Gene expression and activity of digestive proteases in Daphnia: effects of cyanobacterial protease inhibitors
© Schwarzenberger et al; licensee BioMed Central Ltd. 2010
Received: 18 November 2009
Accepted: 4 May 2010
Published: 4 May 2010
The frequency of cyanobacterial blooms has increased worldwide, and these blooms have been claimed to be a major factor leading to the decline of the most important freshwater herbivores, i.e. representatives of the genus Daphnia. This suppression of Daphnia is partly attributed to the presence of biologically active secondary metabolites in cyanobacteria. Among these metabolites, protease inhibitors are found in almost every natural cyanobacterial bloom and have been shown to specifically inhibit Daphnia's digestive proteases in vitro, but to date no physiological responses of these serine proteases to cyanobacterial protease inhibitors in Daphnia have been reported in situ at the protein and genetic levels.
Nine digestive proteases were detected in D. magna using activity-stained SDS-PAGE. Subsequent analyses by LC-MS/MS and database search led to the identification of respective protease genes. D. magna responded to dietary protease inhibitors by up-regulation of the expression of these respective proteases at the RNA-level and by the induction of new and less sensitive protease isoforms at the protein level. The up-regulation in response to dietary trypsin- and chymotrypsin-inhibitors ranged from 1.4-fold to 25.6-fold. These physiological responses of Daphnia, i.e. up-regulation of protease expression and the induction of isoforms, took place even after feeding on 20% cyanobacterial food for only 24 h. These physiological responses proved to be independent from microcystin effects.
Here for the first time it was shown in situ that a D. magna clone responds physiologically to dietary cyanobacterial protease inhibitors by phenotypic plasticity of the targets of these specific inhibitors, i.e. Daphnia gut proteases. These regulatory responses are adaptive for D. magna, as they increase the capacity for protein digestion in the presence of dietary protease inhibitors. The type and extent of these responses in protease expression might determine the degree of growth reduction in D. magna in the presence of cyanobacterial protease inhibitors. The rapid response of Daphnia to cyanobacterial protease inhibitors supports the assumption that dietary cyanobacterial protease inhibitors exert a strong selection pressure on Daphnia proteases themselves.
Increasing nutrient input has led to eutrophication in many lakes, which coincides with the increasing dominance of bloom-forming cyanobacteria in the phytoplankton assemblages [1, 2]. This increasing dominance of cyanobacteria has been claimed to be a major factor leading to the decline in Daphnia abundance across and within lakes [3–5]. These observations from the field are corroborated by laboratory studies which have demonstrated negative effects of cyanobacteria on Daphnia [6, 7]. However, the generality of these observations has been questioned by a manipulative field study , and other recent studies have indicated that Daphnia may adapt to increasingly tolerate dietary cyanobacteria [9–11] and that increased tolerance to cyanobacterial toxins may be transferred to the offspring generations . However, neither on protein nor on genetic level have the underlying mechanisms for increased tolerance been addressed, yet. The genome of Daphnia has recently become available, creating the opportunity to address the interaction of cyanobacteria and Daphnia on the levels of gene expression and proteins more specifically.
Cyanobacteria are known to contain toxins and an array of other biologically active secondary metabolites [13, 14]. Cyanobacterial protease inhibitors are among the most widely spread secondary metabolites, as they have been found in nearly every cyanobacterial bloom [14, 15]. Different protease inhibitors have been isolated from different cyanobacteria genera  as well as from different cyanobacterial strains of the same species [17, 18]. Many cyanobacterial protease inhibitors act against serine proteases (i.e. trypsins and chymotrypsins), which represent the most important digestive proteases in the gut of Daphnia magna , and of which a surprisingly high number was found in the genome of D. pulex , a closely related species of D. magna.
Here we tested whether Daphnia displays physiological plasticity in response to dietary cyanobacterial protease inhibitors, assuming that positive selection for increased plasticity might be one mechanism for the recently reported adaptation of Daphnia to co-occuring cyanobacteria . More specifically, we investigated the physiological response of a given genotype of D. magna to dietary cyanobacterial protease inhibitors, making use of the previously reported specific interaction of these inhibitors with digestive trypsins and chymotrypsins of D. magna . By feeding them mixtures of a green alga with two different strains of the cyanobacterium Microcystis aeruginosa, which either contained trypsin- or chymotrypsin inhibitors, we were able to independently determine the effects of the two families of inhibitors on the expression and the activity of D. magna's digestive proteases.
Somatic growth rates on different food treatments
Activity and stability of Daphnia serine proteases
The chymotrypsin activity of the Daphnia homogenate was 0.23 μmol pNA/min/μg protein. There was a small, albeit significant (one way ANOVA: p < 0.05; F1,4 = 0.0002) decrease between the specific activity of chymotrypsin of the Daphnia homogenate and the same homogenate treated with 2 M urea (0.22 μmol pNA/min/μg protein).
The specific trypsin activity of the Daphnia homogenate was 0.02 μmol pNA/min/μg protein. There was no significant (one way ANOVA: p = 0.06; F1,4 = 0.06) effect of 2 M urea on trypsin activity.
SDS-PAGE and native PAGE of Daphnia homogenate
Food treatments: SDS-PAGE
In the homogenate of D. magna grown on 20% NIVA Cya 43 (which contains strong chymotrypsin inhibitors ), the band pattern of the trypsins with regard to the number and the apparent molecular weight of the bands did not change in comparison to animals grown on pure 100% S. obliquus. However, the intensity of the trypsin bands between 24 and 34 kDa increased; as did the chymotrypsin band at 21 kDa. A different band pattern in the chymotrypsin bands also became obvious (Fig. 3). The two visible bands between 17 and 19 kDa on the SDS-PAGE in the treatment with the cyanobacterium had a different apparent molecular weight than the 18 kDa chymotrypsin band in the treatment with only the green alga.
Amplification efficiencies of the protease primers
Food treatments: QPCR
In the treatment with 20% NIVA Cya 43, the proteases were up-regulated between 5.05-fold (T208) and 26.7-fold (CT383); in the treatment with 20% PCC 7806 Mut the relative expression was also significantly up-regulated in all proteases; however, the effects were weaker than in the treatment with NIVA Cya 43 [between 1.4-fold (T208) and 5.9-fold (T152)]; (Fig. 4).
LC-MS/MS analysis of protease bands
The homogenate of Daphnia fed with 100% S. obliquus and the homogenate of Daphnia fed with NIVA Cya 43 (leading to a different protease band pattern) (Fig. 3) were subjected to LC-MS/MS analysis. Most bands of the SDS-PAGE with homogenate of D. magna fed with 100% S. obliquus could be identified via LC-MS/MS and database search using the MOWSE algorithm as implemented in the MS search engine Mascot (Matrix Science Ltd. London, UK)  (Additional file 1). The sequence match for the mass spectra of the bands from the 100% S. obliquus homogenate was low (≤ 10%). However, there were hardly any strikingly non-matching sequences. Since the proteases had very few cutting sites for trypsins, which is not surprising for they are all serine proteases, the sequence match with 7 to 10% was acceptable.
The bands of the 100% S. obliquus homogenate previously suggested to be chymotrypsins  could be assigned to the proteases 802 (18 kDa band) and 448 (22 kDa and 21 kDa bands), which had the best combination of the factors probability MOWSE score as well as the highest number of matched sequences and sequence coverage (Additional file 1). All three identified proteases were chymotrypsins. Only one (20 kDa) of the suggested chymotrypsin bands could not be identified. The bands between 24 and 34 kDa, formerly specified as trypsins , could be assigned to the proteases 152 and 208, which are both trypsins. They could not be differentiated because they matched to the same set of sequences.
However, the bands of the homogenate of D. magna fed with 20% NIVA Cya 43 and 80% S. obliquus (Fig. 3) could all be identified (Additional file 2). The LC-MS/MS results of the bands between 24 and 34 kDa were identical to those of the respective bands in the 100% S. obliquus lane and were assigned to the trypsins 152 and 208. However, here the identification was clearer: the two bands at 24 and 25 kDa were trypsin 208; the two others were trypsin 152. The band at 75 kDa that was visible in both gels could be identified as protease 610 in the 20% NIVA Cya 43 homogenate, which is also a trypsin, matching the results of Agrawal et al., 2005 . As also found for the gel with D. magna fed with 100% S. obliquus, the four bands between 17 and 22 kDa were also assigned to the proteases 802 and 448, although the two bands between 17 and 19 kDa (chymotrypsin 802) of the gel with D. magna fed with 20% NIVA Cya 43 had another apparent molecular weight. Although no longer active in the SDS-PAGE (no hydrolytic activity), the chymotrypsin 802 at 18 kDa was still found at this position in the LC-MS/MS analysis. These three different bands from the two SDS-PAGEs of both homogenates were all assigned to CT802, and thus represent three different isoforms of the same protease. In the homogenate of Daphnia fed with 20% NIVA Cya 43, the bands between 21 and 22 kDa identified as protease 448 were the same as in the gel with homogenate of Daphni a grown on 100% S. obliquus. The protease at 20 kDa was identified as protease 383, another chymotrypsin. The proteases of both homogenates in the SDS-PAGE are accordingly assigned (Fig. 3).
Expression of serine proteases after 24 h
The proteases T152, T208 and CT448 showed consistent results. In the food treatment with 20% NIVA Cya 43 they were up-regulated after 24 h compared to the calibrator (24 h 100% S. obliquus; Fig. 6). T208 and CT448 were slightly up-regulated after 48 h on 100% S. obliquus, while for T152 the expression stayed the same as after 24 h on 100% S. obliquus; all three proteases showed the highest (3.4 to 5.97-fold) up-regulation in the treatment with 24 h 20% NIVA Cya 43/24 h S. obliquus compared to all other treatments.
In CT383 the results were the same except for the 24 h 20% NIVA Cya 43 treatment. Here, the expression was significantly lower than in the calibrator.
The regulation of CT802, however, differed considerably from that of the other proteases. Here, in the treatment with 24 h 20% NIVA Cya 43 the expression was up-regulated already over 7-fold compared to the calibrator. After 48 h S. obliquus the expression of CT802 increased 11.9-fold compared to 24 h S. obliquus and was therefore even more induced than in the treatment with 24 h 20% NIVA Cya 43. However, CT802 showed a higher level of induction after 24 h 20% NIVA Cya 43/24 h S. obliquus compared to the calibrator (10.5-fold), but was significantly lower than on 48 h S. obliquus.
Expression of serine proteases in the presence of microcystin
Daphnia magna fed with 100% green alga showed normal to high growth rates (Fig. 1), whereas the growth rate when fed with 20% cyanobacterial food was reduced. A reduction in growth rate or body length as an effect of cyanobacterial food has been observed previously in various Daphnia species: Growth reduction due to interference of filamentous cyanobacteria with the filtering apparatus [23, 24] or due to a deficiency of polyunsaturated fatty acids (PUFAs)  or sterols , or because of the toxin content . The M. aeruginosa strains used here were single-celled, small enough to be ingested, and did not contain microcystins [28, 29]. Furthermore, a reduction in growth rate due to PUFA or sterol limitation can be excluded, since ≥ 80% of the dietary carbon was of eukaryotic origin, i.e. S. obliquus . Therefore, in our case, growth rate reduction in response to cyanobacteria is probably caused by serine protease inhibitors, since the cyanobacterial strains used contain either mainly trypsin inhibitors (PCC 7806 Mut ) or strong chymotrypsin inhibitors (NIVA Cya 43 ).
proteases of D. magna
The protease band pattern of D. magna grown on 20% PCC 7806 Mut was the same (Fig. 3) as on 100% S. obliquus. However, all trypsin bands showed reduced activity when the animals were fed with 20% PCC 7806 Mut, which is explicable by the release of cyanobacterial trypsin inhibitors from the Microcystis cells after ingestion by Daphnia during subsequent digestion in the gut. The activity of the chymotrypsins in the gel was not affected by this cyanobacterium, which is in accordance with the findings that PCC 7806 Mut mostly contains trypsin inhibitors . A different effect was visible for D. magna fed with 20% NIVA Cya 43. This cyanobacterial strain affected both types of serine proteases. In spite of the high content of chymotrypsin inhibitors in this cyanobacterial strain , the chymotrypsin band at 21 kDa of the Daphnia homogenate slightly increased in intensity (Fig. 3). Although the protein was still detectable, the 18 kDa chymotrypsin was no longer active in the presence of dietary chymotrypsin inhibitors, leading to reduced total chymotrypsin activity in D. magna homogenate. This reduction of chymotrypsin activity was partly compensated for by the expression of the two new isoforms at 17 and 19 kDa. These two new isoforms proved to be active in the presence of chymotrypsin inhibitors (Fig. 3), indicating that these isoforms are less sensitive against the cyanobacterial inhibitors than the 18 kDa chymotrypsin. The additional expression of less sensitive chymotrypsins strongly suggests that this regulatory response to dietary chymotrypsin inhibitors is adaptive to D. magna.
Despite the expression of additional chymotrypsins, the overall activity of these proteases was visibly reduced in the presence of dietary chymotrypsin inhibitors (Fig. 3), since the intensities of the chymotrypsin protease bands were weaker than those of the chymotrypsin bands in the 100% S. obliquus treatment.
Moreover, chymotrypsin inhibitors led to a strong increase in trypsin activity. This can be considered to be an indirect effect of the chymotrypsin inhibitors and might be a compensatory physiological response of D. magna to cope with a reduced chymotrypsin activity.
In summary, the ingestion of the trypsin inhibitors cyanopeptolins [16, 18, 19] from PCC 7806 Mut only led to a decrease in trypsin activity of D. magna, whereas the chymotrypsin inhibitors nostopeptin BN920 and cyanopeptolin 954  from NIVA Cya 43 not only affected chymotrypsin, but also led to an increase in trypsin activity as a putative compensatory response.
The previous classification of five protease bands on SDS-PAGE as trypsins was based on the inhibition by synthetic inhibitors, and the remaining active protease bands were merely postulated to be chymotrypsins . Here, via LC-MS/MS and subsequent database search, all Daphnia proteases were clearly identified as trypsins or chymotrypsins and assigned to protease genes. The reason for two bands in the same lane in the SDS-PAGE referring to the same protease gene might be protein ripening or unspecific proteolytic degradation during the gel run. Alternatively, it might be attributed to the presence of splice variants or isoforms stemming from two different gene copies simultaneously active in Daphnia.
The two homogenates, which showed differences in the protease band pattern (100% S. obliquus and 20% NIVA Cya 43; Fig. 3) were analysed by LC-MS/MS (Appendices 1 and 2). The chymotrypsin bands, which were identified as CT802, showed a different molecular weight pattern in the two homogenates (Fig. 3). Although not visible as an active protease in the 20% NIVA Cya 43 treatment on the SDS-PAGE (Fig. 3), the CT802 protein at 18 kDa still was found. This result points to total inhibition of the 18 kDa isoform of CT802 due to dietary chymotrypsin inhibitors from NIVA Cya 43. However, other isoforms of CT802 which were more resistant to the inhibitor were expressed, and it is reasonable to assume that these isoforms stem from different gene copies. The D. pulex genome has been shown to contain a surprisingly high number of gene duplicates, leading to lineage-specific gene family expansions, which resulted in high numbers of genes (e.g. peptidases in D. pulex ). Rapid gene family expansions in phenotypically important genes suggest scenarios wherein adaptive natural selection favours additional copies, e.g. for adaptation to increased dosage . In several insects, amplification of different esterase genes was the reason for resistance to organophosphate pesticides [37–39]; resistant strains of the mosquito Culex pipiens even showed a 250-fold increase in copy numbers .
To test if the observed changes in activity of the proteases on the SDS-PAGEs are caused by a change in gene expression, the relative expression of two trypsin genes (T152, T208) and of three chymotrypsin genes (CT383, CT448, CT802) in D. magna fed with three different food treatments were analysed with QPCR (Fig. 4). In the treatment with 20% NIVA Cya 43, both trypsins and CT448 were up-regulated by a factor of between 5 and 23. These results are reflected in the increased activity that was visible on the SDS-PAGE (Fig. 3). However, although the relative expression of CT383 and CT802 comparably increased (Fig. 4), only low activity of CT383 and of the two newly expressed isoforms of CT802 was observed on the SDS-PAGE (Fig. 3). One explanation for the low activity of CT802 might be that the new isoforms are not as active as CT802 in D. magna fed with green alga. CT383, of which no isoforms were detectable, might be more sensitive to the chymotrypsin inhibitors, so that the higher expression of CT383 might have been insufficient to compensate for simultaneous inhibition of the CT383 protein.
The 1.4 to 6-fold increase of the relative trypsin expression in D. magna fed with 20% PCC 7806 Mut was not visible as increased activity in the gel (Fig. 3); the same is true for the increase in chymotrypsin expression (2- to 3-fold; Fig. 3). SDS-PAGE is not sensitive enough to quantify protease activity, as doubling the amount of Daphnia homogenate in SDS-PAGE did not lead to an apparent increase in protease activity on the gels (data not shown). Hence, it is not surprising that the change in expression of trypsins and chymotrypsins of Daphnia from up to 5-fold was not visible as an increase in activity in SDS-PAGE.
Effects of different food treatments on the activity of digestive proteases in D. magna were already observed after 24 hours, which means that only a short period is required for D. magna to respond to the occurrence of dietary protease inhibitors. Such a rapid physiological response seems to be highly adaptive, since newborn Daphnia have to establish an optimal protease pattern quickly after birth to be able to initiate digestion. Gustafsson et al.  have shown that increased tolerance to microcystin-containing cyanobacteria was transferred to the offspring generations. If such a mechanism is also true for dietary protease inhibitors, maternal transfer might also lead to a fast establishment of an optimal protease pattern in newborn Daphnia.
Nevertheless, the additional expression of isoforms after 24 h and the concurrently observed up-regulation of protease expression of Daphnia fed with cyanobacteria are allocating additional resources to these proteins and can be assumed to be costly. To render the induction of proteases an evolutionary stable strategy, the level of expression should be tightly linked to the level of dietary protease inhibitors. However, such an immediate down-regulation of protease expression after sudden removal of dietary protease inhibitors was not observed, and an intermediate band pattern was visible in SDS-PAGE (Fig. 5). These observations can easily be explained by the fact that cyanobacterial mass developments in nutrient-rich lakes usually last for several months in summer so that the disappearance of cyanobacteria is a gradual process that can take several weeks . Hence, the disappearance of cyanobacterial protease inhibitors will be considerably slower under field conditions than under our experimental conditions, which means that Daphnia are fully capable of adjusting the expression level of proteases to the presence of protease inhibitors in the natural diet.
As CT802 was the only protease showing a completely different response to cyanobacterial protease inhibitors in QPCR analyses, it has been concluded that CT802 must be regulated in a manner different from the other proteases. Interestingly, CT802 is the only protease which expresses new isoforms after Daphnia had been fed with dietary cyanobacterial food (Fig. 3 and 5). Further investigation of the regulation and of the processing leading to these new isoforms is needed. However, protease inhibitors are obviously a strong trigger for up-regulation of protease expression and for an induction of new isoforms. These protease inhibitors might also exert a strong selection pressure on Daphnia proteases themselves.
Numerous studies have focused on microcystins as the only reason for decreased fitness in Daphnia due to cyanobacteria, since microcystin LR is known to inhibit protein phosphatases of Daphnia in-vitro . However, other secondary metabolites also have proved to have adverse effects on Daphnia [42, 43]. The most widespread group of cyanobacterial secondary metabolites are protease inhibitors, which appear in nearly all cyanobacterial blooms [14, 15], whereas this is not the case for microcystins. Von Elert et al.  have shown that the most important group of digestive enzymes in Daphnia are trypsins and chymotrypsins; these enzymes are indeed inhibited in vitro by specific cyanobacterial inhibitors . By differentiating the effects of PCC 7806 WT and its microcystin-deficient mutant on Daphnia, both of which are known to contain strong trypsin inhibitors , the negative effects of microcystin-producing cyanobacteria on Daphnia could only be assigned to this compound to a limited degree [44, 45]. QPCR results showed no difference in the regulation of proteases in the gut of D. magna between PCC 7806 WT and Mut, which clearly demonstrates that the interaction of cyanobacterial protease inhibitors with digestive proteases in Daphnia is not affected by microcystins. Protease inhibitors should affect gut proteases of Daphnia immediately after ingestion of the cyanobacterial food particles and the subsequent release of inhibitors during digestion, before microcystins come in contact with their targets, i.e. protein phosphatases I and II. This suggests that the tolerance of digestive proteases against dietary protease inhibitors in Daphnia coexisting with cyanobacteria should be under strong positive selection, even in the presence of other cyanobacterial inhibitors.
Daphnia serine proteases have been shown in-vitro to be inhibited by specific cyanobacterial inhibitors . Here for the first time it was shown that a D. magna clone in-situ physiologically responds to dietary cyanobacterial protease inhibitors by phenotypic plasticity of the targets of these specific inhibitors, i.e. Daphnia gut proteases. The finding that D. magna responds to dietary protease inhibitors by up-regulation of protease expression on the RNA-level and by the expression of new and less-sensitive protease isoforms on the protein level strongly suggest that the observed phenotypic plasticity is adaptive.
To our knowledge this is the first report on physiological plasticity in D. magna in response to the most widely spread cyanobacterial inhibitors, i.e., protease inhibitors. We have been able to show distinct physiological responses to dietary trypsin and chymotrypsin inhibitors. These physiological responses involve increased expression of the targets of these inhibitors, digestive trypsins and chymotrypsins, and the expression of less-sensitive isoforms. Clearly these regulatory responses are adaptive for D. magna as they increase the capacity for protein digestion in the presence of dietary protease inhibitors. It is therefore reasonable to assume that the kind and extent of these responses in protease expression determine the degree of growth rate reduction in D. magna in the presence of cyanobacteria with protease inhibitors. These physiological responses proved to be independent from microcystin effects, as there only were negligible differences between protease expression of D. magna fed with M. aeruginosa PCC7806 WT and its microcystin-free mutant. Daphnia neonates respond very quickly to cyanobacterial food (24 h), which supports the assumption that dietary cyanobacterial protease inhibitors exert a strong selection pressure on Daphnia proteases themselves.
Cultivation of Daphnia magna
The Daphnia magna clone 'Binnensee'  was cultivated in 1 l filtered (0.2 μm) water from a nearby pond (Aachener Weiher in Cologne) and fed daily with a saturating concentration of Scenedesmus obliquus SAG 276-3a. The water and the food were exchanged every two days. Neonates from the 3rd clutch which were no more than twelve hours old were used for the experiments.
Cultivation of algae and cyanobacteria
Scenedesmus obliquus SAG 276-3a was grown in sterile 5 l semi-continuous batch cultures on cyanophycea-medium  at 20°C and constant light (150 μE). Every day 1 l of algal suspension was exchanged with fresh medium.
The cyanobacteria Microcystis aeruginosa NIVA Cya 43, a microcystin-free strain , the wild-type M. aeruginosa PCC 7806 WT and its mutant M. aeruginosa PCC 7806 Mut  (further referred to as NIVA Cya 43, PCC 7806 WT and PCC 7806 Mut) were cultivated in chemostats on cyanophycea-medium at 20°C and constant light (50 μE). The dilution rate was 0.23 d-1.
Somatic growth on different food treatments
Growth experiments were performed in 250 ml of 0.2 μm filtered pond water for six days with five neonates per replicate and a food concentration of 2 mg C/l. The treatments were either 100% Scenedesmus obliquus, 20% NIVA Cya 43 and 80% S. obliquus or 20% PCC 7806 Mut and 80% S. obliquus. Each treatment was run in triplicate. Water and food were exchanged daily. The dry weight of the animals was used to calculate the somatic growth rate (g, d-1) of each treatment according to Wacker et al., 2001  using the formula g = (ln xte - ln xtb)/Δt, for which xte is the weight after six days, xtb is the weight at the start of the experiment and Δt is the test duration, i.e. six days.
Preparation of Daphnia and gut homogenates
Neonates of Daphnia magna grown on 2 mg C/l of S. obliquus for six days were transferred to 5 μl 2 mM Dithiothreitol (DTT) per animal and were homogenized with a pestle. The homogenate was centrifuged for 3 min at 14,000× g. The protein concentration of the supernatant - the Daphnia-homogenate - was analyzed using a Qubit fluorometer and the appropriate Quant-iT™ Protein Assay Kit (Invitrogen, Paisley, UK) as according to the manufacturer's advice.
Guts including the hepatopancreases of D. magna grown on 2 mg C/l of S. obliquus for six days were separated and transferred to 5 μl 2 mM DTT per gut, as according to Agrawal et al., 2005  and treated in the same way as the Daphnia-homogenate.
Activity and stability of serine proteases of D. magna
Chymotrypsin activity of the Daphnia-homogenate was measured photometrically using the artificial substrate N-Succinyl-Alanine-Alanine-Proline-Phenylalanine-para-Nitroanilide (S(Ala)2ProPhepNA; Sigma, Munich, Germany; ). 10 μl Daphnia-homogenate was mixed with 980 μl 0.1 M potassium-phosphate-buffer, pH 6.5. The buffer contained 125 μM S(Ala)2ProPhepNA and 1% Dimethyl sulfoxide (DMSO; Sigma, Munich, Germany). The change in absorption was measured at a wavelength of 390 nm at 30°C continuously over 10 min. The trypsin activity was measured using the artificial substrate N-Benzoyl-Arginine-para-Nitroanilide (BApNA; Sigma, Munich, Germany; ). 10 μl Daphnia-homogenate was mixed with 895 μl 0.1 M potassium-phosphate-buffer, pH 6.5. The buffer contained 1.88 mM BApNA and 7.5% DMSO. The change in absorption was measured at a wavelength of 390 nm at 30°C continuously over 10 min. To test the stability of proteases, the buffers with Daphnia-homogenate were incubated for 2 min with 2 M urea before the kinetic analysis; activity was compared to the control without urea. Protein concentrations were analysed with the Qubit fluorometer.
SDS-PAGE and native gel of Daphnia-homogenate
Daphnia-homogenate (20 μg protein) with 5 μl 4× Laemmli-buffer  was loaded on a 12% SDS-polyacrylamide gel and run at 200 V at 6°C. Daphnia-homogenate (20 μg protein) with 5 μl 4× Laemmli-buffer without SDS was loaded on a native (no SDS) 12% polyacrylamide gel and run at 200 V at 6°C with SDS-free running buffer. After the run the gels were activity stained according to Von Elert et al., 2004 ; the gels were washed and incubated with agitation for 30 min at 4°C and for another 90 min at 20°C in 50 mM Tris-HCl (pH 9) containing 0.75% (w/v) casein Hammerstein. During this time the proteases, which were released from SDS, refolded and digested the casein. Gels were washed, fixed in 12% Trichloracetic acid, stained with 0.25% Coomassie Brilliant Blue in methanol:acetic acid:water (50:10:40, by vol.) and destained in methanol:acetic acid:water (42:8:50, by vol.). The molecular weights of the visible proteases were compared between the two methods. The marker on all PAGEs was the peqGold Prestained Protein Marker III (peqlab, Erlangen, Germany).
LC/MS-MS analysis of protease bands
Proteases were subjected to purification prior to LC-/MSMS analysis as follows:
200 live D. magna grown on 100% S. obliquus or 20% M. aeruginosa and 80% S. obliquus were homogenized and centrifuged as described above. 500 μl of the supernatant were mixed with 500 μl ultrapure water and were loaded onto a strong anion-exchanger column (SAX; Varian, No. 1210-2044; Palo Alto, CA, USA). The proteases bound to the column were eluted with one bed volume of 0.9 M NaCl and dialysed at 4°C for 24 h in 1 l of 10 mM imidazole-buffer, pH 6.9. Subsequently the proteases were precipitated with ice-cold 70% acetone. The pellet (centrifugation: 10 min, 14,000× g at 4°C) was lyophilized and resuspended in 40 μl of ultrapure water. It was mixed with 10 μl 4× Laemmli-buffer, loaded onto a 12% SDS-PAGE and Coomassie-stained after electrophoresis.
Coomassie-stained protein bands were excised from the gel, chopped into cubes and washed three times with acetonitrile-water (1:1). The gel pieces were shrunk with neat acetonitrile, allowed to rehydrate in 50 mM NH4HCO3 and dried in a speedvac. 10 mM DTT in 50 mM NH4HCO3 were added to the dried gel pieces, and proteins were reduced for 45 min at 56°C. To alkylate reduced cysteine residues, the remaining liquid was removed, and an equal volume of 50 mM iodoacetamide in 50 mM NH4HCO3 was added. The reaction was allowed to proceed for 30 min in the dark. Prior to in-gel digestion, the gel pieces were washed and dried as above. The gel pieces were allowed to rehydrate in an ice-cold solution of 12.5 ng/μl semiTrypsin semi-trypsin (for homogenate of Daphnia fed with 20% NIVA Cya 43) or Trypsin (for 100% S. obliquus homogenate; sequencing grade, Promega) in 10 mM NH4HCO3. After 45 min on ice, excessive enzyme solution was replaced by 5 - 20 μl of buffer without enzyme, and proteins were digested at 37°C overnight. The digestion was stopped by the addition of 5 - 20 μl 1% TFA, and peptides were extracted for 30 min at 37°C.
LC-MS/MS data for the 100% S. obliquus homogenate were acquired according to Hanisch et al., 2009 . For the homogenate of Daphnia fed with 20% NIVA Cya 43, LC-MS/MS data were acquired on a HCT ETD II iontrap mass spectrometer (Bruker Daltonics, Bremen, Germany) equipped with a nano ESI source (Bruker Daltonics, Bremen, Germany). Samples were introduced by an easy nano LC system (Proxeon, Odense, Denmark) using a vented column setup comprising a 0.1-mm-by-20-mm trapping column and a 0.075-by-100-mm analytical column, both self packed with ReproSil-Pur C18-AQ, 5 μm (Dr. Maisch, Ammerbuch, Germany). 5 μl to 18 μl of sample were aspirated into the sample loop, and a total of 25 μl was loaded onto the trap column at a flow rate of 6 μl/min. Loading pump buffer was 0.1% formic acid (FA). Peptides were eluted with a gradient of 0% to 35% acetonitrile (ACN) in 0.1% FA over 20 min and a column flow rate of 300 nl/min. Subsequently the ACN content was raised to 100% over 2 min, and the column was regenerated in 100% ACN for additional 8 min.
Data-dependent acquisition of MS and tandem MS (MS/MS) spectra was controlled by the Compass 3.0 software. MS1 scans were acquired in standard enhanced mode. Five single scans in the mass range from m/z 400 to m/z 1400 were combined for one survey scan. Up to three doubly and triply charged ions rising above a given threshold were selected for MS/MS experiments. Ultrascan mode was used for the acquisition of MS2 scans in the mass range from m/z 100 m/z 1600, and three single scans were added up. The ion charge control value was set to 250000 for all scan types. Peaklists in mascot generic format (mgf) were generated from the raw data by using the Data Analysis software module (Bruker Daltonics, Bremen, Germany).
Proteins were identified by using a local installation of MASCOT 2.2 (Matrix Science Ltd, London, UK). All serine proteases (13) from a D. magna EST-database (http://www.nematodes.org/NeglectedGenomes/ARTHROPODA/Crustacea.html; ) and a complete D. pulex database (http://wfleabase.org/; ; release: July 2007) were used. The database search could be reduced to serine proteases because Agrawal et al.  assigned all visible protease bands in SDS-PAGE to serine proteases. Searches were submitted via Proteinscape 2.0 (Bruker Daltonics, Bremen, Germany) with the following parameter settings: enzyme "semitrypsin", fixed modifications "carbamidomethyl", optional modifications "Methionine oxidation" and missed cleavages "1". The mass tolerance was set to 0.4 Da for peptide and fragment spectra. The most probable hits for the bands of the SDS-PAGEs were determined by the number of matched peptides, the percent-wise sequence coverage, and the probability MOWSE score.
Food treatments: SDS-PAGE and quantitative real-time PCR (QPCR)
Fifteen neonates of D. magna clone Binnensee were grown on 2 mg C/l in 1 l filtered pond water on either 100% S. obliquus, 20% NIVA Cya 43 and 80% S. obliquus or on 20% PCC 7806 Mut and 80% S. obliquus. Each treatment was run in triplicate. The water and the food were exchanged daily. The experiment was stopped after six days, after which half of the animals were used for 12% SDS-PAGE followed by activity staining; RNA was extracted from the other half using the RNeasy Mini Kit (Qiagen, Hilden, Germany) following the manufacturer's instructions. RNA was purified with DNase I (Fermentas, St. Leon-Rot, Germany) and reverse transcribed with High-capacity cDNA Reverse Transcription Kit with RNase Inhibitor (Applied Biosystems, Foster City, CA, USA).
Nine different housekeeping genes recently introduced for QPCR in D. magna by Heckmann et al., 2006  were used in QPCR analysis: actin, alpha-tubulin, cyclophilin, glyceraldehyde-3-phosphate dehydrogenase (GapDH), succinate dehydrogenase (SucDH), TATA-box binding protein (TBP), ubiquitin conjugating enzyme (UBC), 18S ribosomal RNA (18S), and 28S ribosomal RNA (28S). A normalisation factor was calculated based on the endogenous controls assessed by geNorm  according to Schwarzenberger et al., 2009 .
Forward and reverse primers for QPCR were established from the EST-database for five proteases that were found in the SDS-PAGEs (http://www.nematodes.org/NeglectedGenomes/ARTHROPODA/Crustacea.html ; Table 2). Real Time PCR with different concentrations of cDNA from six-day-old D. magna grown on S. obliquus was performed, and amplification efficiencies for the protease primers were calculated as according to Livak et al., 2001  using the formula AE = 10^(-1/slope), where AE is the amplification efficiency. qRT- PCR was performed as according to Schwarzenberger et al., 2009 . D. magna fed with 100% S. obliquus served as calibrator, which was always set as 1.
Microcystin effect on the expression of serine proteases
To investigate the effect of microcystin on Daphnia gut proteases, 15 neonates of Daphnia magna Binnensee were grown on 2 mg C/l in 1 l filtered pond water on either 100% S. obliquus, 10% PCC 7806 WT and 90% S. obliquus or on 10% PCC 7806 Mut and 90% S. obliquus for six days. Since the mortality after this time on 20% of the microcystin-containing WT was too high, D. magna were grown in the presence of 10% of either cyanobacterial strain. Each treatment was run in triplicate. The medium was exchanged daily. QPCR was conducted following Schwarzenberger et al., 2009 .
Expression of serine proteases after 24 h
Fifteen neonates of Daphnia magna Binnensee were grown on 2 mg C/l in 1 l filtered pond water on either 100% S. obliquus or on 20% NIVA Cya 43 and 80% S. obliquus. Each treatment was run in triplicate. RNA and proteins were extracted from half of the animals after 24 hours. Thereafter the remaining animals grown on the mixture with cyanobacteria and the animals grown on the green alga were further cultivated for another 24 hours on 100% S. obliquus. Again proteins and RNA were extracted, and Real Time PCR was conducted. The proteases were activity stained after SDS-PAGE.
The statistics were conducted with the program Statistica 6.0 (StatSoft, Inc., Tulsa, OK, USA). The data were analysed via one-way ANOVA and a post-hoc analysis (Tukey HSD). A Levene's Test was conducted to ensure homogenous variances. The data were ln (x+1) transformed when needed. The level of significance was p < 0.05.
The authors would like to thank Christoph Effertz and Jael Winkels for their help in conducting the experiments. This work was funded by the Deutsche Forschungsgemeinschaft (EL 179/6-1 and project B7 within SFB 680, molecular basis of evolutionary innovations). The authors thank Frederic Bartlett for the linguistic improvement of the manuscript.
- Trimbee AM, Prepas EE: Evaluation of total phosphorus as a predictor of the relative biomass of blue-green-algae with emphasis on Alberta Lakes. Canadian Journal of Fisheries and Aquatic Sciences. 1987, 44: 1337-1342. 10.1139/f87-158.View ArticleGoogle Scholar
- Downing JA, Watson SB, McCauley E: Predicting Cyanobacteria dominance in lakes. Canadian Journal of Fisheries and Aquatic Sciences. 2001, 58: 1905-1908. 10.1139/cjfas-58-10-1905.View ArticleGoogle Scholar
- Threlkeld ST: Midsummer dynamics of 2 Daphnia species in Wintergreen Lake, Michigan. Ecology. 1979, 60: 165-179. 10.2307/1936478.View ArticleGoogle Scholar
- Sommer U, Gliwicz ZM, Lampert W, Duncan A: The PEG-model of seasonal succession of planktonic events in fresh waters. Arch Hydrobiol. 1986, 106: 433-471.Google Scholar
- Ghadouani A, Pinel-Alloul B, Prepas EE: Effects of experimentally induced cyanobacterial blooms on crustacean zooplankton communities. Freshwat Biol. 2003, 48: 363-381. 10.1046/j.1365-2427.2003.01010.x.View ArticleGoogle Scholar
- Lampert W, Fleckner W, Rai H, Taylor BE: Phytoplankton control by grazing zooplankton - a study on the spring clear-water phase. Limnology and Oceanography. 1986, 31: 478-490. 10.4319/lo.1986.31.3.0478.View ArticleGoogle Scholar
- Hawkins P, Lampert W: The effect of Daphnia Body size on filtering rate inhibition in the presence of a filamentous cyanobacterium. Limnology and Oceanography. 1989, 34: 1084-1088. 10.4319/lo.19126.96.36.1994.View ArticleGoogle Scholar
- Sarnelle O: Initial conditions mediate the interaction between Daphnia and bloom-forming cyanobacteria. Limnology & Oceanography. 2007, 52: 2120-2127.View ArticleGoogle Scholar
- Hairston NG, Holtmeier CL, Lampert W, Weider LJ, Post DM, Fischer JM, et al: Natural selection for grazer resistance to toxic cyanobacteria: Evolution of phenotypic plasticity?. Evolution. 2001, 55: 2203-2214. 10.1111/j.0014-3820.2001.tb00736.x.View ArticlePubMedGoogle Scholar
- Gustafsson S, Hansson LA: Development of tolerance against toxic cyanobacteria in Daphnia. Aquatic Ecology. 2004, 38: 37-44. 10.1023/B:AECO.0000020985.47348.5e.View ArticleGoogle Scholar
- Sarnelle O, Wilson AE: Local adaptation of Daphnia pulicaria to toxic cyanobacteria. Limnology and Oceanography. 2005, 50: 1565-1570. 10.4319/lo.2005.50.5.1565.View ArticleGoogle Scholar
- Gustafsson S, Rengefors K, Hansson LA: Increases consumer fitness following transfer of toxin tolerance to offspring via maternal effects. Ecology. 2005, 86: 2561-2567. 10.1890/04-1710.View ArticleGoogle Scholar
- Carmichael WW: The toxins of cyanobacteria. Scientific American. 1994, 270: 64-72. 10.1038/scientificamerican0194-78.View ArticleGoogle Scholar
- Carmichael WW: Cyanobacteria secondary metabolites: the cyanotoxins. Journal of Applied Bacteriology. 1992, 72: 445-459.View ArticlePubMedGoogle Scholar
- Agrawal MK, Bagchi D, Bagchi SN: Acute inhibition of protease and suppression of growth in zooplankter, Moina macrocopa, by Microcystis blooms collected in Central India. Hydrobiologia. 2001, 464: 37-44. 10.1023/A:1013946514556.View ArticleGoogle Scholar
- Weckesser J, Martin C, Jakobi C: Cyanopeptolins, depsipeptides from cyanobacteria. Systematic and Applied Microbiology. 1996, 19: 133-138.View ArticleGoogle Scholar
- Von Elert E, Oberer L, Merkel P, Huhn T, Blom JF: Cyanopeptolin 954, a novel chlorine-containing chymotrypsin-inhibitor of Microcystis aeruginosa NIVA Cya43. Journal of Natural Products. 2005, 68: 1324-1327. 10.1021/np050079r.View ArticlePubMedGoogle Scholar
- Martin C, Oberer L, Ino T, Koenig WA, Busch M, Weckesser J: Cyanopeptolins, new depsipeptides from the cyanobacterium Microcystis sp. PCC 7806. Journal of Antibiotics. 1993, 46: 1550-1556.View ArticlePubMedGoogle Scholar
- Agrawal MK, Zitt A, Bagchi D, Weckesser J, Bagchi SN, Von Elert E: Characterization of proteases in guts of Daphnia magna and their inhibition by Microcystis aeruginosa PCC 7806. Environmental Toxicology. 2005, 20: 314-322. 10.1002/tox.20123.View ArticlePubMedGoogle Scholar
- Colbourne JK: wFleaBase: the Daphnia genome database. BMC Bioinformatics. 2005, 6: 10.1186/1471-2105-6-45.Google Scholar
- Blom JF, Baumann H, Codd GA, Jüttner F: Sensitivity and adaptation of aquatic orgenisms to oscillapeptin J and [D-Asp3,(E)-Dhb7]microcystin-RR. Archiv fuer Hydrobiologie. 2006, 167: 547-559. 10.1127/0003-9136/2006/0167-0547.View ArticleGoogle Scholar
- Perkins DN, Pappin DJC, Creasy DM, Cottrell JS: Probability-based protein identification by searching sequence data bases using mass spectrometric data. Electrophoresis. 1999, 20: 3551-3567. 10.1002/(SICI)1522-2683(19991201)20:18<3551::AID-ELPS3551>3.0.CO;2-2.View ArticlePubMedGoogle Scholar
- DeMott WR, Gulati RD, Van Donk E: Daphnia food limitation in three hypereutrophic Dutch lakes: Evidence for exclusion of large-bodied species by interfering filaments of cyanobacteria. Limnology and Oceanography. 2001, 46: 2054-2060. 10.4319/lo.2001.46.8.2054.View ArticleGoogle Scholar
- Gliwicz ZM, Lampert W: Food thresholds in Daphnia species in the absence and presence of blue-green filaments. Ecology. 1990, 71: 691-702. 10.2307/1940323.View ArticleGoogle Scholar
- Martin-Creuzburg D, Von Elert E, Hoffmann KH: Nutritional constraints at the cyanobacteria-Daphnia magna interface: The role of sterols. Limnology and Oceanography. 2008, 53: 456-468. 10.4319/lo.2008.53.2.0456.View ArticleGoogle Scholar
- Von Elert E, Martin-Creuzburg D, Le Coz JR: Absence of sterols constrains carbon transfer between cyanobacteria and a freshwater herbivore (Daphnia galeata). Proceedings of the Royal Society of London - Series B: Biological Sciences. 2003, 270: 1209-1214. 10.1098/rspb.2003.2357.PubMed CentralView ArticlePubMedGoogle Scholar
- DeMott WR: Foraging strategies and growth inhibition in five daphnids feeding on mixtures of a toxic cyanobacterium and a green alga. Freshwat Biol. 1999, 42: 263-274. 10.1046/j.1365-2427.1999.444494.x.View ArticleGoogle Scholar
- Lürling M, Grinten Van der E: Life-history characteristics of Daphnia exposed to dissolved microcystin-LR and to the cyanobacterium Microcystis aeruginosa with and without microcystins. Environmental Toxicology & Chemistry. 2003, 22: 1281-1287.View ArticleGoogle Scholar
- Dittmann E, Neilan BA, Erhard M, Von Doehren H, Börner T: Insertional mutagenesis of a peptide synthetase gene that is responsible for hepatotoxin production in the cyanobacterium Microcystis aeruginosa PCC 7806. Molecular Microbiology. 1997, 26: 779-787. 10.1046/j.1365-2958.1997.6131982.x.View ArticlePubMedGoogle Scholar
- Martin-Creuzburg D, Von Elert E: Ecological significance of sterols in aquatic foodwebs. Lipids in Aquatic Ecosystems. Edited by: Arts MT, Brett M, Kainz M. 2009, Dordrecht, Heidelberg, London, New York: Springer, 43-64. full_text.View ArticleGoogle Scholar
- Von Elert E, Agrawal MK, Gebauer C, Jaensch H, Bauer U, Zitt A: Protease activity in guts of Daphnia magna: Evidence for trypsin and chymotrypsin enzymes. Comparative Biochemistry & Physiology Part B. 2004, 137: 287-296.View ArticleGoogle Scholar
- Saborowski R, Sahling G, del Toro MAN, Walter I, Garcia-Carreno FL: Stability and effects of organic solvents on endopeptidases from the gastric fluid of the marine crab Cancer pagurus. Journal of Molecular Catalysis B-Enzymatic. 2004, 30: 109-118. 10.1016/j.molcatb.2004.04.002.View ArticleGoogle Scholar
- Teschke M, Saborowski R: Cysteine proteinases substitute for serine proteinases in the midgut glands of Crangon crangon and Crangon allmani (Decapoda: Caridea). Journal of Experimental Marine Biology and Ecology. 2005, 316: 213-229. 10.1016/j.jembe.2004.11.007.View ArticleGoogle Scholar
- Watanabe H, Tatarazako N, Oda S, Nishide H, Uchiyama I, Morita M, et al: Analysis of expressed sequence tags of the water flea Daphnia magna. Genome. 2005, 48: 606-609. 10.1139/g05-038.View ArticlePubMedGoogle Scholar
- Schwerin S, Zeis B, Lamkemeyer T, Paul RJ, Koch M, Madlung J, et al: Acclimatory responses of the Daphnia pulex proteome to environmental changes. II. Chronic exposure to different temperatures (10 and 20°C) mainly affects protein metabolism. BMC Physiology. 2009, 9:Google Scholar
- Demuth JP, Hahn MW: The life and death of gene families. BioEssays. 2009, 31: 29-39. 10.1002/bies.080085.View ArticlePubMedGoogle Scholar
- Vontas JG, Hejazi MJ, Hawkes NJ, Cosmidis N, Loukas M, Hemingway J: Resistance-associated point mutations of organophosphate insensitive acetylcholinesterase, in the olive fruit fly Bactrocera oleae. Insect Molecular Biology. 2002, 11: 329-336. 10.1046/j.1365-2583.2002.00343.x.View ArticlePubMedGoogle Scholar
- Vontas JG, Small GJ, Hemingway J: Comparison of esterase gene amplification, gene expression and esterase activity in insecticide susceptible and resistant strains of the brown planthopper, Nilaparvata lugens (Stal). Insect Molecular Biology. 2000, 9: 655-660. 10.1046/j.1365-2583.2000.00228.x.View ArticlePubMedGoogle Scholar
- Field LM, Devonshire AL, Forde BG: Molecular evidence that insecticide resistance in Peach Potato Aphids (Myzus-Persicae Sulz) results from amplification of an esterase gene. Biochemical Journal. 1988, 251: 309-312.PubMed CentralView ArticlePubMedGoogle Scholar
- Mouches C, Pasteur N, Berge JB, Hyrien O, Raymond M, Desaintvincent BR, et al: Amplification of an esterase gene is responsible for insecticide resistance in a California Culex mosquito. Science. 1986, 233: 778-780. 10.1126/science.3755546.View ArticlePubMedGoogle Scholar
- DeMott WR, Dhawale S: Inhibition of in-vitro protein phosphatase-activity in three zooplankton species by microcystin-lr, a toxin from cyanobacteria. Archiv für Hydrobiologie. 1995, 134: 417-424.Google Scholar
- Jungmann D: Toxic compounds isolated from Microcystis PCC 7806 that are more active against Daphnia than two microcystins. Limnology and Oceanography. 1992, 37: 1777-1783. 10.4319/lo.19188.8.131.527.View ArticleGoogle Scholar
- Tillmanns AR, Wilson AE, Pick FR, Sarnelle O: Meta-analysis of cyanobacterial effects on zooplankton population growth rate: Species-specific responses. Fundamental and Applied Limnology. 2008, 171: 285-295. 10.1127/1863-9135/2008/0171-0285.View ArticleGoogle Scholar
- Lürling M: Daphnia growth on microcystin-producing and microcystin-free Microcystis aeruginosa in different mixtures with the green alga Scenedesmus obliquus. Limnology and Oceanography. 2003, 48: 2214-2220.View ArticleGoogle Scholar
- Rohrlack T, Dittmann E, Henning M, Boerner T, Kohl J: Role of microcystins in poisoning and food ingestion inhibition of Daphnia galeata caused by the cyanobacterium Microcystis aeruginosa. Applied & Environmental Microbiology. 1999, 65: 737-739.Google Scholar
- Pijanowska J, Weider LJ, Lampert W: Predator-mediated genotypic shifts in a prey population: experimental evidence. Oecologia. 1993, 96: 40-42. 10.1007/BF00318028.View ArticleGoogle Scholar
- Jüttner F, Leonhardt J, Möhren S: Environmental factors affecting the formation of mesityloxid, dimethylallylic alcohol and other volatile compounds excreted by Anabaena cylindrica. J o General Microbiology. 1983, 129: 407-412.Google Scholar
- Wacker A, Von Elert E: Polyunsaturated fatty acids: evidence for non-substitutable biochemical resources in Daphnia galeata. Ecology. 2001, 82: 2507-2520.View ArticleGoogle Scholar
- Laemmli UK: Cleavage of structural proteins during the assembly of the head of bacteriophage T4. Nature. 1970, 227: 680-685. 10.1038/227680a0.View ArticlePubMedGoogle Scholar
- Hanisch FG, Teitz S, Schwientek T, Muller S: Chemical de-O-glycosylation of glycoproteins for application in LC-based proteomics. Proteomics. 2009, 9: 710-719. 10.1002/pmic.200800492.View ArticlePubMedGoogle Scholar
- Heckmann LH, Connon R, Hutchinson TH, Maund SJ, Sibly RM, Callaghan A: Expression of target and reference genes in Daphnia magna exposed to ibuprofen. BMC Genomics. 2006, 7: 175-182. 10.1186/1471-2164-7-175.PubMed CentralView ArticlePubMedGoogle Scholar
- Vandesompele J, De Preter K, Pattyn F, Poppe B, Van Roy N, De Paepe A, et al: Accurate normalization of real-time quantitative RT-PCR data by geometric averaging of multiple internal control genes. Genome Biology. 2002, 3: research0034.I-0034.II. 10.1186/gb-2002-3-7-research0034.View ArticleGoogle Scholar
- Schwarzenberger A, Courts C, Von Elert E: Target gene approaches: Gene expression in Daphnia magna exposed to predator-borne kairomones or to microcystin-producing and microcystin-free Microcystis aeruginosa. BMC Genomics. 2009, 10: 527-10.1186/1471-2164-10-527.PubMed CentralView ArticlePubMedGoogle Scholar
- Livak KJ, Schmittgen TD: Analysis of relative gene expression data using real-time quantitative PCR and the 2(-Delta Delta C(T)) Method. Methods. 2001, 25: 408-10.1006/meth.2001.1262.View ArticleGoogle Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.