Doxycycline hyclate |
![]() Last updated: 15/09/2025 |
![]() |
(Also known as: doryx) |
|
![]() |
|
A tetracycline hyclate (hydrochloride hemiethanolate hemihydrate) antibiotic drug effective against a broad range of gram-positive and gram-negative bacteria | |
---|---|---|
|
Used to treat bacterial infections including pneumonia and other respiratory tract infections | |
|
Dogs; Cats; Pigs; Chickens; Birds |
Approval status |
|
Approved | |
---|---|---|
|
Approved |
Chemical structure |
|
Doxycycline hyclate exhibits chiral isomerism, primarily due to the presence of multiple asymmetric carbon atoms in its tetracycline backbone. These chiral centres allow for the existence of stereoisomers, but the clinically used form is a single, well-defined stereoisomer with specific configuration. In the solid state, doxycycline hyclate can crystallise in two distinct conformers (T1 and T2), which differ in the orientation of functional groups around the molecule due to rotation around single bonds. These conformers are not true stereoisomers but rather rotational isomers that influence crystal packing and dissolution properties. | |
---|---|---|
|
C₄₆H₅₈Cl₂N₄O₁₈ | |
|
CCO.CC1C2C(C3C(C(=O)C(=C(C3(C(=O)C2=C(C4=C1C=CC=C4O)O)O)O)C(=O)N)N(C)C)O.CC1C2C(C3C(C(=O)C(=C(C3(C(=O)C2=C(C4=C1C=CC=C4O)O)O)O)C(=O)N)N(C)C)O.O.Cl.Cl | |
|
CCO.C[C@@H]1[C@H]2[C@@H]([C@H]3[C@@H](C(=O)C(=C([C@]3(C(=O)C2=C(C4=C1C=CC=C4O)O)O)O)C(=O)N)N(C)C)O.C[C@@H]1[C@H]2[C@@H]([C@H]3[C@@H](C(=O)C(=C([C@]3(C(=O)C2=C(C4=C1C=CC=C4O)O)O)O)C(=O)N)N(C)C)O.O.Cl.Cl | |
|
UHHHTIKWXBRCLT-VDBOFHIQSA-N | |
|
InChI=1S/2C22H24N2O8.C2H6O.2ClH.H2O/c2*1-7-8-5-4-6-9(25)11(8)16(26)12-10(7)17(27)14-15(24(2)3)18(28)13(21(23)31)20(30)22(14,32)19(12)29;1-2-3;;;/h2*4-7,10,14-15,17,25-27,30,32H,1-3H3,(H2,23,31);3H,2H2,1H3;2*1H;1H2/t2*7-,10+,14+,15-,17-,22-;;;;/m00..../s1 | |
|
Yes |
|
![]() |
Common Name | Relationship | Link |
---|---|---|
doxycycline monohydrste | Parent hydrate | ![]() |
General status |
|
Antibiotic, Antiparasitic, Antiprotozoal, Antibacterial, Medicinal drug | |
---|---|---|
|
Tetracycline | |
|
- | |
|
- | |
|
Synthetic | |
|
A protein synthesis inhibitor | |
|
[30S ribosomal protein S9, Antagonist], [30S ribosomal protein S4, Antagonist], [16S rRNA, Antagonist] | |
|
24390-14-5 | |
|
62149-53-5 | |
|
607-368-7 | |
|
- | |
|
- | |
|
- | |
|
Antiinfectants for systemic use: Antibacterials for systemic use | |
|
QJ01AA02 | |
|
No | |
|
Allowed substance (Table 1: Bovine, Porcine, Poultry) | |
|
1025.9 | |
|
- | |
|
(4S,4aR,5S,5aR,6R,12aR)-4-(dimethylamino)-1,5,10,11,12a-pentahydroxy-6-methyl-3,12-dioxo-4a,5,5a,6-tetrahydro-4H-tetracene-2-carboxamide;ethanol;hydrate;dihydrochloride | |
|
- | |
|
- | |
|
- | |
|
- | |
|
- | |
|
Commercial |
|
|
|||
---|---|---|---|---|
|
Current | |||
|
Early 1960s, developed | |||
|
|
|||
|
|
|||
|
Available in a variety of formulations including tablets, drinking water additives and medicated feeds | |||
|
The production of doxycycline hyclate begins with the semi-synthetic transformation of oxytetracycline, a naturally occurring tetracycline antibiotic. This process involves selective hydrogenation and hydration, typically using methacycline or chloromethacycline as intermediates. The reaction is carried out under controlled pressure in the presence of a noble metal alloy catalyst, such as palladium or platinum combined with selenium or tellurium, which enhances selectivity and yield. Once doxycycline is formed, it is converted into its hyclate salt, a hydrochloride hemiethanolate hemihydrate, by reacting it with hydrochloric acid and ethanol. | |||
|
Published GHG data is not available for most pharmaceuticals. However, according to industry, global averages suggest producing 1 kg of a typical active pharmaceutical ingredient can range from 10 to 100 kg CO₂e for small molecule drugs and potentially up to 1000 kg CO₂e for complex biologicals such as vaccines, depending on the drug type, its formulation, complexity of synthesis, solvent recovery, and energy sources used. |
|
![]() |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
Substance may enter the environment via the faeces of treated animals or by leaching from spilt medicated feed. |
Degradation |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
As this parameter is not normally measured directly, a surrogate measure is used: ‘Photochemical oxidative DT₅₀’. Where data is available, this can be found in the Fate Indices section below. | ||||||||||
|
- |
Soil adsorption and mobility |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
|
- |
Fate indices |
|
|
|
|
||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||||||||||||||||||||
|
|
- | - | - | |||||||||||||||||||||||||
|
- | - |
Known metabolites |
None
|
![]() |
Terrestrial ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
> 2000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Low | ||||||||
|
|
- | - | - | |||||||
|
- | - | |||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
- | |||||||||||
|
- | - | - | ||||||||
- | |||||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - |
Aquatic ecotoxicology |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - |
|
- | - | - | |||
|
- | - | - |
|
![]() |
General |
|
|
|
|
||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
|
High (class III) | - | - | ||||||||
|
> 2000 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) Rat3 = Unverified data of known source |
Low | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Largely metabolised and excreted in the faeces (20-40%) and urine (20-30%) | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
- |
Health issues |
|
|
||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
May cause photosensitivity skin reactions May cause nausea and vomiting |
Handling issues |
|
|
|||
---|---|---|---|---|
|
No information available | |||
|
- | |||
|
Not listed (Not listed) | |||
|
- | |||
|
- | |||
|
- |
|
![]() |
|
|
||
---|---|---|---|
|
doxycycline hyclate | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- |
Record last updated: | 15/09/2025 |
Contact: | aeru@herts.ac.uk |
Please cite as: | Lewis, K.A., Tzilivakis, J., Warner, D. and Green, A. (2016) An international database for pesticide risk assessments and management. Human and Ecological Risk Assessment: An International Journal, 22(4), 1050-1064. DOI: 10.1080/10807039.2015.1133242 |