Sampling of herbicides in streams during flood events.

In stream water xenobiotics usually occur as pulses in connection with floods caused by surface run-off and tile drainage following precipitation events. In streams located in small agricultural catchments we monitored herbicide concentrations during flood events by applying an intensive sampling programme of ½ h intervals for 7 h. In contrast to grab sampling under non-flood conditions, clearly elevated concentrations were recorded during the floods, and pulses varying in occurrence, duration and concentration were recorded. Pulses of recently applied herbicides were the most prominent, but also agricultural herbicides used in previous seasons caused pulses in the streams. Asynchronism of chemographs may be related to the characteristics of the compounds as well as their transport pathways and transformation in compartments between the source and the point of sampling in the stream. Thus, the occurrence of chemographs is difficult to predict, which ought to be taken into account when designing a sampling strategy. Even though the chemographs of herbicides and their transformation products (glyphosate and aminomethylphosphonic acid (AMPA) as well as terbuthylazine and desethylterbuthylazine) seem to be synchronous, their occurrence may still be difficult to predict. It is evident that grab sampling under non-flood conditions yields insufficient information on the dynamics of occurrence of herbicides in stream water, both with respect to environmental effects and the calculation of the load to a recipient. In conclusion, the design of a sampling strategy regarding herbicides in stream waters should adequately consider the aim of the investigation.

[1]  R. Schwarzenbach,et al.  Variability of herbicide losses from 13 fields to surface water within a small catchment after a controlled herbicide application. , 2004, Environmental science & technology.

[2]  N. H. Spliid,et al.  Pesticides in Danish watercourses: Occurrence and effects , 1995 .

[3]  G. Merlina,et al.  The role of storm flows in concentration of pesticides associated with particulate and dissolved fractions as a threat to aquatic ecosystems - Case study: the agricultural watershed of Save river (Southwest of France) , 2011 .

[4]  R. Schwarzenbach,et al.  Simultaneous assessment of sources, processes, and factors influencing herbicide losses to surface waters in a small agricultural catchment. , 2004, Environmental science & technology.

[5]  L. Bergström,et al.  Laboratory and lysimeter studies of glyphosate and aminomethylphosphonic acid in a sand and a clay soil. , 2011, Journal of environmental quality.

[6]  A. Gustard,et al.  Low Flow Estimation in the United Kingdom , 1992 .

[7]  Brian Kronvang,et al.  Buffer strip width and agricultural pesticide contamination in Danish lowland streams: Implications for stream and riparian management , 2011 .

[8]  J. Kreuger,et al.  Multiple regression analysis of pesticide occurrence in streamflow related to pesticide properties and quantities applied , 1998 .

[9]  M Coquery,et al.  Assessing pesticide concentrations and fluxes in the stream of a small vineyard catchment--effect of sampling frequency. , 2010, Environmental pollution.

[10]  W. Brack,et al.  A new risk assessment approach for the prioritization of 500 classical and emerging organic microcontaminants as potential river basin specific pollutants under the European Water Framework Directive. , 2011, The Science of the total environment.

[11]  Lucien Hoffmann,et al.  Concentrations of dissolved herbicides and pharmaceuticals in a small river in Luxembourg , 2011, Environmental monitoring and assessment.

[12]  C. Stamm,et al.  Loss rates of urban biocides can exceed those of agricultural pesticides. , 2011, The Science of the total environment.

[13]  J. Kreuger Pesticides in stream water within an agricultural catchment in southern Sweden, 1990-1996. , 1998, The Science of the total environment.

[14]  M. B. David,et al.  Nitrogen Fertilizer and Herbicide Transport from Tile Drained Fields , 2000 .

[15]  J. Syers,et al.  Movement of pesticides to surface waters from a heavy clay soil , 1995 .

[16]  A. Ginebreda,et al.  Water toxicity assessment and spatial pollution patterns identification in a Mediterranean River Basin District. Tools for water management and risk analysis. , 2011, The Science of the total environment.

[17]  R. Schulz Field studies on exposure, effects, and risk mitigation of aquatic nonpoint-source insecticide pollution: a review. , 2004, Journal of environmental quality.

[18]  T. Burt,et al.  A classification of drainage and macropore flow in an agricultural catchment , 2002 .

[19]  Rainer Brüggemann,et al.  Analysis of monitoring data of pesticide residues in surface waters using partial order ranking theory , 2003, Environmental Toxicology and Chemistry.

[20]  R. Schwarzenbach,et al.  Comparison of atrazine losses in three small headwater catchments. , 2005, Journal of environmental quality.

[21]  M. Liess,et al.  DETERMINATION OF INSECTICIDE CONTAMINATION IN AGRICULTURAL HEADWATER STREAMS , 1999 .