The blooms of
L. chlorophorum have significant economic and ecological impacts due to the hypoxic conditions the bloom generates. and the advisement against swimming during the blooms. The ecological consequences of these blooms stem from the hypoxic conditions that are generated from biomass recycling, in combination with the increased concentrations of DIP and NH4 inside the blooms, also associated with high levels of
nutrient recycling. The oxygen concentration in
L. chlorophorum blooms is frequently brought below the threshold that most benthic invertebrates can survive, representing just one of the ecological effects of these blooms. For
bivalves, the typically observed response to hypoxia is reduced feeding and oxygen consumption, thought to negatively affect their growth and survival. It is thought that these blooms are becoming more common with climate change as waters become warmer and the elemental composition of seawater alters. Although the exact mechanism is not known, the presence of
L. chlorophorum is correlated with negative effects on
oyster (Crassostrea gigas) growth, causing economic harm for oyster farmers. It has been suggested that this is due to
L. chlorophorum impairing the filtration ability of
C. gigas by producing acid glycoconjugates and transparent exopolymer particles. It also appears that
C. gigas has a poor ability to assimilate
L. chlorophorum. Both of these mechanisms could explain the observed reduced growth. The problem this causes for farmers is exacerbated by the longevity of
L. chlorophorum blooms. Marine mixotrophic protists such as
Lepidodinium play an important role in oceans in terms of nutrient cycling as well as in the food chain. The carbon rich Transparent Exopolymer Particles (TEP) known to be produced by
L. chlorophorum are important in the sedimentation of organic matter which enables bacteria abundance. Although many other organisms contribute to this process,
L. chlorophorum is particularly important as it produces more TEP than many other organisms, with an average of 380g xanthan equiv [mg chl a] −1 d−1 being produced by
L. chlorophorum. TEP production in
L. chlorophorum also represents a much higher proportion of its carbon intake, with an average of 70% of carbon fixed by photosynthesis and excreted as TEP. During blooms of
L. chlorophorum, the TEP concentration can become very high which promotes bacterial activity to the point where anoxic conditions and high levels of organic carbon degradation are created, leading to the ecological impacts. == Species ==