ライフサイエンスコーパス: herbicide

1 nly at special times (e.g. sensitivity to an herbicide).

2 tacommunities of soil microbes adapting to a herbicide.

3 ty, results in different efficiencies of the herbicide.

4 etely, making it harder to find a successful herbicide.

5 metabolic activities of algae caused by this herbicide.

6 e Fourier transform of DF as an indicator of herbicide.

7 of excess light, or under low light plus the herbicide.

8 s of algae induced by the presence of Diuron herbicide.

9 hosate, the most widely applied agricultural herbicide.

10 for plant physiology and the development of herbicides.

11 hylogenetic signal for diatom sensitivity to herbicides.

12 the development of anti-infective agents and herbicides.

13 nd provide a quantitative method for sensing herbicides.

14 terbutryn, but not by nitrile or phenylurea herbicides.

15 ure is the lack of effective natural product herbicides.

16 e in biotypes of weeds that are resistant to herbicides.

17 ounds and transitioned to the age of organic herbicides.

18 zymes showed insensitivity to five inhibitor herbicides.

19 F1 that had a restricted ability to detoxify herbicides.

20 overies were achieved with RSDs<20% for most herbicides.

21 ncluding incineration and the manufacture of herbicides.

22 ed clover, and alfalfa were not treated with herbicides.

23 weed growth and were developed as bleaching herbicides.

24 dimethyl OP insecticide metabolites and the herbicide 2,4-D in children.

25 followed by the fungicide propiconazole and herbicide 2,4-dichlorophenoxyacetic acid (2,4-D).

26 The herbicide 2,4-dichlorophenoxyacetic acid and the mycotox

27 low-herbicide regime as for the conventional-herbicide 2-year rotation.

28 veral pesticides including the commonly used herbicides 2,4-D and glyphosate, the insecticides permet

29 hosphide and ethylene dibromide; the phenoxy herbicide (2,4,5-trichlorophenoxy)acetic acid (2,4,5-T);

30 thus spp. (that evolved resistances to major herbicides); (2) Lolium spp., important pasture grasses,

31 Seven pesticides (herbicides: 2,4-D and simazine; insecticides: carbaryl,

32 s, 20%), pesticide types (insecticides, 46%; herbicides, 24%), chemical classes (pyrethroids, 77%; bo

33 tion x herbicide combinations except the low-herbicide 3-year rotation, which contained approximately

34 16 fungicides (52%), 8 insecticides (26%), 2 herbicides (6%), 3 pesticide derivatives (10%), 1 insect

35 ne common contaminants (five antibiotics, an herbicide, a beta-blocker, an antidepressant, and an ant

36 er exposed to each pesticide alone, a mix of herbicides, a mix of insecticides, or a mix of all five

37 onferring insect (cry34Ab1 and cry35Ab1) and herbicide (aad1) resistance, and a phiyfp reporter gene

38 ture with new, effective resistance-breaking herbicides along with strategies to sustain their utilit

39 or Rox(V)) have been extensively used as an herbicide and growth enhancers in animal husbandry, resp

40 most hybrids showed strong resistance to the herbicide and insect.

41 (MSMA or MAs(V)) has been used widely as an herbicide and is reduced by microbial communities to MAs

42 The widespread use of herbicides and antibiotics for selection of transgenic p

43 isms and are introduced anthropogenically as herbicides and antimicrobial growth promoters for poultr

44 Agricultural herbicides and daidzein inputs were primarily via upstre

45 des for spina bifida, and 2,6-dinitroaniline herbicides and dithiocarbamates-methyl isothiocyanate fo

46 ms and breakdown products of organoarsenical herbicides and growth promoters.

47 elemental composition, including residues of herbicides and pesticides, of 31 soybean batches from Io

48 is at the base of the exceptional potency of herbicides and potentially a target for the discovery of

49 genic plants acquired resistance to multiple herbicides and showed similar changes in their secondary

50 expression cassettes were tested with three herbicides and showed tolerance to four times the labele

51 apping binding sites of the three classes of herbicides and the structure of their variable parts exp

52 tically engineered (GE) to resist glyphosate herbicides and to produce its own insecticidal toxin, ma

53 iated chemical redox cycling of bipyridinium herbicides and various quinones; this activity was great

54 rve gas byproduct), glyphosate (a ubiquitous herbicide), and inorganic phosphate over a wide range of

55 nfrequent use of fertilizers, pesticides and herbicides), and also dominated by large projects.

56 Terbuthylazine (TBA) is a widely used herbicide, and its heterogeneous reaction with OH radica

57 an efficient way to remove chloroacetanilide herbicides, and also shed new insight into the possible

58 a target for the development of antibiotics, herbicides, and antimalarial drugs.

59 cid (MSMA) have been extensively utilized as herbicides, and aromatic arsenicals such as roxarsone (R

60 ll molecules are used commercially as drugs, herbicides, and fungicides in different systems, but in

61 re introduced by beekeepers; and fungicides, herbicides, and other environmental contaminants.

62 ity (RBA) and bioaccessibility values for 13 herbicide- and mine-impacted soils.

63 ed to a tracer enzyme and used to detect the herbicide-antibody complex in an ELISA format.

64 is biosynthetic route a promising target for herbicides, antifungal agents, and antibiotics.

65 Both CO2 and N2 O fluxes increased following herbicide application in all converted fields, but in th

66 llected before and along a time-course after herbicide application.

67 asing crop rotation diversity while reducing herbicide applications may maintain effective weed contr

68 % of maize, 43% of soybean and 45% of cotton herbicide applications.

69 These herbicides are also very reactive with sulfate radicals

70 Phenoxy acid herbicides are important groundwater contaminants.

71 The benefits achieved by the use of these herbicides are indisputable.

72 tlas demonstrates why some widely used auxin herbicides are not, or are very poor substrates.

73 If herbicides are to remain sustainable, then it is a must

74 eme was evaluated using cationic and anionic herbicides as test analytes in water.

75 phosphate class of compounds includes common herbicides as well as highly toxic nerve gases whose det

76 rt approach enabled chip-HPLC-MS analysis of herbicides at the highest pressure and speed.

77 ise and three-way mixtures between different herbicides at various total combined doses.

78 weeks) exposed to two concentrations of the herbicide atrazine (100 and 250 mug L(-1)).

79 The widely-used herbicide atrazine (ATZ) is detected in ground and surfa

80 generational effects promoted by widely used herbicide atrazine (ATZ).

81 For example, the herbicide atrazine affects host defences (e.g. resistanc

82 The herbicide atrazine, a suspected endocrine disrupting che

83 munosensor (PhAIEI) for the detection of the herbicide atrazine.

84 iotics that frequently contaminate hives-two herbicides (atrazine and glyphosate) and three fungicide

85 s-Triazine herbicides (atrazine, ametryn) are groundwater contamina

86 amine the single and combined effects of two herbicides (atrazine, glyphosate), and three insecticide

87 s performed on four photosystem II inhibitor herbicides (atrazine, terbutryn, diuron, and isoproturon

88 No AUX1 activity was observed for herbicides based on benzoic acid (dicamba), pyridinyloxy

89 The herbicide beflubutamid, which acts as an inhibitor of ca

90 m, CYP76C1, CYP76C2, and CYP76C4 metabolized herbicides belonging to the class of phenylurea.

91 mass spectrometry also show that when these herbicides bind, thiamine diphosphate (ThDP) is modified

92 o develop the sensitivity and selectivity of herbicide binding by the Rba. sphaeroides reaction centr

93 iazolinone ring is inserted deepest into the herbicide binding site.

94 pyrimidinyl group inserted deepest into the herbicide binding site.

95 f the sample flow-rate, exposure time to the herbicide, biomass loading, biosensor film thickness, in

96 hylene) phosphate ester for anencephaly; the herbicide bromoxynil octanoate for spina bifida; and tri

97 he rapidly evolving resistance to commercial herbicides, but a new MOA has not been introduced in ove

98 ns reduced toxicity and system dependence on herbicides by 25-51%.

99 There is widespread use of herbicides by the general public, although likely at low

100 and classified as glyphosate, non-glyphosate herbicides, chemical lepidopteran insecticides, biologic

101 e antibacterial agent chloroxylenol, and the herbicide chloroxynil.

102 herbicide resistance, with a shortage in new herbicide classes, our findings reveal MDHAR6 as a valua

103 cals and the triazine and phenoxyacetic acid herbicide classes.

104 tup phage-free noncompetitive assays for the herbicide clomazone (MW 240 Da).

105 soybean was <25 kg ha(-1) in all rotation x herbicide combinations except the low-herbicide 3-year r

106 able to provide in situ measurements of the herbicide concentration every 180 min.

107 ely yielded a quantitative method to measure herbicide concentration in frequency domain.

108 hrough photosynthesis was different for each herbicide concentration in the examined sample.

109 ship between the Fourier transform of DF and herbicide concentration was theoretically modelled and a

110 ent attenuation provided a direct measure of herbicide concentration, with no need for model-dependen

111 g TWA concentrations that was independent of herbicide concentrations ranging over 2 orders of magnit

112 lso active toward AmGSTF1 and helped restore herbicide control in MHR black-grass.

113 andscape of crossed spatial gradients of the herbicide (Dalapon) and a resource (glucose), whereas th

114 ng either excess light or low light plus the herbicide DBMIB (2,5-dibromo-3-methyl-6-isopropyl-p-benz

115 at were initially bleached without heat by a herbicide (DCMU, at 24 degrees C) also recovered predomi

116 In this way the target herbicide decreases the O2 production of the analyte-sen

117 lleles are robust substitutes for antibiotic/herbicide-dependent marker genes as well as surprisingly

118 Diuron is a widely used herbicide detected in freshwater ecosystems and may impa

119 ater toxicity analysis and more particularly herbicide detection in water.

120 Herbicide detection was achieved through a range (blank

121 nooxygenase-catalyzed O-demethylation of the herbicide dicamba (2-methoxy-3,6-dichlorobenzoic acid).

122 can also serve as brominating agents of the herbicide dimethenamid in solutions of bromide to which

123 s that can serve as the focus of traditional herbicide discovery efforts.

124 that exposure to glyphosate (a commonly used herbicide) does not result in glyphosate bioaccumulation

125 lant species that have evolved resistance to herbicides due to enhanced metabolic capacity to detoxif

126 n of 2,4-Dichlorophenoxy Acetic Acid (2,4-D) herbicide either in standard solution and spiked real sa

127 6%), stability and a LOD (0.3ppb) lower than herbicide emission limits.

128 g the degradation of a no longer widely used herbicide, especially in tandem with an herbicide-resist

129 The sulfonylurea herbicides exert their activity by inhibiting plant acet

130 Five commercial herbicide families inhibit acetohydroxyacid synthase (AH

131 he sulfonylamino-carbonyl-triazolinone (SCT) herbicide families, revealing the structural basis for t

132 The herbicide fluazifop-P-butyl (FPB) is used against grasse

133 Glyphosate is the most widespread herbicide for weed management, being extensively used in

134 vatives for anencephaly, hydroxybenzonitrile herbicides for spina bifida, and 2,6-dinitroaniline herb

135 own that other pesticides (ie, insecticides, herbicides, fungicides) are associated with excess risk

136 long-term succession and diffuse transfer of herbicides, fungicides, and insecticide treatments in a

137 large number of biocidal active ingredients (herbicides, fungicides, and insecticides); we then selec

138 PA commissioned screening of 320 pesticides, herbicides, fungicides, and other chemicals in a series

139 nmentally relevant doses of glyphosate-based herbicides (GBH) is still a debatable and unresolved mat

140 is demonstrated on sensing of a phosphonate herbicide glyphosate and other biologically important an

141 itive response to RT, whereas the use of the herbicide glyphosate did not significantly affect earthw

142 ubsequently determined to be tolerant to the herbicide glyphosate in greenhouse spray tests.

143 t to the insect Helicoverpa armigera and the herbicide glyphosate) and two non-GM lines (Shiyuan321 a

144 sis of phosphorus-containing amino acid-type herbicides (glyphosate and glufosinate) in soil and huma

145 For example, the use of postemergence herbicides (glyphosate), which induce an increase in soi

146 d of resistance to the most extensively used herbicide, glyphosate, is a major threat to global crop

147 A mixture of herbicides had no effect on microbial diversity or struc

148 The application of mixtures of herbicides has been advocated as an anti-resistance stra

149 anging market dynamics, the discovery of new herbicides has declined significantly over the past few

150 ocedure for analysis of difficult high polar herbicides (HPH) in diverse foods of plant origin.

151 is population was screened using glufosinate herbicide, hygromycin leaf painting, and multiplex polym

152 w unrelenting use of a single mode of action herbicide in agricultural weed control drives genetic ad

153 lity to fast and sensitive detection of this herbicide in the environment.

154 re then conducted to detect traces of Diuron herbicide in water samples by evaluating disturbances in

155 hosate is the most important and widely used herbicide in world agriculture.

156 pionate, cyclohexadione and phenylpyrazoline herbicides in agriculture.

157 uaternary ammonium and phenoxypropionic acid herbicides in fortified river water as well as drinking

158 ionship between phylogeny and sensitivity to herbicides in freshwater diatom species.

159 eous determination of 120 various classes of herbicides in oilseed samples.

160 ermination of chlorinated phenoxyacetic acid herbicides in spiked river water.

161 The research of using DF as a measure of herbicides in the literature was mainly conducted in tim

162 At low doses, increasing the number of herbicides in the mixture tended to select for more gene

163 evidence" of an association with exposure to herbicides in Vietnam War veterans.

164 e silicon chip dedicated to the detection of herbicides in water was fabricated by means of silicon-b

165 sistance to glyphosate, the most widely used herbicides, in several weed species, including common wa

166 usly implicated in increasing herbicide use, herbicide increases were more rapid in non-GE crops.

167 Here, we characterize the herbicide indaziflam as a CBI and provide insight into i

168 nalyses have used flawed metrics to evaluate herbicide intensity and toxicity trends.

169 an association between chlorimuron ethyl, a herbicide introduced in 1986, and lung cancer that has n

170 The popularity of these herbicides is due to their low application rates, high c

171 The high reactivity of the herbicides is largely due to the ethyl or isopropyl grou

172 The purpose of modern industrial herbicides is to control weeds.

173 nverting the sesquiterpene farnesene and the herbicide isoproturon, and its transcript profiles are n

174 The worldwide use of the phenylurea herbicide, isoproturon (IPU), has resulted in considerab

175 chanisms by which weeds evolve resistance to herbicides largely determine the level of resistance and

176 s promise to provide an upsurge of potential herbicide leads.

177 The herbicide linuron is used worldwide, and has been detect

178 stence for the drug carbamazepine, while the herbicide MCPA (2-methyl-4-chloro-phenoxyacetic acid) an

179 esented the potential for degradation of the herbicide MCPA in three horizons of an agricultural soil

180 concentrations than the structurally related herbicide (+)-mecoprop.

181 sgenic soybean plants to the HPPD-inhibiting herbicides mesotrione, isoxaflutole, and tembotrione.

182 thione S-transferase are often implicated in herbicide metabolic resistance.

183 e to enhanced metabolic capacity to detoxify herbicides (metabolic resistance) are a major issue.

184 ticide treatments (control, ethanol vehicle, herbicide mixture, and insecticide mixture) for 14 d to

185 iotic resistance literature and confirm that herbicide mixtures can be very effective for resistance

186 dded to the current repertoire of commercial herbicide MOAs.

187 m inhibitory concentrations (MICs) of single-herbicide modes of action and to pair-wise and three-way

188 Using the herbicides molinate and clomazone as model compounds, we

189 very sensitive to the trivalent forms of the herbicide monosodium methylarsenate [MSMA or MAs(V)] and

190 owth conditions, S. putrefaciens reduced the herbicide MSMA (methylarsenate or MAs(V)) to methylarsen

191 ession in a pathway that is abolished by the herbicide norflurazon.

192 bolic resistance often confers resistance to herbicides of different chemical groups and sites of act

193 26 pesticides (insecticides, fungicides, and herbicides) of different chemical classes.

194 Glyphosate is the most widely used herbicide on a world scale for the last 40 years, for bo

195 entration-dependent inhibition effect of the herbicide on photosynthesis was demonstrated.

196 rbicide pollution and evaluate the effect of herbicides on plant leaves.

197 Measurements of the effects of these herbicides on the kinetics of charge recombination in ph

198 onnel who conducted aerial spray missions of herbicides (Operation Ranch Hand) in Vietnam from 1962 t

199 n the basis of plant SHMT inhibitors from an herbicide optimization program, highly potent inhibitors

200 : 1.3, 3.0)] insecticides and phenoxyacetate herbicides [OR=1.9 (95% CI: 1.2, 2.8)].

201 eneration of agricultural growth regulators, herbicides, or defense compounds.

202 tential application as antimicrobial agents, herbicides, or drugs for porphyric disorders.

203 environmental oxidative stressors, like the herbicide paraquat (PQ), has been linked to the developm

204 method for determination of two bipyridylium herbicides, paraquat and diquat, in cowpeas by UPLC-MS/M

205 hich convey resistance to the broad-spectrum herbicide phosphinothricin (also known as glufosinate) v

206 n the biosynthetic pathway to the commercial herbicide phosphinothricin, uncovered an example of such

207 lant leaves can be potentially used to sense herbicide pollution and evaluate the effect of herbicide

208 ctroactive species by algae, the quantity of herbicides present at trace level in the solution can be

209 o the acetolactate-synthase (ALS) inhibiting herbicide pyroxsulam.

210 Quaternary Ammonium Herbicides (QUATs) are nonselective contact herbicides,

211 Individual insecticides but not herbicides reduced the microbial diversity and richness

212 3- and 4-year rotations managed with the low-herbicide regime as for the conventional-herbicide 2-yea

213 ta from 2008-2015 showed that use of the low-herbicide regime reduced freshwater toxicity loads by 81

214 tation were managed with conventional or low-herbicide regimes.

215 ensitivity of acetyl-CoA carboxylase to nine herbicides representing the three chemical classes was s

216 Targeted herbicide research has created a steady stream of succes

217 with a 35S enhancer tetramer and glufosinate herbicide resistance (BAR) on the mobile Ds-ATag element

218 sess the impact of HR cultivated rice on the herbicide resistance and population structure of weedy r

219 er understand weediness and the evolution of herbicide resistance and to devise new management strate

220 review to current understanding of metabolic herbicide resistance evolution in weedy plant species.

221 Antibiotic and herbicide resistance genes have been used in transgene t

222 oncerns related to the use of antibiotic and herbicide resistance genes in the production of transgen

223 sformation are based on either antibiotic or herbicide resistance genes.

224 Herbicide resistance has also become a major problem, in

225 pport agriculture by reversing pesticide and herbicide resistance in insects and weeds, and control d

226 e now revealing the genes endowing metabolic herbicide resistance in plants.

227 gene amplification conferring field-evolved herbicide resistance in weed populations.

228 Metabolic herbicide resistance in weedy plant species first became

229 Herbicide resistance in wild grasses is widespread in th

230 strates and discuss our findings in terms of herbicide resistance management.

231 he ACETOLACTATE SYNTHASE gene, which confers herbicide resistance to Clearfield rice.

232 k was established linking viral infection to herbicide resistance, transcriptome sequencing showed a

233 Moreover, in an environment of increasing herbicide resistance, with a shortage in new herbicide c

234 riers to advances in understanding metabolic herbicide resistance.

235 genetic background for a quick evolution of herbicide resistance.

236 circumvent the potential risk of antibiotic/herbicide-resistance gene transfer into neighboring plan

237 ce, led us to sequence the transcriptomes of herbicide resistant and susceptible populations of black

238 The use of herbicide-resistant (HR) Clearfield rice (Oryza sativa)

239 wever, the role of gene flow in dispersal of herbicide-resistant alleles among weed populations is po

240 In addition, herbicide-tolerant or herbicide-resistant crop technologies have allowed the u

241 used herbicide, especially in tandem with an herbicide-resistant gene that kills all nonhybrids, faci

242 IC(50) shifts (resistance indices) caused by herbicide-resistant mutations were determined using a re

243 CoA carboxylase have been identified in many herbicide-resistant populations of 42 species of grassy

244 ultural weed, Ipomoea purpurea, we show that herbicide-resistant populations self-fertilise more than

245 by chance and plant families that have more herbicide-resistant species than expected by chance.

246 are overrepresented by introduced, weedy or herbicide-resistant species, and we compared phenotypic

247 Lolium spp., important pasture grasses, yet herbicide-resistant weeds in crops; (3) rice (Oryza sati

248 Since both herbicides respond overlapped oxidation peaks and only g

249 proving LOLbase data were relevant to study herbicide response.

250 e investigated the dissipation of the chiral herbicide S-metolachlor (SM) in soil in relation to its

251 ps and sites of action and can extend to new herbicide(s).

252 t mechanism by which plants adapt to intense herbicide selection and a dramatic example of evolution

253 d sensitive population (WCS for Wayne County herbicide-sensitive) was also used for comparison.

254 ved through a range (blank - 1 microM Diuron herbicide solution) covering the limit of maximum accept

255 riod (1962 to 1971) but were not involved in herbicide spray missions (comparison veterans).

256 adsorbent graphite was conducted of triazine herbicides, substituted anilines, heterocyclic aromatic

257 ntavalent organoarsenicals have been used as herbicides, such as monosodium methylarsonic acid (MSMA)

258 d for the determination of four sulfonylurea herbicides (SUHs): flazasulfuron (FS), prosulfuron (PS),

259 ral crop-weed species as a looming threat to herbicide sustainability and thus world crop production.

260 s are also a source for the discovery of new herbicide target sites that can serve as the focus of tr

261 is a widely applied broad-spectrum systemic herbicide that inhibits competitively the penultimate en

262 ndicates that there are molecular targets of herbicides that can be added to the current repertoire o

263 Non-target-site resistance (NTSR) to herbicides that disrupts agricultural weed control is a

264 azine, and terbuthylazine are chlorotriazine herbicides that have been frequently used in agriculture

265 nhibitory activity of many of the commercial herbicides that target AHAS.

266 s such as vitamin E, as well as tolerance to herbicides that target pathways associated with homogent

267 Applied to mode-of-action analysis of herbicides, the approach showed severe disturbance in th

268 ave allowed the use of existing nonselective herbicides to be extended into crops.

269 se (PAT) that confers host plant glufosinate herbicide tolerance traffics and functions inter-specifi

270 ation of ssODN and CRISPR/Cas9 to develop an herbicide tolerance trait in flax (Linum usitatissimum)

271 ide/xenobiotic-responsive genes and improved herbicide tolerance, thus suggesting an additional role

272 opic expression in the whole plant conferred herbicide tolerance.

273 In addition, herbicide-tolerant or herbicide-resistant crop technolog

274 er of these, being instead linked to reduced herbicide uptake and/or translocation.

275 that we adopt diversity in crop rotation and herbicide use as well as increase the use of nonchemical

276 increased, chronic toxicity associated with herbicide use decreased in two out of six crops, while a

277 Even as herbicide use increased, chronic toxicity associated wit

278 Here, I show that herbicide use intensity increased over the last 25 years

279 Herbicide use is among the most criticized aspects of mo

280 ave been previously implicated in increasing herbicide use, herbicide increases were more rapid in no

281 es glyphosate use but reduces non-glyphosate herbicide use; and adoption of GM insect-resistant crops

282 Isoproturon (IPU) is a phenylurea herbicide used to control broad-leaf grasses on grain fi

283 as the basis for a biosensor for classes of herbicides used extensively for the control of weeds in

284 The biosensor limit of detection for this herbicide was 12 mug L(-1), with a working range of 50-8

285 ectrophotometric determination of glyphosate herbicide was developed.

286 d 4-chloro-2-methylphenoxyacetic acid (MCPA) herbicide was studied using density functional theory (D

287 rd ratio for depression among those who used herbicides was 1.93 (95% confidence interval (CI): 0.95,

288 rage (TWA) concentrations and total loads of herbicides was assessed.

289 phosate use, while the use of non-glyphosate herbicides was likely to induce renal dysfunction and de

290 for several OP pesticides, pyrethroids, and herbicides were either infrequently detected and/or not

291 ith MOAs other than those used by commercial herbicides, which indicates that there are molecular tar

292 between an enzyme and a potent experimental herbicide whose chiral center forms an essential part of

293 Herbicides (QUATs) are nonselective contact herbicides, widely used at weed emergence to protect a w

294 Herbicides with new modes of action (MOAs) are badly nee

295 irectly used natural compounds and synthetic herbicides with new target sites based on the structures

296 toward EDI compared to other pesticides and herbicides with similar structures such as diazinon, hep

297 and 2,4-D (2,4-dichlorophenoxyacetic acid, a herbicide), with reductions of 40%, 49%, and 25%, respec

298 There was a major division in sensitivity to herbicides within the phylogenetic tree.

299 nt glyphosate are among the most widely used herbicides worldwide and may contaminate surface waters.

300 ts increased transcript levels of a suite of herbicide/xenobiotic-responsive genes and improved herbi