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23

Examples from lead in petrol debates

4. Ultimately accepting the science but denying its implications for

the issue –

‘Even if the science demonstrates measurable effects, it’s

not actually causing any damage.’

“It was misleading at best and fraudulent at worst to talk about the

symptoms and horrors of lead poisoning. That is just like talking about

the horrors of gassing World War I soldiers with chlorine at a hearing as

to whether we should chlorinate to purify drinking water.”

Blanchard

cited by Stein 1982 in Needleman 2000.

5. Resisting change on the basis of no alternatives, cost

etc.

‘Even

if there is demonstrated damage, then we just have to live with

it because there are no alternatives; it’s too difficult/expensive to

change

etc

.’

“Even when there was subsequently evidence for adverse impacts on

children froma longitudinal study in New Zealand, this appeared to have

little or no impact on the policy process.”

Wilson and Horrocks 2008.

“The amount of extra lead we get from pollution by exhaust gases is

comparatively very small. I accept that we should be better without

it, but if we do without it we have to use a lower octane petrol; we

therefore have to have lower compression engines. These factors bring

other problems in their wake. It is a matter of economics and sense.”

Lord Mowbray and Stoughton 1971.

6. Once change is inevitable, rapid acceptance by interest groups

and denial that there was any problem –

‘Not sure what all the fuss

was about as it’s quite possible to produce cars than run on unleaded

petrol; guns that use non-toxic shot; angling tackle that use non-toxic

weights

etc

.’

“On January 1 [1976] the legal limit of lead in petrol in Germany was

reduced to 0.15 grams per litre, well below that which the DoE accept

British industry cannot reasonably be asked to go. ... Oil companies

throughout the world have been unanimous on the perils of what

Germany has done. These are:

...

(5)

Excessive wear and tear. Unlikely.

German petrol companies are

now fervent in their assurances to motorists that the new petrol will

not harm their engines as they once were in their threat that it would.”

Ottaway and Terry 1976.

It is clear that making faster progress to eliminate the risk

to wildlife from lead would benefit from more insight into

behavioural change theories and the use of more sophisticated

ways of ‘selling’ the need for change to stakeholders. This

will help move the understanding and behaviour of people

(including both the public and those with influence in decision/

policy making processes).

In this regard, the ‘invisible’ nature of lead poisoning of

wildlife, with affected animals seldom being seen by the

public, unfortunately reinforces resistance to what is seen as

unnecessary change. Lead is not a ‘spectacular’ cause of death

in the way that acute episodes of oil pollution are, even though

lead poisoning has likely killed orders of magnitudes more

waterbirds than have marine oil spills.

As noted above, a wide range of international multi-lateral

environmental agreements have now formally recognised the

need to ban the use of lead gunshot in wetlands. Whilst, until

recent years, this international recognition has been largely

restricted to the African-Eurasian region, the acknowledgement

by 120 Parties to CMS of the global nature of the issue in 2014

was a major step forward. The call by CMS COP 11 to Parties

to

“Phase-out the use of lead ammunition across all habitats

(wetland and terrestrial) with non-toxic alternatives within the

next three years…”

is ambitious indeed. It will be important

to make rapid progress to this end to avoid prolonging the

unnecessary poisoning of wildlife.

ACKNOWLEDGEMENTS

Grateful thanks to Julia Newth, Ailsa Benton, Rachel Stroud

and Chris Spray for, variously, the supply of literature and

constructive comments on the draft, and to Ruth Cromie for

discussions. The views expressed are those of the author alone.

Regulation of some sources of lead poisoning