Exposure and Risk Assessment with Respect to Contaminated Soil: Significance of Biomarkers and Bioavailability

Identifying Hazards and Risks of Soil Contamination

The effects of contaminated soils on human health have rarely been observed, although models usually predict high exposure from contaminated soil. Such overestimation mostly results from insufficient data on the bioavailability of the chemical, which largely depends on the mobility of the compound in soil and the absorption rate via direct uptake by humans or indirectly via the food chain. It is therefore questionable to regulate soil contamination on the basis of toxicologically derived control levels because the transfer rates from soil to humans are not predictable unless very specific information on the different parameters affecting this transfer are available. Instead, soil control levels should be derived from ecotoxicological considerations or a specific evaluation of the contaminated area should be performed if contamination significantly exceeds the average. Setting soil control levels by considering effects on ecosystems including plants and possibly animals is presently being discussed by the Beratergremium für umweltrelevante Altstoffe and has been proposed previously.

Simulation and optimization technologies for petroleum waste management and remediation process control

Leakage and spill of petroleum hydrocarbons from underground storage tanks and pipelines have posed significant threats to groundwater resources across many petroleum-contaminated sites. Remediation of these sites is essential for protecting the soil and groundwater resources and reducing risks to local communities. Although many efforts have been made, effective design and management of various remediation systems are still challenging to practitioners. In recent years, the subsurface simulation model has been combined with techniques of optimization to address important problems of contaminated site management. The combined simulation-optimization system accounts for the complex behavior of the subsurface system and identifies the best management strategy under consideration of the management objectives and constraints. During the past decades, a large number of studies were conducted to simulate contaminant flow and transport in the subsurface and seek cost-effective remediation designs. This paper gives a comprehensive review on recent developments, advancements, challenges, and barriers associated with simulation and optimization techniques in supporting process control of petroleum waste management and site remediation. A number of related methodologies and applications were examined. Perspectives of effective site management were investigated, demonstrating many demanding areas for enhanced research efforts, which include issues of data availability and reliability, concerns in uncertainty, necessity of post-modeling analysis, and usefulness of development of process control techniques.

Pharmacokinetics, safety, and hydrolysis of oral pyrroloquinazolinediamines administered in single and multiple doses in rats

Pyrroloquinazolinediamine (PQD) derivatives such as tetra-acetamide PQD (PQD-A4) and bis-ethylcarbamyl PQD (PQD-BE) were much safer (with therapeutic indices of 80 and 32, respectively) than their parent compound, PQD (therapeutic index, 10). Further evaluation of PQD-A4 and PQD-BE in single and multiple pharmacokinetic (PK) studies as well as corresponding toxicity studies was conducted with rats. PQD-A4 could be converted to two intermediate metabolites (monoacetamide PQD and bisacetamide PQD) first and then to the final metabolite, PQD, while PQD-BE was directly hydrolyzed to PQD without precursor and intermediate metabolites. Maximum tolerant doses showed that PQD-A4 and PQD-BE have only 1/12 and 1/6, respectively, of the toxicity of PQD after a single oral dose. Compared to the area under the concentration-time curve for PQD alone (2,965 ng.h/ml), values measured in animals treated with PQD-A4 and PQD-BE were one-third (1,047 ng.h/ml) and one-half (1,381 ng.h/ml) as high, respectively, after an equimolar dosage, suggesting that PQD was the only agent to induce the toxicity. Similar results were also shown in multiple treatments; PQD-A4 and PQD-BE generated two-fifths and three-fifths, respectively, of PQD concentrations, with 8.8-fold and 3.8-fold safety margins, respectively, over the parent drug. PK data indicated that the bioavailability of oral PQD-A4 was greatly limited at high dose levels, that PQD-A4 was slowly converted to PQD via a sequential three-step process of conversion, and that PQD-A4 was significantly less toxic than the one-step hydrolysis drug, PQD-BE. It was concluded that the slow and smaller release of PQD was the main reason for the reduction in toxicity and that the active intermediate metabolites can still maintain antimalarial potency. Therefore, the candidate with multiple-step hydrolysis of PQD could be developed as a safer potential agent for malaria treatment.

Arteether toxicokinetics and pharmacokinetics in rats after 25 mg/kg/day single and multiple doses

Multiple doses of arteether (ARTE) at 25 mg/kg cause CNS and anorectic toxicities in rats. The same dose of ARTE was used to study the toxicokinetics (TK) after multiple injections and the pharmacokinetics (PK) following single administration. Animals were administered ARTE in sesame oil for 7 days, blood samples were collected using destructive sampling for up to 192 h after dosing and assayed by HPLC-ECD. Two other groups of rats were administered either a single 25 mg/kg i.v. or i.m. dose. In addition, the drug remaining in the i.m. injection site was measured. During the 7 day treatments, anorectic toxicity of ARTE was observed, and that caused significant reductions in food consumption and body weight after day 2. TK data on days 2-7 revealed marked changes compared to the PK parameters estimated on day 1. AUC (4367 ng x h/ml) on day 7 was 5-fold higher than AUC (905 ng x h/ml) on day 1. The volume of distribution at steady state (V(SS)) on day 7 (41.8 l) was 40% of the day 1 value of the V(SS) (104.3 l). Clearance (CL) was increased by 89% of the day 1 value, from 0.98 l/h to 1.85 l/h on day 7. The elimination t(1/2) of ARTE was also prolonged from 13.7 h (day 1) to 31.2 h (day 7). These data suggest that ARTE may have altered its distribution and elimination in rats as a result of the systemic toxicity. Analysis of the injection sites showed that 38% and 91% of the total amount of ARTE single dose remained in the muscles at 24 h (after first injection) and 168 h (at 24 h after 7 daily multiple doses), respectively. Fast and slow absorption phases from muscle were seen with t(1/2) of 0.97 h and 26.3 h, respectively. The apparent elimination t(1/2) of ARTE after i.m. injection (13.7 h) was much longer than that after i.v. dosing (0.67 h) due to the prolonged muscle absorption phase. Acute toxicity data of artemisinin drugs demonstrated that animals receiving a high single ARTE dose in sesame oil died between days 5-11, similar to artemether. When animals received dihydroartemisinin formulated in 50% DMAC/oil, or artesunic acid and artelinic acid in 0.9% saline vehicle, they died between days 1 and 2. This suggests that delayed onset toxicity and death in the ARTE rats may also be due to slow absorption and prolonged drug exposure. Therefore multiple i.m. administrations cause anorexia and drug accumulation, possibly affecting the toxicokinetics and efficacy of the drug.