Effects of the herbicide roundup on freshwater microbial communities: A mesocosm study
The impact of the widely used herbicide glyphosate has been mainly studied in terrestrial weed control, laboratory bioassays, and field studies focusing on invertebrates, amphibians, and fishes. Despite the importance of phytoplankton and periphyton communities at the base of the aquatic food webs,...
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2007
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| 024 | 7 | |2 scopus |a 2-s2.0-39349090239 | |
| 024 | 7 | |2 cas |a glycine, 56-40-6, 6000-43-7, 6000-44-8; glyphosate, 1071-83-6; Glycine, 56-40-6; glyphosate, 1071-83-6; Herbicides; Pigments, Biological; Water Pollutants, Chemical | |
| 030 | |a ECAPE | ||
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 100 | 1 | |a Pérez, G.L. | |
| 245 | 1 | 0 | |a Effects of the herbicide roundup on freshwater microbial communities: A mesocosm study |
| 260 | |c 2007 | ||
| 270 | 1 | 0 | |m Pérez, G.L.; Instituto de Investigaciones Biotecnológicas, Instituto Tecnológico de Chascomús (Intech), CONICET, Camino Circunvalación Laguna Km 6, CC 164, 7130, Chascomús, Argentina; email: gperez@intech.gov.ar |
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| 506 | |2 openaire |e Política editorial | ||
| 520 | 3 | |a The impact of the widely used herbicide glyphosate has been mainly studied in terrestrial weed control, laboratory bioassays, and field studies focusing on invertebrates, amphibians, and fishes. Despite the importance of phytoplankton and periphyton communities at the base of the aquatic food webs, fewer studies have investigated the effects of glyphosate on freshwater microbial assemblages. We assessed the effect of the commercial formulation Roundup using artificial earthen mesocosms. The herbicide was added at three doses: a control (without Roundup) and two treatments of 6 and 12 mg/L of the active ingredient (glyphosate). Estimates of the dissipation rate (k) were similar in the two treatments (half-lives of 5.77 and 7.37 d, respectively). The only two physicochemical parameters showing statistically significant differences between treatments and controls were the downward vertical spectral attenuation coefficient kd(λ), where λ is wavelength, and total phosphorus concentration (TP). At the end of the experiment, the treated mesocosms showed a significant increase in the ratio kd(490 nm)/kd(550 nm) and an eightfold increase in TP. Round-up affected the structure of phytoplankton and periphyton assemblages. Total micro- and nanophytoplankton decreased in abundance in treated mesocosms. In contrast, the abundance of picocyanobacteria increased by a factor of about 40. Primary production also increased in treated mesocosms (roughly by a factor of two). Similar patterns were observed in the periphytic assemblages, which showed an increased proportion of dead : live individuals and increased abundances of cyanobacteria (about 4.5-fold). Interestingly, the observed changes in the microbial assemblages were captured by the analysis of the pigment composition of the phytoplankton, the phytoplankton absorption spectra, and the analysis of the optical properties of the water. The observed changes in the structure of the microbial assemblages are more consistent with a direct toxicological effect of glyphosate rather than an indirect effect mediated by phosphorus enrichment. © 2007 by the Ecological Society of America. |l eng | |
| 593 | |a Instituto de Investigaciones Biotecnológicas, Instituto Tecnológico de Chascomús (Intech), CONICET, Camino Circunvalación Laguna Km 6, CC 164, 7130, Chascomús, Argentina | ||
| 593 | |a Instituto de Limnología Dr. Ringuelet, Avenida Calchaquí km 23.5, 1888, Florencio Varela, Buenos Aires, Argentina | ||
| 593 | |a Departamento de Ecología, Genética Y Evolución, Facultad de Ciencias Exactas Y Naturales, Universidad de Buenos Aires, Buenos Aires, Argentina | ||
| 593 | |a Department of Earth and Environmental Sciences, Lehigh University, Bethlehem, PA 18015, United States | ||
| 690 | 1 | 0 | |a GLYPHOSATE |
| 690 | 1 | 0 | |a HERBICIDE |
| 690 | 1 | 0 | |a OPTICAL PROPERTIES |
| 690 | 1 | 0 | |a PERIPHYTON |
| 690 | 1 | 0 | |a PHYTOPLANKTON |
| 690 | 1 | 0 | |a PIGMENTS |
| 690 | 1 | 0 | |a PRIMARY PRODUCTION |
| 690 | 1 | 0 | |a ROUNDUP |
| 690 | 1 | 0 | |a WATER CHEMISTRY |
| 690 | 1 | 0 | |a WETLANDS |
| 690 | 1 | 0 | |a ABUNDANCE |
| 690 | 1 | 0 | |a BIOASSAY |
| 690 | 1 | 0 | |a ECOLOGICAL IMPACT |
| 690 | 1 | 0 | |a FOOD WEB |
| 690 | 1 | 0 | |a FRESHWATER ECOSYSTEM |
| 690 | 1 | 0 | |a GLYPHOSATE |
| 690 | 1 | 0 | |a MESOCOSM |
| 690 | 1 | 0 | |a MICROBIAL COMMUNITY |
| 690 | 1 | 0 | |a NANOPLANKTON |
| 690 | 1 | 0 | |a OPTICAL PROPERTY |
| 690 | 1 | 0 | |a PERIPHYTON |
| 690 | 1 | 0 | |a PESTICIDE APPLICATION |
| 690 | 1 | 0 | |a PHOSPHORUS |
| 690 | 1 | 0 | |a PHYSICOCHEMICAL PROPERTY |
| 690 | 1 | 0 | |a PHYTOPLANKTON |
| 690 | 1 | 0 | |a PIGMENT |
| 690 | 1 | 0 | |a PRIMARY PRODUCTION |
| 690 | 1 | 0 | |a TOXICOLOGY |
| 690 | 1 | 0 | |a WATER CHEMISTRY |
| 690 | 1 | 0 | |a AMPHIBIA |
| 690 | 1 | 0 | |a CYANOBACTERIA |
| 690 | 1 | 0 | |a INVERTEBRATA |
| 690 | 1 | 0 | |a PISCES |
| 690 | 1 | 0 | |a DRUG DERIVATIVE |
| 690 | 1 | 0 | |a FRESH WATER |
| 690 | 1 | 0 | |a GLYCINE |
| 690 | 1 | 0 | |a GLYPHOSATE |
| 690 | 1 | 0 | |a HERBICIDE |
| 690 | 1 | 0 | |a PIGMENT |
| 690 | 1 | 0 | |a ALGA |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a BACTERIUM |
| 690 | 1 | 0 | |a CHEMISTRY |
| 690 | 1 | 0 | |a DRUG EFFECT |
| 690 | 1 | 0 | |a ECOSYSTEM |
| 690 | 1 | 0 | |a ENVIRONMENTAL PROTECTION |
| 690 | 1 | 0 | |a MICROBIOLOGY |
| 690 | 1 | 0 | |a PHYTOPLANKTON |
| 690 | 1 | 0 | |a TIME |
| 690 | 1 | 0 | |a WATER POLLUTANT |
| 690 | 1 | 0 | |a WATER POLLUTION |
| 690 | 1 | 0 | |a ALGAE |
| 690 | 1 | 0 | |a BACTERIA |
| 690 | 1 | 0 | |a CONSERVATION OF NATURAL RESOURCES |
| 690 | 1 | 0 | |a ECOSYSTEM |
| 690 | 1 | 0 | |a FRESH WATER |
| 690 | 1 | 0 | |a GLYCINE |
| 690 | 1 | 0 | |a HERBICIDES |
| 690 | 1 | 0 | |a PHYTOPLANKTON |
| 690 | 1 | 0 | |a PIGMENTS, BIOLOGICAL |
| 690 | 1 | 0 | |a TIME FACTORS |
| 690 | 1 | 0 | |a WATER POLLUTANTS, CHEMICAL |
| 690 | 1 | 0 | |a WATER POLLUTION, CHEMICAL |
| 700 | 1 | |a Torremorell, Ana María | |
| 700 | 1 | |a Mugni, H. | |
| 700 | 1 | |a Rodríguez, Patricia Laura | |
| 700 | 1 | |a Solange Vera, M. | |
| 700 | 1 | |a Do Nascimento, M. | |
| 700 | 1 | |a Allende, L. | |
| 700 | 1 | |a Bustingorry, J. | |
| 700 | 1 | |a Escaray, R. | |
| 700 | 1 | |a Ferraro, M. | |
| 700 | 1 | |a Izaguirre, I. | |
| 700 | 1 | |a Pizarro, H. | |
| 700 | 1 | |a Bonetto, C. | |
| 700 | 1 | |a Morris, D.P. | |
| 700 | 1 | |a Zagarese, H. | |
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