1995
DOI: 10.1007/bf00197443
|View full text |Cite
|
Sign up to set email alerts
|

Comparative toxicities of selected compounds to nauplii of Balanus amphitrite amphitrite Darwin and Artemia sp.

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
1
1
1
1

Citation Types

1
4
0

Year Published

1997
1997
2022
2022

Publication Types

Select...
9

Relationship

0
9

Authors

Journals

citations
Cited by 12 publications
(5 citation statements)
references
References 3 publications
1
4
0
Order By: Relevance
“…In the present study, the 24 h LC 50 for mortality and the EC 50 for attachment for the same species was found to be 25 and 22 mg TBT l 71 , respectively. Although it is difficult to compare these results due to different assay conditions and exposure durations, they are consistent in showing that the cyprids of B. amphitrite are much more tolerant of TBT than its stage II nauplii, as the latter have a much lower 24 h LC 50 (0.71 mg TBTO l 71 , Liberatore et al 1977; 2 mg TBTCl l 71 , Sasikumar et al 1995). This implies that, when AF paints release TBT at a rate that can prevent cyprid attachment, the leachate must have adverse effects on barnacle nauplii, as well as many non-target organisms, such as neogastropods, which may develop imposex and become infertile at 4 ng TBT l 71 (Gibbs et al 1988), and bivalves, whose embryonic and larval development may become abnormal at 1.3 mg TBT l 71 (His et al 1983;Roberts 1987).…”
Section: Biofouling 263supporting
confidence: 53%
“…In the present study, the 24 h LC 50 for mortality and the EC 50 for attachment for the same species was found to be 25 and 22 mg TBT l 71 , respectively. Although it is difficult to compare these results due to different assay conditions and exposure durations, they are consistent in showing that the cyprids of B. amphitrite are much more tolerant of TBT than its stage II nauplii, as the latter have a much lower 24 h LC 50 (0.71 mg TBTO l 71 , Liberatore et al 1977; 2 mg TBTCl l 71 , Sasikumar et al 1995). This implies that, when AF paints release TBT at a rate that can prevent cyprid attachment, the leachate must have adverse effects on barnacle nauplii, as well as many non-target organisms, such as neogastropods, which may develop imposex and become infertile at 4 ng TBT l 71 (Gibbs et al 1988), and bivalves, whose embryonic and larval development may become abnormal at 1.3 mg TBT l 71 (His et al 1983;Roberts 1987).…”
Section: Biofouling 263supporting
confidence: 53%
“…Similarly, the prolongation of larval development due to exposure to low salinity during embryonic development could increase the likelihood of being preyed on or misrouted to an unfavorable habitat. Since the larvae have often been used in settlement or toxicity assays (Rittschof et al 1984, 1986, Holmstrom et al 1992, Clare et al 1994, Kon et al 1995, Sasikumar et al 1995, when obtaining the larvae for bioassays, care should be taken to avoid using adults collected from, or cultured in, low salinity environments.…”
Section: Discussionmentioning
confidence: 99%
“…By using artificial seawater and sibling barnacles, the reproducibility of the assay may be improved (Sasikumar et al, 1995). However, because genetic and other variability in larval settlement responses do occur under natural conditions, it can be argued that exclusion of such variability by selection of sibling barnacles for assays is counter-productive if the aim is to screen for broad spectrum antifouling chemicals.…”
Section: Inter-batch Variabilitymentioning
confidence: 98%