More than 10 years after registration of the first Bt maize cultivar in Europe, there still exists a remarkable lack of data on effects on Lepidoptera which would be necessary for a complete and comprehensive environmental risk assessment. So far only very few European butterfly species have been tested in this aspect. In our study the effect of transgenic Bacillus thuringiensis (Bt) maize pollen (event Bt-176) on the development and survival of neonate larvae of the Peacock butterfly, Inachis io (L.) was for the first time shown. The results of our study suggest that the Peacock butterfly may serve as a model organism for assessing potential side effects of new developed transgenic Bt crops on non-target butterflies in a GMO environmental risk assessment. The study was done under laboratory conditions by exposing larvae of the Peacock butterfly to various pollen doses of transgenic maize event Bt-176 (cv. PACTOL CB) or the conventional isogenic maize (cv. PACTOL) using a no-choice test. Larvae feeding for 48 h on nettle plants (Urtica dioica) that were contaminated with higher pollen concentrations from Bt-176 maize (205 and 388 applied pollen.cm-2) suffered a significantly higher mortality rate (68 and 85% respectively) compared to larvae feeding on leaves with no pollen (11%), or feeding on leaves with pollen from conventional maize (6 to 25%). At lower Bt maize pollen doses (23–104 applied pollen.cm-2), mortality ranged from 11–25% and there were no apparent differences among treatments. The corresponding LC50-and LC90-values for neonate larvae of the Peacock butterfly were 187 and 448 applied pollen grains.cm-2 of Bt-176, respectively. Weight of larvae surviving consumption of Bt-176 maize pollen declined between 10 and 81% with increased pollen doses (r =  −0.95). The highest weight reduction (81%) corresponded to the highest pollen concentration (388 pollen grains applied.cm-2). Ingestion of pollen from the conventional maize hybrid did not have negative effects on larval weight gain or survival rate.

Accumulation of information about natural hybridization between GM soybean (Glycine max) and wild soybean (Glycine soja) is required for risk assessment evaluation and to establish biosafety regulations in Japan. This is particularly important in areas where wild relatives of cultivated soybean are grown (i.e. East Asia including Japan). To collect information on temporal and spatial factors affecting variation in hybridization between wild and GM soybean, a two year hybridization experiment was established that included one wild soybean and five GM soybean cultivars with different maturity dates. Hybridization frequencies ranged from 0 to 0.097%. The maximum hybridization frequency (0.097%) was obtained from wild soybean crossed with GM soybean cv. AG6702RR, which were adjacently cultivated with wild soybean, with 25 hybrids out of 25 741 seedlings tested. Cultivar AG6702RR had the most synchronous flowering period with wild soybean. Ten hybrids out of 25 741 were produced by crossing with cv. AG5905RR, which had the second most synchronous flowering period with wild soybean. Most hybrids were found where GM and wild soybeans were adjacently cultivated, whereas only one hybrid was detected from wild soybean plants at 2 m, 4 m and 6 m from a pollen source (GM soybean). Differences in flowering phenology, isolation distance and presence of buffer plants accounted for half of the variation in hybridization frequency in this study. Temporal and spatial isolation will be effective strategies to minimize hybridization between GM and wild soybean.

This study assessed the impact of Pinus radiata (D. Don) genetically modified (GM) by biolistic insertion of the LEAFY and nptII genes on rhizosphere microbial communities of field grown trees. Rhizosphere soil was sampled quarterly for two consecutive years. A culture-independent approach was used to characterise the microbial communities based on PCR and denaturing gradient gel electrophoresis (DGGE) of 16S/18S rDNA gene fragments, and internal transcribed spacer (ITS) fragments amplified from total rhizosphere DNA. Trees from two independent transformation events were sampled, together with non-modified control trees of the same parental genotype. DGGE profiles of rhizosphere general Bacteria did not differ between GM and control trees with one exception (summer 2006 sample). For Alphaproteo- and Actinobacteria, significant differences between treatments were detected in one out of eight samplings. Small seasonal shifts could be detected in all bacterial communities. General fungal and ectomycorrhizal communities did not differ significantly between GM and control trees with the exception of summer 2006, when ectomycorrhizal communities associated with GM trees from one transformation event differed from those associated with control trees. Small seasonal shifts of general fungal and ectomycorrhizal communities were seen over the two-year sampling period. More detailed analysis of microbial communities at one sampling date (using amplified rDNA restriction analysis (ARDRA) and 16S/18S rDNA sequencing) revealed significant differences in four ARDRA groups between one GM treatment and the control (bacteria), and significant differences in one ARDRA group between the two GM treatments (fungi). When data from all sampling dates are considered together, the low incidence of statistical differences in the microbial communities associated with the genetically modified and control trees suggests that there was no significant impact of this genetic modification on rhizosphere microbial communities.

Transgenic fish in development for aquaculture could escape from farms and interbreed with wild relatives in the nearby environment. Predicting whether escapes would result in transgene introgression is a major challenge in assessing environmental risks of transgenic fish. Previous studies have simulated gene flow from transgenic fish using mathematical modeling of fitness traits to predict the relative selective value of transgenic genotypes. Here, we present the first study of gene flow over the full life cycle in openly-breeding populations of transgenic animals, along with measurement of fitness traits. We conducted two invasion experiments in which we released two lines of growth-enhanced transgenic fish (T67 and T400), Japanese medaka (Oryzias latipes), into populations of wild-type (W) medaka in structured mesocosms. After several generations, the frequency of transgenic fish varied across replicates in the first invasion experiment (6 months), but the frequency of transgenic fish decreased in the second experiment (19 months). We also measured selected fitness traits in transgenic and wild-type medaka because these traits could be used to predict the relative selective value of a genotype. We found that: T400 males were more fertile than W males; offspring of W females lived longer than those with transgenic mothers; and W and T67 females reached sexual maturity sooner than T400 females. In contrast with other research that reported larger transgenic males had a mating advantage, we found that W males obtained more matings with females than T males; genetic background effects may account for our differing results as we compared W and T fish derived from different strains. The decreasing frequency of transgenic fish in the second invasion experiment suggests that transgenic fish had a selective disadvantage in the experimental environment. Our finding of transgenic advantage of some fitness traits and wild-type advantage in others is consistent with our invasion experiment results.

In recent times, it has become imperative for countries to define and implement policy in biosafety due to the widespread adoption of genetically modified crops. As such, countries wishing to utilise transgenic technologies in the development of advanced agricultural products must have regulations in place coupled with trained personnel in national competent authorities able to contribute effectively to the decision-making process. Capacity building initiatives play an important role in supporting such individuals, institutions and governmental authorities by providing training and/or physical structures/equipment and technical assistance. There are many types of capacity building activities; however not all have the same relevance in different regions of the world. For capacity building to be effective, a strategic approach incorporating a variety of forms and disciplines is desired. This commentary discusses the importance of factors such as: the targeting of support to relevant beneficiary(ies); the identification of specific needs and the incorporation of socio-economic conditions when elaborating effective strategies designed to help building capacity. Moreover, the importance of interaction and collaboration amongst the various capacity builders is also discussed such that unnecessary duplication of efforts and best use of available human and economic resources results.