Metals Clause Samples
Metals. (i) Check nameplate details according to specification.
(ii) Physical check for any damage.
(iii) Check calibration by comparing it with a substandard meter.
(iv) Megger all insulated portions.
(v) Check C.T. and V.T. connections with particular reference to their polarities for power type meter.
Metals. Products not displayed above are not eligible for this offer unless otherwise agreed by a BlackBull Markets Employee in writing.
Metals. Restoration processes and success depend a great deal on the metal content of a given coin. What follows here is information on the general efticacy of Restoration techniques on various types of metals.
Metals. The Metals Adjustment shall be calculated and applied separately for all Products ordered for delivery during each Period using the business day immediately preceding the date Federal releases the Binding Order as the measuring date (“Measuring Date”). The Product Price will apply to all Binding Orders and Additional Orders for Products ordered for delivery during the entire applicable Period.
Metals. Metal analyses were conducted on soil and groundwater. In only one case did a metal exceed the State TTLC that classifies soil as hazardous waste for disposal purposes (Marshack, 1988); this was a subsurface soil sample in the refuse fill area that had 3000 ppm lead. Two prior Levi▇▇-▇▇▇▇▇▇ ▇▇▇surface soil samples (one panhandle and one non-refuse fill area) had elevated lead concentrations of 3800 ppm and 2000 ppm. McLaren's groundwater analytic results for metals were consistent with Levi▇▇-▇▇▇▇▇▇'▇ ▇▇▇ults. Although the water is brackish at the site, and therefore unsuitable for drinking, the metals detected in the shallow groundwater were generally below California's Maximum Contaminant Levels (MCLs) for drinking water (CDHS, 1989). Only a few metals slightly exceeded the MCLs. Therefore, the groundwater is near drinking water quality relative to metal concentrations. No elevated metal concentrations were detected in surface water from Belmont Slough. Based on the sampling results, exposure to metals at the site is not considered to pose the potential for creating significant adverse health effects.
Metals. Partition framework, except as otherwise indicated, shall be of 4” nominal stud construction.
Metals. Metal analyses were conducted on soil and groundwater. In only one case did the metals exceed the State TTLCs that classify soil as hazardous waste for disposal purposes (Marshack, 1988): refuse subsurface soil sample 7A had a detected value of 3000 ppm lead. Two prior Levi▇-▇▇▇▇▇▇ ▇▇▇surface soil samples (one panhandle and one non-refuse fill area) had detected elevated lead concentrations of 3800 ppm and 2000 ppm McLaren's groundwater analytic results for metals were consistent with Levi▇▇-▇▇▇▇▇▇'▇ ▇▇▇ults. Although the water is brackish at the site, and therefore unsuitable for drinking, the metals detected in the shallow groundwater were generally below California's Maximum Contaminant Levels (MCLs) for drinking water (CDHS, 1989). Only a few metals slightly exceeded the MCLs. McLaren's surface water analytic results for metals did not demonstrate any elevated levels.
Metals. Never use cleaners with alcohols or solvents on metals. Only use fine cotton or extra soft cloths. We recommend that tarnished metals be professionally cleaned.
Metals. Analytical results from this sampling program indicate that, in general, metals were not detected above commercial-use SCOs. In fact, there were only scattered exceedances reported at eight of the recent borings, including SB-10 through SB-13 (Blue Wing), SB-16 and SB-17 (Grind & Mix Department), SB-25 (Storage Building) and SB-28 (Red Wing). Six metals were detected above commercial-use SCOs, including arsenic, barium, chromium, copper, lead and nickel. In addition, four metals (barium, cadmium, nickel and lead) were detected above commercial-use SCOs at borings B1604, B1605 and B1607 completed in October 2006 on the main level of the Red Wing. As indicated on Plate 3, barium and lead were most often detected above the commercial-use SCOs, identified in ten and seven samples, respectively. In addition, barium and lead exceedances co-occurred in four sampling intervals at three contiguous borings, SB-11, SB-12 and SB-13. The other five metals were detected above the commercial-use SCOs in only one to three samples each. The copper and chromium exceedances coincided with barium and/or lead exceedances, whereas arsenic, cadmium and nickel concentrations above the commercial- use SCOs were most often isolated, with no other metal impacts identified. Based on these analytical results, the following conclusions can be reached regarding metals contamination beneath buildings with respect to the scope and nature of IRM activities: • Metals contamination is present in discolored soil in the upper sampling intervals at contiguous locations SB-10 through SB-13. This discoloration likely results from former pigment manufacturing activities, although the specific source of the staining is not known. However, given its proximity to an underground sewer line, this contamination may have resulted from leakage from the drains. The layout of known industrial sewer system components at the Site is provided on Plate 1. Concentrations of metals were below commercial-use SCOs in the deepest sampling intervals analyzed at SB-10, SB-12 and SB-13, in which staining was not observed. Conversely, the barium concentration exceeded the commercial-use SCO in the deepest sample from SB-11, where soil discoloration was apparent. These data therefore suggest that in the vicinity of these locations, the presence of this soil discoloration can be used as an indicator of metals contamination for purposes of soil removal during the IRM. • Stained soils at boring SB-14A also likely result fro...
Metals. All metals other than Appliances - white goods. Metals are accepted at all WWDC’s and is charged according to tonnage (note: GreenIsle prefers small amounts (½ tonne) large amounts are directed to scap metal dealer);