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About authorsEducation:Bachelor’s degree: Chemical Technology (Study at Department of Chemistry,University of Natural Science, Viet Nam).Master’s Degree: Master of Science in Environmental Technology (Study at HanoiUniversity of Technology, Viet Nam and Institute of Environmental Technology,University of Applied Science Basel, Switzerland).Doctor’s Degree: Environmental Technology (Study at Hanoi University ofTechnology, Viet Nam and University of Applied Science Basel, Switzerland).Countries of work experience: Viet Nam, Switzerland, Thailand, United States ofAmerica.Research Fields: Environmental Toxicology (Persistent Organic Pollutants (POPs)),Environmental Analysis, Environmental Impact Assessment, Wastewater treatment.DDT Residues in Breeding Population of Booted Eagle (Aquila Pennata)Associated with Agricultural Land Practices p.321-p.338Emma Martínez-López, Pedro María-Mojica, José F. Calvo, José E. Martínez,Antonio J. García-FernándezDr. Antonio Juan García-Fernándezajgf@um.esMurcia, SpainDynamic and Batch Adsorption Studies of Isoproturon on Activated Carbonp.339-p.353Juan García, José Luis Sotelo, Araceli Rodríguez, Silvia ÁlvarezJosé Luis Sotelo Sancho (Full Professor), Juan García Rodríguez (AssociateProfessor), Araceli Rodríguez Rodríguez (Associate Professor), Silvia ÁlvarezTorrellas (Ph. D. Student)The authors have taught courses in chemical engineering, Biochemical Engineering,Food Sciences, Chemical Sciences, etc, at the undergraduate and postgraduatelevel. They have supervised numerous under- and postgraduate students in thefields of Chemical Engineering, Environmental Chemistry, etc. They are alsocurrently supervising numerous students at the MA and PhD levels. They havealso presented numerous papers at local and international conferences. They arealso active in research publications having published research papers in severallocal and international journals of repute. They are participating as researchers inseveral projects supported by public and private funds which are focused on thedevelopment of integrated advanced oxidation processes for wastewater treatmentcoming from industry and sewage treatment plants.AcademyPublish.org - The Impact of Pesticides16
About authorsDepartment: Chemical EngineeringAffiliated Organisation: Complutense UniversityContact Details:Grupo de Catálisis y Procesos de Separación (CyPS), Departamento de IngenieríaQuímica, Facultad de Ciencias Químicas, Universidad Complutense de Madrid,Avda. Complutense s/n, 28040 Madrid, Spain. E-mail: juangcia@quim.ucm.esSection 3PESTICIDE ANALYSISModern Sample Preparation Methods for Pesticide Multiresidue Determinationin Foods of Animal Origin by Chromatographic-mass SpectrometricTechniques p.355-p.379Renato Zanella, Osmar Damian Prestes, Caroline Do Amaral Friggi, ManoelLeonardo Martins, Martha Bohrer AdaimeAuthors are from the Laboratory of Pesticide Residues Analysis (LARP) from theChemistry Department of the Federal University of Santa Maria (UFSM).Contact: Prof. Dr. Renato Zanella, Depto. de Química, Campus da UFSM, 97105-900 Santa Maria - RS, Brazil. Phone/Fax: +5555 32208011, http://www.ufsm.br/larpAnalytical Methods to Assess the Impact of Pesticides on Human from Coffeep.380-p.390Zenilda CardealZenilda de Lourdes Cardeal has a master’s degree in analytical chemistry at theUniversidade Estadual de Campinas, Brazil; PhD degree in Chimie from Universitéde Paris XI (Paris, France) and did a Post doctoral stage at the Royal MelbourneInstitute of Technology (Australia, 2005). She is Lecture of analytical chemistryat the Universidade Federal de Minas Gerais, Brazil, since 1994. Works in thedevelopment of methods for the analysis of organic compounds at trace levels.His research work is focused on the following themes: environmental analysis,food analysis, toxicological analysis, gas chromatography, comprehensive twodimensionalgas chromatography, and solid phase microextraction.AcademyPublish.org - The Impact of Pesticides17
Page 1 and 2: The Impactof PesticidesEdited by:Pr
Page 3 and 4: Other access free resources from Ac
Page 5 and 6: The Impact of PesticidesPrepared an
Page 7 and 8: Table of Contentsp.203-p.224 Behavi
Page 9 and 10: About authorspublished by Elsevier.
Page 11 and 12: About authorsof medical researchers
Page 13: About authorsdifferent spatial scal
Page 18 and 19: About authorsSensors - A Nanotechno
Page 20 and 21: Section 1HUMAN EXPOSURE TO PESTICID
Page 22 and 23: ecently explored on preliminary stu
Page 24: individuals within 1 day (Jokanovic
Page 27 and 28: occupational environmental health r
Page 30 and 31: must be considered, since effective
Page 34 and 35: Jensen BH, Petersen A, and Christen
Page 36 and 37: Ragas AMJ, and Huijbregts MAJ (1998
Page 38 and 39: Weichenthal S, Moase C, and Chan P
Page 40 and 41: human poisoning, general acute symp
Page 42 and 43: Management of the cholinergic syndr
Page 44 and 45: 1982; Lotti, 1992; Jokanović et al
Page 46 and 47: exposed populations, revealed high
Page 48 and 49: DiazepamBenzodiazepines are CNS dep
Page 50 and 51: Among the many classes of oximes in
Page 52 and 53: inhibited by dichlorvos (a dimethox
Page 54 and 55: Dawson, 1995). It appears that the
Page 56 and 57: Eddleston M, Eyer P, Worek F, Moham
Page 58 and 59: Jokanović M, Kosanović M (2010b).
Page 60 and 61: Ray DE (1998). Chronic effects of l
Page 62 and 63: Worek F, Eyer P, Kiderlen D, Thierm
Page 64 and 65: developing countries is due to suic
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count and morphology, as well as se
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PON1 modulation of genetic damageFe
Page 70 and 71:
elationship between OP exposure and
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Blatter-Garin MC, James RW, Dussoix
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Hung RJ, Hall J, Brennan P, Boffett
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Rojas-García AE., Solís-Heredia M
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Occupational Exposure to Pesticides
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considered as conditions typical of
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observed adverse health outcome. Su
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within cells can oxidize biomolecul
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of the study. A face-to-face questi
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PesticidesFungicideInsecticide-Nema
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Table 4. Mixtures of pesticides use
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In pesticide applicators, Table 7 s
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DISCUSSIONThe agricultural workers
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changes in the antioxidant enzyme C
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Bajpayee, M.; Pandey, A. K.; Parmar
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Environmental health criteria 155.
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Palus, J.; Rydzynski, K.; Dziubalto
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Singh, N.P.; McCoy, M.T.; Tice, R.R
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INTRODUCTIONPopulations may be occu
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exposure scenarios on the basis of
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not present adverse health effects
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greenhouse workers exposed to malat
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Paraoxon is then either metabolized
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cyclohexene-1,2-dicarboximide, CAS
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metabolite of phthalates, such that
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scenarios were simulated, assuming
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Table 2. Biological reference value
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References N a urinarybiomarkeStudi
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Figure 2. Representation of a BRV d
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Figure 4. Conceptual representation
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Figure 6 Conceptual representation
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REFERENCESACGIH, 2011. Documentatio
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Bradway, D.E., Shafik, T.M., 1977.
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EPA, 1999b. Registration Eligibilit
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Hines, C.J., Deddens, J.A., Jaycox,
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McCollister, S.B., Kociba, R.J., Hu
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Verberk, M.M., Brouwer, D.H., Brouw
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important IGFBP for binding IGF-1 i
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secretion of IGF-1 (Tannheimer et a
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FIGURESFig. 1. An “hormetic” ef
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Landi F, Capoluongo E, Russo A, Ond
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Smith WJ, Underwood LE, Clemmons DR
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Section 2PESTICIDES IN THEENVIRONME
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vicinity of subsoil waters and ther
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Hieracium pilosella, southernwood -
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formed clusters (Figure 3). Ultrast
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Fig. 5. Fragment of hepatocyte of t
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Szarek, J, Skibniewska, K, Wojtacka
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negative effects (ZALUCKI et al., 2
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Figure 2. Appropriated sampling pro
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Figure 4. Illustration of the conse
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(HAILE et al., 1998). Earlier resul
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Table 1. Distribution of the applic
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Means followed by the same letter i
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(involving pests and natural enemie
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efore the pest emergence and their
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Table 3 (continuation)…AcademyPub
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Table 5. Effect of different fungic
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Table 6. Magament used including do
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adopted by Brazilian soybean grower
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Pickle, C.S.; Caviness, C.E. Yield
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This chapter reports on Dutch surfa
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several different occasions at any
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The greatest number of pesticides a
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Accumulated ExceedanceIt is useful
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For the years 2003-2009 the calcula
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Bonzini S, Verro R, Otto S, Lazzaro
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atios of the pesticide amounts in t
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Table 1. (Cont.) Runoff ratios of p
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mefenacet and simetrin were observe
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Table 2. (Cont.)Pesticide concentra
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Table 2. (Cont.)Pesticide concentra
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Fig. 3. Typical weekly variation of
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(BAM) in water (Pukkila et al. 2009
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Table 5. Concentrations of pesticid
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Table 6. Maximum concentrations of
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Iwafune, T, Inao, K, Horio, T, Iwas
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Suzuki, M, Takemine, S, Yoshida, M,
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factor, etc. Levels of pesticides i
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factor of 10 above ambient sea wate
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weight sample. Minimum were shown f
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Figure 3. DDTs in mussel samples fo
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Figure 5. HCB in mussel samples for
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Figure 8. Methoxychlor in mussel sa
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ACKNOWLEDGEMENTAuthors thank UNEP/M
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Pesticide Risk Index of Del Azul Wa
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on that presented in Swanson et al.
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eference value for that substance.
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predict the aquatic toxicity of a s
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Calculation Model of Aggravating Fa
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To estimate the values of Human Hea
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water in comparison with the durati
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Cypermethrin (95 th percentile (P 9
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Table 8 shows the results of the De
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are many ranking systems of dangero
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REFERENCESAres J. (2004). “Estima
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Mackay D. and Paterson S. (1991).
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Long-term Monitoring of Pesticides
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Sampling sites of the survey in 200
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than those in Lake Biwa and Seta Ri
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Fig. 7 Detection of fungicides in R
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Fig. 11 Detection of herbicides in
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Monitoring of pesticides in Yanamun
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A measured volume (1000 mL) of the
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SimetrynePretilachlorConcentration
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Fig. 18 Maximum concentrations of t
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Ecological risk assessmentFig. 20 Y
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REFERENCESAgradi E, Baga R, Cillo F
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Time Trend Variation of Selected Pe
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Table 1. Physical and chemical prop
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marketed under variety of trade nam
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Figure 3. Long-term trends of globa
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laboratory animals fed or injected
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fed for a lifespan at 5-1,600 mg/kg
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Soil samplingSoil sampling was foll
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Figure 5. Map showing sampling area
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concentration (MAC) in surface soil
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Table 7. Concentrations of HCH isom
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Shanghai and Guanting Reservoir (Ch
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Contrary to the results of ΣDDT, t
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DDT metabolites, the ratio of (p,p
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2001). Therefore, the predominance
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Mean concentration (ng g -1 dw)3002
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CONCLUSIONSAn evaluation of selecte
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Hung, D.Q., Thiemann, W., (2002),
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Viet, P.H., Hoai, P.M., Minh, N.H.,
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found in tissues or fluids samples
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Study area and SamplingThis study w
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the liver, mainly to p,p'-DDE and p
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33,370 ha, whilst that of woody cro
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Increase in crops area (x1000)Ha)25
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Table 1. Blood concentrations of or
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Council Directive 90/533/EEC of 15
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Konstantinou, IK, Goutner, V, Alban
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Smith, AG (2004). “Toxicology of
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Pesticides are used in order to pro
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EXPERIMENTALMaterialsIsoproturon wa
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RESULTS AND DISCUSIONEquilibrium is
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As seen in Table 4, as the concentr
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Fig.4. Breakthrough curves of isopr
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Fig.6. Breakthrough curves of isopr
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Fig.8. Experimental and theoretical
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Section 3PESTICIDE ANALYSISAcademyP
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scandal’ are familiar to the gene
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ecoveries (>70%) for certain pH-dep
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Due the versatility of the QuEChERS
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of application, with some still sca
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The main supercritical solvent used
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extracting the pesticides from the
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would be appropriate for the routin
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chromatography with negative-ion el
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GPC was applied as a nondestructive
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Charlton A.J.A., Stuckey, V. (2009)
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Lehotay, S.J., Mastvoska, K. & Yun,
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Rodrigues, F. M., Mesquita, P. R. R
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Analytical methods to assess the im
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acetylcholine, a neurotransmitter t
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1.3 to 22.3% for all pesticides. Li
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Malathion, parathion, fenitrothion,
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Fuller, BH and Berger, GMB (1990).
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Table 1. Largest exporters of coffe
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Fig. 1: Structures of (a) Phosphate
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ELECTROCHEMICAL BIOSENSORBiosensors
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inorganic and organic species a lar
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surface area and be easily modified
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Acetylcholine + H 2 O AChE Choline
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Wang, 2010) and tetracyanoquinodime
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PDDA/AChE/PDDA/CNT/GCAChE-Au-PPy/GC
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ng/mL and good precision (RSD ) 5.3
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FUTURE PERSPECTIVESThe detection of
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Du, D; Wang, M; Cai, J; Qin, Y; Zha
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Martorell, D; Cespedes, F; Fabreaga
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The Pesticide Action Network (PAN).
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About EditorMilan JokanovićProfess
Page 418:
THE IMPACT OF PESTICIDESPesticides
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