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under most climatic conditions. They demand a
degree of maintenance that may need to be increased
in more arduous working environments, for
example, in salty or sandy environments where
corrosion and increased wear may be of concern.
Installed gauges often remain in position for long
periods of time and it is important that they are kept
clean so that identification markings, labels or other
safety markings. Otherwise, in the longer term, the
obvious profile, discernible relevant markings and
even the source’s identity may be lost. The care and
maintenance of ancillary equipment for controlling
the radiation source (tubes and cables used for
radiography and handling rods used for well logging)
are similarly very important (IAEA Safety Report
Series No.34, 2003). The 1985 Edition of the IAEA
Regulations provided for four types of packages,
depending on the activity and physical form of their
radioactive content, these are expressed as follows:
excepted; industrial; Type A; and Type B (WNTI
Review Series No.1, 2006).
3.4 Development of Regulations for the Sea
Transport of Dangerous Goods
The need for international regulations governing the
carriage of dangerous goods by sea was recognized
by the 1929 International Conference on the Safety
of Life at Sea (SOLAS), which recommended that
rules on the subject should have international effect.
The Safety of Life At Sea Conference of 1948
adopted a classification system for dangerous goods
and certain general provisions concerning their
carriage in ships in Chapter VI of the SOLAS
Convention. It also recommended further study with
the object of drafting international regulations.
Meanwhile, in 1956 the UN Committee of Experts
published its first Recommendations, which offered
a general framework to which existing modal
dangerous goods transport regulations could be
adapted and within which they could develop. The
ultimate aim of the UN Orange Book was to bring
uniformity to maritime and other modal transport
rules on a worldwide basis.
As a further step towards meeting the need for
international rules governing the carriage of
dangerous goods in ships, the International
Conference on Safety of Life at Sea in 1960 laid
down a general framework of provisions in Chapter
VII of the SOLAS Convention. The Conference also
invited IMO to undertake a study with a view to
establishing a unified international code for the
carriage of dangerous goods by sea in co-operation
with the UN Committee of Experts, taking account
of existing maritime practices and procedures. The
Conference further recommended that the unified
code prepared by IMO should be adopted by the
governments party to the SOLAS Convention.
Following completion of the necessary development
work, the International Maritime Dangerous Goods
(IMDG) Code was adopted by the fourth IMO
General Assembly in November 1965. Like the other
modal dangerous goods requirements, the IMDG
Code covers nine classes of dangerous goods. Class
7 radioactive material is covered through
incorporation in the IMDG Code of the relevant
provisions of the IAEA Regulations for the Safe
Transport of Radioactive Material (IMDG Code,
2005). During the 1980s, the scope of the IMDG
Code was extended to include provisions and
requirements for the transport of substances and
materials harmful to the marine environment,
identified as marine pollutants. Inclusion of marine
pollutants in the Code also assisted in the
implementation of Annex III of the International
Convention for the Prevention of Pollution from
Ships, 1973, as modified by its 1978 Protocol 61
(the 1973/78 MARPOL Convention). Annex III
contains the regulations for preventing pollution by
harmful substances carried in packaged form,
including packages in portable tanks, freight
containers, road tankers and rail tank wagons. The
harmful substances covered by MARPOL Annex III
are thus those identified by GESAMP 63 as marine
pollutants in the IMDG Code. GESAMP has not
considered packaged radioactive material in the
context of marine pollutants and Annex III does not
apply to radioactive material. In addition to the
IMDG Code, the IMO introduced the Code for the
Safe Carriage of Irradiated Nuclear Fuel, Plutonium
and High-Level Radioactive Wastes in Flasks on
Board Ships (the INF Code) in 1993 (WNTI Review
Series No.1, 2006).
The gamma and neutron sources used in these
tools are normally transported in separate heavy
containers termed shipping shields or carrying
shields. They are Type A transport packages (or
sometimes Type B for the neutron source) that meet
the specifications for Category III labelling as
defined by the IAEA Regulations for the Safe
Transport of Radioactive Material (IAEA Safety
Requirements, 2005). They may be transported by
road in the vehicles of the logging companies to the
land well. When they are to be used offshore, the
shields are usually contained in an overpack. This
may be a large thickwalled box (external dimensions
about 1.75 m × 1.75 m × 1.75 m) that also serves as
a storage container at the well site. The dose rates of
the 137Cs source are significant but not normally
isotropic owing to the construction of the source
assembly. Dose rates may exceed 7.5 μSv/h for up to
30 m in the forward direction and about 4 m behind
the operator. The radiation from the source is
directed away from any occupied areas. The dose