Literature DB >> 31662710

Medical Treatment and Dose Estimation of a Person Exposed to Tritium.

Weibo Chen1, Houwen Li2, Kongzhao Wang2, Huahui Bian1, Youyou Wang1, Fengmei Cui3,4, Yulong Liu1,3,4, Qiu Chen3,4.   

Abstract

In this study, we aimed to investigate the damaging effects and clinical therapy of internal contamination with tritium to provide information and gain experience for medical treatments in case of an emergency due to a nuclear accident. Histories were taken by several doctors who observed and recorded the clinical symptoms of the patient described herein. The general health situation was evaluated by laboratory and equipment analyses. Tritium concentrations in the urine were estimated according to relevant standards during the monitoring period using a liquid scintillation counting method. Clinical observation revealed that the patient had symptoms of mild asthenia and sleep disorder with improvement after appropriate treatment. The last committed effective dose was determined through measurement of the urine tritium concentration and dose estimation and was estimated to be 0.123 mSv; the total effective dose was 14.536 mSv. The medical treatment and dose estimation in this patient with tritium contamination were successful and can provide a reference for similar cases in the future.
© The Author(s) 2019.

Entities:  

Keywords:  dose estimation; internal contamination; medical treatment; tritium

Year:  2019        PMID: 31662710      PMCID: PMC6796214          DOI: 10.1177/1559325819880670

Source DB:  PubMed          Journal:  Dose Response        ISSN: 1559-3258            Impact factor:   2.658


Introduction

Tritium is an important nuclide produced by a light nuclear fusion reaction and is also one of the major nuclides that negatively impact workers in radiation plants. With the continuous development of nuclear energy, the levels of tritium in the environment are increasing, and considering that tritium is affecting the health of humans, it is gaining more attention.[1-3] In particular, with the development of controllable thermonuclear fusion research at home and abroad, the commercial operation of controllable thermonuclear fusion reaction devices in the near future is also within sight. Such reactors produce approximately 10[4] times the amount of tritium produced by the fission reactors currently used in nuclear power plants; consequently, even if only some of this tritium is released into the environment, tritium emissions would still increase by hundreds of times. However, tritium facilities often have good protective preparations and strict management. However, in the process of producing tritium and using the maintenance equipment, accidental exposure or irradiation caused by an accident can still occur; thus, it is very important to seek timely and effective medical treatment for affected individuals. In recent decades, domestic and foreign scholars have conducted a series of studies on the biological effects and toxicity of tritium,[4,5] which has led to the accumulation of valuable experience for follow-up research. However, most of these studies have focused on laboratory animals, and tritium contamination in humans is still rare. We now report a case in our hospital of tritium contamination caused by an accident as follows.

Materials and Methods

General Information and Accident History

“Jia,” male, 42 years old, entered the maintenance department of a nuclear power plant 2 years ago, mainly conducting various welding operations; he had no previous exposure to radioactive materials. On February 25, according to the work plan, a working group added heavy water pipeline access to the system in a room. The working group consisted of 5 members: 1 work leader, 1 welder (Jia), 2 plumbers (responsible for cutting and grinding pipes), and 1 guard. The site construction started at approximately 10:30 on February 25. The work leader and 2 plumbers entered the negative-pressure shed and polished the holes in the pipeline. During the work, they wore plastic clothes and rubber gloves and used a ventilation hood. The drilling operation lasted approximately 15 minutes, during which approximately 11 L of residual heavy water in the pipe was collected. After polishing and reaming, there was still residual heavy water dripping at the opening. According to the chemical analysis results, the concentration of tritium in the spilled heavy water was 6.48 × 108 Bq/mL. After the completion of polishing and reaming, “Jia” began to weld the spot. Since it was difficult to carry out welding within the ventilation hood, “Jia” only wore an ice box filter. The welding work was completed at 13:15. At noon on February 26, the health physics staff found through a urinary tritium analysis of the workers that one worker (namely, “Jia”) had received unplanned tritium irradiation. The final effective tritium dose was 14.536 mSv after on-site medical decorporation. For further treatment, “Jia” was sent to our hospital at 19:30. Diuretic drainage and rehydration therapy were administered from the next day (February 26) to March 5, and he was discharged on March 7. After discharge, “Jia” continued to drink plenty of water and resumed normal work, but his urine sample monitoring continued until March 28.

Clinical Observation and Treatment

After admission to our hospital, several doctors evaluated “Jia” and took note of accidents, clinical symptoms, and so on. A comprehensive physical examination was performed to determine whether the mucous membrane of the skin was ruptured and inflamed. “Jia” was advised to drink a lot of tea, about 5 to 10 L per 24 hours and was administered a 40-mg furosemide injection for daily diuresis. Vitamins and electrolytes were provided, and sleep and blood circulation improved during hospitalization. The following laboratory and instrument inspections were performed: blood cell analysis, urine and stool routine, and electrolyte and biochemical examination; analysis of tumor markers (α fetal protein, carcinoembryonic antigen, carbohydrate antigen CA125 and CA199, prostate-specific antigen); T-cell subgroup analysis and thyroid function detection (triiodothyronine, thyroxine, thyrotropic hormone); chest X-ray; and abdominal B ultrasound examination. Meanwhile, changes to renal function (mainly blood creatinine) and electrolytes (mainly serum sodium and serum potassium) were monitored during hospitalization. A psychological assessment was carried out with the 16-personality factor (16PF) test.

Preparation and Analysis of Chromosome Samples

First, 0.5 mL of venous blood was taken from the patient and inoculated into a culture flask containing 4 mL of mixed culture medium and cultured at 37°C ± 0.5°C for 24 hours. Colchicine was added at a final concentration of 0.05 μg/mL, and the culture was continued for 48 to 52 hours, harvested, pelleted, and stained with Giemsa. The stained slides were scanned with a low-power microscope to observe the mitotic index and the degree of chromosome dispersion. Then, a good fission phase was selected, and all identifiable chromosomal aberrations were observed through microscopy. The distortion rate was calculated for fragments, dicentrics, centromeric rings, and translocations.

Reagents and Instruments

A 1220 QUANTULU liquid scintillation counter, manufactured by Perkin Elmer (Waltham, Massachusetts, USA); an OptiPhase HiSafe 3 scintillation fluid, manufactured by Perkin Elmer (Waltham, Massachusetts, USA); a 202A-S2 digital display thermostatic drying oven, manufactured by Shengwei Experimental Instrument Factory (Changzhou, China); a BP221S electronic balance, manufactured by Sartorius (Goettingen, Germany); and potassium permanganate (purity ≥99.5%) and sodium hydroxide (purity ≥96.0%), provided by Shanghai Reagent Factory (Shanghai, China), were used in the treatment process.

Sampling and Sample Preparation

For each urine sample, the middle segment of the urine was taken (∼30 mL mark in the sample cup), and the number and time was recorded. The first urine sample was taken on February 26 at 19:30, and all urine samples were collected for sample preparation and testing during the hospitalization period (February 26 to March 7); one urine sample was taken daily during the week after discharge (March 8 to March 14), and one urine sample was taken every 3 days after that (March 15 to March 28). The urine samples were treated with potassium permanganate using a dip color distillation method: A 30-mL urine sample plus 0.04-g potassium permanganate and 0.04-g sodium hydroxide were taken and distorted after shaking for approximately 20 minutes; the former 2 mL distillate was discarded, and 8 mL distillation liquid and 12 mL scintillation fluid was placed in 20 mL potassium-free glass bottle, oscillated for approximately 3 minutes, and placed in a liquid scintillation counter sample chamber for 12 hours.

Sample Measurement

First, the counting efficiency of a liquid flash counter for the urine sample was measured (the specific process is abbreviated), and the prepared urine samples were put into a liquid flash counter for measurement. The concentration of tritium in the urine was determined by software provided with the instrument and the following formula (1): where C is the urine tritium concentration, Bq/mL; N is the net count rate of the urine sample, min−1; E is the counting efficiency of the instrument for the sample; and V is the urine sample volume, mL.

Dose Estimation and Dynamic Observation

According to GBT16148-2009 “Rational radionuclide intake and internal radiation dose estimation specifications,”[6] the 95% confidence level during the effective dose monitoring period can be calculated using the following formula (2): where E is the effective dose produced by 2 adjacent periods (usually 1 day), Sv; C i is the urine tritium concentration measured by t i day, Bq/L; C i+1 is the urine tritium concentration measured by t i+1 day, Bq/L; and 4.8 × 10−11 is the dose coefficient of tritium, Sv/(Bq/L), which is calculated from the total dose of 1.15 × 10−12 Sv × standard reference of a person’s water intake of 42 L/d/Bq. Between 1% and 3% of tritium water (HTO) will be bound by the metabolite on carbon and become the organic-bound tritium (OBT). The half-life of this part of tritium is generally set to 40 days, and its contribution to the effective dose is approximately 10% during the entire cycle. If OBT is calculated, the dose coefficient in the above formula should be corrected by approximately 10%; then, formula (2) is corrected to formula (3) as follows: The last effective dose in the monitoring period can be calculated by formula (4). In the absence of other evidence, the reference data of International Commission on Radiological Protection (ICRP) are selected for the biological half-life in this study, which is 10 days.

Results

Clinical Manifestations

“Jia” did not appear to have obvious discomfort after the accident, but after admission into our hospital, he presented symptoms of mild fatigue; no obvious dizziness, headache, nausea, and vomiting; and mild sleep disturbance at night. Meanwhile, due to a large amount of water consumption, which was approximately 5 to 10 L/24 hours, the urine volume per 24 hours was approximately 10 to 13 L, with an average of 12.2 L. The results of the 16PF questionnaire administered to “Jia” showed that his performance was basically normal without obvious neuropsychiatric symptoms.

Laboratory and Instrument Inspection

T-cell subgroup analysis showed that the proportion of natural killer cells was 12.7%, which was slightly lower than the normal lower limit (13.0%). Biochemical examination showed that the blood glucose was high, and considering the past history of “Jia,” it was possible to consider a diagnosis of diabetes. Abdominal B-mode ultrasound showed enhanced echogenicity in the liver area, and because of this result combined with the blood lipid examination, he was considered to have a mild fatty liver. No obvious abnormalities were observed in the remaining examinations. During hospitalization, serum creatinine, serum potassium, and serum sodium were monitored, and the results fluctuated within the normal range. The data are presented in Table 1.
Table 1.

Renal Function and Electrolyte Results.a

DateSerum Creatinine (μmol/L)Serum Potassium (mmol/L)Serum Sodium (mmol/L)
February 26724.68141.5
February 27684.34140.2
February 28744.28138.2
March 1744.15135.6
March 2703.92135.8
March 3724.09138.4
March 4754.21137.9

a The normal range of serum creatinine in the clinical department of our hospital is 45 to 84 mmol/L, the normal range of serum potassium is 3.50 to 5.50 mmol/L, and the normal range of serum sodium is 135.0 to 145.0 mmol /L.

Renal Function and Electrolyte Results.a a The normal range of serum creatinine in the clinical department of our hospital is 45 to 84 mmol/L, the normal range of serum potassium is 3.50 to 5.50 mmol/L, and the normal range of serum sodium is 135.0 to 145.0 mmol /L.

Chromosomal Aberration Analysis

Results are presented in Table 2. The biological dose could not be estimated because the results were within the normal range.
Table 2.

Chromosomal Aberration Results.

Cell NumbersFragmentDicentricCentric RingTranslocationAberration Rate (%)
20020001
Chromosomal Aberration Results.

Results of Urine Tritium Concentration

In addition to the first urine tritium concentration data measured at the nuclear power plant on the day of the accident, the remaining data were measured during hospitalization and after discharge by looking at concentrations of tritium in the urine. On the first day of hospitalization (February 26), the urine concentration was 5.85 × 10[4] Bq/mL; it was 3.10 × 103 Bq/mL when discharged (March 7) and 1.48 × 10[2] Bq/mL during the last day of monitoring (March 28). The data are presented in Table 3; only values measured for the first urine sample per day are listed.
Table 3.

Results of Tritium Concentration Levels on Specified Dates.

DateTritium Concentration (Bq/mL)DateTritium Concentration (Bq/mL)
February 256.61E+04March 82.33E+03
February 265.85E+04March 92.10E+03
February 274.97E+04March 101.53E+03
February 283.68E+04March 111.23E+03
March 12.59E+04March 121.04E+03
March 21.85E+04March 139.82E+02
March 31.20E+04March 148.43E+02
March 48.43E+03March 175.97E+02
March 55.96E+03March 212.57E+02
March 64.04E+03March 242.28E+02
March 73.10E+03March 281.48E+02
Results of Tritium Concentration Levels on Specified Dates.

Dose Estimation

Based on the daily urine tritium concentration data, the effective dose produced by the daily dose can be estimated using formulas (3) and (4). The effective dose on the last monitoring day on March 28 was 14.413 mSv, and the last dose is estimated to be 0.123 mSv. Therefore, the final effective dose was 14.536 mSv. Daily specific data are provided in Table 4.
Table 4.

Effective Dose on Specified Dates.

DateEffective Dose on Specified Date (mSv)DateEffective Dose on Specified Date (mSv)
February 263.606March 913.737
February 276.738March 1013.843
February 288.869March 1113.924
March 110.397March 1213.992
March 211.464March 1314.050
March 312.180March 1414.103
March 412.681March 1714.228
March 513.033March 2114.327
March 613.275March 2414.369
March 713.458March 2814.413
March 813.609Last dose0.123
Effective Dose on Specified Dates.

Discussion

Because of the low β energy of tritium, the maximum range in soft tissue is only 5 μm, which is less than the thickness of the stratum corneum of the skin. Therefore, the external radiation damage by tritium is minor, and acute damage to the human body is mainly caused by internal radiation. Previous studies have shown that the symptoms of low-dose tritium exposure are more likely to occur in the early stages and are often relieved without special treatment. The main symptoms are dizziness, fatigue, loss of appetite, and sleep disorders.[7] The clinical manifestation in “Jia” was consistent with the literature, but the symptoms were relatively mild, which may be related to the dose and individual differences. In addition, these symptoms may also be related to the psychological effects on patients. A prolonged period of tritium exposure in vivo can cause a cumulative radiation effect due to the release of β rays, resulting in mutations and DNA damage to cells and possibly leading to malignant tumors. Although case reports of the carcinogenicity of tritium among humans have not been reported, a large number of animal studies have shown that the dose of tritium is positively correlated with the incidence of leukemia.[4] “Jia” was in the normal range of tumor targets, and it remains to be seen whether cancer will occur in the future. In normal individuals, the urine volume is approximately 1 to 2 L/24 hours, with an average of approximately 1.5 L. “Jia” consumed a lot of water, and after diuretic treatment, the urine volume per 24 hours was above 10 L, with an average of 12.2 L. This output is more than 8 times that for normal individuals, which had an obvious effect of diuresis and was conducive to rapid discharge of tritium in vivo. However, it is also important to note that excessive urination can lead to the loss of fluids and electrolytes, which can cause dehydration and electrolyte disturbances and even acute renal insufficiency. If the urine volume is increased, note that 10% of potassium chloride (20 mL/d) should be given intravenously to prevent hypokalemia. Therefore, attention should be paid to maintaining the balance of water and electrolytes, especially for renal function. In this study, the renal function and electrolytes of “Jia” were monitored during hospitalization, and their concentrations fluctuated within the normal range, possibly due to the intravenous supplementation of electrolytes. In recent years, Zuo X et al[8] carried out research on the toxicology of HTO and developed a traditional Chinese medicine compound named “Chahuangjing.” This composition, which requires further promotion and application, not only is diuretic and promotes the elimination of HTO but also removes free radicals in vivo to protect against HTO injury. Tritium in the urine is mainly composed of HTO and OBT. For reference, 97% of tritium is HTO, which is balanced with body water and is excreted in vitro with a biological half-life of 10 days; the remaining 3% of tritium are combined with organic molecules to form OBT and is excreted in vitro with a biological half-life of 40 days. The concentration of tritium measured by distillation refers only to the concentration of HTO, and OBT is often difficult to measure alone.[9-11] Lanxin[12] analyzed samples of 72 people exposed to tritium and concluded that the OBT concentration was the average of the HTO concentrations (5.4% ± 3.7%). In this study, factors of OBT were taken into account in dose estimation, the corresponding coefficients were modified appropriately, and the results were more objective. However, it was recommended by ICRP reference data for this location that the results could be due to the different environmental temperatures, the intensity of labor, age, and volatility, especially for patients who received medical treatment. Yong et al[13] studied a case of tritium contamination in a patient who received medical treatment. Through analysis of a large amount of urine tritium concentration results, the metabolic data of the individual were obtained, and the effective dose was estimated. The result was more accurate than the reference data, but the estimation process was more complex and still needs to be refined further and applied. In conclusion, the medical treatment of tritium contamination should be carried out as soon as possible. The final effective tritium dose of the present patient was 14.536 mSv, which exceeded the company’s maximum personal effective dose value (12 mSv) but was lower than the company’s management target value (15 mSv) and the national limit value (50 mSv). The early effects in the patient were consistent with the clinical manifestations of internal contamination of low-dose radionuclides, and the later effects remain to be observed after further follow-up. We plan to continue to monitor the results of routine blood tests, urine tritium levels, and chromosomal aberration analyses of the patient. The patient had a good prognosis after effective medical treatment, which provides experience for the management of similar cases. However, the level of occupational and environmental exposure during future fusion reactor operations is still unpredictable, but it is certain that the health problems and ecological impacts caused by tritium will remain a focus of concern. Therefore, it is still necessary to carry out in-depth studies on the mechanism of the toxic effects and ecological toxicology of tritium and to accumulate case data on human contamination with tritium to obtain an objective evaluation of the radiation toxicity of tritium. Click here for additional data file. Supplemental Material, Authorship_change_request_form for Medical Treatment and Dose Estimation of a Person Exposed to Tritium by Weibo Chen, Houwen Li, Kongzhao Wang, Huahui Bian, Youyou Wang, Fengmei Cui, Yulong Liu and Qiu Chen in Dose-Response
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Authors:  P Jean-Baptiste; E Fourré; A Dapoigny; D Baumier; N Baglan; G Alanic
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5.  Distribution of tritium in estuarine waters: the role of organic matter.

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6.  Relative biological effectiveness of tritium for induction of myeloid leukemia in CBA/H mice.

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7.  Comprehensive Review and Critical Evaluation of the Half-Life of Tritium.

Authors:  L L Lucas; M P Unterweger
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8.  Effects of Chahuangjing on Decorporation and Radiation Protection Against Tritiated Water.

Authors:  Xueyong Zuo; Qiu Chen; Houwen Li; Ke Zhang; Kongzhao Wang; Yu Tu; Mingjiang Hu; Fengmei Cui; Yulong Liu
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