By correlating the relative fitness under the different environments with the overall tolerance of the genotype, the researchers assessed the costs and benefits of tolerance.2 In Figure 2, relative fitness values under control and herbicide-application treatments (in graphs A and B, respectively) are correlated with tolerance.
The negative slope in A indicates that there is a fitness cost to tolerance in a glyphosate-free environment; conversely, the positive slope in B signifies a fitness advantage associated with tolerance under the herbicide treatment (as one might expect). A specific example of this fitness cost under the control condition is that the most glyphosate-tolerant line produced 35% fewer viable seeds than the most glyphosate-susceptible line2.
In other words, as long as there is sufficient variation in the genes for tolerance (as there seems to be for I. purpurea), one would expect strong selection for tolerance in the presence of the herbicide, and selection against tolerance when the herbicide is absent.2
For risk assessors, the distinction between resistance and tolerance is an important one, because the two traits are likely to evolve in different ways and therefore have different effects1. In a study modeling the evolutionary dynamics of disease resistance and disease tolerance in a long-lived host, Roy and Kirchner3 found that resistance genes eventually settled at a polymorphic equilibrium, whereas tolerance genes were driven to fixation. Variation still exists in the traits governing tolerance to glyphosate in the morning glory because Roundup represents a relatively new selective force on this plant1. Because theory predicts fixation of tolerance under constant exposure to a selective force3, managers might be encouraged by Baucom and Mauricio’s discovery of fitness tradeoffs associated with tolerance when the selective force is absent. This means that the evolution of tolerance might be delayed, in this case, by halting application of Roundup or possibly by applying an herbicide that acts through a different mechanism1. In the context of a field of Roundup Ready crops, this recommendation necessarily implies rotation to a different crop plant.
Monitoring specifically for tolerance in weedy species will be important to better understand this phenomenon, particularly where selective forces are high, such as in Roundup Ready fields. Further complicating future management of tolerance is the possibility that tolerance and resistance traits are genetically linked, so management schemes may have to account for the evolution of both in certain species. Since the ecology of agricultural landscapes is changing rapidly, including new selective pressures associated with farming herbicide-resistant crops, agronomic practices should be guided by adaptive management. As Roy cautions1, if we don’t learn how to effectively retard the evolution of resistance and tolerance in pest species, we will compromise the efficacy of herbicides and ultimately face a widespread agricultural problem.
Thanks to Drs. Anne Kapuscinski and Karen Oberhauser for comments on an earlier draft of this review.
1. Roy BA (2004) PNAS 101, 13974-13975
2. Baucom RS & Mauricio R (2004) PNAS 101, 13386-13390
3. Roy BA & Kirchner JW (2000) Evolution 54, 51-63
Our experiments thus demonstrated that: (a) insects that are normally susceptible to Bt genes are even more susceptible to the fusion protein between Bt and the ricin B chain, suggesting that we may not require a high dose deployment strategy for transgenic crops expressing such molecules; (b) a major lepidopteran pest that is resistant to Bt now becomes susceptible; (c) a homopteran pest that is outside the normal host range of Bt is now highly susceptible to the hybrid molecule; and (d) not all insects become susceptible to the fusion protein molecule. The last point is extremely important as it demonstrates a degree of selectivity in the mode of action of the fusion protein. This also provides a starting point for further engineering experiments to construct highly specific toxins targeted against particular insect pests but not others.
Standard Bt cotton, maize, and potato crops have been released commercially and have been readily adopted by farmers, while Bt rice, although yet to be commercialized, has been tested successfully in several field trials. Rice plants expressing Bt genes are expected to be commercialized in China in the very near future and are already being cultivated illegally by farmers. Experience has shown the benefits of such enhanced crops in terms of increased yields, reduced chemical inputs and, as a knock-on effect, improved farmer and consumer health. Sustainable resistance against insect pests is the cornerstone of any sensible deployment strategy that utilizes transgenic plants expressing insecticidal proteins, either alone or, preferably, within an integrated pest management system. It is in the context of resistance management that crops expressing fusion proteins such as those described in our work could be the most beneficial.
Bt crops in the U.S. must be co-maintained with refuges that decrease the selection pressure on target pests and reduce the theoretical likelihood of establishing resistance, while in China, refuges in Bt cotton crops are provided by an alternative host plant that supports the major pest species, Helios armigera. This type of mandatory refuge management system may be difficult to implement for crops such as rice and maize in developing countries with many smallholder farms, and where substitute hosts for insect pests are not available. Fusion proteins such as those we have developed have the potential of providing strong and sustainable resistance requiring multiple counter-adaptive mutations, but would require only a single toxin transgene.
Lessons learned following the widespread use of chemical pesticides for the control of insect pests over the past several decades call for reason and caution in how we deploy transgenic plants expressing insecticidal genes presently and in the future, and a requirement to learn about the basic mechanisms. Bt transgenic plants are remarkably specific in their activity, with little or no effect on non-target organisms. Field tests with Bt rice, maize, and other crops have revealed no negative impact on biodiversity and indeed a positive impact resulting from the reduction in pesticide use3. Another strong advantage of conventional Bt crops is that there is no credible evidence for toxicity or allergenicity in humans.
The environmental, economic, and social benefits of insect resistant crops are well known, despite claims to the contrary by opponents of biotechnology applications that particularly benefit developing countries. For Bt cotton, farmers in India have seen a 70% reduction in the use of chemical insecticides translating to a very substantial savings in expenditure on insecticides by subsistence farmers who are the individuals least likely to afford them. Up to 85% increases in cotton yields have been seen by Indian farmers who have adopted the technology. Similarly, in China, farmers who are cultivating Bt cotton have been able to reduce the number of insecticide applications to one third, compared to farmers that grow conventional cotton4. In addition, the number of farmers in China reporting pesticide poisoning symptoms in conjunction with cultivation of Bt cotton was reduced from 50,000 to less than 2,500.
Wider application of this technology will necessitate testing a broad range of insects encompassing agriculturally important pests and also beneficial insects and other organisms to ascertain the full efficacy and safety of these fusion proteins. Prudent and necessary safety evaluations and environmental impact assessments of transgenic insect resistant crops need to be performed in a rational and scientific manner. It is necessary to ascertain effects on non-target organisms; however, we need to keep such evaluations in the appropriate biological perspective. If, for example, there are some minor detrimental effects on the growth rate of the green lacewing, this author believes the plight of hundreds of millions of people in the developing world who are on the brink of starvation or those subsistence farmers who are forced to use toxic chemicals to combat insects should also be a component of the assessment exercise!
As a final thought, an increasing number of resources are being diverted towards the development of ever more sensitive methods to detect so called "unintended effects on non-target organisms" in insect resistant transgenic crops. So far, most, if not all, of the results are negative, especially when compared to current agricultural practices, a control many politically-minded researchers do not usually perform. Is it not perhaps time to apply scientific reasoning and come to the logical conclusion that if a battery of tests fails to demonstrate any substantial detrimental effects, perhaps the answer might be that these plants do not pose any real threat to the environment, rather than pursuing further research to develop even more sensitive methods in the hope that such detrimental effects might be detected?
I would like to thank Jonny Gressel for helpful comments on the final draft of this manuscript and the Rockefeller Foundation for continuous support over the past 15 or so years.
1. Bano-Maqbool S, Riazuddin S, Loc NT, Gatehouse AMR, Gatehouse JA & Christou P (2001) Expression of multiple insecticidal genes confers broad resistance against a range of different rice pests. Molecular Breeding 7, 85-93
2. Mehlo L, Gahakwa D, Nghia P-T, Loc N-T, Capell T, Gatehouse J, Gatehouse A & Christou P (2005). An alternative strategy for sustainable pest resistance in genetically enhanced crops. Proceedings of the National Academy of Sciences USA 102, 7812-7816
3. James C (2004). Global Status of Commercialized Biotech/GM Crops: 2004. ISAAA, Ithaca NY
4. Huang J, Hu R, Rozelle S & Pray C (2005) Insect-resistant GM rice in farmers´ fields: Assessing productivity and health effects in China. Science 308, 688-690
A WIDE CROSS-TOLERANCE OF TRANSGENIC RICE CONTAINING HUMAN CYP2B6 TO VARIOUS CLASSES OF HERBICIDES
Sakiko Hirose and Hiroyuki Kawahigashi*
Pesticides have played very important roles against food shortages and plant diseases, and our modern life would be vastly different without their use. Weed infestation adversely affects crop production by reducing yields and decreasing market prices of the crop. For cost-effective land use, crop yield and price must be maximized, and the cost of weed control minimized. Herbicides substantially lighten the farmer’s heavy physical workload and improve crop yield and product quality. Herbicides are now widely used for crop cultivation and for management of lawns, railroad rights-of-way, highway margins, and other purposes, although there remains the possibility of non-target effects of pesticides to the environment caused by agricultural runoff.
One of the major problems with the use of herbicides is that repeated use of the same herbicide in a field tends to promote the emergence of herbicide tolerant weeds. Indeed, over 290 biotypes of herbicide tolerant weeds have been reported in agricultural fields and gardens worldwide (International survey of herbicide tolerant weeds, http://www.weedscience.org/in.asp). They are categorized into 18 HRAC (The Herbicide Resistance Action Committee) groups (Classification of Herbicides According to Mode of Action 2005, http://www.plantprotection.org/hrac/Bindex.cfm?doc=moa2002.htm). Fifty percent of the biotypes are resistant to inhibitors of acetolactate synthase, such as sulfonylureas, and inhibitors of photosynthesis at photosystem II, such as triazines.
Several strategies are used to prevent or reduce herbicide tolerance in weed populations. Using either several herbicides in rotation or in a mixture including lower doses of herbicides was proposed as the most practical approach to prevent or delay the appearance of tolerance, because most cases of herbicide tolerance are due to a single major gene, and also because the repeated use of a single herbicide for a long time tends to promote weeds that are tolerant1.
To enable crop plants to grow under such an herbicide regime, it would be helpful to develop transformed plants containing a gene for a single mammalian P450 enzyme, which would detoxify several types of herbicides, and thereby give these plants cross-tolerance to herbicides2.
The cytochrome P450 monooxygenase (P450) system, consisting of cytochrome P450 and NADPH-cytochrome P450 oxidoreductase, catalyzes monooxygenation of lipophilic xenobiotic compounds, including herbicides. It has been reported that several microsomal P450s are involved in xenobiotic metabolism in mammals. The individual xenobiotic-degrading P450s appear to show overlapping, broad substrate specificity and thus improve the animal’s ability to catabolize a variety of unknown lipophilic compounds, including herbicides, in liver3.
We introduced a human gene for CYP2B6, a cytochrome P450 monooxygenase that inactivates xenobiotic chemicals, into Oryza sativa cv. ‘Nipponbare’ by Agrobacterium-mediated transformation. In our study, we demonstrated that transgenic rice expressing human CYP2B6 under the control of CaMV 35S showed strong herbicide tolerance that resulted from the detoxification of several types of herbicides by the CYP2B64.
The CYP2B6 rice plants showed normal growth in morphology, including plant height, leaf color, flowering time, fertility, and seed size, compared with non-transgenic Nipponbare plants in a greenhouse. The CYP2B6 rice plants were physiologically the same as non-transgenic Nipponbare, except for the feature derived from the introduced CYP2B6 gene.
The CYP2B6 rice plants showed high tolerance to 13 out of 17 herbicides, which belong to different chemical families. These were chloroacetoamides (acetochlor, alachlor, metolachlor, pretilachlor, and thenylchlor), oxyacetamides (mefenacet), pyridazinones (norflurazon), 2,6-dinitroanilines (trifluralin and pendimethalin), phosphoamidates (amiprofos-methyl), thiocarbamates (pyributicarb), and ureas (chlortoluron).
Significantly high tolerance was observed to the five chloroacetoamides, which inhibit the synthesis of very long chain fatty acids (VLCFA). For example, the CYP2B6 rice seeds were able to germinate and grow in the medium containing 80 μM metolachlor (about 15 times the dose of practical use in cornfields), while non-transgenic Nipponbare did not germinate in the presence of 2 μM metolachlor (about one-third the dose of practical use in cornfields). Another VLCFA synthesis-inhibiting herbicide, mefenacet, inhibited the germination of Nipponbare, but had little effect on the growth of CYP2B6 rice plants.
Microtubule assembly-inhibiting herbicides, pendimethalin and trifluralin, and unknown function herbicide, pyributicarb, inhibited the root growth of Nipponbare, but CYP2B6 rice plants produced roots and grew better than Nipponbare. A photosynthesis-inhibiting herbicide, chlortoluron, inhibited the growth of Nipponbare plants, but the CYP2B6 plants grew vigorously.
CYP2B6 rice was slightly tolerant to norflurazon, which caused bleaching of shoots of Nipponbare by the inhibition of carotenoid synthesis. The CYP2B6 rice metabolized the herbicides during and after germination, keeping the concentration of the herbicide in plant tissues under the lethal threshold. Therefore, the CYP2B6 rice plants could metabolize a broad spectrum of herbicides and showed cross-tolerance to several herbicides having different chemical structures and different modes of action.
The results of thin layer chromatography analysis revealed that the amounts of metolachlor decreased in CYP2B6 rice plants and in the medium of CYP2B6 rice faster than those of non-transgenic Nipponbare. In this study, the CYP2B6 rice plants rapidly metabolized metolachlor to its demethylated metabolite. The metabolism of metolachlor seemed to be enhanced by the introduced CYP2B6 in the transgenic plants, although metolachlor was metabolized not only by CYP2B6 rice but also by control plants.
In the greenhouse, CYP2B6 rice plants grew vigorously in an enamel pot with soil and water that also contained metolachlor at the same dose of practical use in cornfields. On the other hand, non-transgenic Nipponbare plants were almost killed by metolachlor. This result indicated that CYP2B6 rice plants were practically useful as an herbicide tolerant crop under the conditions of a paddy field.
The wider cross-tolerance to herbicides having different modes of action and different chemical structures seems to be a special feature of transgenic plants expressing mammalian P450 genes. This cross-tolerance would prove useful to prevent the development of herbicide resistance of weeds, because the use of several herbicides in rotation would not harm the crop.
The herbicide cross-tolerance during germination should be important for weed control in rice fields, especially with the direct-seeding system. In the transplanting–cultivation system of rice seedling, standing water in paddies prevents the germination of many weeds, and as a result, few kinds of plants are major weeds. However, in the direct-seeding system without water cover, the germinating rice must compete with many kinds of weeds. The transgenic rice with cross-tolerance to various types of herbicide should be an ideal plant for weed control with herbicide mixtures, especially in direct seeding.
We expect that CYP2B6 rice will also prove useful in degrading and thus decreasing the environmental loads of herbicides, insecticides, industrial chemicals, and endocrine-disrupting pollutants in paddy fields and the connected water streams. In the future, transgenic plants expressing P450 species should be good not only for developing herbicide-tolerant rice but also for reducing the environmental impact of agrochemicals.
References
1. Putwain PD. (1990) The resistance of plants to herbicides. In Weed control handbook: Principles, R Hance and K Holly, Eds., Blackwell: Oxford, 217-242
2. Ohkawa H, Tsujii H, & Ohkawa Y. (1999) The use of cytochrome P450 genes to introduce herbicide tolerance in crops: a review. Pestic Sci, 55, 867-874
3. Inui H et al. (2001) Metabolism of herbicides and other chemicals in human cytochrome P450 species and in transgenic potato plants co-expressing human CYP1A1, CYP2B6 and CYP2C19. J Pestic Sci 26, 28-40
4. Hirose S et al. (2005) Transgenic Rice Containing Human CYP2B6 Detoxifies Various Classes of Herbicides. J Agric Food Chem 53, 3461-3467
Sakiko Hirose and Hiroyuki Kawahigashi*
Plant Biotechnology Department
National Institute of Agrobiological Sciences
Ibaraki, Japan
*shiwak@affrc.go.jp

NON-AGROBACTERIAL SPECIES FOR GENE TRANSFER TO PLANTS
P. Janaki Krishna
Agrobacterium tumefaciens is a common soil bacterium that causes crown gall disease by transferring some of its DNA to the plant host. This unique mode of action has enabled this bacterium to be used as a tool in plant breeding1. Many desired genes of agronomic importance are engineered into this bacterial DNA and thereby inserted into plant genomes. Though close relatives of Agrobacterium, such as Rhizobium trifolii and Phyllobacterium myrsinacearum, display the gall producing ability by harboring a Ti (Tumor-inducing) plasmid, no direct molecular evidence of gene transfer to plants by these bacteria has been reported. In fact, until now, the body of research has focused on using Agrobacterium as a vehicle for gene transfer. However, researchers are now attempting to use other Agrobacteria-related species, such as Sinorhizobium and Mesorhizobium, to augment gene transfer techniques.
A research team from CAMBIA (http://www.cambia.org/daisy/cambia/563) has investigated whether a non-Agrobacterial species of bacteria can competently transfer genes in plants2. To do this, a disarmed Ti plasmid (pEHA105) from a hypervirulent Agrobacterium strain was introduced into several species of bacteria. To facilitate transfer of this large plasmid, the origin of transfer (oriT) of a broad host range IncP plasmid was integrated into the Ti plasmid of EHA105 at two different locations (pTiWB1, pTiWB3). The modified plasmids were then mobilized into 1) a Rhizobium species (NGR234) that has an exceptionally broad host range, capable of nodulating over 100 different plants3; 2) the alfalfa-symbiont Sinorhizobium meliloti; and 3) Mesorhizobium loti, a representative of a different family (Phyllobacteriaceae). In order to check the genotype of engineered strains by PCR and confirm that the strains were free of contaminating Agrobacterium by selective plating, additional primers were developed. In addition, the transfer rate and replication potential were enhanced by incorporating two broad-spectrum replication origins (sites) to the disarmed Ti plasmid. To assay for gene transfer, three binary vectors were prepared: pCAMBIA1105.1R was introduced into the Rhizobia bacteria, and either pCAMBIA1105.1 or pCAMBIA1405.1 into Agrobacterium.
The plant transformation events were analyzed through GUS activity, Southern blotting, and PCR assays. First, the GUS assay tested the transformation rate in tobacco. The transformation rate using Sinorhizobium meliloti was about 25% that of Agrobacterium, and M. loti had a rate approximately one third of Sinorhizobium. However, that value is still significant enough to get the attention of researchers interested in plant transformation.
The researchers also tested the non-Agrobacterium bacteria for their ability to transform other plant species, namely Arabidopsis and rice. Arabidopsis was transformed with S. meliloti using the floral dip method, producing six transgenic plants from 70,000 T0 seeds, which is 5–10% of the normal efficiency of A. tumefaciens. Interestingly, in all cases, T-DNA was integrated in a manner identical to that of Agrobacterium. Also, an effort was made to increase the transformation efficiency of the floral dip technique by modifying the infiltration medium, whereby a four-fold improvement was obtained. In rice, the transformation efficiency was considerably lower (0.6%) when compared with Agrobacterium tumefaciens (50–80%). One transformed rice plant from a total of 695 calli was regenerated and rooted. T-DNA integration analysis in this rice plant revealed that the T-DNA had integrated into rice chromosome 11.
Thus, though the transformation efficiency was considerably lower when compared to Agrobacterium mediated transformation, the results confirm that all three non-Agrobacterium species, Rhizobium, Sinorhizobium, and Mesorhizobium strains, belonging to two families of bacteria, can transform plants. Of these, S. meliloti is the most competent to transfer genes into both monocots and dicots and into a range of tissues, including leaf tissue, undifferentiated calli, and immature embryo ovules.
Albeit, at a lower frequency, T-DNA transformation appeared to proceed normally, but most notable is the fact that transformation occurred at all using non-virulent, non-Agrobacterium microbes. Though a number of factors that reside on Ti plasmids (as acting genes and DNA elements) play an important role in DNA transfer, it has been noted that other transacting elements are located on Agrobacterial chromosomes4. In addition, the researchers suggest that if there are gene functions necessary for gene transfer that are not encoded by the Ti plasmid, they must have equivalents or homologues in multiple Rhizobial species. It is likewise possible that the small number of vir-related genes on the Ti plasmid is sufficient to confer gene transfer competence to any bacterium. It is also noted that homologues of these transacting Agrobacterium genes exist in other bacteria and it is suggested they could have evolved from DNA transfer to plants in the past.
This study is a breakthrough in research concerning the exploitation of non-Agrobacterial bacteria for gene transfer to plants. It appears that when it comes to acquiring or transferring genetic information, interestingly, bacteria always show promise.
In addition, it is heartening to note that this alternative technology is available to the public in a "protected technology commons," optimized and improved as a ‘Bioforge’ project (http://www.bioforge.net).
References
1. Gelvin SB (2003) Agrobacterium- mediated plant transformation: the biology behind "gene-jockeying" tool. Microbial. Mol. Biol. Rev. 67, 16–37
2. Broothaerts W et al. (2005) Gene transfer to plants by diverse species of bacteria. Nature 433, 629–633
3. Pueppke SG & Broughton WJ (1999) Rhizobium sp. strain NGR234 and R. fredii USDA257 share exceptionally broad, nested host ranges. Mol. Plant Microbe Interact. 12, 293–318
4. Van Montagu M & Schell J. (2003) (1935–2003): Steering Agrobacterium-mediated plant gene engineering. Trends Plant Sci. 8, 353–354
P S Janaki Krishna
Institute of Public Enterprise
Osmania University Campus
Hyderabad, India
jankrisp@yahoo.com

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