The Blue Baby Syndrome

Abstract

Blue Baby Syndrome or Methemoglobinemia is caused by decreased ability of blood to carry oxygen, resulting in oxygen deficiency
in different body parts. Infants are more susceptible than adults. The disease can be caused by intake of water and vegetables
high in nitrate, exposure to chemicals containing nitrate, or can even be hereditary. Groundwater gets contaminated by leaching
of nitrate generated from fertilizer used in agricultural lands and waste dumps in rural and urban areas. Prevention of water
contamination, abstention from drinking contaminated water and controlling nitrate levels in drinking water by water treatment
are effective preventive measures against nitrate poisoning.

Full text

20 RESONANCE  October 2003
GENERAL  ARTICLE
Blue Baby Syndrome or Methemoglobinemia is caused by
decreased ability of blood to carry oxygen, resulting in
oxygen deficiency in different body parts. Infants are more
susceptible than adults. The disease can be caused by in-
take of water and vegetables high in nitrate, exposure to
chemicals containing nitrate, or can even be hereditary.
Groundwater gets contaminated by leaching of nitrate gen-
erated from fertilizer used in agricultural lands and waste
dumps in rural and urban areas. Prevention of water con-
tamination, abstention from drinking contaminated water
and controlling nitrate levels in drinking water by water
treatment are effective preventive measures against nitrate
poisoning.
Intake of drinking water containing nitrate (as NO
3
–
) > 45 mg
L
–1
(or > 10 mg L
–1
NO
3
–
–N), vegetables rich in nitrate, or
exposure to some drugs and chemicals may cause methemoglo-
binemia in infants and adults. The toxicity of nitrate in humans
is an end result of the reduction of nitrate (NO
3
–
) to nitrite
(NO
2
–
) in the intestine. Nitrate reacts with hemoglobin to form
methemoglobin (MHb), a substance that does not bind and
transport oxygen to tissues, thereby causing asphyxia (lack of
oxygen), resulting in cyanosis of body tissues. Methemoglobin-
emia may be accentuated by an inherited enzyme deficiency,
structural defects in the hemoglobin molecule, or by any toxic
substance, which either oxidizes hemoglobin directly, or facili-
tates its oxidation by oxygen (Box 1).
Methemoglobinemia
Nitrate itself is not toxic to humans. Nitrate becomes a problem
only when it is converted to nitrite in the human body, resulting
The Blue Baby Syndrome
Nitrate Poisoning in Humans
Deepanjan Majumdar
Keywords
Cyanosis, hemoglobin, infants,
methemoglobinemia, nitrate.
Deepanjan Majumdar is
presently working as a
lecturer in the Depart-
ment of Environmental
Science at the Institute of
Science and Technology
for Advanced Studies and
Research (ISTAR),
affiliated to Sardar Patel
University, Vallabh
Vidyanagar, Gujarat,
India. His present
research interests include
global warming and
climate change, water and
soil pollution, environ-
mental impacts of
wastewater irrigation and
soil nutrient management.

21
RESONANCE  October 2003
GENERAL  ARTICLE
in methemoglobinemia. Much of the ingested nitrate is usually
absorbed before reaching the nitrate-reducing bacteria, which
reside in the intestinal tract. Most of the ingested nitrate is
excreted within 24 hours mainly through urine, as well as
through feces and sweat. If nitrate is introduced directly into the
colon, methemoglobinemia is readily produced. Nitrite pro-
duced from nitrate enters the bloodstream mainly through the
upper gastrointestinal tract. Nitrate is converted to nitrite by
intestinal bacteria, and nitrite acts as the oxidizing agent to form
MHb in the red blood cells.
Box 1. Agents Implicated in Acquired Methemoglobinemia
Direct Oxidants
Therapeutic Agents Domestic & Industrial Agents
Amyl nitrite Well water high in nitrates
Ethyl nitrite Food high in nitrates
Sodium nitrite Nitrous gases
Ammonium nitrate Corning extract
Silver nitrate Potassium chlorate
Bismuth subnitrate
Nitroglycerin
Quinines
Indirect Agents
Sulfonamides Miscellaneous Compounds
Sulfamethazole Acetanilid
Sulfanilamide Aminobenzenes
Sulfapyridine Aminophenol
Sulfathiazole Benzocaine
Prontosil Nitrobenzene
Nitrotoluenes
Aniline Dyes Phenacetin
Diaper marking ink Phenazopyridine
Dyed blankets Phenylenediamine
Laundry markings Prilocaine
Freshly dyed shoes Resorcin
Red wax crayons Toluenediamine
Trinitrotoluene
Nitrate itself is not
toxic to humans.
Nitrate becomes a
problem only when
it is converted to
nitrite in the human
body, resulting in
methemoglobinemia.

22 RESONANCE  October 2003
GENERAL  ARTICLE
Oxygen is required for all human tissues to enable them to
combust food materials carried to them by blood and other body
fluids. Hemoglobin in red blood cells carries oxygen to tissues
from lungs by forming oxyhemoglobin. Oxygen is released in
the tissues and deoxyhemoglobin is left behind to return to
lungs for reoxygenation. For hemoglobin to act as a carrier, iron
atom in the molecule has to be in the reduced (Fe
++
) state.
When nitrite is absorbed in bloodstream, it oxidizes hemoglo-
bin to MHb, a Fe
+++
compound with reduced oxygen transport
capacity, as this compound contains iron in its highest oxida-
tion state which is incapable of binding oxygen. Thus, nitrate
reduces the total oxygen carrying capacity of the blood. As
different parts of the body get deprived of oxygen, clinical
symptoms of oxygen starvation start to appear, the main being
cyanosis (derived from ‘cyano’, meaning dark blue; from Greek,
kyanos). The lips or even the skin start to take on a blue
colouration, hence the common name, the blue baby syndrome/
disease. Although persons of any age can suffer from methemo-
globinemia, infants are particularly susceptible during the first
four months of their life, as their total fluid intake per unit body
weight is approximately three times more than that of adults.
The pH of the stomach fluids in infants is also higher (5-7) than
in adults (<4), which allows nitrate-reducing bacteria to grow
in the upper gastrointestinal tract from which nitrite is rela-
tively easily absorbed. In adults, as the stomach fluid is more
acidic, the nitrate reducing bacteria live in the lower intestine,
from which absorption of nitrite to the bloodstream does not
occur. Gastrointestinal illness and diarrhoea in adults may allow
the bacteria responsible for conversion of nitrate to nitrite to
migrate from lower intestine to upper intestine and stomach,
and increase the chances of nitrite formation prior to absorption
in small intestine. Another reason why this disease is not
commonly seen in adults is the presence of an enzyme, MHb
reductase (erythrocyte cytochrome 5b-reductase), in the red
blood cells of adults. This enzyme reduces MHb, and thus helps
avoid the danger of methemoglobinemia in adults.
Although persons of
any age can suffer
from methemo-
globinemia, infants
are particularly
susceptible during
the first four months
of their life, as their
total fluid intake per
unit body weight is
approximately three
times more than that
of adults.

23
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GENERAL  ARTICLE
Since hemoglobin is constantly exposed to oxidative stresses,
small amounts of MHb are naturally formed all the time in the
human body. MHb is produced at a slow, predictable rate in vivo
by the escape of an electron from heme. Following loss of an
electron, binding of oxygen by the oxidized heme cannot occur
unless an electron is regained by means of reducing mechanisms
within the cell. Because the capacity of red cells to reduce
oxidized heme exceeds the spontaneous rate of heme oxidation
by several hundredfold, only 0.5-2.0% of the total hemoglobin is
in MHb form at given time. In normal adults, MHb are effi-
ciently reduced again in a reaction catalyzed by MHb reductase.
The most important pathway of MHb reduction utilizes NADH-
MHb reductase for the transfer of an electron from NADH to
heme. The reaction appears to proceed in two steps: (i) enzy-
matic reduction of cytochrome b5, followed by (ii) nonenzy-
matic transfer of an electron from reduced cytochrome b5 to
MHb (Figure 1a). Another pathway for MHb reduction involves
the direct transfer of electrons from ascorbic acid and glu-
tathione to heme. The NADPH-dependent MHb reductase lacks
an endogenous electron acceptor and is, therefore, physiologi-
cally inert. It may be ‘activated’, however, by an exogenous
electron acceptor, such as methylene blue. The NADPH-depen-
dent enzyme reduces methylene blue to leukomethylene blue,
which rapidly reduces MHb nonenzymatically (Figure 1b). Re-
duction of methylene blue to leukomethylene blue requires an
NADH
Cytochrome b5
(oxidized)
MetHb-REDUCTASE
NAD
Cytochrome b5
(reduced)
Hb(Fe
++
)
MetHb(Fe
++
)
NADH
NADP
MetHb-REDUCTASE
Hb(Fe
++
)
MetHb(Fe
++
)
Methylene Blue
Leukomethylene
Blue
Figure 1. Metabolic path-
ways for the reduction of
MHb to hemoglobin.
a. NADH-dependent MHb
reductase pathway
b. NADPH-dependent MHb
reductase pathway, requir-
ing an exogenous electron
acceptor (methylene blue).
(a) (b)

24 RESONANCE  October 2003
GENERAL  ARTICLE
intact pentose phosphate pathway for regeneration of NADPH.
Consequently, methylene blue is without effect on MHb levels
in patients with glucose-6-phosphate dehydrogenase (G6PD)
deficiency. Unfortunately, newborn infants have a very low
concentration of the enzyme MHb reductase. This concentra-
tion remains low until the age of 4 years. Apart from this, fetal
hemoglobin, present in infants, is highly susceptible to oxida-
tion to form MHb. Moreover, poor excretory power of imma-
ture kidney in infants may favour retention of nitrite ion, which
may aggravate the situation.
Clinical Features
Infected infants show blueness around the mouth, hands, and
feet and hence the common name ‘blue baby syndrome’ has
come into being. At approximately 10% MHb levels, the body
starts to take on a slaty gray appearance of cyanosis, and the
disorder becomes clinically detectable. Diagnosis can confirm
methemoglobinemia by eliminating other causes of cyanosis,
and by spectrophotometric analysis of blood, which gives a
characteristic absorption peak at 634 nm. Patients may show
asthenia (loss of muscular strength), dizziness, headache, drowsi-
ness, dyspnoea (lack of O
2
supply and difficult respiration),
chest pain, nausea, diarrhoea and troubled breathing. Other
symptoms, like renal or liver injury, and hemolysis (lysis of
blood cells) may occur. In extreme cases, there is marked leth-
argy, stupor, an increase in the production of saliva, loss of
consciousness and seizures. If and when MHb levels reach 40%
or more of the total haemoglobin, the patient may collapse and
become comatose, or die.
Treatment
Any patient with evidence of toxicity and/or methemoglobin-
emia levels > 30% should be treated. Mild cases do not require
active treatment other than avoiding the contaminated source of
drinking water and these patients usually recover within 24 to
72 hours, since MHb level automatically goes down to harmless
At approximately
10% MHb levels,
the body starts to
take on a slaty gray
appearance of
cyanosis, and the
disorder becomes
clinically detectable.
When MHb levels
reach 40% or more
of the total
haemoglobin, the
patient may collapse
and become
comatose, or die.

25
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GENERAL  ARTICLE
levels. A severely affected person requires a therapy of methyl-
ene blue, which is optimum at 1-2 mg kg
-1
body wt., through a
1% solution of the same intravenously for a ten-minute period.
This converts MHb to haemoglobin and gives immediate relief.
Ascorbic acid, given orally in divided doses of 300 to 500 mg
daily, also effects a slow, nonenzymatic reduction of MHb.
Dietary intake of vitamin C has been found to help maintain
lower levels of MHb by reducing nitrite to nitric oxide (NO).
Vitamin E (α-tocopherol) and some unsaturated acids e.g. feru-
lic acid, also act as nitrite scavengers. Emergency exchange
blood transfusion is indicated when levels of MHb exceed 60-
70%, or if massive hemolysis occurs. Occasionally, in very severe
cases, administration of high flow oxygen (100%) is done, which
allows saturation of normal hemoglobin and increases dissolved
oxygen.
Hereditary Methemoglobinemia
In contrast to acquired methemoglobinemia, the hereditary
forms are rare. An autosomal recessive mode of transmission
characterizes familial methemoglobinemia due to NADH-MHb
reductase deficiency, and an autosomal dominant mode is char-
acteristic of certain hemoglobin variants, which stabilize iron in
the oxidized state.
Hereditary methemoglobinemia responsive to the administra-
tion of methylene blue or ascorbic acid was initially described in
persons of European descent. Following the demonstration that
these individuals were deficient in NADH-dependent MHb
reductase, a near-global distribution of the disorder was recog-
nized. Congenital deficiency of NADH-MHb reductase has
been recognized as the cause of methemoglobinemia among
Navajo and Alaskan Indians, Cubans, Indians, Chinese, and
Japanese. Affected subjects are presumably homozygous for a
rare, functionally abnormal allele of the enzyme, although double
heterozygosity for two different variants has also been docu-
mented. The carrier or heterozygous state is characterized by
intermediate levels of enzyme activity together with a greater

26 RESONANCE  October 2003
GENERAL  ARTICLE
than normal susceptibility to MHb formation following expo-
sure to oxidants, drugs, and chemicals.
The sole clinical expression of enzyme deficiency is cyanosis,
often dating from birth, in the absence of associated signs or
symptoms, and with no evidence of cardiopulmonary disease.
The hue may be slaty gray, gray-brown or violet. It is generalized
over the whole body but is particularly noticeable in the lips, the
mucous membranes of the mouth, the tongue, the palate, the
nose, over the cheekbones, on the ears and in the nail beds.
Untreated individuals generally maintain levels of MHb be-
tween 15 and 30%. Most of the MHb is segregated in a popula-
tion of older cells. Methylene blue taken orally in doses of 100 to
300 mg daily, or ascorbic acid in doses of 500 mg daily is usually
sufficient to maintain the level of MHb below 10%.
Sources of Nitrate Entering the Human Body
Nitrate Contamination in Groundwater
Nitrogen accumulates in the soil naturally from rainfall, plant
debris, animal residues and microbial fixation of N
2
from atmo-
sphere. Anthropogenic nitrate (NO
3
–
) comes to groundwater
through nitrogenous fertilizers, organic manures, and human
and industrial wastes (Figure 2). When nitrate-nitrogen supply
exceeds plant demand, the groundwater gets contaminated by
leaching which is the downward movement of NO
3
–
–N with
water through the soil. The potential for NO
3
–
–N leaching is
greater in sandy soils, but can occur on finer textured soils (e.g.
clayey soils) also, albeit at a slower rate. In India, groundwater in
many areas has been found to contain more than 45 mg L
–1
NO
3
,
which is potentially dangerous to health, although concentra-
tion seems to vary with time, depending on season, farming
practice, etc.
Nitrate in Leafy Vegetables
Leafy vegetables such as spinach, cauliflower, and cabbage gen-
erally have relatively high nitrate concentrations, which may be
Leafy vegetables
such as spinach,
cauliflower, and
cabbage generally
have relatively high
nitrate
concentrations,
which may be even
higher because of
fertilization practices.

27
RESONANCE  October 2003
GENERAL  ARTICLE
even higher because of fertilization practices. There have been
several reports of methemoglobinemia following the consump-
tion of spinach, but the conversion of nitrates to nitrites during
storage, rather than the nitrates themselves was responsible for
methemoglobinemia. Moreover, it has been suggested that other
compounds, possibly ascorbic acid, present in leafy vegetables,
may provide protection against in vivo reduction of nitrates to
nitrites.
Figure 2. Formation and
cycling of nitrate in the en-
vironment and its arrival in
human and animal bodies
[M: Mineralization; N: Nitri-
fication; U: Uptake; D: Deni-
trification; E: Exudation; IF:
Industrial fixation; B: Bio-
mass addition to soil on
death].

28 RESONANCE  October 2003
GENERAL  ARTICLE
Nitrate Incorporation during Food Preparation
Addition of high nitrate- or nitrite-containing water to a food
product during preparation will increase the nitrate/nitrite con-
tent of the final product. Heating of the water either before its
addition or as part of the preparation procedure will increase the
nitrate/nitrite concentration. Since methemoglobinemia is
caused by nitrites, rather than nitrates, conversion of nitrates to
nitrites in food preparation procedures should be avoided. Dis-
carding the cooking liquid of high-nitrate vegetables would
lower nitrate content of the diet, but some other water-soluble
nutrients, including vitamin C, also would be lost. Conventional
home canning and freezing practices will minimize nitrate/
nitrite conversion by eliminating or limiting the microbial
action responsible for the change.
Nitrate from Chemicals
Various chemical compounds used in home or industry as well
as several therapeutic agents (Box 1) are capable of increasing
the rate of heme oxidation 100 to 1000-fold, thereby overwhelm-
ing the capacity of erythrocytes to maintain hemoglobin in the
reduced state. An indirect effect is postulated for certain aro-
matic amino and nitro compounds including acetanilid, phen-
acetin (Empirin, Anacin, Stanback), sulfonamides, phenazo-
pyridine (Pyridium) and aniline dyes. Since most of these agents
do not produce MHb in vitro, active intermediate compounds
are presumed responsible. The ingestion of deodorant contain-
ing naphthalene and aniline or red wax crayons containing p-
nitroaniline, contact with marking ink, dyed blankets or laun-
dry marks on diapers and benzocaine prilocaine, resorcin, aniline
dyes or other aromatic compounds absorbed orally, rectally or
percutaneously have been shown to lead to methemoglobinemia.
Testing recommendations
The only way to know if drinking water is contaminated with
nitrates is to have it tested. It is recommended that water should
be tested once every three years for nitrates, more often in an
The only way to know
if drinking water is
contaminated with
nitrates is to have it
tested. It is
recommended that
water should be
tested once every
three years for
nitrates, more often in
an area with a history
of high nitrate levels.

29
RESONANCE  October 2003
GENERAL  ARTICLE
area with a history of high nitrate levels, or if someone at home
is at risk from nitrate contamination. Field tests for nitrate
include diphenylamine blue (1% DPB in concentrated sulfuric
acid) and nitrate dipsticks. The DPB test is more suitable to
determine presence or absence of nitrate in suspected forages: a
drop or two are applied on a cross-section of plant stalk material,
then any dark blue color change is noted as an indicator of
excessive nitrate content in the sample. Nitrate dipsticks are
used primarily for testing water supplies. The dipstick method
is rapid and gives indications of both nitrite and nitrate con-
centrations over a relatively wide range. Field tests are presump-
tive and should be confirmed by standard analytical methods at
a recognized laboratory.
Water Treatment Methods to Produce Low-nitrate
Drinking Water
1. Distillation
The distillation process involves heating water to boiling, re-
sulting in evaporation, after which the resulting steam is col-
lected and condensed using a cooled metal coil. Up to 99% of the
nitrate-nitrogen can be removed by this process. Merely boiling
water will increase rather than decrease the nitrate concentra-
tion. Some distillers use activated carbon filters to assist in
removing any organic contaminants, whereas others any pre-
heat the water before it enters the boiling chamber in order to
help remove volatile organic contaminants.
2. Reverse Osmosis
In reverse osmosis, pressure is applied to the impure water
forcing the more concentrated water in a reverse direction
through a semi-permeable membrane. As the water passes
through, the membrane filters out most of the impurities. Ac-
cording to manufacturers’ literature, from 85 to 95% of the
nitrate can be removed by this process. A disadvantage of this
method is that only about 30% of the water entering the reverse
osmosis unit is recovered as treated water. The remaining 70% is
Nitrate dipsticks
are used primarily
for testing water
supplies. The
dipstick method is
rapid and gives
indications of both
nitrite and nitrate
concentrations
over a relatively
wide range.

30 RESONANCE  October 2003
GENERAL  ARTICLE
discharged as waste along with the impurities, which have been
removed from the product water.
3. Ion Exchange
The ion exchange process removes contaminant ions in water
when the water is passed through a treatment tank filled with a
bead-like resin. For nitrate removal, special anion exchange
resins are used that will exchange chloride ions for the nitrate
and sulfate ions in the water as it passes through the resin. Most
anion exchange resins have a higher selectivity for removing
sulfate than nitrate. Thus, the level of sulfate in the water is an
important factor in the efficiency of an ion exchange system.
Another concern with nitrate ion exchange systems occurs when
the resin becomes saturated with nitrate in which case the
treated water may have a higher nitrate content than the un-
treated water. Thus, an ion exchange resin should be regener-
ated frequently. Ion exchange is not commonly used for house-
hold water treatment. It is more applicable for large commercial
or community water system installations.
Conclusion
Although nitrate content in water may not cross the upper safe
limit in many areas, people should be aware of the quality of
drinking water available for them, especially in agricultural and
industrial areas. Special care should be taken to monitor the
water and food given to babies. In India, methemoglobinemia is
not very common, which may be due to lack of awareness or lack
of epidemiological studies on the disease. It seems rather sur-
prising that in a country where agriculture is the livelihood of a
major portion of population, and where general sanitation is
poor in many areas, reported cases of methemoglobinemia are
rare. Groundwater nitrate content in many areas of India has
been found to be at dangerous levels, but in these areas little or
no epidemiological studies have been carried out to find out the
prevalence of the disease.
Suggested Reading
[ 1 ] T M Addiscott, A P Whitmore
and D S Powlson, Farming,
Fertilizers and the Nitrate
Problem, CAB International
Wallingford, Oxon.,1991.
[2] O C Bockman and T Granli,
Human health aspects of ni-
trate intake from food and
water In Chemistry, Agricul-
ture and the Environment (ed
M L Richardson), The Royal
Society of Chemistry, Cam-
bridge, p. 373, 1991.
[3] D D Weisenberger, Potential
health consequences of
groundwater contamination
by nitrates in Nebraska. In
Nitrate Contamination : Ex-
posure, consequence and con-
trol, eds I Bogardi and RD
Kuzella, NATO ASI Ser. G:
Ecological Sciences 30,
Springer Verlag, Berlin,
pp. 309-315, 1991.
Address for Correspondence
Deepanjan Majumdar
Department of Environmental
Science
Institute of Science and
Technology for Advanced
Studies and Research (ISTAR)
Vallabh Vidyanagar
Gujarat 388120, India.
Email: joy_ensc@yahoo.com