INFORMATION SYSTEMS FOR BIOTECHNOLOGY


February 2004
COVERING AGRICULTURAL AND ENVIRONMENTAL BIOTECHNOLOGY DEVELOPMENTS


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IN THIS ISSUE:


APHIS SOLICITS PUBLIC COMMENT ON PROPOSED GENETICALLY ENGINEERED ORGANISM ENVIRONMENTAL IMPACT STATEMENT

Department of Agriculture
Animal and Plant Health Inspection Service
7 CFR Part 340
Docket No. 03-031-2
Federal Register: January 23, 2004; Volume 69, Number 15

The Animal and Plant Health Inspection Service, USDA, is advising the public that the Animal and Plant Health Inspection Service intends to prepare an environmental impact statement in connection with potential changes to the regulations regarding the importation, interstate movement, and environmental release of certain genetically engineered organisms. This notice identifies potential issues and alternatives that will be studied in the environmental impact statement and requests public comment to further delineate the scope of the issues and alternatives.

Comments must be received on or before March 23, 2004 and may be submitted by postal mail/commercial delivery or by e-mail. If you use postal mail/commercial delivery, please send four copies of your comment (an original and three copies) to:

Docket No. 03-031-2
Regulatory Analysis and Development
PPD, APHIS, Station 3C71
4700 River Road, Unit 118
Riverdale, MD 20737-1238.

Please state that your comment refers to Docket No. 03-031-2. If you use e-mail, address your comment to regulations@aphis.usda.gov. Your comment must be contained in the body of your message; do not send attached files. Please include your name and address in your message and "Docket No. 03-031-2" on the subject line.

APHIS documents published in the Federal Register, and related information, including the names of organizations and individuals who have commented on APHIS dockets, are available on the Internet at http://www.aphis.usda.gov/ppd/rad/webrepor.html.

For further information contact:
Ms. Stephanie Stephens
Environmental Services
PPD, APHIS
4700 River Road Unit 149
Riverdale, MD 20737-1238
(301) 734-4836.

Supplementary information is available at http://a257.g.akamaitech.net/7/257/2422/14mar20010800/edocket.access.gpo.gov/2004/04-1411.htm



ENVIRONMENTAL IMPACT OF GM HERBICIDE-TOLERANT CROPS: THE UK FARM SCALE EVALUATIONS AND PROPOSAL FOR MITIGATION
Alan M. Dewar, Mike J. May and John D. Pidgeon

In October this year, the long-awaited results of the UK Farmscale Evaluations (FSE) of the environmental impact of GM herbicide-tolerant (GMHT) crops were published in the prestigious journal, Philosophical Transactions of the Royal Society. In the ensuing media frenzy, the headlines suggested that beet and spring-sown oilseed rape (canola) were harmful and maize less harmful to the environment compared to their conventional equivalents. To the environmentalist, the label `harmful' is based on the premise that fewer weeds lead to fewer weed seeds, the decline of which would provide less food for birds and other wildlife within the crops, and less seed return to the seedbank. To the farmers, the initial outcome of this could be described as beneficial. In essence the study concluded that the already depleted arable ecosystem (compared to an undisturbed environment) would be further depleted by the use of GMHT technology because these 'break crops' are regarded as having a restorative function for the seed bank in a normal rotation. That is, weed control within conventional varieties of beet and oilseed rape is relatively poor, and this allows the in-field plant species to replenish their seed stocks with consequent benefits for the dependent food chain. Environmental organizations such as English Nature and the Royal Society for the Protection of Birds (RSPB) raised major concerns about the long-term impact of these GMHT crops on wildlife in general, and birds in particular. These concerns were raised against the background of declining populations of both weed seeds, especially of broad-leaved plants (circa 3% per annum) and several species of farmland birds (up to 60% decline in some species since 1970), though other species have shown no decline or even gain.

Effects on Plants
To some extent, the results of the FSE reinforce these concerns. As used in the trials, the herbicides applied to GMHT beet (glyphosate: Roundup Biactive from Monsanto) and spring sown oilseed rape (glufosinate ammonium: Liberty from Bayer CropScience) did give better weed control than the conventional herbicides used on the non-GM crops, and this did lead to lower weed biomass at the end of the season, and fewer weed seeds being caught in seed rain traps. There were also fewer seeds in the seed bank in the following year in the next crop (mostly cereals) in the rotation1,2. In maize the opposite was true. Glufosinate applied to the GM variety gave poorer control of weeds than the conventional regimes, which, in 75% of the test crops, were based on atrazine applied mostly pre-emergence. As atrazine is a persistent, relatively broad spectrum residual herbicide, it is not surprising that it gave better control than one that was applied some time after the crop and weeds had emerged. Indeed, conventional maize crops had the fewest weeds, lowest weed biomass, and produced fewest weed seeds of all the crops tested. The recent announcement within the European Union that atrazine would be banned in the near future has cast doubt on the validity of the maize results; however, as this intention was not known at the time the experiment was devised, the results remain valid for the comparisons that were made. Further work may need to be done to re-examine the comparison when farmers have selected alternative conventional products in a couple years time, after the ban has been implemented.

Effects on Invertebrates
Although the results as far as plant survival is concerned are fairly clear cut, the effects of the two treatments on invertebrates were less clear. For the majority of organisms measured, including carabid and staphylinid beetles, spiders, slugs, snails, true bugs, pests, and predators, there was no difference between the conventional and GMHT crops3, 4. Within some of those groups, a few species that rely heavily on the weeds for food or habitat did respond to the differences in weed and seed abundance. For example there were more seed-eating carabid beetles (Harpalus rufipes) in conventional beet and oilseed rape and GMHT maize in July and/or August when more seeds were available; in contrast there were more detritivorous springtails (Collembola) in all three GMHT crops later in the season because there was more decaying plant material to feed on following the later control of large weeds in these fields. This in turn led to more springtail-feeding carabid beetles (Loricera pilicornis) in the GMHT crops3.

The results that contributed most to the headlines in the national and international press, however, concerned butterflies and bees. Bees were significantly reduced in GMHT beet, but not in the other two crops, largely because of the good control of thistles by glyphosate4 compared to conventional herbicides. However, the number of bees recorded in conventional beet was very low compared to the number seen in rape crops (2.26 compared to 36.9 per km of transect), so the importance of this statistic is questionable. The picture is similar for butterflies. Although there were significantly fewer butterflies both within and around GMHT beet and oilseed rape crops, the numbers in the former were much less4,5. Beet is not a favored crop for these aerial insects unless fields are infested with thistles and other flowering plants. Of the butterfly species affected in oilseed rape, more than half were pest species (Pieris). So again, the significance of these results on non-pest species depends on the availability of other food sources within the farmed landscape and is certainly not as draconian as suggested by the headlines.

Implications for Farm Management
In contrast to the perceived harmful effects, there were some considerable benefits in terms of farm management to be gained from using the GMHT technology. The number of spray applications made to the GMHT crops, and therefore also the amount of energy used to apply them, was significantly reduced in beet (by 55%) and oilseed rape (by 12%), but not in maize6. The number and quantity of active ingredients were substantially reduced in beet and maize, but not in spring rape. The cost of the herbicides applied to the GMHT crops, especially beet, is likely to be considerably less than the current cost of conventional herbicides. Other studies7 have shown a potential benefit of £150/ha (approx. USD$110/acre) to be gained from growing GMHT sugar beet compared to conventional crops. These are important considerations for farmers and would contribute to the decision-making process if the crops were to become available.

Mitigation of Adverse Environmental Effects
Are the FSE results bad enough to persuade the government to ban GMHT crops for general release? More than anything else, what these studies have revealed for the first time on a large scale is that intensive agriculture is having a gradual, but nevertheless inexorable, effect on the diversity of life within the UK farmed landscape. These studies showed that there were greater differences between crops than between the herbicide treatments within any individual crop. Conventional maize for example was the least diverse crop, but both conventional and GMHT oilseed rape were more diverse than the others8. The declines in seedbanks that have been highlighted will continue whether or not GM crops are introduced, although there is evidence that the rate of decline of seeds in the seed bank would be significantly enhanced by the technology1. However, it is not the introduction of GMHT crops that needs to be addressed, but the way in which society wants food to be produced in the future.

There are two approaches to this:
  • 1) A return to low intensity farming—this would require more land to be brought into production to compensate for the reduced yields that would inevitably ensue; or
  • 2) Further intensification on the most productive areas of land—this would allow less productive areas to be returned to wildlife.

Both approaches would require some financial encouragement, and indeed both approaches could be used in tandem. However, some scenarios could be achieved only with GM technology. For example, taking a relatively low-intensity approach, we have devised a method within GMHT sugar beet that allows weeds to survive longer between the rows early in the season to the benefit of some wildlife. Glyphosate is applied as a band spray at first application (by using a cheap modification of the nozzles on an existing spray boom) at the 2–4 leaf stage of beet plants, followed by a later overall application that removes weeds when they become competitive. The optimum timing of the latter spray depends on the density and species composition of weeds in the field. None of the conventional herbicides used in sugar beet would be able to achieve this effect, as they give poor control of weeds with more than 2–4 leaves. This approach encourages insects and other invertebrates to remain in the crop for longer9, reduces the number of pests by camouflaging the beet plants and encouraging predators10, and can offer greater food resources and habitat for ground-nesting birds at a time of year when such resources are scarce in the arable environment. Yields from band-sprayed plots were as good as those from plots receiving conventional herbicides, and the cost of the herbicides was much cheaper, so there is a great financial incentive to growers to pursue this strategy.

Another alternative to increase the number of seeds available for granivorous birds later in the season has been to apply glyphosate once overall early in the season. This allows later emerging, but non-competitive weeds to mature and produce seeds. Of course both methods produce crops that look untidy, at least for part of the season, and this will require growers to re-think their approach to crop production—a pristine crop is not necessarily an environmentally-friendly one. However, the power of GMHT technology allows growers to have confidence that yields will not be adversely affected even if some weeds remain in the crops, and that would make it easier to persuade them to adopt these low intensity approaches.

The second approach, to increase the intensity of cropping, is likely to be more acceptable to growers, but probably not environmentalists. Given that crops do need to be grown to produce food, some compromise is necessary. Is it better to provide a larger area of poor diversity or many small areas of rich diversity? This question needs to be tested on a landscape scale.

The high intensity philosophy is to increase production in the most fertile parts of the fields, namely the field centres. Headlands would not be cropped, but would instead be made into set-aside areas with either natural regeneration, or, if necessary, sown with mixtures of wild flower seeds or species to encourage wildlife. Strips of untreated areas would also be left through the fields themselves to mitigate the losses of seeds caused by either conventional or GMHT cropping. However, the influences of this latter approach on populations of farmland birds cannot be examined until large scale ecological studies are set up.

Conclusion
The adverse effects reported to be due to GMHT beet and oilseed rape crops were due to the more efficient control of weeds by the respective broad-spectrum herbicides applied to those crops. In the same way, the better control of weeds by use of the broad-spectrum residual herbicide atrazine caused the same effects in conventional maize crops. More creative use of herbicides such as glyphosate and glufosinate-ammonium could reverse these effects within crops, but more intensive agricultural production of the most fertile land could allow less productive land to be used for the benefit of wildlife.

References

1. Heard MS et al. (2003a) Weeds in fields with contrasting conventional and genetically modified herbicide-tolerant crops. 1. Effects on abundance and diversity. Phil. Trans. R. Soc. Lond. B. 358: 1819-1832.

2. Heard MS et al. (2003b) Weeds in fields with contrasting conventional and genetically modified herbicide-tolerant crops. 2. The effects on individual species. Phil. Trans. R. Soc. Lond. B. 358: 1833-1846.

3. Brooks DR et al. (2003) Invertebrate responses to the management of genetically modified herbicide-tolerant and conventional spring crops. 1. Soil surface active invertebrates. Phil. Trans. R. Soc. Lond. B. 358: 1847-1862.

4. Haughton AJ et al. (2003) Invertebrate responses to the management of genetically modified herbicide-tolerant and conventional spring crops. 2. Within-field plant epigeal and aerial arthropods. Phil. Trans. R. Soc. Lond. B. 358: 1863-1878.

5. Roy DB et al. (2003) Invertebrates and vegetation of field margins adjacent to crops subject to contrasting herbicide regimes in the Farm Scale Evaluations of genetically modified herbicide-tolerant crops. Phil. Trans. R. Soc. Lond. B. 358: 1879-1898.

6. Champion GT et al. (2003) Crop management and agronomic context of the Farm Scale Evaluations of genetically modified herbicide-tolerant crops. Phil. Trans. R. Soc. Lond. B. 358: 1801-1818.

7. May M. (2003) Economic consequences for UK farmers of growing GM herbicide tolerant sugar beet. Ann. Appl. Biol 142: 41-48.

8. Hawes C et al. (2003) Responses of plants and invertebrate trophic groups to contrasting herbicide regimes in the Farm Scale Evaluations of genetically modified herbicide-tolerant crops. Phil. Trans. R. Soc. Lond. B. 358: 1899-1915.

9. Dewar AM et al. (2003) A novel approach to the use of genetically modified herbicide-tolerant crops for environmental benefit. Proceedings of the Royal Society: Biological Sciences 270 (1513): 335-340.

10. Dewar AM et al. (2000) Delayed control of weeds in glyphosate-tolerant sugar beet and the consequences on aphid infestation and yield. Pest Management Science 56(4): 345-350.

Alan M. Dewar, Mike J. May and John D. Pidgeon
Broom's Barn Research Station, Higham,
Bury St. Edmunds, Suffolk, IP28 56NP, UK
Alan.dewar@bbsrc.ac.uk


BIOENGINEERING OF THE ROOT-SOIL INTERFACE: A HAIRY STORY
Marcel Bucher

Terrestrial plants are sessile organisms that stay at the same habitat during their entire life cycle, and as such, their survival is crucially dependent on rapid adaptation to environmental changes. The above-ground chlorophyll-containing parts provide mainly sucrose, derived from photosynthetic carbon fixation basipetally to sustain root growth and development. The root system serves many tasks—it anchors the plant, absorbs water and minerals from the soil, and delivers certain growth regulators.

Despite its importance for plant productivity, the root is a largely unexplored frontier for genetic engineering1. Root processes influence rhizosphere chemistry, nutrient acquisition, and interactions with beneficial and pathogenic organisms. Roots have the remarkable ability to secrete a vast array of low and high molecular weight molecules into the rhizosphere in response to biotic and abiotic stresses—in a process termed rhizosecretion. There is interest in root bioengineering for numerous reasons. Engineered roots may be better adapted to nutrient poor or saline soils, be better hosts to beneficial organisms, resist soil-borne pathogens more effectively, exhibit increased competitiveness with weeds, remediate toxic waste from contaminated locations, or be a cost-effective alternative for the production of bioactive metabolites and proteins for molecular farming.

Today, engineering of rhizosecretion has become possible using molecular genetic tools. We are interested in investigating whether root hair cells (also called trichoblasts) are suitable target cells for genetic engineering of the root secretory machinery to improve attributes such as plant nutrition.

Why root hair cells?
To exploit the soil optimally for often scarce minerals, most terrestrial plants respond with the formation of a well-developed mycorrhiza, i.e., a symbiosis between the root and soil-borne arbuscular-mycorrhizal fungi, thus increasing the below-ground absorptive surface area. This allows improved plant nutrition due to the ability of the large extraradical mycelium to exploit soil volumes that are otherwise not accessible to the non-colonized plant root. A key process in this symbiosis is the transfer of phosphorus as inorganic phosphate (Pi) from the fungus to the host plant in exchange for carbohydrates derived from the plant. Phosphate transfer at the fungus-plant interface is mediated by mycorrhiza-specific Pi transporter proteins2. Another strategy to combat nutrient scarcity is the formation of an increased root-shoot ratio and an enlargement of the absorptive surface area relative to the root volume3. The increase in absorptive root surface area can be attributed in part to the enhanced production of root hairs, their length being especially important for Pi uptake4. The formation of cluster roots (bottlebrush-like clusters of rootlets densely covered with root hairs) in certain plant species such as white lupin is another type of response to Pi deficiency. Cluster roots have been functionally linked with efficient mechanisms for the chemical mobilization of sparingly available Pi sources in the rhizosphere, involving the excretion of large amounts of organic chelators and enzymes (e.g., acid phosphatase)3.

Root hairs are the tubular extensions of trichoblast cells at the root epidermis and make up between 70% to 90% of the total root surface area. They play a dominant role in a number of root functions. For example, membrane proteins responsible for the uptake of certain nutrients have been localized to the root epidermal layer, including root hair cells and are involved in the transport of nutrients such as Pi, potassium, nitrate, and iron (Fe). Increases in both root hair length and density in response to Fe and Pi deficiencies have been reported (Figure 1A), and the study of root hairless mutants revealed an essential role of root hairs in Pi uptake from the soil solution. Moreover, root hairs are instrumental in the anchorage of the plants in the soil, in water uptake, and in the establishment of the Rhizobium symbiosis in legumes.

Cloning of a root hair-specific gene
Having a regulatory genetic unit to direct expression of a foreign gene to root hair cells is a prerequisite to engineer specifically the root-soil interface. During environmental stress conditions, expression of a gene and its encoded protein at the site where it is needed would be an economic process for the plant, which could be of advantage over constitutive gene expression in all tissues. Moreover, expression of the transgene in root hairs avoids accumulation of the encoded protein in, for example, the edible parts of a crop plant.

The differential hybridization technique is a classical method used to identify mRNAs in comparative studies. A tomato cDNA library from root hair cells has been synthesized. Subsequently, a differential screening resulted in the cloning of several cDNAs, the corresponding transcripts of which were highly abundant in root hairs and were found to encode extensin-like proteins from cell walls4,5. One cDNA corresponding to LeExt1 was selected for detailed expression analysis, and genomic fragments from the promoter region were cloned. To visualize promoter activity in planta, the promoter fragments were fused to the E. coli ß-glucuronidase (GUS) reporter gene. The chimeric genes were then introduced into plants by Agrobacterium-mediated T-DNA transfer, and promoter activity was eventually assessed by histological analysis of GUS activity in the transgenic plants. In situ hybridization of LeExt1 mRNA and promoter/GUS expression studies provided evidence for a direct correlation between LeExt1 expression and root hair growth (Figure 1B6). Root hair-specific activity of LeExt1/GUS was comparable in roots of transgenic plants from diverse species such as tomato, potato, tobacco, strong-spined Medick (Medicago truncatula) and cassava.

Secretion of a consensus phytase from root hair cells
Secretion is a basic function of all plant cells and organs and is especially developed in plant roots. Besides secretion of low molecular weight molecules, plant roots have the capacity for protein secretion. Proteins are secreted when targeted to the lumen of the endoplasmic reticulum by signal peptide-mediated translocation, followed by migration through the exocytotic pathway. This allows rhizosecretion to be modulated by transferring chimeric genes encoding recombinant secretory proteins into plants.

In soils rich in organic matter, 20-50% of the organic Pi may be bound in phytate (myo-inositol hexakisphosphate). Phytase activity, which hydrolyzes Pi esters in phytate, in root exudates of potato, a plant with a relatively low Pi acquisition efficiency, is generally missing7. We hypothesized that the development of crop plants with an increased capacity to secrete phytase may enhance acquisition of orthophosphate originating from organic Pi, and may lead to improvements in fertilizer management in agriculture. We therefore aimed at transferring this activity to potato via Agrobacterium-mediated gene transfer. As a candidate gene, we chose a synthetic phytase gene that encoded a consensus phytase exhibiting an increased thermostability and improved stability towards proteolytic degradation. This gene was originally designed to produce a phytase protein that can be added to feed pellets for an increased Pi availability in feed for animal production8. The consensus phytase gene was under the control of the root hair-specific LeExt1 gene promoter, and therefore the encoded consensus phytase was expected to accumulate exclusively in root hairs and was efficiently secreted from transgenic potato roots due to a secretory signal peptide N-terminally fused to the consensus phytase protein. When phytate, the natural substrate for phytase activity, was present in the nutrient solution, a typical pattern of phytate degradation with a transient accumulation of lower molecular weight inositol phosphates was observed (Figure 1C and D). Moreover, transgenic potato plants accumulated 40% more Pi in their leaves and tubers than wild type when phytate was added to the soil substrate in cultures from the greenhouse.

It remains to be analyzed whether secretion of a phytate-degrading activity in these designer plants will eventually lead to an improved phosphate acquisition efficiency and therefore a greater yield especially in organic soils. Phytate is poorly digested by farm animals with simple stomachs as opposed to ruminants. The undigested phytate is excreted with the feces into the environment, i.e., in agricultural land where organic fertility sources such as animal manure and compost have been used, and phytate is degraded due to soil microbial phytase activity leading to an increased soil Pi content. Consequently, Pi loss from the topsoil is a significant water pollution problem mainly in areas where animal production is concentrated. Phytase-secreting plants thus could be used to decontaminate these soils from phytate and eventually reduce the phosphate concentration in the surface runoff water while simultaneously feeding the plant with phosphate. To evaluate the effectiveness of this approach, field tests in suitable agroecosystems would be necessary.

Summary and perspectives
Overall, engineering the root-soil interface was made possible via cell-specific expression in root hair cells of a recombinant gene encoding a secretory phytase, which resulted in an improved Pi nutrition. In future work, engineering rhizosecretion could be used for the development of plants which are more resistant to adverse soil conditions or which help to clean-up contaminated soils. Moreover, it could be possible to develop plants secreting bioactive proteins via their root hairs that are relevant for medical purposes.

Acknowledgements
I would like to thank Prof. Nikolaus Amrhein, ETH Zurich, for his continuous support. I am grateful to Dr. Philip Zimmermann, ETH Zurich, for photographs and Dr. Theresa Fitzpatrick for critical reading of the manuscript
.

References

1. Bucher M. (2001) in Plant Roots: The Hidden Half, eds. Waisel Y, Eshel A & Kafkafi U. (Marcel Dekker, New York), Vol. 3, pp. 279-294.

2. Rausch C et al. (2001) Nature 414: 462-70.

3. Marschner H. (1995) Mineral nutrition of higher plants. Academic Press, London.

4. Bates TR and Lynch JP. (2000) Am J Bot 87: 964-970.

5. Bucher M et al. (1997) Plant Mol Biol 35: 497-508.

6. Bucher M et al. (2002) Plant Physiol 128: 911-23.

7. Zimmermann P et al. (2003) Plant Biotechnol J 1: 353-360.

8. Lehmann M et al. (2000) Protein Eng 13: 49-57.

Marcel Bucher
Federal Institute of Technology (ETH) Zurich
Institute of Plant Sciences, Experimental Station
Eschikon 33, CH-8315 Lindau, Switzerland
marcel.bucher@ipw.biol.ethz.ch



THE CHICKEN GENOME SYMPOSIUM
Eric Wong

The Chicken Genome Symposium: Impact and Applications was held November 13-14, 2003, in Atlanta, GA. One hundred and thirty attendees participated, of which 57 were from Academic Institutions, 62 were from Industry, and 11 were from Government Agencies. This symposium was co-organized by Avigenics Inc. and the University of Georgia with major sponsorship from the Poultry Industry and the USDA. The Program Agenda, Abstracts, and Workshop Summaries can be accessed at http://www.avigenics.com/symposium1.htm.

The chicken will be the first food animal species that will have its entire genome sequenced. Sequencing the bovine genome has begun and sequencing of the pig genome will be initiated in 2005. Because chickens are not only an important agricultural species but also a widely used model system for studying embryology and developmental biology, the sequence of the chicken genome would represent an invaluable resource. For a more detailed rationale for sequencing the chicken genome, see the Proposal to Sequence the Genome of the Chicken by J.D. McPherson, J. Dodgson, R. Krumlauf and O. Pourquie (http://genome.wustl.edu/projects/chicken/).

The Washington University Genome Center (St. Louis) expects to complete the sequencing and a working draft of the chicken genome by January 2004. The approach is to combine an integrated physical map with a six-fold, whole genome shotgun sequence strategy. Individual bacterial artificial chromosome (BAC) clones from four BAC libraries will be DNA fingerprinted and assembled into BAC contigs. In addition, randomly cloned fragments of the chicken genome will be sequenced and assembled. The raw, single-pass sequence data is available in the NCBI Trace Archives database at http://www.ncbi.nih.gov/Traces/trace.cgi? As of December 30, 2003, there were 11,701,769 sequences in the chicken Trace Archives, representing greater than 10 billion nucleotides of sequence.

The chicken genome sequencing project has been entirely supported by $25 million from the NIH. One of the key points brought out at the symposium was the need for an additional $2 million to complete the pre-finishing stage, which will close gaps, extend the size of sequence contigs, and enhance overall sequence quality. The prefinishing stage is roughly analogous to taking a collection of loose pages (the raw sequence) and ordering and binding these pages into a functional "book." If the pre-finishing stage is not completed immediately, the price to prefinish in the future will be much more or it may never be completed. In the absence of prefinishing, it will be left to individual researchers to complete a particular region of interest. Thus, the overall value of the chicken genome sequence to the scientific poultry community would be lessened.

The chicken genome contains an estimated 1.2 billion base pairs, which is 41% GC and is about 40% of the size of the mammalian genome. The smaller size of the chicken genome is due to a low density of repetitive DNA (approximately 7-8% of the genome) and small introns. The chicken genetic map is about 4000 cM (centimorgans), with greater than 2000 mapped markers. A number of chicken BAC (bacterial artificial chromosomes) libraries have been constructed, representing a 25-fold coverage of the genome.

Utilizing the vast amount of data that has been or will be obtained from the various genetic maps, physical maps, EST libraries, microarrays, and whole genome sequence will require powerful bioinformatics tools. The chicken information network, ChickNet at http://www.chicken-genome.org serves as a valuable reference site for bioinformatics tools. These tools can be used for comparative genomics, for example a comparison between the chicken and mammalian genomes. Even though birds and mammals diverged 300 million years ago, the sequence of the chicken genome has proven to be a valuable tool for the analysis of the human genome. Alignment of the chicken genome with the mammalian genome reveals the presence of putative exons in the human genome, because the exon sequences are conserved but the introns are not.

The complete sequence of the chicken genome will have a profound impact on avian genetics. The integration of genomics (gene structure and mRNA expression) with proteomics (protein expression) will provide the key to unraveling the basic mechanisms controlling growth, reproduction and health of poultry.


POULTRY RESEARCH IN THE POST-GENOME ERA
Eric Wong

The completion of a draft sequence of the chicken genome provides another powerful tool for poultry scientists. The challenge will be to utilize this information for improving avian growth, reproduction, and health. Clearly, the integration of all of the current resources (genetic and physical maps, QTL markers, EST libraries and microarrays, whole genome sequence, and proteomics) will be key to unraveling the molecular mechanisms that control complex biological systems.

The genome sequence should facilitate studies of functional genomics that aim to identify genes and their regulatory elements, the encoded gene products and the gene expression patterns for various metabolic processes. For the molecular biologist, no longer will chicken genes need to be cloned by the laborious process of screening lambda or BAC libraries; instead, the genes can now be "cloned" in silico. In the rapidly developing field of proteomics, the genome sequence will be essential to predict the amino acid sequences of encoded proteins/peptides. With a complete genome sequence, the search for candidate genes that are in close proximity to a marker linked to a desirable trait is greatly simplified.

Poultry nutritionists and physiologists will also benefit from genomic and proteomic technologies. Microarrays and proteome analysis will reveal groups of genes that are coordinately regulated in a metabolic pathway. The complete sequence of the chicken genome will facilitate the search for avian genes. For example, the identification of chicken genes that are involved in nutrient transport can be completed by a search of the avian genome for homologues to known transporter genes from other species. This type of genome scan has revealed that chickens and mammals share many transporters, however some mammalian transporters do not appear to be present in the avian genome.

Avian health is another area that should benefit from the genome sequence. Understanding the cellular genes regulating a host-pathogen interaction will be essential for developing strategies to enhance disease resistance. The development of cDNA microarrays for expression profiling of immune genes will reveal key genes or groups of genes involved in host response to infection. The identification of these genes will lead to the development of healthier birds, which in turn will have a direct impact on food safety issues.

Likely the major advances will come from an integrated approach that combines the genetic and physical maps and EST libraries and microarrays with the whole genome sequence. For example, the approach being used by Hans H. Cheng (hcheng@msu.edu) to dissect the molecular basis for Marek's disease virus infection involves the mapping of candidate genes by QTL analysis, categorizing differential gene expression by microarray analysis, and examining protein-protein interactions using a yeast two-hybrid screen. This multi-faceted approach is most likely to reveal the key genes involved in Marek's disease infection.

In addition to avian health, human health should also be improved because of advances in avian biotechnology. Transgenic chickens have been long proposed as bio-reactors for the production of pharmaceutical proteins for human medicine. Some of the advantages of chickens as bioreactors are that a chicken egg contains approximately six grams of protein, an egg is a sterile container that can be obtained non-invasively, and an industry is already in place for the automated collection and processing of eggs. For these reasons, the development of technologies for generating transgenic poultry has been a major goal.

Two companies, Origen Therapeutics (California) and Avigenics (Georgia), have developed efficient methods for producing transgenic chickens. Both companies have shown that large genomic BAC (bacterial artificial chromosome) expression vectors can be introduced into chicken cells and can express genes of interest from chicken promoters. The advantage of being able to transfer large DNA molecules is the ability to include most if not all of the normal regulatory elements required for tissue-specific expression. Both companies have already developed transgenic chickens that express human monoclonal antibodies and other proteins into eggs. These successes demonstrate that transgenic chickens represent a viable alternative to transgenic mammals as bioreactors.

It is an exciting time to be working with chickens both as an important agricultural species and as a model system. The number and variety of resources available will greatly facilitate the study of metabolic processes in avian species. These advances in avian biotechnology will ultimately benefit the poultry industry by producing a more economical and healthier bird. Furthermore, the human population will benefit by having a safer food product and a ready supply of egg-derived pharmaceuticals.

Eric A. Wong
Department of Animal and Poultry Sciences

Virginia Tech
ewong@vt.edu



GM CROPS CONTINUE TO BREED CONTROVERSIES
Phillip B. C. Jones

On December 18, the University of California, Davis, announced its recall of about 30 tomato seed samples distributed during the past seven years to researchers in the United States and abroad. Tests showed that the samples did not contain the intended variety, but rather a type engineered to express the PG gene, which improves the thickness of tomato paste. In 1996 Petoseed Company (since acquired by Seminis Vegetable Seeds) and Zeneca Plant Science commercialized a similar genetically modified (GM) tomato, a variety approved by the U.S. Food and Drug Administration and the U.S. Department of Agriculture.

A different type of GM plant mixing incited controversy in another part of Northern California. Echoing the Nuclear Free Zone movement a generation ago, anti-GM crop activists sponsored a ballot measure that will let Mendocino County residents decide whether to ban GM organisms (GMOs). If ballot Measure H is passed, then the county would become the first in the country to prohibit farmers from planting GM crops and raising GM livestock.

The California Plant Health Association, an agricultural industry group, did not care for the ballot's scare tactic statements, such as the assertion that "GMOs will irreversibly contaminate native plants and trees." The organization filed a lawsuit in December requesting the deletion of portions of the ballot measure. The judge, however, decided that he should not be micromanaging ballot language and that the CPHA has the opportunity to express opposing views on the ballot.

Supporters of the ban, including organic farmers, argue that they need Measure H to prevent their crops from being tainted with GM crops. Although Mendocino's biggest cash crop is reportedly marijuana, the county does have a strong organic farming presence. What Mendocino County seems to lack is the presence of GM crops. Nevertheless, a GM ban would benefit organic farmers who could use it as a marketing tool. A vote on Measure H is slated for March 2.

State and local venues are becoming popular battlefields for anti-GM crop activists and biotech lobbyists. However, the anti-GM movement targeted the federal government in a pending Hawaiian skirmish.

On November 12 a coalition of environmental groups filed suit in the Honolulu federal district court seeking an order for the USDA to develop an Environmental Impact Statement on the environmental and health risks associated with the open-air testing of biopharm crops, plants engineered to produce pharmaceuticals and chemicals for industrial uses. Characterizing the USDA's efforts as a "laissez faire regulatory approach," the plaintiffs alleged that the agency's regulation of field testing is inadequate to assure that biopharm crops do not contaminate soil or food supplies, harm humans or wildlife, or cross-breed with wild plants or conventional crops. This lack of oversight, they argued, violates the National Environmental Policy Act and the Endangered Species Act.

Led by the Center for Food Safety, the groups selected Hawaii for their campaign, because the state has more than one third of all U.S. endangered species. In addition, corn is the most popular plant for biopharming, and the plaintiffs suggest that biopharm corn might pass genetic material to conventional corn plants, thus jeopardizing the state's large seed corn industry. A copy of the complaint is available from the website of the Center for Food Safety (http://www.centerforfoodsafety.org/).

The EU's End to its GM Moratorium: An A-maizing Lack of Progress?
Syngenta's Bt-11 corn, engineered to resist the European corn borer, may be the first biotech food or animal feed approved for marketing in the European Union since 1998. Well, maybe eventually.

Two years ago, the EU Scientific Committee on Foods decided that the GM maize is as safe for human food use as its conventional counterpart. The European Commission then drafted a proposal for a decision about approving the GM corn, a proposal passed to a standing committee of food experts from EU member states. In December, the EU Regulatory Committee's vote split 6-6 with three countries (Belgium, Germany, and Italy) abstaining on whether to approve Bt-11 maize as unprocessed human food. In view of the deadlock, the Commission had been expected to approve a proposal to send the issue to European Union ministers. But a Commission spokeswoman announced on January 12 that members of the EU executive body wanted a debate on the issue and that it would probably be placed on the Commission's agenda for January 28.

An approval of Syngenta's application would sanction the import of Bt-11 into Europe as fresh, canned, or frozen products for human consumption. In 1998, the European Union approved the import of Bt-11 for use in food and animal feed. So, the current decision about Bt-11 does not seem remarkably controversial, especially compared with the looming question about cultivating GM crops.

During a December 18 plenary session, the European Parliament adopted a report that calls upon the Commission and member states not to proceed with the approval of the release of new GM plant varieties until the implementation of binding rules on the coexistence between GM, organic, and conventional crops. These rules must be fortified by a system of liability based on the "polluter pays" principle.

The adopted report also asks the Commission to establish legally binding definitions of "adventitious" and "technically unavoidable," a request that refers to purity thresholds for trace amounts of GM seed in a consignment of non-GM seed. The EU Directive on GM food and feed stipulates that any products containing more than 0.9 percent GMOs have to be labeled as containing GMOs. The Commission recently suggested a tolerance level of 0.3 to 0.7 percent for adventitious or technically unavoidable GMOs in crops, depending on the variety. The biotech industry argued that the lower limits were too restrictive, while green groups found the limits too generous. Since both sides are unhappy, Commission members may see the proposal as a good compromise. The Commission's vote on the issue, expected in October, has been delayed until next spring.

Meanwhile, EU member states struggle with the GM crop farming issue. On January 13, officials on the United Kingdom's Advisory Committee on Releases to the Environment (ACRE) gave a mixed review for the future of crop bioengineering. Environment Secretary Margaret Beckett had asked ACRE to assess the results of three-year farm scale evaluations of GM maize, beet, and oilseed rape. A consortium of research institutions had performed the studies and published their findings on October 16 as a series of eight peer-reviewed scientific papers in the Philosophical Transactions of the Royal Society (Biological Sciences). After studying the results, ACRE concluded that GM herbicide-tolerant beet and oilseed rape could present a danger to farmland wildlife. On the other hand, the Committee decided that GM herbicide-tolerant maize could be commercialized without adverse environmental effects if grown and managed as in the farm scale evaluations. ACRE emphasized that the adverse effects observed with beet and oilseed rape may be mitigated by using a management regime different from the one used in the study. The Committee also stressed that the experiments showed the effects of herbicide management systems, and that the results say nothing about potential direct effects of GM plants.

ACRE forwarded its report to government ministers who will consider the advice before making a final decision about whether the herbicide-tolerant crops should be approved for cultivation. A copy of the report is available from ACRE's website ( http://www.defra.gov.uk/environment/acre/pubs.htm).

In Germany, the Minister for Agriculture and Consumer Affairs, Renate Kuenast, announced that the government sees no risk from GM food, and that she expects GM corn to appear in European supermarkets in the fall. The German government recently reached a consensus on a law to implement the EU Directive on the deliberate release of GMOs into the environment. The new law would establish a framework for farmers who want to grow GM crops and includes "polluter pays" protection for farmers whose non-GM produce becomes contaminated with GMOs. Ms. Kuenast, a member of the pro-environmentalist Green Party, said that the government should adopt the proposed law in February. Only last September, the German Association of Biotechnology Industries alleged that Kuenast was blocking the development of GMOs for ideological reasons.

Selected References

Anonymous. (2003) Tomato seed from seed bank found to be genetically modified. December 18. Available at: http://www. news.ucdavis.edu.

Anonymous. (2004) Germany drafting law to regulate genetically modified crops. January 12. Available at: http://www. eubusiness.com.

Geniella M. (2003) Judge OKs genetically modified crop ban vote. The Press Democrat, B1, December 31.

Miller S. (2003) EU splits on genetically modified corn. Wall Street Journal (Brussels), A.2., December 9.

Phillip B. C. Jones, PhD., J.D.
Spokane, Washington
PhillJones@nasw.org




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