Pone.0005127 1.5
Acute Human Self-Poisoning with ImidaclopridCompound: A Neonicotinoid Insecticide
Fahim Mohamed1*, Indika Gawarammana1, Thomas A. Robertson2, Michael S. Roberts2, Chathura
Palangasinghe1, Shukry Zawahir1, Shaluka Jayamanne3, Jaganathan Kandasamy4, Michael Eddleston1,5,
Nick A. Buckley1,6, Andrew H. Dawson1,7, Darren M. Roberts1,8
1 South Asian Clinical Toxicology Research Collaboration, Department of Clinical Medicine, University of Peradeniya, Peradeniya, Sri Lanka, 2 Therapeutics Research Unit,
School of Medicine, University of Queensland, Brisbane, Australia, 3 Polonnaruwa General Hospital, North Central Province, Polonnaruwa, Sri Lanka, 4 Anuradhapura
General Hospital, North Central Province, Anuradhapura, Sri Lanka, 5 Scottish Poisons Information Bureau, Royal Infirmary of Edinburgh, and Clinical Pharmacology Unit,
University of Edinburgh, Edinburgh, United Kingdom, 6 Medical Professorial Unit, POW Hospital Clinical School, University of New South Wales, Kensington, Australia,
7 School of Medicine and Public Health, University of Newcastle, Callaghan, Australia, 8 Burns, Trauma and Critical Care Research Centre, University of Queensland,
Brisbane, Australia
Background: Deliberate self-poisoning with older pesticides such as organophosphorus compounds are commonly fataland a serious public health problem in the developing world. The clinical consequences of self-poisoning with newerpesticides are not well described. Such information may help to improve clinical management and inform pesticideregulators of their relative toxicity. This study reports the clinical outcomes and toxicokinetics of the neonicotinoidinsecticide imidacloprid following acute self-poisoning in humans.
Methodology/Principal Findings: Demographic and clinical data were prospectively recorded in patients with imidaclopridexposure in three hospitals in Sri Lanka. Blood samples were collected when possible for quantification of imidaclopridconcentration. There were 68 patients (61 self-ingestions and 7 dermal exposures) with exposure to imidacloprid. Of theself-poisoning patients, the median time to presentation was 4 hours (IQR 2.3–6.0) and median amount ingested was 15 mL(IQR 10–50 mL). Most patients only developed mild symptoms such as nausea, vomiting, headache and diarrhoea. Onepatient developed respiratory failure needing mechanical ventilation while another was admitted to intensive care due toprolonged sedation. There were no deaths. Median admission imidacloprid concentration was 10.58 ng/L; IQR: 3.84–15.58 ng/L, Range: 0.02–51.25 ng/L. Changes in the concentration of imidacloprid in serial blood samples were consistentwith prolonged absorption and/or saturable elimination.
Conclusions: Imidacloprid generally demonstrates low human lethality even in large ingestions. Respiratory failure andreduced level of consciousness were the most serious complications, but these were uncommon. Substitution ofimidacloprid for organophosphorus compounds in areas where the incidence of self-poisoning is high may help reducedeaths from self-poisoning.
Citation: Mohamed F, Gawarammana I, Robertson TA, Roberts MS, Palangasinghe C, et al. (2009) Acute Human Self-Poisoning with Imidacloprid Compound: ANeonicotinoid Insecticide. PLoS ONE 4(4): e5127. doi:10.1371/journal.pone.0005127
Editor: Michael B. Gravenor, University of Swansea, United Kingdom
Received January 21, 2009; Accepted March 12, 2009; Published April 8, 2009
Copyright:
ß 2009 Mohamed et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permitsunrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This study is funded by a Wellcome Trust/NHMRC International Collaborative Research Grant GR071669MA through SACTRC (www.sactrc.org). Thefunders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing Interests: The authors have declared that no competing interests exist.
* E-mail:
[email protected]
in the risk assessment and clinical management of patients withacute exposures and support policy decisions by regulatory
Intentional self-poisoning with pesticides is an important public
agencies. Previous restrictions in the availability of highly toxic
health problem in the Asia- Pacific region with an estimated
compounds appeared to substantially reduce deaths from
300,000 deaths occurring each year [1,2]. A large number of these
poisoning [3,4,5] without harming agricultural outputs [5].
deaths are due to poisoning with organophosphorus insecticides
The neonicotinoids are a new major class of highly potent
which are an integral part of agriculture within this region [2].
insecticides that are used for crop protection and flea control [6].
Due to the intrinsic toxicity of these compounds, new pesticides
Insecticides within this class include imidacloprid, acetamiprid,
continue to be developed and released to the market which almost
clothianidine, and thiocloprid. These insecticides are agonists at
always occurs in the absence of data on direct human toxicity.
the nicotinic acetylcholine receptors (nAChRs), particularly the
Instead, human toxicity is often extrapolated from toxicological
a4b2 subtype [7,8], which induces neuromuscular paralysis and
studies in animals, the relevance of which is poorly defined.
eventually death. They are highly selective for nAChRs in insects
Therefore, data reporting the outcomes from human exposures to
compared with mammals, which should reduce morbidity and
these newer insecticides are required. This information can assist
mortality in cases of human poisoning [7]. If clinical data on
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April 2009 Volume 4 Issue 4 e5127
Imidacloprid Human Case Series
human exposures support this, they may potentially replace the
Inclusion and exclusion criteria
more widely used cholinesterase inhibitors (organophosphorus and
All patients presenting to a study hospital with a history of
carbamate compounds) in crop protection.
imidacloprid exposure were considered for this study. Patients
Imidacloprid (CAS 138261-41-3; figure 1) is the most
under 14 years, pregnant women and patients presenting with co-
commonly used neonicotinoid insecticide in Sri Lanka. On the
ingestions are excluded from the study.
basis of animal studies it is classified as moderately hazardous(Class II WHO; toxicity category II EPA) [9,10]. It has low acute
Data collection procedure
lethal toxicity to mammals, birds, and fish: the acute oral LD50
Clinical observations of all patients with imidacloprid poisoning
(dose that is lethal in 50% of animals) of imidacloprid in rats is
were prospectively recorded on a specially designed data base from
475 mg/kg and the acute dermal LD50 exceeds 5000 mg/kg. It
March 2002 to March 2007. The poison ingested was identified
also does not cause eye irritation (rabbits) or skin sensitization
from the patient's or relative's history, examination of the bottle
(guinea pigs) [11].
label and/or the doctor's comments on transfer letters. Blood tests
Data on human exposure to imidacloprid is limited to
such as full blood count, biochemistry or cholinesterase activity
occupational exposures [12,13,14,15] and 13 case reports of self-
were not performed prospectively as there is limited availability of
poisoning [14,16,17,18,19,20,21]. Mild clinical effects such as
such services in these predominantly rural hospitals.
tachycardia, hypertension, mydriasis, nausea and vomiting occur,
Blood samples were collected from patients for quantification of
but more serious sequelae including respiratory failure, seizures
the concentration of imidacloprid and other biochemical assays at
[15,17,20] and even death [16,18,21] are reported. This raises
a later date. Following collection, the plasma was promptly
serious doubts about its assumed superior safety profile over older
separated and samples were stored at 223
uC and transported to
insecticides. However, in the majority of cases the concentration of
the University of Queensland, Australia on dry ice for analysis.
imidacloprid was not quantified so it was not possible to confirm
Samples were analyzed by HPLC (Shimadzu) with MSMS
exposure or consider dose in the risk assessment.
detection (Applied Biosystems API2000) of imidacloprid (MRM
In this study we sought to further describe the spectrum of
255.9/208.9) and internal standard d4-Imidacloprid (MRM
toxicity and clinical outcomes relative to the admission plasma
260.0/213.1) at 3.7 min. Separation of the imidacloprid peak
concentration in patients with acute imidacloprid poisoning.
was performed using Strata C18 (5 mm62 mm) online solid phaseextraction and Gemini (50 mm62 mm) analytical columns
(Phenomenex) using a standard valve configuration [22], the3 minute equilibration step and 6 minute gradient shown in
table 1. Solvent A (Pumps A & B) and Solvent B (Pump C)
This observational study was approved by Human Research
contained 0.1% formic acid with acetonitrile, water and methanol
Ethics committees of the University of Colombo Faculty of
in the ratios 5:95:0 and 90:5:5, respectively. Samples were
Medicine, The Sri Lankan Medical Association, The Australian
prepared by combining plasma (10 mL), d4-imidacloprid (2 mg/
National University and Oxfordshire, UK. Ethics approval
mL) in zinc (II) sulfate solution (100 mM, 20 mL) and acetonitrile
includes provision of a single blood sample on admission, regular
(50 mL). Each sample was prepared by combining the three
clinical reviews during hospitalisation and publication of de-
components, vortex mixing (5 sec), centrifugation (5 min at
indentified clinical data. Multiple blood samples were obtained as
4000 rpm), transfer of supernatant (
,70 mL) and LCMS injection
part of a smaller sub-study which required additional written
of 50 mL (Table 1).
consent. In all cases, informed verbal consent was obtained from
Biochemical analyses were conducted by Queensland Health
the patient or a relative in their native language.
Forensic and Scientific Services at Princess Alexandra Hospital,Australia. This service is accredited by the National Association of
Testing Authorities, Australia and certified to International
A prospective observational cohort study of all poisoning
Standards (ISO 9001).
presentations was established during 2002 in three hospitals inthe North Central and North Western provinces of Sri Lanka and
Table 1. LC Events
the cohort was extended to Central province during the year 2005.
Figure 1. Chemical structure of imidacloprid.
doi:10.1371/journal.pone.0005127.g001
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April 2009 Volume 4 Issue 4 e5127
Imidacloprid Human Case Series
Data were entered in to an excel sheet and analyzed using the
statistical Program STATA IC 10.
Over the 5 year period, 68 patients presented to study hospitals
with a history of imidacloprid exposure. Seven cases wereoccupational dermal exposures, all of whom remained asymptom-atic and were discharged within 24 hours of admission. Fivepatients reported co-ingestion with another pesticide and wereexcluded from further analysis, leaving 56 patients with acuteimidacloprid self-poisoning.
The median time to present to a study hospital since ingestion
was 4 hours (IQR 2.3–6.0 hours). The median volume reported asingested in self-poisoning was 15 mL (IQR: 10–50); although in 23the volume ingested was unknown.
The majority of patients (54/56) had only mild symptoms such
as nausea, vomiting, headache, dizziness, abdominal pain, and
Figure 2. Admission imidacloprid plasma concentrations
diarrhoea during the hospital stay which was largely self-resolving.
(n = 33). Compared to other cases of imidacloprid poisoning where
The median Glasgow Coma Score (GCS) on presentation was 15
the plasma concentration was quantified (12.5 and 2.05 ng/L post-
(IQR: 10–15). There were no deaths giving a case fatality of 0%
mortem [16]), our patients survived despite relatively high concentra-
(95% CI: 0.0–5.2%). However, two patients developed more
severe symptoms requiring management in an intensive care unit
and are described in more detail below.
prophylaxis against aspiration pneumonia. His clinical condition
improved within 24 hours and he was discharged alive 3 days
A 35 year old woman was admitted to a peripheral hospital soon
later. Blood samples were not available to confirm exposure in this
after ingestion of an unknown amount of imidacloprid. Due to an
initial lack of history, she had been managed as a case oforganophosphorus pesticide poisoning. She received forced
Toxicokinetics and biochemistry
emesis, 1.2 mg of atropine and 1g of pralidoxime before her
Of the 56 patients with imidacloprid self-poisoning, 13 patients
transfer to the study hospital. At this time, 2 hours post ingestion,
provided serial blood samples, 38 patients provided a single blood
she was agitated and had a blood pressure of 110/70 mmHg,
sample, and 5 patients refused to give any samples. Blood samples
regular pulse rate of 120/minute, pupil diameter 3 mm bilaterally
from the first 33 cases were analysed as described and the results of
and clear lungs. She received a bolus dose of haloperidol (5 mg
imidacloprid quantification are shown in figure 2. Exposure was
intramuscularly) for agitation. At 16 hours after ingestion she
confirmed in 28 patients, with a median admission plasma
developed a respiratory arrest requiring endotracheal intubation
concentration of 10.58 ng/L; IQR: 3.84–15.58 ng/L and range:
using atracurium 25 mg and midazolam 5 mg. She received an
0.02–51.25 ng/L. In 5 patients the concentration was less than the
atropine infusion at 1.2 mg/hour and prophylactic cefuroxime
level of quantification (0.008 ng/L), consistent with minimal
750 mg 8 hourly and metronidazole 500 mg every 8 hours for
exposure to imidacloprid.
suspected pulmonary aspiration. On her second day in ICU, she
Imidacloprid was only detected in eight of the patients who
became hypotensive which was treated with dopamine infusion.
provided serial blood samples but in one patient the plasma
Other treatments included regular pralidoxime (1g every 6 hours)
concentrations were all less than 0.3 ng/L. The concentration-
and chest physiotherapy. She was extubated on her 4th ICU day
time profiles for these seven patients are shown in Figure 3 and
after 3 days of mechanical ventilation and discharged home 9 days
demonstrate a rapid initial absorption with high concentrations
post-ingestion with no apparent residual effects. During her
being noted on admission. However, the concentration remained
recovery the patient reported a history of imidacloprid only. This
elevated for up to 10–15 hours post-ingestion, which might suggest
was subsequently confirmed on laboratory testing of a blood
that absorption and/or elimination are saturable (zero-order) or
sample obtained 5 hours post-ingestion when the plasma concen-
prolonged at high doses. In one of the patients there was a rapid
tration of imidacloprid was 44.6 ng/L (Figure 2) and the butyryl
decrease in concentration soon after the admission sample which
cholinesterase activity was normal.
might represent a distribution phase; the reason for this samplediffering from the others is not apparent from this data.
Quantification of metabolite production may further define the
A 26 year old man presented to a peripheral hospital following
toxicokinetics underpinning these observations, but unfortunately
ingestion of an unknown amount of imidacloprid under the
these were not able to be conducted at this time.
influence of alcohol. He received forced emesis and atropine (3 mgbolus followed by infusion of 2 mg/hour) and was then transferred
to one of the study hospitals. On admission to the study hospital
Admission blood samples from the same 33 patients were
(4.5 hours post-ingestion) he had vomiting, a regular pulse rate of
screened for biochemical abnormalities. No major abnormalities
84/minute, blood pressure 100/80 mmHg, pupil diameter 6 mm
were noted in terms of electrolytes, blood glucose, renal function
bilaterally, respiratory rate 40/minute, pulse oximetry was 100%
and liver function tests. Minor abnormalities included median
and GCS 3/15. The patient was transferred to the ICU 9 hours
venous bicarbonate of 14 mmol/L (IQR 10–15 mmol/L) and the
post-ingestion for closer monitoring. He received nebulised
median anion gap was raised at 20 mmol/L (IQR 18–26 mmol/
salbutamol and intravenous cefuroxime and metronidazole for
L). We were not able to perform arterial blood gases which might
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April 2009 Volume 4 Issue 4 e5127
Imidacloprid Human Case Series
formulation (as observed with some other pesticides) may causeanaerobic metabolism and produce a lactic acidosis which maycause a moderate decrease in bicarbonate.
In animals, imidacloprid penetrates the blood-brain barrier to
only a very limited extent [7]. While a decreased level ofconsciousness was uncommon in our study, prolonged sedationand respiratory depression was noted in two patients which mayhave been due to co-ingestion of ethanol. Transient respiratoryimpairment appeared to contribute to deaths reported in patientswith severe poisoning where co-ingestion of ethanol was notreported [20,21].
There are no specific antidotes for neonicotinoid poisoning in
mammals [7,25]. On the basis of our experience, symptomatic andsupportive care is all that is required for the management ofpatients with acute imidacloprid poisoning. Treatment withoximes such as pralidoxime is expected to be either ineffectiveor contraindicated. Oximes in the absence of organophosphoruspesticides have a weak inhibitory effect on acetylcholinesterase
Figure 3. The toxicokinetics of imidacloprid in patients withself-poisoning (n = 8 patients). The concentration was high on
activity and therefore might increase nicotinic effects (tachycardia,
admission and remained elevated in the majority of patients suggesting
hypertension, muscle weakness). It is notable that our two most
either prolonged absorption and/or elimination.
seriously poisoned cases received treatment with pralidoxime.
The concentration-time profile shown in Figure 3 suggests that
there is rapid absorption, with high concentrations being noted on
have confirmed the presence of high anion gap metabolic acidosis.
admission. In rats, imidacloprid is rapidly and almost completely
Median creatine kinase (CK) was measured at 115 IU/L (IQR
absorbed (.92%) from the gastrointestinal tract. The peak plasma
75–124), which is within the commonly quoted reference range
concentration is observed within approximately 2.5 hours and is
and troponin-I was not elevated.
followed by a rapid disposition phase. However, in our patients theconcentrations generally remained elevated for up to 10–15 hours
post-ingestion, which might suggest saturation of one or morekinetic (absorption or elimination) pathways in humans at high
This is the only prospective human case series reporting
doses. A possible factor influencing the observed kinetic profile is
outcomes from acute self-poisoning with the neonicotinoid
the administration of atropine (commonly given routinely to
insecticide imidacloprid. We demonstrated that imidacloprid
insecticide poisonings in Sri Lanka) which is known to prolong the
self-poisoning resulted in mostly minor toxicity with a case-fatality
absorption phase of xenobiotics [26].
of 0%. This is favourable compared to outcomes with other
Of the patients who provided serial samples, the final blood
insecticides, in particular the widely used organophosphorus
sample was generally obtained from patients around the time of
compounds which commonly have a case fatality between 5 and
discharge, when they appeared to be in good health. It is noted in
30% [23,24]. The most severely poisoned patients were both
figure 3 that for many of these patients the imidacloprid
administered antidotes used for the treatment of organophospho-
concentration remained elevated. Therefore, plasma concentra-
rus pesticides (a common cause of poisonings in the region) and
tions do not appear to be useful for guiding clinical management,
this may have increased the apparent toxicity. Many patients may
which may reflect the contribution of metabolites or co-
have had a moderate metabolic acidosis on admission; however,
formulants. In rats, the metabolism of imidacloprid is rapid and
simple supportive care was sufficient to ensure a good outcome for
extensive where only 10–16% of a dose is excreted unchanged [6].
all patients in this series.
Metabolites may contribute to human toxicity as they do in insects,
Tachycardia and hypertension have usually been reported in
in particular the olefin metabolite which retains insecticidal
previous cases, and recurrent ventricular fibrillation was the
activity and nAChR activity [7]. Potentially, individual variation
reported cause of death in a 69 year-old woman with coronary
in cytochrome P450 isoenzymes involved in oxidative imidaclo-
artery disease [18]. Only 2 patients in our case series developed
prid metabolism may contribute to variable toxicity [7,27].
any cardiovascular toxicity which was predominantly hypotension
Admire SL 200
H (200 g/L), the most popular imidacloprid-
and biomarkers of cardiac toxicity were not elevated. While
containing product in Sri Lanka, contains dimethylsulfoxide and
electrocardiographic monitoring was not conducted in these
N-methylpyrolidone as solvents which are irritants and may
patients, blood pressure improved with intravenous fluids.
induce gastrointestinal toxicity.
Therefore serious arrhythmias were unlikely to have caused the
Four deaths have been reported in the literature, and the post-
mortem blood concentrations in two cases were 12.5 and 2.05 ng/
Biochemical abnormalities and rhabdomyolysis have been
L [16], which surprisingly is not substantially greater than the
reported as potentially serious complications that might lead to
median plasma concentration in our study (9.86 ng/L). However,
mortality [15,21]. Most of the patients in our series had normal
ante-mortem plasma concentrations were not reported in these
CK and biochemistry with the exception of low venous
two fatalities and a direct comparison of the concentrations may
bicarbonate. The cause of this is not clear given the other
be misleading. There are no data on the blood/plasma
biochemical results, although diarrhoea may be contributory. It
concentration ratio or post-mortem redistribution.
may also be due to acidic metabolites of imidacloprid such as 6-
This study demonstrates that an acute ingestion of 20% SL
chloronicotinic acid and other metabolites [6]; however, metabolic
formulations of imidacloprid, even following large ingestions in
pathways of imidacloprid have not been extensively studied in
patients with self-poisoning, is relatively safe. Therefore, it may be
humans. Direct mitochondrial toxicity from a component of the
advantageous to promote the use of imidacloprid or similar
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April 2009 Volume 4 Issue 4 e5127
Imidacloprid Human Case Series
pesticides in areas where the incidence of self-poisoning is high.
However, before this occur the relative risks and benefits of thisinsecticide (which has been debated)[28,29,30] must be compared
We thank SACTRC doctors, directors, medical and nursing staff of thestudy hospitals for their support. We also thank Chigusa Yokobori and
to those of existing pesticides. This will require careful consider-
Maeno Momoe for translations, and Brian Mullins for coordinating the
ation by independent regulatory authorities.
Imidacloprid pesticides appear to be of low toxicity to humans
causing only mild symptoms such as vomiting, abdominal pain,
Author Contributions
headache and diarrhoea in the majority of cases. Large ingestionsmay lead to sedation and respiratory arrest. Patients with a low
Conceived and designed the experiments: FM CP SZ ME AD NAB.
GCS should be closely monitored for onset of respiratory
Performed the experiments: FM CP SJ JK. Analyzed the data: FM IG SZ
compromise but most patients only need symptomatic and
ME DR. Contributed reagents/materials/analysis tools: TAR MSR DR.
Wrote the paper: FM IG ME AD NAB DR.
supportive care. More research is required to show if thereplacement in agriculture of older anti-cholinesterase pesticideswith newer pesticides with much lower in-hospital case-fatality willlead to an overall reduction in deaths from self-poisoning.
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Viterol.A (viatrozene gel) 16% and patients with sunburn should beadvised not to use the product until ful y recovered. • Weather extremes, such as wind or cold, also may be irritating to patients under treatment with Viterol.A. Drug Interactions: Concomitant use of potential y irritating topical products (medicated or abrasive soaps and cleansers, soaps and cosmetics that have a strong drying ef ect, and products with high concentrations of alcohol, astringents, spices, or lime) should be approached with caution. Particular caution should be exercised in using preparations containing sulfur, resorcinol, or salicylic acid in combination with Viterol.A.