industry and environment - DTIE
industry and environment - DTIE
industry and environment - DTIE
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
Other topics<br />
Figure 2<br />
SANGEA summary chart<br />
example, indirect emissions could<br />
include those from the production of<br />
purchased electricity, contract manufacturing,<br />
contracted drilling operations<br />
<strong>and</strong> product transport by third parties.<br />
The Guidelines provide a rationale for<br />
accounting <strong>and</strong> reporting indirect emissions<br />
from energy consumption. An<br />
example for the petroleum <strong>industry</strong><br />
illustrated in the Guidelines is accounting<br />
for power plants located within a<br />
refinery that export electricity <strong>and</strong>/or<br />
steam to other companies.<br />
Another unique situation for the<br />
petroleum <strong>industry</strong> is contract operations<br />
where a petroleum company provides<br />
fuel to a contract operator. This<br />
occurs in drilling operations, as well as<br />
in transportation of crude oil or products.<br />
The Guidelines suggest that companies<br />
consider accounting for significant<br />
contract operations as sources of indirect<br />
emissions. Based on the accounting approach<br />
described in the Guidelines, provision of fuel to a<br />
contract operator should not influence whether<br />
the emissions are included as operated or equity<br />
share. Since the emissions come from a contracted<br />
operation, they are indirect emissions.<br />
Once the inventory accounting approach has<br />
been set, <strong>and</strong> decisions have been made as to what<br />
types of reports will be developed <strong>and</strong> what the<br />
data will be used for, the next step is to underst<strong>and</strong><br />
the specific sources included in each facility<br />
<strong>and</strong> what methodology is appropriate to<br />
estimate the emissions. The Guidelines provide<br />
an overview of the types of methodologies that<br />
are appropriate for exploration <strong>and</strong> production<br />
facilities <strong>and</strong> petroleum <strong>and</strong> petrochemical refining/manufacturing<br />
facilities. These approaches<br />
are described for the two types of facilities for various<br />
ranges of accuracy, using a tiered approach.<br />
Tier A represents the highest level of accuracy.<br />
Tier B includes somewhat less rigorous methods,<br />
<strong>and</strong> is therefore likely to be more straightforward<br />
<strong>and</strong> less costly to implement. However, the<br />
uncertainty associated with these methods is<br />
greater. Finally, for an assessment of<br />
emissions where uncertainties of 30-<br />
60% are acceptable, Tier C methods<br />
may be employed. Each of the Tiers in<br />
the Guidelines is linked to appropriate<br />
calculational methodologies in the<br />
API Compendium.<br />
Specific information about the<br />
types of approaches available for estimating<br />
emissions is found in the<br />
Compendium. For a given facility, <strong>and</strong><br />
a given range of uncertainty, the specific<br />
method used for each source will<br />
de pend on the information available<br />
about that source. For example, the<br />
Compendium recommends that the<br />
preferred method for estimating emissions<br />
from combustion sources is to<br />
determine the mass of carbon per mass<br />
of fuel <strong>and</strong> the mass of fuel used. However,<br />
the Guidelines <strong>and</strong> the Compendium<br />
recognize that this type of information is<br />
not available for all devices in all facilities. Where<br />
the preferred information is not available, the<br />
Compendium provides alternative methodologies<br />
that utilize existing information to develop a reasonable<br />
estimate of emissions. For example, in<br />
many cases a facility may measure the volume of<br />
fuel used <strong>and</strong> periodically analyze the specific<br />
gravity <strong>and</strong>/or heating value of the fuel. As an<br />
alternative to mass based estimates, this information<br />
can be used to estimate carbon dioxide emissions<br />
from fuel combustion.<br />
Developing an inventory:<br />
methodologies<br />
As described above, the Guidelines provide information<br />
on accounting for <strong>and</strong> reporting to corporate<br />
level of greenhouse gas emissions at the facility.<br />
A companion publication, the API Compendium of<br />
Greenhouse Gas Emissions Estimation Methodologies<br />
for the Oil <strong>and</strong> Gas Industry, documents a number<br />
of currently recognized calculation techniques <strong>and</strong><br />
emission factors available for developing GHG<br />
emissions inventories for oil <strong>and</strong> gas <strong>industry</strong> operations.<br />
The Compendium was developed to<br />
Figure 3<br />
SANGEA normalized emissions summary<br />
accomplish the following:<br />
1. assemble an expanse of relevant<br />
emission factors for estimating GHG<br />
emissions from oil <strong>and</strong> gas <strong>industry</strong><br />
activities, based on currently available<br />
public documents;<br />
2. outline detailed procedures for conversions<br />
between different measurement<br />
unit systems, with particular<br />
emphasis on implementation of oil<br />
<strong>and</strong> gas <strong>industry</strong> st<strong>and</strong>ards;<br />
3. provide descriptions of the multitude<br />
of oil <strong>and</strong> gas <strong>industry</strong> operations<br />
– from exploration <strong>and</strong> production<br />
through refining to the marketing of<br />
products, as well as the transportation<br />
of crude oil, natural gas <strong>and</strong> petroleum<br />
products – <strong>and</strong> the associated emissions<br />
sources that should be considered;<br />
4. develop emission inventory examples<br />
– based on selected facilities from the various<br />
<strong>industry</strong> segments – to demonstrate the broad<br />
applicability of the methodologies.<br />
The Compendium is neither a st<strong>and</strong>ard nor a<br />
recommended practice for the development of<br />
GHG inventories. Rather, it represents a compilation<br />
of recognized methodologies for estimating<br />
GHG emissions specific to oil <strong>and</strong> gas <strong>industry</strong><br />
operations.<br />
Source classification<br />
The Compendium groups oil <strong>and</strong> gas <strong>industry</strong><br />
GHG emission sources into three categories:<br />
combustion devices, process emissions <strong>and</strong> fugitive<br />
emissions.<br />
1. Combustion devices include both stationary<br />
sources, such as engines, burners, heaters <strong>and</strong><br />
flares, <strong>and</strong> fleet-type transportation devices, such<br />
as trucks <strong>and</strong> ships, where these sources are essential<br />
to operations (i.e. transportation of material or<br />
personnel);<br />
2. Point sources include vents from oil <strong>and</strong> gas<br />
<strong>industry</strong> units, such as hydrogen plants <strong>and</strong> glycol<br />
dehydrators, that emit CO 2 <strong>and</strong>/or CH 4 . They<br />
also include other stationary devices such as storage<br />
tanks, loading racks <strong>and</strong> similar equipment;<br />
3. Non-point sources include fugitive<br />
emissions (equipment leaks), emissions<br />
from wastewater treatment facilities,<br />
<strong>and</strong> a variety of other emissions<br />
generated by waste h<strong>and</strong>ling;<br />
4. Non-routine activities, associated<br />
with maintenance or emergency operations,<br />
also may generate GHG emissions;<br />
5. Indirect emissions are defined as<br />
GHG emissions associated with oil<br />
<strong>and</strong> gas company operations, but<br />
physically occurring from sites or operations<br />
owned or operated by another<br />
organization.<br />
The Compendium includes calculation<br />
<strong>and</strong> estimating techniques for<br />
determining CO 2 , CH 4 <strong>and</strong> N 2 O<br />
emissions from all of these sources.<br />
74 ◆ UNEP Industry <strong>and</strong> Environment April – September 2004