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14 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />

measurements tropospheric halogen species can have profound effects on many aspects of tropospheric<br />

chemistry, these include:<br />

(1) Reactive halogen species, and in particular reactive bromine and iodine can readily destroy tropospheric<br />

ozone, which can have a multitude of consequences, both chemical and climatic (e.g. [Roscoe<br />

et al. , 2001], [Platt & Hönninger, 2003]). Catalytic ozone destruction essentially occurs by two distinct<br />

reaction cycles. Either (I) involving self reaction of halogen oxide radicals with other halogen oxide<br />

radicals (XO+XO or XO+YO) or (II) reaction of halogen oxides with hydrogen radicals XO+HO2):<br />

leading to the net result:<br />

O3 + O3 → 3O2<br />

Cycle (I) has been identified as the prime cause for polar boundary layer ozone destruction (e.g.<br />

[Barrie & Platt, 1997]). Since the rate of ozone destruction is usually proportional to the square of<br />

the halogen oxide concentration, cycle (I) ineffective at low XO levels usually found in mid-latitude<br />

coastal areas. At low RHS levels, however O3 destruction takes place by reaction cycle (II), here the<br />

rate of O3 destruction is linearly dependent on the XO concentration.<br />

(2) An important side effect of cycle (II) the conversion of HO2 to OH and thus a reduction of the<br />

HO2/OH ratio, in particular at low NOX levels. At a given photochemical situation (O3, H2O levels,<br />

insolation) the presence of BrO or IO will therefore increase the OH concentration. It is interesting<br />

to note that both effects have been observed in the upper troposphere (e.g. [Wennberg et al. , 1998]).<br />

(3) The reaction of XO with NO leads to conversion of NO to NO2 and thus to an increase of the<br />

Leighton ratio (L=[NO2]/[NO]). An increase in L is thus usually regarded as an indicator for photochemical<br />

ozone production (due to the presence of RO2 (R = organic radical)) in the troposphere.<br />

However, as already noted by [Platt & Janssen, 1996] an increase in L due to halogen oxides will not<br />

lead to O3 production.<br />

(4) A more subtle consequence of reactive halogen species for the ozone levels in the free troposphere<br />

is due to the combination of the above effects (2) and (3) as pointed out by [Stutz et al. , 1999]:<br />

Photochemical ozone production in the troposphere is limited by the reaction<br />

(2.1)<br />

NO + HO2 → NO2 + OH (2.2)<br />

However, the presence of reactive bromine will reduce the concentrations of both educts of the above<br />

reaction and thus reduce the NOX - catalysed ozone production.<br />

(5) Heterogeneous reactions of bromine species (i.e. HOBr) with (sea salt) chloride can lead to the<br />

release of Cl-atoms. This process constitutes a Br catalysed chlorine activation. Since Cl-atoms are<br />

highly reactive, this process directly enhances the oxidation capacity of the troposphere, see e.g. [Platt<br />

et al. , 2004].<br />

(6) Gas-phase iodine species (like IO, OIO or HOI) may facilitate transport of I from the coast to<br />

inland areas and thus contribute to our iodine supply [Cauer, 2004], [Cox et al. , 1999].<br />

(7) Deposition of mercury was found to be enhanced by the presence of reactive bromine species in<br />

particular in polar regions (e.g. [Barrie & Platt, 1997]), this process appears to be linked to the<br />

oxidation of Hg0 to Hg(II), likely by reaction with BrO [Lindberg et al. , 2002].<br />

(8) The reaction of BrO with dimethyl sulfide (DMS) might be important in the unpolluted remote<br />

marine boundary layer where the only other sink for DMS is the reaction with OH radicals (e.g. [von<br />

Glasow et al. , 2004], [von Glasow & Crutzen, 2004]).<br />

(9) Iodine species have been shown to be involved in particle formation in the marine BL ([Leck &<br />

Bigg, 1999], [Hoffmann et al. , 2001], [O’Dowd et al. , 2002], [Burkholder et al. , 2004]).<br />

(10) Evidence is accumulating (see e.g. [Platt & Hönninger, 2003]) that there is a wide-spread ”background”<br />

level of BrO radicals in the free troposphere, due to the processes described under (1)-(5)<br />

and (8) above there might be an important effect of reactive halogens on the global tropospheric<br />

chemistry as summarised by [von Glasow et al. , 2004].<br />

Main methods<br />

include the experimental determination of the halogen oxide distribution and the distribution of related<br />

species in several compartments of the troposphere:<br />

1) The marine boundary layer in coastal regions (Mace Head, Ireland).<br />

2) The open ocean.<br />

3) The free troposphere.<br />

4) Volcanic emissions (contents of reactive halogen species, e.g. BrO, ClO, OClO in volcanic plumes).

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