North Star QRA Update Chlorine and VCM Plant (Rafnes)

Total Page:16

File Type:pdf, Size:1020Kb

North Star QRA Update Chlorine and VCM Plant (Rafnes) Working together for a safer world North Star QRA Update Chlorine and VCM plant (Rafnes) Report for: Wood Report no: PRJ11090011 Rev: Final Date: 11 January 2019 Document history Revision Date Description/changes Changes made by Draft 30.11.2018 First issue of report Andrea Risan / Ingebjørg Valkvæ / Stian Jensen Final 11.01.2019 Comments from client Andrea Risan / Ingebjørg Valkvæ incorporated Executive summary Lloyds Register (LR) has been engaged by Wood and INOVYN Norge to conduct an update of the quantitative risk assessment (QRA) of the Chlorine and VCM plant at the Rafnes Industrial Site (Grenland, Norway) to accommodate any changes in the risk picture due to the North Star project. The North Star project includes implementation of several modifications to the facility which will increase the total production capacity with around 10 %. The QRA update is conducted by using the existing risk model of the facility and adding the events potentially caused by the planned modifications. A similar approach as applied in the existing QRA is applied in the risk assessment of the North Star modifications. In that manner the risk level before and after the modification can be compared. The risk acceptance criteria proposed by DSB are applied in the study. Hence, the focus in the study is directed towards major accident events that may cause fatal exposure outside of the boundary of the facility. The main conclusion of the study is that the North Star project only contributes with a modest risk increase to third parties, and that the main risk drivers remain unchanged after the update. It is still toxic releases of chlorine and HCl that dominates the risk picture, in addition to BLEVE events in the VCM storage area. The calculated risk picture is shown in the below figure. Report no: PRJ11090011 Rev: Final Page ii Date: 11 January 2019 ©Lloyd’s Register 2019 Glossary/abbreviations ALARP As Low As Reasonably Practicable AT The Norwegian Labour Inspection Authority (Arbeidstilsynet). A governmental agency under the Ministry of Labour, focused on occupational safety and health BLEVE Boiling Liquid Expanding Vapour Explosion CFD Computational Fluid Dynamics DSB Norwegian Directorate for civil protection (Direktoratet for Samfunnssikkerhet og Beredskap) EDC Ethylene DiChloride, 1,2-dichloroethane ESD Emergency Shut Down EX Ex-equipment or explosive protected equipment, both electric and mechanical. FTM Forslag Til Modifikasjoner Hazardous substances Flammable, reactive, pressurised and explosive substances HAZID Hazard Identification Report no: PRJ11090011 Rev: Final Page iii Date: 11 January 2019 ©Lloyd’s Register 2019 HCl Hydrogen Chloride HTDC High Temperature Direct Chlorination IR Individual Risk LFL Lower Flammability Limit LNF Landbruk-, Natur- og Friluftsområde LOC Loss Of Containment OHCL Oxy HydroChlorination PSD Process Shut Down QRA Quantitative Risk Analysis RAC Risk Acceptance Criteria Safeti Safeti QRA software tool - A user-friendly, industry standard method for carrying out Quantitative Risk Assessments (QRA) of onshore process, chemical and petrochemical facilities. Developed by DNV-GL. Third party (3rd person) People outside the production plant that may be affected by its activities. (2nd person: People that are not directly related to the operation of the plant, but benefit from being close to the plant 1st person: People who are directly involved in the operations of the plant, i.e. the employees at the plant) VCM Vinyl Chloride Monomer Report no: PRJ11090011 Rev: Final Page iv Date: 11 January 2019 ©Lloyd’s Register 2019 Table of contents Page 1 Introduction 1 1.1 Background 1 1.2 Objective 1 1.3 Scope of work 1 1.4 Presumptions and limitations 1 1.4.1 Presumptions 1 1.4.2 Limitations 1 1.5 Regulations and standards 2 2 Framework 2 2.1 Methodology 2 2.2 Assumptions and input data 4 2.3 Acceptance criteria 4 3 System description 5 3.1 General description 5 3.2 Process description 5 3.2.1 Chlorine – INOVYN scope 5 3.2.2 VCM – Wood scope 6 3.3 North Star project 7 3.3.1 VCM plant modifications 7 3.3.2 Safety measures for the new HTDC module 8 3.3.3 Water curtain in the HTDC module 8 3.3.4 Chlorine plant modifications 9 3.4 Safety measures 9 3.4.1 Pressure monitoring and shutdown 9 3.4.2 Chlorine absorption system 9 3.4.3 Gas detection and emergency shutdown 9 3.4.4 Fire proofing of storage spheres 9 3.4.5 Emergency preparedness 9 4 Selection of hazardous events 9 4.1 Existing QRA 9 4.2 Scenarios for the new HTDC module 11 4.3 Scenarios for the new OHCL reactor 12 4.4 Risk screening of other North Star modifications 12 5 Frequency analysis 14 6 Consequence analysis 15 6.1 Event tree 15 6.2 Fatality criteria 16 6.3 Consequence modelling 16 7 Risk picture and risk evaluation 18 7.1 Total risk picture 18 Report no: PRJ11090011 Rev: Final Page v Date: 11 January 2019 ©Lloyd’s Register 2019 7.2 Risk from the chlorine plant 19 7.3 Risk from the VCM plant 21 7.4 Individual risk at nearest resident 24 8 Uncertainties 26 9 Potential conservatism in the QRA 26 9.1 Release durations and transient effects 26 9.2 Terrain effects 27 9.3 Release modelling 27 9.4 Event frequencies 27 9.5 BLEVE 27 9.6 Flash fire envelope 27 10 Conclusion and recommendations 28 10.1 Recommendations 28 10.2 Conclusions 28 11 References 29 Appendix A – Assumptions and input data Appendix B – Risk screening workshop – VCM plants Appendix C – Risk screening workshop – Chlorine plant Report no: PRJ11090011 Rev: Final Page vi Date: 11 January 2019 ©Lloyd’s Register 2019 1 Introduction 1.1 Background Lloyd’s Register (LR) has been engaged by Wood and INOVYN Norge to carry out an update of the quantitative risk assessment (QRA) for INOVYN’ s Chlorine and Vinyl Chloride Monomer (VCM) plant at the Rafnes Industrial Site (Rafnes) conducted in 2015 (Ref. /1/). The North Star project introduces several modifications to the Chlorine and VCM plant in order to increase the production capacity of the plant. The modifications include: • Installation of a new High Temperature Direct Chlorination (HTDC) module • Replacing the existing Oxy HydroChlorination (OHCL) reactor with a new one • Several other modifications to process vessels and equipment in the VCM plant to allow for the increased capacity • Installation of a new electrolyser in the chlorine plant • Replacement of the hydrogen compressor, chlorine compressor and chlorine cooler. INOVYN Norge is classified as a so called major accident facility according to “Storulykkeforskriften” (Ref. /9/). Hence, the facility is required by regulations to minimize the risk for major accidents. The QRA can be seen as part of the effort to reach this objective. 1.2 Objective The objective of the QRA update is to investigate the impact of the North Star project on the existing risk picture at INOVYN’s facility at Rafnes. The modifications will be assessed and included in the existing QRA of the facility. Potential risk drivers will be identified, and it will be evaluated if the project introduces significant change in the risk for third parties. The proposed risk acceptance criteria by DSB (Ref. /2/) are applied in the risk assessment. 1.3 Scope of work The scope of work involves using the risk model developed in the existing QRA of INOVYN’s facility at Rafnes as a starting point. The risk model is implemented using the Safeti software. Events introduced by the North Star project will be handled in a similar manner as in the existing QRA by using, e.g., the same event frequency references, fatality criteria and overall assumptions as a basis. The focus in the QRA is to address major accidental events that may influence the extent of risk zones (“hensynssoner” in Norwegian) around the facility. 1.4 Presumptions and limitations 1.4.1 Presumptions The following presumptions apply to the study: 1. Normal operation including regular shut down and maintenance and start up activities are the base of the QRA. 2. If risk reducing measures are disengaged during operation, it is a prerequisite that compensating measures are implemented so that the barrier’s function is kept. If compensating measures are not taken, the QRA is not valid. 1.4.2 Limitations The following limitations apply to the study: 1. Events while ship is at sea or mooring are not included 2. The ships on-board systems (tanks, pumps, piping) are not included Report no: PRJ11090011 Rev: Final Page 1 Date: 11 January 2019 ©Lloyd’s Register 2019 3. The tunnel with export pipelines to Herøya is not included. A separate risk assessment for the tunnel has been conducted, Ref. /3/ 4. Escalation effects have not been quantified. An escalation is defined as an initial event on the site, e.g. a fire that impairs other equipment containing flammable or toxic material on the same site. Thereby leading to a larger fire or more severe toxic effects. One exception is the inclusion of Boiling Liquid Expanding Vapour Explosion (BLEVE) events in the QRA. A BLEVE can be considered as an escalated event, since a prerequisite for such a scenario to occur is long exposure time to relatively high heat loads, i.e. fire exposure. 5. Domino effects, e.g. events where fire and explosion triggers new release scenarios (or other effects) from equipment in adjacent facilities, have not been calculated specifically. Domino effects are discussed in the risk analysis from 1991 and 1998 (Ref. /4/ and /5/) and in the report "Vurdering av dominoeffekter mellom fabrikkanleggene på Borealis AS, Noretyl AS og Hydro Polymers AS i forbindelse oppdatering av Sikkerhetsrapporten for Hydro Polymers og Noretyl", Ref.
Recommended publications
  • Eradication of Introduced Signal Crayfish Pasifastacus Leniusculus Using the Pharmaceutical BETAMAX VET.®
    Aquatic Invasions (2010) Volume 5, Issue 1: 75-81 This is an Open Access article; doi: 10.3391/ai.2010.5.1.9 © 2010 The Author(s). Journal compilation © 2010 REABIC Proceedings of the 16th International Conference on Aquatic Invasive Species (19-23 April 2009, Montreal, Canada) Research article Eradication of introduced signal crayfish Pasifastacus leniusculus using the pharmaceutical BETAMAX VET.® Roar Sandodden1* and Stein Ivar Johnsen2 1National Veterinary Institute, Section for Environmental and Biosecurity Measures. Tungasletta 2. NO-7485 Trondheim, Norway 2Norwegian Institute for Nature Research (NINA). Fakkelgården, N-2624 Lillehammer, Norway E-mail: [email protected] (RS), [email protected] (SIJ) *Corresponding author Received: 28 May 2009 / Accepted: 23 November 2009 / Published online: 6 January 2010 Abstract Signal crayfish Pasifastacus leniusculus were first discovered in Norway in the Dammane area of Telemark County in October 2006. This introduced population was found to be infected with the oomycete Aphanomyces astaci, the causative agent of crayfish plague. The Dammane watershed consists of 5 small ponds, the largest with a surface area of approximately 2000 m2. The Norwegian National Veterinary Institute conducted a feasibility study for the eradication of the Dammane signal crayfish population at the request of the Norwegian Food Safety Authority and Directorate for Nature Management. This study recommended the use of the pharmaceutical BETAMAX VET.®, followed by pond drainage as a feasible course of action. BETAMAX VET.® is a cypermethrin-based pharmaceutical developed for treatment of salmon louse (Lepeophtherius salmonis) infestations of farmed Atlantic salmon (Salmo salar). Cypermethrin is a synthetic pyrethroid and a common agent in many insecticides licensed throughout Europe.
    [Show full text]
  • Green Industry Cluster.Pdf
    Til Vestfold og Telemark fylkeskommune Fra Green Industry Cluster Porsgrunn 31.05.2021 Innspill til de regionale vannforvaltningsplanene for Vestfold og Telemark Følgende forslag til plandokumenter er lagt ut på høring og offentlig ettersyn: • Forslag til regional plan for vannforvaltning 2022-2027 i Vestfold og Telemark vannregion • Forslag til regionalt tiltaksprogram 2022-2027, Vestfold og Telemark vannregion • Forslag til handlingsprogram 2022-2027, Vestfold og Telemark vannregion Det vises til «Høringsbrev» datert 04.03.2021 fra Vestfold og Telemark Fylkeskommune der det bes om innspill i forhold til ovennevnte dokumenter. Innledning Industrien i Grenland har helt siden tidlig på 1970 tallet da de første konsesjonene/tillatelsene ble gitt, vært opptatt av og har arbeidet målbevisst for å redusere utslipp til luft og vann. Det har vært et nært og konstruktivt samarbeid med myndighetene lokalt, regionalt og nasjonalt og det er oppnådd betydelige miljøforbedringer i Grenland. Det gode samarbeidet med myndighetene ønsker vi å videreføre for å utvikle Industrien i Grenland med etablering av nye arbeidsplasser. Green Industry Cluster (GIC) er en industriklynge for landbasert og offshore industri i regionen med mål om økt vekst og verdiskaping i industrien. Dette krever et godt samarbeid med myndigheter og forvaltere av rammevilkår med konsekvenser for næringsvirksomhet. Vi ønsker å gi en samlet tilbakemelding til fylkeskommunen. Utkast til Forvaltningsplan Utkast til Forvaltningsplanen henviser til § 12 i Vannforskriften som har som hovedregel at det IKKE skal gis tillatelse til ny aktivitet eller nye inngrep som kan medføre at miljømålene IKKE nås eller at miljøtilstanden forringes. Det synes å være urimelig og direkte negativt for videre industriutvikling i Grenland hvis dette skal forstås slik at det ikke vil bli gitt nye eller økte utslippstillatelser generelt.
    [Show full text]
  • Valuing the Benefits of Remediating Contaminated Marine Sediments – a Case Study from the Grenlandsfjord Norway
    Valuing the benefits of remediating contaminated marine sediments – a case study from the Grenlandsfjord Norway David N. Barton Norwegian Institute for Water Research(NIVA) 5th International SedNet Conference 27-29th May, 2008, Oslo Source: http://www.miljostatus.no/templates/pagewide____2795.aspx E-mail: [email protected] Tel: +47 924 42 111 Acknowledgements • SEDFLEX project, Norwegian Research Council grant 139032/720 under the Profo Programme • Norsk Hydro and County Government Telemark for funding the survey •Ståle Navrud (IØR-UMB), for assistance with survey design and data analysis •Heid Bjørkeslett and Ingrid Lilleby (IØR-UMB) for conducting the household surveys Overview 1. Contingent valuation of household willingness to pay to remove dietary health advisories around the Grenlandsfjords 2. Challenges to willingness to pay as a measure of benefits of sediment remediation measures Grenland fjords Source: http://www.miljostatus.no/templates/pagewide____2795.aspx Source: SEDFLEX Project Willingness to pay for reducing time to removal of seafood consumption advisories Probability Contaminant concentration in seafood Remediation benefits (B) Costs (C) US$ Alternative 0: No measures / natural recovery Advisories limit value (4 ng/kg ww whole cod) Remediation Alternative 1: Capping/dredging cont. sediment benefits Year Source: adapted from Magnussen et al. 2006 Willingness to pay for reducing time to removal of seafood consumption advisories Probability Costs (C) Contaminant concentration in seafood Remediation benefits (B) US$ Alternative
    [Show full text]
  • Statistisk Analyse Av Data for Dioksin-Nivåer I Organismer I Frierfjorden/Grenlandsområdet
    Statlig program for forurensningsovervåking Statistisk analyse av data for dioksin-nivåer i organismer i Frierfjorden/Grenlandsområdet Prosjektleder: Birger Bjerkeng Medarbeider: Anders Ruus SFT-rapport 860/2002 ISBN 82-577-4255-4 NIVA-rapport 4595-2002 TA-1916/2002 Statistisk analyse av data for dioksin-nivåer i organismer i Frierfjorden/Grenlandsområdet (TA-1916-2002) Forord Overvåkingen i Grenlandsfjordene er en del av Statlig program for forurensningsovervåking, som administreres av Statens forurensningstilsyn (SFT). Undersøkelsen finansieres av SFT, den lokale industrien (Hydro Porsgrunn Industripark, Borealis A/S, Union A/S og Eramet Norway avd. Porsgrunn (tidligere Elkem Mangan KS-PEA), samt kommunene Skien, Porsgrunn og Bamble. Denne rapporten omfatter en grundig statistisk vurdering (i sin helhet utarbeidet av Birger Bjerkeng) av utviklingen i dioksininnhold (uttrykt som ’toksiske ekvivalenter’) i torsk, ørret, skrubbe, krabbe og blåskjell fra Grenlandsområdet. Rapportens innhold var første gang presentert som et vedlegg i Overvåkingsrapport 835/01 (TA-nr. 1832/2001) ”Overvåking av miljøgifter i fisk og skalldyr fra Grenlandsfjordene 2000”, forfattet av Knutzen et al. På initiativ fra Kristoffer Næs og etter ønske fra SFT presenteres den statistiske vurderingen her i rapportform, tilrettelagt av Anders Ruus. Oslo, 1. desember 2002 Birger Bjerkeng forsker Statistisk analyse av data for dioksin-nivåer i organismer i Frierfjorden/Grenlandsområdet (TA-1916-2002) Innhold Sammendrag 5 Summary 7 1. Innledning 7 2. Materiale og metoder
    [Show full text]
  • Prosjekt «Ren Frierfjord» Og Tilgrensende Vassdrag
    Prosjekt «Ren Frierfjord» og tilgrensende vassdrag Forslag til vedtak: 1. Kommunene i Grenlandsrådet slutter seg til beskrivelsen knyttet til forurensningssituasjonen i Frierfjorden og tilgrensende vassdrag i saksframstillingen, og vil jobbe for å forbedre miljøtilstanden. 2. Kommunene i Grenland ønsker å bidra til en klar forbedring av forurensningssituasjonen i Frierfjorden og tilgrensende vassdrag, gjennom å starte et forprosjekt med mål om å: a. Kartlegge kunnskapsgrunnlaget b. Kartlegge tilgrensede problemstillinger som rensekrav til avløp c. Kartlegge interessenter og samarbeidspartnere lokalt, regionalt og statlig d. Utforme en konkret søknad/innspill til statsbudsjettet for å finansiere et prosjekt som skal gjennomføre konkrete tiltak for å forbedre miljøtilstanden i Frierfjorden og tilgrensende vassdrag 3. Sekretariatet kommer tilbake til Grenlandsrådet med ny sak i løpet av 1. halvår 2021 som konkretiserer et slikt forprosjekt. Bakgrunn: Bamble kommune har fremmet forslag til områdereguleringsplan for industriarealer og ny havnekapasitet på Frier Vest. Fylkesmannen har gått til innsigelse med hjemmel i vannforskriften (Forskrift om rammer for vannforvaltningen) § 12. Bakgrunnen er særlig bekymring for oppvirvling av gamle, forurensede bunnsedimenter ved oppankring på Frierflaket. Bamble kommune er enig at det er utfordringer med forurensede masser i sedimentene i vannområdet og forurensningssituasjonen generelt, men mener at tiltak for å møte dette ikke kan legges på en enkelt reguleringsplan. Bamble kommune har neppe hjemmel etter plan- og bygningsloven til å pålegge bestemmelser (forbud mot oppankring) i en annen kommune og i myndighetsområdet for Kystverket (farleder og oppankringsplasser). Det er grunn til å tro at flere nye tiltak i vannområdet også i andre kommuner som grenser til vannområdet kan utløse innsigelse fra Fylkesmannen om ikke forurensningssituasjonen adresseres av kommunene i Grenland.
    [Show full text]
  • Biomarker Responses in Fish from Frierfjord and Eidanger
    View metadata, citation and similar papers at core.ac.uk brought to youCORE by provided by NIVA Open Access Archive REPORT SNO 4857-2004 Biomarker responses in fish from Frierfjord and Eidanger Frierfjorden Eidangerfjorden Kastebukta [ [ Kalvsundet Langesundsfjorden 3,5 3,0 2,5 2,0 [ Vesle1,5 Arøya female 1,0 0,5 0,0 -0,5 3,5 3,0 log (EROD) 2,5 2,0 1,5 male 1,0 0,5 N Langesundsbukta0,0 -0,5 E EF EF EF S 0246810Kilometers Contaminants in the Grenland fjords Biomarker responses in fish from Frierfjord and Eidanger Subproject 3 – biological effects NIVA 4857-2004 Preface The current report forms part of a 3-year project on the abiotic transport, bioaccumulation and effects of dioxins and dibenzofurans in Frierfjord and Eidanger. The main project was managed by Kristoffer Næs, NIVA, and was a collaboration between NIVA, IMR (Flødevigen) and NGI. NIVA was in charge of the activity described herein, which was performed in collaboration with IMR (collection of material, herring egg exposure). Oslo, 5. July, 2004 Ketil Hylland NIVA 4857-2004 Contents Summary 6 1. Introduction 7 2. Interpretation of biological effects 8 2.1 Baseline responses 8 2.2 Comparing populations 9 2.3 Correcting for other factors 10 3. Materials and methods 11 3.1 Collection and sampling 11 3.2 Calculation of condition and LSI 11 3.3 Sample treatment 11 3.4 Analysis of protein 11 3.5 Analysis of CYP1A protein 11 3.6 Analysis of EROD (CYP1A activity) 12 3.7 Analysis of GST activity 12 3.8 Analysis of glutathione reductase 12 3.9 Analysis of vitellogenin 12 3.10 Statistical analyses 12 4.
    [Show full text]
  • Common Procedure for the Skagerrak Coast Report 983/2007
    SPFO-Report: 983/2007 TA-number: 2253/2007 ISBN-number:978-82-577-5135-7 Employer: The Norwegian Pollution Control Authority (SFT) Executing research institution: Norwegian Institute for Water Research (NIVA) Common Procedure for Report the Skagerrak coast 983/2007 Eutrophication Status of the Norwegian Skagerrak Coast Norwegian Institute for Water Research – an institute in the Environmental Research Alliance of Norway REPORT Main Office Regional Office, Sørlandet Regional Office, Østlandet Regional Office, Vestlandet Akvaplan-NIVA A/S Gaustadalléen 21 Televeien 3 Sandvikaveien 41 P.O.Box 2026 N-0349 Oslo, Norway N-4879 Grimstad, Norway N-2312 Ottestad, Norway N-5817 Bergen, Norway N-9005 Tromsø, Norway Phone (47) 22 18 51 00 Phone (47) 37 29 50 55 Phone (47) 62 57 64 00 Phone (47) 55 30 22 50 Phone (47) 77 68 52 80 Telefax (47) 22 18 52 00 Telefax (47) 37 04 45 13 Telefax (47) 62 57 66 53 Telefax (47) 55 30 22 51 Telefax (47) 77 68 05 09 Internet: www.niva.no Title Serial No. Date Common Procedure for Identification of the Eutrophication Status 5400-2007 18.4.2007 of Maritime Area of the Oslo and Paris Conventions Report on the Eutrophication Status for the Norwegian Skagerrak Report No. Sub-No. Pages Price Coast O-26399 69 Author(s) Topic groups Distribution Jarle Molvær, Wenche Eikrem, Jan Magnusson, Are Pedersen and Oceanography and Open Torulv Tjomsland Marine Eutrophication Printed NIVA Geographical area Southern Norway Client(s) Client ref. Norwegian Pollution Control Authority 6006150 Abstract The Norwegian Skagerrak coast has been classified according to the OSPAR Common Procedure.
    [Show full text]
  • Porsgrunn.Pdf
    Utsikt over Porsgrunn med Frierfjorden. PO G R U ~I ~I [~ ~,ORSGR.UNN er den midterste av Telemark fylkes ~frCY~~,'~?~ femdragetsk]øbsteder.utløp i Frierfjorden.Byen ligger vedElven,Telemarkvass•som i det ovenfor liggende Nordsjø har samlet i sig" Vest• fjellenes" og "Østfjellenes" hovedavløp, går tvers igjennem Porsgrunn. Omtrent 2/3 av byen ligger på elvens østside (Østre Porsgrunn) og 1/3 ligger på vestre side (Vestre Pors• grunn). Begge bydeler forbindes ved en bro over det 200 m brede elveløp. Størsteparten av det terreng byen ligger på er flatt og stiger få meter over elvens nivå. Kun utover mot de til• støtende landdistrikter stiger terrenget tildels op til noe større høide. 3 Porsgrunns rådhus. Porsgrunn ligger i hjørnet mel1em tre landkommuner. Eidanger, Gjerpen og Solum herreder støter inn til byens grenser. På den annen side av den 3 km. brede Frierfjord ligger Bamble herred. De nærmeste byer er Skien ca. 6 km. nordenfor og Brevik ca. 10 km. søndenfor. Mot øst ligger Larvik i Vest• fold fylke ca. 30 km. borte. Fra havet er det ca. 17 km. seilled op til Porsgrunns havn. I et tidligere utgitt skrift om Porsgrunn heter det: "Porsgrunn er ingen gammel by. Kjøbstad blev den først i 1807, men dens oprindelse ligger dog meget lengre tilbake i tiden. Ca. 1650 oprettet kronen en tollbod på "den øde ø Porsgrunn". Herved blev stedet et slags centrum i fjorden. De gode havneforhold og stedets heldige be• liggenhet skapte gunstige betingelser for handel og skibs- 4 Gammel gård ved Osebro. Lerkuppelven. fart. Særlig på skibsfartens område har Porsgrunn gjennem tidene inntatt en ledende stilling, ikke bare i distriktet, men har været blandt de første sjøfartsbyer i landet.
    [Show full text]
  • Prosjekt «Ren Frierfjord» Presentasjon for Grenlandsrådet 27.11.2020
    Prosjekt «Ren Frierfjord» Presentasjon for Grenlandsrådet 27.11.2020 Kommunedirektør Geir H. Bjelkemyr-Østvang Bakgrunn • Selskapet Frier Vest AS ble opprettet i 2015 • INEOS, Grenland Havn IKS og Bamble kommune var eiere med 1/3 hver • I 2018 startet Frier Vest AS arbeidet med områderegulering av Frier vest • Formålet med planen er å legge til rette for videre industri- og næringsutvikling • Planen ble lagt frem til førstegangsbehandling i juni 2019, og deretter til offentlig ettersyn • Fylkesmannen fremmet innsigelse med hjemmel i Vannforskriften § 12 Kilde: Google Maps, foto av Knut Robert Sevland • Etter at innsigelsen ble fremmet, har reguleringsarbeidet stoppet opp i påvente av nødvendige avklaringer • Prosjektarbeidet har pågått videre - selskaper, rekruttering DL, dialog med mulig aktører. I dag BK og Grenland Havn. Plankart Frier Vest (nytt utviklingsselskap) Innsigelsen fra Fylkesmannen • Innsigelsen ble fremmet med bakgrunn i motstrid med Vannforskriften § 12 om ny aktivitet eller nye inngrep • I henhold til forskriften skal miljøtilstanden forbedres ved nye tiltak i vannområdet • Fylkesmannen er særlig bekymret for oppvirvling av gamle, forurensede bunnsedimenter ved oppankring på Frierflaket • Virksomhetene som etablerer seg i området vil kunne føre til økt skipstrafikk med økt oppankring Felles utfordring for Grenland • Forurensningssituasjonen i Frier, med tilgrensede vassdrag, er en felles utfordring for kommunene i Grenland • Forurensning er et problem i seg selv • Forurensningssituasjonen er et hinder for videre utvikling
    [Show full text]
  • Echo-Soundings in the Skagerrak. with Remarks on the Geomorphology
    Echo-soundings in the Skagerrak. With remarks on the geomorphology. By Olaf Holtedahl With 1 plate and 7 text-figures. Introduction. In a paper of 1956, published in "Geotektonisches Symposium zu Ehren von Hans Stille", the writer has briefly (pp. 59-60) mentioned Norwegian echo-sounding work carried out during the years 1953-55 and also reproduced two bottom-profiles across the Norwegian Channel from the Norwegian coast towards northern Jutland (cf. also Geology of Norway, N.G.U. 208, p. 354, 1960). In the said paper attention was drawn to the investigations by the Deutsches Hydrographisches Institut 1950-52 and especially to the very important paper of 1952 "Zur Geo logie der norwegischen Rinne" by the late Dr. Otto Pratje, an authority on submarine geology. In the present publication a more general account of the Norwegian work, with reproduction of a considerable number of sounding profiles will be given. The work was started1 in order to provide supplementary data concerning the submarine relief of the area shown in No. VII (the most southern one) of the series of coloured bathymetrical maps of the writer's publication of 1940, "The submarine relief off the Norwegian coast». To begin with the work was concentrated in the northernmost part of the Skagerrak area where amongst others, wc have the interesting trenches outside the Langesundsfjord and the Hvaler Islands. Soundings were carried out here in 1953 by M/S "Gunnar Knudsen", research vessel of Institutt for marin biologi, section A, of the University of Oslo, director Prof. J. T. Ruud. The Captain was the late H.
    [Show full text]
  • The Middle Ordovician of the Oslo Region, Norway", the Previous Research Is Dealt with More Extensively in a Special Chapter on a Historical Review
    THE MIDDLE ORDOVICIAN OF THE OSLO REGION, NORWAY 1 . Introduction to Stratigraphy. BY LEIF STORMER assisted by A. Heintz, G. Hennings�oen, S. Skjeseth and N. Spjeldnæs. With 6 p!ates and 16 figures in the text. CONTENTS. Abstract 38 Introduction . 38 The term Middle Ordovician . 41 Historical review. 45 The sections of the Oslo Region . 51 l. The Oslo-Asker District . 54 2. The Holmestrand District . 70 3. The Langesund-Gjerpen District . 70 4. The Sandsvær-Eiker District . 78 5. The Modum District . 82 6. The Ringerike District . 82 7. The Hadeland District . 88 8. The Feiring District . 94 9-11. The Mjøsa Districts . 95 9. The Toten District . 96 10. The Nes-Hamar District . 100 11. The Ringsaker District .................................... 108 Additional Districts. l. Snertingdal . 111 2. Hedmarksvidda ...... .................... 111 Comparison of the various districts and the sequences correlated with the international graptolite time scale . 112 The base of the Middle Ordovician . 114 The Ogygiocaris Series . 119 38 LEIF STØRMER The Upper Didymograptus Shale (4a a1-2) and the Ogygocaris-bronni ••••••••••.•••••••••••••.••••••••••••.•••.•••••• beds (4a a3-4) 119 The Chasmops Series .......................................... 123 The Ampyx Limestone (4a (3) and the Lower Chasmops Shale (4b a) 123 The Lower Chasmops Limestone (4b (3) and the Upper Chasmops Shale (4b y) and contemporaneous deposits .......................... 125 The Upper Chasmops Limestone (4b b) and contemporaneous deposits 126 A preliminary correlation chiefly with Swedish and Baltic sections. 129 A b s t r a c t : The present paper is the first in a series dealing with the stratigraphy, paleontology and tectonics of the Middle Ordovician of the Oslo Region, the latter comprising 11 districts located between Langesund and Ringsaker.
    [Show full text]
  • Dioxins Associated with Suspended Particulate Matter in Grenlandsfjords
    REPORT SNO 6144-2011 Dioxins associated with NIVA: Norway’s leading centre of competence in aquatic environments suspended particulate matter in NIVA provides government, business and the public with a basis for preferred water management through its contracted research, reports Grenlandsfjords (Norway) and development work. A characteristic of NIVA is its broad scope of professional disciplines and extensive contact network in Norway and abroad. Our solid professionalism, interdisciplinary working methods and holistic approach are key elements that make us an excellent advisor for government and society. Gaustadalléen 21 • NO-0349 Oslo, Norway Telephone: +47 22 18 51 00 • Fax: 22 18 52 00 www.niva.no • [email protected] Norwegian Institute for Water Research – an institute in the Environmental Research Alliance of Norway REPORT Main Office Regional Office, Sørlandet Regional Office, Østlandet Regional Office, Vestlandet Regional Office Central Gaustadalléen 21 Jon Lilletuns vei 3 Sandvikaveien 59 Thormøhlens gate 53 D Pirsenteret, Havnegata 9 NO-0349 Oslo, Norway NO-4879 Grimstad, Norway NO-2312 Ottestad, Norway NO-5006 Bergen Norway P.O.Box 1266 Phone (47) 22 18 51 00 Phone (47) 22 18 51 00 Phone (47) 22 18 51 00 Phone (47) 22 18 51 00 NO-7462 Trondheim Telefax (47) 22 18 52 00 Telefax (47) 37 04 45 13 Telefax (47) 62 57 66 53 Telefax (47) 55 31 22 14 Phone (47) 22 18 51 00 Internet: www.niva.no Telefax (47) 73 54 63 87 Title Report No.. Date Dioxins associated with suspended particulate matter- in the 6144-2011 March 2011 Grenlandsfjords (Norway) Project No.
    [Show full text]