8 research outputs found

    Decomposition dynamics and structural plant components of genetically modified Bt maize leaves do not differ from leaves of conventional hybrids

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    The cultivation of genetically modified Bt maize has raised environmental concerns, as large amounts of plant residues remain in the field and may negatively impact the soil ecosystem. In a field experiment, decomposition of leaf residues from three genetically modified (two expressing the Cry1Ab, one the Cry3Bb1 protein) and six non-transgenic hybrids (the three corresponding non-transformed near-isolines and three conventional hybrids) was investigated using litterbags. To elucidate the mechanisms that cause differences in plant decomposition, structural plant components (i.e., C:N ratio, lignin, cellulose, hemicellulose) were examined. Furthermore, Cry1Ab and Cry3Bb1 protein concentrations in maize leaf residues were measured from harvest to the next growing season. While leaf residue decomposition in transgenic and non-transgenic plants was similar, differences among conventional cultivars were evident. Similarly, plant components among conventional hybrids differed more than between transgenic and non-transgenic hybrids. Moreover, differences in senescent plant material collected directly from plants were larger than after exposure to soil for 5months. While the concentration of Cry3Bb1 was higher in senescent maize leaves than that of Cry1Ab, degradation was faster, indicating that Cry3Bb1 has a shorter persistence in plant residues. As decomposition patterns of Bt-transgenic maize were shown to be well within the range of common conventional hybrids, there is no indication of ecologically relevant, adverse effects on the activity of the decomposer communit

    A critical examination of the protection level for primary producers in the first tier of the aquatic risk assessment for plant protection products

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    Abstract Background The aim of environmental risk assessment (ERA) for pesticides is to protect ecosystems by ensuring that specific protection goals (SPGs) are met. The ERA follows a prospective tiered approach, starting with the most conservative and simple step in risk assessment (RA) (so-called tier 1) using the lowest available appropriate endpoint derived from ecotoxicological tests. In 2015, for the tier 1 RA of aquatic primary producers, the recommendation was changed from using the lowest of the 50% inhibition (EC50) values based on biomass (area under the curve—EbC50), increase in biomass (yield- EyC50) or growth rate (ErC50) to only using the growth rate inhibition endpoint (ErC50) because it is independent of the test design and thus more robust. This study examines the implications of this such on the level of conservatism provided by the tier 1 RA and evaluates whether it ensures a suitable minimum protection level. Results Our analysis shows that replacing the lowest endpoint with the growth rate inhibition endpoint while maintaining the assessment factor (AF) of 10 significantly reduces the conservatism in the tier 1 RA. Comparing protection levels achieved with different endpoints reveals that the current assessment is less protective. To maintain the previous level of protection, and since the protection goals have not changed, we recommend to multiply the default AF of 10 by an extra factor of minimum 2.4 in the tier 1 RA based on ErC50. Independently of the endpoint selected in tier 1 RA, several issues in the general RA of pesticides contribute to uncertainties when assessing the protection levels, e.g., lack of appropriate comparison of the higher tier experimental studies (i.e., best achievable approximation of field situation, so-called surrogate reference tier) with field conditions or the regulatory framework's failure to consider realistic conditions in agricultural landscapes with multiple stressors and pesticide mixtures. Conclusions We advise to consider adjusting the risk assessment in order to reach at least the previous protection level for aquatic primary producers. Indeed continuing using an endpoint with a higher value and without adjustment of the assessment factor is likely to jeopardize the need of halting biodiversity loss in surface waters

    The lewis-Y carbohydrate antigen is expressed by many human tumors and can serve as a target for genetically redirected T cells despite the presence of soluble antigen in serum

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    In this study we aimed to determine the suitability of the Lewis-Y carbohydrate antigen as a target for immunotherapy using genetically redirected T cells. Using the 3S193 monoclonal antibody and immunohistochemistry, Lewis-Y was found to be expressed on a range of tumors including 42% squamous cell lung carcinoma, 80% lung adenocarcinoma, 25% ovarian carcinoma, and 25% colorectal adenocarcinoma. Expression levels varied from low to intense on between 1% and 90% of tumor cells. Lewis- was also found in soluble form in sera from both normal donors and cancer patients using a newly developed enzyme-linked immunosorbent assay. Serum levels in patients was often less than 1á mg/mL, similar to normal donors, but approximately 30% of patients had soluble Lewis-Y levels exceeding 1áng/mL and up to 9á mg/mL. Lewis-Y-specific human T cells were generated by genetic modification with a chimeric receptor encoding a single-chain humanized antibody linked to the T-cell signaling molecules, T-cell receptor-zeta, and CD28. T cells responded against the Lewis-Y antigen by cytokine secretion and cytolysis in response to tumor cells. Importantly, the T-cell response was not inhibited by patient serum containing soluble Lewis-Y. This study demonstrates that Lewis-Y is expressed on a large number of tumors and Lewis-Y-specific T cells can retain antitumor function in the presence of patient serum, indicating that this antigen is a suitable target for this form of therapy
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