Processing techniques of selected oilseed by-products of potential use in animal feed: Effects on proximate nutrient composition, amino acid profile and antinutrients.

The effects of processing by autoclaving (AC), soaking (SK), short-term fermentation (S-TF, 4 d) and long-term fermentation (L-TF, 14 d) on the nutritional composition, amino acid profile and some antinutrients were determined for cottonseed meal (CSM), groundnut meal (GNM) and groundnut husk (GH) in this study. After processing, crude protein content improved by 11% after L-TF, and crude lipid content 25% after SK for CSM; crude protein content improved by 27% after S-TF and L-TF, and crude lipid content 13% after SK for GNM. Soaking and fermentation were shown to significantly increase essential amino acid contents by 44% (SK, methionine) in CSM and 46% in GNM (L-TF, histidine). Phosphorus content was reduced by 59% in CSM and 57% in GNM by L-TF. All processing techniques, with the exception of AC, reduced phytic acid and gossypol contents in CSM and GNM. It was concluded that SK and fermentation were simple, cost-effective, and efficient ways to improve the nutritional value of the selected oilseed by-products.

Bioconcentration of two basic pharmaceuticals, verapamil and clozapine, in fish.

The present study examined the bioconcentration of 2 basic pharmaceuticals: verapamil (a calcium channel blocker) and clozapine (an antipsychotic compound) in 2 fresh water fishes, fathead minnow and channel catfish. In 4 separate bioconcentration factor (BCF) experiments (2 chemicals × 1 exposure concentration × 2 fishes), fathead minnow and channel catfish were exposed to 190 µg/L and 419 µg/L of verapamil (500 µg/L nominal) or 28.5 µg/L and 40 µg/L of clozapine (50 µg/L nominal), respectively. Bioconcentration factor experiments with fathead consisted of 28 d uptake and 14 d depuration, whereas tests conducted on catfish involved a minimized test design, with 7 d each of uptake and depuration. Fish (n = 4-5) were sampled during exposure and depuration to collect different tissues: muscle, liver, gills, kidneys, heart (verapamil tests only), brain (clozapine tests only), and blood plasma (catfish tests only). Verapamil and clozapine concentrations in various tissues of fathead and catfish were analyzed using liquid chromatography-mass spectrometry. In general, higher accumulation rates of the test compounds were observed in tissues with higher perfusion rates. Accumulation was also high in tissues relevant to pharmacological targets in mammals (i.e. heart in verapamil test and brain in the clozapine test). Tissue-specific BCFs (wet wt basis) for verapamil and clozapine ranged from 0.7 to 75 and from 31 to 1226, respectively. Tissue-specific concentration data were used to examine tissue-blood partition coefficients.

Tissue-specific uptake and bioconcentration of the oral contraceptive norethindrone in two freshwater fishes.

The environmental presence of the oral contraceptive norethindrone (NET) has been reported and shown to have reproductive effects in fish at environmentally realistic exposure levels. The current study examined bioconcentration potential of NET in fathead minnow (Pimephales promelas) and channel catfish (Ictalurus punctatus). Fathead minnows were exposed to 50 µg/l NET for 28 days and allowed to depurate in clean water for 14 days. In a minimized 14-day test design, catfish were exposed to 100 µg/l NET for 7 days followed by 7-day depuration. In the fathead test, tissues (muscle, liver, and kidneys) were sampled during the uptake (days 1, 3, 7, 14, and 28) and depuration (days 35 and 42) phases. In the catfish test, muscle, liver, gill, brain, and plasma were collected during the uptake (days 1, 3, and 7) and depuration (day 14) stages. NET tissue levels were determined by gas chromatography-mass spectrometry (GC-MS). Accumulation of NET in tissues was greatest in liver followed by plasma, gill, brain, and muscle. Tissue-specific bioconcentration factors (BCFs) ranged from 2.6 to 40.8. Although NET has been reported to elicit reproductive effects in fish, the present study indicated a low potential to bioconcentrate in aquatic biota.

Algal bioaccumulation of triclocarban, triclosan, and methyl-triclosan in a North Texas wastewater treatment plant receiving stream.

Algae comprise the greatest abundance of plant biomass in aquatic environments and are a logical choice for aquatic toxicological studies, yet have been underutilized in this capacity. The lipid content of many algal species provides a point of entry for trophic transfer of lipophilic organic contaminants. Triclosan (TCS) and triclocarban (TCC), widely used antimicrobial agents found in numerous consumer products, are incompletely removed by wastewater treatment plant (WWTP) processing. Methyl-triclosan (M-TCS) is a metabolite of TCS more lipophilic than the parent compound. The focus of this study was to quantify algal bioaccumulation factors (BAFs) for TCS, M-TCS, and TCC in Pecan Creek, the receiving stream for the City of Denton, Texas WWTP. The complex algal compartment was field identified for collection and verified by laboratory microscopic description as being comprised of mostly filamentous algae (Cladophora spp.) and varying inconsequential levels of epiphytic diatoms and biofilm. Algae and water column samples were collected from the WWTP outfall, an upstream site, and two downstream sites and analysed by isotope dilution gas chromatography/mass spectrometry (GC/MS) for TCS and M-TCS and liquid chromatography/mass spectrometry (LC/MS) for TCC. TCS, M-TCS, and TCC in Pecan Creek water samples taken at and downstream from the WWTP were at low ppt concentrations of 50-200 ng l(-1) and were elevated to low ppb concentrations of 50-400 ng g(-1) fresh weight in algae collected from these stations. The resulting BAFs were approximately three orders of magnitude. TCS, M-TCS and TCC appear to be good candidate marker compounds for evaluation of environmental distribution of trace WWTP contaminants. Residue analysis of filamentous algal species typically occurring in receiving streams below WWTP discharges is a readily obtained indicator of the relative bioaccumulative potential of these trace contaminants.