Diseases transmitted by insect vectors are a major health concern throughout the world and result in millions of deaths each year [
Application of pesticides is a simple vector control method that individuals can afford and is often the only option available to a household seeking to prevent vector-borne diseases in developing nations. However, the use of pesticides to prevent vector-borne diseases does not come without consequences. Studies have shown that human illness and death due to occupational and accidental pesticide exposures are significant health issues throughout the world [
Occupational exposures to pesticides may cause acute and long-term health effects [
Local communities must often take action to protect themselves from disease vectors. Most individuals purchase pesticides from pesticide vendors, individuals without an actual store, who travel to local street markets to sell pesticides along the road. These pesticides are generally affordable for the local population but with limited regulation; the quality of substances being sold as pesticides is unknown. The concerns with obtaining pesticides from unregulated sources are that the products being sold may be of poor quality, or they may not actually be pesticides and therefore will not control the vectors. Some of the products sold kill vectors effectively, but they may be highly toxic and dangerous for home use by individuals. Another concern is that the pesticides purchased may not have labels so the individual will not know what pesticide is being used, how to properly mix and apply the pesticide, and how to protect themselves and their families during use.
The objective of this research was to evaluate potential health risks due to the sale and distribution of vector control pesticides at local street markets. Specifically, this research identified pesticides being sold and whether they were appropriate for vector control activities. It also determined the proportion of pesticides samples that were sold without labels. To our knowledge, there have been no published studies that have identified the types of pesticides sold and used in local communities in The Gambia.
This study was conducted in four locations in The Gambia, West Africa from July, 2005 to November, 2005. The four main locations involved in the research included the towns of Kuntaur, Brikama, Farafenni, and Serrekunda. These towns were selected as the major locations of street markets, also known as lumos
To collect the pesticide samples, one sample of each type of product identified by a vendor as a pesticide was purchased. Samples were purchased from all pesticide vendors present at the market. The interviewers asked each vendor to sell them pesticides for killing mosquitoes and insects that might cause disease around their home. Multiple pesticides were purchased from the same vendor if they were considered different types. Pesticide samples were collected at each location over two different market days in 2 ounce, wide-mouth polypropylene bottles (Fisher Scientific, Pittsburg, PA). These bottles were then packaged in expanded polystyrene containers within a box for international shipment. The samples were transported to the National Institute for Occupational Safety and Health in Cincinnati, Ohio, USA for chemical analysis.
Pesticides were identified by gas chromatography with mass spectrometry (GC/MS). An Agilent 6890 N GC (Agilent Technologies, Palo Alto, CA, USA) equipped with a 7683 autoinjector (Agilent), split/splitless inlet, and 5973 mass selective detector operated in electron impact (EI) ionization mode was used for screening analyses of 116 samples. A mass range from
GC-MS operating conditions for analysis of pesticide samples.
GC/MS parameter | Component or setting |
---|---|
Gas chromatograph | Agilent 6890 N |
Mass detector | Agilent 5973 |
Column | HP-5MS (30 m × 0.25 mm id, 0.25 |
Carrier gas | Helium |
Purge flow and time | 25.5 mL/min at 1.5 min |
Injection | 1- |
Inlet temperature | 325°C |
Column temperature program | 40°C (2 min) |
Detector temperature | 230°C source |
MSD transfer line | 325°C |
All samples were prepared in dichloromethane (DCM) by adding 10 microliter (
Full scan mass spectral data and library searching were used for compound identification. Identifications were based on a National Institute of Standards and Technology (NIST) standard library search. Specifically, if the library search gave a match factor above 90% for a given sample peak and low matches for other compounds listed in the search results, then the sample peak was identified as the compound with the high-match result. Most of the sample peaks were identified by this approach.
In some cases, the library search on a given peak found several possible compounds with similar matches (above 85%) or the matches for the possible compounds listed were all lower than 90%. Confirmed identifications for these compounds require further analytical work and results are not reported here. A relatively small number of samples were not soluble in DCM or other solvents, while others were soluble but no peaks were observed, or no library matches were found for the peaks present. Identifications for these samples could not be made.
Statistical analyses were performed using SAS/STAT version 9.1 (SAS Institute Inc., Cary, NC, USA). Descriptive statistics were used to characterize pesticides identified. Likelihood Ratio Chi-Square analyses were conducted to compare the characteristics of pesticide vendors using questionnaire data. The Fisher’s Exact Test was conducted in addition to Likelihood Ratio Chi-Square when cell counts were insufficient to ensure the validity of results. An
A total of 128 pesticide samples were collected from street market vendors. Only 10.2% of the samples was labeled, with the majority being sold in unlabeled plastic bags or containers. The 13 pesticide samples sold in original, labeled packaging consisted of the active ingredients chlorpyrifos, endosulfan, and deltamethrin. These were not restricted for use in The Gambia [
Active ingredients in 111 (96.5%) of the unlabeled samples (Table
Analysis of pesticide samples collected from local street markets.
Total samples | Labeled | Unlabeled | Unlabeled Samples | Components Identified | ||||||
Samples | Samples collected | Identified by GC-MS | Single compound | Multiple compounds | ||||||
# | % | # | % | # | % | # | % | # | % | |
128 | 13 | 10.2 | 115 | 89.8 | 111 | 96.5 | 59 | 53.2 | 52 | 46.8 |
The pesticide components identified were primarily organophosphate (37.9%), organochlorine (26.7%), and carbamate chemical classes (21.7%), with organophosphate pesticides the most abundant (Table
Chemical Classes of Pesticide Components Collected From Local Street Markets and Identified By gc-MS.
Chemical class | # Components | % Total components |
---|---|---|
Organophosphates | 61 | 37.9 |
Organochlorines | 43 | 26.7 |
Carbamates | 35 | 21.7 |
Permethrins | 14 | 8.7 |
Other | 8 | 5.0 |
Table
Identities of 168 pesticide components collected from local street markets (see text for analysis conditions).
Pesticides identified* | WHO classification | Use | Chemical class | Number of samples | % |
---|---|---|---|---|---|
Class II | Acaricide, insecticide, nematicide | Organophosphate | 25 | 14.9 | |
Endosulfans | Class II | Acaricide, insecticide | Organochlorine | 24 | 14.3 |
Class IB | Acaricide, insecticide, nematicides | Carbamates | 22 | 13.1 | |
Fenitrothion | Class II | Insecticide | Organophosphate | 22 | 13.1 |
Class II | Acaricide, insecticide, rodenticide | Organochlorine | 14 | 8.3 | |
Propoxur | Class II | Acaricide, insecticide | Carbamate | 12 | 7.1 |
Deltamethrin | Class II | Insecticide | Pyrethroid | 6 | 3.7 |
Tetramethrin | Minimal hazard in normal use | Insecticide | Pyrethroid | 5 | 3.0 |
Dimethoate | Class II | Acaricide, insecticide, nematicide | Organophosphate | 4 | 2.4 |
Considered discontinued for pesticide use | Acaricide | Organochlorine | 3 | 1.8 | |
Cypermethrin | Class II | Acaricide, insecticide | Pyrethroid | 3 | 1.8 |
Class IA | Insecticide | Organophosphate | 3 | 1.8 | |
Sulfur | Minimal hazard in normal use | Acaricide, fungicide | Unclassified | 3 | 1.8 |
Dicofol | Class III | Acaricide | Organochlorine | 2 | 1.2 |
Malathion | Class III | Acaricide, insecticide | Organophosphate | 2 | 1.2 |
Class IB | Acaricide, insecticide | Organophosphate | 2 | 1.2 | |
Napthalene | Considered discontinued for pesticide use | Fumigant insecticide | Unclassified | 2 | 1.2 |
Profenofos | Class II | Insecticide | Organophosphate | 2 | 1.2 |
Carbaryl | Class II | Acaricide, insecticide | Carbamate | 1 | 0.6 |
Metolachlor | Class III | Herbicide | Chloroacetanilide | 1 | 0.6 |
Chlorfenson | Class III | Acaricide | Unclassified | 1 | 0.6 |
Pirimiphos methyl | Class III | Acaricide, insecticide | Organophosphate | 1 | 0.6 |
Tetradifon | Minimal hazard in normal use | Acaricide | Unclassified | 1 | 0.6 |
Not identified | Unknown | Unknown | 7 | 4.2 |
*Italicized pesticide components are severely restricted in the United States.
Boldfaced pesticide components are banned in the United States.
Underlined pesticide components are on the United Nations PIC list.
Sixty-nine of the pesticide components used in The Gambia are restricted or banned in the United States (Table
Hazard classification of identified pesticide components.
Number of pesticide components | Percent of all pesticide components | |
---|---|---|
Not an insecticide | 5 | 3.1 |
Pesticides restricted in the USA | 39 | 24.2 |
Pesticides banned in the USA | 30 | 18.6 |
Pesticides classified hazardous by World Health Organization | 27 | 16.8 |
UN prior informed consent pesticide | 22 | 13.7 |
Additional nonpesticide components also were identified in the samples. The majority of these additional substances were carrying agents, but the analysis did show individual samples that contained nonpesticide components. Compounds found in materials sold as pesticides included chlorphenamine (antihistamine), methanamine (antibiotic), vitamin E, and mebendazole (drug to treat tapeworms).
The type of pesticide formulation can affect transportation, storage, and use. The majority of the pesticides used were powdered (59.1%). Powdered formulations were preferred by vendors due to easy repacking into small, plastic bags. Liquid pesticides made up 20.9%, granular pesticides made up 15.5%, and solids in the form of pellets, discs, or chalk-like products made up 9.1% of the pesticide samples.
The four villages Brikama, Kuntaur, Farafenni, and Serrekunda represent the primary street markets where pesticide purchase for community use occurs (Table
Pesticide street markets targeted for sample collection and pesticide classes identified.
Market | City population | Percent of pesticides labeled | Pesticide classes identified | ||||
% OP | % OC | % C | % P | % Other | |||
Kuntaur | 7,237 | 9.4 | 30.8 | 10.3 | 12.8 | 23.0 | 10.3 |
Farafenni | 42,434 | 16.7 | 37.7 | 26.1 | 23 | 6.6 | 3.3 |
Brikama | 88,870 | 5.6 | 34.0 | 35.8 | 22.6 | 1.9 | 1.9 |
Serrekunda | 1,205,034 | 8.3 | 30.0 | 10.0 | 30.0 | 0 | 20 |
OP: Organophosphate pesticides.
OC: Organochlorine pesticides.
C: Carbamate pesticides.
P: Pyrethroid pesticides.
This study showed that there were a wide variety of pesticides in circulation in The Gambia, many of which are considered unsafe for use by the United States and WHO. Identifying the sources, types, and potential hazards of dangerous pesticides was complicated by the fact that pesticides sold on the street were rarely labeled so that the identities of the pesticides were not known, often not even by the pesticide vendor. The high percentage of multiple pesticide components is likely due to the common practice of mixing together leftover pesticides. Most pesticide storage containers were unlabeled, so when volumes were low there was no deterrent to combining different pesticide formulations together and selling these mixtures.
The high percentage of pesticide components identified that are considered severely restricted pesticides in the United States is a concern because those pesticides are hazardous and should be applied only for specific uses and only by individuals with advanced training. Individuals purchasing these pesticides for home use most often were not properly trained, and the pesticides were inappropriate and potentially dangerous for home use. The banned pesticides are not allowed for use in the United States for health or environmental reasons. These pesticides, as well as those classified as hazardous by WHO and PIC, were clearly inappropriate for home use, posing potential safety risks for individuals and their families. The identification of twenty-two ingredients covered under the United Nations prior informed consent rules illustrates the lack of effective regulations as these were pesticides that should be fully regulated by the Gambian government for both distribution and use. A portion of the samples identified were not even insecticides as claimed by the vendor. Though not presenting exposure risks, these random substances are ineffective in eliminating insect vectors and could provide a false sense of protection within the homes.
The results of this study are a reminder of the fluid movement of dangerous pesticides within African countries. The high-risk pesticides listed by the EPA and WHO require specialized experience and knowledge that does not exist with the individuals purchasing these pesticides at the markets. Our results indicate that regulations regarding the importation of pesticides were ineffective. The Gambia has limited resources and personnel to commit to monitoring its border, which makes it difficult to prevent the large influx of unregulated pesticides across the border from Senegal. The most effective way to regulate the movement of pesticides and protect the population from toxic pesticide exposures may be through the education and regulation of the pesticide vendors themselves. Toxic pesticides are a risk not only to vendors and individual pesticide applicators but also could present significant exposure risks for families by increasing the risk of pesticide exposure for vulnerable populations such as children and pregnant women.
Though minimal information could be discovered about where the pesticides were originally produced, an important finding was that even the labeled pesticides were written in a variety of world languages, limiting the effectiveness of labels at times in communicating health risks to both vendors and customers. These findings correspond with pesticide vendors who that claim illegal smuggling of pesticides across borders is rampant and introduces a wide variety of unregulated pesticides into Gambian markets. A limitation of this study is that samples were not systematically collected from all markets in The Gambia and the results are not representative to the entire population.
The government has specific guidelines discussing the importation of pesticides and what is allowed within The Gambia. Awareness that some pesticides are illegal and all pesticides should be sold with labels could be communicated to pesticide vendors. Public health officers could inspect pesticide vendors on market day to enforce that all pesticides are being sold with labels (even if hand written) as an initial deterrent. That would be a feasible course of action that could encourage cooperation with current pesticide policies.
There have always been public health concerns regarding the sale of hazardous pesticides in developing countries. This is the first study in Africa to quantitatively sample pesticides where they are commonly sold and identify unknown pesticides to determine the exposure health risks associated with the pesticides in circulation. The results show significant percentages of the pesticides in use in The Gambia were extremely hazardous and should not be used by untrained individuals and without proper protection equipment. Even worse, these pesticides were commonly being sold without safety labels, so there was no method for a customer to know the difference between use of a less hazardous pesticide such as deltamethrin versus a highly toxic pesticide banned throughout the world. The results of this research can further discussions about enforcement of pesticide importation laws and the revision of current pesticide regulations to target major issues that could minimize pesticide exposure risks and protect human health.
The mention of any company or product does not constitute an endorsement by the Centers for Disease Control and Prevention. The findings and conclusions in this paper are those of the authors and do not necessarily represent the views of the National Institute for Occupational Safety and Health.
The authors would like to thank the University of Iowa Great Plains Center for Agricultural Health and the University of Iowa Educational and Research Center for their financial support.