organic compounds
3,5,6-Trichloropyridin-2-ol
aDepartment of Environmental Toxicology, Southern University and A&M College, Baton Rouge, Louisiana 70813, USA, bDepartment of Comparative Biomedical Sciences, School of Veterinary Medicine, Louisiana State University, Baton Rouge, Louisiana 70810, USA, and cDepartment of Chemistry, Louisiana State University, Baton Rouge, LA 70803, USA
*Correspondence e-mail: rao_uppu@subr.edu
The title compound, C5H2Cl3NO, is almost planar. In the crystal, the molecules form centrosymmetric hydrogen-bonded dimers through pairwise O—H⋯N interactions to generate R22(8) loops.
Keywords: crystal structure; chlorpyrifos; triclopyr derivatives.
CCDC reference: 2403937
Structure description
3,5,6-Trichloro-2-pyridinol (TCP, C5H2Cl3NO) is the primary degradation product of chlorpyrifos (CPP, C9H11Cl3NO3PS) and chlorpyrifos-methyl (CPFM, C7H7Cl3NO3PS), two of the most widely used organophosphate insecticides in agriculture (Bouchard et al., 2011). TCP has been shown to intensify the toxic effects of CPF(M), leading to endocrine disruption, cellular toxicity, and organ damage (Gao et al., 2021; Li et al., 2020). It enhances the impact of CPF(M) on testosterone synthesis and Sertoli cell function by inhibiting testosterone binding to androgen receptors, furthering hormonal disruption through pathways involving luteinizing hormone and signaling molecules such as CREB and Star, essential for testosterone production. TCP also downregulates genes critical for spermatogenesis, posing potential risks to male fertility (Mansukhani et al., 2024). Molecular modeling indicates that TCP interacts with sex-hormone-binding globulin, potentially aggravating hormonal imbalances (Hazarika et al., 2019).
Beyond endocrine effects, TCP exhibits direct cytotoxicity (Gao et al., 2021) and may bind to DNA in a groove-binding manner similar to Hoechst, possibly favoring specific base-pair regions without significantly distorting the DNA structure (Bailly et al., 1993; Bucevičius et al., 2018; Kashanian et al., 2012). Studies have demonstrated substantial cellular damage in human embryonic kidney cells (HEK 293) following TCP exposure, signaling a risk of kidney toxicity (Van Emon et al., 2018). TCP is further linked to hepatotoxicity and nephrotoxicity in animal models, where it accumulates in vital organs and may cause structural and functional damage (Deng et al., 2016). Additionally, age-dependent sensitivity to TCP has been observed, with pre-weanling rats displaying heightened vulnerability due to pharmacokinetic differences (Timchalk et al., 2002).
TCP is notable for its long half-life in soil, ranging from 65 to 360 days depending on environmental conditions, and its high solubility in water (80.9 mg l−1), facilitating contamination of surface and groundwater (Zhao et al., 2017; Timchalk et al., 2002). This persistence raises substantial concerns about bioaccumulation, biomagnification, and ecosystem disruption, especially in aquatic environments where TCP has been found to be toxic to organisms (Echeverri-Jaramillo et al., 2020; Van Emon et al., 2018). TCP levels in human urine serve as biomarkers for CPF(M) exposure, aiding in occupational and environmental exposure assessments (Bouchard et al., 2011).
In the United States, the EPA revoked all food-related uses of CPF(M) in 2021, effectively banning its use on crops intended for human consumption; however, a November 2023 court ruling temporarily reinstated CPF(M) tolerances while the EPA reconsiders its decision (EPA, 2023). In the European Union, both CPF and CPFM were banned in 2020, with strict limits on residue levels in food (EFSA, 2020). As of 2024, CPF(M) remains restricted for non-food uses in some areas, with existing stocks allowed under controlled conditions, though further bans and stricter regulations are anticipated. While these restrictions are in place, it is important to note that TCP can also result from the soil and microbial degradation of triclopyr, triclopyr butoxyethyl ester and triclopyr triethylamine salt, three commonly used pyridine-based herbicides for managing woody plants, vines, and broadleaf weeds (Cessna et al., 2002; Deng et al., 2016; Dias et al., 2017). The primary concern with these herbicides is non-target toxicity.
Given its widespread relevance to human and animal health, and to support the identification of potential molecular targets in biological systems, we have investigated the P21/c with one molecule in the (Fig. 1). The molecule is close to planar, with the six atoms of the pyridine ring lying a mean of 0.007 Å from their best plane. The Cl atoms lie out of this plane by an average of 0.058 Å, and the O atom lies 0.0430 (14) Å out of plane. The C—N distances are 1.3343 (11) and 1.3347 (11) Å, the C—Cl distances fall in the range 1.7189 (8)–1.7202 (8) Å and the C—O distance is 1.3207 (11) Å. In the crystal, the molecules form centrosymmetric hydrogen-bonded dimers through pairwise O—H⋯N interactions (Table 1) to generate R22(8) loops. No other directional interactions could be identified. The hydrogen-bonded dimer is shown in Fig. 2, and the is illustrated in Fig. 3.
of TCP: it crystallizes in the monoclincSynthesis and crystallization
3,5,6-Trichloro-2-pyridinol, C5H2Cl3NO (CAS 6515–38-4) was obtained from AmBeed (Arlington Heights, Illinios, USA) and was used without further purification. Crystals in the form of colorless laths were prepared by slow cooling of a nearly of the title compound in boiling deionized water (resistance ca. 18 MΏ cm−1).
Refinement
Crystal data, data collection and structure .
details are summarized in Table 2Structural data
CCDC reference: 2403937
https://doi.org/10.1107/S241431462401126X/hb4494sup1.cif
contains datablock I. DOI:Structure factors: contains datablock I. DOI: https://doi.org/10.1107/S241431462401126X/hb4494Isup2.hkl
Supporting information file. DOI: https://doi.org/10.1107/S241431462401126X/hb4494Isup3.cml
C5H2Cl3NO | F(000) = 392 |
Mr = 198.43 | Dx = 1.928 Mg m−3 |
Monoclinic, P21/c | Ag Kα radiation, λ = 0.56086 Å |
a = 6.1616 (3) Å | Cell parameters from 9745 reflections |
b = 22.3074 (10) Å | θ = 2.6–31.9° |
c = 5.0396 (2) Å | µ = 0.64 mm−1 |
β = 99.356 (1)° | T = 100 K |
V = 683.47 (5) Å3 | Lath fragment, colourless |
Z = 4 | 0.47 × 0.23 × 0.14 mm |
Bruker D8 Venture DUO with Photon III C14 diffractometer | 4626 reflections with I > 2σ(I) |
Radiation source: IµS 3.0 microfocus | Rint = 0.035 |
φ and ω scans | θmax = 32.0°, θmin = 2.6° |
Absorption correction: multi-scan (SADABS; Krause et al., 2015) | h = −11→11 |
Tmin = 0.840, Tmax = 0.916 | k = −42→42 |
56728 measured reflections | l = −9→9 |
4816 independent reflections |
Refinement on F2 | Primary atom site location: dual |
Least-squares matrix: full | Hydrogen site location: mixed |
R[F2 > 2σ(F2)] = 0.034 | H atoms treated by a mixture of independent and constrained refinement |
wR(F2) = 0.073 | w = 1/[σ2(Fo2) + (0.0157P)2 + 0.4001P] where P = (Fo2 + 2Fc2)/3 |
S = 1.33 | (Δ/σ)max = 0.001 |
4816 reflections | Δρmax = 0.78 e Å−3 |
94 parameters | Δρmin = −0.50 e Å−3 |
0 restraints |
Geometry. All esds (except the esd in the dihedral angle between two l.s. planes) are estimated using the full covariance matrix. The cell esds are taken into account individually in the estimation of esds in distances, angles and torsion angles; correlations between esds in cell parameters are only used when they are defined by crystal symmetry. An approximate (isotropic) treatment of cell esds is used for estimating esds involving l.s. planes. |
Refinement. Both H atoms were located in difference maps and the one on C was treated as riding in a geometrically idealized position with C—H distance = 0.95 Å, while the coordinates for the one on O were refined. Hydrogen displacement parameters were assigned as Uiso(H) = 1.2Ueq for the attached C atom and 1.5Ueq for the attached O atom. |
x | y | z | Uiso*/Ueq | ||
Cl1 | 0.93128 (4) | 0.66668 (2) | 0.00185 (5) | 0.01441 (4) | |
Cl2 | 0.32839 (4) | 0.69555 (2) | 0.65348 (4) | 0.01403 (4) | |
Cl3 | 0.17530 (4) | 0.56134 (2) | 0.51565 (5) | 0.01375 (4) | |
O1 | 0.72509 (13) | 0.54889 (3) | −0.08395 (16) | 0.01555 (12) | |
H1 | 0.661 (3) | 0.5167 (9) | −0.111 (4) | 0.023* | |
N1 | 0.47368 (12) | 0.55968 (3) | 0.20415 (15) | 0.01124 (10) | |
C1 | 0.63850 (14) | 0.58150 (4) | 0.09104 (17) | 0.01105 (11) | |
C2 | 0.72170 (14) | 0.63936 (4) | 0.15463 (17) | 0.01084 (11) | |
C3 | 0.62942 (14) | 0.67423 (4) | 0.33201 (17) | 0.01121 (12) | |
H3 | 0.684573 | 0.713275 | 0.378054 | 0.013* | |
C4 | 0.45373 (14) | 0.65136 (4) | 0.44307 (17) | 0.01050 (11) | |
C5 | 0.38383 (13) | 0.59348 (4) | 0.37596 (17) | 0.01031 (11) |
U11 | U22 | U33 | U12 | U13 | U23 | |
Cl1 | 0.01297 (8) | 0.01471 (8) | 0.01651 (9) | −0.00232 (6) | 0.00528 (6) | 0.00075 (6) |
Cl2 | 0.01719 (9) | 0.01155 (7) | 0.01464 (8) | −0.00103 (6) | 0.00649 (6) | −0.00281 (6) |
Cl3 | 0.01369 (8) | 0.01177 (7) | 0.01685 (8) | −0.00229 (6) | 0.00571 (6) | 0.00032 (6) |
O1 | 0.0175 (3) | 0.0118 (2) | 0.0191 (3) | −0.0019 (2) | 0.0083 (2) | −0.0045 (2) |
N1 | 0.0115 (2) | 0.0093 (2) | 0.0132 (3) | −0.00046 (19) | 0.0027 (2) | −0.0007 (2) |
C1 | 0.0112 (3) | 0.0095 (3) | 0.0126 (3) | 0.0002 (2) | 0.0025 (2) | −0.0006 (2) |
C2 | 0.0105 (3) | 0.0103 (3) | 0.0119 (3) | −0.0008 (2) | 0.0023 (2) | 0.0005 (2) |
C3 | 0.0124 (3) | 0.0090 (3) | 0.0121 (3) | −0.0011 (2) | 0.0017 (2) | −0.0003 (2) |
C4 | 0.0116 (3) | 0.0090 (3) | 0.0110 (3) | 0.0002 (2) | 0.0022 (2) | −0.0006 (2) |
C5 | 0.0103 (3) | 0.0090 (3) | 0.0117 (3) | −0.0005 (2) | 0.0021 (2) | 0.0002 (2) |
Cl1—C2 | 1.7191 (8) | N1—C1 | 1.3347 (11) |
Cl2—C4 | 1.7202 (8) | C1—C2 | 1.4063 (12) |
Cl3—C5 | 1.7189 (8) | C2—C3 | 1.3757 (12) |
O1—C1 | 1.3207 (11) | C3—C4 | 1.3937 (12) |
O1—H1 | 0.821 (19) | C3—H3 | 0.9500 |
N1—C5 | 1.3343 (11) | C4—C5 | 1.3854 (11) |
C1—O1—H1 | 110.9 (13) | C2—C3—H3 | 120.5 |
C5—N1—C1 | 119.73 (7) | C4—C3—H3 | 120.5 |
O1—C1—N1 | 120.16 (8) | C5—C4—C3 | 118.30 (7) |
O1—C1—C2 | 119.06 (8) | C5—C4—Cl2 | 122.12 (6) |
N1—C1—C2 | 120.78 (8) | C3—C4—Cl2 | 119.58 (6) |
C3—C2—C1 | 119.55 (8) | N1—C5—C4 | 122.66 (8) |
C3—C2—Cl1 | 120.69 (6) | N1—C5—Cl3 | 116.53 (6) |
C1—C2—Cl1 | 119.73 (6) | C4—C5—Cl3 | 120.80 (6) |
C2—C3—C4 | 118.95 (7) | ||
C5—N1—C1—O1 | −178.44 (8) | C2—C3—C4—C5 | 1.98 (12) |
C5—N1—C1—C2 | 1.22 (13) | C2—C3—C4—Cl2 | −177.11 (7) |
O1—C1—C2—C3 | 178.53 (8) | C1—N1—C5—C4 | 0.35 (13) |
N1—C1—C2—C3 | −1.14 (13) | C1—N1—C5—Cl3 | −179.07 (7) |
O1—C1—C2—Cl1 | 0.66 (12) | C3—C4—C5—N1 | −1.97 (13) |
N1—C1—C2—Cl1 | −179.01 (7) | Cl2—C4—C5—N1 | 177.10 (7) |
C1—C2—C3—C4 | −0.50 (13) | C3—C4—C5—Cl3 | 177.43 (6) |
Cl1—C2—C3—C4 | 177.35 (7) | Cl2—C4—C5—Cl3 | −3.51 (11) |
D—H···A | D—H | H···A | D···A | D—H···A |
O1—H1···N1i | 0.821 (19) | 1.919 (19) | 2.7371 (10) | 174.3 (19) |
Symmetry code: (i) −x+1, −y+1, −z. |
Funding information
The authors acknowledge the support from the National Institutes of Health (NIH) through the National Institute of General Medical Sciences (NIGMS) Institutional Development Award (IDeA) grant No. P20 GM103424–21, the US Department of Education (US DoE; Title III, HBGI Part B grant No. P031B040030), and the National Science Foundation (NSF) under grant No. 1736136, CREST Center for Next Generation Multifunctional Composites (NextGen Composites Phase II). The purchase of the diffractometer was made possible by National Science Foundation MRI award CHE–2215262. The contents of the manuscript are solely the responsibility of authors and do not represent the official views of NIH, NIGMS, NSF, or US DoE.
References
Bailly, C., Colson, P., Hénichart, J. P. & Houssier, C. (1993). Nucleic Acids Res. 21, 3705–3709. CrossRef CAS PubMed Google Scholar
Bouchard, M. F., Chevrier, J., Harley, K. G., Kogut, K., Vedar, M., Calderon, N., Trujillo, C., Johnson, C., Bradman, A., Barr, D. B. & Eskenazi, B. (2011). Environ. Health Perspect. 119, 1189–1195. CrossRef CAS PubMed Google Scholar
Bruker (2016). APEX4 and SAINT, Bruker AXS Inc., Madison, Wisconsin, USA. Google Scholar
Bucevičius, J., Gražvydas Lukinavičius, G. & Rūta Gerasimaitė, R. (2018). Chemosensors 6, 18. Google Scholar
Cessna, A. J., Grover, R. & Waite, D. T. (2002). Rev. Environ. Contam. Toxicol. 174, 19–48. CrossRef PubMed CAS Google Scholar
Deng, Y., Zhang, Y., Lu, Y., Zhao, Y. & Ren, H. (2016). Sci. Total Environ. 544, 507–514. CrossRef CAS PubMed Google Scholar
Dias, J. L. C. S., Banu, A., Sperry, B. P., Enloe, S. F., Ferrell, J. A. & Sellers, B. A. (2017). Weed Technol. 31, 928–934. CrossRef Google Scholar
Echeverri-Jaramillo, G., Jaramillo-Colorado, B., Sabater-Marco, C. & Castillo-López, M. (2020). Environ. Sci. Pollut. Res. 27, 32770–32778. CAS Google Scholar
EFSA (2020). European Food Safety Authority. Chlorpyrifos and chlorpyrifos-methyl banned in the EU. Google Scholar
EPA (2023). Environmental Protection Agency. Court ruling on CPF tolerances. Google Scholar
Gao, H., Li, J., Zhao, G. & Li, Y. (2021). Toxicology, 460, 152883. CrossRef PubMed Google Scholar
Hazarika, J., Ganguly, M. & Mahanta, R. (2019). J. Appl. Toxicol. 39, 1002–1011. CrossRef CAS PubMed Google Scholar
Kashanian, S., Shariati, Z., Roshanfekr, H. & Ghobadi, S. (2012). DNA Cell Biol. 31, 1341–1348. CrossRef CAS PubMed Google Scholar
Krause, L., Herbst-Irmer, R., Sheldrick, G. M. & Stalke, D. (2015). J. Appl. Cryst. 48, 3–10. Web of Science CSD CrossRef ICSD CAS IUCr Journals Google Scholar
Li, J., Fang, B., Ren, F., Xing, H., Zhao, G., Yin, X., Pang, G. & Li, Y. (2020). Sci. Total Environ. 726, 138496. CrossRef PubMed Google Scholar
Macrae, C. F., Sovago, I., Cottrell, S. J., Galek, P. T. A., McCabe, P., Pidcock, E., Platings, M., Shields, G. P., Stevens, J. S., Towler, M. & Wood, P. A. (2020). J. Appl. Cryst. 53, 226–235. Web of Science CrossRef CAS IUCr Journals Google Scholar
Mansukhani, M., Roy, P., Ganguli, N., Majumdar, S. S. & Sharma, S. S. (2024). Pestic. Biochem. Physiol. 204, 106065. CrossRef PubMed Google Scholar
Sheldrick, G. M. (2015). Acta Cryst. C71, 3–8. Web of Science CrossRef IUCr Journals Google Scholar
Timchalk, C., Nolan, R. J., Mendrala, A. L., Dittenber, D. A., Brzak, K. A. & Mattsson, J. L. (2002). Toxicol. Sci. 66, 34–53. CrossRef PubMed CAS Google Scholar
Van Emon, J. M., Pan, P. & van Breukelen, F. (2018). Chemosphere, 191, 537–547. CrossRef CAS PubMed Google Scholar
Westrip, S. P. (2010). J. Appl. Cryst. 43, 920–925. Web of Science CrossRef CAS IUCr Journals Google Scholar
Zhao, Y., Wendling, L. A., Wang, C., & Pei, Y. (2017). J. Soils Sediments, 17, 889--900. Google Scholar
This is an open-access article distributed under the terms of the Creative Commons Attribution (CC-BY) Licence, which permits unrestricted use, distribution, and reproduction in any medium, provided the original authors and source are cited.