natgillin/translations-raw huggingface dataset:
Dette vil især være relevant under større regnskyl, hvor banens dræn ikke kan modtage al regnvand.
This is particularly during heavy showers where the pitch's drainage system cannot take all the rainwater.
Beregningen er udført med samme forudsætninger som i den norske undersøgelse (T.
The calculation is made under the same assumptions as the Norwegian study (T.
Afdræningsvandets koncentration Ceff antages at blive fortyndet 10 gange (f) ved tilledning til grøft/mindre vandløb som angivet default i TGD (Technical Guidance Document, 2003).
The concentration of the drainage water Ceff is assumed to be diluted 10 times (f) when drained to a catchwater drain/small watercourse as specified as default in TGD (Technical Guidance Document, 2003).
Koncentrationen i vandfasen kan beregnes til:
The concentration in the water phase can be calculated to be:
PECvand= Ceff /((1+Kpsusp x SUSPvand x 10-6)*f)
PECwater = Ceff /((1+Kpsusp x SUSPwater x 10-6)*f)
hvor Kpsusp er fordelingskoeeficenten mellem faststof og vand beregnet fra KOC med et indhold af organisk stof i suspenderet materiale sat til default-værdien c org,susp= 10 %.
where Kpsusp is the distribution coefficient between solid and water calculated from KOC with a content of organic substance in suspended material put at the default value c org,susp= 10%.
SUSPvand er koncentrationen af suspenderet materiale (mg/l) -værdien sættes til default-værdien 15 mg/l.
SUSPwater is the concentration of suspended material (mg/l) - the value is put at the default value of 15 mg/l.
Koc beregnes ud fra Kow ud fra QSAR-modellen for ikke-hydrofobe organiske stoffer i TGD.
Koc is calculated on the basis of Kow from the QSAR model for non-hydrophobic organic substances in TGD.
den volumenbaserede fordelingskoefficient af suspenderet materiale i forhold til vand Ksusp-vand (m³/m³) beregnes med modelværktøjet EUSES 2.0 med input af KOC og den valgte QSAR-model (EUSES 2.0).
the volume-based distribution coefficient of suspended material in relation to water Ksusp-water (m³/m³) is calculated using the model tool EUSES 2.0 with input of KOC and the selected QSAR model (EUSES 2.0).
Endelig beregnes forholdene PECvand/PNECvand, samt PECsediment/PNECsediment
Finally, the following ratios are calculated: PECwater/PNECwater as well as PECsediment/PNECsediment
(sikkerhedsmarginer) til at vurdere, om der er en mulig lokal miljøeffekt ved udledning af de undersøgte stoffer.
(margins of safety) to assess whether there is a potential local environmental effect from discharge of the substances investigated.
I Tabel 8.12 er vist en worst case-beregning af miljøeffekten ved udledning af drænvand stammende fra elastisk fyldmateriale til et nærliggende vandløb, idet det antages, at afdræningsvandets koncentrationer af stoffer svarer til de fundne koncentrationer i kontaktvand.
Table 8.12 shows a worst case calculation of the environmental effect of discharging drainage water from elastic infills to an adjacent watercourse, under the assumption that the drainage water concentrations of substances correspond to those found in contact water.
Tabel 8.12 beregning af udledning af udvaskede stoffer fra infill til vandløb
Table 8.12 Calculation of discharge of leached substances from infills to watercourses
Som beskrevet i 8.9.1, er de fundne koncentrationer i kontaktvand worst case, idet koncentrationen af udvaskede stoffer må forventes at falde med tiden, ligesom den benyttede udvaskningsmetode skønnes at være mere effektiv med større væske-faststofkontakt end den reelle situation på en boldbane.
As described in 8.9.1, the concentrations found in contact water are worst case scenarios as the concentration of leached substances must be expected to decrease over time just as the leaching method used is deemed to be more efficient with more liquid-solid contact than the actual situation on a football pitch.
Det skal her bemærkes, at en test i lysimeter formentlig underestimerer udvaskningen, da den fysiske påvirkning fra spillerne på en våd boldbane (under regnvejrsforhold) bør øge væske-faststofkontakten i forhold til et lysimeter, hvor der er ikke er en mekanisk påvirkning af banen fra fodboldspillerne.
In this connection, it should be noted that a lysimeter test probably underestimates the leaching level as the physical impact from the players on a wet pitch (during rain) should increase the liquid-solid contact compared to a lysimeter where there is no mechanical impact on the pitch from the football players.
Tabel 8.12 viser, under forudsætning af en udvaskning fra elastisk infill under brug på en boldbane svarende til resultaterne fra udvaskningstesten, en effekt på nærliggende vandløb fra zink på niveau med resultaterne i den norske undersøgelse.
Table 8.12 shows - based on the assumption that the leaching from elastic infills during use of a football pitch corresponds to the results from the leaching test - an effect on adjacent watercourses from zinc at a level corresponding to the result in the Norwegian study.
Tilsvarende koncentrationsniveauer ses for phenol, 2,4-bis(1,1-dimethylethyl)-.
Similar concentration levels are observed for phenol, 2,4-bis(1,1-dimethylethyl)-.
I Tabel 8.13 og er vist en worst-case beregning af miljøeffekten ved udledning af drænvand stammende fra kunstgræs til et nærliggende vandløb.
Table 8.13 shows a worst case calculation of the environmental effect of discharge of drainage water from artificial turf into an adjacent watercourse.
Tabel 8.13 beregning af udledning af udvaskede stoffer fra kunstgræs til vandløb.
Table 8.13 Calculation of discharge of leached substances from artificial turf to watercourses.
Lysimeterforsøgene vurderes at være mere repræsentative for forholdene på en boldbane.
This is because significantly lower leaching values from football pitches were expected.
Om der er en reel miljøeffekt, kræver gennemførelse af lysimeterforsøg eller måling på drænvand fra boldbaner over længere tid (fx et år).
The substance concentrations in contact water have been compared to the requirements set out in the Executive Order on Drinking Water.
[2] Det fremgår ikke, om det er en indendørs eller en udendørs bane.
[2] It is not indicated whether the pitch is indoors or outdoors.
[3] Ud fra de detaljerede oplysninger fra en kommune må det forventes, at DBU´s tal i vedligeholdelsesvejledningen er usikre i forhold til det reelle saltforbrug på nogle af banerne.
[3] Based on detailed information from one municipality, DBU's figures in the maintenance guide must be expected to be somewhat unreliable in relation to the actual consumption of salt on some of the pitches.
Bilag C: DST kategorisering af smykker
Appendix C: DST categorization of jewelleries
Smykker på markedet i Danmark opdeles i statistisk henseende i en række kategorier.
Jewelleries on the market in Denmark can statistically be divided into a number of categories.
Eurostat og Danmarks Statistik anvender følgende koder:
Eurostat and Statistics Denmark use the following codes:
Smykker af ædelmetaller, med en underopdeling i syv kategorier (7113xxxx, 7114xxxx og 7115xxxx).
Jewelleries of precious metals, with a sub-division in seven categories (7113xxxx, 7114xxxx and 7115xxxx).
De syv kategorier, der ikke beskrives nærmere her, omfatter produkter af guld, sølv, platin, ædelstene, halvædelstene og perler.
The seven categories, which are not described in details here, include products of gold, silver, platinum, precious stones, semiprecious stones and pearls.
Disse typer smykker er generelt underlagt regler i den professionelle smykkeindustri, og metalindholdet kontrolleres af Ædelmetalkontrollen.
These types of jewelleries are in general placed under rules in the professional jewellery industry and the content of metal is controlled by the Danish assay office.
Bijouteri, der også opdeles i en række underkategorier:
Bijouterie (custom jewellery), which also can be divided into a number of sub-categories:
Bijouterivarer (undtagen manchet- og kraveknapper) af uædle metaller, der eventuelt er belagt med ædelmetaller, og som indeholder dele af glas (7117 1910).
Bijouterie goods (except sleevelinks and collar studs) of base metals which might be coated with precious metals and which contain parts of glass (7117 1910).
Varetekst: ”Bijouterivarer af uædle metaller med bestanddele af glas, undt manchetknapper og kraveknapper”
Text on goods: ”Bijouterie goods of base metals with parts of glass with exception of sleevelinks and collar studs”
Bijouteri (undtagen manchet- og kraveknapper) af uædle metaller, der eventuelt er belagt med ædelmetaller, uden dele af glas (7117 1991).
Bijouterie (except sleevelinks and collar studs) of base metals which might be coated with precious metals, without parts of glass (7117 1991).
Varetekst: ”Bijouterivarer af uædle metaller, uden bestanddele af glas, forgyldte, forsølvede el platinerede”
Text on goods:”Bijouterie goods of base metals, without parts of glass, gold-coated, silver-coated or platinum-coated”
Bijouteri af uædle metaller, der ikke er belagt med ædelmetal (7117 1999).
Bijouterie of artificial metals which are not coated with precious metal (7117 1999).
Varetekst: ”Bijouterivarer af uædle metaller, uden bestanddele af glas, ej forgyldte, forsølvede el platinerede”
Text on goods: ”Bijouterie goods of base metals, without parts of glass, not gold-coated, silver-coated or platinum-coated”
Bijouteri af andre materialer end uædle metaller (f.eks. læder, plast, træ, horn, mv.) (7117 9000).
Bijouterie of other materials than base metals (e.g. leather, plastic, wood, horn etc.) (7117 9000).
Varetekst: ”Bijouterivarer, undt af uædle metaller”
Text on goods: ”Bijouterie goods, except base metals”
Manchet- og kraveknapper af uædle metaller, eventuelt belagt med ædelmetal (7117 1100).
Sleevelinks and collar studs of base metals, with possible coating of precious metal (7117 1100).
Varetekst: ”Bijouterivarer af uædle metaller, også forsølvede, forgyldte el platinerede, manchetknapper og kraveknapper”
Text on goods: ”Bijouterie goods of base metals, also silver-coated, gold-coated or platinum-coated, sleevelinks and collar studs”
Undersøgelse og vurdering af kemiske stoffer i vinduesfarver
Survey and assessment of chemical substances in window colours
Sonja Hagen Mikkelsen, Sven Havelund og Anders Skibsted Mogensen, COWI A/S
Sonja Hagen Mikkelsen, Sven Havelund and Anders Skibsted Mogensen, COWI A/S
2 SAMMENSÆTNING AF OG TYPISKE INDHOLDSSTOFFER I HOBBYFARVER
2 COMPOSITION OF AND TYPICAL CONSTITUENT SUBSTANCES IN HOBBY PAINTS
2.1 PIGMENTER 2.2 BINDEMIDDEL 2.3 BÆREMATERIALE 2.4 TILSÆTNINGSSTOFFER
2.1 PIGMENTS 2.2 PAINT BINDERS 2.3 VEHICLE 2.4 ADDITIVES
3.1 PRODUCENTER 3.2 LEVERANDØRER 3.3 VINDUESFARVER
3.1 MANUFACTURERS 3.2 SUPPLIERS 3.3 WINDOW COLOURS
4.1 PIGMENTER 4.2 BINDEMIDDEL 4.3 BÆREMIDDEL 4.4 TILSÆTNINGSSTOFFER
4.1 PIGMENTS 4.2 PAINT BINDERS 4.3 MEDIUM 4.4 ADDITIVES
5.2.1 GC/MS screening (ekstraherbare organiske stoffer) 5.2.2 Røntgen (grundstoffer) 5.2.3 Vandindhold ved Karl Fisher titrering 5.2.4 IR-screening
5.2.1 GC/MS screening (extractable organic substances) 5.2.2 X-ray analysis (elements) 5.2.3 Water content using Karl Fisher titration 5.2.4 IR screening
5.3.1 GC/MS screening (ekstraherbare organiske stoffer)
5.3.1 GC/MS screening (extractable organic substances)
5.4 SAMMENFATNING AF ANALYSER
5.4 SUMMARY OF ANALYSIS
6.1 BAGGRUND FOR UDVÆLGELSE AF STOFFER 6.2 UDVALGTE STOFFER 6.3 DATASØGNING
6.1 BASIS FOR THE SELECTION OF SUBSTANCES 6.2 THE SELECTED SUBSTANCES 6.3 DATA SEARCH
7.2 TOKSIKOLOGISK PROFIL FOR DIOXAZIN
7.2 TOXICOLOGICAL PROFILE OF DIOXAZINE
7.3 TOKSIKOLOGISK PROFIL FOR DIMETHYLOXAZOLIDIN
7.3 TOXICOLOGICAL PROFILE OF DIMETHYLOXAZOLIDINE
7.4 TOKSIKOLOGISK PROFIL FOR ETHYLMETHYLPYRIDIN
7.4 TOXICOLOGICAL PROFILE FOR ETHYLMETHYLPYRIDINE
7.6 TOKSIKOLOGISK PROFIL FOR METHENAMIN
7.6 TOXICOLOGICAL PROFILE OF METHENAMINE
7.7 TOKSIKOLOGISK PROFIL FOR DODECANTHIOL
7.7 TOXICOLOGICAL PROFILE OF DODECANTHIOL
7.8 TOKSIKOLOGISK PROFIL FOR 2-ETHYLHEXYLACRYLAT
7.8 TOXICOLOGICAL PROFILE OF 2-ETHYLHEXYLACRYLATE
7.9 TOKSIKOLOGISK PROFIL FOR PIGMENT RED 146
7.9 TOXICOLOGICAL PROFILE OF PIGMENT RED 146
7.10 TOKSIKOLOGISK PROFIL FOR PIGMENT YELLOW 138
7.10 TOXICOLOGICAL PROFILE OF PIGMENT YELLOW 138
ANDEN ANVENDT LITTERATUR OG BENYTTEDE DATABASER:
OTHER LITERATURE AND DATABASES CONSULTED:
Miljøstyrelsen har iværksat en indsats for at belyse forbrugernes udsættelse for og risiko i forbindelse med kemiske stoffer i forbrugerprodukter.
The Danish EPA has undertaken an initiative to examine consumer exposure to chemical substances in consumer products and the associated risks.
Det er projektets formål at kortlægge hvilke indholdsstoffer, der findes i vandbaserede vinduesfarver både med og uden CE-mærkning.
The object of the project is to carry out a survey of the constituent ingredients of water-based window colours, both those which are CE marked and those which are not.
Kortlægningen er baseret på oplysninger fra producenter, leverandører og uafhængige rådgivere.
The survey is based on information from producers, suppliers and independent consultants.
Det er desuden formålet at foretage en humantoksikologisk vurdering af udvalgte stoffer i produkterne, samt at estimere omfanget af den eksponering forbrugerne udsættes for, hvis muligt.
Yet another object is to carry out a human toxicological evaluation of selected substances in the products and, if possible, give an estimate of the extent of consumer exposure to these products.
Den humantoksikologiske vurdering foretages med henblik på at give input til eventuel efterfølgende risikovurdering, hvor der lægges vægt på børns mulige eksponering for stofferne.
The human toxicological evaluation was undertaken with a view to producing input for a possible subsequent risk assessment with emphasis on the possible exposure of children to these substances.
Samtidig er det formålet at dokumentere indholdet af udvalgte kemiske stoffer gennem kemiske analyser af et antal produkter, som findes på markedet.
Moreover, the project is aimed at documenting the content of selected chemical substances through chemical analysis of a number of products to be found in the market.
Afslutningsvis er det formålet at vurdere behovet for yderligere kemiske analyser på baggrund af de fremkomne resultater.
Finally, the purpose was to assess the need for further chemical analysis based on the results produced.
Projektrapporten "Undersøgelse og vurdering af kemiske stoffer i vinduesfarver" indeholder en oversigt over producenter hvis produkter findes på det danske marked, de vigtigste leverandører af produkterne samt de produkter som findes på det danske marked.
The project report "Examination and Evaluation of Chemical Substances in Window Paints" contains a review of the producers whose products are available on the Danish market, the most important suppliers of these products and of the products available on the Danish market.
I oversigtsform er vinduesfarvernes indholdsstoffer angivet - kategoriseret som pigmenter, bindemidler og tilsætningsstoffer.
The constituent substance are presented in table form - classified as pigments, vehicles and additives.
Stoffernes kemiske navn, formel, CAS nr., og udvalgte fysiske egenskaber er angivet.
The chemical name, chemical formula, CAS no. and selected physical properties are given for each substance.
Projektet blev begyndt i november 2001.
The project was initiated in November 2001.
Første del blev afsluttet i december 2001 og anden del i juni 2003.
The first stage was completed in December 2001 and the second in June 2003.
Projektet er gennemført af COWI.
The project was carried out by COWI.
MILJØ-KEMI Dansk Miljø Center A/S, nu Eurofins Danmark A/S har foretaget analyser af udvalgte vinduesfarver.
MILJØ-KEMI Dansk Miljø Center A/S, now named Eurofins Danmark A/S carried out analysis on selected window colours.
Projektteamet bestod af Sonja Hagen Mikkelsen (projektansvarlig), Sven Havelund, Anders Skibsted Mogensen og Frank Stuer-Lauridsen (kvalitetsansvarlig).
The project team consisted of Sonja Hagen Mikkelsen (project officer), Sven Havelund, Anders Skibsted Mogensen and Frank Stuer-Lauridsen (quality assurance).
Panduro har under hørringsperioden henledt opmærksomheden på, at produktet ”SunArt” produceret af Palmer Paint Products ikke kan betegnes som en ”vinduesfarve”.
During the hearing Panduro have pointed out that the product “SunArt” manufactured by Palmer Paint Products cannot be described as a “window paint”.
Produktet er en meget tyndtflydende maling, der kan bruges på emner af glas eller akryl.
The product is a very thin fluid paint, which may be used on glass or acrylic.
Forkortelsesliste CAS nr.
List of abbreviations CAS no.
C.I. nr.
C.I. no.
Kow Oktanol/vand fordelingskoefficient LC50
Kow Octanol-Water Partition Coefficient LC 50
Den koncentration af et kemikalie, som medfører at 50% af forsøgsdyrene dør (Lethal concentration)
The concentration of a chemical that results in the death of 50% of test animals (Lethal Concentration)
Den dosis af et kemikalie, som medfører at 50% af forsøgsdyrene dør (Lethal dose)
The dose of a chemical that results in the death of 50% of test animals (Lethal Dose)
Giftig ved hudkontakt
Harmful by inhalation
Meget giftig for organismer, der lever i vand
Irritating to respiratory system
Kan give overfølsomhed ved indånding og ved kontakt med huden
May cause sensitization by skin contact
i overensstemmelse med ASTM D
Combinations of R-phrases
Heraf er nogle identificeret med navn og andre som stofgruppe.
May cause sensitization by inhalation and skin contact
I litteraturen er der endvidere rapporteret om krydsallergi med methylmethacrylat, som blandt andet findes i lime.
As a consequence, there is a need to chart the substances that consumers may be exposed to during use.
Twenty pigments including both inorganic and organic substances are identified in the survey.
Only one pigment, copper phthalocyanine, containing a heavy metal was found.
Among the organic pigments, azo-pigments and polycyclic pigments have been identified.
One of the inorganic pigments identified during the survey contained heavy metals.
Only one pigment, copper phthalocyanine, containing heavy metal has been identified.
All the window colours included in the survey were water-based.
None of the inorganic pigments identified in the survey contain heavy metals.
The primary paint binders were acrylates, often thermoplastic (meth)acrylates.
Additives include among others thickeners, surfactants, preservatives, anti foaming agents and solvents (co-solvents).
Additives include thickening agents, surfactants, preservatives, anti-foaming agents and solvents (cosolvents).
In windows colour, preservatives like isothiazolones and bronopol are used.
Preservatives such as isothiazolones and bronopol are used in window colours.
These preservatives are also used in CE marked products.
These preservatives are also found in CE marked products.
A range of glycols and alcohols are furthermore found in this type of products.
The window colours also contain a number of glycols and alcohols.
ASTM D 4236: Americal standard for labelling of Arts and crafts materials concerning chronic health hazards.
ASTM D 4236: American standard for the marking of arts and crafts materials for chronic health hazards.
ACMI: Art & Creative Materials Institute, Inc.
identified by name and others by substance group.
products are between 2.3 to 5,500 mg/kg corresponding to 0.00023% and 0.55% in the products.
The levels contained in the various products vary between 2.3 and 5500 mg/kg, equivalent to 0.00023% to 0.55% in the products.
Other substances identified in high concentrations in a single product are 'unidentified phthalates' (two peaks) measured at 2,7003,100 mg/kg (double measurement) corresponding to 0.
Other substances found in high concentrations in a single product are unidentified phthalates (two peaks), which upon double determination were measured at 2700-3100 mg/kg, equivalent to 0.
Other substances are found in concentrations ranging from about 1 mg/kg (0.0001%) up to 1,000 mg/kg (0.1%), most in the lower end.
Other substances were found in concentrations from approx. 1 mg/kg (0.0001%) and up to approx. 1000 mg/kg (0.1%), mostly at the lower end.
This is also the case for the substances selected for toxicological evaluation based on the results from the chemical analysis.
This was also the case with products selected for toxicological assessment based on the chemical analysis.
The concentrations are therefore below the general minimum limits used for classification according to Statutory Order No. 329 of 16 May 2002 from the Ministry of Environment on classification, packaging, labelling, sale and storage of chemical substances and products (classification order).
Thus we are dealing with concentrations below the general triviality limits stipulated in the Danish EPA's Statutory Order No. 329 of 16 May 2002 on the classification, packaging, labelling, sale and storage of chemical substances and products (the Classification Statutory Order).
Among the metals, lead, copper, aluminium and titanium have been measured.
Among the metals found were lead, copper, aluminium and titanium.
Based on the survey and the results from the chemical analysis, 10 substances are selected for toxicological evaluation.
On the basis of the survey and the results of the chemical analysis carried out, 10 substances were selected for toxicological assessment.
The substances are:
These are as follows:
Of the 10 evaluated substances, three are on the List of dangerous substances and two substances are on the Danish EPA's guidance list for self classification.
Of the 10 substances investigated, three are included on the List of Dangerous Substances and two substances are on the Danish EPA's guideline list for selfclassification.
For these substances toxicological literature has been available which supports and to some extent supplements the information expressed through the classification.
Literature has been found for these substances that supports and to some extent adds to the information conveyed by the classification.
For the five other substances nothing or only very limited information on toxicological properties has been available in the searched literature.
Only extremely limited or no data at all has been found that would elucidate on the toxicological effects of the five other substances.
This is also the situation regarding NOAEL values, which are only referred in very few of the examined studies.
This also applies to information on possible NOAEL values, which were established/referred to in only very few of the examined studies.
There is however, always reason for concern in relation to children's exposure to sensitising substances even in low concentrations.
The permitted limit in cosmetics indicates that the substance is not considered a problem at this concentration.
In the reviewed literature it is mentioned that dodecanthiol has a high sensitising potential.
The literature examined mentioned that dodecanethiol possesses a high sensitization potential.
No further documentation for this information has been identified and also no further information about the relation between exposure and allergic reactions.
However, no additional documentation was found to substantiate this information, nor was information found on the correlation between exposure and the triggering of an allergic reaction.
Patch testing in humans with a solution of 0,5% 2-ethylhexylacrylat did result in allergic dermatitis in already sensitised individuals.
Patch tests on humans using solutions of 0.5% 2-ethylhexylacrylate triggered allergic dermatitis in already sensitized individuals.
No information has been found about the relation between exposure and primary sensitisation.
No information on the correlation between exposure and primary sensitization was found.
For both dodecanthiol and 2-ethylhexylacrylate no documentation has been found about the sensitising potential of the substances and thereby the risk for children using windows colour containing these substances.
Thus, neither for dodecanethiol or 2-ethylhexylacrylate has any real documentation been found for the sensitizing potential of these substances and consequently the risk children may be exposed to through the use of window colours containing these substances.