Miguel’s mother brought her 3-month-old son to a rural clinic for an urgent care visit. Miguel was vomiting and had diarrhea. Among his other worrisome symptoms were cyanosis, drowsiness, and rapid breathing. His physician told his mother he needed to go to the nearest ER by ambulance and she agreed. At the ER, they were rushed into an exam room, with the baby on oxygen.
Miguel was found to have central cyanosis which had not improved despite the oxygen. After talking to his mother about the baby and their living situation, the ER physician ordered some specialized blood tests, co-oximetry, and a methemoglobin level. The infant was diagnosed with methemoglobinemia, and therapy was started, alleviating the cyanosis almost immediately. Miguel went home on the second hospital day with no evidence of brain damage from hypoxia.
Miguel was the fifth child seen in the hospital over an 8-week period with methemoglobinemia. The doctors believed all the cases were caused by nitrate toxicity. The widespread use of nitrate fertilizers increases the risk of water contamination in rural areas. Infants under 4 months of age are at particular risk of nitrate toxicity from contaminated water. Physicians suspected that the water Miguel’s mother was mixing with his powdered formula was contaminated with nitrates.
Her primary doctor at the rural clinic told her, “your well water is probably contaminated. So you see, Miguel’s blood has been changed by this water; it can’t transport oxygen from the air he breathes around his body. So, that’s why he was turning blue. It was dangerous. He needs safe water in his formula. Try finding some bottled water for now.”
The case of Miguel illustrates how exposure to a toxin that can be lethal for infants may be overlooked because the resulting condition is not a reportable disease. Miguel responded to treatment for a diagnosis secondary to nitrate exposure with no recognized sequelae. The hospital staff was attuned to the condition because Miguel was the fifth child seen with a diagnosis of methemoglobinemia during an 8-week period. By contrast, Wisconsin, a state which has had an active surveillance program for methemoglobinemia, identified eight cases from 1990 to 1999, three of which involved infants with formula prepared with water from nitrate-contaminated wells .
This extremely high incidence could be considered a public health threat, so it is appropriate for the hospital staff or pediatrics department that recognized the trend to notify the county or state public health department. More than 2,000 cases have been reported worldwide and sporadically in the United States since the first case of a fatal ingestion by an Iowa infant of nitrate-contaminated well water was reported in 1945 [2, 3]. Other sources of acquired methemoglobinemia include nitrate-contaminated food and medications such as benzocaine (used for teething), lidocaine, sulfonamides, and topical silver nitrates used for burns [2, 4, 5].
Physicians who see infants 6 months and younger with cyanosis in agricultural or rural areas should consider the possibility of nitrate-contaminated rural drinking water. The disease is more common in infants who are bottle-fed with formula that has been diluted with water from private wells than in breast-fed infants. Boiling water used to dilute formula increases the concentration of nitrates, but breast milk does not appear to be affected by maternal consumption of contaminated water .
Nitrates are one of the most common water contaminants found in agricultural states. An estimated 43 million U.S. citizens—15 percent of the population—are served by private well water, and 4 percent of the wells in one national sample had nitrates above the federal drinking-water standard of 10 mg/L nitrates . In Wisconsin, 6.5 percent of private wells sampled had nitrate levels above the federal standard . This study identified the following associations with elevated well water nitrate levels: (1) living on a farm, (2) lower annual incomes, and (3) older and shallower wells than families whose wells were low in nitrates . A study in upstate New York identified 15.7 percent of sampled wells as having above-standard levels and found a positive association between larger farms and higher percentages of samples with elevated nitrate levels .
An environmental health history should be obtained from the parents of children diagnosed with methemoglobinemia, asking where their water supply comes from, whether other household members have had similar problems, and what the parents’ occupations are . Further questioning of medications used, folk remedies, and breast-feeding status of the infant is a critical component of the environmental history. Infants may have other illnesses and may have dehydration, acidosis, and diarrhea from wells contaminated from coliforms, often associated with elevated nitrate levels. Where these conditions are present, physicians may fail to consider a diagnosis of methemoglobinemia.
Infants less than 4 months old are susceptible to methemoglobinemia due to a number of physiological factors: (1) alkaline gastric conditions increase gastrointestinal microflora which convert nitrates to nitrites; (2) lower circulating hemoglobin levels and higher fetal hemoglobin, which is more susceptible to oxidation; and (3) decreased amount of methemoglobin reductase [4, 5, 11]. Methemoglobin is oxidized hemoglobin and is incapable of carrying oxygen to tissues. After 4 months of age the gastrointestinal environment becomes more acidic and alters the microbial flora, methemoglobin reductase levels increase, and the proportion of fetal hemoglobin decreases to the point that there is less susceptibility to methemoglobinemia. The normal level of circulating methemoglobin in healthy individuals is less than 1 percent .
The maximum contaminant level (MCL) standard for nitrates set by the Environmental Protection Agency applies only to municipal water supplies since private wells are not subject to federal regulation . Private water supplies do, however, fall under state health advisories in many if not all states. The advisories recommend that private well owners monitor nitrate levels every 2 to 3 years—or yearly if elevated nitrate levels have been previously detected—test for coliforms, and maintain nitrate levels below 10 mg/L nitrate. Monitoring annually is also recommended if there are infants under 6 months of age in the household or pregnancy is anticipated. Routine testing should be scheduled during the late spring or early fall of the year when the nitrate levels would be at the highest due to fertilizer application or rainfall .
Discharge planning should include education of the parents about environmental contamination of drinking water and safe drinking water for the family members at risk. Questions have been raised about chronic consumption of nitrate-contaminated drinking water and illnesses such as cancer and reproductive health concerns, but evidence is equivocal for such associations [2, 14]. Reproductive concerns include complications and adverse outcomes such as anemia, preeclampsia, threatened spontaneous abortions, premature labor, neural-tube defects, low birth weight, congenital cardiac defects, and other congenital malformations. Not all studies identify sufficient evidence of a causal relationship between these outcomes and exposure to nitrates in drinking water . Nevertheless, the goal should be avoidance of exposure above the federal standard, which is set to prevent methemoglobinemia in infants. Resuming the same patterns of diluting the infant’s formula with water contaminated with high levels of nitrates will increase the likelihood of a recurrence of methemoglobinemia.
The drinking water source should not be used until the water has been tested for nitrates. Testing can be arranged by contacting the public health department and requesting that the county public health nurse arrange for evaluation of the water supply at the family’s residence and take steps to coordinate the evaluation of the drinking water source of the other children with observed methemoglobinemia. If the family has not given permission to share its information with public agencies, be sure to review HIPAA regulations on release of personal health information.
Methemoglobinemia is generally not a reportable disease; few states have surveillance programs for methemoglobinemia, and there may not be another method for informing public health professionals that a community environmental health risk may exist. Because Miguel, in our case scenario, is the fifth child to have this diagnosis in a short period of time and in the same region, a common source of nitrate contamination that could lead to additional cases of toxicity should be sought. Mapping of the recent cases of methemoglobinemia and the associated water supplies to identify a common point source of pollution falls under the responsibility of the state epidemiologist of the public health department or state environmental control agency. An excellent account of the classic work of John Snow and others in unraveling the source of cholera in London and the role of epidemiological mapping was published in 2006 .
If the families of affected infants are migrant workers living in camps or other housing provided by their employers, the Occupational Safety and Health Administration (OSHA) should be contacted by the health professional or the employees of the agricultural operation. OSHA regulates migrant housing, and the housing inspection checklist addresses proper location and maintenance of wells and requires that the housing have an adequate water supply that has been approved by the appropriate health authority . Some states, such as Ohio, also mandate testing of potable water for coliforms and nitrates on a regular basis as part of migrant labor-camp oversight .
Families that are not documented and do not have valid visas or worker permits may not cooperate with a public health referral. Promotores—lay health educators serving the Hispanic community—are excellent community resources who aid in health efforts and outreach and may help persuade the families to allow public health or environmental regulatory agencies to test the water and provide abatement. Migrant labor camps, federally funded neighborhood clinics, and community health centers in many states have promotores [19, 20]. Testing well water for coliforms and nitrates (usually done together) costs from $7 to $25 and $20 to $40, respectively, per test and is usually carried out at the well owner’s expense .
The only effective methods of lowering nitrate levels at the point of entry into the house are reverse osmosis, ion exchange, or distillation devices . These devices are expensive and must be monitored because they can fail. Activated charcoal filters at the faucet or point-of-use are not effective. The end result may be that the family must move or buy bottled water to prepare formula for bottle feeding.
Practitioners who are not experienced in treating methemoglobinemia should consult the regional poison-control center or a medical toxicologist for aid in managing cases of methemoglobinemia. The hospital staff treating the children with methemoglobinemia in our case scenario should offer continuing medical education and public outreach to address a significant environmental health concern in their service area and increase awareness of potentially lethal exposures not otherwise commonly seen by the majority of practitioners. For online resources, see the CDC Agency for Toxic Substance and Disease Registry Case Studies in Environmental Medicine, nitrate/nitrite toxicity , the CDC National Agricultural Safety Database , and the EPA safewater homepage .
- Knobeloch L, Salna B, Hogan A, Postle J, Anderson A. Blue babies and nitrate-contaminated well water. Environ Health Perspect. 2000;108(7):675-678.
Gehle K; Agency for Toxic Substances and Disease Registry. Nitrate/nitrite toxicity. Case studies in environmental medicine (CSEM).http://www.atsdr.cdc.gov/csem. Accessed April 25, 2009.
- Comely HH. Landmark article Sept 8, 1945: cyanosis in infants caused by nitrates in well-water. JAMA. 1987;257(10):2788-2792.
- Wright RO, WJ Lewander, Woolf AD. Methemoglobinemia: etiology, pharmacology, and clinical management. Ann Emerg Med. 1999;34(5):646-656.
Price D. Methemoglobin inducers. In:Flomenbaum NE, Goldfrank LR, Hoffman RS, Howland MA, Lewin NA, Nelson LS, eds. Goldfrank’s Toxicologic Emergencies. 8th ed. New York, NY: McGraw-Hill; 2006:1734-1745.
Etzel RA, Balk SJ. Nitrates and nitrites in water. In: Etzel RA, Balk SJ, eds. Pediatric Environmental Health. 2nd ed. Elk Grove Village, IL: American Academy of Pediatrics; 2003: 301-306.
DeSimone LA, Hamilton PA, Gilliom RJ. Quality of water from domestic wells in principle aquifers of the United States, 1991-2004: overview of major findings. Geological Survey Circular 1332. 2009. http://pubs.usgs.gov/circ/circ1332/includes/Circular1332.pdf. Accessed April 30, 2009.
- Schubert C, Knobeloch L, Kanarek MS, Anderson HA. Public response to elevated nitrate in drinking water wells in Wisconsin. Arch Environ Health. 1999;54(4):242-247.
- Gelberg KH, Church L, Casey G, et al. Nitrate levels in drinking water in rural New York State. Environ Res. 1999;80(1):34-40.
Frank Al, Balk S; Agency for Toxic Substances and Disease Registry. Taking an exposure history. Case studies in environmental medicine (CSEM). http://www.atsdr.cdc.gov/HEC/CSEM/exphistory/index.html. Accessed May 1, 2009.
- Knobeloch L, Proctor M. Eight blue babies. WMJ. 2001;100(8):43-47.
US Environmental Protection Agency. Ground water & drinking water. http://www.epa.gov/safewater/index.html. Accessed April 25, 2009.
Glanville T. Make sure drinking water is safe. Iowa State University Fact Sheet Pm-1563g. 2002. www.cdc.gov/nasd/docs/d001001-d001100/d001074/d001074.pdf. Accessed on May 1, 2009.
- Mensinga TT, Speijers GJ, Muelenbelt J. Health implications of exposure to environmental nitrogenous compounds. Toxicol Rev. 2003;22(1):41-51.
- Manassaram DM, Backer LC, Moll DM. A review of nitrates in drinking water: maternal exposure and adverse reproductive and developmental outcomes. 2006. Environ Health Perspect. 2006;114(3):320-327.
Johnson S. The Ghost Map. The Story of London’s Most Terrifying Epidemic and How It Changed Science, Cities, and the Modern World. New York, NY: Penguin Books; 2006.
US Department of Labor. Temporary labor camps. CFR 1910.142. OSHA standards. http://www.osha.gov/pls/oshaweb/owadisp.show_document?p_table=standards&p_id=9791. Accessed April 25, 2009.
Sachs T, Espinoza F, Fleming R. Operating an agricultural migrant labor camp in Ohio. Ohio State University Extension Fact Sheet. FLR-1-01. http://ohioline.osu.edu/flr-fact/0001.html. Accessed May 1, 2009.
Nichols DC, Berrios C, Samar H. Texas’ community health workforce: from state health promotion policy to community-level practice. Prev Chronic Dis. 2005. http://www.pubmedcentral.nih.gov/articlerender.fcgi?artid=1459466. Accessed May 1, 2009.
Migrant Health Promotion. Who are promotores(as)? http://www.migranthealth.org/our_programs/who_are_promotora.php. Accessed May 1, 2009.
Minnesota Department of Health. Well management: nitrate in well water. http://www.health.state.mn.us/divs/eh/wells/waterquality/nitrate.html. Accessed May 1, 2009.
Woodward J, Parrott K, Ross B. Nitrates in household water. Virginia cooperative extension. http://www.cdc.gov/nasd/docs/d001201-d001300/d001233/d001233.html. Accessed May 1, 2009.
US Centers for Disease Control. National Agricultural Safety Database. http://www.cdc.gov/nasd/. Accessed May 1, 2009.