<?xml version='1.0' encoding='utf-8'?>
<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>James L. Carter</dc:contributor>
  <dc:creator>Harry V. Leland</dc:creator>
  <dc:date>1985</dc:date>
  <dc:description>&lt;ul id="l1" class="custom"&gt;&lt;li&gt;&lt;span class="bullet"&gt;1&lt;/span&gt;Production of periphyton, nitrogen fixation and processing of leaf litter were examined in an oligotrophic Sierra Nevada stream and the responses of these processes to copper (2.5, 5 and 10&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sub&gt;T&lt;/sub&gt; [total filtrable copper]; approximately 12, 25 and 50 ng 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sup&gt;2+&lt;/sup&gt;) were determined.&lt;/li&gt;&lt;li&gt;&lt;span class="bullet"&gt;2&lt;/span&gt;Autotrophic and total production were estimated from 3-week accumulations of biomass on artificial substrates. Mean autotrophic production in the control ranged from 0.22 to 0.58 mg C m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt; in summer-autumn 1979, but declined to 0.08–0.28 mg C m &lt;sup&gt;2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt; after peak discharge in summer 1980, apparently due to phosphorus-limited growth. Total production in the control ranged from 0.30 to 0.82 mg C m&lt;sup&gt;-2&lt;/sup&gt; h &lt;sup&gt;-1&lt;/sup&gt; in summer-autumn 1979 and from 0.16 to 0,68 mg C m &lt;sup&gt;-2&lt;/sup&gt; h &lt;sup&gt;-1&lt;/sup&gt; in 1980. Mean autotrophic productivity, estimated by &lt;sup&gt;l4&lt;/sup&gt;C-bicarbonate uptake in daylight, ranged from 0.30 to 2.8 mg C m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;.&lt;/li&gt;&lt;li&gt;&lt;span class="bullet"&gt;3&lt;/span&gt;Autotrophic productivity was reduced by 57–81% at 2.5&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sub&gt;T&lt;/sub&gt;, 55–96% at 5&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt;Cu&lt;sub&gt;T&lt;/sub&gt;, and 81–100% at 10&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; CU&lt;sub&gt;T&lt;/sub&gt;, Heterotrophic productivity (based on dark &lt;sup&gt;35&lt;/sup&gt;S-sulphate uptake) was inhibited to a lesser extent (28–63% at 2.5&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sub&gt;T&lt;/sub&gt;, 24–84% at 5&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sub&gt;T&lt;/sub&gt;, and 67–92% at 10&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sub&gt;T&lt;/sub&gt;), The inhibition of autotrophic and heterotrophic productivity persisted through the year of exposure. Production in stream sections previously exposed to 2.5 and 5&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt;Cu&lt;sub&gt;T&lt;/sub&gt; increased to control levels within 4 weeks after dosing, but remained depressed for more than 7 weeks after exposure to 10&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sub&gt;T&lt;/sub&gt;.&lt;/li&gt;&lt;li&gt;&lt;span class="bullet"&gt;4&lt;/span&gt;The specific rate of photosynthesis (mg C mg chlorophyll &lt;i&gt;a&lt;/i&gt;&lt;sup&gt;-1&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;) of mature periphyton communities declined at all test concentrations of copper, but the rate for periphyton on newly-colonized surfaces did not change. The species composition of benthic algae shifted during exposure to an assemblage more tolerant of copper. &lt;i&gt;Achrtanthes minutissima&lt;/i&gt; and &lt;i&gt;Fragilaria crotonensis&lt;/i&gt; were the primary replacement species on newly-colonized surfaces.&lt;/li&gt;&lt;li&gt;&lt;span class="bullet"&gt;5&lt;/span&gt;The nitrogenase activity of blue-green algae was low. with controls ranging from 2.4 to 12 nmol C&lt;sub&gt;2&lt;/sub&gt;H&lt;sub&gt;2&lt;/sub&gt; m&lt;sup&gt;-2&lt;/sup&gt; h&lt;sup&gt;-1&lt;/sup&gt;. Nitrogenase activity was inhibited during the initial weeks of exposure by 5 and 10&lt;i&gt;μ&lt;/i&gt;g 1&lt;sup&gt;-1&lt;/sup&gt; Cu&lt;sub&gt;T&lt;/sub&gt;. However, after 9 months of exposure, control and copper-treated sections did not differ.&lt;/li&gt;&lt;li&gt;&lt;span class="bullet"&gt;6&lt;/span&gt;The rate of processing of leaf litter, estimated by microbial respiration and nutrient quality of litter of resident riparian woodland taxa, was inhibited at all test concentrations of copper.&lt;/li&gt;&lt;/ul&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1111/j.1365-2427.1985.tb00189.x</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Wiley</dc:publisher>
  <dc:title>Effects of copper on production of periphyton, nitrogen fixation and processing of leaf litter in a Sierra Nevada, California, stream</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>