Environmental Toxicology and Chemistry, 22(12) (2003) pp.3009-3016
REPRODUCTIVE AND DEVELOPMENTAL EFFECTS OF ATRAZINE ON THE
ESTUARINE MEIOBENTHIC COPEPOD AMPHIASCUS TENUIREMIS
ADRIANA C. BEJARANO* and G. THOMAS CHANDLER
Department of Environmental Health Sciences, Norman J. Arnold School of
Public Health, University of South Carolina, Columbia,
South Carolina 29208, USA
Atrazine is one of the most widely used herbicides in the United States. Atrazine
concentrations in coastal environments chronically range from 90 ng/L to 46
µg/L, with rare but measured concentrations near 60 µg/L at edge-of-field
conditions. Chronic atrazine effects on estuarine benthos exposed to environmentally
relevant concentrations are unknown. The purpose of this research was to assess
atrazine reproductive and developmental effects over multiple-generation exposures
of the copepod Amphiascus tenuiremis. Copepods were chronically exposed to
two environmentally relevant nominal atrazine concentrations (2.5 and 25 µg1
L, and to an environmentally unrealistic concentration (250 µg/L). Chronic
exposures were performed using a 96-well microplate life cycle bioassay. Individual
stage I copepodites (C1, n = 60/treatment) were reared through two generations
(F0 and F1) to sexual maturity and individually mated in microwells containing
200 µl of atrazine solution. Copepod survival across all treatments
and generations was >95%. Atrazine did not affect development to reproductive
maturity, time to egg extrusion, or time to egg hatch (p > 0.05). However
reproductive failures increased across generations with increasing atrazine
concentrations. Reproductive failures in the 0-, 2.5-, 25-, and 250-µ.g/L
atrazine treatments were 11, 11, 20, and 24% for the F0, and 4, 9, 26, and
38% for the F1 respectively. Compared to controls, total nauplii production
per female was reduced by approximately 22% in F0, females exposed to 250
µg/L atrazine (p < 0.05), and by approximately 23%, approximately
27%, and approximately 32% in F1 females exposed to 2.5-, 25-, and 250-µg/L
atrarine treatments, respectively (p < 0.05). The combined effect of reproductive
failure and reduced offspring production significantly reduced total population
growth in the F1 generation (p < 0.05) even at atrazine concentrations
lower than that considered safe for seawater chronic exposure (26 µg/L).
Environmental Science and technology, 38 (2204) pp.522-528
Phenylpyrazole
Insecticide Fipronil Induces Male Infertility in the Estuarine Meiobenthic
Crustacean Amphiascus tenuiremis
TAWNYA L. CARY (a), G. THOMAS CHANDLER.(a, *), DAVID C.
VOLZ (a), SPENCER S. WALSE (b), and JOHN L. FERRY(b)
(a) Department of Environmental Health Sciences, Norman J.
Arnold School of Public Health and
(b) Department of Chemistry. University of South Carolina. Columbia, South
Carolina 29208
Copepods are the most abundant arthropods on earth and are often the most
important secondary producers in estuarine/marine food webs. The new GABA
(?-aminobutyric acid)-disrupting insecticide fipronil (FP) induces unique
sex-specific reproductive dysfunction in male meiobenthic copepods, leading
to trans-generational population depression at environmentally realistic concentrations
(0.63 µg/L). Using a newly developed 96-well microplate lifecyde bioassay,
more than 700 individual Stage-I juveniles were reared to adulthood in as
short as 12 days in only 200µL of control (CTL) or 0.63µg-FP/L
seawater solution. Individual virgin male: female pairs were then cross-mated
for all possible combinations within and across rearing treatments and allowed
to mate for an additional 12 days in CTL or 0.63 µg-FP/L solution. FP
at 0.63 µg/L caused no significant lethality to any mating combinations
but evoked 73% or 89% inhibition of reproduction when FP-reared males were
mated with either a control- or FP-reared female in FP solution, respectively.
In contrast, when C71-reared males were mated with FP-reared females in FP
solution, there was no difference in reproductive success compared to FP-free
controls. When FP-reared males were mated with either female group in FP-free
solution, these mating pairs displayed a 3-day delay in time to brood sac
extrusion but ultimately did reproduce. As fipronil (1) has a high Kow, (2)
is persistent in sediments where meiobenthic copepods live, and (3) has been
detected in estuarine waters >0.7 µg/L, it may pose high risk to
copepod production in estuarine systems.
Environmental Science and Technology, 38 (2004) pp.6407-6414
Population Consequences of Fipronil and Degradates to Copepods at Field Concentrations: An Integration of Life Cycle Testing with Leslie Matrix Population Modeling
G. THOMAS CHANDLER (*,a), TAWNYA L. CARY (a), ADRIANA C. BEJARANO (a), JACK
PENDER (b), and JOHN L. FERRY (b)
(a) Department of Environmental Health Sciences Norman J Arnold School of
Public Health, (b)
Department of Chemistry, University of South Carolina, Columbia, South Carolina
29209
The predominant data used in ecological risk assessment today are individual-based
rather than population-based; yet environmental policies are usually designed
to protect populations of threatened species or communities. Most current
methods in ecotoxicology are limited by largely logistic/ technology-driven
requirements that yield data for a relatively small number of test species
and end points that focus on acute lethality or sublethal nonproductionbased
parameters (e.g., biomarkers, mutagenesis, genetic change, physiological condition).
A contrasting example is presented here showing the predictive ability of
meiobenthos-based full life cycle toxicity testing to extrapolate multi-generational
effects of chemicals on variables of import to population growth and maintenance.
Less than 24-h-old larvae of a meiobenthic copepod were reared individually
in 96-well microplate exposures to parent and degradates of the phenylpyrazole
insecticide fipronil. Survival, development rates, sex ratio change, fertility,
fecundity, and hatching success were tracked daily for 32 d through mating
and production of three broods in spiked seawater. These data were then inserted
in a Leslie (Lefkovitch) matrix stage-based population growth model to predict
relative rates of population increase (lambda) and changes in net population
growth with time and toxicant concentration. Field-reported test concentrations
produced strong reproductive (52- 88%) and net production (40-80%) depressions
for parent (at 0.25 and 0.5,µg/L), desthionyl (0.25 and 0.5µg/L),
and sulfide (0.15 µg/L) moieties as compared to controls. Spiked sediment
exposures of 65-300 ng of fipronil/g of dry sediment yielded significantly
reduced production rates per female that were 67-50% of control production.
The consistent reproductively linked impacts of fipronil and its degradation
products at the population maintenance levels suggest risks to sediment-dwelling
crustaceans at concentrations well below noneffects for most aquatic test
species based on risk assessment data from primarily acute and sub-life cycle
toxicity tests.
POLYCYCLIC AROMATIC HYDROCARBON BIOACCUMULATION
BY MEIOBENTHIC
COPEPODS INHABITING A SUPERFUND SITE: TECHNIQUES FOR MICROMASS
BODY BURDEN AND TOTAL LIPID ANALYSIS
SUSAN L. KLOSTERHAUS (*,a), P. LEE FERGUSON (b), and G. THOMAS CHANDLER (a)
(a) University of South Carolina, Norman J. Arnold School of Public Health,
Department of Environmental Health Sciences, Columbia,
South Carolina, USA 29208
(b) State University of New York-Stony Brook, Marine Sciences Research Center;
Stony Brook, New York, USA 11794
Microtechniques for polycyclic aromatic hydrocarbon (PAH) body burden and total lipid analysis were developed and applied to determine the first lipid-normalized bioaccumulation factors for a hydrophobic organic toxicant in a meiobenthic organism (0.063-0.500 mm) living in field-contaminated sediments. The total lipid microtechnique combines the standard Bligh-Dyer extraction method with a colorimetric quantification method for analysis of samples containing 1 to 50 µg lipid. The microtechnique for body burden analysis quantifies PAHs from tissue samples containing as little as 10 pg PAH. Fluoranthene, benz[a]anthracene, and benzo[a]pyrene biota-sediment accumulation factors (BSAFs) were determined for the meiobenthic copepod Microarthridion littorale living in an estuarine U.S. Environmental Protection Agency Superfimd site. Gravid female, nongravid female, and male BSAFs were 0.82, 0.54, and 0.36, respectively, for fluoranthene; 0.50, 0.44, and 0.40, respectively, for benz[a]anthracene; and 0.09, 0.12, and 0.15, respectively, for benzo[a]pyrene. Comparison of nonlipid-normalized bioaccumulation factors (BAFs) to BSAFs indicates that M. littorale bioaccumulated PAHs on a gram lipid basis. The BSAFs declined consistently with increasing PAH log Kow for all copepod sex and reproductive stages. Sex- and stage-specific comparisons of BSAFs suggest that differences in lipid content and quality may lead to differences in BSAF values depending on PAH molecular weight and/or hydrophobicity.
Environmental Toxicology and Chemistry, 23(5) (2004)
DISTRIBUTION OF ATRAZINE INTO THREE CHEMICAL
FRACTIONS: IMPACT OF
SEDIMENT DEPTH AND ORGANIC CARBON CONTENT
Kelly L. SMALLING (a) and C. Marjourie AELION (*,a,b)
(a) Department of Environmental Health Sciences,
(b) Marine Science Program, University of South Carolina, Columbia, South
Carolina 29208, USA
Abstract- The fate and transport of organic contaminants in aquatic sediments are impacted largely by microbial degradation and sorption to organic matter. Atrazine, a pre-emergent herbicide, has the potential to contaminate groundwater because of its slight water solubility, long half-life, and sorption to organic matter Mineralization and distribution of 14C-atrazine into three chemical factions were monitored over time in surface and subsurface coastal aquatic sediments of different land use. Sediments were extracted with an organic solvent followed by alkali extraction, and 14C activity was measured in the aqueous, solvent, and basic fractions (representing nonsorbed compounds, loosely sorbed compounds, and humic or fulvic acid bound compounds, respectively). Limited mineralization of atrazine occurred (< 4%). The 14C activity in the aqueous and basic fractions increased over time, was greater in surface versus subsurface sediments, and was positively correlated with sediment organic carbon (SOC) content, indicating greater biological and chemical activity. Total 14C recovered ranged from 50 to 90%, was less in surface versus subsurface sediments, and was not correlated with SOC after 80 d. These results suggest that in native aquatic surface sediments, atrazine sorption plays a major role, whereas in subsurface sediments atrazine may be available for degradation and transport to shallow groundwater.