https://doi.org/10.25678/0004Q3

Risk assessment for tropical streams of a small-scale horticultural catchment based on spatio-temporal pesticide monitoring data

There is a newer version of this dataset.

This package contains the supplementary information (SI) of chapter 3 of the dissertation of Frederik T. Weiss with the Dissertation No. ETH 27434 (defended: 24th February, 2021), entitled: "Pesticides in a tropical Costa Rican stream catchment: from monitoring and risk assessment to the identification of possible mitigation options". Generally within this thesis the supplementary information (SI) is divided into three parts (SI A, SI B, SI C). For each chapter, SI A section contains background information/data for the reader with quick and easy access added directly after each main chapter. SI B contains raw data, further processed data for analysis, and figures of processed data presented as Excel files. SI C combines the R scripts with information and commands utilized for the statistical analysis.

The abstract of chapter 3 reads as follows:

"A pesticide monitoring in the Tapezco river catchment region in two subsequent years (2015/2016) revealed that intensive pesticide use leads to contamination of streams. As shown in Chapter 2, 87 pesticide and pesticide transformation products (PPTP), comprising insecticides, herbicides, fungicides and several of their transformation products (TP) were identified by applying sorbent-based passive sampling approaches at the five (2015), respectively eight (2016), sub-catchment (SC) sites. Using these monitoring data as a basis, the first aim of this study was to exploit the measured environmental concentrations (MEC) of the PPTP with regard to their spatio-temporal distribution among the different sampling sites in the Tapezco river catchment. To enable a comparison between the two sampling years, of the 87 detected PPTP, the data set was narrowed down to those which were found in both sampling years, leading to a subset of 62 PPTP. Two MEC-based risk assessment approaches, one relying on Environmental Quality Standards (EQS) and the other on the Toxic Units (TU) concept focusing on invertebrates, were used to identify if the PPTP pose health risks to aquatic biota either singly or in mixture. As well, available macroinvertebrate data for four sites (SC1, SC4, SC5 and SC8) was evaluated in view of the indicated water quality, applying the species at risk pesticide (SPEARpesticide), the Costa Rican Biological Monitoring Working Party (BMWP-CR) Index, and the Ephemeroptera, Plecoptera and Tricoptera (EPT)-taxa richness indices. For the 62 considered PPTP, spatial trends were observed. In more detail, at two connected sites (SC2 and SC3), the average number of PPTP was 2-fold lower compared to the six remaining sites. At all sites, insecticides had the broadest detected spectrum as opposed to the numbers of individual herbicides and fungicides. Conversely, at all sites and periods, fungicides had the highest average %contribution of the average sum-concentration among the individual detected pesticide types. Independent of the risk assessment approach applied, the quality of the water was indicated to be generally poor, pointing at chronic, and even acute effects to be expected for aquatic communities at all sampling sites. Invertebrates were the most affected organism group based on EQS and TU without any apparent time window to recover from pesticide stress during both sampling years. The SPEARpesticide and the BMWP-CR indices both indicated that, despite the continuous pesticide pollution stress at all sites, water quality seemed to be improved at SC5 and reached even a good to regular water quality at the most downstream site (SC8) compared to the other remaining sites (SC1 and SC4) for which macroinvertebrate data was available. The EPT-taxa richness index showed as well an improvement in water quality at SC8. This finding could be due to a larger river stretch upstream to the sampling site with no horticultural land and high share of natural forest. Given that all applied approaches confirmed substantial risks, there is an urgent need for a reduction of pesticides in streams of the Tapezoco catchment to improve the water quality in order to protect aquatic communities in these streams."

Dataset extent

Data and Resources

Citation

This Data Package

Weiss, F., Ruepert, C., Echeverria Saenz, S., Schirmer, K., Eggen, R., & Stamm, C. (2021). Risk assessment for tropical streams of a small-scale horticultural catchment based on spatio-temporal pesticide monitoring data (Version 1.0) [Data set]. Eawag: Swiss Federal Institute of Aquatic Science and Technology. https://doi.org/10.25678/0004Q3

The associated article

Metadata

Open Data Open Data
Author(s)
  • Weiss, Frederik
  • Ruepert, Clemens
  • Echeverria Saenz,Silvia
  • Schirmer, Kristin
  • Eggen, Rik
  • Stamm, Christian
Keywords macroinvertebrates,ecotoxicology,Toxic Units,Spear,environmental quality standard,horticulture,BMWP
Variables
  • concentration
Substances (scientific names)
  • 2,4-D C8H6Cl2O3
  • 2,6-Dichlorbenzamide C7H5Cl2NO
  • 3,5,6-Trichloro-2-pyridinol C5H2Cl3N1O1
  • 3-Phenoxybenzoic acid C13H10O3
  • Acephate C4H10NO3PS
  • Acetachlor + Alachlor C14H20ClNO2
  • Acetamiprid C10H11ClN4
  • Alachlor-ESA + Acetochlor-ESA C14H21NO5S
  • Allethrine C19H26O3
  • Atrazine C8H14Cl1N5
  • Atrazine-2-hydroxy C8H15N5O
  • Atrazine-desethyl-2-hydroxy C6H11N5O
  • Azoxystrobin C22H17N3O5
  • Azoxystrobin (free acid) C21H15N3O5
  • Benalaxyl C20H23NO3
  • Bentazon C10H12N2O3S
  • Bifenthrine C23H22ClF3O2
  • Boscalid C18H12Cl2N2O
  • Bromazil C9H13BrN2O2
  • Buprofezin C16H23N3OS
  • Butachlor C17H26ClNO2
  • Carbaryl C12H11NO2
  • Carbendazim C9H9N3O2
  • Carbofuran C12H15NO3
  • Chlorpyrifos C9H11Cl3NO3PS
  • Clethodim C17H26ClNO3S
  • Clothianidin C6H8ClN5O2S
  • Compound Molecular formula
  • Cyazofamid C13H13ClN4O2S
  • Cyhalothrin C23H19ClF3NO3
  • Cypermethrin C22H19Cl2NO3
  • Cyproconazole C15H18ClN3O
  • Cyromazin C6H10N6
  • Deltamethrin C22H19Br2NO3
  • Desisopropylatrazine C5H8ClN5
  • Diazinon C12H21N2O4P1
  • Dichlorvos C4H7Cl2O4P
  • Difenoconazole C19H17Cl2N3O3
  • Dimefuron C15H19ClN4O3
  • Dimethoate C5H12NO3PS2
  • Dimethomorph C21H22ClNO4
  • Diuron C9H10Cl2N2O1
  • Diuron-desdimethyl C7H6Cl2N2O
  • Diuron-desmonomethyl (DCPMU) C8H8Cl2N2O
  • Empenthrin C18H26O2
  • Epoxiconazole C17H13ClFN3O
  • Ethoprophos C8H19O2PS2
  • Etofenprox C25H28O3
  • Fenamidone C17H17N3OS
  • Fenpropimorph C20H33NO
  • Fipronil C12H4Cl2F6N4O1S1
  • Fipronil-sulfide C12H4Cl2F6N4S1
  • Fipronil-sulfone C12H4Cl2F6N4O2S1
  • Fluazifop (free acid) C15H12F3NO4
  • Fludioxonil C12H6F2N2O2
  • Fluopicolide C14H8Cl3F3N2O
  • Fluopyram C16H11ClF6N2O
  • Fluroxypyr (free acid) C7H5Cl2FN2O3
  • Flutolanil C17H16F3NO2
  • Hexazinone C12H20N4O2
  • Imidacloprid C9H10ClN5O2
  • Imidacloprid-desnitro C9H11ClN4
  • Imidacloprid-urea C9H10ClN3O
  • Indoxacarb C22H17ClF3N3O7
  • Iprovalicarb C18H28N2O3
  • Irgarol-descyclopropyl C8H15N5S
  • Linuron C9H10Cl2N2O2
  • Malathion C10H19O6PS2
  • Metalaxyl C15H21NO4
  • Metconazole C17H22ClN3O
  • Methiocarb C11H15NO2S
  • Methomyl C5H10N2O2S
  • Methoxyfenozid C22H28N2O3
  • Metolachlor C15H22ClNO2
  • Metribuzin C8H14N4O1S1
  • Metribuzin-Desamino (DA) C8H13N3OS
  • Metribuzin-Diketo (DK) C7H12N4O2
  • Metsulfuron-methyl C14H15N5O6S
  • Monolinuron C9H11ClN2O2
  • Monuron C9H11ClN2O
  • Myclobutanil C15H17ClN4
  • Pencycuron C19H21ClN2O
  • Permethrin C21H20Cl2O3
  • Prochloraz C15H16Cl3N3O2
  • Profenophos C11H15BrClO3PS
  • Prometryn + Terbutryn C10H19N5S
  • Propamocarb C9H20N2O2
  • Propazine-2-hydroxy + Terbuthylazine-2-hydroxy C9H17N5O
  • Propiconazole C15H17Cl2N3O2
  • Pymetrozin C10H11N5O
  • Pyraclostrobin C19H18ClN3O4
  • Pyrimethanil C12H13N3
  • Quizalofop-p C17H13ClN2O4
  • Tebuconazole C16H22ClN3O
  • Tefluthrin C17H14ClF7O2
  • Terbacil C9H13ClN2O2
  • Terbuthylazine C9H16ClN5
  • Terbuthylazine-desethyl C7H12Cl1N5
  • Tetramethrin C19H25NO4
  • Thiabendazol C10H7N3S
  • Thiamethoxam C8H10ClN5O3S
  • Triadinemol C14H18ClN3O2
  • Triclocarban C13H9Cl3N2O
  • Triclosan C12H7Cl3O2
  • Trifloxystrobin C20H19F3N2O4
Substances (generic terms)
  • fungicide
  • herbicide
  • insecticide
  • metabolite
  • transformation product
Systems
  • river
  • stream
Timerange
  • 2015-07 TO 2015-10
  • 2016-05 TO 2016-10
Geographic Name(s)
  • Tapezco, Costa Rica
Review Level general
Curator Weiss, Frederik
Contact Frederik.Weiss@eawag.ch
DOI 10.25678/0004Q3