At left, Orion pH-meter with combination electrode for measurement of H ion activity in water and soil extracts


The Lab for Contaminant Analysis has a range of capabilities for determining other routine and customized analtyical services for geologic, aqueous, and environmental samples. In addition to the instrumentation and services located at the Whitehall Forest lab facility, the Soil Charactertization Lab located in the Crop and Soil Sciences Department on campus has a range of instrumentation for basic characterization of solid materials that can be accessed thru the Contaminants Lab. Pricing for the various services are given in the fee schedule.

pH, EC and Eh

Hydrogen ion activity (pH), electrical conductivity (EC, in units of S [Siemens] per m) and redox potential (Eh, in volts) are important characterisitcs of both solutions and extracts of solids that can be readily determined at the Lab. pH is determined with a H-sensitive glass electrode calibrated against solutions of known (H+). Precision is typically only good to two decimal places. EC is determined with a conductivity cell monitored using a resistance/conductivity meter; EC in mS/cm is closely related to total dissolved salts in a solution. Redox potential is an estimate of the oxidation-reduction status, indicative of dissolved oxygen and the potential for formation of reduced gas species such as hydrogen sulfide. It is measured potentiometrically using a standard platinum electrode, and reported to the nearest mV.
For solids, a paste is typically mixed at a 2.5(water):1(solids) ratio, equilibrated, and pH and EC determined in the supernatent; pH and Eh do not vary greatly with the chosen ratio, but EC is sensitive to the volume of water and is thus a relative or comparative value.

Particle Size Analysis

Particle size distribution of a soil or sediment material is determined using sedimentation rate of particles in water as described by Stokes' Law. Materials are disaggregated and suspended in water, and suspension densities or particle concentrations measured over time of settling to obtain a particle size distribution. Typically sand (0.05-2 mm), silt (0.002-0.05 mm) and clay (<0.002 mm) sizes are determined, although other size limits may be chosen. Sand may be further sub-divided by mechanical seiving into coarse and fine fractions. Clay or colloidal content is an important property affecting many other physical and chemical characteristics of a soil material.

Cation Exchange Capacity

Cation exchange capacity (CEC) refers to the capacity (in meq or cmol of cation charge) of a mass of soil material to retain cations on charged surfaces in the colloid fraction of the soil; thus, it describes the number of negatively charged sites on a soil material. It is typically determined by displacing adsorbed cations (largely limited to Ca, Mg, Na, K, and Al) with a neutral salt such as BaCl2, and measuring the displaced cations using atomic absorption or ICP spectroscopy (the "sum of cations" method). Alternatively, a cation such as ammonium may be used to fully saturate the exchange sites of a sample, then dispaced and measured as an estimate of CEC. Anion exchange capacity (AEC, or the number of positive sites) can also be measured in this method by determining retention of an associated anion such as nitrate or chloride. Anion concentrations are determined by ion chromatography or colorimetry. CEC and AEC are important surface chemical properties related to nutrient status and contaminant behavior in soil/sediment systems.

Surface Area

Surface area of a soil or geologic material is closely related to both particle size distribution and mineralogy; it represents the amount of potential reactive surface of soil that may be in contact with pore waters, and therefore reactive with contaminants. Surface areas may be measured a variety of ways, but nitrogen (N2) gas adsorption is a standard method; this measures external surface area, excluding very fine pores within expansible clay minerals. A Micromeretics BET surface area instrument located in the Soil Characterization Lab automates the process of measuring the amount of N2 gas adsorbed by a sample, which is used to calculate surface area in m2 per g of solid, assuming a monolayer coverage of the surface with adsorbed gas. Adjusting mass of adsorbent allows determination of areas over the range of 0.05 to 500m2/g.

Mineralogy

Identification of the minerals present in a geologic, soil, or sediment sample is an advanced characterization technique that may be important in understanding the physical and chemical behavior of that material in a wide range of settings. Mineralogy of the clay colloid (<0.002 mm) fraction is of most importance, since minerals in this size fraction possess most of the charge and chemical reactivity in a sample from a nutrient or contaminant point of view. Organic colloids are determined by measurement of organic carbon in the solid; inorganic colloids can be identified and semi-quantified using X-ray diffraction analysis. In this analysis, the <0.002 mm fraction is separated using sedimentation and mounted on glass slides after saturation with different exchangeable cations. The slides are placed in a diffractometer located in the Soil Characterization Lab, which impinges x-rays on the sample over a range of angles of incident radiation. Diffraction patterns so obtained can be used to identify phyllosilicate (clay) minerals such as kaolinite and vermiculite present in the sample, and estimate their abundance.
Improved quantification of clay mineralogy is possible using Differential scanning calorimetry (DSC). Dried samples of material are heated in a DuPont DTA unit, which records calorimetric changes corresponding to mineral phase transitions within the sample. Amounts of heat absorbed or released at given temperatures can be used to accurately compute quantities of minerals such as kaolinite, gibbsite, and Fe oxides present in the sample.
Amounts of reactive oxides such as Fe oxides (hematite and goethite), Al oxides (gibbsite), and Mn oxides are important in specific reactions related to trace metals and organic contaminants in soils and sediments. Amounts of "free" (oxidic) oxides can be estimated by reductive extraction of the soil with dithionite reagent, and measurement of Fe, Mn, and Al in the extract. Results are reported as % Fe2O3, % Al(OH)3, and % MnO2 in the sample