Monitoring Parameters. 2.1.1 The Project Specific EM&A Manual designated 4 air quality monitoring stations, 2 noise monitoring stations, 21 water monitoring stations (9 Impact Stations, 7 Sensitive Receiver Stations and 5 Control/Far Field Stations) to monitor environmental impacts on air quality, noise and water quality respectively. Pre-set and fixed transect line vessel based dolphin survey was required in two AFCD designated areas (Northeast and Northwest Lantau survey areas). The impact dolphin monitoring at each survey area should be conducted twice per month.
2.1.2 For impact air quality monitoring, monitoring locations AMS2 (Xxxx Xxxxx Development Pier) and AMS7 (Hong Kong SkyCity Marriott Hotel) were set up at the proposed locations in accordance with Project Specific EM&A Manual. The conditional omission of Monitoring Station AMS6 was effective since 19 November 2012. For monitoring location AMS3 (Ho Yu College), as proposed in the Project Specific EM&A Manual, approval for carrying out impact monitoring could not be obtained from the principal of the school. Permission on setting up and carrying out impact monitoring works at nearby sensitive receivers, like Caribbean Coast and Coastal Skyline, was also sought. However, approvals for carrying out impact monitoring works within their premises were not obtained. Impact air quality monitoring was conducted at site boundary of the site office area in Works Area WA2 (AMS3B) respectively. Same baseline and Action Level for air quality, as derived from the baseline monitoring data recorded at Ho Yu College, was adopted for this alternative air quality location.
2.1.3 For impact noise monitoring, monitoring locations NMS2 (Seaview Crescent Tower 1) was set up at the proposed locations in accordance with Project Specific EM&A Manual. However, for monitoring location NMS3 (Ho Yu College), as proposed in the Project Specific EM&A Manual, approval for carrying out impact monitoring could not be obtained from the principal of the school. Permission on setting up and carrying out impact monitoring works at nearby sensitive receivers, like Caribbean Coast and Coastal Skyline, was also sought. However, approvals for carrying out impact monitoring works within their premises were not obtained. Impact noise monitoring was conducted at site boundary of the site office area in Works Area WA2 (NMS3B) respectively. Same baseline noise level, as derived from the baseline monitoring data recorded at Ho Yu College was adopted for this alterna...
Monitoring Parameters. Water chemistry sampling must conform with the minimum required monitoring parameters in Section 12.0 of Appendix L.
Monitoring Parameters. Project Proponents shall identify parameters that can be used to properly monitor each non-neutral Sustainable Development Indicator according to section T.
Monitoring Parameters. In order to establish permanent operating and monitoring parameters for the Alternative HAP Treatment Technology, PCA shall propose, contemporaneous with the submission of the analytical results from the initial performance test, values (or value ranges) for those operating parameters that WDNR and Region 5 approved in connection with the test protocol. PCA’s proposed values must be justifiable under the data collected during the initial performance test, other data and engineering assessments generated as part of the treatability study and quarterly performance tests, or manufacturers’ recommendations.
Monitoring Parameters. 2.2.1 During the reporting period, there was no night-time operation of 8-car train, except on 15 January 2017, and therefore no night-time monitoring was conducted for 8-car train between 16 January and 14 February 2017. However, due to adverse weather on 15 January 2017, night-time noise monitoring was cancelled.
Monitoring Parameters. Table 3-2 provides the monitoring parameters and reporting limits for general and major ions, nutrients and metals required for the GNA.
Monitoring Parameters. Water samples for total phosphorus, total nitrogen, soluble reactive phosphorus and total soluble inorganic nitrogen are collected from the euphotic zone (2.5x Secchi depth). Nitrogen variables will be monitored to evaluate N:P ratios (see discussion, Pages 16-17.) If resources allow, it is recommended that soluble phosphorus and nitrogen also be analyzed to provide a more robust data set that may help with identification of nutrient sources. Samples will be taken using a 1000 xx Xxxxxxxx sampler, and depth integrated from the euphotic zone. Chlorophyll-a samples will be collected from the same two locations. Field parameters will also include Secchi depth measured at Hope, Granite and Bayview. Detailed sampling methods will be contained in a sampling and analysis plan currently being prepared by Land & Water and to be approved by Montana and Idaho. Table 3. Sample volumes, containers, preservation and holding times for lake nutrient samples Analyte Sample Volume Container Preservation Holding Time Total P and N 125 ml polyethylene add H2SO4 to pH<2, cool to <4°C 28 days Total Soluble inorganic N4 (NO2+NO3+NH4) 125 ml polyethylene filter, add H2SO4 to pH<2, cool to <4°C 28 days Soluble Reactive Phosphorus1 125 ml polyethylene filter, cool to <4°C 48 hours Chlorophyll-a 1000 ml amber polyethylene Filter, freeze 7 days Monitoring and Assessment Program Costs Funding for the following monitoring program elements will need to be covered: • Monitoring for the above parameters at two stations (Hope and Granite); • Applicable data from the Council’s existing Xxxxx Fork-Pend Oreille monitoring program; • Trend analyses and reporting; and • Source loading analysis from Idaho
