Background
15
Fendioxypyracil is a novel protoporphyrinogen oxidase (PPO)–inhibiting herbicide (HRAC 16
Group 14) developed to address the increasing prevalence of herbicide-resistant weeds and 17
to expand available weed control options. PPO inhibitors disrupt chlorophyll biosynthesis by 18
blocking the conversion of protoporphyrinogen IX to protoporphyrin IX, resulting in light-19
promoted formation of reactive oxygen species and rapid plant necrosis. Building on 20
established PPO chemistry, fendioxypyracil incorporates a pyridine-based core and an 21
aryloxy sidechain designed to enhance binding affinity and post-emergence activity. 22
Results
23
Greenhouse evaluations demonstrated high efficacy of fendioxypyracil against key grass 24
weeds, including wild oat (Avena fatua), crabrass (Digitaria Sanginalis), goosegrass 25
(Eleusina indica) and barnyard grass (Echinochloa crus-galli), as well as strong control of 26
major broadleaf species. Physiological characterization and enzyme inhibition assays 27
confirmed PPO as the primary site and mode of action, with IC₅₀ values lower than those of 28
the commercial standard saflufenacil for both PPO isoforms. 29
Conclusion
30
Fendioxypyracil represents a next-generation PPO inhibitor with broad-spectrum and 31
systemic activity, offering a valuable new tool for integrated weed management. Its high 32
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biological activity and efficacy across multiple weed taxa supports its potential to enhance 33
on-farm weed control strategies and contributes to resistance management programs. 34
35
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1. Introduction 36
37
Protoporphyrinogen oxidase (PPO) inhibitor herbicides – classified as Group 14 by the 38
Herbicide Resistance Committee (HRAC) – play a crucial role in modern weed management, 39
providing effective control of broadleaf and some grass weeds across diverse cropping 40
systems. These herbicides are valued for their rapid action, often producing visible 41
symptoms within hours under favorable environmental conditions (1). Their versatility allows 42
for both pre- and post-emergence applications, either as stand-alone products or in tank 43
mixtures, supporting both efficacy and resistance management strategies (2). 44
PPO inhibitors act by targeting two key enzymes in the tetrapyrrole biosynthetic pathway, 45
PPO 1 and 2, which are involved in the synthesis of chlorophyll and heme – two compounds 46
vital for plant survival. Inhibition of these enzymes disrupts the conversion of 47
protoporphyrinogen IX to protoporphyrin IX, leading to the accumulation of toxic 48
intermediates. Under light and aerobic conditions, this results in the strong generation of 49
reactive oxygen species (ROS), causing rapid membrane damage, tissue necrosis, and 50
ultimately plant death (3). 51
Several chemical families fall under PPO inhibitors, including diphenylethers (e.g., 52
fomesafen), N-phenyltriazolinones (e.g., sulfentrazone), and N-phenylimides (e.g., 53
saflufenacil (4)). Despite their structural diversity, these herbicides share a common mode of 54
action (MoA) and are widely used in crops such as soybean, corn, cotton, and cereals. Their 55
high efficacy, rapid symptom development, and relatively short environmental persistence 56
make them attractive for both conventional and conservation tillage systems. 57
Continuous innovation in PPO inhibiting chemistry has led to the discovery of new active 58
ingredients, even decades after the first introduction of nitrofen in 1964. Recent advances 59
include the development of molecules with improved characteristics, such as tiafenacil 60
(launched in 2020) (5). However, the emergence of herbicide resistance and the need for 61
broader-spectrum solutions drive ongoing research in this area (6, 7). 62
In response to these challenges, we introduce fendioxypyracil – provisionally approved by 63
ISO - a novel PPO inhibitor designed for broad-spectrum, post-emergence weed control in 64
major crops. Here, we present details on the discovery and synthesis, MoA confirmation, 65
and greenhouse efficacy of fendioxypyracil, highlighting its value as next-generation tool for 66
sustainable weed management (8). 67
68
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PPO herbicides generally provide strong dicot control both pre- and post-emergence (9). For 69
example, saflufenacil (Kixor®) is an excellent tool for post-emergence conyza control, one of 70
the most difficult dicot weeds to manage (10). Trifludimoxazin (Tirexor®) proved to be 71
exceptionally effective in controlling even PPO-resistant amaranth weeds (11). With the 72
horizon of PPO-tolerant crops in the midterm future and expected, as well as already 73
observed, resistance issues for Glyphosate on grass weeds (12, 13), we aimed to develop a 74
new post-emergence, broad-spectrum PPO herbicide – a crucial tool for future weed 75
management. 76
In the late 1990s, Novartis (now Syngenta) published PPO inhibitor herbicides bearing 77
pyridinone (Scheme 1, 1) as well as pyridine cores (2) (14-16). The pyridine motif was 78
further explored by the newly formed Syngenta company in the early 2000s, resulting in 79
pyrido-oxazinone (Scheme 1, 3) and 3-arylpyridine structures (4) (17-19). None of these 80
structures were commercialized, and the central pyridine motif in PPO structures did not 81
receive further attention until BASF revisited it in 2017 (8). By employing nucleophilic 82
aromatic substitution (SNAr) reactions, diverse nucleophiles can be readily introduced onto 83
the pyridine core. Even complete warheads bearing a nucleophilic nitrogen can be directly 84
attached (20). Besides warheads, sidechains connected via nucleophilic atoms like oxygen 85
can be easily introduced. For PPO herbicides, ether sidechains proved to be highly active, 86
ranging from simple methoxy- or propargyloxy-ethers to lactic acid- and acetal-sidechains (9, 87
21). Another interesting class of ether sidechains includes substituted aryloxy residues. In 88
the early 2000s, Sumitomo described a set of phenoxy-, pyridyloxy-, and pyrimidyloxy-89
sidechains with diverse substitutions in the ortho-, meta-, or para-positions (22, 23). 90
Sumitomo’s work on aryloxy sidechains ultimately led to the PPO market product 91
Epyrifenacil (Rapidicil®) (24), which features a pyridyl-ether sidechain and a phenyl core. 92
Connected through SNAr reactions, the aryloxy side chains are particularly intriguing when 93
combined with the pyridine core. The preferred dihedral angle between the PPO core and 94
the aryloxy side chain is more constrained with a pyridine core compared to a phenyl core 95
(Figure 1). This pyridine core induced preorganization matches the ligand’s dihedral angle in 96
the enzyme pocket more closely, thereby promoting a favorable fit with the targeted binding-97
mode geometry. While, in general, ortho-, meta-, and para-substituted phenoxy as well as 98
pyridyloxy residues show good biological activity in combination with the pyridine core (19), a 99
simple catechol unit elongated by ethyl acetate provided excellent grass and dicot control 100
post-emergence. This led to the invention of compound 5, provisionally approved by ISO as 101
fendioxypyracil, BASF’s next-generation herbicide for post-emergence broad-spectrum weed 102
control (Scheme 1, 5). Here, we present evidence for the high efficacy of fendoxypyracil and 103
the mode and site of action of fendioxypyracil. 104
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105
106
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2. Material and Methods 107
108
2.1 Statistical distribution of dihedral angle in Figure 1 109
The histogram of the statistical distribution of dihedral angles was generated with the 110
software MOE (25). 111
The data were obtained from the Mogul program (CSD 6.00 with CSD Aug25 update) of the 112
CCDC suite (26). 113
The analyzed dihedral angles were C–C–O–C for the phenyl variant and N–C–O–C for the 114
pyridine variant. 115
2.2 Synthetic Method 116
2.2.1 Synthesis of Fendioxypyracil (5) 117
Step (a): 2-azido-6-(2-benzyloxyphenoxy)-5-chloro-3-fluoro-pyridine (7) 118
To a solution of 5.0 g (29 mmol) 3-chloro-2,5,6-trifluoropyridine (CAS 2879-42-7) in 50 mL 119
DMSO was added 2.1 g (33 mmol) NaN3 and the solution was stirred at room temperature 120
for 3 hours. Then 19.5 g (60 mmol) Cs2CO3 was added followed by a solution of 6.2 g (31 121
mmol) 2-(Benzyloxy)phenol) in 40 mL DMSO. The mixture was stirred at room temperature 122
for 16 hours, water (200 mL) was added and the mixture was extracted with ethyl acetate 123
(3*300 mL). The organic layer was separated, washed with brine, dried over anhydrous 124
Na2SO4, filtered and the solvent was removed under reduced pressure. The crude material 125
(15 g) was used without further purifiction in the next step. [M+H] = 371.0; Rt = 1.368 min 126
Step (b): 2-amino-6-(2-benzyloxyphenoxy)-5-chloro-3-fluoro-pyridine 127
To a solution of 15 g of compound 7 in THF (100 mL) was added 9.7 g (150 mmol) zinc and 128
100 mL aq. NH 4Cl dropwised at 0°C. The mixture was stirred for 16 hours at room 129
temperature, filtered and the filter cake was wa shed with ethyl acetate (50 mL). The filtrate 130
was extracted with ethyl acetate (3*200 mL), the combined organic layer was dried over 131
anhydrous Na 2SO4, filtered and the solvent was removed under reduced pressure. The 132
crude material was purified by silica gel column (petrol ether/ethyl acetate) to give 8.8 g 133
(25.6 mmol, 88% from 3-chloro-2,5,6-trifluoropyridine) of 2-amino-6-(2-benzyloxyphenoxy)-5-134
chloro-3-fluoro-pyridine. [M+H] = 345.0; Rt = 1.232 min 135
Step (c): ethyl N-[6-(2-benzyloxyphenoxy)-5-chloro-3-fluoro-2-pyridyl]carbamate (8) 136
To a solution of 8.8 g (25.6 mmol) of 2- amino-6-(2-benzyloxyphenoxy)-5-chloro-3-fluoro-137
pyridine in 80 ml dichloromethane was added 3 g (38 mmol) pyridine followed by 4 g (37.5 138
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mmol) ethyl chloroformate. The mixture was stirred at 25°C for 20 hours, diluted with water 139
and extracted with dichloromethane. The combined organic layer was washed with brine, 140
dried over anhydrous Na 2SO4 and concentrated to give 14.4 g of a mixture of carbamate 8 141
and the di-substituted derivative. The crude mi xture (12.4 g) was dissolved in 200 ml ethanol 142
and aqueous NaOH (1 M) was added dropwise at 0° C with stirring. The mixture was stirred 143
at 15°C for 6 hours, diluted with brine and extracted with ethyl acetate. The combined 144
organic layer was dried over anhydrous Na2SO4, filtered and the solvent was removed under 145
reduced pressure. The crude product was purified by column chromatography on silica 146
(petrol ether/ethyl acetate) to give 6.6 g (15.9 mmol, 62%) of the desired compound 8. [M+H] 147
= 417.1; Rt = 1.293 min 148
Step (d): 3-[6-(2-benzyloxyphenoxy)-5-chloro-3-fluoro-2-pyridyl]- 6-(trifluoromethyl)-1H-149
pyrimidine-2,.4-dione 150
To a solution of 1.7 g (43 mmol) NaH in NMP (60 mL) at 0°C was added 6 g (14 mmol) of 151
compound 8 and the mixture was stirred for 30 minutes at 35°C. Then 3.9 g (21 mmol) of 152
ethyl (E)-3-amino-4,4,4-trifluoro-but-2- enoate (CAS: 372-29-2) was added and the reaction 153
mixture was stirred at 100°C for 3 days. The resulting mixture was quenched with ice water 154
(100mL), acidified to pH=2 by using 6N HCl and extracted with ethyl acetate (3*100mL). The 155
combined organic layer was washed with brine, dried over anhydrous Na 2SO4, concentrated 156
and directly used in the next step. [M+H] = 508.0; Rt = 1.240 min 157
Step (e): 3-[6-(2-benzyloxyphenoxy)-5-chloro-3-fluoro-2-pyridyl]-1-methyl-6-(trifluoromethyl)- 158
pyrimidine-2,4-dione (9) 159
To a solution of 6.5 g (12.8 mmol) of 3-[6-(2-benzyloxyphenoxy)-5-chloro-3-fluoro-2-pyridyl]-160
1-methyl-6-(trifluoromethyl)-pyrimidine-2,.4-dione in 65 mL acetonitrile was added 5.3 g (38 161
mmol) K2CO3 followed by 7.3 g (51 mmol) methy iodide at 0 o C with stirring. The mixture 162
was stirred at 15°C for 16 hours, then water (80 mL) was added, and the pH was adjusted to 163
pH=5 by using 2M HCl. The mixture was extracted with ethyl acetate (3*90mL), the 164
combined organic layer was washed with brine and dried over anhydrous Na 2SO4, filtered 165
and the solvent was removed under reduced pressure yielding 7 g of the crude product 9, 166
which was used without further purification. 167
1H-NMR (CDCl3, ppm): 7.63 (d, J=7.28 Hz, 1 H); 7.21 - 7.25 (m, 4 H); 7.12 - 7.17 (m, 2 H); 168
6.98 (t, J=7.03 Hz, 3 H); 6.26 (s, 1 H); 4.99 (s, 2 H); 3.47 (s, 3 H). [M+H] = 522.0; Rt = 1.323 169
min 170
Step (f): 3-[5-chloro-3-fluoro-6-(2-hydroxyphenox y)-2-pyridyl]-1-methyl-6-(trifluoromethyl) 171
pyrimidine-2,4-dione 172
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To a solution of 7 g (13.4 mmol) of compound 9 in 70 mL xylene was added 3.6 g (26 mmol) 173
solid AlCl 3 at 15°C with stirring. The mixture was stirred at 130 o C for 16 hours and after 174
cooling to 15°C, ice-water (100 mL) was added to the mixture. After separation of the xylene 175
layer, the water phase was extracted with ethyl acetate (3*80 mL), the combined organic 176
layer was dried over anhydrous Na 2SO4, filtered and the solvent was removed under 177
reduced pressure. The crude product was purified by column chromatography on silica gel 178
(petrol ether/ethyl acetate) to give 3.2g (7 .4 mmol, 55%) of 3-[5-chloro-3-fluoro-6-(2-179
hydroxyphenoxy)-2-pyridyl]-1-methyl-6-(trifluoromethyl)-pyrimidine-2,4-dione. 180
1H-NMR (CDCl3, ppm): 7.80 (d, J=7.26 Hz, 1H); 7.03 – 7.19 (m, 3H); 6.93 (dt, J=7.68 Hz, 181
J=1.7 Hz, 1H); 6.3 (s, 1H); 5.6 (s, 1H); 3.5 (s, 3H).[M+H] = 431.9; Rt = 1.077 min 182
Step (g): ethyl 2-[2-[[3-chloro-5-fluoro-6-[3-methyl-2,6-dioxo-4-(trifluoromethyl)pyrimidin-1-yl]-183
2-pyridyl]oxy]phenoxy]acetate, Fendioxypyracil, (5) 184
To a solution of 0.2 g (0.46 mmol) of 3-[5-c hloro-3-fluoro-6-(2-hydroxyphenoxy)-2-pyridyl]-1-185
methyl-6-(trifluoromethyl)-pyrimidine-2,4-dione in 10 mL dry acetonitrile was added 0.19 g 186
(1.3 mmol) K 2CO3 at 0 oC followed by dropwise addition of 0.15 g (0.92 mmol) ethyl 187
bromoacetate. The mixture was stirred at 15° C for 16 hours, diluted with 15 ml water and 188
extracted with ethyl acetate (3*15mL). The combined organic layer was washed with brine, 189
dried over anhydrous Na 2SO4, filtered and the solvent was removed under reduced 190
pressure. The crude product was purified by reversed phase preparative HPLC containing 191
TFA to give 0.16 g (0.31 mmol, 67%) of ethyl 2-[2-[[3-chloro-5-fluoro-6-[3-methyl-2,6-dioxo-192
4-(trifluoromethyl)pyrimidin-1-yl]-2-pyridyl]oxy]phenoxy]acetate (5, Fendioxypyracil). 193
1H-NMR (CDCl3, ppm): 7.76 (d, J=7.28 Hz, 1 H); 7.22 (d, J=7.72 Hz, 1 H); 7.17 (t, J=7.83 194
Hz, 1 H); 6.99 - 7.06 (m, 1 H); 6.88 (d, J=7.94 Hz, 1 H); 6.25 (s, 1 H); 4.49 (s, 2 H); 4.19 (q, 195
J=7.20 Hz, 2 H); 3.47 (s, 3 H); 1.25 (t, J=7.17 Hz, 3 H). [M+H] = 518.0; Rt = 1.217 min 196
197
2.3 Biochemistry test Methods 198
2.3.1 Recombinant Expression, Purification, and In Vitro Inhibition Assays of wild type 199
Amaranthus tuberculatus PPO1 and PPO2 enzymes. 200
The complete coding sequences of wild-type Amaranthus tuberculatus PPO1 and PPO2 201
were synthesized de novo and inserted into the pRSetB expression vector (Invitrogen, 202
Carlsbad, CA, USA) using BamHI and HindIII rest riction sites. To facilitate purification, an N-203
terminal hexahistidine tag was included. Recombinant constructs were transformed into 204
Escherichia coli strain BL21(DE3)pLysS (Novagen, EMD Millipore, Billerica, MA, USA), and 205
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transformants were selected on LB agar plates containing 100 µg mL ⁻ ¹ ampicillin and 34 µg 206
mL⁻ ¹ chloramphenicol. 207
For protein expression, a single colony was inoculated into 3 mL LB medium with antibiotics 208
and incubated at 37 °C with shaking (200 rpm) for 6 h. A 20-µL aliquot of this starter culture 209
was transferred into 20 mL fresh LB medium and grown overnight. The following day, 100 µL 210
of the overnight culture was inoculated into 100 mL ZYM-5052 autoinduction medium 211
supplemented with antibiotics. Cultures were incubated at 37 °C for 5 h and then shifted to 212
25 °C for an additional 21 h. 213
Cells were collected by centrifugation at 6,000 × g for 30 min at 4 °C. Pellets were 214
resuspended in PPO lysis buffer [10 mL g ⁻ ¹ pellet; 50 mM NaH ₂ PO₄ , 100 mM NaCl, 5 mM 215
imidazole, 5% (v/v) glycerol, pH 7.5] supplemented with 20 mg mL ⁻ ¹ lysozyme, 30 U mL ⁻ ¹ 216
DNase I, and protease inhibi tors (complete EDTA-free, Roche Diagnostics, Mannheim, 217
Germany). Suspensions were sonicated on ice (3 min total, 30 s bursts at 90% amplitude). 218
After centrifugation at 38,000 × g for 30 min at 4 °C, the supernatant was collected and 219
supplemented with 2 mL of 5 M NaCl. 220
For affinity purification, a 500-µL bed volume of HisPur Ni-NTA resin (Thermo Fisher 221
Scientific, IL, USA) was equilibrated with buffer (20 mM NaH ₂ PO₄ , 50 mM NaCl, 5 mM 222
imidazole, 5 mM MgCl ₂ , 17% glycerol, 0.1 mM EDTA, pH 8.0). The clarified extract was 223
applied to the resin, which was then washed with 5.6 mL wash buffer (20 mM NaH ₂ PO₄ , 50 224
mM NaCl, 5 mM imidazole, 17% glycerol, pH 7.5). Bound proteins were eluted with 1 mL 225
elution buffer (20 mM NaH ₂ PO₄ , 50 mM NaCl, 250 mM imidazole, 17% glycerol, pH 7.5). 226
Protein concentrations were measured us ing a Scandrop nano volume spectrophotometer 227
(Analytikjena, Life Science, Germany). Purity and solubility were confirmed by SDS–PAGE 228
(10%) with 2.5 µg protein per lane. 229
Enzyme activity assays for PPO1 and PPO2 were performed using a fluorescence-based 230
approach (excitation 405 nm, emission 630 nm). Reactions (187 µL) contained 100 mM 231
Tris–HCl, 1 mM EDTA, 5 mM DTT, 0.0085% Tween 80, and 15 µL enzyme in resuspension 232
buffer (50 mM Tris–HCl, pH 7.3, 3.2 mM EDTA, 20% v/v glycerol). Enzyme concentrations 233
were adjusted for each variant to normalize maximum fluorescence in the absence of 234
inhibitor under saturating substrate conditions. 235
Dose–response assays were carried out with f endioxypyracil and saflufenacil, dissolved in 236
80% DMSO. Ten concentrations (10 µL; 1 × 10 ⁻ /i1 to 5.12 × 10 ⁻ ¹² M) were tested in the 237
assay mixture, with a 30-min pre-incubati on at room temperature before addition of 238
protoporphyrinogen IX. Fluorescence was monitored for 30.25 min (33 cycles of 55 s each) 239
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using a CLARIOstar microplate reader (BMG LabTech, Germany). Percent inhibition was 240
calculated relative to untreated (positive) and no-enzyme (negative) controls. All assays 241
were performed in triplicate. IC ₅₀ values (inhibitor concentrati on reducing PPO activity by 242
50%) were estimated by nonlinear regression usin g three- or four-parameter log-logistic 243
models. 244
2.3.2 Physiological Profile 245
Generation of the physiological profiles were performed exactly as described in Johnen et 246
al., 2022 (27). 247
2.3.2.1 Cell Galium 248
Freely suspended callus from Galium mollugo was heterotrophically cultivated in a modified 249
Murashige-Skoog Medium (4.4g/L M&S basal medium, 30g/L sucrose, 29.7mg/L L-alanine, 250
3.1mg/L L-arginine-monohydrochloride, 3.8mg/L L-asparagine, 1.7mg/L L-aspartic acid, 26 251
mg/L gamma-aminobutyric acid, 3 mg/L L-cysteine, 0.3mg/L L-glutamine, 15.7 mg/L L-252
glutamic acid, 2.7mg glycine, 0.05 mg/L L-histidine-monohydrochloride, 5 mg/L L-leucine, 2 253
mg/L L-lysine hydrochloride, 0.05 mg/L DL-methionine, 0.05 mg/L DL-phenylalanine, 1.9 254
mg/L L-proline, 12.8 mg/L L-serine, 4.1 mg/L DL-threonine, 0.05 mg/L L-tyrosine, 2.3 mg/L 255
DL-valine, 2 mg IAA, 0.1mg 2,4-D). The cells were subcultured in 7-day intervals. For 256
screening, acetone solutions of the test compounds were pipetted into plastic tubes, and the 257
solvent was allowed to evaporate before adding 2 mL of exponentially growing cell 258
suspension. The tubes were shaken at 400 rpm and 25°C in the dark on a rotary shaker with 259
an attachment for 288 test tubes. After incubation for eight days, the conductivity of the 260
growth medium was measured using a micro-electrode (Mettler Toledo FiveEasyPlus with 261
the electrode InoLab-752). The mean of three replicates was determined and subtracted 262
from the value obtained before incubation. The reduction in conductivity is inversely 263
proportional to the increase in growth. Results were expressed as percentage growth 264
inhibition relative to untreated control. 265
2.3.2.2 Algae 266
Cells of Scenedesmus acutus (culture collection Gottingen, 276-3a) were propagated 267
photoautotrophically in aerated culture tubes containing an inorganic medium (1 g/L 268
potassium nitrate, 260 mg/L disodiumhydrogenphosphat dihydrate, 740 mg/L potassium 269
dihydrogen phosphate, 2.55 g/L magnesium sulfate heptahydrate, 25 mg/L calcium chloride 270
hexahydrate, 0.0066 mg/L aluminum sulfate octadecahydrate, 0.099 mg/L manganese 271
chloride tetrahydrate, 0.005 mg/L copper sulfate pentahydrate, 0.028 mg/L cobalt sulfate 272
pentrahydrate, 0.0063 mg/L zinc sulphate heptahydrate, 0.03 mg/L boric acid, 0.002 mg/L 273
ammonium molybdate tetrahydrate, 0.0029 mg/L Ammonium metavanadate, 0.026 mg/L 274
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Nickel(II) sulphate hexahydrate, 0.25 mg/L potassium iodide, 0.24 mg/L potassium bromide, 275
0.0084 mg/L potassium bromide, 14.5 mg/L iron(III) nitrate nonahydrate, 13.3 mg/L 276
Titriplex® III, 0.048 mg/L copper sulfate pentahydrate) and kept at 22°C under continuous 277
light (Thorn white neon tubes, c.90 pmol m-z s-l, 400-750 nm). The bioassay was performed 278
in plastic microtiter dishes (8.5 x 12.5 cm, NUNC) containing 24 wells. Before loading the 279
wells with 1 mL cell suspension each, the test compounds were added in acetone, and the 280
solvent was allowed to evaporate. The 15 additional compartments of the dishes were filled 281
with sodium carbonate/bicarbonate buffer (0.5 ml) generating a 0.25 % partial pressure of 282
carbon dioxide. The dishes were sealed with plastic lids and incubated on a MTS 4 shaker 283
(IKA, Staufen, Germany) at 500 rpm under continuous light (Osram white neon tubes, c.70 284
pmol m-' s-l, 400-750 nm) at 23°C. After 24 h, the contents of each well were removed, 285
diluted and cell numbers were determined by a Coulter Counter (type ZM, Coulter 286
Electronics, Luton, UK). Two replicates were measured, and growth inhibition was calculated 287
as a percentage of the control. 288
2.3.2.3 Lemna 289
For L. paucicostata cultivation and treatments, stock cultures were propagated 290
mixotrophically in an inorganic medium containing 1 % (w/v) sucrose (KNO3 (400 mg/L), 291
CaCl2 * 2 H2O (540 mg/L), MgSO4 * 7 H2O (614 mg/L), KH2PO4 (200 mg/L), Fetrilon 13 % 292
(2,81 mg/L), MnCl2 * 4 H2O (0.415 mg/L), H3BO3 (0.5 mg/L), Na2MoO4 * 2 H2O (0.12 mg/L), 293
ZnSO4 * 7 H2O (0.05 mg/L), CuSO4 * 5 H2O (0.025 mg/L) and CoCl2 (0.025 mg/L). The 294
bioassay was conducted under aseptic conditions in plastic petri dishes (5 cm in diameter), 295
which contained 15 mL medium without sucrose. The test compounds were added to the 296
dishes in acetone solution, and the organic solvent was allowed to volatilize before four 297
fronds were added to each dish (4 leaves per dishes). The culture dishes were then closed 298
with plastic lids and incubated under continuous light (white LED irradiation, 70 µmol m-2 s-1) 299
in a growth chamber at 25°C. Eight days after treatment, the increase of the area covered by 300
the fronds in each dish was determined as the growth parameter using an image analyzing 301
system (LemnaTec Scanalyzer; LemnaTec, Würselen, Germany). The area of fronds before 302
incubation was subtracted from this value. Results were expressed as percentage growth 303
inhibition relative to untreated control. 304
2.3.2.4 Arabidopsis 305
Sterilized seeds (MC24 ecotype) were stratified overnight at 4°C in 48-well plates containing 306
250 µL half-strength Murashige & Skoog incl. Gamborgs B5 Vitamins (Duchefa: 307
M0231.0050; 2,2 g /1 L) containing 2.5 µL of acetone (as solvent control) or 2.5 µL 308
respective compound resulting in the following concentrations 0.001, 0.01 and 0.1 mM. 48-309
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well plates were sealed with micropore tape and grown for 7 d in constant light at 22 °C 75% 310
humidity. Growth inhibition and symptoms were evaluated manually. 311
2.3.2.5 Cress germ. D and Cress germ. L 312
For the germination bioassay, seeds of cress (Lepidum sativum L) were placed in 6-well 313
plates filled with a vermiculite substrate. Stock solutions of the test compounds in acetone 314
were added together with 12 mL of water to reach respective test concentrations. Control 315
seeds were moistened only with water and acetone. The plates were incubated in a growth 316
chamber at 22 °C in the dark for 72 h. Inhibition of germination and seedling development 317
was evaluated visually (0 = no influence, 100 = total inhibition). Afterwards, the dishes were 318
incubated for further 3 days under light conditions (16h/8 h light:dark at 22 °C and 75% 319
relative humidity, 230 µmol m−2 s−1 photon irradiance, 400–750 nm) and seedling 320
development and plant symptoms were evaluated. 321
2.3.2.6 Hill Assay 322
Thylakoids were isolated from shoots of 3 weeks-old plants of Triticum aestivum L, as 323
follows. Plants were put 24 h in dark and subsequent steps were performed under green 324
light. Shoots were cut and homogenized in Hill-Medium (HM) containing 50 mM tricine, 10 325
mM NaCl, 5 mM MgSO4 and 0.4 M sucrose (pH 8.0 adjusted with NaOH) using a mixer. 326
Homogenate was filtered and centrifuged at 500 x g. Pellet was washed with suspension 327
medium (SM) containing 50 mM tricine, 10 mM NaCl and 5 mM MgSO4 (pH 8.0 adjusted 328
with NaOH) once at 500 x g and resuspended in reaction medium (RM) containing 50 mM 329
tricine, 5 mM MgSO4 and 0.1 M sucrose (pH 8.0 adjusted with NaOH). For the Hill assay, 330
isolated thylakoids (chlorophyll content 41 µg ml−1) in reaction medium were used. The 331
influence of the compounds on photosynthetic electron transport in photosystem II was 332
evaluated according to the method of Avron and Shavit (28). Briefly, the assay mixture 333
consisted of thylakoid suspension (0.23 ml), test compound dissolved in 80% aqueous 334
acetone + water (80 + 20 by volume; 0.05 ml), and K-ferricyanide (0.02 ml) with and without 335
compound. During the subsequent illumination, ferrocyanide was formed in the Hill reaction 336
if not inhibited by compound present. Then, in darkness, the ferrocyanide was allowed to 337
react with ferric salt to form the ferrous salt which produced a complex with phenanthroline. 338
The complex was measured photometrically by its absorption at 510 nm. Results were 339
expressed as percent inhibition relative to untreated control and after subtraction of 340
absorbance of the compound itself. 341
2.3.2.7 CO2 assimilation 342
The plants of Galium aparine L, which had been raised under greenhouse conditions to the 343
second-whorl stage, were cultivated in Vermiculite containing pots watered with half 344
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Linsmaier Skoog medium (KNO3 950 mg/L, NH4NO3 825 mg/L, MgSO4*7H2O 185 mg/L, 345
CaCl2*2H2O 219 mg/L, KH2PO4 85 mg/L, Fetrilon 13 % 46.2 mg/L, H3BO3 3 mg/L, 346
MnSO4*H2O 6.8 mg/L, ZnSO4*7H2O 5.3 mg/L, KJ 0.42 mg/L. Na2MoO4*2H2O 0.125 mg/L, 347
CuSO4*5H2O 0.015 mg//L, CoCl2*6H2O 0.015mg/L, pH 5.8) for 5 days in a Phytotron 348
chamber (12h day/ 12h night for 25°C / 22°C, 75% humidity). The plant treatment is a foliar 349
spray application of a compound with the concentration of 10-3M. The measurement of the 350
photosynthetic rate (µmol (CO2) m-2 s-1) to determine the inhibition was accomplished with a 351
LI-COR, LI-6400XT, comparing the untreated Galium plant at timepoint 0h with the same 352
plant 1 day after the compound application (24h). Additionally, epinasty and necrosis 353
symptoms are evaluated visually. Results were expressed as percent inhibition relative to 354
untreated control. 355
2.3.2.8 Respiration 356
Galium mollugo were cultivated as described in Cell Galium (see point 1.1). 3 mL Galium cell 357
suspensions were treated with compound in plastic tubes for 3-5 h in the dark on a rotary 358
shaker. Measurement of oxygen consumption using the dissolved oxygen measuring system 359
Mettler Toledo SevenExcellence. After 30 s of calibration the oxygen consumption (mg/L) in 360
a time frame of 60 s was determined. The resulting consumption was used to calculate the 361
inhibition of oxygen consumption relative to the mock treated control. 362
2.3.2.9 Uncoupler 363
50 mL BY-2 suspension culture cells (7-9 days old) heterotrophically grown in Linsmaier & 364
Skoog medium supplemented with 3 % (w/v) sucrose and 200 µg/L 2,4-D were pelleted by 365
gravity and resuspended in 50 mL suspension buffer (50 mM HEPES, 0.5 mM CaCl2, 0.5 366
mM K2SO4, 10 mM Glucose, pH of 7.0 with KOH). 2 mL of cell suspension was treated with 367
the respective compound in respective concentration in Greiner tubes and incubated for 1.5 368
h at 25°C in the dark while shaking (300 rpm). Cells were washed with suspension buffer. 369
750 µL cell suspension was incubated with 2 µg/µL JC-1 Dye in 24-well plates (Thermo 370
Fisher, T3168) for 15 min in the dark while shaking. JC-1 exhibits potential-dependent 371
accumulation in mitochondria, indicated by a fluorescence emission shift from green to red 372
(29). Fluorescence emission at 590 nm at an excitation at 500 nm was measured using a 373
plate fluorometer. Inhibition value is calculated as follows: fluorescence intensitymock ctrl – 374
fluorescence intensitytest compound /fluorescence intensitymock control – fluorescence intensitypositive 375
ctrl (dinoseb). Samples were measured in duplicates. 376
2.3.2.10 ROS Assay 377
To determine the formation of reactive oxygen species (ROS), Lemna plants grown 7 to 9 378
days according to point 1.3 were treated with respective compounds and mock for 18 h and 379
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then stained with 10 μ M of dihydroethidium (DHE) in 100 μ M of CaCl2, pH 4.75, while 380
shaking for 30 min at room temperature in the dark according to (30). DHE is a superoxide 381
anion specific indicator that is oxidized by ROS to yield fluorescent 2-hydroxyethidium. After 382
soaking in 100 μ M of CaCl2 for 5 min to remove the residual dye, fluorescence of 2-383
hydroxyethidium in Lemna roots was observed using an Olympus BX61 epifluorescence 384
microscope (Hamburg, Germany). ROS formation was evaluated visually (0 = no formation, 385
100 = strong formation). 386
2.3.2.11 Chlorophyll fluo. 387
For L. paucicostata cultivation and treatments, stock cultures were propagated 388
mixotrophically in an inorganic medium containing 1 % (w/v) sucrose (KNO3 (400 mg/L), 389
CaCl2 * 2 H2O (540 mg/L), MgSO4 * 7 H2O (614 mg/L), KH2PO4 (200 mg/L), Fetrilon 13 % 390
(2,81 mg/L), MnCl2 * 4 H2O (0.415 mg/L), H3BO3 (0.5 mg/L), Na2MoO4 * 2 H2O (0.12 mg/L), 391
ZnSO4 * 7 H2O (0.05 mg/L), CuSO4 * 5 H2O (0.025 mg/L) and CoCl2 (0.025 mg/L)). The 392
bioassay was conducted under aseptic conditions, using 15 mL medium without sucrose. 393
The bioassay was performed in plastic microtiter dishes (8.5 x 12.5 cm, NUNC) with 24 394
wells. Loading the wells with 1 mL cell suspension and approx. 12 fronds of Lemna. Effects 395
on chlorophyll fluorescence (fluorescence quantum yield, Y(II)) were measured after 24 h 396
compound treatment using an Imaging Pulse-Amplitude-Modulation (PAM) M-Series system 397
(Walz, Effeltrich, Germany). Measurements were taken after 5 minutes of darkness with the 398
following settings: Meas.light=1, act. Light=2. Results were expressed as percent inhibition 399
relative to untreated control. 400
2.3.2.12 ATP content 401
Growth and treatment were performed according to Chlorophyll fluorescence (point 1.11). 402
ATP content was measured with the ATP Determination Kit (A22066, Thermo Fisher 403
Scientific,Grand Island, NY14072) according to manufacturer’s instructions using 9-12 mg L. 404
paucicostata extract in tricine buffer. Results were expressed as percentage growth 405
inhibition relative to untreated control and fresh weight. 406
2.3.2.13 Neural Network Modeling of Physiological Profiling Data 407
A variational autoencoder was fitted to the results of 14 types of physiological assays for 408
herbicide compounds which were assessed at different concentrations as described in 409
Johnen et al., 2022 (10.1002/ps.7004). Concentrations were treated as different features, 410
resulting in a total of 34 features. Samples per compound/assay/concentration combinations 411
were aggregated by median. The autoencoder was semi-supervised with a classification 412
network attached to the latent samples and learned a latent space with eight dimensions. 413
Multilabel classification was applied to allow for non-mutually exclusive MoA predictions. 414
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Eight classes of modes of action, along with an 'Unknown Mode of Action' class were used 415
as targets. Monte-Carlo dropout was applied in the classification network. The uncertainty 416
resulting from the samples in latent space along with the Monte-Carlo dropout samples of 417
the classification network allowed for assessments of uncertainty of predicted MoA labels. 418
Reference
sample contributions to the cross entropies MoA class were inversely weighted 419
by the number of positive examples over negative examples, for their respective MoA 420
classes. Missing values for input features and labels were imputed with zeros but were 421
masked in the respective loss function terms. The Kullback-Leibler Divergence (KLD) and 422
classification loss terms were balanced using weight parameters in the loss function. The 423
KLD and classification weights were slowly ramped up during training, to help the learning. 424
The test compound fendioxypyracil was part of the test set of unknown mode-of-actions. 425
426
2.4 Herbicidal Test Methods 427
2.4.1 POST- Emergence Greenhouse Trials 428
The active ingredients for the POST-Emergenc e greenhouse trials were selected from the 429
most used PPO inhibitors (HRAC E, 14) in US and Brazil Soy fields: saflufenacil (N-Phenyl-430
imide, manufacturer: BASF), trifludimoxazin (N-Phenyl-imide, BASF), tiafenacil (N-Phenyl-431
imide, Nufarm), Flumioxazin (N-Phenyl-imide, Sumitomo). 432
The key broadleaf weed species and the grass species that were tested in the greenhouse 433
trials are described in Table 1, including the EPPO Codes (former Bayer Codes, European 434
and Mediterranean Plant Protection Organization). All used seeds are an own production in 435
BASF’s Germany site at Limburgerhof. Application was done at BBCH 12/13. 436
The plants were cultivated using standard methods in Limburgerhof soil (slightly loamy sand 437
soil, clay 6,9% dm; loam 16,6% dm; sand 76,5% dm, organic matter (OM) 1,38% dm; pH 438
7,4). The plant pots had a diameter of 9 cm at the broadest point and contained 439
approximately 313 cm3 of soil (standard pot size). Monocot weeds were cultivated directly in 440
the plant pots. Dicot weeds were cultivated in propagation soil (pH 5,6; N 14%, P 2O5 16%, 441
K2O 18%, Fe 0,09%) and transplanted into pots with Limburgerhof soil after emergence. 442
The plants were treated with specific formulated active ingredients at various application 443
rates to evaluate their responses to different dosages. The application was carried out under 444
controlled conditions to facilitate a clear distinction between the active compounds and to 445
manage the various weed species effectively. An initial trial aimed to establish suitable 446
application rates. Given that most of the compounds are UV-dependent, significantly lower 447
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rates were employed in greenhouse trials compared to field rates. For consistency, all PPO 448
inhibitors were applied at a uniform rate (Table 2). 449
The POST-Emergence trial was repeated 4 times in terms of having enough replication for 450
each evaluation of each rate. The application volume was standardized at 200 liters per 451
hectare, with 0.5% methylated seed oil (MSO) used as an adjuvant. All applications were 452
conducted using a flat spray nozzle from the XR Teejet 110015VS series. After treatment, 453
the solvents and water were allowed to evaporate from the plants for 30 minutes in a 454
separate tunnel with an airflow of 3000 m-3 h. Subsequently, the plants were transferred to 455
greenhouses tailored to the required growing conditions. The trials utilized three different 456
greenhouses: a warm house (22-24°C, mean humidity 57%), a cold house (18-21°C, mean 457
humidity 64%), and a cold cabin (12-14°C, mean humidity 83%). Each greenhouse was 458
illuminated with photosynthetically active radiation (PAR; 380 – 780 nm) from 10:00 p.m. to 459
4:00 a.m., in addition to natural daylight. 460
Irrigation for the plants was conducted using specially prepared water that included nutrients 461
tailored to their growth stage, biomass availability, and water needs. The irrigation water was 462
prepared by diluting 1 per mile of the liquid fertilizer "Kamasol brilliant Grün 10-4-7®" in tap 463
water. 464
Plant damage was assessed at 7- and 20-days post-application of the active ingredients. 465
The evaluation involved a visual inspection of the above-ground parts of the plants, with 466
damage quantified as a percentage of Plant Damage Compared to Untreated Control 467
(PDCU) using a scale ranging from 0 to 100, including increments of 2 (0%, 5%, 10%, 15%, 468
…, 90%, 95%, 98%, 100%). A PDCU value of 0% indicated no damage, while 100% 469
indicated complete plant death. For the analysis of the rating data collected, the statistical 470
software R was utilized. The analysis of variance (ANOVA) technique, as outlined by Stahle 471
and Wold in 1989, was employed to identify differences in means. When significant 472
differences were noted in the ANOVA results, the means were categorized into distinct 473
groups following the method described by Scott and Knott, using a significance level (α ) of 474
0.05. The clustering analysis method developed by A. Scott and M. Knott (31) was applied to 475
group the variants into cohesive and homogeneous categories. 476
477
3. Results and discussion 478
479
3.1 Synthesis 480
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Fendioxypyracil can be synthesized starting from 3-chloro-2,5,6-trifluoropyridine (Scheme 2). 481
In a sequential one-pot nucleophilic substitution reaction using sodium azide followed by 2-482
(benzyloxy)phenol, the respective aryl-ether azide is formed. Reduction of the azide to the 483
amine using zinc and subsequent reaction with ethyl chloroformate generates the respective 484
carbamate building block 8. From the carbamate the uracil ring is constructed by employing 485
ethyl 3-amino-trifluorobutenoate followed by N-methylation. Deprotection of the benzyl-group 486
and alkylation with ethyl bromoacetate provides then fendioxypyracil (5) with very good 487
yields. 488
489
3.2 Physiological profiling of fendioxypyracil indicates inhibition of PPOs as MoA 490
Physiological profiling for the identification of herbicidal modes of action has been 491
successfully used and refined for decades (30, (27, 32). The MoA identification is based on 492
the generation of an inhibition fingerprint from an array of different assays that also includes 493
the assessment of the compound-induced symptoms. To identify its mode of action, we 494
generated a physiological profile (P-Profile) for fendioxypyracil (Fig 2A). Fendioxypyracil 495
induced rapid necrosis and led to substantial inhibition in plant tissues that were incubated in 496
light, as observed in Lemna paucicostata, algae and cress seedlings. In addition, the 497
germination and growth of light incubated Arabidopsis thaliana seedlings was strongly 498
inhibited by fendioxypyracil. In contrast, heterotrophically, dark grown Galium cell 499
suspensions were only affected at high concentrations and cress germination in darkness 500
was only mildly inhibited. Carbon dioxide (CO2) assimilation in Galium plants was strongly 501
inhibited by fendioxypyracil. In contrast, fendioxypyracil only slightly affected the Hill reaction 502
and the chlorophyll fluorescence assay, which uses the quantum yield (Y(II)), as an indicator 503
for how much absorbed light energy is used for photochemical reactions in photosystem II 504
(PSII). The above-described results show that even though the overall photosynthesis is 505
affected by fendioxypyracil, it is not based on the direct inhibition of the PSII but it is light 506
dependent. No or only mild effects were observed in the respiration assay as measured 507
through oxygen consumption in heterotrophic Galium cell suspensions and on mitochondrial 508
membrane potentials in Lemna roots. Fendioxypyracil treatment led to rapid necrosis, 509
chlorosis and inhibition of root growth in Lemna; necrosis and inhibition of root growth in the 510
cress germination assay and in Galium plants used for the analysis of CO2 accumulation. 511
To identify the mode of action, we analyzed the P-Profile result by application of a semi-512
supervised variational autoencoder model. The effects of the test compound fendioxypyracil 513
were investigated first by exploration of the learned latent space and second by calculated 514
probabilities for nine target classes (eight known modes of action and ‘Unknown Mode of 515
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Action’) in the multilabel classification prediction. The latent space which has been learned 516
over results derived from a diversity of herbicides including commercially-relevant reference 517
herbicides listed and classified by the herbicide resistance action committee (based on 518
herbicides listed on the HRAC poster 2024 (33), is shown in Figure 2B (latent space). The 519
eight dimensions of the learned latent space have been reduced to two dimensions by 520
UMAP (Uniform Manifold Approximation and Projection) for visualization purpose. 521
Fendioxypyracil (treated as test compound in the model prediction) aligns within a cluster of 522
established PPO inhibitors, saflufenacil, trifludimoxazin, epyrifenacil and tiafenacil (Figure 523
2B, latent space) (4) . The calculated probabilities for eight different known MoA classes and 524
‘Unknown Mode of Action’ modeled are shown in Fig. 2C (probabilities) and in Table 3 and 525
indicate a probability of over 99% for the MoA PPO inhibition and a very low probability of all 526
other target classes. The very low uncertainty of the prediction as modeled by Monte Carlo 527
dropout and displayed by the spread of the probabilities in Fig. 2C (probabilities) indicates a 528
high reliability of the prediction results. Both the location of fendioxypyracil within the latent 529
space (Figure 2B, latent space) as well as the calculated probabilities of the classification 530
model (Fig. 2C, Table 3, probabilities) indicated PPO inhibition as MoA. 531
For the known PPO inhibitor saflufenacil a P-Profile was already reported by Grossmann et 532
al., 2010 (4) albeit in a slightly refined setup as exploited here. Nevertheless, the inhibitory 533
effects and symptoms in the P-Profile of saflufenacil (i.e. light dependent inhibitory effects on 534
photosynthesis without affecting the PSII and induction of necrotic symptoms, 535
https://doi.org/10.1614/WS-D-09-00004.1) are resembling the profile of fendioxypyracil. 536
Furthermore, we generated profiles with saflufenacil, trifludimoxazin, epyrifenacil and 537
tiafenacil identified in the PPO cluster (Fig. 2B) in the current P-Profile setup and to compare 538
the profiles to that induced by fendioxypyracil. The inhibition profile and the observed 539
symptomology induced by fendioxypyracil were highly similar to those of saflufenacil, 540
trifludimoxazin, epyrifenacil and tiafenacil (Fig 2A, D-G) corroborating the outcome of the 541
classification model. Collectively, these analyses indicated that the MoA of fendioxypyracil is 542
based on the inhibition of PPOs in planta. 543
544
4.2 Fendioxypyracil inhibits both the Amaranth tuberculatus PPO1 and PPO2 wild 545
type enzymes in vitro 546
547
Enzyme inhibition assays confirmed that both PPO1 and PPO2 from A. tuberculatus are 548
strongly inhibited by fendioxypyracil and the benchmark compound saflufenacil, as well-549
characterized PPO inhibitor (34) (Table 4). For PPO1, fendioxypyracil displayed an IC ₅₀ of 550
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195 nM, whereas saflufenacil was less potent, with an IC ₅₀ of 412 nM. This indicates that 551
fendioxypyracil requires roughly half the concentration of saflufenacil to achieve comparable 552
inhibition of PPO1 activity. A more pronounc ed difference was observed with PPO2, where 553
fendioxypyracil exhibited an IC ₅₀ of only 2.8 nM compared with 11 nM for saflufenacil. Thus, 554
fendioxypyracil inhibited PPO2 with approx imately four-fold greater potency than the 555
benchmark herbicide. At a saturating concentra tion of 10 µM, both compounds fully inhibited 556
PPO1 and PPO2 activity, resulting in 100% loss of enzymatic activity. Taken together, these 557
Results
demonstrate that fendioxypyracil is a highly effective inhibitor of both PPO isoforms in 558
vitro. While saflufenacil confirmed its expected inhibitory activity, fendioxypyracil consistently 559
showed stronger potency, particularly against PPO2, highlighting its potential as a powerful 560
PPO-targeting herbicide. 561
562
4.3 Weed performance of Fendioxypyracil in Post-emergence application in the 563
greenhouse and confirmation in field trials 564
565
The post-emergence greenhouse trials demonstrated that fendioxypyracil is highly effective 566
against a broad spectrum of weed species, including both grasses and broadleaf weeds. At 567
a rate of 16 g active ingredient per hectare, fendioxypyracil controlled more than 80 weed 568
species, as shown in Table 5 (fig 4 and 5). This broad activity was confirmed in multiple field 569
trials, highlighting its robust performance under practical conditions (fig 7). 570
A key finding is fendioxypyracil’s exceptional control of grass weeds—such as wild oat, 571
barnyard grass, crabgrass, and goosegrass—by foliar application in greenhouse pot tests 572
(fig 5 and 6). This level of grass control is unique among PPO inhibitors, which typically 573
show limited efficacy against grasses. In comparative trials in the greenhouse, 574
fendioxypyracil was tested alongside other PPO-inhibiting herbicides (saflufenacil, 575
trifludimoxazin, flumioxazin, tiafenacil), all applied at identical rates and with the same 576
adjuvant. The results showed that all PPO inhibitors provided strong control of broadleaf 577
weeds, with minimal differences in efficacy (Figure 4). However, fendioxypyracil stood out for 578
its consistently high efficacy, even at the lowest tested dose of 1 g ai/ha on the greenhouse, 579
and for its flat dose-response curve, indicating reliable performance across a range of 580
application rates. Fendioxypyracil achieved high average control of broadleaf weeds, 581
matching or exceeding the performance of other PPO inhibitors. Specific weeds such as 582
Amaranthus palmeri (AMAPA), Bidens pilosa (BIDPI), Capsella bursa-pastoris (CAPBP), 583
and Kochia scoparia (KCHSC) were effectively controlled (fig 4). 584
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Fendioxypyracil provided superior control of both cold-season grasses (e.g., Avena fatua, 585
AVEFA) and warm-season grasses (e.g., Digitaria sanguinalis, DIGSA; Eleusine indica, 586
ELEIN) compared to other PPO inhibitors. Notably, only tiafenacil approached similar levels 587
of grass control, but fendioxypyracil maintained a steadier response rate and higher overall 588
efficacy (Figure 5). 589
Fendioxypyracil has demonstrated outstanding efficacy in global field trials. Field data 590
showed (fig 7) that fendioxypyracil achieves rapid and thorough weed control at low use 591
rates (25 g ai/ha) in pre-plant burndown applications, outperforming other PPO inhibitors, 592
especially in grass weed management (ECHCG and Setaria species, SETSS). In the US, 593
fendioxypyracil delivered near-complete control of AMAPA a major driver of herbicide 594
resistance issues. These results position fendioxypyracil as a valuable tool for sustainable 595
weed management in major cropping systems, offering growers a new solution for pre-plant 596
burndown and resistance management strategies. 597
In summary, fendioxypyracil offers outstanding post-emergence weed control, particularly for 598
grass species a significant advancement for PPO-inhibiting herbicides. Its broad-spectrum 599
activity, reliable efficacy at low dose rates, and unique strength against grasses makes it a 600
valuable tool for sustainable weed management in major crops. 601
602
4. Conclusion 603
Fendioxypyracil is a novel PPO-inhibiting foliar herbicide with strong PPO target inhibition, 604
offering broad spectrum weed control (grass and broadleaf weeds) at low use rates. These 605
key attributes will make fendioxypyracil a useful (effective?) preplant burndown herbicide for 606
broad acre crops such as soybeans and corn. Future PPO inhibitor tolerant crops will enable 607
over-the-top applications of fendioxypyracil, thereby broadening its use in future weed 608
management programs. Fendioxypyracil is being developed in many key agricultural 609
countries such as USA, Brazil and Argentina. It is expected to be commercially available in 610
the first countries around the end-2020s, contributing to global food production in the 611
midterm future. Resistance testing is in progress and aims to assess fendioxypyracil activity 612
against PPO-resistant weed populations target site mutant PPO enzymes, and a 613
comprehensive evaluation of resistance mechanisms and management implications will be 614
the objective of a subsequent study. 615
616
5. Acknowledgements 617
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We would like to thank Susanne Knauer, Misha Manuchehri Byrd, Simone Huber, Sarina 618
Rühm und Stefanie Zimmermann for the experimental support. This research did not receive 619
any specific grant from funding agencies in the public, commercial, or not-for-profit sectors. 620
621
6. Conflict of Interest 622
Authors affiliated with BASF have contributed to the planning and implementation of 623
research activities. 624
625
626
627
628
629
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631
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7. Tables 632
Table 1: Investigated monocotic weeds and dicot weeds of the Post-Emergence Trial 633
EPPO Code Scientific name English name Authority
ABUTH Abutilon theophrasti velvet leaf Medicus
AMAPA Amaranthus palmeri palmer amaranth Watson
AMARE Amaranthus retroflexus redroot pigweed Linnaeus
AMATA Amaranthus x tamariscinus tall amaranth Nuttall
AMBEL Ambrosia artemisiifolia common ragweed Linnaeus
BIDPI Bidens pilosa hairy beggarticks Linnaeus
CAPBP Capsella bursa-pastoris shepherd's purse (Linnaeus) Medicus
CHEAL Chenopodium album common lambsquarters Linnaeus
COMBE Commelina benghalensis Bengal day flower Linnaeus
EPHHL Euphorbia heterophylla wild poinsettia Linnaeus
ERICA Erigeron canadensis Canadian horseweed Linnaeus
GALAP Galium aparine cleavers Linnaeus
IPOHE Ipomoea hederacea morning glory Jacquin
KCHSC Kochia scoparia kochia (Linnaeus) Schrader
MATCH Matricaria chamomilla wild chamomile Linnaeus
PAPRH Papaver rhoeas common poppy Linnaeus
RAPRA Raphanus raphanistrum wild radish Linnaeus
SEBEX Sesbania herbacea coffeebean (Miller) McVaugh
SIDRH Sida rhombifolia common sida Linnaeus
SOLNI Solanum nigrum black nightshade Linnaeus
XANST Xanthium strumarium common cocklebur Linnaeus
ALOMY Alopecurus myosuroides blackgrass Hudson
AVEFA Avena fatua wild oat Linnaeus
BRARU Brachiaria decumbens Surinam grass Stapf
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Internal
BROST Bromus sterilis poverty brome Linnaeus
CYPIR Cyperus iria rice flatsedge Linnaeus
DIGSA Digitaria sanguinalis crabgrass (Linnaeus) Scopoli
ECHCG Echinochloa crus-galli barnyard grass (Linnaeus) Palisot de
Beauvois
ECHCO Echinochloa colonum small barnyard grass (Linnaeus) Link
ELEIN Eleusine indica goosegrass (Linnaeus) Gärtner
ERBVI Eriochloa villosa woolly cupgrass (Thunberg) Kunth
LEFFA Leptochloa fusca subsp.
fascicularis
bearded sprangletop (Lamarck) Snow
LOLMU Lolium multiflorum Italian ryegrass Lamarck
LOLPE Lolium perenne English ryegrass Linnaeus
PANDI Panicum dichotomiflorum fall panicum Michaux
SETFA Setaria faberi giant foxtail Herrmann
SETIT Setaria italica foxtail millet (Linnaeus) Palisot de
Beauvois
SETVE Setaria verticillate bristly foxtail (Linnaeus) Palisot de
Beauvois
SETVI Setaria viridis green foxtail (Linnaeus) Palisot de
Beauvois
SORHA Sorghum halepense Johnson grass (Linnaeus) Persoon
* from EPPO Global Database: https://gd.eppo.int/ 634
635
636
637
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Internal
638
Table 2. Application conditions for active ingredients in the Post-Emergence Trial. All actives 639
were applied with 1% MSO (Lecitech) as adjuvant and a water volume of 200 L/ha 640
Active Ingredient Formulation* Rate (g ai ha-1)
Water Control
Saflufenacil 342 g L-1 SC 8 4 2 1
Trifludimoxazin 500 g L-1 SC 8 4 2 1
Flumioxazin 51% WG 8 4 2 1
Tiafenacil 50 g L-1 ME 8 4 2 1
Fendioxypyracil 342 g L-1 SC 8 4 2 1
*SC: Suspension concentrate, WG: Water dispersible granules, ME: Microemulsion, SL: 641
Soluble liquid concentrate, g ai ha-1: gram active ingredient per hectare 642
643
644
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Internal
Table 3. Calculated probabilities computed by a multilabel classification network including 645
nine target classes reveal PPO as the most likely MoA of fendioxypyracil and a very low 646
probability for other modes-of-action target classes. 647
648
Target class Probability
ACCase 0.00000
ALS 0.00001
Auxin Mimics 0.00000
HPPD 0.00000
Microtubule Assembly 0.00000
PPO 0.99995
Photosynthesis 0.00005
Unknown Mode of Action 0.00000
VLCFA Synthesis (Elongase) 0.00000
649
650
651
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Internal
Table 4. In vitro inhibition of Amaranthus tuberculatus PPO1 and PPO2 wild-type enzymes 652
by fendioxypyracil and the benchmark herbicide saflufenacil. 653
IC₅₀ values (nM) represent the herbicide concentration required to reduce enzyme activity by 654
50%, as estimated from nonlinear regressi on of dose–response curves. Saflufenacil was 655
included as a reference compound. % inhibition values were determined at a saturating 656
concentration of 10 µM, at which both enzymes were fully inhibited. Each value is an 657
average of three replications (P < 0.0001). 658
659
660
661
662
PPO
isoform
Enzyme
backbone
Fendioxypyracil
IC50[nM]
P<0.0001
Saflufenacil
IC50[nM]
P<0.0001
Fendioxypyracil
% Inhibition
at saturation
Saflufenacil
% Inhibition
at saturation
PPO1 AMATU 195 412 100 100
PPO2 AMATU 2.8 11 100 100
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Table 5 Examples of weeds controlled by fendioxypyracil in Greenhouse at 16 g/ha 663
Weed Type
Broadleaf weeds Abutilon theo phra s ti, Amar anthu s pal m e r i , Amaran thu s re t r ofl ex us,
Amaran thu s x tama r i sci nu s , A m bro sia artem i s ii fo lia, Bi den s pilo sa,
Cap sell a bursa -pa st ori s , Cen taur ea c yanu s, Che nop odium a lbum, C ir sium
arven se, Comm elina b enghal en s i s , Co nv olvu lus arven si s, Euphorbia
hete rophyll a, Eri oc hloa v illo sa, E r ig e ron ca naden si s, G a lium a pa rine,
G e ra nium dis se ctum, Gera nium pus i l lum, Ipo moea h ed e r a cea , Ipomo ea
lac unose , Koch ia scopa ria , La mium ampl exic aule, Lami um purpur eum,
Matr i ca ria chamomi lla, M a tric aria ino dora , O ry z a ru fipog on , Pa nicum
dicho t omi fl or u m, Panic um mil iace um, P a pa ver rho ea s, Phy s a li s ixoc arpa ,
Polyg onum c onvolv ulus, Por t u laca ol erac ea, P ortul ac a ol e r a cea s ub sp .
s a t iv a, Ra pha nu s rapha nis trum, S al sola k al i s u b s p . ruth eni ca, S e sbania
herbac e a, Si da rh ombifoli a, Si napi s al ba , Sina pis arven si s , Sola n um
nigrum, S onchus ole ra ceu s, St ell ari a medi a, Ta r a xac um of fici nale , T hla spi
arven se, Ver onic a pe rsica , Viol a arven si s, Xanthium s trumarium
Grasses Agro s ti s s tol o nif era , Alopec u ru s m yosu r o ides, A p e r a s p ica -v enti, Avena
fatu a, Br ac hiaria de cumbe n s , B rac hiari a plantagi n ea, Br omus in ermi s,
B r om us st e r i li s, C y p e r us es c u le nt us , Cy pe r us i r i a , D i g it a r i a s an g u i n al is ,
Echi nochlo a cru s-galli , Ech inochl oa c olon um, El eusin e indi ca, E r i ochl oa
vill os a, Is c h aemum r ug o s um , Lep toc hloa c hinensi s , Le ptochl oa fu s c a
s ub sp . fa sc icula r is , L eptochl o a muc r ona te , Lol ium multiflo rum, Lolium
perenn e, O ryza ru fipogon, Panic um dic h otomifl orum, P a nicum miliac eum,
Pa spalum n o t a t u m , Phal a r i s c anari en si s, Poa annu a, Ro t tbo el lia
coc hinch inen si s , Se taria fa b er i , Se tar ia it alic a, Se ta r i a ver tic illa te, Se tar ia
viridis, S o r g hum hale p en s e
664
665
666
667
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28
Internal
8. Schemes and Figures 668
669
670
1
34
2
5
Novartis 1999
Syngenta 2001 Syngenta 2004
BASF 2017
Fendioxypyracil 671
Scheme 1: Discovery of PPO herbicide structures with a central pyridine core 672
673
674
675
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Internal
5
a b,c d,e f,g
67 8 9
676
Scheme 2: Fendioxypyracil synthesis: (a) i) NaN3, ii) 2-(Benzyloxy)phenol; (b) Zn, NH4Cl; 677
(c) ethyl chloroformate; (d) ethyl (E)-3-amino-4,4,4-trifluoro-but-2-enoate; (e) MeI; (f) AlCl3; 678
(g) ethyl bromoacetate. 679
680
681
682
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30
683
Figure 1: Histograms of the dihedral angle distributions for the phenyl-core (left) and 684
pyridine-core (right) variants. The 3D structures, which correspond to the conformations 685
observed in the protein binding pocket, are shown in stick representation. Carbon atoms are 686
colored white, nitrogen blue, oxygen red, chlorine dark green, and fluorine light green. The 687
angles shown in the histograms are indicated in the structures by black arrows. 0° (magenta 688
line in the histograms) means the C–C–O–C (phenyl) or N–C–O–C (pyridine) atoms lie in the 689
same plane (shown as magenta plane in the 3D structures). 690
691
692
693
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31
694
Figure 2: (A, D-G) (A) Physiological profiles of fendioxypyracil, saflufenacil, trifludimoxazin, 695
epyrifenacil and tiafenacil. Effect of respective compounds on heterotrophic Gallium mollugo 696
cell suspensions, green algae Scenedesmus obliquus, Lemna paucicostata plants, 697
Arabidopsis thaliana seedling morphology, germination of cress (Lepidium sativum L.) under 698
dark/light conditions, the Hill reaction in isolated Triticum aestivum chloroplasts, CO2 699
assimilation in G. mollugo plants, oxygen consumption (respiration) in heterotrophic G. 700
mollugo cell suspensions, uncoupler activity and accumulation of reactive oxygen species 701
(ROS) in L. paucicostata root tissue, chlorophyll fluorescence, and ATP content are shown. 702
Uncoupler activity and ROS accumulation are shown as effect compared with control, while 703
values of all other assays are expressed as percentage of inhibition. Letters indicate 704
physiological symptoms observed: rapid necrosis (NR), necrosis (N), root growth inhibition 705
(I), chlorosis (C) and inhibition of germination (K) (B) Latent Space learned by a variational 706
autoencoder model using P-Profile results generated for a diversity of herbicides. 707
Dimensional reduction of the latent space has been performed by UMAP. Pesticides with 708
unknown target class are shown in light grey along pesticides with known target classes, 709
highlighted in red for known PPO (protoporphyrinogen oxidase) inhibitors, namely 710
saflufenacil, trifludimoxazin, epyrifenacil and tiafenacil, and in dark grey for eight additional 711
Reference
target classes detailed in C. The test compound fendioxypyracil is displayed as 712
light grey dot with a black border. Fendioxypyracil aligns with known PPO inhibitors in the 713
latent space (C) Calculated probabilities (y axis) computed by a multilabel classification 714
network including nine target classes (x axis). Prediction uncertainty has been assessed by 715
Monte Carlo dropout and is shown as spread (y axis). 716
717
718
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32
719
Figure 3. Dose–response curves showing percent inhibition of (left) PPO1 and (right) PPO2 720
by fendioxypyracil (red circles) and Saflufenacil (green triangles). Enzymatic activity was 721
measured across a range of inhibitor concentrations (0.001–100,000 nM), and percent 722
inhibition was calculated relative to the activity of enzyme with no herbicide (positive control). 723
Data points represent mean values from three replications, and curves were fitted using a 724
four-parameter logistic model to estimate IC₅₀ values (Table 4). 725
726
727
728
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33
729
730
Figure 4: Broadleaf weed (BLW) control in greenhouse. Represented is the BLW average 731
control as well as activity against specific BLW, such as AMAPA, BIDPI, CAPBP, KCHSC. 732
The assessment was done 20 days after treatment 733
734
735
736
0
10
20
30
40
50
60
70
80
90
10 0
12 48 12 48 12 48 12 48 12 48
[ g a i/ h a] [ g a i/ h a] [ g ai/ h a] [ g ai/ h a] [ g ai/ h a]
F e ndi ox y py r ac il Ti af e na c il T r if l ud imo x az in S af l uf e na ci l F lu mi ox az in BL W me an AMA PA BI D P I CAP B P KC HS C
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34
737
738
Figure 5: Grass control after greenhouse application. Represented is the mean grass control 739
as well as activity against AVEFA as cold season grass, DIGSA, ELEIN and ECHCG as 740
warm season grasses. The assessment was done 20 days after treatment. 741
742
743
744
0
10
20
30
40
50
60
70
80
90
10 0
12 48 12 48 12 48 12 48 12 48
[ g a i/ h a] [ g a i/ h a] [ g ai/ h a] [ g ai/ h a] [ g ai/ h a]
F e ndi ox y py r ac il Ti af e na c il T r if l ud imo x az in S af l uf e na ci l F lu mi ox az in gras s mean AVE FA DI GS A EL EIN ECH CG
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35
745
746
Figure 6: Grass activity in glasshouse pot trial. Post-emergence application on wild oat, 747
crabgrass and goosegrass. Comparison of fendioxypyracil, saflufenacil and flumioxazin. 748
Spray volume 200 L/ha with 0.5 % MSO, 20 Days after treatment 749
750
751
752
753
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36
754
755
Figure 7: Field Trials in Seymour, IL, USA. Pre-Plant Burndown application, using 200 l/ha 756
with 0,5 % MSO and 1 % AMS. 9 days after application. Control of AMASS, ECHCG and 757
SETSS 758
759
760
761
762
763
764
765
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37
Internal
766
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