1 Introduction

One of the most important and vexing challenges in the field of public health is the proper investigation and subsequent control of air, water and soil pollution in industrialized urban cities and rural areas. Polluting substances released to the environment can have important toxicological effects on aquatic, animal and plant ecosystems. These substances can and do undergo long-range transport through the atmosphere. The primary pathway back to Earth is by means of precipitation, both wet and dry, often at distances hundreds to thousands of kilometers downwind from the original sources.

Among recent environmental studies the measurement of trace elements in fine particles and in wet atmospheric deposition has received increased attention because of their potential toxic effects (Reference Jeffries and SnyderJeffries and Snyder 1981, Reference LindbergLindberg 1981, Reference Tanaka, Darzi and WinchesterTanaka and others 1981, Reference ThorntonThornton and others 1981, Reference Hamilton and ChattHamilton and Chatt 1982). Sulphur has recently received a significant amount of attention because it is one of the main precursors of acid precipitation. However, the co-contaminants of acid snow are also considered to be worthy of investigation. Elements such as vanadium, manganese, mercury, lead, nickel, copper, zinc, arsenic, cadmium and selenium, all of which can be emitted with sulphur, are all potentially toxic, even at quite low concentrations. Often studies have been initiated of which the toxicologist, the environmental and the analytical scientists have not been aware, and they may not have seen the significance of each other’s work. Certain new analytical techniques, pushed to their detection limits, have often been considered too imprecise or time-consuming by one or other of the workers and new methods often have difficulty in being accepted as being useful and reliable. Nuclear analytical techniques are prime examples.

While the chemistry of polar snows has received attention for many years (Reference Murozumi, Chow and PattersonMurozumi and others 1969, Reference Boutron, Echevin and LoriusBoutron and others 1972, Reference Weiss, Herron and LangwayWeiss and others 1978, Reference BoutronBoutron 1980, and many references in the above papers), detailed analysis of urban snow has not benefited from such intense investigations.

Investigation of trace contaminants in urban snow has been much less frequent for the obvious reason that snowfall does not occur often enough in many places to warrant useful environmental studies. However, a study of snow composition can be potentially just as fruitful as that from rainfall. This is especially true for countries such as Canada (Reference Barrie and WalmsleyBarrie and Walmsley 1978, Reference BarrieBarrie 1979 and Reference Barrie1980, Reference Jeffries and SnyderJeffries and Snyder 1981, Reference Jervis, Landsberger, Lecomte, Paradis and MonaroJervis and others 1982, Reference Jervis, Landsberger, Aufreiter, Van Loon, Lecomte and Monaro1983, Reference Landsberger, Jervis, Kajrys and MonaroLandsberger and others 1983[a], Reference Landsberger, Jervis, Kajrys and Monaro1983[b]), Norway (Reference Forland and GjessingForland and Gjessing 1975, Reference Johannessen, Dale, Gjessing, Henriksen and WrightJohannessen and others 1977, Reference Dovland and EliassenDovland and Eliassen 1976, Reference Johannessen, Dale, Gjessing, Henriksen and WrightWright and Dovland 1977, Reference Johannessen and HenriksenJohannessen and Henriksen 1978), USA (Reference StruemplerStruempler 1976, Reference Moore, Gosz and WhiteMoore and others 1978, Reference ThorntonThornton and others 1981), Poland (Reference Zajac and GrodzinskaZajac and Grodzinska 1981), and Germany (Reference Schrimpff, Thomas and HerrmannSchrimpff and others 1979) where winters are long and snowfalls are abundant. However, in many of these reports only a few pollutants were investigated and environmental analytical interpretations were scarce while studies were not always focused on urban snow. This, coupled with the fact that laboratory procedures varied significantly for each study, makes intercomparisons hard to achieve (e.g. insoluble/soluble fractions).

Here we describe the results for three multi-elemental analytical techniques to determine sulphur and heavy metal pollution in urban snow: neutron activation analysis (NAA), proton-induced X-ray emission (PIXE) and inductively coupled plasma-atomic emission spectroscopy (ICP-AES). Possible environmental interpretations, including soluble/insoluble fractions, wash-out factors, enrichment factors, inter-elemental correlations, mobilization factors and toxicity potential are also presented. A large part of this paper has arisen from a snow study carried out by the author and co-workers (Reference Landsberger, Jervis, Kajrys and MonaroLandsberger and others 1983[a]).

2 Multi-Elemental Techniques

2.1 Neutron activation analysis (NAA)

Although some important rain studies have employed NAA techniques (Reference BogenBogen 1974, Reference SalmonSalmon 1975, Reference Schuyster, Maenhaut and DamsSchuyster and others 1978, Reference Beavington and CawseBeavington and Cawse 1979, Reference Slanina, Mols, Baard, Van der Sloot and Van RaaphorstSlanina and others 1979, Reference Hamilton and ChattHamilton and Chatt 1982), urban snow studies have largely been neglected.

Barrie (Reference Barrie1979, Reference Barrie1980) using NAA in conjunction with other analytical techniques, determined the transport, transformation and removal of atmospheric particulate matter in Alberta, Canada. The ambient concentrations, deposition patterns and deposition rates of several elements in air and snow were studied.

Landsberger and others (Reference Landsberger, Jervis, Kajrys and Monaro1983[a], Reference Landsberger, Jervis, Kajrys and Monaro1983[b]) and Jervis and others (Reference Jervis, Landsberger, Aufreiter, Van Loon, Lecomte and Monaro1982, Reference Jervis, Landsberger, Aufreiter, Van Loon, Lecomte and Monaro1983) have successfully employed instrumental neutron activation methods to undertake an in-depth study of urban snow. A typical gamma-ray spectrum can be seen in Figure 1 while some typical detection limits in rain or snow samples are shown in Table I. The detection limits are a combination of unconcentrated and/or freeze-dried methods.

Fig.1

Typical spectrum of preconcentrated snow soluble portion using instrumental NAA (Reference Jervis, Landsberger, Aufreiter, Van Loon, Lecomte and MonaroJervis and others 1983).

Table I

Some Typical Detection Limits of Precipitation Samples, Unconcentrated and Freeze Dried, Using Neutron Activation Analysis

In particular NAA can determine halides and rare-earth elements, These two groups of elements are usually not capable of being detected by many existing methods in a non-destructive fashion.

2.2 Proton-induced X-ray emission (PIXE)

PIXE methods are now well accepted for many environmental investigations. At present it appears that only one group from Canada (Reference Jervis, Landsberger, Lecomte, Paradis and MonaroJervis and others 1982, Reference Jervis, Landsberger, Aufreiter, Van Loon, Lecomte and Monaro1983, Reference Landsberger, Jervis, Kajrys and MonaroLandsberger and others 1983[a], Reference Landsberger, Jervis, Kajrys and Monaro1983[b]) have extensively used PIXE techniques to study soluble and insoluble fractions of either urban, remote or polar snow. Typical X-ray spectra for snow analysis are shown in Figures 2 and 3. The above-mentioned references discuss the salient features of PIXE.

Fig.2

Characteristic PIXE spectrum of snow soluble portion at 1.6 MeV (Reference Landsberger, Jervis, Kajrys and MonaroLandsberger and others 1983[a]).

Fig.3

Characteristic PIXE spectrum of snow particulate portion at 3.0 Mev (Reference Landsberger, Jervis, Kajrys and MonaroLandsberger and others 1983[a]).

Of prime importance is the detection of total sulphur, lead and nickel with excellent sensitivities. Typical detection limits are seen in Table II.

Table II

Typical Detection Limits of Snow Soluble and Particulate Portion Using Pixe Method (Reference Landsberger, Jervis, Kajrys and MonaroLandsberger and others 1983[a])

2.3 Inductively coupled plasma-atomic emission spectrometry (ICP-AES)

As with PIXE methods, application of ICP-AES to determine sulphur and metals in either rain or snow has not been greatly used. Reference BarnesBarnes (1978) has effectively reviewed the analytical techniques of ICP-AES, but it appears that only one study has exploited this powerful technique to determine elements in rain (Reference Schuyster, Maenhaut and DamsSchuyster and others 1978). Concentrations and detection limits for 17 elements (Table III) in three Montreal snow sites are presented here for the first time. The analytical accuracy of this method is shown by analyzing the trace elements in water NBS-SRM 1643a (Table IV).

Table III

Concentrations and Detection Limits of Elements in Three Montreal Snow Sites as Determined by ICP-AES

Table IV

Concentrations of Elements in Water NBS-SRM 1643A as Determined by ICP-AES

3 Interpretation of Trace Concentrations

A detailed environmental assessment of trace elements in wet atmospheric deposition is beyond the scope of this paper. It has been effectively reviewed by Reference Galloway, Thornton, Norton, Volchok and McLeanGalloway and others (1982). Below is a list of the more common techniques which could be employed for environmental assessments.

a Wash-out factor and dry deposition velocity

Reference ChamberlainChamberlain (1960) proposed the use of a wash-out factor (W_i) and dry deposition velocity factor V_g which are defined as follows:

where C_i is the concentration of the element of interest in rain or snow and in the aerosol.

b Enrichment factor

In order to distinguish naturally-occurring elements in precipitation or aerosols from those arising from various types of pollution, Reference Gordon, Zoller, Gladney and HemphillGordon and others (1973) suggested the use of elemental enrichment factors (EF). The enrichment factor of an element is defined as follows:

where X and C are the concentrations of the element of interest and a reference element, respectively. An element found in the atmosphere primarily as a result of natural processes such as wind erosion should exhibit an EF close to unity. An EF value greater than unity should suggest that the element arises predominantly from anthropogenic sources.

A list of trace concentrations and EF values for soluble and insoluble snow fractions are shown in Tables V and VI (Reference Landsberger, Jervis, Kajrys and MonaroLandsberger and others 1983[a]). Aluminum was used as the reference element.

Table V

Range of Concentrations and Enrichment Factors in the Snow-Melted Portion^*

Table VI

Range of Concentrations and Enrichment Factors in the Snow-Particulate Portion^*

d Other environmental analytical interpretations

The preceding interpretations of analytical results are by no means the only ones available to the analytical environmental scientist. Determination of historical trends in deposition, especially in Arctic and Antarctic regions and glaciers, provide a good indication of increasing industrialization by analyzing the different layers of snow, Reference Weiss, Herron and LangwayWeiss and others (1978) have found increased concentrations of lead, zinc and sulphate in Greenland.

The technique of mobilization factor (MF) (Reference Lantzy and MacKenzieLantzy and Mackenzie 1979), defined as:

can also contribute to the understanding of the different rates of emission from natural and anthropogenic sources. Still another technique called toxicity potential (TP) (Reference ThorntonThornton unpublished), defined as

can give an indication of how wet atmospheric deposition may possibly pollute drinking water.

4 Conclusions

The capability and versatility of these three multi-elemental techniques described here for snow deposition studies cannot be over-emphasized. Detection limits in parts per billion and even parts per trillion can be reached. More effort to improve preconcentration methods along with ICP-AES can also be investigated. The use of ICP-mass spectrometry which is now commercially available will also probably be of great analytical importance, not just in achieving lower detection limits but also in giving some clearer fingerprinting of elemental pollution.

Clearly, improvements can still be made, For instance, a serious shortcoming that should and could be Clrcumvented is the apparent lack of standardized techniques employed by the various research groups. These include sampling techniques, filtration procedures, use of reference standards and interpretation of data.

Snow sampling techniques could be improved to include weekly or monthly collections. The combined use of aerosol and atmospheric precipitation analysis at the same sampling sites could give a much clearer and badly needed overall picture of the competing scavenging processes in the atmosphere.

All these analytical techniques and environmental interpretations have great potential not only for urban snow but also for polar ice and snow samples.