|
Most aquarists have
some familiarity with nitrite. It is part of the "nitrogen
cycle" that takes place in most aquariums, and so is
one of the first encounters that many aquarists have with
their aquariums' chemistry. The marine aquarium hobby is replete
with commentary about nitrite, some of which is, unfortunately,
incorrect or misleading. Its toxicity in marine systems is
far lower than in freshwater systems. Nevertheless, many aquarists
incorrectly extrapolate this toxicity to reef aquariums and
suggest that any measurable amount of nitrite is a concern.
In reality, nitrite probably is not toxic enough to warrant
measuring in most marine systems. This article serves to provide
a backdrop for that opinion by addressing what nitrite is,
where it comes from, where it goes, the mechanisms by which
it can be toxic and the evidence for its toxicity (or lack
thereof) in typical reef aquariums.
Contents
Nitrite in the Ocean
Nitrite (NO2-) is a fairly
small ion, consisting of a central nitrogen atom with two
attached oxygen atoms in a bent configuration (Figure
1). One of the oxygen atoms carries a negative charge.
More correctly, the nitrite ion has two oxygen atoms that
are capable of carrying the negative charge, and in reality,
the solvated
ion in solution probably has two identical oxygen
atoms, each with a partial negative charge. Nitrite is a fairly
strong acid, and becomes protonated
to nitrous acid (HNO2) only
as the pH drops below 4 (pKa = 3.35).
In the ocean, nitrite typically varies in concentration from
very low levels to about 0.2 ppm.1,2
The higher end of this range is typically found only in anoxic
layers deep below the surface. Nitrite in surface Atlantic
and Caribbean seawater has been reported to range from 0.000005
to 0.00002 ppm,3 and a series
of measurements in the South China Sea and the Philippine
Sea showed an average of 0.00002 ppm.4
Nitrite is sometimes elevated in the water buried in sediments
due to decomposing organic material, and the fact that such
pore water is often anoxic. In natural coral reef sediments,
however, nitrite can still be very low
(much lower than ammonia (NH3) and
nitrate
(NO3-), which can rise to
as high as 0.7 ppm).5
|
Figure 1. A nitrite ion (left) comprised of a
central nitrogen atom (blue) and two oxygen atoms (red),
one of which carries a negative charge. A water molecule
(H2O) is shown on the right for
comparison.
|
Where Does Nitrite Come From?
Most aquarists associate
nitrite with the traditional "nitrogen
cycle." In this process, bacteria convert ammonia
into nitrite and then into nitrate by oxidizing it. The bacteria
gain chemical energy in this fashion, just as other organisms
(from bacteria to people) gain energy by oxidizing carbon
compounds (such as ethanol, CH3CH2OH)
into more oxidized versions, such as carbon dioxide (CO2).
This process can be described as starting with ammonia (NH3)
excreted by animals or by bacteria and other organisms that
are consuming organic compounds containing nitrogen, such
as proteins. The ammonia from the water column is taken up
by bacteria and is oxidized in a step-wise fashion, first
to nitrite:
NH3
+ 3/2
O2
ŕ
NO2- + H+
+ H2O
And then to nitrate
(possibly in bacteria species other than those that produce
the nitrite):
NO2-
+ ˝ O2 ŕ
NO3-
During an aquarium's initial setup, few of these ammonia-
and nitrite-oxidizing bacteria are present. As the ammonia
accumulates, bacteria that utilize it increase in population.
As that occurs, they consume the initial ammonia spike, and
a nitrite spike results. Then, the nitrite-oxidizers take
advantage of the nitrite spike, increase in population, and
consume the nitrite, thereby producing nitrate.
After some period of time (often a few weeks), the bacterial
action begins to equilibrate, and neither ammonia nor nitrite
is present in high concentrations. This doesn't mean that
a lot of each is no longer being produced, only that they
are consumed as fast as they are produced, leaving a low steady-state
concentration. In most reef aquaria, the steady-state concentrations
of both ammonia and nitrite are quite low (less than 0.1 ppm),
and often are below the detection limits of many test kits.
What happens when an aquarium is initially set up, however,
is not necessarily what happens later. Many organisms in reef
aquaria consume ammonia and nitrite directly, and metabolize
it into organic matter. Macroalgae, for example, can take
up ammonia directly, and many species actually take up ammonia
preferentially to nitrate. Consequently, in a reef aquarium
such as mine where most of the nitrogen export is via macroalgae,
little nitrite may be produced in the first place. I have
no way of knowing how much of the nitrogen added to my aquarium
from foods enters the macroalgae as ammonia, and how much
in other forms (such as nitrite or nitrate), but it is very
likely that not all of the nitrogen added passes through a
nitrite stage before becoming part of the macroalgae.
In addition to the standard nitrogen cycle, there are other
ways that nitrite can be produced. One of these ways is by
photolysis
of nitrate. That is, nitrate can break apart when exposed
to UV light, producing nitrite and hydroxyl radical (OH).6,7
NO3-
+ H2O + UV ŕ
NO2- + 2 OH
Another method of nitrite synthesis can occur inside organisms,
although this nitrite may not be released back into the water.
For example, nitrite can be produced from nitrate internally
by corals (e.g., Pocillopora damicornis) and macroalgae
(e.g., Ulva lactuca).8
Where Does Nitrite Go?
Nitrite can take a number of different
pathways in the ocean. Many organisms can directly take up
nitrite. Such uptake has been demonstrated in anemones (Condylactis
sp., for example, take up nitrite, possibly for its symbionts),9
diatoms (Eucampia zodiacus)10
and zooxanthellae isolated from a variety of species (Zoanthus
spp., Tridacna crocea, Seriatopora hystrix,
Montastrea annularis, Porites furcata and Stylophora
pistillata).11
Nitrite can also be broken down by exposure to UV light,
producing nitric oxide (NO), hydroxyl radical (OH) and hydroxide
ion (OH-).6,7,12
NO2-
+ H2O + UV ŕ
NO + OH + OH-
In a laboratory situation with nitrate-free seawater with
no organisms present, ambient sunlight can reduce the nitrite
concentration by 2-15% per day.12,13
The primary products of this reaction are nitric oxide (NO)
and hydroxyl radical (OH). Both of these compounds are chemically
and biologically active, so this reaction may be important
to a number of biochemical pathways in the ocean and in various
organisms. The effect of nitric oxide is discussed in more
detail later in this article.
In the anammox
process, bacteria use nitrite to oxidize ammonia, producing
N2:
NH3
+ NO2- + H+
ŕ
N2 + 2H2O
The importance of this process in marine sediments has long
been unknown. In recent studies, however, it has been shown
to be important in some circumstances.14-17
In two continental shelf sites, the conversion of ammonia
to N2 by this pathway produced 24%
and 67% of the total N2 produced. In
a eutrophic
bay, however, this process was negligible compared
to ordinary denitrification (the conversion of nitrate into
N2 when the nitrate is used as an electron
acceptor for degradation of organic material in low oxygen
situations). A different study showed that this process accounted
for between 4% and 79% of the N2 produced
in coastal sediments.
Finally, in a reef aquarium, nitrite can be removed by reaction
with ozone, presumably to produce nitrate.18
NO2-
+ O3 ŕ
NO3- + O2
Effects of Nitric Oxide
As described above, nitrite can break
down under UV light to produce nitric oxide. Consistent with
this process, nitric oxide is found to increase during the
day and to decrease at night.12
Nitric oxide itself has a variety of different biological
effects. Exposure to different concentrations of supplemental
nitric oxide was found to speed or inhibit the growth of four
species of phytoplankton (Skeletonema costatum, Dicrateria
zhanjiangensis nov. sp., Platymonas subcordiformis
and Emiliania huxleyi) , consistent with its known
role as a growth regulator in terrestrial plants.19
Nitric oxide also may play a role in the symbiosis of certain
cnidarians with dinoflagellates. An enzyme that produces nitric
oxide has been found in the cnidarian Aiptasia pallida.
This enzyme is apparently downregulated when the organism
goes into acute heat shock, and inhibitors of the enzyme cause
retraction of the tentacles, as is observed under heat shock
conditions.20 Further, addition
of nitric oxide donors to the system prevents this retraction
of tentacles. Whether this process has anything to do with
nitrite or nitric oxide in the water column is not clear.
The effects, if any, that nitric oxide and this reaction
from nitrite in particular might have on reef aquaria is unclear.
Nitric oxide effects on marine organisms is an active area
of research, and a greater understanding of it is expected
in the future. Whatever the effects are, however, any effect
attributable to NO produced from nitrite may be most pronounced
in a newly cycling reef aquarium (where nitrite is elevated)
and when a UV system is in use.
How is Nitrite Toxic?
Nitrite can be toxic in a number of
ways.21 Freshwater fish
rapidly take up nitrite through their gills, leading to high
levels in their bodies. In freshwater fish, nitrite taken
up through the gills can compete with chloride for the same
uptake proteins, so in some cases of elevated nitrite the
fish can suffer from chloride depletion. It has been observed
that some freshwater fish (e.g., bluegill; Centrarchidae:
Lepomis macrochirus) do not take up chloride via their
gills, and these species are notably resistant to nitrite
toxicity.22
The internalized nitrite then causes a number of internal
disturbances, including loss of potassium from certain tissues
(such as skeletal muscle) and the oxidation of hemoglobin
into methemoglobin, which reduces the blood's oxygen carrying
capacity. This can cause reduced tissue oxygenation, hyperventilation
and heart rate increases. Many other biochemical pathways
become altered as well, including steroid synthesis, vasodilation
(blood vessel enlargement) and changes in internal levels
of ammonia and urea. Nitrite detoxification in freshwater
fish is accomplished by direct nitrite excretion and by internal
conversion of nitrite into nitrate.23
Marine species are less susceptible to nitrite toxicity because
chloride (at 19,350 ppm in seawater) outcompetes nitrite for
the same uptake mechanisms. Nevertheless, it is possible for
some marine fish to take up nitrite via both their gills and
their intestines after swallowing seawater. For example, when
exposed to 46 ppm nitrite in seawater, the European flounder
(Platichthys flesus) takes up 66% of its nitrite via
intestinal routes.24 Further,
its internal nitrite concentration was found to remain below
the ambient nitrite level in the water. At these concentrations,
there was some alteration of internal biochemical parameters
(such as an increase in methemoglobin levels from 4% in nonexposed
fish to 18% of hemoglobin in exposed fish). Nevertheless,
there were no mortalities under these conditions, and the
difference between this result and what is often observed
in freshwater fish at similar nitrite concentrations is attributed
to differences in their internal nitrite concentrations.
How Toxic is Nitrite to Fish?
For the reason described above, nitrite
is considerably more toxic to many freshwater fish (Table
1) than it is to most marine species (Table
2). The data in these tables are primarily the LC50,
which is the concentration at which 50% of the test organisms
die (24-h LC50 is the concentration
that kills half of the tested organisms within 24 hours).
As Table 1 shows, some freshwater fish can die at nitrite
levels below 1 ppm. This toxicity is the reason many aquarists
worry about nitrite in aquaria. It can be a significant problem
in freshwater aquaria. Tests in marine species, however, showed
the toxicity to be much lower. None of the thirteen marine
fish species for which I could find nitrite toxicity data
had LC50 values below 100 ppm, and
half had LC50 values of 1,000 - 3,000
ppm or more.
Death is, of course, a very crude indicator of toxicity.
An aquarium's nitrite level should not come anywhere close
to the LC50 value, because less severe
toxicity can occur even at levels below that. In the previous
section, I showed data on one marine species in which biochemical
effects could be detected at levels well below concentrations
that caused death. We saw, for example, a rise in methemoglobin
at values as low as 46 ppm nitrite. However, the point remains
valid that marine species are orders of magnitude less susceptible
to the effects of nitrite than are many freshwater species.
The marine aquaculture industry often uses a rough guideline
that the safe rearing level of many compounds is a factor
of 10 or less than their LC50.30
In examining ammonia, nitrite and nitrate toxicity in marine
species, one might think to look at the effects on larval
fish to see if they are more sensitive. In examining the incidence
of the larvae's first feeding after hatching, and the 24-h
LC50, it was found that for seven different
marine species, only ammonia was found to be toxic at concentrations
that might possibly be encountered in aquaculture facilities.25
Table 3 brings out the distinction between
freshwater and seawater organisms most clearly. In these tests,
two fish and one shrimp species that are able to live in both
freshwater (or brackish water) and seawater were tested for
toxicity at different salinities. At least for these three
species, it is clearly shown that nitrite is much more toxic
in freshwater (or at lower salinity) than in seawater, even
to the same species.
In the only published
article26 that I could
find showing toxicity tests to typical reef aquarium fish,
Tom Frakes and Bob Studt exposed tank-raised clownfish (Amphiprion
ocellaris; Figure 2) to nitrite concentrations
ranging from 0 to 330 ppm in artificial seawater. Two of five
fish died after a few days at 330 ppm,
giving an LC50 not appreciably different
from the other species listed in Table 1. At 33 ppm (the next
dose down from 330 ppm), the fish were lethargic and breathing
with difficulty, but otherwise experienced no lasting problems.
At 3.3 ppm nitrite no effects were observed.
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Figure 2. This female clownfish (Amphiprion
ocellaris) in my aquarium would likely experience
lethal effects of nitrite toxicity at levels above 300
ppm nitrite.
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One of the difficulties with interpreting toxicity issues,
as related by hobbyists who claim to have seen nitrite toxicity
in marine fish, is the possible presence of ammonia. In any
aquarium with elevated nitrite, the ammonia level also may
be elevated. Since ammonia is known to be very toxic to marine
fish (LC50 value below 1 ppm), on the
aquarist must ensure that the observations are not flawed
by such contaminants. In all of the toxicity
tests described above, nitrite is added directly to the seawater,
and ammonia would not be expected to be present at significant
concentrations, whereas in aquariums the levels of the two
materials are not independent of one another.
|
Table
1. Toxicity of Nitrite to FRESHWATER
Fish.
|
| Freshwater
or Brackish Species |
Effect
|
Mean
Concentration
(ppm; result is the mean of between 1 and 98 studies
for each species)
|
Reference27
|
Zambezi
barbell
Clarias gariepinus |
LC50
|
1,257
|
|
Catfish
Clarias lazera |
LC50
|
6.1
|
|
Grass
carp, white amur
Ctenopharyngodon idella |
LC50
|
2.7
|
|
Zebra
danio
Danio rerio |
LC50
|
130
|
|
Western
mosquitofish
Gambusia affinis |
LC50
|
1.5
|
|
Channel
catfish
Ictalurus punctatus |
LC50
|
7
|
|
Green
sunfish
Lepomis cyanellus |
LC50
|
160
|
|
Ide,
silver or golden orfe
Leuciscus idus |
LC50
|
27
|
|
Largemouth
bass
Micropterus salmoides |
LC50
|
140
|
|
Guadalupe
bass
Micropterus treculi |
LC50
|
187
|
|
Striped
bass
Morone saxatilis |
LC50
|
163
|
|
Striped
bass
Morone sp. |
LC50
|
49
|
|
Striped
catfish
Mystus vittatus |
LC50
|
23
|
|
Cutthroat
trout
Oncorhynchus clarki |
LC50
|
0.4
|
|
Rainbow
trout, Donaldson trout
Oncorhynchus mykiss |
LC50
|
1.6
|
|
Chinook
salmon
Oncorhynchus tshawytscha |
LC50
|
2.3
|
|
Flatfish
Paralichthys orbignyanus
(brackish water) |
LC50
|
38
|
|
Perch
Perca fluviatilis |
LC50
|
83
|
|
Fathead
minnow
Pimephales promelas |
LC50
|
9
|
|
Ayu
Plecoglossus altivelis |
LC50
|
1.8
|
|
Harlequinfish,
red rasbora
Rasbora heteromorpha |
LC50
|
60
|
|
Roach
Rutilus rutilus |
LC50
|
10
|
|
Red
drum
Sciaenops ocellatus
(brackish) |
LC50
|
44
|
|
Tilapia
Tilapia aurea |
LC50
|
16.2
|
|
Tench
Tinca tinca |
LC50
|
3,450
|
|
|
Table
3. Toxicity of Nitrite to Marine Organisms as a Function
of Salinity.
|
| Species |
Effect
|
Salinity(ppt)
|
Toxic
Concentration(ppm)
|
Litopenaeus
vannamei
(juvenile shrimp)30 |
144-h
LC50
|
15
|
201
|
| |
144-h
LC50
|
25
|
501
|
| |
144-h
LC50
|
35
|
845
|
| |
Safe
level for rearing
|
15
|
20
|
| |
Safe
level for rearing
|
25
|
50
|
| |
Safe
level for rearing
|
35
|
84
|
| |
Mullet
Mugil platanus31 |
96-h
LC50
|
23
times higher in seawater
|
| |
Chinook
salmon fingerlings
(Oncorhynchus tshawytscha)32 |
48-h
LC50
|
0
|
19
|
| |
|
35
|
>>
1070
|
How Toxic is Nitrite to Invertebrates?
Reef aquaria, obviously, contain far
more organisms than just fish. Unfortunately, however, the
number of organisms that have been examined for nitrite toxicity
is fairly low. Those selected for study are most often those
for which there is a significant aquaculture industry, such
as prawns. It turns out that most invertebrates studied are
fairly insensitive to nitrite (Tables 4-6). Because of the
nature of these studies, many endpoints besides death were
examined. These other endpoints include growth rates, "intoxication"
and feeding. Like fish, the invertebrates showed a wide range
of susceptibility to nitrite toxicity. Some showed little
effect at hundreds of ppm nitrite. The lowest noted effect
was a slowing of gonadal development in a sea urchin at 1.6
ppm, although it was feeding normally and surviving at 33
ppm nitrite.
|
Table
4. Toxicity of Nitrite to Crustaceans.
|
Crustaceans
(some shrimp may have been tested in freshwater since
they are often farmed that way) |
Effect
|
Mean
Toxic Concentration (ppm; result is the mean of
between 1 and 8 studies for each species)
|
Reference27
|
Blue
crab
Callinectes
sapidus |
LC50
|
82
|
|
Tiger
crab
Orithyia
sinica
(juvenile) |
Growth
rate
|
Decreased
at 150 ppm
Unchanged at 100 ppm
|
33
|
Fleshy
prawn
Penaeus
chinensis
nauplius third substage (N3) |
24-h
LC50 in 30 ppt seawater
|
76
|
34
|
Fleshy
prawn
Penaeus
chinensis
zoea second substage (Z2) |
24-h
LC50 in 30 ppt seawater
|
185
|
34
|
Fleshy
prawn
Penaeus
chinensis
mysis second substage (M2) |
24-h
LC50 in 30 ppt seawater
|
242
|
34
|
Fleshy
prawn
Penaeus
chinensis
postlarva twelfth substage (PL12) |
24-h
LC50 in 30 ppt seawater
|
222
|
34
|
Fleshy
prawn
Penaeus
chinensis
|
“Safe
level for Rearing” (10x below toxic effects)
|
4.5
|
34
|
Fleshy
prawn
Penaeus
chinensis
|
LC50
|
110
|
|
Redtail
prawn
Penaeus penicillatus
juveniles |
144-h
LC50
|
86
|
35
|
Indian
prawn
Penaeus
indicus |
LC50
|
14
|
|
Jumbo
tiger prawn
Penaeus
monodon |
LC50
|
16
|
|
Jumbo
tiger prawn
Penaeus
monodon
(adolescents in 20 ppt seawater) |
24
h-LC50
|
716
|
29
|
| |
48
h- LC50
|
634
|
|
| |
96
h- LC50
|
561
|
|
| |
144
h- LC50
|
460
|
|
| |
192
h- LC50
|
420
|
|
| |
240
h- LC50
|
348
|
|
| |
“Safe
level” for rearing (calculated)
|
35
|
|
Jumbo
tiger prawn
Penaeus
monodon
juveniles |
80-day
survival
|
100%
at 0 ppm
|
39
|
| |
80-day
survival
|
100%
at 6.6 ppm
|
|
| |
80-day
survival
|
96.7%
at 13 ppm
|
|
| |
80-day
survival
|
86.7%
at 26 ppm
|
|
| |
80-day
survival
|
70%
at 66 ppm
|
|
San
paulo shrimp
Penaeus
paulensis |
LC50
|
1424
|
|
Northern
white shrimp
Penaeus
setiferus |
LC50
|
173
|
|
Penaeidean
shrimp
Penaeus sp. |
LC50
|
170
|
|
|
Table
6. Toxicity of Nitrite to Other Marine Organisms.
|
| Other
Marine Organisms |
Effect
|
Mean
Effect Concentration (ppm)
|
Reference27
|
Cyanobacteria
Anacystis aeruginosa |
Reduced
Growth
|
70
|
|
Diatoms:
Gyrosigma spencerii
Navicula salinarum
Nitzschia dissipata
Nitzschia dissipata
Nitzschia sigma
Phaeodactylum tricornutum
Navicula cryptocephala |
Relative
Population Changes
|
700
|
|
Abalone
Haliotis
tuberculata ( Linnaeus) |
Growth
Rate
|
Stimulated
at 6.6 ppm
Safe (no effect) at > 16 ppm
|
37
|
Sea
urchin
Paracentrotus
lividus (Lamarck) |
Growth
Rate
|
Safe
(no effect) at 3-7 ppm | |