Ghekiere, A.

Open Marine Archive

  
 
 
 
 
 
 
 
AN GHEKIERE 
 
 
 
 
 
 
 
STUDY OF INVERTEBRATE-SPECIFIC EFFECTS OF ENDOCRINE DISRUPTING 
CHEMICALS IN THE ESTUARINE MYSID NEOMYSIS INTEGER (LEACH, 1814)  
 
 
 
 
 
 
 
 
 
 
 
 
Thesis submitted in fulfillment of the requirements 
For the degree of Doctor (PhD) in Applied Biological Sciences 
 
 Dutch translation of the title: 
Studie van invertebraat-specifieke effecten van endocrien-verstorende stoffen in de estuariene 
aasgarnaal Neomysis integer (Leach, 1814) 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
ISBN 90-5989-105-8 
 
 
 
 
 
 
 
 
 
 
 
The author and the promotor give the authorisation to consult and to copy parts of this work 
for personal use only. Every other use is subject to the copyright laws. Permission to 
reproduce any material contained in this work should be obtained from the author. 
 
 
 
 
CHAPTER 9 
 
 
 
 
 
GENERAL CONCLUSIONS AND RESEARCH 
PERSPECTIVES 
 
 
 
GENERAL CONCLUSIONS 
CHAPTER 9 
 
 
 
GENERAL CONCLUSIONS AND RESEARCH PERSPECTIVES 
 
 
 
Despite the many studies on endocrine disruption using vertebrate models published over the 
past decade, few studies on invertebrates are available. This is surprising since 95% of all 
animal species do not have a backbone. Two main reasons for this observation can be given. 
First, initial studies with invertebrates were directly based on those with vertebrates thereby 
ignoring major differences in hormonal control strategies between both groups. Second, basic 
understanding of hormonal regulation in most invertebrates is still largely lacking. Some 
groups of invertebrates like the arthropods offer major advantages in this perspective as their 
hormone systems have been characterized in detail. For example, it has been well established 
that in arthropods and other ecdysozoa (animals that grow through molting) ecdysteroids 
(molting hormones) are major endocrine signaling molecules involved in the control of 
physiological processes such as molting, embryonic development, metamorphosis, and 
reproduction. To date, the uniqueness of this hormonal regulation is not reflected in proposed 
regulatory screening and testing programs that only focus on estrogen, androgen, and thyroid 
signaling which are not functional hormones in arthropods. Since arthropod models have been 
proposed for inclusion in many regulatory screening and testing programs for endocrine 
disruptors, assays are urgently needed to assess chemical interference with ecdysteroid 
signaling as a way of identifying invertebrate-specific endocrine toxicity. Specifically, mysids 
are the only invertebrates that have been proposed by the US Environmental Protection 
Agency in their endocrine disruptor testing and screening program. 
The aim of this doctoral thesis is to specifically address the issues raised above by developing 
novel methods to evaluate invertebrate-specific endocrine disruption using the mysid shrimp 
Neomysis integer (Crustacea: Mysidacea). A number of crucial physiological processes that 
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are under ecdysteroid control were selected for this purpose, vitellogenesis, molting, and 
embryonic development.  
 
Vitellogenesis involves the production of the egg yolk protein vitellin. This protein is the 
major source of nourishment during embryonic development of egg-laying invertebrates and 
vertebrates. Upregulation of vitellogenin, the precursor of vitellin, has been a reliable way of 
quantifying estrogenic exposure in fish. In ecdysozoans, vitellogenesis is known to be under 
ecdysteroid control. However, little research has been done on crustacean vitellogenesis 
following exposure to endocrine disrupting chemicals. In this study, we purified and 
characterized vitellin from the mysid Neomysis integer (Chapter 2) and subsequently 
developed a quantitative enzyme-linked immunosorbent assay (ELISA) (Chapter 3). The 
availability of a mysid vitellin ELISA is of particular importance for two reasons: (1) as a 
research tool to study the hormonal control of vitellogenesis in a crustacean (2) as a potential 
assay to study chemically-induced disruptions in mysid vitellogenesis and how this relates to 
effects on well-established reproductive endpoints. In Chapter 4 we evaluated the usefulness 
of the N. integer vitellin ELISA to detect potential effects of three suspected endocrine-
disrupting chemicals on mysid vitellogenesis. From these studies we can conclude that while 
developing an ELISA method is time-consuming, once established it is relatively rapid and 
easy to use. Our studies determined the size of N. integer vitellin (~700 kDa) and found that it 
is associated with a carotenoid moiety that facilitates the identification of vitellin during gel 
filtration. A protein elution profile will show two peaks with absorptions at both 474 nm 
(cartenoid) and 280nm (protein). Our purified vitellin was injected into rabbits to produce 
polyclonal antibodies. With the purified vitellin and the polyclonal antibodies, the ELISA was 
optimised. The time needed to optimise the final ELISA assay depends on the accuracy that 
one wants to achieve. The production of the polyclonal antibodies took a few months and the 
development of the mysid vitellin ELISA took approximately 3 to 4 weeks to complete. 
In the next step, the ELISA was used to study the effects of methoprene (insecticide), 
nonylphenol (surfactant and xeno-estrogen) and estrone (natural estrogen) on the 
vitellogenesis of N. integer (Chapter 4). These studies further added to the weight-of-evidence 
that estrogens appear to be less effective in causing disruption of normal vitellogenesis in 
crustaceans than in oviparous vertebrates. Most likely, this is a result of the different 
hormonal control strategies for vitellogenesis in crustaceans compared with oviparous 
vertebrates. Future studies should therefore be aimed at the identification and quantification 
of the hormones, the hormone receptors and downstream hormone-responsive genes and gene 
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GENERAL CONCLUSIONS 
products involved in the control of vitellogenesis and other hormone-regulated processes in 
crustaceans. Overall, such studies should lead to a better understanding of the mode-of-action 
of chemicals on crustacean hormone-regulated processes.  
In Chapter 8, preliminary steps were taken to validate the developed mysid vitellin ELISA 
method in the field by quantifying levels in ovigorous mysids collected from the Scheldt 
estuary. This study led to the first reported levels of vitellin in a mysid field population. 
Significant difference in vitellin levels were observed in females at different sampling sites in 
April 2005, and these could not be correlated with differences in either brood size or standard 
length. Similarly, no obvious correlations were observed between the abiotic factors 
(temperature, salinity, and dissolved oxygen) and the in situ vitellin levels. The most striking 
finding was significantly lower levels of vitellin in animals collected from the most upstream 
sites (S12, S15 and S22) compared to the most downstream site (S09). Verslycke et al. 
(2004b) previously studied seasonal and spatial patterns in energy allocation of N. integer in 
the Scheldt estuary at the same sites. N. integer in the latter study had less energy at the more 
upstream sites S15, and S22, where pollution was highest. Lower energy levels would be 
expected to impact a high energy-demanding process such as vitellogenesis. This would lead 
to eggs with lower vitellin levels that would be of lower quality (Arcos et al., 2003). While 
these spatial differences were significant in the spring campaign, no such differences were 
observed during the sampling campaign of July 2005. Although our study in the Scheldt 
estuary demonstrated the usefulness of the mysid vitellin ELISA to quantify vitellin in mysid 
field populations, a more comprehensive dataset needs to be compiled in the future to confirm 
the spatial trends observed in these preliminary studies. 
 
Molting of N. integer was also studied as an invertebrate-specific endpoint to evaluate 
chemical interference with ecdysteroid signaling. The effects of the insecticide methoprene, a 
juvenile-hormone analog, on mysid molting were examined in Chapter 5. Crustaceans are an 
ecologically important part of the aquatic fauna, making this an essential group for assessing 
potential non-target effects of many pesticides - such as the mosquitocidal agent methoprene - 
that end up in aquatic ecosystems. Our study demonstrated that methoprene can indeed 
significantly affect mysid molting and growth at a sublethal concentration of 100 µg/l. This 
potential for invertebrate-specific endocrine toxicity of chemicals to non-target organisms is 
presently not addressed in regulatory screening and testing programs and could lead to a 
significant underestimation of the actual environmental risk of chemicals. Future studies 
should focus on measuring the hormones and receptors involved in mysid ecdysteroid 
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signaling to provide insights into the mode-of-action of juvenile hormone analogues and other 
pesticides in non-target arthropods and how this compares to what is known in insects. 
 
Fockedey et al. (2005a) recently described embryogenesis in N. integer. 
Subsequently, we evaluated embryonic development in mysids as a tool to study the potential 
effects of endocrine disruptors (Chapters 6,7). In this study, we examined mysid embryonic 
development from oviposition to free-living juveniles following exposure to methoprene, 
nonylphenol, and estrone. Embryos exposed to 1 and 100 µg methoprene/l had a significantly 
lower hatching success and lower survival rates than embryos in the control treatment. 
Nonylphenol had no effect on the duration of the three different developmental stages, but it 
significantly reduced survival and hatching at the highest tested concentration (100 µg/l) 
compared to the control. Estrone only affected hatching at the highest tested concentration of 
1 µg/l. In addition, we observed that hatched embryos exposed to 1 and 100 µg nonylphenol/l 
were more lethargic, and higher mortality was noted at these concentrations during the first 
two days after the final embryonic molt to free-living juveniles. Behavioral changes should be 
further examined in future studies and might provide sensitive and alternative ways of 
evaluating endocrine disruption.  
 
In conclusion, the juvenoid methoprene was capable of interfering with all three ecdysteroid-
regulated processes in N. integer. Methoprene affected mysid molting at 100 µg/l, 
embryogenesis at 1 µg/l, and lowered vitellin levels at all concentrations tested, although this 
latter effect was not statistically significant. It should be noted that differences in effect 
concentrations between these endpoints are to some extent a reflection of the exposure 
duration (i.e., 96h for vitellogenesis compared to 3 weeks for molting and 2 weeks for 
embryonic development) and therefore are not a direct indication of endpoint sensitivity. 
Interestingly, methoprene is a juvenile-hormone analog and not an ecdysteroid-analog. 
However, our studies and an increasing number of other studies have demonstrated that there 
is significant cross-communication between the juvenile hormone and ecdysteroid regulatory 
pathways (Mu and LeBlanc, 2004). Future studies could use a mechanistic approach to 
unravel further this crosstalk between regulatory pathways by quantifying the hormones in 
question, selecting chemicals with a known mode-of-action, by including other endpoints, and 
by doing lifecycle exposures in which all processes are quantified in a single exposure 
experiment. 
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GENERAL CONCLUSIONS 
Overall, this doctoral study produced data on chemical interference with three invertebrate-
specific endpoints in a standard toxicity invertebrate model, the mysid N. integer. While a 
previous doctoral study by Verslycke (2003) highlighted the use of mysid models in 
endocrine disruption research, this doctoral work points out the need for a shift in paradigm 
away from vertebrate-type approaches toward an assessment of invertebrate-specific 
endocrine disruption. Much is still unknown about invertebrate endocrine systems and 
fundamental studies are urgently needed to get a mechanistic understanding of the effects of 
endocrine disruptors in invertebrates. Our results can provide a guide as to which processes 
and which chemicals can be used in these types of mechanistic studies. Specifically, ongoing 
studies are using molecular approaches to characterize hormone receptors involved in mysid 
ecdysteroid/juvenoid signaling (Soin et al., unpublished data; Verslycke et al., unpublished 
data). These studies will provide a crucial next step in our understanding of ecdysteroid 
disruption in mysids. However, not all chemicals with molt-interfering potency will exert 
their effect at the receptor level. As such, a combination of in vivo and in vitro assays will 
continue to be needed for screening effects of chemicals on crustacean. The endpoints 
developed in this doctoral study could be an important and integral part of an in vivo mysid 
assay to evaluate endocrine disruption. 
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General conclusions and research perspectives

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