Fine roots of forest trees form together with certain soil fungi symbiotic structures (ectomycorrhizas), where fungal hyphae are in intimate contact with plant cells. Due to root cell degeneration, plant DNA is released and could be taken up by the fungus. The possibility that horizontal gene transfer might result in a risk for the environment should be evaluated before a massive release of genetically engineered trees into nature occurs, even though only a few convincing examples of horizontal gene transfer are known. Transgenic poplars containing a construct of the Streptomyces hygroscopicus bar gene under the control of the Cochliobolus heterostrophus GPD (glyceraldehyde-3-phosphate dehydrogenase) promoter were generated by Agrobacterium-mediated transformation. The functionality of this construct in the ectomycorrhizal model fungus Amanita muscaria was previously verified by protoplast-based fungal transformation. 35 000 ectomycorrhizas, formed between transgenic poplars and non-transgenic A. muscaria hyphae, were isolated and transferred to selective agar plates. Putative herbicide-resistant fungal colonies were obtained after the first round of selection. However, none of these colonies survived a transfer onto fresh selection medium, nor did they contain the bar gene, indicating that no horizontal gene transfer from poplar to A. muscaria occurred during symbiosis under axenic conditions. However, since ectomycorrhizas are associated under natural conditions with viruses, bacteria and other fungi, these additional associations should be evaluated in future.

The intrinsic toxicity of lepidopteran-active Bt proteins necessitates assessment of non-target risks associated with environmental release of transgenic crops expressing these proteins. Principles of ecological risk assessment provide a means for assessing non-target risks when information regarding exposure to the toxin and species-specific effects are lacking. This is shown for the case of Bt Cry1F maize release in Japan, where off-field pollen dissemination and effect on butterfly species is of concern. The specific ecological entity of concern for the assessment of the non-target impact of Cry1F maize pollen was Yamato-shijimi (pale grass blue butterfly), Pseudozizeeria maha (Kollar), a commonly occurring, susceptible species. Yamato-shijimi is widely adapted in Japan where it occurs in both rural and metropolitan settings, corresponding to the distribution and habitat of katabami (Oxalis corniculata (L.)), the larval host plant. The northern extent of Yamato-shijimi habitat lies to the south of major maize production regions in Japan, but exposure may occur elsewhere where maize and Yamato-shijimi co-occur. Screening level assessment of potential adverse effects to Yamato-shijimi in the field environment considered the probability for spatial-temporal co-occurrence of the life stages of concern (1st and 2nd instars) and the stressor (Cry1F protein expressed in maize pollen) at environmentally relevant concentrations. In the event of exposure to maize pollen, early instars of Yamato-shijimi feed exclusively on the underside of katabami leaves, which further limits the portion of the butterfly population that would be exposed. Projected levels of exposure to Cry1F pollen are below the toxicity level of concern and, thus, indicate negligible risk. Most sensitive species characterization (intergenera sensitivity) similarly shows negligible risk to other Japanese butterfly species of concern when distributed beyond the maize field or field margin.