Please note that the authors wish to make the following changes to the above paper: Abstract last sentence Thresholds for acceptable daily intake levels ADI might be reached when consume
Trang 1Pham Manh Hoaia, Zita Sebesvarib, Tu Binh Minha, Pham Hung Vieta,
Fabrice G Renaudb,*
a Research Center for Environmental Technology and Sustainable Development, Hanoi University of Science, 334 Nguyen Trai Str., Hanoi, Viet Nam
b United Nations University, Institute for Environment and Human Security (UNU-EHS), Hermann-Ehlers-Str 10, D-5311, Bonn, Germany
The authors regret to say that there was a unit conversion error in the calculations and some of the results were reported incorrectly Please note that the authors wish to make the following changes to the above paper:
Abstract (last sentence)
Thresholds for acceptable daily intake levels (ADI) might be reached when consumed for a few of the analyzed food products while typically several pesticides co-occurred in the same sample pointing to the fact that current pesticide management practices do not only result in a pollution of the environment but may also pose threats to human health
Section 3.3.1 Recently used pesticides (3rd paragraph)
Since the MRL does not account for health risk, the reported concentrations were compared with the acceptable daily intake (ADI) values established by the European Food Safety Authority (EFSA) and the WHO/FAO Joint Expert Committee on Food Additives (JECFA) The ADI is a measure for the toxicity of a substance by long-term and repeated ingestion Among the studied pesticides ADI was established for cypermethrin (0.02 mg/kg bw.), cyfluthrin (0.04 mg/kg bw) and trichlorfon (0.002 mg/kg bw) (all ADIs derived from WHO, 2009) A daily intake of 1 kg of any of thefish samples would be safe i.e would not reach the ADI for any above-mentioned compounds (calculation for a person with 50 kg body weight; exception: onefish sample for trichlorfon in which the ADI is reached with the consumption of 390 g fish) Tea can be considered as safe for use since - assuming again 70% moisture content of the leaves a consumption of ca.19 kg dry tealeaves on a daily basis would be necessary to exceed the ADI for at least one analyzed pesticide (tea bags usually have 2.5e5 g filling weight) In case of mugwort, trichlorfon exceeds the ADI by a consumption of 690 g per day while several kilograms of heartleaf and water spinach can be safely consumed daily Health risk might be higher when different sources of contaminated food items are consumed and daily intake adds up 3.3.2 Organochlorine pesticides (1st paragraph)
DDTs, Drins and HCHs were detected in tea, vegetable andfish samples ADI is established for DDT (PTDT, provisional tolerable daily intake, 0.01 mg/kg bw), lindane (0.005 mg/kg bw) and aldrin/dieldrin (PTDT, provisional tolerable daily intake, 0.0001 mg/kg bw) (all ADIs derived from WHO, 2009) Considering again a person with 50 kg body weight a daily intake of 1.2 to 2.9 kgfish would cause that the ADI is exceeded for all samples for aldrin/dieldrin, while the samples were safe for lindane and DDT Water mimosa contains aldrin/dieldrin in a concentration which does not allow for a consumption of more than 280 g per day, while ca 500 g heartleaf or water spinach can be consumed without exceeding the respective ADIADI was not exceeded for lindane and DDT in vegetables Health risk might be higher when different sources of contaminated food items are consumed and daily intake adds up
Conclusions (last sentence of 2nd paragraph)
Since acceptable daily intake (ADI) levels were exceeded in somefish and vegetable samples for individual pesticides (depending on consumed daily amount) while typically several pesticides co-occurred in the same sample, the improvement of pesticide management practices would be crucial from a human health perspective, particularly in terms of reducing exposure
We sincerely apologize for the mistake
DOI of original article: http://dx.doi.org/10.1016/j.envpol.2011.08.044
* Corresponding author.
E-mail address: renaud@ehs.unu.edu (F.G Renaud).
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http://dx.doi.org/10.1016/j.envpol.2015.08.004
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Environmental Pollution 206 (2015) 720