The effect of ozone on organics is very complex, and I go into it in great detail in the first ozone article above. That said, my review of the literature in that area would seem to say the effect is not so clear as you suggest. If you have actual data, I'd love to see it. From it:

"The oxidation of organics is, it turns out, the primary reason that reef aquarists use ozone because it is the organic material in seawater that causes clarity and color issues. Its impact on organic materials is also why ozonation impacts skimming. While most organic compounds that are exposed to enough ozone for a long enough period will be oxidized in some way, some are very much more sensitive than others. In fact, at the levels of ozone attained in a typical reef aquarium contact chamber (less than about 0.3 ppm ozone) or even disinfection applications where the doses are much higher, the total dissolved carbon does not appreciably change during the ozone exposure (although it may later if bacteria find the newly oxidized organics more bioavailable; see below).

In a marine mammal pool,18 for example, it was found that disinfection with 4 ppm ozone with a 30 minute contact time (a disinfection level much higher than is typically used in reef aquaria) did not reduce the pool's total organic carbon (TOC) (~13 ppm TOC), while the use of granular activated carbon (GAC) did reduce it by 37%. Interestingly, the combination of ozone and GAC was even more effective, removing 60-78% of the TOC, suggesting that the ozonation may have altered some of the molecules in a way that made them bind more strongly (or more rapidly) to GAC. An alternative explanation that cannot be ruled out involves biological transformations of the organic compounds taking place on the GAC surface as it became colonized with bacteria)."
 
Ozone is also a disinfecting agent. Since it can combat with most pathogens,

I address that in great detail too, and disagree that typical reefers expereicne such an effect:

http://reefkeeping.com/issues/2006-03/rhf/index.php#13
Reducing Bacteria When Using Ozone



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Bacteria and other organisms suspended in water can be killed by adequate exposure to ozone. That process is widely used to disinfect drinking water and wastewater in a variety of applications. The doses and exposures of ozone required for disinfection, however, are quite high. They are higher than are used in reef aquarium applications, where typical doses of ozone range up to about 0.3 ppm in typical contact chambers, and last for only a few seconds. Consequently, aquarists must be careful when translating disinfection literature to reef aquarium effects.

In a recent study of a recirculating seawater system,35 the dosing of 0.52 ppm of ozone was tested for its ability to decrease the system's bacterial load. That dose is similar to a 300 mg/hr ozone unit applied to a typical small skimmer flow rate of 150 gallons per hour (568 L/h). In this experiment, the levels of suspended bacteria (both Vibrio and coliform) were analyzed in a variety of locations (intake, pre-ozone, post-ozone, pre-tank, and post-tank). In no case was there a statistically significant reduction in bacteria. Even the addition of a venturi injector to the contact chamber did not adequately help (although it trended toward fewer bacteria, the result was not statistically significant). For comparison purposes, at higher ozone concentrations and contact times (5.3 ppm ozone for 240 minutes), Vibrio vulnificus is easily killed, with fewer than one in a hundred million of the initial bacteria remaining.36

How much ozone, and for how long, is required to kill suspended organisms in seawater? In one study of a suspended dinoflagellate algae (Amphidinium sp. isolated from Australia's Great Barrier Reef), it was found that 5-11 ppm ozone for six hours of exposure was required to kill 99.99% of the organisms.37 While that kill rate is impressive, that exposure is far higher than is ever achieved in a reef aquarium application. Lower doses and shorter contact times had smaller effects. A dose of 2 ppm and a short contact time (with the time not stated in the paper) showed a reduction in bacteria of abut 98% (which is still quite significant, but would not be referred to as disinfection).

Similar results were found for the spores of the bacterium Bacillus subtilis.38 In this case, doses of 14 ppm ozone for 24 hours were required to kill 99.99 percent of the spores. In another study 99.9% of fecal coliforms, fecal streptococci and total coliforms were killed with 10 ppm ozone and a contact time of 10 minutes.39 The exposure of Vibrio species and Fusarium solani (bacteria that are pathogenic to shrimp) to 3 ppm ozone for five minutes killed 99.9% of the bacteria.40 Water from a seawater swimming pool was effectively sterilized using 0.5-1.0 ppm ozone in a contact tower.41

The data for the disinfection of freshwater systems are much more extensive, and so include more data at lower contact times and concentrations. In one experiment at a Rainbow trout hatchery, the addition of 1-1.3 ppm of ozone with a contact time of 35 seconds reduced heterotrophic bacteria in the aquarium water itself by about 40-90%.42

Does the ozone used in a typical reef aquarium application reduce bacteria? Maybe, but certainly not to the extent required for disinfection. Still, a reduction of 50% of the living bacteria could have significant effects. The above study in the trout hatchery showed that the use of ozone at several times the typical reef aquarium rate and for about five to ten times the typical contact time results in such a drop. While the data are unavailable, I expect that the bacteria in the water exiting a normal reef aquarium's ozone application are not decreased by as much as 50%.

It seem reasonable to conclude from such literature studies that most bacteria that enter the ozone reaction chamber in a typical reef aquarium application will not be killed by ozone or its byproducts. If killing bacteria in the water column is a goal, then a UV (ultraviolet) sterilizer may be more useful.

Reducing Other Pathogens When Using Ozone



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There has been extensive analysis of the amount of ozone needed to kill the human pathogen Cryptosporidia parvum in freshwater. Most such studies are looking for significant disinfection, but some data points show the effects at lower doses and contact times, and some researchers have developed models that suggest the amount of killing at any dose/time combination.43 For example, at 22° C approximately 63% of the organisms would be expected to be killed at 1 ppm ozone with a contact time of one minute. The contact times and concentrations are inversely related, so at a contact time of six seconds, the required dose to kill 63% is on the order of 10 ppm ozone. At 0.3 ppm ozone and a six second contact time, typical for the high end of reef ozone applications, less than 5% of the organisms would be expected to be killed.

Many viruses are much easier to inactivate with ozone than are other pathogens.44 Enteric adenovirus, for example, is inactivated to the extent of 99.8% after exposure to 0.5 ppm for 15 seconds.44 Feline calicivirus is inactivated to the extent of 98.6% after exposure to 0.06 ppm for 15 seconds.44 Poliovirus type 1 was inactivated to 99% within 30 seconds of contact time at 0.15 ppm ozone.45 Hepatitis A virus was inactivated to the extent of 99.999% within one minute at 1 ppm ozone.46 Norwalk virus was inactivated by 99.9% in 10 seconds of contact at 0.37 ppm ozone.47 Adenovirus type 2 was inactivated by 99.99% by 0.2 ppm ozone with a contact time of about one minute.48

The eggs of a pathogenic helminth (Ascaris suum) were killed to the extent of 90% by exposure to 3.5-4.7 ppm ozone for one hour. One additional hour of exposure killed the remainder.49

It seems reasonable to conclude from such literature studies that many viruses that enter the ozone reaction chamber in a typical reef aquarium application may be killed by ozone or its byproducts. Larger pathogens, however, are likely much more resistant to ozone, and are unlikely to be killed. For such ends, a UV sterilizer may be more useful, but still may not be completely effective.
 
Ozone enhances the quality of the water. Ozone is a fresh gas, present in the higher realms of the atmosphere where it is purer. The same kind of purity is brought into the reef tank when ozone is used in it. Ozonized water is odorless, colorless and tasteless.

That is meaningless nonsense, IMO. It sounds like a marketing line with no way to debate it as the words do not convey anything clear. You don't sell such equipment, do you?

At the very least, you'd have to define what you mean by quality and fresh. You'd also want to understand the difference between sterilizing applications performed by fresh water suppply companies, and the use in a reef tank.
 
Ozone does not leave chemical wastes in the water when it is passed through it. That means, when water is ozonized, there will be effectively less amount of wastes and chemical discharges into the water.

That is simply incorrect. Ozone leaves terrible toxic compounds in seawater if you are not careful to remove them with activated carbon.. I detail them here:

http://reefkeeping.com/issues/2006-03/rhf/index.php#15

Toxicity of Ozone Produced Oxidants (OPOs)



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Two sorts of toxicity studies of ozone produced oxidants (OPOs, such as bromate, hypobromous acid, etc.) are relevant to reef aquarists. The first involves the testing of seawater that has been exposed to ozone, and the second involves the testing of specific compounds dissolved in seawater that are known to form when using ozone. Most of the OPOs are unstable, and so have few or no specific toxicity studies. Bromate (BrO3-) is the notable exception, and its toxicity is examined in the next section.

Much of the study of OPOs stems from applications slightly different from aquaria, and such studies must be viewed in that light. Often they relate to aquaculture facilities, where ozone is used at high doses to sterilize the water. Other studies are done on the disinfection of wastewater using ozone, another high dose application. Bear in mind that OPOs in reef aquarium applications will be at a maximum of about 0.3 ppm in typical reaction chambers, and will be lower (hopefully, much lower) once the water passes over activated carbon (assuming it does) and finally enters the aquarium. The concentration of OPO is always given in terms of the weight of ozone that produces that amount of oxidant.

In terms of the toxicity of ozonated seawater itself, one group concluded that fish were relatively insensitive to OPOs:

"Ozonation of estuarine or marine waters can produce significant amount of bromate…Toxicity studies showed that the concentrations of bromate which theoretically could be formed in an ozonated discharge were not toxic to the early life stages of striped bass (Morone saxatilis) and juvenile spot (Leiostomus xanthurus)."50

Larvae are, in general, more sensitive to OPOs than are eggs,51 adults or juveniles.52 Japanese flounder eggs were found to be impacted by OPOs to the extent that 50% did not hatch after one minute of exposure to 2.2 ppm OPO. Larvae aged 3-15 days were killed to the extent of 50% in 24 hours at 0.02-0.05 ppm OPO. Larvae aged 44 days were killed to the extent of 50% in 24 hours at 0.15 ppm OPO. In this case, the larvae were shown to have damage to their branchial tissues.53

The eggs and larvae of Japanese whiting (Silago japonica) also have been tested for toxicity by OPOs. In this case, half of the eggs and larvae died in about 24 hours when exposed to 0.18 and 0.23 ppm OPOs, respectively.54

Certain microalgae are also relatively insensitive to OPOs (perhaps to the disappointment of many aquarists). The growth of the microalgae Tetraselmis chuii was found to be unaffected at levels up to 0.7 ppm.55 At 1 ppm, growth was impacted negatively.

Toxicity tests of OPOs on shrimp show them to be less sensitive than fish. Penaeus chinensis and Paralichthys olivaceus were found to live up to 48 hours at OPO concentrations of more than 1 ppm, while Bastard halibut (fish) in the same study lived only three hours at 1 ppm and 48 hours at 0.13 ppm.56

As for other organisms, the damage to the American oyster (Crassostrea virginica) by OPOs varied with their age. Even for adults, fecal matter accumulation was reduced at OPO levels as low as 0.05 ppm.57

The effect of OPOs on rotifers (Brachionus plicatilis) has also been determined.58 No effect on survival was seen at less than 0.22 ppm OPO, but effects became significant above that level. The authors point out that bacteria and other pathogens can be killed at that level, so rotifer cultures can be used with that amount of continuous ozone to reduce bacterial contamination.

Are these levels of OPO toxicity important to reef aquarists? That is difficult to answer without knowing the levels that are attained in reef aquaria. In a typical ozone application in reef aquaria that might produce 0.1-0.3 ppm OPO in a reaction chamber, the levels are quite significant compared to potential toxicity to fish larvae and other organisms at as little as 0.02-0.05 ppm. After passing the reactor's effluent over activated carbon, the OPO concentrations should be much lower, but exactly how low is unclear and will vary considerably in different setups.

Toxicity of Bromate



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The toxicity of ozone and bromate at "natural" levels in the ocean has been assessed and usually found to be minimal.59 Few studies have examined the toxicity of excess bromate itself to marine organisms.60 One review article concluded:

"Bromate toxicity tests on marine animals indicate the levels of bromate produced by chlorination or ozonation of power plant cooling waters are not acutely toxic. The LC50 ranged from 30 ppm bromate for Pacific oyster, Crassostrea gigas, larva to several hundred ppm for fish, shrimp and clams."9

One individual study showed that Pacific oysters (Crassostrea gigas) had abnormal larval development at bromate levels of 30-300 ppm.61,62 Fertilized eggs of the oyster Crassostrea virginica were killed at 1 ppm.63 The clams Protothaca staminea (littleneck) and Macoma inquinata (bent-nosed) were killed by 880 ppm.64 The marine dinoflagellate Glenodinium halli showed changes in population growth at 16 ppm.65 The marine microalgae Isochrysis galbana showed changes in population growth at 8 ppm.65 The marine diatom (Skeletonema costatum) showed changes in population growth at 0.125 to 16 ppm.65 The marine diatom Thalassiosira pseudonana showed changes in population growth at 16 ppm.65 The salmon Oncorhynchus keta was killed at 500 ppm and the perch Cymatogaster aggregata at 880 ppm.64 Two shrimp (Pandalus danae and Neomysis awatschensis) were killed at 880 and 176 ppm, respectively.64

Are these levels of toxicity important to reef aquarists? That is difficult to answer without knowing the levels that are attained in typical reef aquaria. The one study in the literature of bromate in a seawater aquarium, described above, showed the accumulation of up to 0.6 ppm bromate, although that was an application in which ozone was used for disinfection, so it was used at high doses. That level is high enough, however, to cause toxicity to certain organisms, but not others. In a typical reef aquarium ozone application, the bromate in the aquarium water is likely to be much lower. How much lower will likely depend on the way it is used, especially the dose and whether it is passed over activated carbon before entering the aquarium. It may also depend on the other husbandry practices used in the aquarium, because some procedures (such as denitrification) may reduce bromate levels. In any case, the potential toxicity data for bromate support the practice of using activated carbon after ozone exposure.
 
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