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In a recent article,1
Ron Shimek showed that two salt mixes and natural seawater
were more conducive to the development of sea urchin embryos
than were two other salt mixes and the water from two reef
aquaria using one of them. In that article, Shimek suggested
that elevated metal levels, such as copper, could have been
responsible. The two salt mixes with poor development are
reported to have higher levels of a number of potentially
toxic metals than the other two salt mixes or natural seawater.
While there may be other explanations for
the observed differences, including ammonia, nitrite, pH,
organic compounds present intentionally or as impurities,
and the elevation or depletion of many different inorganic
chemicals, the hypothesis concerning toxic metals is quite
reasonable. As a result of that article, as well as earlier
ones that showed the elevated levels of certain metals in
reef aquaria and salt mixes,2,3
many aquarists have become interested in finding out what
they can do to lower the toxic metals concentrations in their
aquaria. This article starts with the premise that toxic metals
are responsible for the biological effects that Shimek observed,
and explores what options aquarists have to solve the problem.
Some have assumed, seemingly incorrectly,
that if they use natural seawater or one of the salt mixes
shown to have lower metals, that the problem will be solved.
Unfortunately, some of the things that aquarists need to do
in maintaining reef aquaria may well be a primary source of
metals. Specifically, the foods and calcium and alkalinity
supplements that aquarists use are a big source of metals
to reef aquaria. The complication of these inputs may make
it difficult, if not impossible, to maintain an aquarium with
natural levels of these metals. Both foods and supplements
have enough metals in them to take natural seawater to the
levels found in the "high metals" salt mixes in
a fairly short period of time. In evidence of this possibility,
the one aquarium in Shimek's study of reef aquaria that used
natural seawater had amongst the highest levels of many of
these toxic metals.2 Habib
Sekha has also indicated that he has obtained similar results
on two other aquaria using natural seawater (pers. comm.).
That is, the copper and nickel levels were equivalent to those
levels found by Shimek in aquaria using artificial salt mixes
such as Instant Ocean.2
The copper levels in these three aquaria using natural seawater
are also comparable to the levels found in my own tank using
only Instant Ocean salt mix (10-13 ppb copper).
Additionally, one would expect that the
total input of these different metals would be very different
between reef aquaria. And yet, all of the aquaria in the study
mentioned above had copper concentrations within a factor
of two of each other.2 That
suggests to me that the controlling factor is more likely
to be export than import, and this possibility and how it
impacts the actions of aquarists wanting to maintain aquaria
with low metals is discussed at the end of this article.
In this article, I will focus on those
potentially toxic metals that have been found to be elevated
in operating reef aquaria,2
including copper, nickel, zinc, molybdenum, and cobalt. I
will also use the premise that aquarists want to maintain
an aquarium with a lower concentration of such potentially
toxic metals, and will provide some guidance and general information
on how aquarists might usefully go about operating aquaria
in that fashion. In some cases, these techniques will relate
to many metals, and in some cases they will only apply to
certain metals, such as copper.
Using methods described in this article,
and other articles to follow that will attempt to further
quantify how effective these suggestions are, some aquarists
can potentially begin to operate aquaria with much lower levels
of such metals. Whether such a reduction will have important
advantages that aquarists will appreciate can only be demonstrated
when reef aquaria are operated under such low metal concentrations
and compared to reef aquaria operated in more traditional
means. Once that has been accomplished, then aquarists will
be able to look at the results and determine for themselves
if this is a necessary, or at least a prudent action for them
to adopt.
To begin, however, it is important to
note that there are no simple solutions to this potential
concern. The two obvious ways to consider lowering the metals
concentrations in aquaria are to add less, and export more.
There are things that aquarists can do to immediately reduce
additions of toxic metals, and these will be detailed in this
article. Whether the "normal" export systems (skimming,
growth and harvesting of macroalgae, activated carbon, etc.)
can be useful may in part depend on how much of an input load
for which they are expected to compensate. Other "chemical
filtration" systems have been promoted to hobbyists for
this purpose, but in the end may not be successful in reducing
metals levels below those already present in many aquaria,
regardless of the inputs. Still other approaches to export,
such as binding metals to calcium carbonate media, are more
speculative and will be mentioned as suggestions that will
be reported on in more detail in future articles.
In order to understand how and why certain
methods of dealing with metals may work (or not), we also
need to know the nature of these metals in aquaria. Many aquarists
will naturally think of these metals as being like the more
familiar calcium ion, floating free through the water on its
own. The true situation for many of these metals is, however,
much more complicated. It is expected that more than 99.9%
of the copper ions present in the water column of reef aquaria
are attached to something else, and what they are bound to
has a big impact on how they behave. Consequently, before
getting into metal removal methods, this article will describe
what forms the metals take in seawater, and what forms they
are expected to take in reef aquaria.
Metals in Seawater and Aquaria
Different metals take different forms in
seawater. Some exist primarily as free metal ions in solution.
Of those that aquarists are most familiar with, sodium (Na+),
potassium (K+), calcium
(Ca++) and magnesium (Mg++)
fall into this category.4
All of these may, to some extent, form complexes with other
ions and organic materials, but the free ion tends to predominate
in seawater and in typical aquaria.
The metals that we are most concerned about
in this article, however, have much more complex behavior.
Copper, for example, exists in a multitude of forms.4
In natural seawater, it has recently become clear that copper
is almost completely bound by organic materials.5
Many of these organics are called chelators. A chelating agent
is one that can grab onto the copper from two or more directions
at once.
In natural seawater, these organics take
many forms. Humic and fulvic acids, for example, are two of
the most important types of materials that bind copper and
other metals in seawater.6
They are also known to greatly reduce the toxicity of metals
because in many cases it is the free copper that is the most
toxic.5 These classes of
organic materials comprise what remains when proteins, carbohydrates,
and many other naturally occurring organic materials are biodegraded
to a state where further degradation is very slow. Humic and
fulvic acids (the distinction between the two being just that
humic acids are more hydrophobic than fulvic acids) have a
wide range of structures and physical properties. They typically
are high molecular weight organic acids, with sizes ranging
from 500 to 10,000 daltons (grams/mole). They can also be
parts of larger assemblies of organic materials that would
be called colloidal (very small particulates) rather than
"dissolved". The humic and fulvic acids are comprised
of amino acids, sugars, amino sugars, fatty acids, and other
organic functional groups. Different localities and depths
in the ocean have different amounts and specific types of
these organic materials present. Typical values for the total
dissolved organic carbon are on the order of 1 ppm carbon
for tropical surface seawater.6
Humic substances typically account for about 10-20 % of that
total, and fulvic substances can account for more than 50%.6
Within these structures will be sites where
several carboxylic acid, phenolate, thiolate, amino, or other
metal-binding groups come together. These sites are where
a metal ion will be most strongly bound. Structurally, it
is hard to show a "typical" humic acid binding to
copper, but the structure below shows one possibility:
Figure 1. A schematic of a copper ion (Cu++;
shown in red) being
chelated by a naturally occurring humic acid (shown in green).
In this figure, the central positively-charged
copper ion (Cu++) is chelated by the larger humic
acid shown in green. It is bound ionically by two negatively
charged carboxylic acid groups and complexed by one neutral
amino group. Together these three groups may hold the copper
ion more strongly by many orders of magnitude more strongly
than could any individual binding group.
In the very extensive book "Biogeochemistry
of Marine Dissolved Organic Matter",6
it is stated:
"It is now widely accepted that the chemical speciation
of most bioactive metals in seawater is regulated by strong
complexation with natural organic chelators
The cycling
of bioactive metals therefor is intrinsic to the behavior
of this subset of organic constituents."
And also:
"The collective findings establish that a significant
component of bioactive, or nutrient, metals (Mn, Fe, Co, Ni,
Cu, Zn, Cd) occur in the colloidal phase along with numerous
other trace metals."
Free Metal Ions
In seawater, copper is expected to be bound
to organic materials. In one recent study of copper in natural
seawater, more than 99.97% was bound to organic materials.5
Other metals, such as zinc, may not be as extensively chelated.
In aquarium water, where the level of both metals and organics
can be higher than in seawater, the percentage bound to organics
may be even greater. Nevertheless, unchelated metals are very
important. In the case of copper, for example, the unchelated
copper ions may represent that portion of the total copper
that is toxic to many organisms.5
These inorganic forms of copper and other metals are also
expected to predominate in freshly mixed artificial salt water
that has not been exposed to sources of organic materials.
Assuming that the organism does not take
up the entire organic molecule to which the metal is attached
(and many humic acids are known to be poorly taken up due
to their refractory chemical nature6),
then chelated metals are often much less toxic than unchelated
metals. In seawater, for example, the speciation of copper
(i.e., whether and how it is chelated) is often much more
important for understanding overall toxicity than is the total
copper concentration.7
The portions of metals in seawater that
are not bound to organic materials are very complicated in
their own right. Copper, for example, takes at least 7 different
soluble inorganic forms in seawater.4
It is comprised of Cu++
(3.9% of the inorganic copper), CuOH+
(4.9%), Cu(OH)2 (2.2%), CuSO4
(1%), CuCO3 (73.8%), Cu(CO3)2--
(14.2%) and Cu(HCO3-
)+ (0.1%). Similar complications
hold for many of the metals that we are concerned with in
this article.4
Speciation and its Effect on Binding Metals in
Aquaria
Since these metals take many different
forms in aquaria, one must consider the nature of these different
forms when developing methods for removing them. For example,
metal ions such as Cu++
or Ni++ will never absorb
at the air/water interface to permit selective removal by
skimming. However, if the same metals were bound to an organic
material that itself adsorbed to the air/water interface,
the metals might well be exported by skimming. Similar concerns
relate to claims about metal removal using activated carbon,
polymeric ion exchange and complexation resins, and binding
to inorganic materials like iron oxides and calcium carbonate.
In fact, any proposed method of metal removal will be significantly
impacted by the nature of the metal speciation. Depending
on what is added to any particular aquarium, the speciation
may actually vary from aquarium to aquarium, potentially making
generalizations about them less useful.
Further, any experiment that purports to
show how well something works must be carried out under conditions
of the real speciation present in aquaria. Tests run in artificial
salt water (or worse yet, fresh water) are not necessarily
of any use in predicting efficacy of metal removal if not
carried out in the presence of the typical organics present
in aquaria. So when you see products make claims about their
ability to remove metals, be skeptical unless you understand
what conditions the claims relate to.
Input of Metals: Foods
If the goal is to reduce metals, then looking
at the foods that you feed can be important. It will be impossible
to eliminate all additions of metals this way, because all
marine-sourced materials contain significant amounts of metals
that they absorbed when growing in the ocean. Some of these
metals are used by the organisms involved, and some are just
incidentally accumulated. Nevertheless, there are some things
that you might consider when selecting foods if you want low
metals.
It turns out that there has been a fair
amount of study of many foods for certain metals because they
impact human health in various ways. For healthy people looking
to ingest adequate copper levels in food, the USDA recommends
shellfish, among other things, because they have a naturally
high level of copper and zinc.7,8
Some fish and shellfish may also be unusually high in many
metals (including copper, zinc, cadmium, mercury, and lead)
because of local pollution in the areas where they are harvested.9,10
People with Wilson's disease have problems
dealing with elevated copper levels, and they need to restrict
dietary copper. At a website
designed for people with this condition is a table
listing the copper levels in many foods, including many that
we feed to our aquaria (Table 1).
Table 1. The copper concentrations present in certain
shellfish.
|
Food
|
Copper
Concentration (ppm wet)
|
|
Fish
|
0.61
|
|
Scallops
|
0.27
|
|
Clams
|
6.1
|
|
Crab
|
7.4
|
|
Shrimp
|
1.8
|
|
Oysters
|
2.9
|
|
Mussels
|
4.8
|
|
Lobster
|
37.0
|
From this table it is clear that one can
select lower copper foods when shopping at the grocery store.
Scallops and shrimp, for example, would be much better choices
than clams, crab, or lobster. Also, the viscera of squid and
crabs contain much more in the way of heavy metals than does
muscle tissue.10 Over the
course of a year, these contributions really add up. If you
add 5 grams of each of the foods in Table 4 to a 100-gallon
aquarium every day, the addition over a year amounts to 178
ppb of copper using lobster and 1.3 ppb of copper using scallops.
For comparison, the amount of copper in the salt mixes described
in Shimek's article1 as
being high in metals are on the order of 100-200 ppb copper
(but only 18 ppb copper in an earlier article2),
and those low in copper were 1-40 ppb copper (for comparison,
my aquarium using only Instant Ocean salt mix presently has
10-13 ppb copper). So obviously, the choice of foods can potentially
make a big impact on the copper levels.
Many aquarists feed commercial foods to
their aquaria, rather than fresh seafood. In a study of the
amounts of different elements in certain foods,11
Shimek presented the results shown in Tables 2 and 3. While
none of these foods appears as high in copper as lobster,
lancefish is close and the differences between the various
foods are significant. In these tables I have highlighted
those values that stand out as unusually high in red and unusually
low in green. Bear in mind that some of these foods contain
substantial water, and so are naturally more "dilute."
For that reason, I included the first line in each table that
shows the calories/gram for each food. In this sense, it is
easy to see that the "wet" foods are about 4-5 times
less concentrated than the dry foods, so in looking at metals,
their concentrations need to be multiplied by 4-5 to get equivalent
values in terms of actual dosing.
Based on this metals analysis alone, and
no other nutritional properties, the Tahitian Blend would
seem to be a good overall choice if lower metals were a significant
goal (However, Eric Borneman has indicated that Tahitian Blend
is a plant material suspension that is of a particle size
that will be unusable by many organisms (pers.
comm.)). If we knew exactly what specific
metal to be most concerned with, the choice might well be
different.
Table 2. The metals content of a variety of commercial
foods (ppm as is).
|
Metals
|
Formula
One
|
Formula
Two
|
Prime
Reef
|
Lancefish
|
Brine
Shrimp
|
Plankton
|
|
Calories/gram
|
0.8
|
0.8
|
0.8
|
0.9
|
0.3
|
0.7
|
|
Aluminum
|
15.00
|
15.00
|
11.00
|
9.80
|
120.00
|
8.10
|
|
Arsenic
|
<0.50
|
<0.46
|
<0.52
|
2.10
|
<0.44
|
<0.42
|
|
Barium
|
0.55
|
0.73
|
0.72
|
<0.025
|
0.72
|
0.63
|
|
Cadmium
|
0.08
|
0.10
|
0.07
|
<0.02
|
<0.02
|
<0.02
|
|
Chromium
|
0.28
|
0.07
|
0.12
|
1.10
|
0.52
|
0.18
|
|
Cobalt
|
0.10
|
0.10
|
0.12
|
0.11
|
0.11
|
0.07
|
|
Copper
|
2.30
|
1.80
|
2.00
|
24.00
|
1.30
|
10.00
|
|
Manganese
|
4.40
|
13.00
|
14.00
|
3.40
|
10.00
|
0.62
|
|
Molybdenum
|
<0.25
|
<0.23
|
<0.26
|
<0.25
|
0.22
|
<0.21
|
|
Nickel
|
<0.25
|
<0.23
|
<0.26
|
<0.25
|
0.32
|
<0.21
|
|
Tin
|
0.72
|
0.70
|
0.70
|
2.40
|
0.34
|
0.38
|
|
Zinc
|
37.00
|
99.00
|
120.00
|
30.00
|
6.90
|
5.80
|
Table 3. The metals content of a variety of commercial
foods (ppm as is).
|
Metals
|
Gold
Flakes
|
Tahitian
Blend
|
Saltwater
Staple
|
Nori
|
Golden
Pearls
|
|
Calories/gram
|
4.2
|
2.4
|
3.6
|
3.6
|
3.9
|
|
Aluminum
|
80.00
|
14.00
|
95.00
|
83.00
|
49.00
|
|
Arsenic
|
2.30
|
<0.17
|
2.70
|
25.00
|
3.70
|
|
Barium
|
5.20
|
0.83
|
6.90
|
5.90
|
1.70
|
|
Cadmium
|
<0.84
|
<0.02
|
1.30
|
1.20
|
0.90
|
|
Chromium
|
5.60
|
0.80
|
<0.05
|
1.30
|
1.00
|
|
Cobalt
|
0.80
|
0.40
|
0.80
|
1.30
|
4.40
|
|
Copper
|
10.00
|
6.50
|
9.50
|
3.00
|
22.00
|
|
Manganese
|
23.00
|
18.00
|
90.00
|
110.00
|
49.00
|
|
Molybdenum
|
1.80
|
0.19
|
0.61
|
<3.30
|
1.20
|
|
Nickel
|
1.80
|
0.30
|
0.25
|
<3.30
|
<0.23
|
|
Tin
|
2.50
|
1.40
|
1.40
|
4.80
|
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