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suitable passive acoustic protection
sulcotrione

Sulcotrione is a foliar herbicide. Its mode of action is the Inhibition of 4-hydroxyphenyl-pyruvate-dioxygenase (4-HPPD).

Common name (ISO): Sulcotrione
Chemical name (IUPAC): 2-(2-chloro-4-mesylbenzoyl)cyclohexane-1,3-dione
Chemical name (CA): 1,3-cyclohexanedione, 2-[2-chloro-4-(methylsulfonyl)-benzoyl]-
CIPAC No: 723; CAS No: 99105-77-8;
Minimum purity: 950 g/kg (on a dry weight basis)
Molecular formula:: C14 H13 Cl O5 S
Identity of relevant impurities (of toxicological, ecotoxicological and/or environmental concern)
Hydrogen cyanide: maximum content 80 mg/kg on a dry weight basis
Toluene: maximum content 4 g/kg on a dry weight basis.
Molecular mass: 328.77 g/mol

The Standing Committee of the EUROPEAN COMMISSION HEALTH AND CONSUMERS DIRECTORATE-GENERAL on the Food Chain and Animal Health at its meeting on 28 October 2008 decidedon the inclusion of sulcotrione in Annex I of Directive 91/414/EEC (the placing of plant protection products on the market).

The following reference values have been finalised as part of the re-evaluation:
ADI: 0.0004 mg/kg bw/day
ARfD: not allocated, not necessary
AOEL: 0.0006 mg/kg bw/day.

Complete characterisation:

General status:

Pesticide Type Herbicide
Chemical Group Triketone
Substance origin Synthetic
Mode of Action Absorbed mainly by the leaves but also some root uptake. 4-HPPD inhibitor.
CAS RN 99105-77-8
EC Number -
CIPAC Number 723
US EPA Chemical code -
Chemical Formula C14H13ClO5S
SMILES O=C(c1ccc(cc1Cl)S(=O)(=O)C)C2C(=O)CCCC2=O
International Chemical Identifier (InChI) InChI=1/C14H13ClO5S/c1-21(19,20)8-5-6-9(10(15)7-8)14(18)13-11(16)3-2-4-12(13)17/h5-7,13H,2-4H2,1H3
Structure diagram available? Yes
Molecular Mass (g mol-1) 328.77
IUPAC Name 2-(2-chloro-4-mesylbenzoyl)cyclohexane-1,3-dione
CAS Name 2-[2-chloro-4-(methylsulfonyl)benzoyl]-1,3-cyclohexanedione
Other status information -
Herbicide Resistance (HRAC) Classification F2
Insecticide Resistance (IRAC) Classification Not applicable
Fungicide Resistance (FRAC) Classification Not applicable
Physical State White solid

ENVIRONMENTAL FATE

Property Value Source/Quality Score/Other Information Interpretation
Solubility - In water at 20oC (mg l-1) 1670 A4 High
Solubility - In organic solvents at 20oC (mg l-1) 2000 A5 - Xylene -
190000 A5 - Dichloromethane -
48000 A5 - Acetone -
300 A5 - 1-Octanol -
Melting Point (oC) 139 A5 -
Boiling Point (oC) Decomposes before boiling A5 -
Degradation point (oC) 170 A5 -
Flashpoint (oC) Not highly flammable A5 -
Octanol-water partition coefficient at pH 7, 20oC P 2.00 X 10-02 Calculated -
Log P -1.7 A5 Low
Bulk density (g ml-1)/Specific gravity - - -
Dissociation constant (pKa) at 25oC 3.13 A5 -
Note: Weak acid
Vapour pressure at 25oC (mPa) 5.00 X 10-03 A5 Volatile
Henry's law constant at 25oC (Pa m3 mol-1) 6.0 X 10-07 A5 Non-volatile
Henry's law constant at 20oC (dimensionless) 4.33 X 10-09 Q2 Non-volatile
GUS leaching potential index 3.42 Calculated High leachability
SCI-GROW groundwater index (µg l-1) for a 1 kg ha-1 or 1 l ha-1 application rate Value 4.02 X 10-01 Calculated -
Note -
Potential for particle bound transport index - Calculated Low
Maximum UV-vis absorption
L mol-1 cm-1
285nm = 15239, 283.5nm = 16868, 259 nm = 20364 A5 -
Surface tension (mN m-1) 69.0 A5 at 20oC, 90% solution -

Degradation:

Property Value Source/Quality Score/Other Information Interpretation
Soil degradation (days) (aerobic) DT50 (typical) 25 A5 Non-persistent
DT50 (lab at 20oC) 25.3 A5 Non-persistent
DT50 (field) 3.6 A5 Non-persistent
DT90 (lab at 20oC) 100.2 A5 -
DT90 (field) 18.4 A5 -
Note EU dossier lab studies DT50 range 10.8-89.7 days, DT90 range 47-246 days; field studies DT50 range 1.2-11.4 days, DT90 range 6.9-38 days
Aqueous photolysis DT50 (days) at pH 7 Value 25.6 A5 Slow
Note pH sensitive: DT50 13 days at pH 4, 40.9 days at pH 9, all data for 5 cm depth and seasonal mean values. Degradation slower at 30 cm depth.
Aqueous hydrolysis DT50 (days) at 20oC and pH 7 Value Stable A5 Very persistent
Note Stable at pH 5 to pH 9, temp 25-40 Deg C
Water-Sediment DT50 (days) 63.9 A5 Moderately fast
Water phase only DT50 (days) 9.5 A5 Moderately fast

Soil adsorption and mobility:

Property Value Source/Quality Score/Other Information Interpretation
Linear Kd - - -
Koc -
Notes and range -
Freundlich Kf 1.05 A5 Mobile
Kfoc 36
1/n 0.839
Notes and range EU dossier Kf range 0.29-2.26, Kfoc range 17-58 mL/g, 1/n range 0.812-0.888, Soils=6
pH sensitivity Predominantly OC-dependent but pH-dependent to a minor extent

Key metabolites:

Metabolite Formation Medium Estimated Maximum Occurrence Fraction 91/414 Relevancy
2-chloro-4-methylsulfonyl-benzoic acid Soil 0.603 Major fraction, Relevant

Other known metabolites:

Metabolite name and reference Aliases Formation Medium / Rate Estimated Maximum Occurrence Fraction Metabolising Enzymes
4-hydroxyphenyl pyruvate - Rat (Blood) - -
4-hydroxy-sulcotrione, 2-[2-chloro-4-(methylsulfonyl)benzoyl]-4-hydroxycyclohexane-1,3-dione sulcotrione metabolite M02 Rat (Urinary) - -
5-hydroxy-sulcotrione, 2-[2-chloro-4-(methylsulfonyl)benzoyl]-5-hydroxycyclohexane-1,3-dione sulcotrione metabolite M04 Rat (Urinary) - -


ECOTOXICOLOGY

Property Value Source/Quality Score/Other Information Interpretation
Bio-concentration factor BCF - - -
CT50 (days) - -
Bioaccumulation potential - Calculated Low
Mammals - Acute oral LD50 (mg kg-1) > 5000 A5 Rat Low
Mammals - Short term dietary NOEL (mg kg-1) > 0.5 L2 Rat, 2 year High
(ppm diet) > 100 -
Birds - Acute LD50 (mg kg-1) > 1350 A5 Anas platyrhynchos Moderate
Birds - Short term dietary (LC50/LD50) > 1259 mg kg bw-1 day-1 A5 Anas platyrhynchos -
Fish - Acute 96 hour LC50 (mg l-1) 227 A5 Oncorhynchus mykiss Low
Fish - Chronic 21 day NOEC (mg l-1) 3.2 A4 Oncorhynchus mykiss, Juvenile growth -
Aquatic invertebrates - Acute 48 hour EC50 (mg l-1) > 848 A5 Daphnia magna Low
Aquatic invertebrates - Chronic 21 day NOEC (mg l-1) > 75 A5 Daphnia magna -
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 - Acute 7 day EC50, biomass (mg l-1) 0.051 A5 Lemna gibba Moderate
Algae - Acute 72 hour EC50, growth (mg l-1) 1.2 A5 Raphidocelis subcapitata Moderate
Algae - Chronic 96 hour NOEC, growth (mg l-1) - - -
Honeybees - Acute 48 hour LD50 (µg bee-1) 50 A5 Oral Moderate
Earthworms - Acute 14 day LC50 (mg kg-1) > 1000 A5 Moderate
Earthworms - Chronic 14 day NOEC, reproduction (mg kg-1) - - -
Other soil macro-organisms - e.g. Collembola LR50product ha
EC50product ha
NOECproduct ha
% Effect
- - -
Other arthropod (1) LR50 g ha-1 450 48 hour
A5 Aphidius rhopalosiphi, adult
Moderately harmful at 1 kg ha-1
% Effect - - -
Other arthropod (2) LR50 g ha-1 450 7 day
A5 Typhlodromus pyri
Moderately harmful at 1 kg ha-1
% Effect - - -
Soil micro-organisms Nitrogen mineralisation: No significant effect
Carbon mineralisation: No significant effect
A5
Dose: 4.5 kg/ha, 28 days
-
Mesocosm study data NOEAEC mg l-1 - - -
NOEAEC mg l-1 - - -


HUMAN HEALTH AND PROTECTION

General:

Property Value Source/Quality Score/Other Information Interpretation
Mammals - Acute oral LD50 (mg kg-1) > 5000 A5 Rat Low
Mammals - Dermal LD50 (mg kg-1 body weight) > 4000 A5 Rat -
Mammals - Inhalation LC50 (mg l-1) > 1.63 A5 Rat, 4hr (nose only) -
Other Mammal toxicity endpoints -   -
ADI - Acceptable Daily Intake (mg kg-1bw day-1) 0.0004 A5 Rat, SF=100 -
ARfD - Acute Reference Dose (mg kg-1bw day-1) None allocated A5 -
AOEL - Acceptable Operator Exposure Level - Systemic (mg kg-1bw day-1) 0.0006 A5 Rat, SF=100 -
Dermal penetration studies (%) 0.1-0.5 A5 concentration dependant -
Dangerous Substances Directive 76/464 - - -
Exposure Limits - - -
Exposure Routes Public [No unacceptable risks to bystanders identified for intended use]
Occupational [No unacceptable risks to operators or other workers identified for intended use]
Examples of European MRLs (mg kg-1) Value Maize: 0.05
Note [A5 EU dossier proposals]
For the EU pesticides database click here
Drinking Water MAC (µg l-1) - - -

Health issues: skin sensitiser, potential kidney and liver toxicant, may cause eye damage

Handling issues:

Property Value Source/Quality Score/Other Information Interpretation
General <="" font="" border="0"> [Not explosive or oxidising]
EC Risk Classification <="" font="" border="0"> [Reproduction risk category 3: R63], [Xi - Irritant: R43]
EC Safety Classification <="" font="" border="0"> -
WHO Classification NL - Not listed
US EPA Classification (formulation) No consensus across products or no products available - -
UN Number -
Waste disposal & packaging <="" font="" border="0"> -

 

 

Sources:

http://sitem.herts.ac.uk/aeru/iupac/Reports/600.htm

http://ec.europa.eu/food/plant/protection/evaluation/existactive/list_sulcotrione.pdf

http://compendium.bayercropscience.com/BAYER/CropScience/CropCompendium/BCSCropComp.nsf/id/sulcotrione.htm#

 

sulphur dioxide
summary report, REACH
supercritical fluid extraction
an extraction method (SCFE) where the extraction fluid, usually CO2 is present at a pressure and temperature above its critical point.
supersound
supplyer, REACH
surface tension
intrinsic property of liquids caused by cohesion (the attraction of molecules to similar molecules). Since the molecules on the surface of the liquid are not surrounded by similar molecules on all sides, they are more attracted to their neighbours on the surface. It corresponds to the minimum work required to expand the surface by one unit area (J/m2, N/m). A physico-chemical parameter required by REACH. Surface tension is not used as a Classification and Labelling (C&L) (classification and labelling of chemicals) criterion, to define PBT properties, or as a specific property in the chemical risk assessment. It can be used to provide guidance as to whether a chemical would be considered a surfactant under EU Regulation 648/2004 (last modified by Regulation 907/2006 - Detergents). (http://www.prc.cnrs-gif.fr/reach/en/physicochemical_data.html) The study need only be conducted if based on structure, surface activity is expected or can be predicted; or surface activity is a desired property of the material. If the water solubility is below 1 mg/l at 20°C the test does not need to be conducted.
surface water
surface water damage
Surface water sediment
surface water status

"surface water status" is the general expression of the status of a body of surface water, determined by the poorer of its ecological status and its chemical status.

surface waters ecological status

"ecological status" is an expression of the quality of the structure and functioning of aquatic ecosystems associated with surface waters, classified in accordance with Annex V. of the Water Framework Directive (WFD), 60/2000/EC

surface waters good chemical status

"good surface water chemical status" means the chemical status required to meet the environmental objectives for surface waters established in Article 4(1)(a) of WFD (60/2000/EC) that is the chemical status achieved by a body of surface water in which concentrations of pollutants do not exceed the environmental quality standards established in Annex IX and under Article 16(7), and under other relevant Community legislation setting environmental quality standards at Community level.

surface waters good ecological potential

"good ecological potential" is the status of a heavily modified or an artificial body of water, so classified in accordance with the relevant provisions of Annex V. of Water Framework Directive (WFD), (60/2000/EC).

surface waters good ecological status

"good ecological status" is the status of a body of surface water, so classified in accordance with Annex V. of WFD (Water Framework Directive), 60/2000/EC

Surfactant Enhanced Aquifer Remediation (SEAR)

Surfactant Enhanced Aquifer Remediation (SEAR), in its most basic form, could thus be considered a chemical enhancement to pump and treat. A chemical solution is pumped across a contaminated zone by introduction at an injection point and removal from an extraction point. To cover the entire contaminated zone, a number of injection and extraction wells are used; the well configuration is determined by the subsurface distribution of NAPL and the hydrogeologic properties of the aquifer.

SEAR is a source zone remediation technology. SEAR removes the residual phase contamination from which the dissolved phase plume is derived. Free phase contamination is typically removed by conventional pumping before SEAR is employed. SEAR does not have an immediate effect on the dissolved phase plume concentrations and is not a dissolved phase plume remediation technology. Removal of the source does however cause an intermediate and long-term reduction in dissolved phase contaminant concentrations.

Surfactants are unique chemical agents that greatly enhance the solubility of organic contaminants in aqueous media. They are also able to reduce the interfacial tension (IFT - that force existing where two fluids meet that keeps them as separate fluids) between the aqueous and organic phases to mobilize the organic phase. To illustrate the two mechanisms, we can use the familiar examples of the cleaning action of household cleaning detergents, which contain surfactants as a common constituent. We have witnessed surfactant-induced solubilization in the oily solution resulting from soaking oily pots and pans in dish detergent; we have observed a reduction in IFT from oil droplets or a sheen of oil coming off the pan due to the presence of a detergent. A surfactant flood can be designed to remove contaminants either primarily by solubilization or primarily by mobilization. Surfactant mobilization can remove more DNAPL in less time; however, there is greater risk of uncontrolled downward movement of DNAPL, as DNAPL is being physically displaced by the surfactant solution. Thus, to conduct a mobilization flood, it is necessary to have an aquitard as a barrier to prevent vertical DNAPL migration. It is important to identify from the outset whether solubilization or mobilization of DNAPL is desired, because not all surfactants can be used to conduct a mobilization flood.

The primary objective in SEAR design is to remove the maximum amount of contaminant with a minimum amount of chemicals and in minimal time while maintaining hydraulic control over the injected chemicals and contaminant. Each step in the design process must keep this in mind. Design challenges include precisely locating the DNAPL, finding the optimum surfactant solution for a given DNAPL composition and soil type, and fully characterizing the hydraulic properties of the aquifer, particularly the heterogeneities typically present in the subsurface environment. Because it is impossible to know with certainty the variations in aquifer properties over the treatment zone, numerical modeling tools are used to simulate how the system may respond in the presence of these unknown factors. Numerical modeling is also necessary to understand the dynamics of the flooding process under the hydrogeologic conditions at the site. SEAR has been acknowledged to be a promising, innovative technology for the removal of DNAPLs primarily because of the history of the use of surfactant-enhanced oil recovery by the petroleum industry.

Source: http://www.cpge.utexas.edu/ee/sear.html

survey

a systematic collection of information or data. A survey can be conducted to collect information from a group of people or from the environment. Surveys of a group of people can be conducted by telephone, by mail, or in person. Some surveys are done by interviewing a group of special people.

Environmental survey is data collection about an area, a catchment, about ecosystems and ecosystem members, about contamination at a site or the integrated collection of many different information.

suspendible part of the soil
sustainable development
sustainable use
SVOC
abreviation for Semi-Volatile Organic Compounds, which are organic compounds of a boiling point higher than water and which may vaporize when exposed to temperatures above room temperature, including pesticides, PAHs, PCBs and phthalates. SVOCs are typically industrial plasticizers e.g. phthalates, by-products of incomplete combustion of fossil fuels e.g benzo[a]pyrene.
SWOT analyses

Streghts, Weeknesses, Opportunities, Threats. Methodology for descriptive evaluation of new technologies, processes, methods, projects or businesses. It is a strategic planning method used to evaluate the Strengths, Weaknesses, Opportunities, and Threats involved in a project or business. It involves specifying the objective of the business venture or project and identifying the internal and external factors that are favourable and unfavourable to achieving that objective.

syndrome

the group or recognizable pattern of symptoms or abnormalities that indicate a particular trait or disease.

synergism, synergistic effect

a biologic response to multiple substances where one substance worsens the effect of another substance. The combined effect of the substances acting together is greater than the sum of the effects of the substances acting by themselves.

See also additive effect and antagonistic effect.

system boundaries, LCA
SZ signed document for hasardous waste transportation, HU legislative term
SZ signed document for hazardous waste transportation, HU legislat
szmektit
szomszédjog