|
|
Table 1:
Tree characteristics
and suitability of trees for dendroremediation purposes.
|
|
Characteristic
/ Tree |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
1 Availability |
Hybrid willow |
Hybrid willow |
Hybrid willow |
Hybrid poplar |
Birch |
Norway spruce |
Canadian white spruce |
Scots pine |
|
Local forest nurseries |
|
|
|
|
X |
X |
X |
X |
|
X |
X |
|
X |
|
|
|
|
|
|
Schoenmuth (berndschoenmuth@yahoo.de) |
|
|
X |
|
|
|
|
|
|
2 Propagation |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
Vegetative propagation (cloning) |
++ |
+ |
+++ |
++ |
- |
-- |
-- |
-- |
|
Seed propagation |
|
|
|
|
X |
X |
X |
X |
|
3 Physiological activity time |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
Leaf/needle
emergence |
++ |
+ |
± |
± |
± |
-- |
- |
- |
|
Dormancy |
+ |
++ |
+ |
++ |
+++ |
+++ |
+++ |
+++ |
|
4 Utilization in the present project |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
Outdoor experiments |
X |
X |
|
X |
X |
X |
|
|
|
Dynamical dendrotoxicity experiments with basal pollutant application |
X |
X |
|
X |
X |
X |
X |
X |
|
Radiotracer experiments with [14C]-TNT |
|
X |
|
|
|
X |
|
|
|
tree analysis on former ammunition plant sites |
|
(X) |
|
|
X |
X |
|
|
|
5
Evidence
for TNT-degradation |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
TNT and/or ADNT in roots |
X |
X |
X |
X |
X |
X |
X |
X |
|
TNT and/or ADNT in above-ground tree compartments |
X |
X |
X |
X |
--- |
(X) |
|
|
|
[14C]-TNT transformation |
|
X |
|
|
|
X |
|
|
|
6 Further characteristics |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
Velocity of culture establishment |
+++ |
++ |
+++ |
++ |
+ |
+ |
+ |
+ |
|
Flooding tolerance (temporarily !) |
++ |
+ |
+++ |
++ |
- |
-- |
-- |
-- |
|
Transpiration productivity |
++ |
++ |
+++ |
+++ |
+- |
++ |
++ |
+ |
|
Drought resistance |
|
++ |
|
|
+ |
+ |
|
++ |
|
Suitability for rapid wood composting |
+ |
+ |
+ |
+ |
|
|
|
|
|
Dendroremediation improvement by mycorrhiza action expected |
|
|
|
|
|
+ |
+ |
+ |
|
Dry mass yield per year [dt/ha] |
84 |
56 |
n.det. |
86 |
55 |
78 |
n.det. |
26 |
|
Dry mass yield per year [kg/m²] |
0.84 |
0.56 |
n.det. |
0.86 |
0.55 |
0.78 |
n.det. |
0.26 |
|
Suitability as short rotation crop |
X |
X |
X |
X |
|
|
|
|
|
7
sanitation
potential basing on experimental data
|
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
Yearly dendroremediation potential [g TNT/m²] |
6.0 |
8.5 |
n.det. |
4.2 |
5.2 |
1.9 |
n.det. |
0.8 |
|
8 Suitability for experimental dendroremediation |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
Suitability for wick application experiments |
++ |
+ |
++ |
+ |
- |
+ |
++ |
+ |
|
Suitability for field bioindication of TNT |
+++ |
+ |
+ |
+ |
+ |
+ |
+ |
+ |
9 Suitability for practical dendroremediation |
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
|
Tree based constructed wetlands |
++ |
+ |
+++ |
++ |
- |
- - |
- - |
- - |
|
Hydraulic control |
++ |
+ |
+++ |
++ |
- |
- - |
- - |
- - |
|
Tree buffer strips and run-off-avoidance |
++ |
++ |
+++ |
++ |
+ |
+ |
+ |
+ |
|
Tree planting on clamps of contaminated soil |
+ |
++ |
|
|
+ |
|
|
|
|
Vegetation cover for reduction of leachate (reducing evapotranspiration) |
+ |
++ |
+ |
|
|
|
|
|
Suitability as reposition plants |
+ |
++ |
|
|
+ |
|
|
+ |
|
|
Salix |
Salix |
Salix |
Populus |
Betula |
Picea |
Picea |
Pinus |
Planting of forests after soil homogenization |
+ |
+ |
+ |
+ |
+ |
+++ |
+ |
+++ |
|
Interception of tree crowns |
+ |
+ |
+ |
+ |
+ |
++ |
++ |
+++ |
|
Enhancement of natural attenuation processes |
+ |
+ |
+ |
+ |
+ |
+ |
+ |
+ |
Web date: June 2002, last update: 13.02.04 18:05 by Bernd Schoenmuth@yahoo.de