SCIENTIFIC PROGRESS SINCE 1993.
|
Doug Bright, Royal Roads University, 2005 Sooke Road, Victoria,
BC, V9B 5Y2 |
3. ENVIRONMENTAL FATE PROCESSES
| Table 3.1 | Compound previously detected in
pulp mill final effluents (before and after treatment) and expected environmental behavior |
| Table 4-1 | Compounds, effluents, and process streams
from pulp mills that are associated with specific physiological responses of fish |
| Table 4-2 | Results of chronic toxicity tests using effluents from mills with ECF bleaching |
| Table 5.1 | Toxicity criteria and hazard quotients for
chlorinated compounds in mill effluents produced from bleaching processes with 100% chlorine dioxide substitution |
| Table 5.2 | Probabilistic assessment of chlorophenol TEQs exceeding the EPA FW criteria |
| Figure 1 | The risk assessment process as proposed
for use under CEPA (Environment Canada, 1997) |
| Figure 2 | The process of pulp production under bleaching. |
| Figure 3 | Chlorinated aromatic compounds identified from
samples of degraded fulvic acid from both natural and bleached kraft mill effluents. |
| Figure 4 | A reaction of lignin with chlorine dioxide. |
| Figure 5 | New organic substances identified in effluent from ECF bleaching. |
| Figure 6 | The reaction of lignin with ozone. |
| Figure 7 | Diagrammatic representation of exposure pathways in pulp mill effluents. |
| Figure 8 | Sterols and triterpenoids found in pulp mill effluents. |
| Figure 9 | Biotransformation reactions in pulp mill effuents. |
| Figure 10 | Temporal trends in total TCDD/TCDF loads from pulp mill in BC, Canada. |
| Figure 11 | Temporal trends in concentration of TCDD/TCDF
reported in mill effluents from BC, Canada. |
| Figure 12 | Changes in liver tissue EROD activity in rainbow
trout exposed to 1/400 dilution of effluents from pulp mills and other sources. |
| Figure 13 | Illustration of the tiers of risk assessment. |
| Figure 14 | Distributions of concentration of tetrachloroguaiacol
and tetrachlorocatechol from mills using 100% chlorine dioxide substitution compared to the most sensitive toxicity enpoint. |
| Figure 15 | Distribution of concentrations of all chlorinated
phenols from mills using 100% chlorine dioxide substitution expressed as pentachlorophenol TEQs and compared to assessment criteria for pentachlorophenol. |
APPENDIX 1 | Compounds identified since 1993 in effluent from mills employing ECF bleaching |