Moving to the south, we encounter the palaeochannels CL1 and CL2,

Moving to the south, we encounter the palaeochannels CL1 and CL2, described in the last section. Between the Vittorio Emanuele III Channel and the Contorta S. Angelo Channel there are a few palaeochannels meandering mainly in the west–east direction. These palaeochannels probably belong to another Holocene path of the Brenta river close to Fusina (depicted in Fig. 4. 68, p. 321, in Bondesan and Meneghel, 2004). In

the lower right hand side of the Vemurafenib mw map, we can see the pattern of a large tidal meander that existed already in 2300 BC that is still present today under the name Fasiol Channel. Comparison with the 1691 map shows that the palaeochannels close to the S. Secondo Channel disappeared, and so did the palaeochannel CL1 (Fig. 4b). The palaeochannel CL2 is no longer present in our reconstruction, but it may still exist under the Tronchetto Island, as we observed in the last section. The acoustic areal reconstruction of CL3 overlaps well with the path of the “coa de Botenigo” from the 1691 map that was flowing into the Giudecca Channel. This channel is clearly visible also

in Fig. 4c and Target Selective Inhibitor Library in vivo d. On the other hand, the palaeochannels close to the Fusina Channel of Fig. 4a have now disappeared. This may be related to the fact that in 1438 the Fusina mouth of the Brenta river was closed (p. 320 of Bondesan and Meneghel, 2004). To the lower right, the large meander of the Fasiol Channel is still present and one can see its ancient position and continuation. In 1811, the most relevant changes are the disappearance of the “Canal Novo de Botenigo” and of the “Canal de Burchi” (in Fig. 4c), that were immediately to the north and to the south of the Coa de Botenigo in Fig. 4b, respectively. The map in Fig. 4d has more details with small creeks developing perpendicular to the main channel. Moreover, the edification of the S. Marta area has started, so the last part of the “Coa de Botenigo”

was Florfenicol rectified. Finally, the meander close to the Fasiol Channel is now directly connected to the Contorta S. Angelo Channel. In the current configuration of the channels, the morphological complexity is considerably reduced (Fig. 4e). The meanders of the palaochannel CL3 (“Coa de Botenigo”) and their ramification completely disappeared as a consequence of the dredging of the Vittorio Emanuele III Channel. The rectification of the palaochannel CL3 resulted in its rapid filling (Fig. 2d). This filling was a consequence of the higher energetic regime caused by the dredging of the new deep navigation channels in the area. The old Fusina Channel was partially filled and so it was the southern part of the Fasiol Channel meander. The creeks developing perpendicular to the main palaeochannels in 1901 (Fig. 4d) completely disappeared. A more detailed reconstruction of the different 20th century anthropogenic changes in the area can be found in Bondesan et al.

g chemokine receptor (CCR)2 are used as measurements of cell act

g. chemokine receptor (CCR)2 are used as measurements of cell activation. The h-CLAT assay uses THP-1 cells (a human monocytic leukemia cell line) as a surrogate for dermal dendritic cells. The THP-1 cells are treated with eight different concentrations of a test substance for 24 h. After selleck removing the test substance, expression

of CD86 and CD54 is measured by flow cytometry. Relative fluorescence intensity (RFI) compared to vehicle-only treated control cells is used as an indicator of CD86 and CD54 induction. A test substance is considered a skin sensitiser in case the RFI of either CD86 or CD54 reaches defined thresholds (CD86 ⩾ 150% and/or CD54 ⩾ 200%), in at least two of three independent measurements at any concentration. Concentrations exceeding 50% cytotoxicity, measured with propidium iodide selleck compound (PI), are excluded from analysis (Ashikaga et al., 2010). The MUSST assay, which uses the U937 cell line (a human histiocytic leukemia cell line) is designed to evaluate the capacity of a substance to induce dendritic cell activation. To achieve this, CD86 expression is assessed by flow cytometry, following a 45 h incubation with the test substance in at least four different concentrations up to a maximum of 200 μg/mL. Concentrations exceeding 30%

cytotoxicity, measured with PI, are excluded from analysis. A substance inducing an increase in CD86 protein expression of ⩾150% with evidence of a dose response in at least two concordant experiments is considered to be a sensitiser. If the CD86 positive threshold is not reached and no perturbations are observed in at least two concordant experiments, the substance

is considered to be a non-sensitiser. In the other cases, rules based on CD86 expression or cell viabilities are used in order to classify the chemical as sensitising or non-sensitising (Ade et al., 2006). The mMUSST also uses the U937 cell line measuring CD86 by flow cytometry. Five concentrations, chosen based on preliminary PI cytotoxicity assays, are applied for 48 h. The highest tested concentration in the main experiment is two times the concentration causing a PRKACG cytotoxicity of 25% (CV75). A test substance is predicted to have a dendritic cell line activating potential when CD86 induction exceeds the threshold of 1.2 with respect to vehicle treated cells at any tested concentration showing sufficient cell viability (⩾70%) in at least two independent experiments (Bauch et al., 2012). In contrast to the above cell line-based assays, the PBMDC assay uses human peripheral blood monocyte-derived dendritic cells isolated from the fresh buffy coats of five different donors. CD1a negative/CD14 positive monocytes are selected and differentiated by culturing with GM-CSF and IL-4. Cells are then exposed to at least six concentrations of the test substance. The second highest concentration should correspond to a viability of at least 80%.

The biological functions of NSun3 and NSun6 proteins are unknown

The biological functions of NSun3 and NSun6 proteins are unknown. In summary, although the precise molecular and biological functions of RNA m5C methyltransferases are still poorly understood some commonalities are emerging. A conspicuously high number of NSun-proteins are associated with human disease syndromes that include PD-0332991 manufacturer growth retardation and neurological deficits. This specific link to human diseases may be explained by a direct role of 5-methylcytidine in rRNA and tRNA to regulate global protein translation.

Protein synthesis pathways are coupled to cell size, which may explain the small statue described for many organisms lacking RNA methyltransferases. Another commonality is that in the absence of RNA methylases, the affected organs are often brain and testis,

which both have been described to be the most susceptible organs to altered protein translation rates [44 and 45]. m6A is thought to be the most abundant internal modification in mRNA (Figure 1c) [46]. The detection of m6A was long challenging because of the inert chemical reactivity of the methyl group and the fact that this modification does not change base-pairing properties or inhibit reverse transcription. Recently, two independent groups determined the occurrence of m6A system-wide using RNA-immunoprecipitation methods followed by next generation sequencing [47•• and 48••]. m6A was found in more than 7000 mRNAs and over 200 long non-coding RNAs (lncRNAs), and the conserved most pronounced location of this modification was in stop codons, see more 3′UTRs and long internal exons in human, mouse and yeast [47••, 48•• and 49].

The consensus sequence is RRm6ACH (R = A/G and H = A/C/U), yet additionally RNA structure or RNA binding proteins are likely to be involved in determining the methylation sites [49]. The occurrence of m6A-methylation is highly dynamic, and both the fraction of modified RNAs and distribution of the modification within RNAs can vary depending on cell types, tissues and stress conditions [47••, 48•• and 50••]. The addition of a single methyl group to adenosines Cytidine deaminase does not perturb Watson–Crick base pairing, but it weakens RNA secondary structure [51]. Thus, the molecular role of m6A is thought to relate to various aspects of mRNA metabolism, including mRNA expression and degradation, splicing, translational regulation and regulation of microRNA-binding [46]. Notably, with the exception of m6A regulating RNA-protein interactions, there is currently a considerable lack of evidence supporting other proposed functions in vivo. The presence of m6A in mRNA modulates the binding affinity to the RNA binding proteins Hu-antigen R (HUR) and YTHDF1–3, which in turn regulate the stability and cellular distribution of the bound mRNA [ 47••, 52 and 53].

Zambrano et al conducted a phase I trial hydralazine in women wi

Zambrano et al. conducted a phase I trial hydralazine in women with cervical cancer and were able to demonstrate partial reversal of a panel of aberrantly silenced genes at all dose levels tested, with gene re-expression in three-quarters of the informative cases  [8]. Epigenetics are the processes that modulate DNA Rapamycin research buy expression without changing the DNA code. At the DNA level, epigenetic changes modulate the genome through the covalent addition of a methyl group to the 5-position of the cytosine ring within the context of cytosine and guanine (CpG) dinucleotides. Although the majority of the genome is CpG poor,

about three-quarters of the CpG residues in the mammalian genome are methylated. These areas of the genome BMS-354825 concentration are called CpG islands and are often found at the 5′ ends of genes. DNA methylation can promote oncogenesis through an increased mutation rate or by silencing transcription of tumor suppressor genes [10], [11] and [12]. For example, some colorectal carcinomas

with microsatellite instability have a high frequency of promoter region hypermethylation of the mismatch repair gene hMLH1. Colon cell lines containing a hypermethylated hMLH1 gene re-express hMLH1 when treated with 5-aza-2′-deoxycytidine and show restoration of mismatch repair ability, indicating that hypermethylation of the hMLH1 CpG island could be the primary inactivating event [13]. In patients with heterozygous mutations in tumor suppressor genes, the second hit can occur by hypermethylation of the wild-type allele, leading to tumorigenesis. Five-methylcytosine itself may be mutagenic by undergoing spontaneous deamination to form thymine, leading to a C→T transition

[10], [11] and [12]. Hydralazine reverses aberrant gene promoter methylation in vitro at concentrations that are achieved clinically [6]. At the histone level, posttranslational modification of amino acids can alter the histone conformation. Modification of histones ensures that a differentiated cell remains differentiated and does not convert back into a stem cell. Histone recognition by protein next complexes called readers, writers, and erasers of the histone code helps shape the structural determinants of histone functions. Although histone modifications occur throughout the entire sequence, the “histone tails” (unstructured N termini) are the targets of most modifications. These include acetylation, methylation, ubiquitylation, phosphorylation, and sumoylation. Of particular interest to the current study design, acetylation leads to transcriptional competence. HDAC inhibitors represent a novel class of therapeutic agents that increase histone acetylation to maintain the chromatin structure in a more open conformation. This conformational change may lead to restoration of transcriptionally silenced pathways or suppression of aberrantly expressed genes through recruitment of repressor proteins [14].

aureus (gram-positive), and of fungal suspensions of C albicans

aureus (gram-positive), and of fungal suspensions of C. albicans. In their study, polylysine conjugate was highly effective against fungal and bacterial suspensions, click here although

lower concentrations were required for bacterial (0.75 μM) than for fungal inactivation (5 μM). Toluidine blue needed concentration and light doses of 10 μM and 32 J/cm2 to promote S. aureus inactivation, 35 μM and 32 J/cm2 to promote E. coli inactivation, and 50 μM and 40 J/cm2 to promote C. albicans inactivation. Moreover, to cause cell inactivation with Rose Bengal as a PS, it was necessary to use 0.25 μM and 4 J/cm2 for S. aureus, 35 μM and 8 J/cm2 for E. coli, and 200 μM and from 40 to 80 J/cm2 for C. albicans. Thus, C. albicans was shown to be more resistant

to PDT, when compared with bacteria, which may be attributed to differences in cell size. Candida species are approximately 25–50 times larger than bacterial cells. 27, 39 and 51 Furthermore, as an eukaryotic microorganism, the presence of a nuclear membrane could act as an additional barrier to the PS. 39 and 51 This study showed the effectiveness of Cur-mediated PDT on the photoinactivation of the three evaluated Candida species. For the planktonic cultures of Candida spp. the results demonstrated that different PITs presented no statistical differences in photoinactivation of any of the evaluated species. In addition, the association of 20 μM Cur and LED light, after 5, 10 and 20 min of PIT promoted complete inactivation of the C. albicans, C. glabrata and C. dubliniensis cells. These results are in agreement this website with Dahl et al. 36 whose study demonstrated that a long PIT is not required for Cur phototoxicity. 3-mercaptopyruvate sulfurtransferase In their study, the authors obtained photoinactivation of

both gram-positive and gram-negative bacteria with Cur at 1 and 10 μM, respectively, which is less than the concentration required in the present study for the photoinactivation of Candida species. Furthermore, they observed that the Cur which remained in contact with bacterial cells for different times before irradiation did not significantly modify its phototoxic effects. Also, the removal of Cur before illumination promoted a significant reduction in its phototoxicity, suggesting that Cur in the extracellular bulk phase or loosely bound to the cells is responsible for most of the phototoxic effects. As a lipophillic molecule, Cur first interacts with the cell membrane and membrane bound proteins and is then distributed to different parts of the cell. 45 The nature of these interactions may justify the results obtained for the planktonic cultures of this study, in which an increase in PIT did not promote substantial alterations in photoinactivation of the three evaluated species. Furthermore, C. albicans and C. glabrata suspensions pre-incubated with 20 μM Cur for only 1 min resulted in 89.

Note that the contribution

Note that the contribution

Epigenetics inhibitor of physical processes to FIB dynamics reported here is specific to our study date on October 16th. Because our AD model was not validated with an independent data set, it is not suitable for forecasting or prediction. The model, however, does provide a baseline for estimating the degree of control advection and diffusion are likely to have on FIB at Huntington Beach, as the contribution of these processes to FIB dynamics should increase/decrease as a function of the magnitude of nearshore mixing/transport. Although the AD model captured FIB dynamics during HB06 well overall, the underestimation of FIB decay rates (especially at offshore stations) suggests that it is missing important processes governing FIB decay. Given the reported sensitivity of FIB to variations in solar insolation, organic matter, pH, salinity,

etc., it is likely that some form of extra-enteric FIB mortality may have contributed to the FIB decay observed during HB06 (Anderson et al., 2005, Curtis et al., 1992 and Sinton et al., 2002). The contribution see more of mortality to nearshore FIB variability is addressed in Rippy et al. (2012). This work was partially funded by NSF, ONR, CA SeaGrant (NOAA project #NA10OAR4170060, California Sea Grant Project #25793B; through NOAA’s National Sea Grant College Program, U.S. Dept. of Commerce), the California Coastal Conservancy, the California Department of Boating and Waterways Oceanography Program, and NOAA. The statements, findings, conclusions and recommendations are those of the author(s) and do not necessarily reflect the views of the aforementioned organizations. Tests for FIB analysis were provided and performed by the Orange County Sanitation District. Non-specific serine/threonine protein kinase Special thanks to volunteers and staff from the Integrative Oceanography Division (B. Woodward, B. Boyd, D. Clark, K. Smith, D. Darnell, I. Nagy, J. Leichter, M. Omand, M.

Okihiro, M. Yates, M. McKenna, S. Henderson, D. Michrokowski) for their assistance in data collection. “
“Human pathogenic bacteria are a persistent social, health, and economic problem at beaches around the world. The significant health risks and economic losses associated with beach bacterial pollution have prompted extensive monitoring programs and concerted research efforts aimed at predicting pollution events (Boehm, 2003, Boehm et al., 2005 and Sanders et al., 2005). Multiple mechanisms have been identified that introduce pathogens and associated fecal indicator bacteria (FIB) into the surfzone, including: tidal pumping from estuaries (Grant et al., 2001) and groundwater (Boehm et al., 2004), river flow (Gersberg et al., 2006), and re-suspension from sediments (Yamahara et al., 2007). Similarly, many factors governing rates of FIB mortality in seawater have been identified, including: solar insolation (Sinton et al., 2002 and Sinton et al., 2007), temperature (Solic and Krstulovic, 1992), dissolved organic nutrients (Hartke et al.

This could explain the lack of a clear difference between the two

This could explain the lack of a clear difference between the two variants following unilateral administration; therefore, the variants were dosed bilaterally. The total brain dose of 2.4 µg was the same as in the previous study, but a 1.2 µg (0.6 µL) dose of either N434A or H435A was administered bilaterally. Serum levels were measured at 5 min, 4, and 24 h and rats were allowed to recover from anesthesia immediately after surgery. After 24 h, N434A serum levels reached 25.9±5.2 ng/mL which was significantly greater (P<0.001) than the serum levels of the low FcRn binding variant, H435A, at 6.6±0.6 ng/mL.

The rate of efflux of N434A was calculated to be three times greater RO4929097 cell line than H435A ( Fig. 4A). In a separate group of animals, brain hemispheres were excised 5 min after either N434A or H435A antibody administration. Levels of N434A detected at 5 min were 2.2±0.5 µg/g

of tissue (average mass of the hemispheres was 1.0 g) which was the expected range after administration. After 24 h, levels of N434A in the hemispheres decreased by 48%. Levels of the non-FcRn binding mAb, H435A, did not change over the same time period (Fig. 4B). In order to visualize the presence of human IgG immunohistochemically in the rat brain, three animals were dosed either N434A or H435A bilaterally into the SiFl region of the cortex similar to the previous experiment. After 24 h rats were perfused and brains prepared for immunohistochemistry Stem Cells inhibitor using an anti-human Fc rabbit polyclonal in thin (5 µm) brain sections. Brains were processed for routine histology (hematoxylin and eosin and Luxol fast blue), as well as human IgG and anti-rabbit IgG negative controls. At 24 h after dosing both N434A and H435A mAb variants were visualized in brain tissue (Fig. 5). There was a range of staining intensity visualized in sections at an equivalent coronal plane in the region of the somatosensory cortex in pyramidal and supporting cells that was localized to the cortex or spread into the corpus callosum region. The staining intensity of N434A (Fig. 5A) in the cortex was consistently

less than brains injected with Bupivacaine H435A (Fig. 5B). There was no specific staining detected in PBS microinjected brains (Fig. 5C) or mAb injected brains incubated in serum (Fig. 5D). Semi-quantitative immunostaining scores supported the impression that less of the FcRn binding variant was visualized in brain after 24 h (HA=7.0±1.4 vs. NA=4.4±1.7 of a total of 12.0 maximum staining; P=0.3 by unpaired t-test), which is consistent with greater efflux of the FcRn binding mAb variant. This study used two in vivo drug delivery models in rats, intranasal-to-CNS and direct intra-cranial dosing, to determine the contribution of FcRn to IgG receptor-dependent reverse-transcytosis (efflux) from the brain parenchyma to the circulation.

, 2006a, Yuliani et al , 2006b, Yuliani et al , 2009 and Conti-Si

, 2006a, Yuliani et al., 2006b, Yuliani et al., 2009 and Conti-Silva et al., 2012). Thus, further work to develop better understanding of the effect of extrusion conditions on the structure and retention of flavor in pre-flavored extrudates is required. Therefore, the aim of this study was to investigate the effects of the moisture content of

the raw material, extrusion temperature and screw speed on the structural parameters, volatile compounds retention and sensory acceptability selleck chemicals llc of corn grit extrudates flavored using response surface methodology. The corn grits (7.7 g/100 g protein, 1.1 g/100 g fat, 0.3 g/100 g ash and 90.0 g/100 g total carbohydrates, on a dry basis) were purchased from a local market

and were not subjected to any process before extrusion. For flavoring, a mixture of three volatile liquid compounds was used: isovaleraldehyde, ethyl butyrate and butyric acid (Sigma–Aldrich, Milwaukee, USA). The corn grits composition was determined in accordance with the AOAC (1997) for ash and proteins, and in accordance with the AOCS (2009) specifications for lipid content, and the total carbohydrates content was estimated by difference. The corn grits were ground in a knife mill (model 340, Marconi, Piracicaba, Brazil) and Akt inhibitor ic50 the analyses were performed in triplicate. The response surface methodology was applied using a rotational central composite design for three independent variables (Barros-Neto, Scarminio, & Bruns, 2010), namely: the moisture content of the raw material (dry basis), the extrusion temperature (temperature in third barrel zone) and the screw speed. The dependent variables used were the expansion ratio, density, cutting force and volatile retention for each compound individually and in total for all the compounds. Seventeen tests were performed: eight tests of factorial points (23) (three levels for each factor), six axial points (two for each variable) and three repetitions of the central point (Table 1). The results from the dependent

variables were subjected to multiple regression analysis using the Statistica 7.0 software (StatSoft Inc., Oklahoma, EUA) and coefficients with p values below 0.05 were considered significant. The regression was evaluated by means of analysis P-type ATPase of variance: the regression was considered to be significant when p ≤ 0.05, but no lack of fit at p > 0.05. Linear and quadratic models were tested to explain the influence of independent variables on the response variables, because in Response Surface Methodology, the relationship between these variables is unknown and, therefore, it is necessary to find an adequate approximation to the true relationship between the response and the independent variables ( Montgomery & Runger, 2006). Samples of 400 g of grits were prepared to achieve moisture contents of 10, 12, 15, 18 and 20 g/100 g on a dry basis.

On the other hand, cadmium concentrations in the sediments have b

On the other hand, cadmium concentrations in the sediments have been increasing continuously during the past 100 years as a result of agricultural effluent being discharged into the pond. The reported concentrations of dissolved zinc and cadmium in Nozha Hydrodrome are low when compared with natural levels: this is an indication of the good quality of its water and provides evidence that both metals are trapped

in the solid phase (sediment and particulate matter). Unless major changes in the physicochemical properties (especially pH) of the water take place, cadmium and zinc do not at present pose a serious environmental threat to the Nozha Hydrodrome ecosystem. “
“Long-range atmospheric transport and chemical condensation reactions are responsible for Cyclopamine concentration the widespread distribution of compounds such as poly- cyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs) and hexachlorobenzene (HCB) in the Arctic (e.g. Halsall et al. 2001, Wania & Su 2004). In the European sector of the Arctic, regional sources of pollutants such as metallurgical smelters and military installations operating along the Norwegian and Russian coasts

add to supplies from global emissions sources (Savinov et al. 2003, Carroll et al. 2008a). Marine sediments are the final sink for volatile persistent organic pollutants (POPs) entering the Arctic (Wania & Su 2004). Marine sediments acquire XL184 purchase their contaminant composition through direct particle deposition (Ab Razak et al. 1996) and by transfer from seawater to the bottom surface sediments during downwelling events. For example, in the Norwegian Sea the PCB flux via settling particles was 320 kg yr−1 compared to a direct removal flux to surface sediment deposits of 870 kg

yr−1 in the North Atlantic VAV2 (Lohmann et al. 2006). Sea ice transport also facilitates the transfer of contaminants from industrialized areas of the Siberian coast to other locations in the Arctic (Pfirman et al. 1995, 1997, Pavlov et al. 2004). Estimates prepared by the Arctic Monitoring and Assessment Program (AMAP) report that approximately 45% of PCBs reaching Svalbard are by air transport, 30% by ocean currents and 25% by sea ice transport (AMAP 2004). Sediment accumulation is an important process governing the storage of contaminant-laden sediments on the sea floor. However, contaminant distribution and composition are further affected by post-depositional processes. Sediment mixing may affect the down-core concentration and composition of contaminants, causing chemicals to spread further down the sediment column. In high energy and/or high benthic infauna density environments, resuspension events may result in contaminant reintroduction to the water column (Thibodeaux & Bierman 2003, Carroll & Lerche 2003). Moreover, polychlorinated biphenyls can be degraded by both anaerobic and aerobic bacteria.

Understanding neural S–R systems, and their reciprocal signalling

Understanding neural S–R systems, and their reciprocal signalling with the body, is already opening new fields in medicine. Murakami and colleagues [18] demonstrated that inducing electrical signals in mouse soleus muscles can open the brain–blood barrier to immune system T cells. Furthermore, Torres-Rosas et al. activated the sciatic nerve and dramatically reduced the levels of autoinflamatory cytokines in a sepsis model mouse [ 19•]. Engineering electrochemically-coupled

S–R systems is only just beginning and has great potential for both biomimetics and synthetic neural networks. selleck compound Developmental patterning provides us with a huge range of S–R systems to explore, and direct cell-cell communication is exemplified by the Notch–Delta system found in most multicellular organisms (reviewed in [20]). By acting in both cis and trans, these cell membrane receptors directionally shape pattern formation [21]. The receptors are providing new tools for synthetic biology, such as engineering trigger waves for intercellular information propagation, by transplanting Notch–Delta systems into naive cells [22]. The gap between nearby intercellular and distal multicellular communication is filled by organisms such as the fungus Physarum Polycephalum, which communicates with long protoplastic tubes

to send signals between cells [ 23]. Strikingly, the organisation of tubes optimises resource distribution [ 24 and 25], and the electric potential recorded between joined cells resembles brain waves [ 26]. check details Information transfer in Physarum involves multiple mechanisms: feeding protoplastic arms with fluorescent beads has revealed a peristaltic mechanism for signal transport [ 27]. This capability has been translated into computer algorithms to model the dynamical transport networks [ 28 and 29]. Furthermore, Physarum is a robust organism which can grow on many different substrates,

making it a good candidate for development of synthetic biosensors [ 30]. Overall, such systems may provide an intriguing scaffold for engineering contact-based S–R systems and studying them on a quantitative basis. Contactless S–R systems, with diffusing biochemical signals, have been a major focus of research in synthetic biology and have been reviewed extensively elsewhere [31 and 32]. The first example of a synthetic S–R system involved a pulse generating response in E. coli [ 33•]. Sender cells secreted the quorum-sensing signalling molecule acyl-homoserine lactone (AHL) while receiver cells activated a feed-forward transcription factor network to create a transient pulse of GFP expression. Thus, the simple diffusing signal created dynamic spatiotemporal patterns of gene expression. Later studies demonstrated elegant stripe or band-patterning systems, also using quorum-sensing signalling components [ 34••].