Fate and transport of copper-based crop protectants in plasticulture runoff and the impact of sedimentation as a best management practice

被引:33
作者
Gallagher, DL [1 ]
Johnston, KM [1 ]
Dietrich, AM [1 ]
机构
[1] Virginia Tech, Blacksburg, VA 24061 USA
关键词
plasticulture; copper; crop protectant; best management practice; sedimentation control; pesticide;
D O I
10.1016/S0043-1354(00)00594-7
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The fate and distribution of copper-based crop protectants. applied to pl:plasticulture tomato fields to protect against disease. were investigated in a greenhouse-scale simulation of farming conditions in a coastal environment. Following rainfall. 99% of the applied copper was found to remain on the fields sorbed to the soil and plants: most of the suit-bound copper was found sorbed to the top 2.5 cm of soil between the plasticulture rows. Of the copper leaking the agricultural fields. 82% was found in the runoff with the majority, 74%, sorbed to the suspended solids. The remaining copper, 18%, leuched through the soil and entered the groundwater with 10%: in the dissolved phase anti 8% sorbed to suspended solids. Although only 1% copper was found to leave the held, this was sufficient to cause high copper concentrations (average 2102 +/- 433 mug/L total copper and 189 +/- 139 mug L dissolved copper) in the runoff. Copper concentrations in groundwater samples were also high (average 312 +/- 198 mug L total copper and 216 +/- 99 mug/L dissolved copper). Sedimentation, a best management practice for reducing copper loadings. was found to reduce the total copper concentrations in runoff by 90% to a concentration of 245 +/- 127 mug/L L; however, dissolved copper concentrations remained stable, averaging 139 +/- 55 mug L. Total copper concentrations were significantly reduced by the effective removal of suspended solids with sorbed copper. (C) 2001 Elsevier Science Ltd. All rights reserved.
引用
收藏
页码:2984 / 2994
页数:11
相关论文
共 39 条
[1]  
*AM PUBL HLTH ASS, 1995, STAND METH EX WAT WA
[2]  
BLANCARD D, 1994, COLOUR ATLAS TOMATO
[3]  
Brezonik P.K., 1991, METAL ECOTOXICOLOGY
[4]   CONTAMINATED MARINE-SEDIMENTS - WATER COLUMN AND INTERSTITIAL TOXIC EFFECTS [J].
BURGESS, RM ;
SCHWEITZER, KA ;
MCKINNEY, RA ;
PHELPS, DK .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 1993, 12 (01) :127-138
[5]   SURVIVAL AND GROWTH OF BIVALVE LARVAE UNDER HEAVY-METAL STRESS [J].
CALABRESE, A ;
MACINNES, JR ;
NELSON, DA ;
MILLER, JE .
MARINE BIOLOGY, 1977, 41 (02) :179-184
[6]  
CHEADLE R, 1999, P ASCE CSCE NAT C EN, P20
[7]  
DIETRICH AM, 1996, P 2 VIRG E SHOR NAT, P125
[8]  
DIETRICH AM, 2001, IN PRESS J AM WATER
[9]   Metal available sites on colloidal organic compounds in surface waters (Brazil) [J].
Eyrolle, F ;
Benaim, JY .
WATER RESEARCH, 1999, 33 (04) :995-1004
[10]   Experimental evidence of transport of pesticides through field soils - A review [J].
Flury, M .
JOURNAL OF ENVIRONMENTAL QUALITY, 1996, 25 (01) :25-45