I am 47years old and have returned to swimming as a fitness choice. I get 3 workouts of 2500yds/week and feel great. I also have an inground pool that my family enjoys in the summer months. My question relates to the long term consequences of chlorine exposure. Do studies exist that show whether swimmers have an increased health risk to cancers? Has anyone looked at pool chlorine exposure as a health risk in any way? The pools I swim in all use chlorine as a sanitizer and I would hate to think my exercise regimen may be doing me more harm than good!
Former Member
In regards to chlorine.
I recently read that chlorine kills the bacteria in your body- healthy and unheathly. The article even states that chlorine in your shower is a culprit which must be much less than the pool chlorine level.
I wonder what any swimming doctors think about this.
i tend to itch too if the chlorine levels are up,also my eyes still get sore even with goggles,i have to re shower when i get home .chlorine however does chemically remove greater nasties than it creates..the skin has natural oils and too much bathing removes these oils,this makes you itch..i too shower before and after entering the pool
Are there any chemistry whizes out there that can answer this?....Are Chlorine and Dioxin simillar enough to cause the same effects in the human body?? Dioxin has been proven to cause endometriosis in women. It has also been linked to many other health problems....just curious!
RESEARCH
In the course of preparing materials for the Swimming Science Journal, I came across the following articles concerning chlorinated pools. Abstracts of contents and appropriate comments are included below. Please read the discussion points and articles that follow the abstracts.
WHAT IS KNOWN
Exercising competitive swimmers absorb toxic levels of chlorine products in the course of a training session.
Training two or more times a day will not allow the toxins to be completely cleared from the body in most swimmers.
Children inhale more air per unit of body weight than mature persons, and have lesser developed immune and defense systems.
Young children absorb relatively greater amounts of toxins than older swimmers and therefore, are at greater risk.
In hyper-chlorinated pools, even dental enamel can be eroded because of the increased acidity in swimmers in training.
Exercise intensity and number of sessions increase the toxic concentrations in competitive swimmers.
Greater toxin absorption occurs through the skin than through breathing. However, the breathing action alone is sufficient to cause hypersensitivity and "asthma-like" respiratory conditions in at least some swimmers. The percentage of asthma-like symptoms in swimmers that is attributable to exposure to chlorinated hydrocarbons versus being unrelated to chlorine exposure is presently unknown. This is an area clearly deserving of further research.
Overchlorination is particularly hazardous to the health of swimmers.CHILDREN DEVELOP ASTHMA IN CHLORINATED POOLS
Bernard, A., Carbonnelle, S., Michel, O., Higuet, S., de Burbure, C., Buchet, J-P., Hermans, C., Dumont, X., & Doyle, I. (2003). Lung hyperpermeability and asthma prevalence in schoolchildren: unexpected associations with the attendance at indoor chlorinated swimming pools. Occupational and Environmental Medicine, 60, 385-394.
This study assessed whether exposure to nitrogen trichloride in indoor chlorinated pools may affect the respiratory epithelium of children and increase the risk of some lung diseases such as asthma.
Healthy children (N = 226), were measured for serum surfactant associated proteins A and B (SP-A and SP-B), 16 kDa Clara cell protein (CC16), and IgE. Lung specific proteins were measured in the serum of 16 children and 13 adults before and after exposure to NCl3 in an indoor chlorinated pool. The relation between pool attendance and asthma prevalence were studied in 1881 children. Asthma was screened with the exercise induced bronchoconstriction test (EIB).
Pool attendance was the most consistent predictor of lung epithelium permeability. A positive dose-effect relation was found with cumulated pool attendance and serum SP-A and SP-B. Serum IgE was unrelated to pool attendance, but correlated positively with lung hyperpermeability as assessed by serum SP-B. Changes in serum levels of lung proteins were reproduced in children and adults attending an indoor pool. Serum SP-A and SP-B were significantly increased after one hour on the poolside without swimming. Positive EIB and total asthma prevalence were significantly correlated with accumulated pool attendance indices.
Implications. Regular attendance at chlorinated pools by young children is associated with an exposure-dependent increase in lung epithelium permeability and increase in the risk of developing asthma, especially in association with other risk factors. It is postulated that increased exposure of children to chlorination products in indoor pools might be an important cause of the rising incidence of childhood asthma and allergic diseases in industrialized countries. Further epidemiological studies should be undertaken to test this hypothesis.
SWIMMING IN INDOOR POOLS ACCELERATES THE CONCENTRATION OF CHLORINATION CONTAMINANTS IN SWIMMERS
Aggazzotti, G., Fantuzzi, G., Righi, E., & Predieri, G. (1998). Blood and breath analyses as biological indicators of exposure to trihalomethanes in indoor swimming pools. Science of the Total Environment, 217, 155-163.
In this article, exposure to trihalomethanes (THMs) in indoor swimming pools as a consequence of water chlorination was reported.
Environmental and biological monitoring of THMs assessed the uptake of these substances after a defined period in competitive swimmers (N = 5), regularly attending an indoor swimming pool to train for competition during four sampling sessions. Analyses were performed by gas-chromatography and the following THMs were detected: chloroform (CHC13), bromodichloromethane (CHBrC12), dibromochloromethane (CHBrsC1) and bromoform (CHBr3). CHC13 appeared the most represented compound both in water and in environmental air before and after swimming. CHBrC1w and CHBr2C1 were always present, even though at lower levels than CHC13, CHBr3, was rarely present. In relation to biological monitoring, CHC13, CHBrC12 and CHBr2C1 were detected in all alveolar air samples collected inside the swimming pool. Before swimming, after one hour at rest at the pool edge, the mean values were 29.4 +/- 13.3, 2.7 +/- 1.2 and 0.8 +/- 0.8 micrograms/m3, respectively, while after spending one hour of swimming, higher levels were detected (75.6 +/- 18.6, 6.5 +/- 1.3 and 1.4 +/- 0.9 micrograms/m3, respectively). Only CHC13 was detected in all plasma samples (mean: 1.4 +/- 0.5 micrograms/1) while CHBrC1x and CHBr2C1 were observed only in few samples at a detection limit of 0.1 micrograms/1. After one at rest, at an average environmental exposure of approx. 100 micrograms/m3, the THM uptake was approx. 30 micrograms/h (26 micrograms/h for CHC1c, 3 micrograms/h for CHBrC12 and 1.5 micrograms/h for CHBr2C1). After one hour of swimming, the THM uptake was approximately seven times higher than at rest: a THM mean uptake of 221 micrograms/h (177 micrograms/h, 26 micrograms/h and 18 micrograms/h for CHC13, CHBrC12 and CHBr2C1, respectively) was evaluated at an environmental concentration of approx. 200 micrograms/m3.
Implication. Training for swimming in a poorly ventilated indoor swimming pool has the potential to cause illness through breathing undesirable concentrations of mainly chloroform.
CHLORINE PRODUCT ABSORPTION IN SWIMMERS IS GREATEST VIA THE SKIN
Lindstrom, A.B., Pleil, J.D., & Berkoff, D.C. (1997). Alveolar breath sampling and analysis to assess trihalomethane exposures during competitive swimming training. Environmental Health Perspectives, 105(6), 636-642
Alveolar breath sampling was used to assess trihalomethane (THM) exposures encountered by collegiate swimmers during a typical 2-hr training period in an indoor natatorium.
Breath samples were collected at regular intervals before, during, and for three hours after a moderately intense training session. Integrated and grab whole-air samples were collected during the training period to help determine inhalation exposures, and pool water samples were collected to help assess dermal exposures.
Resulting breath samples collected during the workout demonstrated a rapid uptake of two THMs (chloroform and bromodichloromethane), with chloroform concentrations exceeding the natatorium air levels within eight minutes after the exposure began. Chloroform levels continued to rise steeply until they were more than two times the indoor levels, providing evidence that the dermal route of exposure was relatively rapid and ultimately more important than the inhalation route in this training scenario. Chloroform elimination after the exposure period was fitted to a three compartment model that allowed estimation of compartmental half-lives, resulting minimum blood borne dose, and an approximation of the duration of elevated body burdens. It was estimated that dermal exposure route accounted for 80% of the blood chloroform concentration and the transdermal diffusion efficiency from the water to the blood was in excess of 2%. Bromodichloromethane elimination was fitted to a two compartment model that provided evidence of a small, but measurable, body burden of this THM resulting from vigorous swim training.
These results suggest that trihalomethane exposures for competitive swimmers under prolonged, high-effort training are common and possibly higher than was previously thought and that the dermal exposure route is dominant. The exposures and potential risks associated with this common recreational activity should be more thoroughly investigated.
Implication. In this study the greater importance of transdermal (via the skin) uptake of chlorinated hydrocarbons compared to the respiratory route is demonstrated. This indicates that improved ventilation alone will not have a major impact on exposure to these materials because it is being immersed in the liquid that is the greatest threat. In contrast, ozonation allows markedly reduced levels of chlorine in the pool water.
EXERCISING INCREASES THE TOXICITY OF A "SAFE" CHLORINATED POOL ATMOSPHERE
Drobnic, F., Freixa, A., Casan, P., Sanchis, J., & Guardino, X. (1996). Assessment of chlorine exposure in swimmers during training. Medicine and Science in Sports and Exercise, 28(2), 271-274.
The presence of a high prevalence of bronchial hyperresponsiveness and asthma-like symptoms in swimmers has been recently reported. Chlorine, a strong oxidizing agent, is an important toxic gas that a swimmer can breath during training in chlorinated pools.
Measurements of the chlorine concentration in the breathing zone above the water ("safe" levels, it is a swimmer's exercising that produces abnormal levels of exposure to this toxin.
There has not been sufficient research to even begin understanding the health effects of this repetitive exposure.
AMOUNT OF EXERCISE IS RELATED TO CHLORINE-RELATED CONCENTRATIONS IN THE BODY
Cammann, K., & Hubner, K. (1995). Trihalomethane concentrations in swimmers' and bath attendants' blood and urine after swimming or working in indoor swimming pools. Archives of Environmental Health, 50(1), 61-65
The influence of working or swimming in indoor swimming pools on the concentrations of four trihalomethanes (haloforms) in blood and urine was investigated. Different groups (bath attendants, agonistic swimmers, normal swimmers, sampling person) were compared.
The proportions of trihalomethanes in blood and urine correlated roughly with those in water and ambient air. Higher levels of physical activity were correlated with higher concentrations. Within one night after exposure in the pool the blood concentrations usually were reduced to the pre-exposure values. Secretion of trichloromethane in urine was found to be less than 10%.
Implication. Exercising in a chlorinated pool increases the levels of assimilation of chlorine related gases. The greater the amount of exercise, the greater the concentrations. Thus, hard training swimmers are at greater risk than more sedentary pool attendants and coaches.
It takes at least one night for absorbed substances to be removed. If insufficient time exists between training sessions the possibility of toxic build-up is real.
It takes at least one night for absorbed substances to be removed. If insufficient time exists between training sessions the possibility of toxic build-up is real.
Ok what does one night mean? 8 hours? 22hours? Or does something happen when you're sleeping to rid the body of toxins?
Just thinking if you're doing 2 a day at 5am and 5pm...is there a "night's worth" of time in there?
Rich
Well all of this depends on the pool you swim in!
I swim in Christchurch New Zealand. Heated indoor and chlorinated!
I can smell the chlorine the next day from my skin, and this maybe after 2 showers with complete washes with soap.
I also have cancer and I am fighting this from every direction I can. I am very fit, however I now understand cancer. I simply cant take the risk of adding to the long list of chemicals we are already exposed to.
Don't worry I will beat it, however I found the above study in my search for answer's.
If did not have cancer and lead a life that assisted in my bodies own immune system to fight against cancer buildup then I would continue to swim as I believe the benefit outweighs the risk.
It's all in moderation, however the lower the chlorine level the better!!
This is an old thread, wonder if there are folks, like me, interested in this topic? Any new development? If you swim 7 days a week, 1 hour each time, in a heavily chlorinated pool, does it take months or years for the serious harm to be done? The place where I swim, the pool is many floors up on top of the building (indoor pool), but you can already smell very strong chlorine at the building entrance on street level.
This is an old thread, wonder if there are folks, like me, interested in this topic? Any new development? If you swim 7 days a week, 1 hour each time, in a heavily chlorinated pool, does it take months or years for the serious harm to be done? The place where I swim, the pool is many floors up on top of the building (indoor pool), but you can already smell very strong chlorine at the building entrance on street level.
I'm wondering if the street-level chlorine odor is an artifact of how the building is vented, espec if it is an older building.
I'm definitely not an expert, but my take on the above-referenced studies is that you probably do not have the type of exposure that would cause serious harm in a normal, healthy person. The one study I read on exposure in elite swimmers looked at those who swam exhaustively many hours a day. Perhaps it would help to reread the abstracts put up by "daggles69" and note the study groups: "competitive swimmers," "intense training," "two hours" (or more) per day, in a poorly ventilated pool area. If you are highly concerned or have a predisposing condition, you may be able to find a pool that does not use chlorine; the newer ones are more commonly using alternatives.
I'm wondering if the street-level chlorine odor is an artifact of how the building is vented, espec if it is an older building.
The odor definitely comes from the pool. The building is very new. I do hope it takes years and years of intense training for the harm to be done. OTH given the very strong smell in this place perhaps a few months is bad enough. The smell of chlorine on my skin remains the next day like daggles69.