Thông tin tài liệu:
Việc lựa chọn loại tác động và các chỉ số thể loại và các mô hình có thể ổ đĩa tập hợp các dữ liệu kiểm kê. Ví dụ, người ta có thể chọn để đánh giá khoáng sản chỉ có dự trữ được dự đoán bị cạn kiệt trong vòng 100 năm, hoặc một số khung thời gian hợp lý khác.
Nội dung trích xuất từ tài liệu:
Process Engineering for Pollution Control and Waste Minimization_11
linkage between the inventory results and effects in the environment. Others
(e.g., habitat modification) are known to play a critical role in environmental
impacts of products (e.g., agricultural products), but are difficult to model
quantitatively. Life cycle impact assessment practice is moving more and more
toward using sophisticated fate and transport models to evaluate indicators of
environmental impacts.
The choice of impact categories and category indicators and models can
drive the collection of inventory data. For example, one might choose to evaluate
only minerals whose reserves are predicted to be depleted within 100 years, or
some other reasonable time frame. This would eliminate the need to gather data
on such materials as bauxite, clay, or iron ore, and would decrease the cost of
inventory collection and management.
To date, no “standardized” listing of impact categories to be used in LCA
has been established, but several categories are employed in common practice, as
shown in Table 5.
The Classification Step. Inventory data need to be classified into the
relevant impact categories for modeling. Some emissions have influence on more
than one environmental mechanism and must be classified into more than one
category. The classic example oif this is oxides of nitrogen, or NOx, which acts
as catalyst in the formation of ground-level ozone (smog), but also is a source of
acid precipitation. These substances must be characterized into both categories.
One form of NOx (nitrous oxide, N2O) is also active as a greenhouse gas. The
classification rules for any LCIA must be clearly reported, so that readers of a
study understand what exactly was done to the inventory data.
The Characterization Step The goal of life cycle impact assessment is
to convert collected inventory inputs and outputs into indicators for each cate-
gory (aggregates can be system-wide, by life cycle stage, or by unit operation).
TABLE 5 Typical Impact Categories
1. Stratospheric ozone depletion
2. Global warming
3. Human health
4. Ecological health
5. Smog formation
6. Nonrenewable resource depletion
7. Land use/habitat alteration
8. Acidification
9. Eutrophication
10. Energy: processing/transportation
Copyright 2002 by Marcel Dekker, Inc. All Rights Reserved.
These indicators do not represent actual impacts, because the indicator does not
measure actual damage, such as loss of biodiversity. However, together, they do
constitute an ecoprofile for a product or service.
While there is no universally accepted “right” list of impact categories or
indicators, basic objectives have been set by the Society of Toxicology and
Chemistry (SETAC) that help define categories:
1. Category definition begins with a specific relevant endpoint. Ideally,
the endpoint can actually be observed or measured in the natural
environment.
2. Inventory data are correctly identified for collection. In principle, those
inventory inputs and outputs which relate to the particular impact are
identified.
3. An indicator describes the aggregated loading or resource use for each
individual category. The indicator is then a representation of the
aggregation of the inventory data.
Figure 7 compares the real-world causes and effects (the environmen-
tal mechanism) with the modeled world of LCIA. There are many differences
between the two. In an LCI, for example, the inventory information is typi-
cally modeled as a constant and continuous flow, while in the real world,
emissions typically occur in a discontinuous fashion, varying from minute
to minute.
FIGURE 7 Comparison of “real-world” endpoints to LCIA indicators.
Copyright 2002 by Marcel Dekker, Inc. All Rights Reserved.
Both natural and anthropog ...