by: Tom M.
Although it makes up 90-95% of beer ingredients by weight, the majority of brewers rarely consider what type of water to use. How often have you seen a recipe in Zymurgy that lists what water was used to brew it? Probably never. Most brewers rarely give it much thought, and water is the least appreciated of beer ingredients. At the other extreme, many brewers spend hard earned dollars on spring water because they don’t fully understand how water affects flavor.
This
article will cover water chemistry from both a theoretical and a practical
'what does this stuff have to do with beer?' standpoint and hopefully benefit
advanced all-grain brewers by providing insight into water chemistry, and how
it can affect beer flavor. At the very
least, you can print this out and save it for when and if your interest grows
and you actually give a hoot about water chemistry. Extract brewers are strongly encouraged to relax, not worry, have
a homebrew, and skip to the extract brewing tips section.
Some of
the background information here can be found in a home brewing how-to book,
such as Dave Miller's 'The Complete Handbook of Homebrewing', Randy Mosher's
'The Homebrewing Companion', or John Palmer's 'How to Brew', my personal
favorite.
This
basic type information is usually scattered, and for me never gave a complete
picture to understand exactly what was going on. This article is my attempt to bring together information from a
large number of sources into one stand-alone water chemistry crash course that
also pre-calculates what you need to know for brewing with Nashville water.
First,
what is an ion? Basically it is a
mineral that has been dissolved in water into separate parts, called ions. For
example, salt is a crystalline solid of the chemical form NaCl until you put it
in water, and when dissolved, the Na and Cl separate and attach themselves to
the electrically polar water molecules.
Dissolved salt is then two separate ions: Na+, and Cl-. The plus sign refers to sodium's lack of an
electron and the negative sign means the chloride has an extra electron.
Water
soluble minerals are naturally found in soil deposits. As very soft rainwater makes its way down
through the soil, through underground caves, over rocks into streams or
aquifers it picks up some of the following dissolved minerals (ions) along the
way: calcium (Ca++),
carbonate (CO3--), chloride (Cl-), bicarbonate (HCO3-),
magnesium (Mg++), sodium (Na+),
sulfate (SO4-), and trace metals such as iron (Fe) and copper
(Cu).
I would
recommend contacting your local water authority to obtain a free water report
if you believe your water may be questionable for brewing or if you want to
check some of the things talked about here.
For private wells or springs, you may obtain a full water report from www.wardlab.com. Order Household Mineral Test W-6 ($15),
which tests for all brewing related ions and parameters.
Side Note:
The symbol Cl can cause confusion. In
water chemistry chloride (Cl-) is from a salt, and is not the
same thing as elemental chlorine (Cl2), which does not exist
in tap water, even when bleach is added.
This is another confusion - that bleach puts chlorine in water. Bleach or sodium hypochlorite (NaOCl) added
to water creates hypochlorous acid (HOCl).
The HOCl partially breaks up into H+ and OCl- in a chemical equilibrium,
as all acids do. The percentage of
which it breaks up is dependent on pH.
HOCl is a strong sanitizer, and OCl- is a strong oxidizer (bleaching
agent). OCl- is unstable and can break
up into Cl2 readily. HOCl is
also broken down rapidly at low pH levels into H2O and Cl2 gas,
which is why you should never mix acid and bleach. The reason is acids give up lots of H+ ions, which react with
HOCl and to yield water and chlorine gas.
3.0 CALCIUM CARBONATE (CaCO3)
The two
biggest players in all-grain brewing water are the ions calcium (Ca++)
and bicarbonate (HCO3-).
Top surface runoff dissolves CaCO3 out of limestone, but can
only dissolve enough CaCO3 to result in about 58 ppm of bicarbonate
(HCO3-), because this is the equilibrium saturation level
for HCO3- in
water exposed to air. The maximum amount
of HCO3- possible in water at equilibrium is directly
related to the partial pressure of CO2, or more simply, the % of CO2
in the air we breathe.
In
underground situations, respiring bacteria can increase the CO2
level to an equilibrium partial pressure of 60 times as much as surface water,
and this allows a much higher amount of bicarbonate (HCO3-)
to be dissolved. For example, the
famous brewing water of Burton on Trent is from underground sources, and one
source is reported as having over 300 ppm of HCO3-.
Equilibrium
is analogous to the most sugar that will dissolve in a liquid at a given
temperature. The un-dissolved sugar at
the bottom is in equilibrium with a saturated sugar solution above it. No more is dissolving, no more is dropping out. Now, if you cool that liquid, it becomes supersaturated
with sugar, which means there is more dissolved than should be, so if crystals
have a place to form they will, at a very slow rate, but faster when cooled
greatly. With carbo (bicarbonate, carbonic,
and carbonate) the opposite is true, it is one of the few solutions whose
solubility (amount that can be dissolved) goes down as the water temp
increases. This is why boilers, coffee
makers, and irons get calcium carbonate deposits on their hot surfaces. We will use that to our advantage in Part 2
under the pre-boiling section.
Nashville Metro Water has a HCO3- level of 61 ppm, so
from this we figure Metro water consists mainly of surface runoff water, which
coming from a river it certainly does. Since
it is over 58 ppm, it is slightly supersaturated with bicarbonate (HCO3-).
Hardness
is the amount of Ca++ and/or Mg++ ions, and is usually
given in ppm (same as mg/l) or in terms of ppm as CaCO3.
If a
water report gives only total hardness and you want to estimate the calcium and
magnesium hardness, assume that 4/5ths of the total hardness is calcium
hardness and 1/5th is magnesium hardness.
This ratio varies by water source, but Metro water stays fairly constant
at this ratio.
There is
another type of hardness called temporary hardness, which is simply the amount
of hardness you can get rid of by boiling.
Boiling causes Ca to react with CO3 in the water and
precipitate out (see section on pre-boiling). Permanent hardness cannot be
removed by boiling, hence the name.
Hardness is beneficial to brewing water. Calcium helps to protect mash enzymes,
and if depleted, mashes could take much longer, and may not have the proper mix
of alpha and beta amylase activity.
Many sugar refineries that use amylase and glucosidase enzymes add
calcium chloride to soft tap water to obtain over 35 ppm of calcium, which
prolongs enzyme life. Calcium also aids
in getting a good hot break (coagulation of proteins and polyphenols in the
boil). Magnesium hardness is needed in
trace amounts for yeast health.
If you have a household water
softener to reduce water hardness, you should bypass it when drawing out water
used for brewing. These contain an ion
exchange bed with sodium (Na+) ions.
The Ca++ and Mg++ ions are almost all replaced by
Na+, which can lead to very high levels of sodium if the water is hard. Also, don't use Brita(tm) filters for
brewing water, these have both activated charcoal and ion exchange resin. The only filter you need for brewing water
is activated charcoal to remove chlorine compounds. See the section on Removal of Chlorine Compounds in this article
Although
the hardness level of water is not detrimental, it is always accompanied by
high alkalinity. It is the alkalinity (bicarbonates et. al.) which makes hard water undesirable for
brewing. As will be discussed later,
water can be extremely hard and still be capable of producing a relatively
light colored beer.
Alkalinity
of tap water is defined as the amount of acid required to bring a sample of
water from its initial pH down to a pH of 4.3.
The acid is added slowly, or titrated, and when the solution hits a pH
of 4.3 the amount of acid is recorded and converted into the appropriate units
of Alkalinity, which are ppm as CaCO3 .
This can
be estimated mathematically for tap water assuming all alkalinity comes from
CaCO3, and not from nitrates or other anions.
The formula to use is:
Alkalinity
= 2 x carbonate (CO3--)
+ bicarbonate (HCO3-) + OH- - H+
where they are all in the same units.
Alkalinity is almost always given in water reports in terms of ppm as
CaCO3. The OH-
and H+ terms are due to the dissociation of water itself, and are
extremely small, so we can ignore them.
You will
notice that the carbonate is multiplied by 2 in the definition of
alkalinity. If you are thinking that is
because carbonate has two little minuses beside it, you are right. In very simple terms, alkalinity is a
measurement of the anions in the water, or put even simpler, adding up all the
negatives.
Recall
alkalinity is measured by adding acid.
Well, the acid is continually added, contributing H+ ions until the pH
is 4.3 (the ‘zero’ point). At that
point the amount of plus’s added (amount of acid) is figured out and this
yields the alkalinity, or number of minuses.
That’s all there is to it, in algebraic terms.
One thing of note in regards to alkalinity is that bicarbonate (HCO3-),
carbonic acid (H2CO3), and carbonate (CO3--)
all exist together in a 3-way relationship that is determined solely by pH of
the water they are dissolved in. In
normal water of about 7 pH, there is 81% bicarbonate (HCO3-),
19% carbonic (H2CO3), and 0% carbonate (CO3--). For any given pH, the % of bicarbonate,
carbonic, and carbonate can be easily determined.
This chart shows the
fractional amount (percentage) of each that exist for any given pH

Chart 5.0 - Carbonate System in tap water
Notice from this table that carbonate (CO3--) does not
exist below a pH of 8.3. As a result
Bicarbonate (HCO3-) is the source of all alkalinity in
tap water of less than 8.3 pH.
Side Note:
It is important to note that, as shown in the above chart of bicarbonate,
carbonic, and carbonate, if the pH of the water is lowered (say with acid
addition), the alkalinity is decreased as the ‘carbo’ shifts from bicarbonate
(HCO3-) to carbonic acid (H2CO3),
which does not contribute to alkalinity.
See part 2 for acid additions.
Because
the ratio of carbonate and bicarbonate is related to pH, if your water report
gives carbonate/ bicarbonate levels and pH, but doesn’t list alkalinity, you
can roughly calculate the alkalinity as outlined in section 5.1 below.
Alright
so we know what alkalinity is. Remember
that solar powered calculator you got free a few years ago? Let’s pull that out of the catch-all drawer
and blow the dust off it.
Side Note:
The unit conversions for all minerals shown here are given in an easy to use
table form - see Attachment 2
If your water report gives: bicarbonate (HCO3-) in ppm
(aka mg/l), then you can calculate alkalinity assuming the pH is <8.3 and no
carbonate exists. Note that sometimes
water profiles erroneously list CO3-- when they are
actually referring to HCO3-. As shown in the table above, CO3-- is not
present at normal tap water pH. The
formula to calculate alkalinity given this information is:
Alkalinity (in ppm as CaCO3) =
(mg HCO3-/l ) x (1 mEq/61 mg HCO3-)
x (50 mg CaCO3/1 mEq)
or without units shown: Alkalinity = HCO3- x
50 / 61
If
your water report gives Alkalinity as ‘hardness’, ‘ppm CaCO3’, or no
units, then your
calculator can go back in the drawer, you already have your alkalinity in ppm
as CaCO3 (sorry for the let
down). If you need or want to, you can
calculate HCO3- using:
mg/l of HCO3- =
Alkalinity [in mg CaCO3/liter] x (1 mEq /50 mg CaCO3)
x
(61 mg
HCO3-/mEq)
or without units shown: HCO3- = Alkalinity
x 61 / 50 (this assumes pH of
<8.3)
To give some history, before brewing chemistry was widely understood highly alkaline waters were generally unsuitable for brewing light styles. The water in London was favorable to brewing ESB and Porters, highly alkaline Dublin water was used to brew stouts, and only the very soft water of Pilsen was capable of properly brewing with extremely light kilned malts. The reason dark beers are traditionally brewed with alkaline waters is because roasted grains add acidity to the mash, buffering the alkalinity of water and bringing mash pH down to an acceptable range.
If a pilsener grist were mashed with untreated Dublin water, the result would be a high mash pH, resulting in poor enzyme activity, long mash times, and possible extraction of tannins from the husk. Without modern day knowledge of water chemistry, brewing cities gravitated towards styles which mashed easily and whose flavors blended well with the local water.
Now that
we have calculated and understand basic water chemistry and alkalinity, we can
discuss residual alkalinity. If you
recall from the discussion on calcium and carbonates, we said that
Burton-on-Trent water was very high in bicarbonate (300 ppm). Consequently, it is also high in hardness.
Here is the water profile:
Water Profile: Burton on Trent*
|
Ca++ |
HCO3-- |
Cl- |
Mg++ |
Na+ |
SO4--
-- |
|
295 |
300 |
25 |
45 |
55 |
725 |
*all values listed are
in mg/l (same thing as ppm)
We have
also discussed that generally, water high in alkalinity (which HCO3-
contributes to) is only suitable for brewing darker beers. However, in the case of Burton on Trent,
brewers have traditionally been able to brew good pale ales and IPAs. The reason for this lies in a property of brewing
water called Residual Alkalinity.
Looking
at the Burton profile you can see that calcium is a high 295 ppm, and yet is
only balanced by 300 ppm of carbonate.
Where did all that calcium come from then? Probably CaSO4, (gypsum) dissolved in the soil. The SO4-- levels are
sky high at 725 ppm. Remember that when
we defined alkalinity, we said it was HCO3- + CO3--
(no SO4-- term), so although gypsum (CaSO4)
adds calcium it does not contribute to alkalinity, but as we will discover
later, it does reduce ‘Residual’ Alkalinity.
Residual
Alkalinity was studied by a German brewing scientist named Kolbach, who
observed that calcium and magnesium reacted with phytin present in the mash to
produce hydrogen ions, which effectively lowers the mash pH.
This means
that the higher the calcium and magnesium for a given level of alkalinity, the
lower the mash pH will be.
6.1 CALCULATING RESIDUAL ALKALINITY
Residual alkalinity
can be determined using the known characteristics of the water and a simple
formula. For water where the report gives alkalinity, calcium, and magnesium
all in ‘hardness’ (ppm as CaCO3), the formula is
Residual Alkalinity (RA)
= Alkalinity - Ca / 3.5 - Mg / 7, where all are in ppm as CaCO3
The formula for calculating RA where Ca and Mg are given in
ppm (not as hardness) is:
RA = Alkalinity (ppm as CaCO3) - 0.714 x Ca (ppm) - 0.585 x Mg (ppm)
For water
where the report gives alkalinity and total hardness (TH) both in hardness (ppm
as CaCO3), the residual alkalinity can be estimated by assuming ~80% of hardness is Ca, and ~20% is Mg. The formula is then:
RA = Alkalinity -
0.80 x TH / 3.5 - 0.20 x TH / 7
6.2 CALCULATING pH SHIFT
Now for the most important part of
this entire article! The pH shift!
Kolbach observed that water with a residual alkalinity of 10 degrees
German Hardness caused the pH of a pale malt mash to be 0.3 pH units above the
pH realized if distilled water was used.
This observation quantifies the
relationship between residual alkalinity and its resultant effect on mash
pH. Kolbach did his work based on
German degrees of hardness, but if we convert his numbers to appropriate US
units, we find that the pH shift of the mash can be calculated from Residual
Alkalinity as follows:
pH Shift = 0.00168 x RA
Where residual alkalinity (RA) is
in ppm as CaCO3 (as calculated above)
Assuming a 100% pale/pils malt
with distilled water results in a mash pH of 5.8, this gives us the estimated pH of the mash:
pH = 5.8 + 0.00168 x RA
Example 1:
Burton on Trent water, HCO3- = 300 ppm, Ca =
295 ppm, Mg = 45 ppm
First we need to calculate alkalinity in terms of ppm as CaCO3.
This is done by assuming the water pH is less than 8.3 (which is likely)
and recognizing that 100% of alkalinity is from HCO3-;
since the pH is less than 8.3 (see carbo chart in alkalinity section) CO3--
is zero, and remember H2CO3 does not contribute to
alkalinity. Convert to the proper units
as follows, remembering that 300 ppm = 300 mg/l
300 mg HCO3-/liter x (mMol/61 mg HCO3-) x (50 mg CaCO3/mMol)= 246 mg/l as CaCO3
Discussion:
Therefore a 100% pale malt mash with this water is predicted to be
5.815 pH. This is not a significant
amount of increase over 5.8, but consider that the optimum range of a mash pH
is 5.3 to 5.5 pH, and 5.8 pH is the upper bound for a proper mash. However, a British Pale Ale often consists
of up to 10% crystal or other higher kilned specialty malts. All higher kilned malts contribute to the
acidity of the mash, and would lower the pH below the 5.815 pH predicted for a
100% pale malt mash. With a grainbill
of 20% crystal or roasted malt, the pH will be shifted down as much as 0.5 pH.
7.0 WATER FOR EXTRACT BREWING:
The water used for extract
brewing is not nearly as critical.
Since your malt has already been mashed, you don't have to worry about
the mash pH, and are only concerned with flavor impact ions like Na, Cl, Mg,
and SO4. However, you don’t want water
that is so hard it tastes bad. Metro
Nashville water is relatively soft, and is perfectly fine for extract brewing
all beer styles.
You may want to consider adding a small amount of CaCl to aide clarity and hotbreak. The chloride is also good in malty styles. Some gypsum would accentuate the hops in an English Bitter. Do some research, and take a look at the recommended mineral table in the attachment to this article.
It is worth noting however, that extract contains all of the minerals (calcium, carbonate, sulfate, chloride etc.) of the extract Manufacturer’s water supply. The mash uses their water supply, then the wort is run off and evaporated, concentrating all the minerals into the extract (and some of the manufacturers have hard water supplies). Now, when you use Nashville tap water you are adding in even more minerals.
For this reason, if you feel you are getting some harsh carbonate or sulfate bitterness in your extract beer, I recommend switching to 100% distilled water. If that doesn’t clear it up then you know it is not a water issue.
8.0 REMOVAL OF CHLORINE COMPOUNDS
If you don’t already know, chlorine is great for keeping pools clean and
sanitizing things, but it is very bad for brewing. Failure to remove chlorine compounds prior to adding steeping
grains, mashing in, or adding extract will result in the polyphenols (aka
tannins) in the grain/extract reacting with the chlorine compounds and creating
funky medicinal off flavors called chlorophenolics, and you don’t want that in
your beer.
Metro does seem to have a
large amount of chlorine odor and the water report shows the yearly average
level of trihalomethanes (THM) that is half the acceptable EPA limit of the
maximum allowed. THMs are a cancerous
byproduct of chlorine based sanitizer reacting with organic material in the
water, and at high levels is indicative of a poor separation of organics from
the water that is treated.
Anyway, if you use Metro water, I would recommend you use a carbon filter tube – the inline kind made for ice maker tubing, or the undersink kind. The carbon will filter out all chlorine in Metro water. It will not remove chloramines, so if you are not on Metro water, you might want to call and ask if your supplier adds ammonia to the water to stabilize the chlorine and create chloramines.
If you can’t filter your tap water, do one of the following:
· Use all store bought spring water. It is ozonated, not chlorinated, and all excess ozone is destroyed before bottling.
· Boil your tapwater then let it cool back down before adding steeping grains (works for chlorine only)
·
Add ½ a crushed campden tablet (or 1/16 teaspoon of
metabisulfite) per
5 gallons cool water, stir in and let stand 5 minutes for chlorine to be driven
off. Not advisable for people who can’t
tolerate sulfites (wine has tons of them). Note: This is the only known
method to adequately remove chloramines short of using an RO water filter.
The
recommended ranges for brewing ions/minerals are shown in the following table,
and are adapted from various sources.
Also shown are the actual levels found in Nashville Metro water (2001
yearly average).
Recommended mineral ranges:
|
Name |
Symbol |
Ideal Range* |
Metro Water* |
Notes |
|
Bicarbonate |
HCO3-- |
0-250 ppm |
61 ppm |
Ideal range varies by style. High levels in pale-based beers cause high
mash pH, decreased enzyme activity, and can increase tannin levels extracted
from grain husk, creating tea-like harshness. Increases ‘reddening’ of wort. |
|
Sulfate |
SO4-- |
<150 ppm |
44 ppm |
At upper levels can increase
perception of hop bitterness and makes it seem drier. 150-300 ppm ok for British style bitters |
|
Chloride |
Cl- |
<200 ppm |
8 ppm |
Rounds out flavor of beer, keep
low if paired with sodium. |
|
Sodium |
Na+ |
<150 ppm |
5.3 ppm |
At 70-100 ppm it rounds flavor and
accentuates sweetness of malt. |
|
Magnesium |
Mg++ |
10-15 ppm |
5.3 ppm |
Yeast trace nutrient, required at
10-15 ppm level, but some is provided by grains. Higher levels cause unpleasant sourness. |
|
Calcium |
Ca++ |
50-100 ppm |
29.6 ppm |
Required for mash enzyme
stabilization and a yeast nutrient.
Higher levels increase hot break of boil and clarity of finished beer. |
* Note that
ppm is equivalent to mg/l for all measurements
Additional parameters:
|
Parameter |
Ideal Range |
Metro Water |
Notes |
|
pH |
6.5-8 |
7.0-7.2 |
Generally unimportant to brewing
chemistry, but required to calculate alkalinity using only HCO3—ppm
if pH>8.3 |
|
Alkalinity |
Varies by style |
50 |
Ideal range varies by style. Same
impacts as bicarbonate listed above. |
Use this
table to convert a water chemistry value from one unit to the other. The ‘mEq/l’ designates milliequivalents per
liter. Simply put this is the molecular
weight divided by the absolute value of the charge. For example, Ca++ is 40 / 2 = 20, since it has a charge of
2. Likewise HCO3-
is 61 / 1 = 61, since it has a charge of only 1.
|
To Get |
From |
Do This |
|
Alkalinity as CaCO3 |
HCO3 (ppm) |
Divide by 61 and
multiply by 50 |
|
Ca (mEq/l) |
Ca (ppm) |
Divide by 20 |
|
Ca (ppm) |
Ca (mEq/l) |
Multiply by 20 |
|
Ca (ppm) |
Ca Hardness as CaCO3 |
Divide by 50 and
multiply by 20 |
|
Ca Hardness as CaCO3 |
Total Hardness as CaCO3 |
Divide by 5 and
multiply by 4 (estimated) |
|
Ca Hardness as CaCO3 |
Ca (ppm) |
Divide by 20 and
multiply by 50 |
|
CaCO3 (mEq/l) |
CaCO3 (ppm) |
Divide by 50 |
|
HCO3
(mEq/l) |
HCO3 (ppm) |
Divide by 61 |
|
HCO3 (ppm) |
Alkalinity as CaCO3 |
Divide by 50 and
multiply by 61 |
|
Mg (mEq/l) |
Mg (ppm) |
Divide by 12.1 |
|
Mg (ppm) |
Mg (mEq/l) |
Multiply by 12.1 |
|
Mg (ppm) |
Mg Hardness as CaCO3 |
Divide by 50 and
multiply by 12.1 |
|
Mg Hardness as CaCO3 |
Total Hardness as CaCO3 |
Divide by 5 (estimated) |
|
Mg Hardness as CaCO3 |
Mg (ppm) |
Divide by 12.1 and
multiply by 50 |
|
Total Hardness as CaCO3 |
Ca as CaCO3
and Mg as CaCO3 |
Add them. |
Note: ppm is equivalent to mg/l for all
measurements