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The toxic mixing zone of neutral and acidic river water: Acute aluminium toxicity in brown trout (Salmo trutta L.)
Authors:P. M. Verbost  M. H. G. Berntssen  F. Kroglund  E. Lydersen  H. E. Witters  B. O. Rosseland  B. Salbu  S. E. Wendelaar Bonga
Affiliation:1. Department of Animal Physiology, University of Nijmegen, NL-6525-ED, Nijmegen, The Netherlands
2. Norwegian Institute for Water Research, Televn. 1, 4890, Grimstad, Norway
3. Norwegian Institute for Water Research, Kjels?s N-0411, Oslo, Norway
4. Radioprotection Department, VITO, Boeretang 200, B-2400, Mol, Belgium
5. Laboratory for Analytical Chemistry, Agricultural University of Norway, N-1432?S, Norway
Abstract:Mixing of acid river water containing aluminium (pH 5.1, Al 345 mgrg.l–1) with neutral water of a lake (pH 7.0, Al 73 mgrg.l–1) resulted in water (pH 6.4, Al 245 mgrg.l–1) with a pH (6.4) and Al concentration (245 mgrg.l–1) expected to have low toxicity to fish on the basis of current Al toxicity models. However, under semi-field conditions the freshly mixed water (a few sec. after mixing) proved to be highly toxic to brown trout. The fish were exposed to the water at different places along a 30 m channel. At the beginning of the channel acid and neutral water were continuously mixed; the mixed water left the channel after 340 sec. The cells of the gills showed a highly increased rate of cell death by apoptosis and necrosis. Intercellular spaces were enlarged, and many leucocytes penetrated in these spaces. Mucus release was stimulated to depletion. Plasma chloride levels were hardly affected. There was a clear gradient in the deleterious effects on the fish along the channel. The fish at the beginning of the channel (about 12 sec. after mixing of the water), were severely affected, whereas the fish kept at the end of the channel (340 sec. after mixing) were only mildly affected. In the natural situation fish will relatively quickly pass through a mixing zone. In our study we therefore focused on the effects on fish after a 60 min exposure to a mixing zone (5 sec after mixing), with subsequent recovery in a region downstream of the confluence and in neutral water with low Al. The recovery in the downstream area (at the end of the channel, i.e. 5 min after mixing) was clearly hampered when compared to the recovery in neutral water with low aluminium. Thus, a short exposure to the toxic mixing zone followed by a stay in water downstream of this zone, as may occur in nature, is detrimental to migrating trout. We conclude that freshly mixed acid and neutral water contain toxic components during the first seconds to minutes after mixing, that can not be explained by current models on aluminium toxicity.
Keywords:aluminium toxicity  non-equilibrium chemistry  pH  stress  apoptosis  necrosis  trout
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