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De Beers Victor Mine – 2014 TRA Annual Report Summary 1 | P a g e
ONTARIO TOXICS REDUCTION ACT
DE BEERS CANADA INC. VICTOR MINE
2014 REPORT ON TOXIC SUBSTANCE ACCOUNTING SUMMARY
INTRODUCTION
In 2009, the Toxics Reduction Act (Act) and its associated regulation (O.Reg. 455/09) were
promulgated as part of the Ministry of Environment and Climate Change (MOECC’s) toxics
reduction strategy, with the purposes of preventing pollution and protect human health and the
environment by reducing the use and creation of toxic substances, and to inform Ontarians
about toxic substances (TRA 2009, c. 19, s. 1.).
The Act is applicable to manufacturing facilities with North American Industry Classification
System (NAICS) codes starting with “31”, “32” or “33” and facilities with NAICS codes starting
with “212”. Regulated substances under the Act include all substances listed in Environment
Canada’s National Pollutant Release Inventory (NPRI) and O.Reg. 127/01. Forty-seven
substances and substance groups were listed in Table A of O.Reg. 455/09 as Phase I priority
substances, and reduction plans were prepared and submitted in December 2012. Phase II of
the Act required accounting for all other NPRI substances and the TRPs were prepared in 2013.
For De Beers Victor Mine, nineteen substances were determined to be subject to the Toxics
Reduction Act, and a total of seven Toxic Reduction Plans have been prepared. They include
dioxins and furans individual congeners, hexachlorobenzene (HCB), metals (arsenic, cadmium,
chromium, cobalt, copper, lead, manganese, nickel, selenium, vanadium and zinc),
phosphorous, carbon monoxide, nitrogen oxides and particulate matter (TSP, PM10, and PM2.5).
The annual toxic substance accounting requirements were completed for the 2014 reporting
year, and this annual toxic substance accounting summary has been prepared in accordance
with the requirements of the Ontario Toxics Reduction Act and Ontario Regulation 455/09.
Further information on the Toxics Reduction Act is provided by the Ministry of the Environment
on their website www.ontario.ca/ministry-environment-and-climate-change.
TOXIC REDUCTION POLICY STATEMENT OF INTENT
De Beers Canada Inc., Victor Mine is committed to playing a leadership role in protecting the
environment. Wherever feasible, we will reduce the creation and discharge of toxic substances
in full compliance with all federal and provincial regulations. Our employees are encouraged to
participate in all types of toxic substance reduction activities. Toxic substance reduction will be
an ongoing effort at DeBeers, and we will continue to monitor advancements to ensure that
options that are both technologically and financially viable are implemented at our facility. No
current options were identified that are technically or economically feasible.
De Beers Victor Mine. – 2014 TRA Annual Report Summary 2 | P a g e
BASIC FACILITY INFORMATION
Company Name: DeBeers Canada Inc., Victor Mine
Contact Information: 119 Pine St. South, Suite 310, Timmins, ON. P4N 2K3
Highest Ranking Employee: James Kirby
Mine General Manager
416-645-3888 Ext. 2180
Technical Contacts: Terry Ternes P.Geo.
[email protected] 416-645-3888 ext 5779
Parent Company: De Beers Canada Inc.
100% ownership
Address: Suite 900 – 250 Ferrand Dr.
Toronto, Ontario
M3C 3G8
Business Number: 103749735
The facility’s NPRI ID: 10984
250 full time employees (equivalent).
Site Location (UTM Coordinates): Zone 17,304227 E and 5856029 N
The NAICS codes applicable to the facility are:
21 – Mining, quarrying, and oil and gas extraction
2123 – Non metallic mineral mining and quarrying
212392 – Diamond Mining
De Beers Victor Mine. – 2014 TRA Annual Report Summary 3 | P a g e
REDUCTION OBJECTIVES
Particulates (TPM, PM10, PM2.5)
There was no reduction option identified because there is no additional viable way of reducing
the creation of particulates. Particulates (TPM, PM10 and PM2.5) are primarily created and
released at the DeBeers Canada Inc. Victor Mine site through truck travel on unpaved roads for
hauling purposes. In addition, some small amounts of particulates are created and released
through combustion of fuel oil, incinerator use and primary and secondary crushing. DeBeers
already employs a fugitive dust management plan to minimize particulate emissions that
includes watering the unpaved roads, maintenance of the roads and speed limits. No further
reduction options have been considered because any further mitigation will only increase costs
while offering no viable payback.
Nitrogen Oxides
There was no reduction option identified because DeBeers is already improving their facility
operations to minimize the release of nitrogen oxides. Nitrogen oxides is primarily created and
released at the DeBeers Canada Inc. Victor Mine site during the use of emulsion explosives for
blasting and removing the ore. Emulsion explosives are widely used in the mining sector due
to their low cost, ease of use and the ability to work in wet environments. DeBeers already
employs a great deal of planning and scheduling to minimize the use and increase the efficiency
and effectiveness of the explosives. There are no viable alternatives to the use of emulsion
explosives based on cost and other viable explosives will create and release similar amounts of
nitrogen oxides.
Carbon Monoxide
There was no reduction option identified because DeBeers is already improving their facility
operations to minimize the release of carbon monoxide. Carbon monoxide is primarily created
and released at the DeBeers Canada Inc Victor Mine site during the use of emulsion explosives
for blasting and removing the ore. Emulsion explosives are widely used in the mining sector
due to their low cost, ease of use and the ability to work in wet environments. DeBeers already
employs a great deal of planning and scheduling to minimize the use and increase the efficiency
and effectiveness of the explosives. There are no viable alternatives to the use of emulsion
explosives based on cost and other viable explosives will create and release similar amounts of
carbon monoxide.
Metals (arsenic, cadmium, chromium, cobalt, copper, lead, manganese, nickel, selenium,
vanadium and zinc)
DeBeers does not intend to reduce the transfer of metals because these substances are
naturally occurring in ore from which diamonds are extracted and eventually disposed into the
onsite tailings management facility. The only way to reduce the amount of metals transferred to
the tailings facility would be to reduce the amount of ore processed, which could only be
obtained by reducing output and plant operations. DeBeers is committed to ensuring their
tailings transfers are handled in a safe and responsible manner. While DeBeers does not
intend to reduce the transfer of the aforementioned metals, technologies that may reduce the
releases to the environment of these substances will be monitored.
De Beers Victor Mine. – 2014 TRA Annual Report Summary 4 | P a g e
Dioxins and Furans, Hexachlorbenzene
There was no reduction option identified because there is no viable way of reducing use and
creation of Dioxins and Furans, and Hexachlorobenzene. Dioxins and furans and
Hexachlorobenzene are not brought into the site but are created and released during the
incineration of mine waste. In addition, the incinerator emissions have met the reporting criteria
for the Toxic Reduction Act, although at extremely low levels, because emissions below the
level of detection were required to be reported as if they were in fact occurring at the Method
Detection Limit. Consequently, there are few practical options for lowering the emissions
reported, which are for the most part not scientifically quantifiable.
DeBeers Canada Inc has made recent plant improvements. All employees at the Victor Mine
will be involved in waste reduction efforts. Waste Segregation will be one of our first priorities
for reduction. Our goal is to reduce the use of plastic substances where technically and
economically feasible. Steps taken include a reduction in plastic use and employee education
to help with waste segregation.
Phosphorus
DeBeers does not intend to reduce the transfer of phosphorus because it is naturally occurring
in ore from which diamonds are extracted and eventually disposed into the onsite tailings
management facility. The only way to reduce the amount of phosphorus transferred to the
tailings facility would be to reduce the amount of ore processed, which could only be obtained
by reducing output and plant operations. DeBeers is committed to ensuring their tailings
transfers are handled in a safe and responsible manner. While DeBeers does not intend to
reduce the transfer of phosphorus, technologies that may reduce the releases to the
environment of phosphorus will be monitored.
De Beers Victor Mine. – 2014 TRA Annual Report Summary 5 | P a g e
TOXIC SUBSTANCES
The site uses and emits thirteen Phase 1 MOE Toxic compounds and uses or emits six Phase 2
toxic compounds.
The nineteen MOE Toxic Compounds are listed below:
Chromium NA - 04
Cobalt NA - 05
Copper NA - 06
Manganese NA - 09
Nickel NA - 11
Vanadium 7440-62-2
Zinc NA - 14
Arsenic NA - 02
Cadmium NA - 03
Lead NA - 08
Selenium NA - 12
Dioxins and furans - total NA - D/F
Hexachlorobenzene 118-74-1
NOx 11104-93-1
CO 630-08-0
TPM N/A - M08
PM10 N/A - M09
PM2.5 N/A - M10
Phosphorus NA-22
A total of six Toxic Reduction Plans have been prepared. They include dioxins and furans
individual congeners, hexachlorobenzene (HCB), metals (arsenic, cadmium, chromium, cobalt,
copper, lead, manganese, nickel, selenium, vanadium and zinc), phosphorous, carbon
monoxide and particulate matter (TSP, PM10, and PM2.5).
TRACKING AND QUANTIFICATIONS
The method used to calculate the TRA quantifications was a combination of source testing
results, published emission factors and mass balance.
Table 1 is a summary of reported TRA quantities for the 2014 operational year. When compared
to the last reported values, overall there were no significant changes. The decrease in use and
De Beers Victor Mine. – 2014 TRA Annual Report Summary 6 | P a g e
creation of metals, dioxins and furans can be attributed to updated source testing results. The
change in reported values for carbon monoxide created can be attributed to an increase in AN
emulsified explosive use.
In the 2014 operational year, there were no out of the ordinary incidents or significant process
changes at the facility.
COMPARISION OF TRACKING AND QUANTIFICATION
No changes were made in the quantification and tracking methodology from 2013 to 2014.
DESCRIPTION OF STEPS TAKEN TO ACHIEVE OBJECTIVE AND ASSESS
EFFECTIVNESS
There was no technologically feasible reduction strategy objectives identified for De Beers
Canada Inc. and as such there was no economic feasibility study completed for the Phase I or
Phase 2 substances.
There are no objectives to track or reduction targets to evaluate.
Table 2 provides a summary of the facility TRA changes and updates which took place in 2014.
De Beers Victor Mine – 2014 TRA Annual Report Summary 7 | P a g e
Table 1: Comparison of Quantities Reported
Substance CAS
Description of Processes that Use
or Create Substance
Reporting under
NPRI Part
NPRI Threshold
2014 Used (tonnes)
2013 Used - Last
Reported Value
% Change 2014
Created (tonnes)
2013 Created -
Last Reported
Value
% Change
2014 Contained In Product (tonnes)
2013 Contained in Product
- Last Reported
Value
% Change Reason for Changes
Chromium NA - 04
Metals contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
>0-1 >0-1 -25.00 0 0 NA 0 0 NA Update to source testing
Cobalt NA - 05
Metals contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
0.0000 0.0000 0 0 0 NA 0 0 NA No significant change
Copper NA - 06
Metals contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
>0-1 >0-1 -52.63 0 0 NA 0 0 NA Update to source testing
Manganese NA - 09
Metals contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
>0-1 >0-1 -33.3 0 0 NA 0 0 NA update in source testing
Nickel NA - 11
Metals contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
>0-1 >0-1 -16.67 0 0 NA 0 0 NA update in source testing
Phosphorus NA-22
contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
>0-1 >0-1 0.00 0 0 NA 0 0 NA No significant change
Vanadium 7440-62-2
Metals contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
0 0 NA 0 0 NA 0 0 NA No significant change
Zinc NA - 14
Metals contained in Solid waste incinerated
Part 1
10 tonnes (MPO or
Transferred to Tailings)
>0-1 >0-1 -10.09 0 0 NA 0 0 NA Update to source testing
NOx 11104-93-1
Explosives use, Combustion
Part 4 20 tonnes (Release)
0 0 NA >10-100 >10-100 1.06 0 0 NA No significant change
CO 630-08-0
Explosives use, Combustion
Part 4 20 tonnes (Release)
0 0 NA >10-100 >10-100 22.99 0 0 NA Increased explosives use
TPM N/A - M08 Road dust Part 4
20 tonnes (Release)
0 0 NA >100-1000
>100-1000
-9.04 0 0 NA Slight decrease in vehicle
kms travelled
PM10 N/A - M09 Road dust Part 4
0.5 (Release)
0 0 NA >100-1000
>100-1000
-8.85 0 0 NA Slight decrease in vehicle
kms travelled
PM2.5 N/A - M10 Road dust Part 4
0.3 (Release)
0 0 NA >10-100 >10-100 -8.22 0 0 NA Slight decrease in vehicle
kms travelled
De Beers Victor Mine – 2014 TRA Annual Report Summary 8 | P a g e
Substance CAS
Description of Processes that Use
or Create Substance
Reporting under
NPRI Part
NPRI Threshold
2014 Used (tonnes)
2013 Used - Last
Reported Value
% Change 2014
Created (tonnes)
2013 Created -
Last Reported
Value
% Change
2014 Contained In Product (tonnes)
2013 Contained in Product
- Last Reported
Value
% Change Reason for Changes
Arsenic NA - 02
Metals contained in Solid waste incinerated
Part 1B 50 kg (MPO or contained in tailings)
>0-1 >0-1 0 0.00 0.00 NA 0 0 NA No significant change
Cadmium NA - 03
Metals contained in Solid waste incinerated
Part 1B
5 kg (MPO or
Transferred to Tailings)
>0-1 >0-1 66.67 0.00 0.00 NA 0 0 NA Increased loading to
incinerator and update to source testing
Lead NA - 08
Metals contained in Solid waste incinerated
Part 1B 50 kg (MPO or contained in tailings)
>0-1 >0-1 -48 0.00 0.00 NA 0 0 NA update in source testing
Selenium NA - 12
Metals contained in Solid waste incinerated
Part 1B
100 kg (MPO or
contained in tailings)
>0-1 >0-1 20 0.00 0.00 NA 0 0 NA Slight increase in loading
to the incinerator
Substance CAS
Description of Processes that Use
or Create Substance
Reporting under
NPRI Part
NPRI Threshold
2014 Used (tonnes)
2013 Used - Last
Reported Value
% Change 2014
Created (tonnes)
2013 Created -
Last Reported
Value
% Change
2014 Contained In Product (tonnes)
2013 Contained in Product
- Last Reported
Value
% Change Reason for Changes
1234678-HpCDD(Dioxin) 35822-46-9
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -77.70 0 0 NA update to source testing
1234678-HpCDF(Furan) 67562-39-4
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -69.55 0 0 NA update to source testing
1234789-HpCDF(Furan) 55673-89-7
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -65.42 0 0 NA update to source testing
123478-HxCDD(Dioxin) 39227-28-6
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -78.69 0 0 NA update to source testing
123478-HxCDF(Furan) 70648-26-9
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -67.11 0 0 NA update to source testing
123678-HxCDD(Dioxin) 57653-85-7
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -77.38 0 0 NA update to source testing
123678-HxCDF(Furan) 57117-44-9
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -67.88 0 0 NA update to source testing
123789-HxCDD(Dioxin) 19408-74-3
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -77.50 0 0 NA update to source testing
123789-HxCDF(Furan) 72918-21-9
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -50.0 0 0 NA update to source testing
De Beers Victor Mine – 2014 TRA Annual Report Summary 9 | P a g e
Substance CAS
Description of Processes that Use
or Create Substance
Reporting under
NPRI Part
NPRI Threshold
2014 Used (tonnes)
2013 Used - Last
Reported Value
% Change 2014
Created (tonnes)
2013 Created -
Last Reported
Value
% Change
2014 Contained In Product (tonnes)
2013 Contained in Product
- Last Reported
Value
% Change Reason for Changes
12378-PeCDD(Dioxin) 40321-76-4
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -76.83 0 0 NA update to source testing
12378-PeCDF(Furan) 57117-41-6
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -52.85 0 0 NA update to source testing
234678-HxCDF(Furan) 60851-34-5
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -59.42 0 0 NA update to source testing
23478-PeCDF(Furan) 57117-31-4
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -59.22 0 0 NA update to source testing
2378-TCDD(Dioxin) 1746-01-6
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -61.11 0 0 NA update to source testing
2378-TCDF(Furan) 51207-31-9
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >1-10 -47.19 0 0 NA update to source testing
Octa CDD (Dioxin) 3268-87-9
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -76.37 0 0 NA update to source testing
Octa CDF (Furan) 39001-02-0
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -65.56 0 0 NA update to source testing
Hexachlorobenzene 118-74-1
Solid Waste Incineration
Part 3 Solid Waste Incineration
0 0 NA >0-1 >0-1 -3.70 0 0 NA No significant change
De Beers Victor Mine – 2014 TRA Annual Report Summary 10 | P a g e
Table 2: Changes in Quantifications, Quantities and Plan Updates
Substance CAS Quantification
Method(s) Used
Change in Quantification Method Used
Rationale for Using Selected Method(s)
Incidents out of the Ordinary
Significant Process Change
Objectives, Descriptions, Targets
Actions Amendments
Chromium NA - 04 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Cobalt NA - 05 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Copper NA - 06 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Manganese NA - 09 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Nickel NA - 11 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Phosphorus NA-22 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Vanadium 7440-62-2 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
De Beers Victor Mine – 2014 TRA Annual Report Summary 11 | P a g e
Substance CAS Quantification
Method(s) Used
Change in Quantification Method Used
Rationale for Using Selected Method(s)
Incidents out of the Ordinary
Significant Process Change
Objectives, Descriptions, Targets
Actions Amendments
Zinc NA - 14 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
NOx 11104-93-1 Emission Factors No change No site specific monitoring
data available No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
CO 630-08-0 Emission Factors No change No site specific monitoring
data available No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
TPM N/A - M08 Emission Factors No change No site specific monitoring
data available No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
PM10 N/A - M09 Emission Factors No change No site specific monitoring
data available No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
PM2.5 N/A - M10 Emission Factors No change No site specific monitoring
data available No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Arsenic NA - 02 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
De Beers Victor Mine – 2014 TRA Annual Report Summary 12 | P a g e
Substance CAS Quantification
Method(s) Used
Change in Quantification Method Used
Rationale for Using Selected Method(s)
Incidents out of the Ordinary
Significant Process Change
Objectives, Descriptions, Targets
Actions Amendments
Cadmium NA - 03 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Lead NA - 08 Mass Balance/Source
Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Selenium NA - 12 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
1234678-HpCDD(Dioxin) 35822-46-9 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
1234678-HpCDF(Furan) 67562-39-4 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
1234789-HpCDF(Furan) 55673-89-7 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
123478-HxCDD(Dioxin) 39227-28-6 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
De Beers Victor Mine – 2014 TRA Annual Report Summary 13 | P a g e
Substance CAS Quantification
Method(s) Used
Change in Quantification Method Used
Rationale for Using Selected Method(s)
Incidents out of the Ordinary
Significant Process Change
Objectives, Descriptions, Targets
Actions Amendments
123478-HxCDF(Furan) 70648-26-9 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
123678-HxCDD(Dioxin) 57653-85-7 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
123678-HxCDF(Furan) 57117-44-9 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
123789-HxCDD(Dioxin) 19408-74-3 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
123789-HxCDF(Furan) 72918-21-9 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
12378-PeCDD(Dioxin) 40321-76-4 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
12378-PeCDF(Furan) 57117-41-6 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
De Beers Victor Mine – 2014 TRA Annual Report Summary 14 | P a g e
Substance CAS Quantification
Method(s) Used
Change in Quantification Method Used
Rationale for Using Selected Method(s)
Incidents out of the Ordinary
Significant Process Change
Objectives, Descriptions, Targets
Actions Amendments
234678-HxCDF(Furan) 60851-34-5 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
23478-PeCDF(Furan) 57117-31-4 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
2378-TCDD(Dioxin) 1746-01-6 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
2378-TCDF(Furan) 51207-31-9 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Octa CDD (Dioxin) 3268-87-9 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Octa CDF (Furan) 39001-02-0 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
Hexachlorobenzene 118-74-1 Source Testing No change Most accurate method No No
No reduction options were identified to be both
technically and economically feasible.
Therefore, no options were chosen for implementation. None None
De Beers Victor Mine. – 2014 TRA Annual Report Summary 15 | P a g e
CERTIFICATIONS BY HIGHEST RANKING OFFICIAL
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