ENVIRONMENTAL AUDIT OF THE SITES IMPACTED BY THE PROBO KOALA TOXIC WASTE DUMPING IN ABIDJAN, CÔTE D IVOIRE

Similar documents
SITE 2: VRIDI CANAL 1 (CAP LOGISTICS) ENVIRONMENTAL AUDIT OF THE SITES IMPACTED BY THE PROBO KOALA TOXIC WASTE DUMPING IN ABIDJAN, CÔTE D IVOIRE

ENVIRONMENTAL AUDIT OF THE SITES IMPACTED BY THE PROBO KOALA TOXIC WASTE DUMPING IN ABIDJAN, CÔTE D IVOIRE

SITE 1: TREICHVILLE ENVIRONMENTAL AUDIT OF THE SITES IMPACTED BY THE PROBO KOALA TOXIC WASTE DUMPING IN ABIDJAN, CÔTE D IVOIRE

SITE 13: AKOUÉDO 3 ENVIRONMENTAL AUDIT OF THE SITES IMPACTED BY THE PROBO KOALA TOXIC WASTE DUMPING IN ABIDJAN, CÔTE D IVOIRE

ENVIRONMENTAL AUDIT OF THE SITES IMPACTED BY THE PROBO KOALA TOXIC WASTE DUMPING IN ABIDJAN, CÔTE D IVOIRE

BC CSR Omnibus Amendment: A Case Study on the Impacts to Environmental Investigation and Remediation

National Inventory of Potential Sources of Soil Contamination in Cyprus

IXPER 70C Calcium Peroxide CASE STUDY

gauging of site monitoring wells MW-1, MW-2 and MW-3 was completed on October 25, 2018 (tank field observation pipes were gauged as dry this day);

A Review of Environmental Impacts and Environmental Applications of Shredded Scrap Tires

Assessing the environmental impacts of landfill mining activities

January 13, Mr. Mike Zamiarski New York State Department of Environmental Conservation, Region East Avon Lima Road Avon, New York 14454

Guidelines For Disposal of Contaminated Solids in Landfills

75C Calcium Peroxide

VOLUME SECTION SUBSECTION PAGE 1 of 7

WA Waste Classification. Analytical Guide 2018 Update

WASTE ACCEPTANCE CRITERIA AND DEVELOPMENT OF SOIL TRIGGER VALUES FOR EPA-LICENSED SOIL RECOVERY FACILITIES

MUNICIPAL DRINKING WATER PRODUCED BY DORVAL DRINKING WATER TREATMENT PLANT 2016

Contaminated Land Assessment Guidance

E N V I R O N M E N T A L I N C O R P O R A T E D

Rhode Island Standards for Hydrocarbon Contaminated Groundwater a Groundwater Objectives (GA and GB) b

Table 30. Summary of benzene concentrations (mg/l). MCL=0.005 mg/l.

PIPELINE RISK ASSESSMENT

Limited Remedial Action Reference Documentation For Site Professionals

CETC CANMET Energy Technology Centre Hazardous Waste Combustion in a CFBC

TABLE 1-1 ENVIRONMENTAL SCREENING LEVELS AND CLEANUP/ACTION LEVELS FOR PETROLEUM CONSTITUENTS. Groundwater

Thomas G. Braga Manager, Research and Development. SulfaTreat, a Business Unit of M I L.L.C. A Smith/Schlumberger Company

Setting the Stage for Successful Reclamation Strategies. Session Number 19 Sponsored by: CAPLA Presented by: Paul Kelly

Table B1: Analytical Results for Nutrients in Surface Water

MARYLAND DEPARTMENT OF THE ENVIRONMENT 1800 Washington Boulevard Baltimore Maryland

This report was prepared by Stanley Abraham, Bioremediation of Hydrocarbon-Contaminated Soil

Summary of Findings: Understanding Health Impacts from Hydraulic Fracturing

Optimization of Volatile Petroleum Hydrocarbons Analysis by Automated Headspace Using Method Development Tools

Linking Risk and Sustainability

"INOGATE Technical Secretariat & Integrated Programme in support of the Baku Initiative and the Eastern Partnership energy objectives" Project

DESIGNING DRAINS AND SEWERS FOR BROWNFIELD SITES. Guidance Notes

Turnkey configurations for gas chromatographic analysis, including instrumentation, methods, supplies and service. Analysis of Natural Gas

City of Las Cruces, New Mexico INDUSTRIAL WASTE QUESTIONNAIRE AND PERMIT APPLICATION

Using PVC Sheet Piling for Organic Chemical Cut-off and Containment Barriers. A Whitepaper by: Steve Hargrave

LSPA Online Technical Journal

Imagine the result. Ms. Jeannette DeBartolomeo Oil Control Program Maryland Department of Environment 1800 Washington Boulevard Baltimore, MD 21230

ANALYTICAL METHODOLOGY FOR GROUNDWATER AND SOIL ASSESSMENT GUIDELINES

DECISION ON MARINE DISCHARGE CONSENT APPLICATION

EU ECOLABEL USER MANUAL GROWING MEDIA, SOIL IMPROVERS AND MULCH

Autumn Leaf Litter Composting Trial

Guidance Document Risk-Based Corrective Action (RBCA) For Residential and Commercial Heating Oil Systems. National Oilheat Research Alliance (NORA)

STRATEGIES FOR CHARACTERIZING SUBSURFACE RELEASES OF GASOLINE CONTAINING MTBE

Participating Schedule for 2018/19

Discharge and Discovery Reporting Standard. Saskatchewan Environmental Code

GAS SUPPLIER INTERCONNECTION PROJECT FACT SHEET

Environmental Assessment of Ogoniland Site Specific Fact Sheets ALUEJOR- ONNE

Borehole Logging Record

Midwest Analytical Services, Inc. "Where industry comes for answers." PRICE LIST 2009

North Carolina Cleanup Standards for Hydrocarbon Contaminated Groundwater

Obstructed or Non-Vertical Oriented Toxic Air Pollutant Permitting Emission Rates (TPER) Toxicants

Background. Pre-Design Investigation Scope. Thomas Campbell Project Manager. May 30, 2012

Clean Harbors (Sarnia) Air Monitoring Plan and Sampling Results

Toxicity Datasheets and

Agilent 7667A Mini Thermal Desorber MEASURE VOCS IN GAS MATRIX WHEN MOBILITY MATTERS

EPA Primary. (mg/l as CaCO3) (mg/l as CaCO3)

CORRECTIVE ACTION COMPLETION REPORT

Supplementary guidance for the selection of water pipes in land potentially affected by contamination

Calibration equipment

Environmental Assessment of Ogoniland Site Specific Fact Sheets WIIKARAGU- KPEAN

ASBG s Comparison of Queensland vs NSW and Victoria s Hazardous Waste Classifications

REPORT Study of Impact of Large Landfills on Environment of the Leningrad Oblast

Water Governance Benchmarking Criteria

FINAL PLAN OF REMEDIAL ACTION. Burns and McBride. South Market and A Streets August 19, 2008

New Jersey Private Well Water Test Reporting Form

Bio-Remediation General Information

PROTOCOL NO. 5: Petroleum Hydrocarbon Analytical Methods and Standards

List of Analytical Methods for Trade Waste

ADDITIONAL SAMPLING REPORT WITH SITE CLOSURE REQUEST BUILDING 311 NCDENR Incident Number: Marine Corps Base Camp Lejeune, North Carolina

Contaminated Media Management Plan. DEQ UST Site # Del Oeste Veterinary Clinic Prairie Road Eugene, Oregon

The Impact of Elevated Leachate Levels on LFG Generation and Recovery at MSW Landfills in Asia

North Dakota Oilfield Waste and TENORM Issues

WHY RAMSORB? PERFECT FOR: The Industrial Strength Absorbent That Makes Environmental Problems Disappear

WATER QUALITY ASSESSMENT OF RIVER RAVI AROUND LAHORE CITY

Carcinogens. lb/yr. lb/day

CLOSURE AND POST-CLOSURE OF LANDFILLS IN MALAYSIA CASE STUDIES

Krasny Bor: May October Monitoring: facts and opinion

LABORATORY TURNAROUND TIMES AND CHARGES

Submittal Guidelines for Imported Soil. Soil Review & Acceptance Process

Groundwater remediation with the use of PRB Technology. PRB TECHNOLOGY haw does it work and when to use it

Qualitycheck Proficiency Testing Schemes Independent external evaluation of the analytical competence of testing laboratories. Application Form

RE: Public Comment Period regarding proposed closure of the following four Leaking Underground Fuel Tank (LUFT) Cases:

Lambton Facility Update

Continental Aluminum Exposure Investigation Executive Summary

least two (2) being taken during "flush events", with the final baseline sampling to culminate in approximately October Any analyte detected

Clinical Laboratory of San Bernardino, Inc. Celebrating 50 Years of Analytical Service

Environmental Assessment of Ogoniland Site Specific Fact Sheets NWEEKOL/ZORBUKE, K.DERE

Treatment System Locations. Treatment System Sampling Activities and Analytical Results. June 15, 2011

Stage 10 Amendments to the Contaminated Sites Regulations

Keep Your Eye on the Sky - Clouds and Weather

Recent Field Applications of Activated Persulfate Including Petroleum Sites

Engineering sustainability the need for eco efficiency and eco effectiveness

Drinking Water Supply and

Can Analytical Methods Predict Bioavailability? Chris Swyngedouw Oct. 21, 2005 Remtech 2005

1. What is the cleanup level look-up table and where can I find it?

APPLICATION FOR SPECIAL DISCHARGE APPROVAL

Transcription:

ENVIRONMENTAL AUDIT OF THE SITES IMPACTED BY THE PROBO KOALA TOXIC WASTE DUMPING IN ABIDJAN, CÔTE D IVOIRE This series of fact sheets was prepared as part of UN Environment s environmental audit of the sites impacted by the Probo Koala toxic waste dumping in Abidjan, Côte d Ivoire. The fact sheets provide complete analysis results, observations and the recommendations for each of the sampling sites. They should be read in conjunction with the full assessment report, available at: www.unep.org/cotedivoire 1

Site Description Site name: Vridi Canal 2 (Petroci) UN Environment site reference no: 3 2

Spill History The site is located along the same road as Site 2, within the Vridi Canal industrial zone, on grounds owned by the Ivorian national oil company, Petroci. The site of interest represents the location at which the pipe connected to the drain into which Probo Koala wastes were dumped at Site 2 intersects with a concreted canal flowing to the lagoon. The pipework and canal were reportedly remediated by Trédi in 2006-2007, and continue to carry drainage to the lagoon. Approach One air sample, one groundwater sample and one surface water sample were collected at this site. As the pipe and canal were concreted, no soil samples were retrieved from this location. Assessment Criteria Three key sets of parameters were analyzed for groundwater samples, which together would constitute a theoretical fingerprint of the Probo Koala wastes: (i) sulfur; (ii) phenols; and (iii) hydrocarbons. In addition, a number of heavy metals that were included in the Government s contract for soil clean-up were also analyzed. Results for groundwater quality were compared against control site values (Site 19 at Anyama) and, in the absence of national standards for water quality, Dutch intervention values. It was not possible to compare surface water results, however, as Côte d Ivoire does not have a national standard for surface water quality, and surface water was not sampled at any of the control sites 3

Laboratory Analysis Findings Air Site 3 Control site 21 Parameters/units Vridi Canal 2 Agboville Dimethyl sulfide ppm v/v < 0.1 < 0.1 Ethyl mercaptan ppm v/v < 0.1 < 0.1 Methyl ethyl sulfide ppm v/v < 0.1 < 0.1 Carbonyl sulfide ppm v/v < 0.1 < 0.1 Tertiary butyl mercaptan ppm v/v < 0.1 < 0.1 Hydrogen sulfide ppm v/v < 0.1 < 0.1 Methyl tert-butyl ether µg/m3 ND ND Benzene µg/m3 ND ND Toluene µg/m3 110 ND Ethylbenzene µg/m3 ND ND m,p-xylene µg/m3 ND ND o-xylene µg/m3 ND ND Naphthalene µg/m3 ND ND TPH (C4-C6) µg/m3 22 10 TPH (C6-C8) µg/m3 180 20 TPH (C8-C10) µg/m3 60 35 TPH (C10-C12) µg/m3 37 53 TPH (C4-C12) µg/m3 300 120 Aliphatic (C4-C6) µg/m3 22 ND Aliphatic (C6-C8) µg/m3 72 17 Aliphatic (C8-C10) µg/m3 28 31 Aliphatic (C10-C12) µg/m3 35 53 Aromatic (EC5-EC7) µg/m3 ND ND Aromatic (EC7-EC8) µg/m3 110 ND Aromatic (EC8-EC10) µg/m3 33 ND Aromatic (EC10-EC12) µg/m3 ND ND 4

a Surface water Site 3 Vridi Canal 2 Parameters (µg/l) Surface water drain Total Hy C5-35 75,100 Benzene < 7 Ethylbenzene < 5 Toluene < 4 Xylene < 11 Free sulfur < 150 Pb 21 Cd < 0.25 As 7 Cr 15 Ni 51 Co 2 Hg 2.3 Cu 46 Zn 470 Groundwater Site 3 Vridi Canal 2 Control site 19 Anyama Parameters (µg/l) Well 3 m Borehole Dutch intervention values (µg/l) Total Hy C5-35 < 10 < 10 600,000 Benzene < 7 < 7 30 Ethylbenzene < 5 < 5 1 000 Toluene < 4 < 4 150 Xylene < 11 < 11 70 Free sulfur < 50 < 50 - Pb 1.3 < 0.25 75 Cd < 0.25 < 0.25 6 As 3.3 < 0.25 60 Cr 7 0.41 30 Ni 13 1.5 75 Co 1.5 1.4 100 Hg 0.41 < 0.25 0.3 Cu 6.8 1.8 75 Zn 78 5.4 800 5

Conclusions and Recommendations The results of the air quality analysis can be summarized as follows: Mercaptans, hydrogen sulfide and related components cannot be detected in this site, nor the control site. This is significant considering that the key odorants in the Probo Koala wastes were most likely hydrogen sulfide and mercaptans. Concentrations of the various analytes at the affected site are comparable to the concentrations found at the control site. Two observations can be made regarding the analysis groundwater quality for this site: The sample collected near this site does not show the combined presence of sulfur and hydrocarbons, which could have been indicative of leachate contamination from sites impacted by the Probo Koala wastes. Mercury concentrations, however, exceed Dutch intervention values and are above background levels. As conventional treatment systems for drinking water do not remove heavy metals, their concentrations in drinking water supplies should be monitored regularly and treatment such as carbon filtration should be introduced if needed. Surface water quality results for Site 3 show high levels of hydrocarbons, which is indicative of industrial pollution from local sources. In addition, heavy metal pollution is observed in the surface water samples, which is also to be expected in urban industrial areas and municipal waste disposal sites. The following recommendation can be made to address these issues: the Government should establish environmental monitoring systems for the Vridi industrial zone, based on sound environmental standards, to ensure that pollution is not draining into and further contaminating Ébrié Lagoon. 6

Site Photos Source: UN Environment Source: UN Environment 7

Source : UN Environment Source : UN Environment 8