Abstract:Selected biological and physiological parameters of hydrilla [Hydrilla verticillata(L.f.) Royle # HYLLI] biotypes were compared in growth chambers, glasshouse, or outside aquaria. Salinity tolerance was similar for both biotypes with an injury threshold of approximately 13 parts per thousand (ppt). The registered aquatic herbicides diquat (6,7-dihydrodipyrido [1,2-α:2′,1′-c] pyrazinediium ion) and dipotassium and monoamine salts of endothall (7-oxabicyclo [2.2.1] heptane-2,3-dicarboxylic acid)4produced similar… Show more
“…The general pattern in this experiment agrees with that noted previously by other researchers (Hailer et aL 1976, Van et al 1978, Bowes et al 1979, Spencer and Anderson 1986, 1987, Steward and Van 1987, Van 1989. Propagule production is enhanced by short photoperiod and reduced by long photoperiod.…”
Section: Discussionsupporting
confidence: 92%
“…Previous reports have demonstrated that photoperiod (HalIer et al 1976, Van et al 1978, Bowes et al 1979, Spencer and Anderson 1986, 1987, Steward and Van 1987 and soil fertility (Bruner and Batterson 1984, Barko and Smart 1986, McFarland and Barko 1987, Spencer 1990, Spencer et al 1992) influence vegetative 134 propagule production. For many species, interactions between environmental factors and propagule production have not been studied.…”
Potamogeton pectinatus, P. gramineus, and monoecious ltydrilla verticillata were grown in greenhouse experiments at 2 photoperiods, 5 levels of sediment nutrients, and from initial propagules of 3 different size classes to determine how these factors influenced growth and production of vegetative propagules. Potamogeton pectinatus weight increased with increasing tuber size and soil fertility, but differences between plants grown at two photoperiods were small. Mean weight of tubers was greater for plants grown under a 10-h photoperiod and from tubers in the medium or large size class. Tuber production by plants grown from small tubers under a 10-h photoperiod was much less and was about the same as that for all plants grown under the 16-h photoperiod whatever the initial tuber size. Potamogeton gramineus weight was greater for plants grown on more fertile soils at the 16-h photoperiod. Plant weights at the 10-h photoperiod were less affected by soil fertility. Plants from larger winter buds weighed more. Winter buds were only produced under the 10-h photoperiod. For 1t. verticillata, there were several significant interactions. In general, plants from larger tubers weighed more if they grew on more fertile soils or at the 16-h photopefiod. Plants grown at the short photoperiod produced more tubers with increasing soil fertility and with increasing propagule size. These results imply that propagule size may be important in determining aquatic plant persistence in an area through its effects on growth and propagule production.
“…The general pattern in this experiment agrees with that noted previously by other researchers (Hailer et aL 1976, Van et al 1978, Bowes et al 1979, Spencer and Anderson 1986, 1987, Steward and Van 1987, Van 1989. Propagule production is enhanced by short photoperiod and reduced by long photoperiod.…”
Section: Discussionsupporting
confidence: 92%
“…Previous reports have demonstrated that photoperiod (HalIer et al 1976, Van et al 1978, Bowes et al 1979, Spencer and Anderson 1986, 1987, Steward and Van 1987 and soil fertility (Bruner and Batterson 1984, Barko and Smart 1986, McFarland and Barko 1987, Spencer 1990, Spencer et al 1992) influence vegetative 134 propagule production. For many species, interactions between environmental factors and propagule production have not been studied.…”
Potamogeton pectinatus, P. gramineus, and monoecious ltydrilla verticillata were grown in greenhouse experiments at 2 photoperiods, 5 levels of sediment nutrients, and from initial propagules of 3 different size classes to determine how these factors influenced growth and production of vegetative propagules. Potamogeton pectinatus weight increased with increasing tuber size and soil fertility, but differences between plants grown at two photoperiods were small. Mean weight of tubers was greater for plants grown under a 10-h photoperiod and from tubers in the medium or large size class. Tuber production by plants grown from small tubers under a 10-h photoperiod was much less and was about the same as that for all plants grown under the 16-h photoperiod whatever the initial tuber size. Potamogeton gramineus weight was greater for plants grown on more fertile soils at the 16-h photoperiod. Plant weights at the 10-h photoperiod were less affected by soil fertility. Plants from larger winter buds weighed more. Winter buds were only produced under the 10-h photoperiod. For 1t. verticillata, there were several significant interactions. In general, plants from larger tubers weighed more if they grew on more fertile soils or at the 16-h photopefiod. Plants grown at the short photoperiod produced more tubers with increasing soil fertility and with increasing propagule size. These results imply that propagule size may be important in determining aquatic plant persistence in an area through its effects on growth and propagule production.
“…Dioecious Hydrilla tubers may not sprout as well at the cooler temperatures (typical of the greenhouse during the periods that the experiments were conducted) as monoecious Hydrilla or Potamogeton propagules (Steward andVan 1987, Madsen andAdams 1988).…”
Vegetative propagules of Potamogeton pectinatus, P. gramineus, and Hydrilla verticillata were exposed to aerobic or anaerobic atmospheres for 7, 14, or 21 days in the dark at 18 °C or 7 °C. There were no differences in the proportion of propagules sprouting due the presence or absence of oxygen. However, propagules exposed to an anaerobic atmosphere at 18 °C sprouted sooner than those exposed to an aerobic atmosphere. This effect was less apparent when exposure to anaerobic conditions was at 7 °C. In field experiments, Potamogeton gramineus winter buds were buried at 4 depths in Byrnes Canal sediment. Those buried tbr 25 days at 25 cm (where sediment redox potential is < 50 mV and conditions are likely hypoxic) showed discoloration consistent with sulfide deposition, and they sprouted more rapidly than winter buds buried at 5 or 15 cm. As the duration of burial in Byrnes Canal sediment increased, propagule sprouting time decreased, lh-edicting the timing of propagule sprouting in habitats with fluctuating water levels may benefit from information on seasonal changes in the oxygen status of the sediments.
“…Seasonal means (April to October) of the measurements were calculated as well as early growing season means. Early growing season was defined by temperature and included data from the first 2 months when temperatures reached 15°C, which is when experiments have shown these freshwater species, particularly H. verticillata, to sprout from tubers or germinate (Carter et al 1994;Steward and Van 1987).…”
Submersed aquatic vegetation (SAV) communities have undergone declines worldwide, exposing them to invasions from non-native species. Over the past decade, the invasive species Hydrilla verticillata has been documented in several tributaries of the lower Chesapeake Bay, Virginia. We used annual aerial mapping surveys from 1998 to 2007, integrated with spatial analyses of water quality data, to analyze the patterns and rates of change of a H. verticillata-dominated SAV community and relate them to varying salinity and light conditions. Periods of declining SAV coverage corresponded to periods where salinities exceeded 7 and early growing season (April to May) Secchi depths were <0.4 m. Increases were driven by the expansion of H. verticillata along with several other species into the upper estuary, where some areas experienced an 80% increase in cover. Field investigations revealed H. verticillata dominance to be limited to the upper estuary where total suspended solid concentrations during the early growing season were <15 mg l −1 and salinity remained <3. The effect of poor early growing season water clarity on annual SAV growth highlights the importance of water quality during this critical life stage. Periods of low clarity combined with periodic salinity intrusions may limit the dominance of H. verticillata in these types of estuarine systems. This study shows the importance of the use of these types of biologically relevant episodic events to supplement seasonal habitat requirements and also provides evidence for the potential important role of invasive species in SAV community recovery.
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