IN THE NATIONAL ASSEMBLY OF THE REPUBLIC OF SOUTH AFRICA

The Mineral and Energy Affairs Port folio Committee public hearings on

The Petroleum Products Amendment Bill

Response to Submission by Associated Octel Company SA (Pty)Ltd

Submitted by the Legal Resources Centre on behalf of Environmental Justice networking Forum

 

  1. Introduction
  2. The Legal Resources Centre hereby amplifies its submission to the Portfolio Committee in order to address the submission of the Associated Octel Company SA Pty (Ltd) ( the "Octel Submission"which is presented by Realsearch) regarding issues surrounding the phase out of lead

  3. Legal issues
    1. Impact assessment

The Octel opinion states that a decision on petrol specifications is an administrative act that "materially and adversely affects the rights of the public" and will require an environmental impact assessment.

Our law provides for environmental impact assessments in two circumstances.

  1. For activities scheduled in terms of section 21(1) of the Environment Conservation Act No 73 of 1989; and
  2. Activities under s24(1) of the National Environmental Management Act 107 of 1998 ie activities that require authorisation or permission and which may significantly affect the environment.
  3. It is submitted that restrictions on what additives may be permitted into fuel do not fall into either of these categories and accordingly an environmental impact assessment is not required.

    1. Constitutionality of the proposed Petroleum Products Amendment Bill
    2. The Department of Mineral & Energy Affairs proposes to the amend the Petroleum Products Act 120 of 1977 by the addition of a provision (s 12C) which allows the Minister to make regulations to "prescribe the specifications and standards of petroleum products".

      The Petroleum Products Amendment Bill accordingly delegates to the Minister the power to make laws to govern the specifications for vehicle fuels without specific guidelines in the Bill as to how to exercise his/her administrative discretion.

      The Octel opinion states that certain constitutional rights may be affected in the passing of these regulations and that it is trite law that parliament must provide guidelines to officials on how to exercise an administrative discretion. It refers to a number of decided cases. These cases do not deal with the situation where the Minister exercises his or her discretion to in performing delegated legislative functions.

      In the case of the proposed regulations the legislative grant of delegated authority to the Minister is not unconstitutional because it involves policy questions to be decided by the Minister involving technical matters and when the Minister makes his decisions he does not do so in the absence of guidelines as to how to exercise his discretion. S/he is at all times to be guided by the National Environmental Management Act 107 of 1998.

      The drafting of regulations in terms of the proposed Bill may or may not constitute administrative action, but in any event such action does not affect the constitutional rights of secondary parties such as the Associated Octel Co Pty Ltd. If it is the case that their rights have been affected (and it is not conceded that they had such rights) the discussion of policy in regard to fuel specifications has been in the public domain over an extended period of time and they had ample opportunity to make representations at the time.

    3. Rationality of the date of 2006 for lead phase out.

As regards the rationality of the date of phase out of lead the administrative law issue is not a question of the wisdom of the decision but a question of whether the action serves a legitimate government purpose and whether what was done is rationally connected to that purpose. The purpose is to phase out lead and the setting of the date is rationally connected to that purpose. Hence the rationality test is complied with. The Octel opinion provides no basis for its assertion that the date of 2010 is more rational than the date of 2006.

 

 

  1. Issues surrounding the phase out of lead in South Africa
  2. The submission by Octel does not state its own particular interest interest pertinently at the beginning of the submission. The submission instead concentrates on attempting to articulate the interests of the SA oil industry, disadvantaged groups, consumers and others. We understand that the Associated Octel Company Limited is internationally the last remaining major producer of tetraethyl lead, the octane booster used in leaded petrol, which is due to be phased out of use in 2006.

    The concerns that it raises purportedly on behalf of other interest groups are not raised by those groups and hence should be disregarded.

    The credibility of the assertions of the Octel submission are in doubt given the massively inaccurate statement it makes regarding the cost of lead phase out, giving this as R15 billion. This is in fact the cost of all fuel specification reforms including lead based on much higher rand/dollar exchange values than are currently the case.

    What the submission fails to state is that the cost of these reforms as well as the implementation dates have been accepted by a broad range of interested and affected parties including the oil industry, motor industry, SABS, civil society groups and government which has taken place in terms of a broadly consultative process extending over many years. The difficulties such as they may exist in fuel reformulation and in particular lead phase out have been extensively traversed in this process and submissions made by the parties are there for all to see. Strangely Octel has waited till this late stage to make its submission suggesting that there has been inadequate consultation and that this decision is over hasty. Its submission is not supported by the facts of how these reforms have evolved.

     

  3. Challenges to some of Octels Assertions

a) South African studies

In 1999 a study of maternal and foetal blood lead levels was done which assessed blood lead levels during pregnancy in 2 hospitals serving disadvantaged communities. The average maternal blood level was 7.3 ug/dl but 18.7% of the samples had values greater than 10 ug/dl (the US Centres for Disease Control public health intervention level for raised blood lead level in children and pregnant women). The average umbilical cord blood level was 6..3 ug/dl and 12% had values greater than 10 ug/dl. The conclusion drawn was that there is a significant risk associated with maternal and foetal lead exposure in Durban and that public health measures to reduce exposure are needed.

In a study of lead poisoning of children in South Central Durban in 1998 twenty primary schools in 3 areas of South Central Durban were studied to determine if dust lead loading high enough to constitute a risk to children. 25% of primary schools were found to have mean outside dust lead loading above 1000 micrograms/m2. Exposure to dust lead in classrooms and in the school yard is considered to be an important contributor to blood lead levels and hence potential health hazard to children in many urban areas of the city.

In 1997 a study into lead poisoning of children in Africa found that in the Durban metropolitan area 5% of children showed blood lead levels of greater than 25 micrograms /dl . The figure for rural children was 2% of the blood lead levels were greater than 10 micrograms/dl. The study concluded that many children in Kwa Zulu-Natal are at risk of being lead poisoned. Average blood lead levels in Besters, an informal settlement , were 10 micrograms /dl. The USA Centre for Disease Controls benchmark for intervention is 10 micrograms per dl. A further study into childhood lead poisoning in Africa in March 1996 concluded that over 90% of the children in urban and rural communities of the Cape Province, South Africa, have blood lead levels of overall equal to 10 micrograms/dl. The introduction of unleaded petrol in 1996 has not caused a significant reduction of lead emissions as annual leaded petrol sales have remained more or less constant (see figure 1). Annual leaded petrol sales in fact increased from 1996 to 1998 and has subsequently decreased marginally. One can therefore expect that these studies will still be pertinent today. South Africa moreover in 1996/7 was the second largest user of leaded gasoline in the world.

 

 

 

b) Distribution of high blood lead levels

High lead blood levels follow socio demographic patterns. Research has shown in South Africa and internationally that the poor and vulnerable e.g. children, show higher relative blood lead levels. High blood lead levels correlate with living in dense urban settlements, inner city areas and near to roads. In 1991 for example a survey of South African children showed that 13% of black children had blood lead levels elevated more than double the US action level whereas no white children had blood lead levels as high as this. A subsequent study in 1997 showed that even after a significant decrease in the lead content of our fuel 5% of children in an informal settlement in Kwa Zulu-Natal had blood lead levels greater than 25 micrograms/dl.

The National Environmental Management Act, Principle 2(4)(c) states that: "Environmental justice must be pursued so that adverse environmental impacts shall not be distributed in such a manner as to unfairly discriminate against any person particularly vulnerable and disadvantaged persons".

The continued use of leaded petrol results in a distribution of the neurotoxin lead in a manner which, as research has demonstrated, impacts to a far greater extent on vulnerable and disadvantaged communities and persons, such as black children in South Africa. A duty therefore rests on the state to take measures to eliminate this adverse health impact.

 

No less than the World Bank has called for a worldwide elimination of leaded petrol:

"A broad range of governments and institutions, including the World Bank, have called for worldwide elimination of lead in gasoline on account of the documented adverse effect of lead on public health, particularly the intellectual development of children. Gasoline lead removal has been consistently correlated with reductions in the level of lead in the blood of exposed populations. Exposure to lead leads to diminished IQ which results in lower productivity. Direct costs, such as for health care and remedial education for children, are also incurred. There is evidence that more lead is absorbed when dietary calcium intake is low or if there is iron deficiency. The amount of lead absorbed by the body increases significantly when the stomach is empty. The rate of absorption is also higher for children than adults. In short, poor, malnourished children are more susceptible to lead poisoning than others. The benefits to society of eliminating lead from gasoline exceed the cost (which is typically in the neighborhood of 1–2 U.S. cents per liter) by an order of magnitude." Kojima, M. & Mayorga-Alba, E. (July 1998) "Cleaner Transportation Fuels for Air Quality Management," The World Bank, Energy Issues No. 13, p. 2.

In this light, it is imperative that we critically examine for its truth the recent submission to the National Assembly of the Republic of South Africa by REALSEARCH (on behalf of Octel Company Ltd.) requesting an additional 4-year delay in the phase-out of leaded petrol in South Africa. What follows, then, is an examination of the most egregious of the errors in the submission.

  1. Specific Issues

1. Octel through REALSEARCH has asserted: "6. In the USA and the European Union, there was a legal requirement to continue to supply leaded petrol for the existing, non-catalyst cars."

The truth is – On November 15, 1990, the U.S. Congress, in enacting the U.S. Clean Air Act Amendments of 1990, merely allowed the continued sale of leaded petrol with low levels of lead for five more years, until December 31, 1995. Under this provision of law, U.S. retailers were free to discontinue the sale of leaded petrol. Many retailers did, in fact, discontinue the sale of leaded petrol far earlier than this date. The relevant provision of U.S. law is as follows: "Prohibition on Leaded Gasoline for Highway Use.- After December 31, 1995, it shall be unlawful for any person to sell, offer for sale, supply, offer for supply, dispense, transport, or introduce into commerce, for use as fuel in any motor vehicle [as defined in section 216(2)] any gasoline which contains lead or lead additives." U.S. Clean Air Act, section 211(n); 42 U.S.C. section 7545(n).

To confirm that no regulations or laws required the sale of leaded gasoline for older cars, we conferred with James W. Caldwell, Senior Engineer, Transportation and Regional Programs Division, Office of Transportation and Air Quality, United States Environmental Protection Agency (U.S. EPA).  Mr. Caldwell has almost thirty years of experience working on gasoline regulation at the U.S. EPA.  Mr. Caldwell informed us that there has never been a U.S. law requiring the continuing sale of leaded gasoline.

Mr. Caldwell supplied a short history of unleaded fuel in the U.S. According to Mr. Caldwell, by 1982, lead in gasoline was capped at a maximum of 1.1 grams/gallon. At that time, about 50% of gasoline sold in the U.S. was leaded gas, and about 50% was unleaded. In 1985, as a result of new information about the deleterious human health effects of lead, the maximum allowable concentration of lead was reduced to 0.1 grams/gallon of gas.  There was some concern from farmers and antique car owner interest groups about removing lead entirely from gasoline, since these groups were worried that engines in agricultural equipment and antique cars, respectively, might be damaged. The continuing presence of up to 0.1 grams/gallon of lead was allowed in part to alleviate these concerns and protect older engines, but there was no requirement that leaded gasoline continue to be sold.  Mr. Caldwell added that the fears of damage to these older engines in fact never materialized.

According to Mr. Caldwell, by 1990, when the Clean Air Act Amendments mandated the elimination of all lead in gasoline by Jan. 1 1996, leaded gasoline comprised only about 10% of the U.S. market.  Although leaded gasoline was available until Jan. 1, 1996, there was no requirement that it be supplied in the U.S.

2. Octel has asserted: "11. Whilst petrol lead contributes around 90% to lead in air, a UK study clearly showed that its contribution to lead in blood was 10-15%, making it a minor contributor to body burdens (1). 12. This conclusion was supported in a report issued by the authoritative International Lead Zinc Research Organisation (ILZRO) (2). … The trend of decreasing blood lead levels in the USA when petrol lead usage fell was attributed to the attention paid to reduce significantly all the other contributors to lead in the body, eg industrial emissions, paint, food, beverages and drinking water. 13. Eliminating lead from petrol will not, therefore, bring about a marked lowering in blood lead levels in the RSA. Where blood levels are unacceptably high, attempts should be put in place to identify the principal sources. Unusually high levels of lead in the local environment are most often caused by specific point sources of emissions (3)."

The truth is – In every country that has severely restricted or eliminated the sale of leaded petrol, human blood levels of lead have declined dramatically. According to a United Nations technical report:

"One argument against an association between leaded gasoline and body burdens, namely that lead levels were decreasing before limits were put on gasoline lead and did not rise in response to increasing emissions of lead from gasoline, has been persuasively debunked. The data on which this argument was based have been shown to be unreliable, due to deficiencies in analytical methods available in earlier years. More recently, studies on lead in air, blood, and gasoline from Belgium, Canada, Finland, Greece, Italy, Japan, Nepal, New Zealand, Spain, Sweden, Switzerland, the United Kingdom and the United States and Venezuela were analyzed. Notwithstanding the inclusion of data in which the lead content of gasoline was constant and lead levels in blood were decreasing due to other factors (removal of lead from food packaging), this analysis found a strong correlation between lead in gasoline and lead in blood, as well as between concentrations of lead in air and blood. For a subset of studies where lead levels in gasoline changed, the correlation was higher, as would be expected. Levels of lead in gasoline and air accounted for 75% of the variation in blood lead levels. … Lead in gasoline is not the only source of blood lead or even necessarily the most important source for any particular population, but the studies reviewed here give clear evidence of its influence on human exposure. Regardless of the role of different sources of lead in a country, using less lead in gasoline will bring meaningful improvement in body burdens of lead. No matter what else a nation could or should do to reduce lead exposures, reducing the lead content of gasoline can be counted on to yield benefits to public health, especially for poor urban communities." United Nations Environment Programme (September 1998) "Global Opportunities for Reducing the Use of Leaded Gasoline: Leaded Gasoline in Context," pp. 29-31.

3. Octel has asserted: "14. Apart from one or two exceptions, international studies have established that there is no correlation between low levels of environmental lead and hypertension and impairment of neuropsychological development in children. However, studies have been conducted on children exposed to unacceptably high levels of lead exposure, e.g. living close to lead smelter plants. Adverse health effects were observed in children with blood lead levels in excess of 25µg per dl (4)."

The truth is – There is irrefutable and robust scientific evidence proving that exposure to low levels of lead causes irreversible mental retardation of children (IQ deficits) at blood lead levels below 10 µg per dl. According to a scientific paper by a researcher at Harvard University School of Public Health:

"To assess the strength of the association between blood lead and children's IQ, a meta-analysis of the studies examining the relationship in school age children was performed. Emphasis was given to the size of the effect, since that allows comparisons that are informative about potential confounding and effect modifiers. Sensitivity analyses were also performed. A highly significant association was found between lead exposure and children's IQ (P < 0.001). An increase in blood lead from 10 to 20 micrograms/dl was associated with a decrease of 2.6 IQ points in the meta-analysis. This result was robust to inclusion or exclusion of the strongest individual studies and to relaxing the age requirements (school age children) of the meta-analysis. Adding eight studies with effect estimates of 0 would still leave a significant association with blood lead (P < 0.01). There was no evidence that the effect was limited to disadvantaged children and there was a suggestion of the opposite. The studies with mean blood lead levels of 15 micrograms/dl or lower in their sample had higher estimated blood lead slopes, suggesting that a threshold at 10 micrograms/dl is implausible. The study with the lowest mean blood lead level was examined using nonparametric smoothing. It showed no evidence of a threshold down to blood lead concentrations of 1 microgram/dl. Lead interferes with GABAergic and dopaminergic neurotransmission. It has been shown to bind to the NMDA receptor and inhibit long-term potentiation in the hippocampal region of the brain. Moreover, experimental studies have demonstrated that blood levels of 10 micrograms/dl interfere with a broad range of cognitive function in primates. Given this support, these associations in humans should be considered causal." Schwartz, J. (April 1994) "Low-level lead exposure and children's IQ: a meta-analysis and search for a threshold," Environ Res; 65(1):42-55 (emphasis added).

If this were not enough, exposure to lead also is a cause of increased rates of violent crime and unwed pregnancies. According to a recent scientific paper:

"This study compares changes in children's blood lead levels in the United States with subsequent changes in IQ, based on norm comparisons for the Cognitive Abilities Test (CogAT) given to representative national samples of children in 1984 and 1992. … Furthermore, long-term trends in population exposure to gasoline lead were found to be remarkably consistent with subsequent changes in violent crime and unwed pregnancy. Long-term trends in paint and gasoline lead exposure are also strongly associated with subsequent trends in murder rates going back to 1900. The findings on violent crime and unwed pregnancy are consistent with published data describing the relationship between IQ and social behavior. The findings with respect to violent crime are also consistent with studies indicating that children with higher bone lead tend to display more aggressive and delinquent behavior. This analysis demonstrates that widespread exposure to lead is likely to have profound implications for a wide array of socially undesirable outcomes." Nevin, R. (May 2000) "How lead exposure relates to temporal changes in IQ, violent crime, and unwed pregnancy," Environ Res.; 83(1):1-22.

4. Octel has asserted: "15. ENVIRON, an internationally renowned US firm of consultants, reviewed the lead and health studies …"

The truth is - ENVIRON is an environmental consulting firm for corporations. According to its promotional materials, ENVIRON "strives to provide strategic solutions that are aligned with the business goals of our clients."

5. Octel has asserted that: "16. In particular … a causal association between low level lead exposure and IQ has not been firmly established and that the cardiovascular risks associated with lead exposure in adults are scientifically unsupportable (5). 17. The World Health Organisation’s International Programme on Chemical Safety issued a publication, in 1995, entitled ‘Inorganic Lead. Environmental Health Criteria 165’ … the following points were also made ‘…observational epidemiology cannot provide definitive evidence of causality (ie between blood leads and IQ effects) when the key statistical association is weak, the temporal relationship is unclear and major confounders are present’ … ‘Despite intensive efforts to define the relationship between body burden of lead and blood pressure or other effects on the cardiovascular system, no causal relationship has been demonstrated in humans and the mechanisms remain obscure.’

The truth is – There is strong scientific evidence showing that exposure to low levels of lead causes increased blood pressure in adults, leading to increased rates of heart attacks and strokes. According to a scientific paper by a researcher at Harvard University School of Public Health:

"This paper examines the robustness of the previously reported association between blood lead and blood pressure in adult males. The association remains strong and is essentially unchanged in tests that include nutritional factors and demographic factors, alone or together, or in tests that include insignificant terms. The relationship was not confounded by age; it held for all adult men in the 20-45 age group, the 40-59 age group, and the 46-74 age group. Interaction terms for 25 30-year age groups (20-49, 21-50,. . . , 45-74) were all insignificant, indicating no difference in the relationship by age. The relationship is also robust to the inclusion of a time trend to account possible omitted time-varying factors, and it held in a model that controlled for possible site effects. Given the strong experimental evidence, the relationship is likely causal." Schwartz, J. (July 1988) "The relationship between blood lead and blood pressure in the NHANES II survey," Environ Health Perspect, 78:15-22.

According to a scientific paper by a researcher at University of Michigan School of Medicine:

"Numerous observations have indicated a relationship between moderate or heavy lead exposure and high blood pressure. To determine whether low-level lead exposure is related to blood pressure in the U.S. population, we analyzed data from the National Health and Nutrition Examination Survey II for persons 12 to 74 years of age. Significant correlations were found between blood lead and blood pressure for each race-gender group, and blood lead levels were significantly higher in groups with high diastolic blood pressure (greater than 90 mm Hg). Multiple stepwise regression models were developed to predict blood pressure. After adjusting for age, race, and body mass index, blood lead levels were significantly related to systolic and diastolic pressures in males but not in females. These findings and those from other studies confirm the relationship of blood lead and blood pressure at relatively low levels commonly observed in the general population. The strength and importance of this relationship require further study through epidemiologic and metabolic investigations," Harlan, W.R. (July 1988) "The relationship of blood lead levels to blood pressure in the U.S. population," Environ Health Perspect, 78:9-13.

6. Octel has asserted that: "19. Solely focusing on the contribution of petrol lead in air to lead in blood in developing countries carries with it the danger of overlooking the major contribution of lead from other sources. For example, potentially highly significant sources of atmospheric lead are: fossil fuel burning in industry and in homes; lead-product manufacture (eg lead smelting); poorly-glazed cooking and eating ware; from lead-soldered food cans; lead in drinking water and beverages; in old flaking paint work; and illicit car battery meltdown to recover and sell the lead. 20. From the above, the assertion can be made that, unless there is compelling evidence of elevated blood levels that can be directly attributed to petrol lead, there is no justification on health grounds for a rapid phase-out of petrol lead by 1st January 2006."

The truth is - In urban areas of developing countries, exposure to airborne lead from motor vehicles using leaded petrol is the primary source of lead toxicity. According to a World Bank technical publication:

"The sources of exposure to lead include gasoline, lead pipes or lead-based solder in water supply systems, cottage industries, and lead-based paint. The importance of particular sources varies across countries and locations, meaning that targeted programs and interventions are required. In India, for example, the use of cosmetics containing lead is a major source of exposure; in Mexico it is the widespread use of lead for glazing pottery used to hold food and water. In Egypt lead solder used in the grinding stone of flour mills was recently found to cause alarming levels of lead poisoning. Many of these problems can be reduced by public education and awareness raising. Unlike these locally important sources, leaded gasoline is a problem worldwide; in large cities where it is still used, it accounts for 80 to 90 percent of airborne lead pollution. Lead contamination and exposure in cities are typically 3 to 4 times higher than in the suburbs and 10 times higher than in rural areas (see Figure 2 for an example). As a result of this exposure, children living in the inner cities may suffer as much as a 4-point IQ loss compared with those in the suburbs. The problems will worsen if use of leaded gasoline continues. Vehicle use is soaring in developing cities." Lovei, M. (May 1999) "Eliminating a Silent Threat: World Bank Support for the Global Phaseout of Lead from Gasoline," pp. 4-5 (emphasis added).

7. Octel has asserted that "26. Adverse environmental consequences can arise due to the change in petrol composition made necessary by lead’s reduction and elimination. As already mentioned above, traditionally, lead’s octane numbers are replaced by using increased amounts of aromatics, such as benzene, toluene and xylene. Olefins and oxygenates, such as methyl tertiary butyl ether (MTBE) and ethanol, are other popular octane blending components. 27. Higher exhaust emission levels of benzene result from increased usage of aromatics as a blending component. This is not just due to benzene itself – the other aromatics undergo de-alkylation reactions during the combustion process to form benzene (12, 13)."

The truth is – Increased environmental exposure to benzene is by no means a necessary consequence of phasing out leaded petrol. Even where use of unleaded petrol does lead to increased environmental exposure to benzene, the benefits of reduced exposure to lead far outweigh the costs of increased exposure to benzene. According to a World Bank technical report:

"The largest producer of tetra-ethyl lead (TEL), Octel, claims that unleaded gasoline should not be used in cars without catalytic converters, since unleaded gasoline contains more benzene then leaded, and without converters, the emission of benzene cannot be controlled. However, there are several weaknesses in this argument: 1) The production of unleaded gasoline does not necessarily lead to significant increases in the benzene content of gasoline, since it can be controlled by various refining processes; 2) Research has shown that personal activities, and pollution sources in homes, far outweigh the contribution of outdoor air to human exposure to benzene. The exposure of smokers, for example, exceeds the exposure of nonsmokers nearly 10 times. It was estimated that more than half of the nationwide exposure to benzene in the United States could be attributed to smoking (Wallace, 1989), and only 20 percent to traditional sources including traffic and industrial emissions; and 3) Of all exposures originating from gasoline, leaded and unleaded, a significant share is attributed to the evaporation of gasoline in garages, during driving, and pumping gasoline. Such exposures are associated with gasoline used in cars with or without catalytic converters. Additionally, the magnitude of health impacts caused by benzene exposure should be compared to those of lead exposures. It has been estimated (Tancrede et al., 1987; U.S. EPA, 1986) that the excess risk of leukemia associated with 70 years of exposure to 1 µg/m 3 airborne benzene was 4-8 x 10 -6 . Based on emission estimates of 202 thousand tons of benzene annually in 1976, the U.S. EPA’s Carcinogen Assessment Group estimated that 47 cases of deaths from leukemia could be attributed to the exposure to benzene from gasoline (U.S. EPA, 1985). For comparison, the annual number of deaths avoided by the reduction of lead in gasoline (only one of the positive health impacts of reducing lead), has been estimated between 4,000 and 5,000." Lovei, M. (January 1998) "Phasing Out Lead from Gasoline: Worldwide Experience & Policy Implications," World Bank Technical Paper No. 397. p. 12.

8. Octel has asserted that: "30. It is widely accepted that increasing the aromatic content of petrol produces more oxides of nitrogen (NOx) at the tailpipe (18). This is due to the resultant elevated combustion chamber temperatures caused by the higher calorific value of the aromatics. NOX contributes to ozone formation and adversely affects pulmonary function."

The truth is – use of unleaded petrol results in reduced emissions of hydrocarbons (HC) and carbon monoxide (CO) that outweigh increased emissions of nitrogen oxides (NOx). According to a World Bank technical publication:

"Blending small percentages of oxygenated compounds, such as ethanol, methanol, tertiary butyl alcohol (TBA), and MTBE and other ethers has the effect of improving the antiknock performance. Thus, the amount of lead can be reduced or even eliminated, without substituting potentially hazardous aromatic compounds. Exhaust HC and CO emissions are reduced by the use of oxygenates, but NOx emissions may be increased slightly by leaner air-fuel mixtures. The U.S. Auto/Oil study recently tested the effects of adding 10% ethanol … and adding 15% MTBE … to industry-average gasoline. For newer vehicles, the ethanol addition results showed a net decrease in HC (5.9%) and CO (13.4%) and a net increase in NOx emissions (5.1%). The MTBE addition showed net decreases in HC (7.0%) and CO (9.3%) and a net increase in NOx emissions (3.6%). … To summarize, it is possible to substitute certain oxygenates in place of lead to produce unleaded gasoline with maximum health benefits, no lead, and no increases in other toxic compounds. The case of Honk Kong … demonstrates how unleaded gasoline can have virtually the same aromatic content as leaded gasoline, in part due to the use of oxygenates." Walsh M. & Shah, J.S. (September 1997) "Clean Fuels for Asia: Technical Options for Moving Toward Unleaded Gasoline and Low-Sulfur Diesel," World Bank Technical Paper No. 377, pp. 15-16.

9. Octel has asserted that: "44. Lead traps (ie exhaust gas lead filters) offer a cost-effective and environmentally-beneficial alternative to the rapid elimination of lead from petrol in South Africa. … 45. Lead traps are a well-proven technology providing an economic and environmental solution to reduce lead emissions from existing non-catalyst cars. Historically, governments have allowed non-cat cars to continue to use leaded fuel whilst encouraging as many as possible of them to switch to unleaded. This was the original preferred approach to the gradual reduction in vehicular lead emissions."

The truth is – lead traps are an unproven technology for controlling tailpipe emissions of lead. There is not a single country in the world where more than a handful of vehicles use lead traps for controlling tailpipe emissions of lead. The way to eliminate tailpipe emissions of lead is to prohibit the addition of lead to petrol.

10. Octel asserts that: "47. In almost every case when a country moves to unleaded petrol the oil industry has been asked by government to develop energy penalty and cost implications. There is an energy penalty because making more aromatics and olefins consumes more crude oil in the refinery. Without exception, refineries have been required to find the capital investment costs to upgrade their octane-enhancing component units. Governments accepted the oil industry’s energy penalties and costs to produce unleaded fuel knowing that the latter would have to be passed on to the motorist. 48. Additional reforming to produce more aromatics has been the traditional and most cost effective route to up-grade. Cracking to make more transport fuels from a barrel of crude also contributes high octane petrol blending components to the refinery pool. Expensive alternatives to refinery up-grading do exist in the form of importing high octane components. However, this has detrimental effects on a nation’s balance of payments and the viability of its local industry."

The truth is – The costs of eliminating leaded petrol are minimal. In a free market system, these costs can be passed on to the consumer. Since the economic benefits of unleaded petrol outweigh the economic costs by more than 10-fold, consumers can easily bear the costs of eliminating leaded petrol. According to a World Bank technical report:

"Under well-functioning free market systems, refineries are able to finance the capital costs of investment from commercial sources, and pass on the costs to their customers. In countries where ex-refinery prices are controlled by the state, refineries should be provided with incentives through the pricing system to carry out the necessary investments. … The typical cost of phasing out leaded gasoline – including the annualized refinery investment costs amortized over the life of the investment, the incremental operating costs of producing gasoline without lead, and/or the cost of gasoline additives – has been estimated in the range of US$ 0.01-0.02 per liter …. The cost difference between the production of leaded (0.15 g/l) and unleaded gasoline in Germany, for example, was estimated at US$0.01 per liter (Thomas, 1995). Even in technologically less developed skimming refineries, the cost of total phase-out of leaded gasoline has been estimated under US$0.03 per liter …. Refinery modernization investments necessary to reduce the lead content of gasoline often improve productivity and refining efficiency, and increase revenues. Therefore, only the investment costs directly associated with accelerating investments in refinery modernization, and changes in refinery configuration necessary to produce gasoline without lead, should be charged to the lead phaseout process. The proper method to assess the incremental costs due to the phaseout of lead is to compare with and without project scenarios. A recent study (Abt Associates, 1996), for example, pointed out that phasing out leaded gasoline at a hydroskimming refinery in the Russian Federation would cost between US$0.005 and US$0.02 per liter of gasoline (depending on technical solutions) if current production structure was maintained. However, due to changes in the refining sector, the refinery's current product slate was expected to change in the near future. Taking this factor into account halved the estimated cost of lead phase-out." Lovei, M. (January 1998) "Phasing Out Lead from Gasoline: Worldwide Experience & Policy Implications," World Bank Technical Paper No. 397. pp. xv, 10-11.

 

11. Octel asserts that: "55. A high proportion of cars in South Africa have engines that were designed and manufactured to run on high-octane leaded fuel. This is a consequence of the fact that the average age of the RSA car-pool is approximately 13 years. In most cases these engines need the higher octane of leaded fuel and have ‘soft’ valve seats that need lead’s protection. Converting all of them to run without catastrophic engine failure on lower octane unleaded petrol is not a practical proposition, neither is it economically feasible."

The truth is – The vast majority of older vehicles with soft valve seats experience no problems using unleaded gasoline. This is because valve seat recession in these vehicles is strictly limited to vehicles that travel consistently at very high loads and speeds. According to a World Bank publication:

"As engine technology advanced during the leaded gasoline era, motor vehicle designers used lead’s friction-reducing properties to serve as a lubricant between exhaust valves and their seats, enabling them to use a lower grade metal for the valve seats. Leaded fuel shielded the valve seats from excessive wear, or valve seat recession, which can occur at high speeds in engines without hardened valve seats. This protection function is the reason why USEPA limited gasoline lead content to 0.1 grams per gallon, rather than banning its use entirely in 1985. However, the actual incidence of valve seat recession is miniscule; the only vehicles even appearing to be vulnerable travel consistently at very high loads and speeds, and even in these vehicles additives other than lead have been shown to protect valve seats. There is no technical argument to retain any lead in gasoline, if the refining capacity exists to provide the required octane in some other manner. For example, although Thailand completely eliminated the sale of leaded fuel on January 1, 1996, there has been no evidence of valve recession problems in existing vehicles." Walsh M. & Shah, J.S. (September 1997) "Clean Fuels for Asia: Technical Options for Moving Toward Unleaded Gasoline and Low-Sulfur Diesel," World Bank Technical Paper No. 377, p 14.

Thus, the problem of valve seat recession in older vehicles with soft valve seats using unleaded petrol would be virtually absent in South African cities. This is because drivers in urban areas, where the majority of older vehicles with soft valve seats are concentrated, simply do not travel consistently at very high loads and speeds.

12. Octel asserts that: "61. Petrol pricing policies impact on the poorer members of society who run older cars. Fiscal strategies might involve applying a lower excise duty to unleaded fuel to off-set its higher manufacturing cost, thereby making it cheaper than leaded at the pump. However, this would unfairly penalise the socially disadvantaged motorist. … 63. In South Africa the majority of drivers of the ‘old’ cars that need leaded petrol for safe operation are Historically Disadvantaged South Africans (HDSAs). Therefore, requiring HDSAs to convert their cars to run on unleaded or run them on more expensive leaded fuel is unfairly discriminatory. This would be particularly penal for motorists who need their car to help them earn a wage, for example commuting to work and using it to transport goods in a small private business."

The truth is – Delaying by four years the phase-out of unleaded petrol will disproportionately burden Historically Disadvantaged South Africans (HDSAs).

First, the health effects of lead emissions from motor vehicles using leaded petrol are suffered most by persons living in congested urban areas. According to a World Bank technical report:

"In many countries, evidence suggests that exposure to lead is one of the most serious environmental problems. Sample blood lead levels of urban populations, especially children, often reach alarmingly high levels (figure 3). It has been estimated (ATECLP and EDF, 1994) that among urban children in developing countries with no identified stationary source, 100 percent of those under 2 years of age, and over 80 percent of those between the ages of 3 and 5, had average blood lead levels greater than 10 mg/dl. Ingested lead is believed to be absorbed from the stomach more effectively when the stomach is empty, and when diet lacks essential trace elements, such as iron, calcium, and zinc (ATECLP and EDF, 1994). The population group most seriously affected by the exposure to lead, therefore, is likely to be the urban poor." Lovei, M. (January 1998) "Phasing Out Lead from Gasoline: Worldwide Experience & Policy Implications," World Bank Technical Paper No. 397. pp. 3-4.

Second, the use of unleaded petrol will result in a substantial net savings for motorists because of the damage leaded petrol causes to vehicle components. According to a United Nations technical report:

"The elimination of lead from gasoline has several additional benefits. The use of lead free gasoline can save money for motorists by reducing the need for frequent replacements of spark plugs, mufflers and the automobile hardware exposed to gasoline and its combustion products. A major reason is that the lead scavengers are highly corrosive and reactive. Several surveys carried out when leaded gasoline was widely used in the United States and Canada demonstrated that motorists who use lead free gasoline spend much less for exhaust system and ignition servicing than motorists who use leaded gasoline. As a rough rule of thumb, spark plug change intervals are roughly doubled by the use of unleaded gasoline and at least one exhaust system and exhaust silencer (muffler) replacement is eliminated. ... Another significant advantage associated with the use of lead free gasoline is the lengthened oil change interval. The use of unleaded fuel has been demonstrated to significantly reduce engine rusting and ring wear and to a lesser degree sludge and varnish deposits and cam and lifter wear. Because of this, oil change intervals on cars in the United States using unleaded fuel were at least twice as long as had traditionally been the case. Intervals of 10,000 miles are not uncommon with late model cars. Increased oil change intervals cannot be attributed solely to lead removal (as is indicated by some increases in vehicles using leaded gasoline) but the lead removal appears to be a major contributing factor. This is significant not only because of the reduced cost to the motorist but also because of the oil savings over the life of the vehicle and the reduction of the potential pollution problem resulting from the disposal of used oil. Experience had shown that in the United States significant quantities of used oil are disposed of in ecologically unacceptable ways, such as dumping it on the ground. ... Overall maintenance savings from unleaded fuel were estimate to average about $38 per year; for a car averaging 10 liters per 100 kilometers fuel consumption, this is equivalent to 2.4c per liter of gasoline. In summary, the potentially detrimental effects of eliminating leaded gasoline appear to have been greatly exaggerated in the public mind, while the potentially beneficial effects have been understated or ignored." United Nations Environment Programme (1999) "Older Gasoline Vehicles In Developing Countries and Economies in Transition: Their Importance and the Policy Options for Addressing Them," p. 27-28.

 

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