Venetian Municipality is developing several actions to control lagoon pollution, including the planting of windbreaks and hedgerows. These are reintroduced by means of particular landscape planning model, accounting for the needing of local agriculture (Franco et al., 1995b, 1996).
There was a lack of knowledge about the effect of the buffer strips in pollution control in Northern Italy environment (Franco et al., 1995a). To assess the non-point source pollution functionality in the planning system, a filed test was established.
This test was a part of a more complex experimentation on non-point
pollution in the area of Venice Lagoon (Perelli et al., 1993), including
control of manure utilisation and the implementation of the "Dafne®
1" approach to animal manure utilisation (Perelli and Franco, 1994a,
1994b).
The hedgerow was realised with several experimental structure scheme using local species selected for their high capacity to control nutrients leaching:
Fertilization was made with mineral fertiliser (urea, mono-ammonium
phosphate and potassium muriate), compared with liquid animal manure, both
to supply 300 kg/ha of nitrogen, 120 kg/ ha of phosphorus (P2O5) and 120
kg/ ha of potassium (K2O)
The control (with an efficiency of about 50%) was very effective for nitrate, the most dangerous pollutant in water quality assessment. The control of ammonium and organic nitrogen was less effective, but we have to consider that these compounds are less mobile in the soil and generally less dangerous for water quality.
The mean control efficiency of total nitrogen was higher than
30% and this may be considered a good result. Phosphorus control was less
effective (16.1%), but its content in water was very low (Table 1). Pollutant
control was very strong for runoff: the hedgerow stops more than 85% of
solids, and consequently there is a good control of total phosphorus (Table
2).
Table 1. Water table quality. Mean: December 1994 - July 1996
| No hedgerow | Hedgerow | ||
|---|---|---|---|
| N-NH4 | mg/l | 0.231 | 0.160 |
| N-NO2 | mg/l | 0.029 | 0.033 |
| N-NO3 | mg/l | 3.042 | 1.556 |
| Organic N | mg/l | 1.668 | 1.639 |
| Total N | mg/l | 4.946 | 3.288 |
| Total P | mg/l | 0.596 | 0.501 |
| No hedgerow | Hedgerow | ||
|---|---|---|---|
| Water | mm | 29.69 | 11.05 |
| Solids | kg/ha | 4501.90 | 550.00 |
| N-NH4 | g/ha | 492.12 | 227.18 |
| N-NO2 | g/ha | 31.59 | 14.27 |
| N-NO3 | g/ha | 260.50 | 50.71 |
| Organic N | g/ha | 1584.90 | 292.40 |
| Total N | g/ha | 2319.85 | 581.21 |
| Soluble P | g/ha | 51.708 | 23.65 |
| Total P | g/ha | 9481.87 | 2325.24 |
The good abatement of runoff is probably due to a very rapid growing
of a permanent vegetated bank above the multistoried one-line shelterbelt.
The minor control of buffer strips, instead, is probably linked to the
reduced activity in the first year after planting. For a quicker effect
in pollutant abatement, in this experiment older plant material, which
suffers of heavier planting stress, was used instead of seedlings.
Figure 2. Seasonal variation of abetement
As show in figure 3, in fact, the control efficiency of all groundwater pollutants is increasing with the hedgerow taking roots: this is more clear taking in account plant growing season, which in Mediterranean climate is reduced during all winter and in full summer.
Figure 3. Effect on cumulative runoff
Especially nitrogen and N-NH4 have a contrasting seasonal evolution,
and phosphorous seems to have slower evolution trend than N-NO3. These
behaviours are probably linked to the soil and rizosphere biological activity,
as it will be possible to state in further experiment phases.
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