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Journal of Toxicology
Volume 2010 (2010), Article ID 313280, 7 pages
http://dx.doi.org/10.1155/2010/313280
Research Article

An Outbreak of Hepatic Veno-Occlusive Disease in Western Afghanistan Associated with Exposure to Wheat Flour Contaminated with Pyrrolizidine Alkaloids

1Ministry of Public Health, Kabul, Afganistan
2London School of Hygiene and Tropical Medicine, Keppel Street, London WC1E 7HT, UK
3World Health Organisation, Geneva, Switzerland
4National Institute for Public Health & the Environment, RIVM, 3720 BA Bilthoven, The Netherlands

Received 16 November 2009; Revised 19 February 2010; Accepted 16 May 2010

Academic Editor: Peter John O'Brien

Copyright © 2010 Faizullah Kakar et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract

Pyrrolizidine alakloids (PAs) are known to cause hepatic veno-occlusive disease (VOD). Outbreaks have occurred in Western Afghanistan since 1974, the latest in February 2008. We conducted an outbreak investigation using a case-control design. Sixty-seven cases of VOD were compared with 199 community controls. Consumption of bread was strongly associated with disease (adjusted odds ratio: 35.8 [95%CI: 7.6–168.2]). Toxic doses of PA were found in plant extracts and in samples of wheat flour taken from the study area. Compared to wheat flour there was 1000 times less PA in milk and whey and in water samples the PA content was zero. Although direct analysis was not possible, contaminated wheat flour used to make bread was the likely source of PA causing the outbreak. Eating a more varied diet including meat and fruit may be protective. Prevention and control measures will rely on community awareness and agricultural interventions to ensure safety of the food supply.

1. Introduction

Hepatic veno-occlusive disease (VOD), where toxic exposure causes rapid onset of massive ascites, has historically been called Gulran Disease in Afghanistan because it has consistently occurred in Gulran district of Herat Province, Western Afghanistan. While first reported as “bread poisoning” in 80 cases in South Africa in 1920 [1] and then as “camel belly” in about 1500 cases in Uzbekistan starting in 1931 and 1945 [2], the largest outbreak ever reported was from 1974 to 1976 in Gulran District affecting an estimated 7800 people with about 1600 deaths. “Gulran Disease” was attributed to consumption of bread made from wheat contaminated with seeds of a weed, locally called charmac [3], and hepatic veno-occlusive disease was diagnosed on liver biopsy [4]. The weed plant species was identified as Heliotropium popovii H. Riedl subsp. gillianum H. Riedl and was shown to contain pyrrolizidine alkaloids (PAs), primarily heliotrine [5].

Numerous PAs have also been found to cause VOD and as many as 3% of the world’s flowering plants (6000 species) contain PAs [6]. PAs are not toxic per se but undergo metabolic oxidation by hepatic multifunction oxidases to pyrrole derivatives, which then undergo hydrolysis to strongly alkylating metabolites [7]. The dose and duration of exposure to heliotrine required to produce liver damage in humans has been previously estimated as 4–10 mg/kg per day for 3–7 weeks [8]. WHO has indicated that the lowest intake causing disease may be 1 mg total PAs per day for a 70 kg adult [9], and German regulations for herbal remedies establish a maximum oral intake of 1 microgram per day [10].

Without effective action in the interim, a second outbreak occurred from 1999 to 2001 with estimated 400 cases and over 100 deaths [11], and on 19 February 2008, Afghanistan’s outbreak and disease surveillance system, the Disease Early Warning System (DEWS) team responded to rumors of a further outbreak of Gulran Disease in the same district. They identified 38 cases of massive ascites and four deaths which appeared to be associated with consumption of contaminated wheat flour [12].

The DEWS Team noted that farmers were not convinced of the cause of disease pointing out that the charmac weed is present every year throughout Gulran District, but the disease was reported from only five out of 230 villages. Furthermore, in large households, only one or two persons had the disease yet they all ate the same bread made from the same flour. In response to the outbreak, we conducted a case-control study amongst the population of Gulran District in order to better understand specific risk factors and to help guide control measures.

2. Methods

2.1. Study Area

Gulran district has an area of approximately 150 km2 with a population estimated at 110,000 people [13]. It consists of undulating hills with scanty vegetation serving as pasturelands. Water is scarce, salty in some places, and obtained from shallow wells and small springs. During winter the villages are snowbound and totally isolated. The inhabitants are illiterate, mostly wheat farmers who also may raise legumes, and many keep sheep and goats. Their diet consists of wheat bread and occasionally meat. In 2007-2008 the level of rain was normal and there were no reports of water shortages.

2.2. Selection of Cases and Controls

Active case detection was conducted, starting with cases from the District Hospital and then going house-to-house in villages of the cases. Cases were defined as having all three of the following: (1) residence in Gulran district; (2) acute appearance of massive ascites occurring in the last 6 months; and (3) no edema on face and arms. Two controls were matched by age-group and sex with each case and systematically selected, from neighboring households in the same village, and from other nearby villages which had not reported cases. One additional control was selected from within affected households, although it was not possible to match these controls for age group. Sample size for analysis included all cases identified during the active case detection.

2.3. Procedures and Questionnaire

All activities were conducted under the auspices of the Ministry of Public Health of Afghanistan. The case-control study was conducted as part of an outbreak investigation, and verbal consent was obtained from cases and controls prior to interview. Interviews were conducted in April and May 2008.

Cases and controls were interviewed in local language (Persian Dari) by trained Afghan surveyors using a structured questionnaire format. The questionnaire consisted of six sections: Demographic and socioeconomic details including farm size, number of animals, and water availability; clinical and treatment history; food consumption history; food and wheat preparation; knowledge of VOD; and a mortality report to ascertain if any household members had died of suspected VOD in the last six months.

Because food consumption differs considerably between seasons, cases and controls were asked about frequency of consumption of 33 food items commonly consumed in Afghanistan during a typical week in the winter and in the summer. Assuming flat-bread (naan) consumption to be ubiquitous, we asked how often bread was consumed as the only food in a meal.

Serum was collected from both cases and controls and analyzed for levels of aspartate aminotransferase (SGOT), alanine aminotransferase (SGPT), bilirubin, Hepatitis B, and Hepatitis C.

Samples of flour, grain, and plant materials were collected where it was available (as a convenience sample) from the houses of cases and controls and stored for later analysis for PA content. As goats graze on the charmac weed, we also collected samples of goat’s milk, the dried whey product called qurut, and water to examine if PAs are present [14].

2.4. Laboratory Methods

PA content was assessed by means of liquid chromatography/mass-spectrometry. Test portions (flour, qurut, and milk) were weighed and extracted with a solvent mixture of 30% water and 70% methanol, containing 5% acetic acid (flour and qurut) or with 100% methanol containing 0.1% acetic acid (milk). After centrifugation, an aliquot was taken from the clear supernatant and evaporated to dryness. The residue was resuspended in water, containing 0.1% acetic acid. An aliquot of the extract was filtered and analysed using LC/MS/MS (Acquity UPLC BEH C18 column, water containing 0.1% acetic acid/acetonitrile gradient, Ultima Pt). Standards of lycopsamine, heliotrine, heliotrine N-oxide, retrorsine, senecionine, echimidine, jacobine, jacobine N-oxide, trichodesmine—and at a later stage also lasiocarpine—were available. PAs for which no standards were available were quantified using standards of the above-mentioned PAs having a similar structure. During the analytical sessions, duplicate determinations were performed at regular intervals. Method recovery percentages were close to 100%. Therefore, the results were not corrected for recovery. The results of the duplicate determinations were within the expected variability, associated with possible inhomogeneity of samples and analytical methodology. In the blanks no PAs were found.

2.5. Statistical Issues

We assessed different exposure factors using univariate and multivariate analysis. Potential confounders were identified on an a priori basis and included in multivariate logistic regression analysis. A restricted analysis was also conducted which separately examined the different categories of controls. Secondarily, an analysis was conducted which compared exposure factors between cases and cohabiting controls in order to assess intrahousehold differences, if any.

To assess food consumption, we first reviewed the frequency of consumption of each food item. Then, removing those items rarely eaten, we developed index scores for five different food groups, summing the number of times each food item was reportedly eaten weekly in summer and in winter, and totaling food items in each of five food groups. Components of each food group were as follows. Protein: meat (beef, lamb, and goat), liver, chicken, goat milk, cow milk, qurut, yogurt, egg, chickpeas, lentil, and beans; Dairy: goat milk, cow milk, egg, yogurt, and qurut; Pulse: peas, lentils, and beans; Fruit: apple, melon, and watermelon; and Vegetables: carrot, and tomato. The food group scores were then divided into ordinal categorical variables. Protein consumption was categorized into quartiles, while other food groups were categorized into binary variables, either above or below the median score or classified as “ever” or “never” consumed. Frequency of sole bread consumption was similarly summed across seasons and categorized by quartiles. In addition, an overall food consumption level was assessed using the sum of all index scores divided into quartiles.

Socioeconomic status was assessed using principle components analysis [15] with household assets, employment, and education of head of household serving as variables in the model to define socioeconomic quartiles.

3. Results

3.1. Epidemiological Assessment

In total, 67 residents of Gulran district met the case definition and were included in the study. Cases were identified from among 28,443 individuals surveyed, including 3,700 households, the district and provincial hospital, and affected clinics in Gulran district. Point prevalence was 0.24% [95%CI 0.18–0.3%]). Table 1 shows enrollment characteristics of cases and controls. Self-reported onset of symptoms was reported progressively from October 2007, with a peak of 14 cases in February 2008. All cases reported exposures in Gulran district and enhanced surveillance in surrounding districts revealed no additional cases. By local report, a small number of cases sought care in neighboring Iran and are not included here.

tab1
Table 1: Demographic characteristics of cases and controls.

One-hundred and ninety-nine controls met the inclusion criteria and were included in the study. Nineteen of these (9.5%) were from the households of cases, 99 (47.7%) were from the same village as cases, and 81 (40.7%) were from villages in unaffected areas. The study was designed as a frequency matched study for age group and sex so there were no differences in proportion of each of these variables between cases and community controls, although there was a nonsignificant difference in age group between household cases and controls (Table 1).

Table 2 shows results from risk factor analysis. Those who frequently consumed bread as the sole item in a meal had higher odds of disease; (adjusted odds ratio (AOR) 35.8 [95%CI: 7.6–168.2]) and those who had relatively high protein consumption were at decreased risk of disease (AOR: 0.1 [95%CI: 0.02–0.9]). High rice consumption (suggestive of high carbohydrate diet) was associated with disease (AOR: 2.6 [95%CI: 1.1–5.9]). High fruit consumption was negatively associated (AOR: 0.2 [95%CI: 0.06–0.6]). The magnitude of the association with carbohydrate and fruit intake compared to that for bread and protein consumption suggests that these are minor contributory factors. Water source other than a spring (well, pump, or other source of water) was associated with disease. There was no clear trend in the association of socioeconomic status to odds of disease. Having charmac growing on the household’s land was associated with disease (AOR: 8.5 [95%CI: 2.1–33.1]). The level of consumption of individual food stuffs was also examined individually, but no single item appeared to be associated with disease. Amongst these were qurut and other dairy products (goats and cows milk, yogurt).

tab2
Table 2: Univariate and multivariate analysis of potential exposure factors for hepatic veno-occlusive disease in Gulran District, Afghanistan, 2008. Odds ratios presented with 95% confidence intervals in parentheses.

Controls ( ) who cohabited with cases ( ) were assessed using Mantel-Heintzel test for trend. Within households, frequent consumption of bread as the sole food item was associated with disease, controlling for protein level (MH-OR 2.7 [95%CI: 1.3–5.5]). By this analysis, none of age, sex, or other food intake levels were associated with disease on univariate analysis.

Liver function was also measured amongst cases and controls. Analysis shows that cases more frequently had elevated levels of aspartate aminotransferase (SGOT), alanine aminotransferase (SGPT), bilirubin, and mean (and geometric mean) levels differed between cases and controls (Table 3). Tests for hepatitis B antigen and hepatitis C were also conducted to be assessed as risk factors for disease, but difference in prevalence between cases (Hep B: 7.6%; Hep C: 1.5%) and controls (Hep B: 2.6%; Hep C: 1.0%) was not significant.

tab3
Table 3: Comparison of liver function between cases and controls, Gulran District, Afghanistan, 2008.
3.2. Laboratory Analysis for PAs

During the survey samples of flour, grain, qurut, and plant matter were collected. Thirty-two samples of flour were collected from a convenience sample of 17 households and analysed for PA by LC/MS/MS. Median total concentration of PA in these flour samples was 4.0 mg/kg. Amongst samples taken from the houses of cases ( ), median concentration of total PA was 5.6 mg/kg (95%CI: 0.4–38.38), whereas amongst controls ( ) the median concentration was 2.7 mg/kg (95%CI: 0.4–4.0) (Wilcoxon rank-sum test: , ). Heliotrine, lasiocarpine and heliotrine-N-oxide were detected in all flour samples with higher levels of heliotrine found in samples from the houses of cases (Wilcoxon rank-sum test: , ) (Table 4). A chromatogram of a sample of wheat grain collected in a suspected area is given in Figure 1. Samples of stems and leaves ( ), roots ( ) and seeds ( ) of the charmac plant also contained PAs (Table 5).

tab4
Table 4: PA content of thirty-two flour samples collected from affected villages, Gulran District, Afghanistan, 2008.
tab5
Table 5: PA content of four specimens of charmac plant matter collected from affected villages, Gulran District, Afghanistan, 2008.
fig1
Figure 1: Chromatogram of wheat sample from a suspected area. The traces (mother daughter ions) shown are those from the strongest transition of the two traces acquired for each PA.

PA concentration from the 32 flour samples was categorized into 3 groups on a logarithmic scale from 0-1 mg/kg, 1–10 mg/kg, and 10–100 mg/kg. PA levels in flour were higher amongst those who had charmac growing on their land (Fisher’s exact, ), those who had charmac growing amongst their wheat (Fisher’s exact, ), and those whose primary source of wheat was their own land (Fisher’s exact, ). There was a trend to suggest that samples collected from cases were more likely to be in the higher PA level (10–100 mg/kg) ( [95%CI: 0.7–491.7], ) although the sample size is small for this analysis.

Qurut and water samples were also analyzed as a possible source of PA in the diet. Water samples contained no PAs but they were found in the qurut samples (median concentration, 0.09 mg/kg [range: 0–0.6]). The ratios between heliotrine and heliotrine N-oxide in the qurut samples (derived from goats milk) were reversed compared to those in the flour samples. This can be expected because of metabolic action in the goat. Therefore, contamination of these samples with flour is unlikely. Large amounts of trichodesmine, a PA not found in the charmac or wheat samples, were also found.

4. Discussion

Identified cases were significantly more likely than controls to report frequent consumption of bread and samples of flour were found to be contaminated with high levels of PA. The principle source of PA appears to be wheat flour contaminated with the seeds of the Heliotropium plant which commonly grows with wheat in this area. A secondary, though minority, source is likely to be qurut (whey) from the milk of goats which have ingested plants containing PAs while grazing. Consumption of a high ratio of bread to other food-item consumption was strongly associated with disease, while a diet high in protein appeared to be protective. This association was also seen within households, using a matched analysis which may result from different behavioral factors related to diet within the household. It seems likely, therefore, that a combination of prolonged, regular exposure to contaminated wheat in the presence of a low-protein diet is chiefly responsible for clinical presentation. Those with a more varied diet were also less likely to be cases.

The primary analysis is partly based on an index measure of self-reported food intake over two seasons which recorded the number of times an individual food item was eaten per week. The sum of the frequencies provided an intake score for each food group. This provided an indirect measure of food intake which may be subject to recall and other biases of self-reported dietary intake assessments [16].

Numerous PAs have been identified which have been shown to be hepatotoxic in human and animal models. The mechanism of action of PA is well established [17]. PAs are not toxic per se but require metabolic oxidation by hepatic multifunction oxidases to pyrrole derivatives, which then undergo hydrolysis to strongly alkylating metabolites [17]. In general, the diester PAs are more toxic than the monoesters; thus, the diester lasiocarpine is more hepatotoxic than the monoester, heliotrine.

Some PAs in the qurut are not present in charmac (i.e., trichodesmine), suggesting that the animals are grazing on other plants that contain PA and indicating potentially that charmac is not the only plant responsible for the human exposure to PAs. Although the amount of PAs in the qurut is in general much less than in wheat samples tested, this route of exposure may also be a contributory factor.

The amount of PA contained in the charmac is consistent with other Heliotropium species. A total alkaloid content of 0.76% for whole plant and 1.7% for seed has been found in other heliotropic plants, and thus a level of 1.9% for the Afghanistan samples is not unreasonable. Estimated dose and duration of exposure to PA required to produce liver damage in humans has been previously noted [18]. For heliotrine, an intake of 4–10 mg/kg per day for 3–7 weeks could lead to necrosis and VOD. The WHO has indicated a lowest intake rate of 1 mg total PAs per day (for a 70 kg adult) [4] with German regulations for herbal remedies establish a maximum oral intake of 1 microgram per day [19]. The high PA levels in the Afghanistan samples could certainly result in toxic exposure.

Sustained action is required to ensure the long-term safety of food. Amongst these is to identify appropriate technologies for elimination of the contamination, development of in-country capacity to assess PA content in samples, and implementation of routine testing in historically affected areas.

Global food shortages, changes in local ecology due to climate change, and ongoing lack of development in agricultural sectors make food safety an important public health issue. As food prices increase, it is likely that the proportion of the rural poor who rely on subsistence farming and locally traded produce will increase. If adequate food-safety practices are not employed at this level of society, incidents such as this outbreak are likely to become more common.

Acknowledgments

The authors are grateful to the Herat provincial and Gulran district health staff, Italian Army, Afghan National Police, and World Health Organization for assistance in conducting the study. In particular, the authors appreciate the collaboration by the people of Gulran district and sufferers of the disease. This study was funded by the World Health Organisation and the US Office of Disaster Assistance and Coordination of Humanitarian Aid through the US Naval Medical Research Unit #3. Many other stakeholders in Herat Province took part in the surveillance and case management of the Gulran Disease cases. The authors acknowledge the valuable support and coordination inputs of (i) Dr. Bernadette Abela-Ridder, Food Safety, Zoonoses and Foodborne Diseases, Health Security and Environment, World Health Organization, Geneva, Switzerland; (ii) Ms. Joanna Tempowski, Scientist, International Programme on Chemical Safety, Evidence & Policy for Environmental Health (EPE), World Health Organization, Geneva, Switzerland; (iii) Dr. Francis Williams, Combined Security Transition Command, Kabul, Afghanistan; (iv) Dr. Bashir Noormal, Director, Afghan Public Health Institute, Ministry of Public Health, Kabul, Afghanistan; (v) Dr. Said Abobakr Rasooli, National Health Coordinator, WHO, Herat, Afghanistan; and (vi) Dr. Suzette “Rana” Kakar, Technical Officer, World Health Organization, Kabul, Afghanistan. The authors acknowledge the support of analytical knowledge and laboratory testing provided by Russell J Molyneux (Western Regional Research Center, Albany, CA, USA) and by Ronald C. Schothorst and Hester J. van den Top (National Institute for Public Health & the Environment, RIVM, Bilthoven, The Netherlands). The authors acknowledge with appreciation Dr. Binay Kumar (Indian Institute of Health Management Research, Kabul, Afghanistan), Dr. Samad Hami, Dr. Edris Ayazi, Dr. Palwasha Anwari, Dr. Zakhmi Barakzai, and Dr. Gulam Farouq for their contributions to the data analysis. The views expressed herein are solely those of the authors and do not necessarily reflect the views of donors or affiliated organisations.

References

  1. F. C. Wilmot and G. W. Robertson, “Senecio disease or cirrhosis of the liver due to Senecio poisoning,” Lancet, vol. 23, pp. 848–849, 1920, World Health Organisation, Environmental Health Criteria no. 80: Pyrrolizidine alkaloids, 1988, http://www.inchem.org/documents/ehc/ehc/ehc080.htm.
  2. S. B. Dubrovinskii, “About the alimentary toxicosis caused by heliotrope,” J. Sov. Prot. Health, vol. 6, pp. 17–21, 1946 (Russian), World Health Organisation, Environmental Health Criteria no. 80: Pyrrolizidine alkaloids, 1988, http://www.inchem.org/documents/ehc/ehc/ehc080.htm.
  3. O. Mohabbat, M. S. Younos, A. A. Merzad, R. N. Srivastava, G. G. Sediq, and G. N. Aram, “An outbreak of hepatic veno occlusive disease in north western Afghanistan,” Lancet, vol. 2, no. 7980, pp. 269–271, 1976.
  4. H. D. Tandon, B. N. Tandon, and A. R. Mattocks, “An epidemic of veno-occlusive disease of the liver in Afghanistan. Pathologic features,” American Journal of Gastroenterology, vol. 70, no. 6, pp. 607–613, 1978.
  5. H. D. Tandon and B. N. Tandon, “Epidemic of liver disease—Gulran district, Herat Province, Afghanistan,” Assignment Report EM/AFG/OCD/001/RB, World Health Organisation, Geneva, Switzerland, 1975, World Health Organisation, Environmental Health Criteria no. 80: Pyrrolizidine alkaloids, 1988, http://www.inchem.org/documents/ehc/ehc/ehc080.htm.
  6. C. C. J. Culvenor, “Alkaloids and human disease,” in Toxicology in the Tropics, R. L. Smith and E. A. Bababunmi, Eds., pp. 124–141, Taylor & Francis, London, UK, 1980.
  7. A. R. Mattocks, Chemistry and Toxicology of Pyrrolizidine Alkaloids, Academic Press, London, UK, 1986.
  8. C. C. J. Culvenor, “Estimated intakes by pyrrolidizine alkaloids by humans. A comparison with dose rates causing tumors in rats,” Journal of Toxicology and Environmental Health, vol. 11, no. 4–6, pp. 625–635, 1983.
  9. Pyrrolizidine Alkaloids, Environmental Health Criteria no. 80, World Health Organisation, Geneva, Switzerland, 1988, http://www.inchem.org/documents/ehc/ehc/ehc080.htm.
  10. German Federal Health Bureau. Bundesanzeiger, June, 4805.
  11. H. Bower, Drought Brings Back Gulran Disease, WHO Health Talks, Kabul, Afghanistan, 2001.
  12. Z. Akbarian, “DEWS Investigation of Liver Disease Outbreak, Gulran District,” unpublished.
  13. Central Statistics Office, Kabul, Afghanistan, 2003.
  14. M. L. Deinzer, B. L. Arbogast, D. R. Buhler, and D. R. Cheeke, “Gas chromatographic determination of pyrrolizidine alkaloids in goat’s milk,” Analytical Chemistry, vol. 54, no. 11, pp. 1811–1814, 1982.
  15. D. Filmer and L. H. Pritchett, “Estimating wealth effects without expenditure data—or tears: an application to educational enrollments in states of India,” Demography, vol. 38, no. 1, pp. 115–132, 2001.
  16. K. R. Westerterp and A. H. C. Goris, “Validity of the assessment of dietary intake: problems of misreporting,” Current Opinion in Clinical Nutrition and Metabolic Care, vol. 5, no. 5, pp. 489–493, 2002. View at Publisher · View at Google Scholar
  17. A. R. Mattocks, Chemistry and Toxicology of Pyrrolizidine Alkaloids, Academic Press, London, UK, 1986.
  18. C. C. J. Culvenor, “Estimated intakes by pyrrolidizine alkaloids by humans. A comparison with dose rates causing tumors in rats,” Journal of Toxicology and Environmental Health, vol. 11, no. 4–6, pp. 625–635, 1983.
  19. German Federal Health Bureau. Bundesanzeiger, June, 4805.