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Oil in the Sea III: Inputs, Fates, and Effects
TABLE E-18 Summary of Average Total Load from Accidental Spills during Years 1990-1999, for Vessels in U.S. Waters by Type of Vessel and by Type of Oil (tonnes)
Tankers
Tank Barges
Other Vessels
Totals
% of Total
Crude oil
16,525
1,184
162
17,872
36%
Gasoline
187
1,459
50
1,697
3%
Light distillate
545
5,466
6,247
12,259
25%
Heavy distillate
2,340
12,556
2,651
17,546
36%
TOTALS
19,597
20,665
9,110
49,373
(Percent of total)
40
42
18
incompleteness of the data and the fact that the smaller spills, under 10,000 gallons (34 tonnes), comprised about 13 percent of the U.S. totals, the international spill quantities were increased by 25 percent to obtain the minimum estimate, by an additional 10 percent to obtain the best estimate, and further increased by 25 percent to obtain the maximum estimate. Results are summarized in Table E-21.
Accidental Spills from Vessels Worldwide
The North American and international spill estimates are combined to provide worldwide estimates (Tables 2-2 through 2-6). The best estimate for total spillage worldwide is 110,000 tonnes (30 million gallons) per year. The 1985 report (National Research Council, 1985) and the 1990 study (IMO, 1990) both used data from the International Tanker Owners Pollution Federation Ltd. (ITOPF) to estimate the quantity of oil entering the marine environment from tanker accidents. In the 1990 study, the spillage was averaged for the 10-year period from 1981 to 1989, establishing an annual average of 114,000 tonnes per year. In the 1990 report no adjustments were made for the deficiencies in the database, so care should taken when comparing these figures.
Inputs To The Sea From The Aircraft Industry
There are inputs to the sea from deliberate and continual releases of fuel from aircraft. There are two sources: deliberate discharge due to emergency conditions aboard the aircraft, and normal operation releases including the release of partially burned fuel in inefficient engines or inefficient operating modes and emptying of fuel injection bypass canisters. Modern aircraft have take-off weights exceeding their landing weights, sometimes by as much as 150 tonnes. For example, a 747 can carry as much as 220,000 L of fuel weighing about 175,000 kg or 175 tonnes. If a fully laden 747 jettisoned its fuel because it was required to return to an airport, it could dump as much as 150 tonnes of the fuel to enable it to land safely. Fuel dumping is infrequent but not rare. One airport reported on 16 fuel dumps in one year out of 7,000 flights conducted [Canadian Environmental Assess
TABLE E-19 Summary of Average Annual Loads from Accidental Spills (for Vessels in North American Waters)
Tank Vessels (gallons)
Other Vessels (gallons)
All Vessels (gallons)
Tank Vessels (tonnes)
Other Vessels (tonnes)
All Vessels (tonnes)
Spill Volume—U.S. Waters (per year)
1,089,173
252,013
1,341,186
4,026
911
4,937
Est. Spill Volume—Canada (per year)
100,000
38,000
138,000
384
137
521
Est. Spill Volume—Mexico (per year)
170,000
15,000
185,000
631
55
686
1,359,173
305,013
1,664,186
5,042
1,102
6,144
Tank Vessels
Other Vessels
(gallons)
(tonnes)
(gallons)
(tonnes)
North American Waters
Minimum (based on 1990’s data)
1,400,000
5,000
300,000
1,100
Best Estimate (1990’s data + 5 percent)
1,400,000
5,300
300,000
1,200
Maximum (Best estimate + 20 percent)
1,700,000
6,400
400,000
1,400
NOTE: All totals rounded to two significant figures.