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Propylene carbonate
Last updated: 03/09/2026
(Also known as: carbonic acid propylene ester)

SUMMARY
Hazard alerts

The following Pesticide Hazard Tricolour (PHT) alerts are based on the data in the tables below. An absence of an alert does not imply the substance has no implications for human health, biodiversity or the environment but just that we do not have the data to form a judgement. The alerts for Highly Hazardous Pesticides (HHPs) are based on applying the FAO/WHO (Type 1) and the PAN (Type II) criteria to PPDB data. Further details on the HHP indicators are given in the tables below. Neither the PHT nor the HHP hazard alerts take account of usage patterns or exposure, thus they do not represent risk.

PHT: Environmental fate PHT: Ecotoxicity PHT: Human health Highly Hazardous Pesticide
Environmental fate
High alert:
Drainflow: Very mobile
Warning:
Significant data are missing
Ecotoxicity
Low alert:
Fish acute ecotoxicity: Low; Daphnia acute ecotoxicity: Low
Warning:
Significant data are missing
Human health
Low alert
 
GENERAL INFORMATION
Description
A cyclic carbonate ester lquid used as a polar organic solvent and adjuvant in pesticide product formulations
GB regulatory status
GB COPR regulatory status
Not applicable - not a ppp. May be authorised at national level under different legislation
Date COPR inclusion expires
Not applicable
GB LERAP status
Not applicable
EC Regulation 1107/2009 (repealing 91/414)
EC Regulation 1107/2009 status
Not applicable - not a ppp. May be authorised at national level under different legislation
Dossier rapporteur/co-rapporteur
Not applicable
Date EC 1107/2009 inclusion expires
Not applicable
EU Candidate for substitution (CfS)
Not applicable
Listed in EU database
Not applicable
Approved for use (✓) under EC 1107/2009 in the following EU Member States
ATAustria
BEBelgium
BGBulgaria
CYCyprus
CZCzech Republic
DEGermany
DKDenmark
EEEstonia
ELGreece
                 
ESSpain
FIFinland
FRFrance
HRCroatia
HUHungary
IEIreland
ITItaly
LTLithuania
LULuxembourg
                 
LVLatvia
MTMalta
NLNetherlands
PLPoland
PTPortugal
RORomania
SESweden
SISlovenia
SKSlovakia
                 
Approved for use (✓) under EC 1107/2009 by Mutual Recognition of Authorisation and/or national regulations in the following EEA countries
ISIceland
NONorway
                 
Additional information
Also used in
-
Chemical structure
Isomerism
Propylene carbonate exhibits stereoisomerism because the carbon atom bearing the methyl group in its five-membered cyclic carbonate ring is a chiral centre. Consequently, it exists as two enantiomers, (R)-propylene carbonate and (S)-propylene carbonate. Commercial propylene carbonate is normally supplied as a racemic mixture rather than as a single enantiomer.
Chemical formula
C₄H₆O₃
Canonical SMILES
-
Isomeric SMILES
-
International Chemical Identifier key (InChIKey)
-
International Chemical Identifier (InChI)
-
2D structure diagram/image available?
Yes
General status
Pesticide type
Other substance
Other bioactivity & uses
Solvent; Adjuvant
Substance groups
Cyclic carbonate ester
Minimum active substance purity
-
Known relevant impurities
-
Substance origin
Synthetic
Mode of action
Substance does not exhibit pesticidal activity
CAS RN
108-32-7
EC number
203-572-1
CIPAC number
-
US EPA chemical code
-
PubChem CID
-
Molecular mass (Da)
102.09
PIN (Preferred Identification Name)
4-methyl-1,3-dioxolan-2-one
IUPAC name
4-methyl-1,3-dioxolan-2-one
CAS name
1,2-propanediol carbonate
Global Governance status: Listed (✓) under
UK Poisons List Order 1972 Rotterdam Convention Montreal Protocol
Stockholm Convention OSPAR EU Water Framework Directive
Relevant Environmental Water Quality Standards
-
Forever chemical
-
Highly Hazardous Pesticide (HHP)
Type I
-
Type II
-
Other status information
-
Herbicide Resistance Class (HRAC MoA class)
Not applicable
Herbicide Resistance Class (WSSA MoA class)
Not applicable
Insecticide Resistance Class (IRAC MoA class)
Not applicable
Fungicide Resistance Class (FRAC MOA class)
Not applicable
Examples of recorded resistance
-
Physical state
Clear colourless, liquid
Commercial
Property
Value
Availability status
Current
Introduction & key dates
-
Example manufacturers & suppliers of products using this active now or historically
-
Example products using this active
-
Example products using this substance as a possible coformulant
 
Selected: Aeron (Open in PFC)
   
Selected: Alasi (Open in PFC)
   
Selected: Altus (Open in PFC)
   
Selected: Amigo 175 EC (Open in PFC)
   
Selected: Carnadine (Open in PFC)
   
Selected: Carnadine 200 (Open in PFC)
   
Selected: Claw 100 (Open in PFC)
   
Selected: Demand G (Open in PFC)
   
Selected: Efficon (Open in PFC)
   
Selected: Falcon (Open in PFC)
   
Selected: Grandstand (Open in PFC)
   
Selected: Kalamos (Open in PFC)
   
Selected: Kestrel (Open in PFC)
   
Selected: Materra (Open in PFC)
   
Selected: Optimus (Open in PFC)
   
Selected: Revyflex (Open in PFC)
   
Selected: Riamba (Open in PFC)
   
Selected: Shogun (Open in PFC)
   
Selected: Sivanto 200 SL (Open in PFC)
   
Selected: Sivanto HL (Open in PFC)
   
Selected: Sivanto Prime (Open in PFC)
   
Selected: Stemper (Open in PFC)
   
Selected: Sword (Open in PFC)
   
Selected: Tithe (Open in PFC)
   
Selected: Velocity (Open in PFC)
   
Selected: Zypar (Open in PFC)
 
Formulation and application details
Supplied commercially as a liquid
Commercial production
Commercially, propylene carbonate is principally manufactured by reacting propylene oxide with carbon dioxide, producing the cyclic carbonate in a catalytic reaction.
Impact on climate of production and use
The principal carbon burden from the manufacture of propylene carbonate arises from the fossil-derived propylene oxide and the energy required for reaction, compression and purification. Consequently, the overall footprint is highly dependent on the production route, energy mix and CO₂ source; using captured waste CO₂ and renewable energy can substantially reduce emissions. Overall, its CO₂-utilisation chemistry is favourable, but propylene carbonate should not automatically be considered a low-carbon solvent.
ENVIRONMENTAL FATE
Property
Value
Source; quality score; and other information
Interpretation
Solubility - In water at 20 °C at pH 7 (mg l⁻¹)
240000
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
High
Solubility - In organic solvents at 20 °C (mg l⁻¹)
- - -
Melting point (°C)
- - -
Boiling point (°C)
242
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
-
Degradation point (°C)
- - -
Flashpoint (°C)
116
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
-
Octanol-water partition coefficient at pH 7, 20 °C
P
- - -
Log P
- - -
Fat solubility of residues
Solubility
- - -
Data type
- - -
Density (g ml⁻¹)
1.2
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
-
Dissociation constant pKa) at 25 °C
- - -
-
Vapour pressure at 20 °C (mPa)
- - -
Henry's law constant at 25 °C (Pa m³ mol⁻¹)
- - -
Volatilisation as max % of applied dose lost
From plant surface
- - -
From soil surface
- - -
Maximum UV-vis absorption L mol⁻¹ cm⁻¹
- - -
Surface tension (mN m⁻¹)
- - -
Degradation
Property
Value
Source; quality score; and other information
Interpretation
General biodegradability
Readily biodegradable, 79% in 28 days
Soil degradation (days)
DT₅₀ (typical)
- - -
DT₅₀ (lab at 20 °C)
- - -
DT₅₀ (field)
- - -
DT₉₀ (lab at 20 °C)
- - -
DT₉₀ (field)
- - -
DT₅₀ modelling endpoint
- - -
Note
-
Soil mineralisation
Aerobic (at 20 °C)
- - -
Anaerobic (at 20 °C)
- -
Dissipation rate RL₅₀ (days) on plant matrix
Value
- - -
Note
-
Dissipation rate RL₅₀ (days) on and in plant matrix
Value
- - -
Note
-
Aqueous photolysis DT₅₀ (days) at pH 7
Value
- - -
Note
-
Aqueous hydrolysis DT₅₀ (days) at 20 °C and pH 7
Value
- - -
Note
-
Water-sediment DT₅₀ (days)
- - -
Water phase only DT₅₀ (days)
- - -
Sediment phase only DT₅₀ (days)
- - -
Air 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.
Decay in stored produce DT₅₀
-
Soil adsorption and mobility
Property
Value
Source; quality score; and other information
Interpretation
Linear
Kd (mL g⁻¹)
-
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
Very mobile
Koc (mL g⁻¹)
5.0
Notes and range
estimated
Freundlich
Kf (mL g⁻¹)
- - -
Kfoc (mL g⁻¹)
-
1/n
-
Notes and range
-
pH sensitivity
-
Fate indices
Property
Value
Source; quality score; and other information
Interpretation
GUS leaching potential index
- - -
SCI-GROW groundwater index (μg l⁻¹) for a 1 kg ha⁻¹ or 1 l ha⁻¹ application rate
Value
Cannot be calculated - -
Note
-
Potential for particle bound transport index
- - -
Potential for loss via drain flow
Very mobile Calculated -
Photochemical oxidative DT₅₀ (hrs) as indicator of long-range air transport risk
96
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
Calculated using the Atkinson method. Assumed 1.5E+06 OH/cm³, 12 hr. EU trigger for long-range transport is DT₅₀ in air <2 days.
Substance of concern for long-range air transport
Bio-concentration factor
BCF (l kg⁻¹)
3.0
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
estimated
Low potential
CT₅₀ (days)
- -
Known metabolites

None

ECOTOXICOLOGY
Terrestrial ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
>E3 Rat 5000 - Low
Mammals - Short Term Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Mammals - Long Term (Chronic) Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Birds - Acute LD₅₀ (mg kg⁻¹)
- - -
Birds - Short term dietary LC₅₀ (mg kg⁻¹ bw d⁻¹)
- - -
Birds - Chronic 21d NOEL (mg kg⁻¹ bw d⁻¹)
- - -
Earthworms - Acute 14 day LC₅₀ (mg kg⁻¹ dw soil)
- - -
Earthworms - Chronic NOEC, reproduction (mg kg⁻¹ dw soil)
- - -
Soil micro-organisms
- - -
Collembola
Acute LC₅₀ (mg kg⁻¹)
- - -
Chronic NOEC (mg kg⁻¹)
- - -
Non-target plants
Vegetative vigour ER₅₀ (g ha⁻¹)
- - -
Seedling emergence ER₅₀ (g ha⁻¹)
- - -
Honeybees (Apis spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Unknown mode acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Chronic
- - -
Notes
-
Bumblebees (Bombus spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
-
Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
-
Mason bees (Osmia spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Other bee species (1)
Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)
- - -
Mode of exposure
-
Other bee species (2)
Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)
- - -
Mode of exposure
-
Beneficial insects (Ladybirds)
- - -
Beneficial insects (Lacewings)
- - -
Beneficial insects (Parasitic wasps)
- - -
Beneficial insects (Predatory mites)
- - -
Beneficial insects (Ground beetles)
- - -
Beneficial insects (Butterflies)
Contact
- - -
Notes
-
Oral
- - -
Notes
-
Aquatic ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Temperate Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)
> 1000
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
Cyprinus carpio
Low
Temperate Freshwater Fish - Chronic 21 day NOEC (mg l⁻¹)
- - -
Tropical Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Temperate Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)
> 500
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
Daphnia magna
Low
Temperate Freshwater Aquatic invertebrates - Chronic 21 day NOEC (mg l⁻¹)
- - -
Tropical Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)
- - -
Aquatic crustaceans - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Sediment dwelling organisms - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Sediment dwelling organisms - Chronic 28 day NOEC, static, water (mg l⁻¹)
- - -
Sediment dwelling organisms - Chronic 28 day NOEC, sediment (mg kg⁻¹)
- - -
Aquatic Plants (free-floating, fonds growth, fresh) - 7 day (mg l⁻¹)
- - -
Aquatic plants (rooted, growth rate, fresh) - 14 day (mg l⁻¹)
- - -
Algae - Acute (growth rate, fresh; mg l⁻¹) (EC₅₀ 72 hr)
> 500
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
Desmodesmus subspicatus
Low
Algae - Chronic (growth rate, fresh; mg l⁻¹)
- - -
Mesocosm study data
NOEAEC mg l⁻¹
- - -
NOEAEC mg l⁻¹
- - -
Marine bivalves
- - -
Regulatory Threshold Levels (RTLs)

Note: These RTLs have been calculated using the regulatory approach used in the European Union and based on ecotoxocity values in the PPDB.

Species group
RTL
Notes
Mammals
500 Worst case of acute and chronic mammals
Birds
No data No data for acute and chronic birds
Soil organisms
No data No data for acute and chronic earthworms
Terrestrial plants
No data No data for non-target plants vegetative vigour and seedling emergence
Pollinators
No data No data for contact and oral honeybees
Arthropods
No data No data for parasitic wasps and predatory mites
Fish
10 Worst case of temperate acute and chronic fish
Aquatic invertebrates
5 Worst case of temperate acute and chronic aquatic invertebrates
Aquatic plants
50 Worst case of free-floating plants, rooted plants, acute and chronic algae
HUMAN HEALTH AND PROTECTION
General
Property
Value
Source; quality score; and other information
Interpretation
Threshold of Toxicological Concern (Cramer Class)
- - -
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
>E3 Rat 5000 - Low
Mammals - Short Term Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Mammals - Long Term (Chronic) Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Mammals - Dermal LD₅₀ (mg kg⁻¹ body weight)
> 3000
E3 E = Manufacturers safety data sheets
3 = Unverified data of known source
Rabbit
-
Mammals - Inhalation LC₅₀ (mg l⁻¹)
- - -
Other Mammal toxicity endpoints
- - -
ADI - Acceptable Daily Intake (mg kg⁻¹ bw day⁻¹)
- - -
ARfD - Acute Reference Dose (mg kg⁻¹ bw day⁻¹)
- - -
AAOEL - Acute Acceptable Operator Exposure Level (mg kg⁻¹ bw day⁻¹)
- - -
AOEL - Acceptable Operator Exposure Level - Systemic (mg kg⁻¹ bw day⁻¹)
- - -
Dermal penetration studies (%)
- - -
Dangerous Substances Directive 76/464
- - -
Exposure Routes
Public
-
Occupational
-
MRLs
European
EU MRL pesticide database 
Great Britain
GB MRL Register 
Notes
-
Drinking Water Standards
- - -
Drinking Water MAC (μg l⁻¹)
- - -
Mammalian dose elimination route and rate
- - -
Health issues
Specific human health issues (hazard-based)
Carcinogen
Genotoxic
Endocrine disruptor
XNo, known not to cause a problem
A0 A = Chromosome aberration (EFSA database)
0 = No data
;
B0 B = DNA damage/repair (EFSA database)
0 = No data
;
C0 C = Gene mutation (EFSA database)
0 = No data
;
D0 D = Genome mutation (EFSA database)
0 = No data
;
E3 E = Unspecified genotoxicity type (miscellaneous data source)
3 = Negative
XNo, known not to cause a problem
Reproduction / development effects Acetyl cholinesterase inhibitor Neurotoxicant
XNo, known not to cause a problem
XNo, known not to cause a problem
No data found
Respiratory tract irritant Skin irritant Skin sensitiser
?Possibly, status not identified
?Possibly, status not identified
XNo, known not to cause a problem
Eye irritant Phototoxicant  
Yes, known to cause a problem
XNo, known not to cause a problem
 
General human health issues
Consumption may lead to gastrointestinal disturbances and nausea
Handling issues
Property
Value and interpretation
General
Autoignition temerature 430 DegC
Heating to decomposition will emit irritating gases
Hygroscopic
Incompatible with strong oxidising agents, reducing agents and peroxides
CLP classification 2013
-
WHO Classification
-
UN Number
-
Waste disposal & packaging
Not regulated
Shelf-life, storage, stability and reactivity
-
TRANSLATIONS
Language
Name
English
propylene carbonate
French
-
German
-
Danish
-
Italian
-
Spanish
-
Greek
-
Polish
-
Swedish
-
Hungarian
-
Dutch
-
Norwegian
-

Record last updated: 03/09/2026
Contact: aeru@herts.ac.uk
Please cite as:

Tzilivakis, J., Lewis, K.A., Green, A. and Warner, D.J. (2026) A decade of growth and impact of the Pesticide Properties Database (PPDB). Human and Ecological Risk Assessment: An International Journal, 1–26. DOI: 10.1080/10807039.2026.2702066

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


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