pesticide residues in soil, water and crops

2
Motivation Outlook First results of pesticide analyses soil water crops insects Pesticide residues in soil, water and crops resulting from cash crop cultivation in Benin and Burkina Faso Y. Bo nzi Cou liba ly 1 , H. Tapsoba 1 , C. Stechert 2 , M. Kolb 2 , M. Bahadir 2 1 Laboratoire de Chimie Organique: Structure & R éactivité , Université de Ouagadougou, Burkina Faso; [email protected] 2 Institute of Ecological Chemistry and Waste Analysis, Technische Universitaet Braunschweig, Germany For cash crop cultivation, especially in cotton cultures in Benin and Burkina Faso imported insecticides are used, that are mostly toxic. For example, the organo-chlorinated endosulfan banned in many countries is still in use in both Western African countries. One consequence of pesticide application is the formation of residues in soil, water, and crops. These two countries have important natural reserves in proximity to cotton farms as Pama Reserve P arc in the East of Burkina Faso and Parc National de la Pendjari in the North of Benin. Thus, contamination of soils and water especially in those areas is important for their key function as habitat media for a great number of non-target organisms (e.g. arthropods, amphibians and bats) that fullfill important ecosystem functions (Fig. 1). Pesticide residues in soil and water at BIOTA biodiversity observatories of these areas and at vicinal agricultural areas are monitored in order to evaluate the pollution levels. 0 200 400 600 800 1000 1200 1400 1600 1800    K   O   S   C    B    K   O   S   C    B    M    B   S   S   O   S   S    B   S   C    V   S   C   O   S   C    K   S   C    N   S   C   C    M   a    t   e   r    i   c   o   n   c  .    i   n   µ   g    /    k   g   s   o    i    l    d   m α-endosulfan β-endosulfan endosulfan sulfate Biocotton BF Sesam BF Conventional Cotton BF / Benin Fig. 2: Endosulfan residues in ag ricultural soils f rom sampling si tes in Benin (cotton field i n Materi near Pendjari Park in Oc tober 2007) and Burkina Faso (BF) in November 2007 Sampling sites Fig. 1: Interaction of non-target organisms with environmental compartment s The sampling sit es are selected on cash crop farmla nd of Burkina Faso and Benin (disturbed areas) and in the undisturbed area of the Pendjari National Park in Benin in cooperation with zoologists that sample the non- target organisms at the same sites in Benin. Sampling strategy is matching the climatic conditions by considering the two seasons: dry (November to  April) and wet (May to October) and the crop growing season, especially of cotton. Residue analyses of soil and water samples were performed for typically applied insecticides in cotton like organochlorines, organophosphates and pyrethroides. Residues of endosulfan isomers and their main meta bolite endosulfan sulfate were detected (Fig. 2 and Tab. 1). Endosulfan is a non systemic organochlorineinsecticide with a DT50 value of about 50 days (time for the disappearance of 50 % of the applied insecticide). It is know n to be carcinogenic, teratogenic, and neurotoxic as well as toxic to aquatic organisms. In soil samples from the beginning of the dry season (end of October / November) the applied insecticide mixture of endosulfan (α- and β-isomer in ratios of 2:1 or 7:3) was degraded for a major part (50 to 80 %) to the metabolite endosulfan sulfate that is more persistent and similar toxic than its parent compounds. The residues levels in soil of conventional cotton growing were relatively high in a range of 160 µ g/kg to 2300 µ g/kg (sum of all three substances). Even in soil from a bio-cotton field low concentrations of e ndosulfan were found but with an untypical domination of the α-isomer. This might be due to a contamination with the volatile isomer α-endo sulfan via evapo transp iration and atmospheric transp ort from treated fields in the neighborhood. Sampling location Benin Burkina Faso Pendjari Park Hunting zone Cotton area Cotton area Bali I Bali II Batia I Batia II Taya- cou I Taya- cou II Materi I Kiki- deni Natia- bouani Conc. of α-, β- endosulfan, endosulfan sulfate in µg/L n.d. n.d . 0.02 0 .02 n.d. <0.02  0.03 < 0.02  0.05 Tab. 1: Endosulfan residues in pond water from samp ling sites in Benin and Burkina Faso n.d.: not detected Information on pesticide products and their application pattern used in cash crop cultivation in the two countries will be supplemented . Sampling of soil, water and crops will be continued in 2008 and 2009. Analytical data will provide an overview of the environmental contamination state due to cotton cultivation and thus complete the data of pesticide residues in non- target organisms to evaluate possible influences of pesticides on bio- diversity. Sampling sites in the vicinity of Biodiversity Observatories (NSCC, KOSCB, KOSCBM Kikideni, Natiabouani in B urkina Faso; Tayacou, Materi, Batia, Bali in Benin)  Additional cotton sites of conventional cotton in Burkina Faso (BSC, VSC, OSC, KSC) Pama reserve parc Parc Natio nal de la Pendjari 

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Page 1: Pesticide Residues in Soil, Water and Crops

8/2/2019 Pesticide Residues in Soil, Water and Crops

http://slidepdf.com/reader/full/pesticide-residues-in-soil-water-and-crops 1/1

Motivation

Outlook

First results of pesticide analyses

soil

water 

crops

insects

Pesticide residues in soil, water and crops

resulting from cash crop cultivation

in Benin and Burkina FasoY. Bonzi Coulibaly1, H. Tapsoba1, C. Stechert2, M. Kolb2, M. Bahadir 2

1Laboratoire de Chimie Organique: Structure & Réactivité , Université de Ouagadougou, Burkina Faso; [email protected] 

2Institute of Ecological Chemistry and Waste Analysis, Technische Universitaet Braunschweig, Germany

or cash crop cultivation, especially in cotton cultures in Benin and Burkina

aso imported insecticides are used, that are mostly toxic. For example,

he organo-chlorinated endosulfan – banned in many countries – is still in

se in both Western African countries. One consequence of pesticide

pplication is the formation of residues in soil, water, and crops.

hese two countries have important natural reserves in proximity to cotton

arms as Pama Reserve Parc  in the East of Burkina Faso and Parc 

National de la Pendjari  in the North of Benin. Thus, contamination of soils

nd water especially in those areas is important for their key function asabitat media for a great number of non-target organisms (e.g. arthropods,

mphibians and bats) that fullfill important ecosystem functions (Fig. 1).

esticide residues in soil and water at BIOTA biodiversity observatories of 

hese areas and at vicinal agricultural areas are monitored in order to

valuate the pollution levels.

0

200

400

600

800

1000

1200

1400

1600

1800

   K  O  S  C   B

   K  O  S  C   B   M    B  S

  S  O  S  S

   B  S  C

   V  S  C

  O  S  C    K  S

  C

   N  S  C  C

   M  a   t  e  r   i

  c  o  n  c

 .   i  n  µ  g   /   k  g  s  o   i   l   d  m

α-endosulfan

β-endosulfan

endosulfan sulfate

Biocotton BF Sesam BF Conventional Cotton BF / Benin

Fig. 2: Endosulfan residues in agricultural soils from sampling sites in Benin

(cotton field in Materi near Pendjari Park in October 2007) and Burkina

Faso (BF) in November 2007

Sampling sites

ig. 1: Interaction of non-target organisms with environmental compartments

he sampling sites are selected on cash crop farmland of Burkina Faso

nd Benin (disturbed areas) and in the undisturbed area of the Pendjari

National Park in Benin in cooperation with zoologists that sample the non-

arget organisms at the same sites in Benin. Sampling strategy is matchinghe climatic conditions by considering the two seasons: dry (November to

April) and wet (May to October) and the crop growing season, especially of 

otton.

Residue analyses of soil and water samples were performed for typically

applied insecticides in cotton like organochlorines, organophosphates and

pyrethroides. Residues of endosulfan isomers and their main metabolite

endosulfan sulfate were detected (Fig. 2 and Tab. 1).

Endosulfan is a non systemic organochlorine insecticide with a DT50 valueof about 50 days (time for the disappearance of 50 % of the applied

insecticide). It is known to be carcinogenic, teratogenic, and neurotoxic as

well as toxic to aquatic organisms.

In soil samples from the beginning of the dry season (end of October /

November) the applied insecticide mixture of endosulfan (α- and β-isomer 

in ratios of 2:1 or 7:3) was degraded for a major part (50 to 80 %) to the

metabolite endosulfan sulfate that is more persistent and similar toxic than

its parent compounds. The residues levels in soil of conventional cotton

growing were relatively high in a range of 160 µ g/kg to 2300 µ g/kg (sum of 

all three substances). Even in soil from a bio-cotton field low

concentrations of endosulfan were found but with an untypical domination

of the α-isomer. This might be due to a contamination with the volatile

isomer  α-endosulfan via evapotranspiration and atmospheric transport

from treated fields in the neighborhood.

Samplinglocation

Benin Burkina Faso

PendjariPark

Huntingzone

Cotton area Cotton area

BaliI

BaliII

BatiaI

BatiaII

Taya-couI

Taya-couII

MateriI

Kiki-deni

Natia-bouani

Conc. of α-, β- endosulfan,endosulfan sulfatein µg/L  n.d. n.d. 0.02 0.02 n.d. <0.02

 

0.03 < 0.02

 

0.05

Tab. 1: Endosulfan residues in pond water from sampling sites in Benin andBurkina Faso

n.d.: not detected

Information on pesticide products and their application pattern used in

cash crop cultivation in the two countries will be supplemented. Sampling

of soil, water and crops will be continued in 2008 and 2009. Analytical data

will provide an overview of the environmental contamination state due to

cotton cultivation and thus complete the data of pesticide residues in non-

target organisms to evaluate possible influences of pesticides on bio-

diversity.

Sampling sites in the vicinity of Biodiversity

Observatories (NSCC, KOSCB, KOSCBM

Kikideni, Natiabouani in Burkina Faso;Tayacou, Materi, Batia, Bali in Benin)

 Additional cotton sites of conventional

cotton in Burkina Faso

(BSC, VSC, OSC, KSC)

Pama reserve parc 

Parc National de la Pendjari