Sampling Frequency. Source coding algorithm *
Sampling Frequency. Sampling for public health monitoring under this plan will occur at each of the identified sites as listed in Table 2. Public health sampling in Upper Klamath Lake and Keno, X.X. Xxxxx, Copco, and Iron Gate reservoirs will begin in May. Public health samples will be submitted for cell-count analysis only from May (ODEQ and PacifiCorp sites only), June, and July and analysis of all samples will be rushed. After July, no cyanobacteria samples will be analyzed. Samples will continue to be sent to EPA for microcystin analysis throughout the season. Public health memos will include the microcystin toxin data as it is received from the EPA lab. Monitoring data from previous annual public health sampling efforts (2005- 2018) indicates that Microcystis cell counts and/or microcystin levels in non-river samples (Iron Gate and Copco reservoirs and Upper Klamath Lake) typically remain elevated until cooler weather and shorter days terminate the blooms.
Table 1. 2019 Klamath River sampling sites for public health monitoring of cyanobacteria and cyanotoxins in surface water samples, approximate river mile, and sampling entity. Site ID Location River Mile Sampling Entity
Sampling Frequency. EO data on optical properties of inland waters are typically available every few days (e.g. Sentinel 2 and 3). For algorithm calibration, the temporal match with the satellite overpass should be short, ranging from 1 hour to ~3 days. The ideal time difference depends on the temporal variability of the water quality parameter of interest, so defining a specific frequency is context dependent. A recommendation is to derive match-ups within 3 hours. Measurements taken during late morning (local time) are closest to the overpasses of optical sensors across the globe. For providing match-up with EO data, sampling frequency of in-situ data should by high, ideally, every day or every few days. Permanent measurement installations help to provide a large number of match-ups, though not all parameters can be measured with automated systems. Sampling frequencies of monthly or less are likely to have fewer close match-ups with satellite data, unless monthly in-situ sampling programmes are explicitly designed to ensure match-up with satellite overpasses. Sampling frequency varies a lot across the different variables and depends on the measurement technique. The frequency ranges from every few minutes for parameters that can be measured automatically using sensors (e. g. temperature, dissolved oxygen, chlorophyll-a fluorescence, turbidity) to parameters that need to be processed in a laboratory, which are more typically sampled at weekly to monthly frequency (e.g. microbiology, cyanobacteria, chlorophyll-a concentration, suspended matter concentration). The possibility of making campaigns though the year or years, also determines the sampling frequency, from months to years. Monthly sampling is most common and corresponds to the sampling frequency typically required for monitoring inland water quality by regulations (e.g. the European Water Framework Directive). However, hourly to weekly sampling can be required for some water quality parameters for research or investigative monitoring purposes to adequately capture natural variability (e.g. diurnal changes in dissolved oxygen or turbidity changes associated with storm events). Permanent measurement stations such as AERONET-OC stations and the GLEON network provide very valuable data sets as they enable match-ups with each overflight and provide key data on reflectance and/or water quality in very many different conditions (light, sun/viewing angles, atmospheric conditions).
Sampling Frequency. The Stillwater Oversight Committee shall determine the frequency of chemical and physical monitoring at each site location.
Sampling Frequency. Suspended and bedload sediment sampling must be conducted once every 3 years at all monitoring site locations designated in this Section 1.19 of this Appendix at the same time of year.
Sampling Frequency. The East Boulder Oversight Committee shall determine the frequency of chemical and physical monitoring at each site location. Currently, sites EBR-001, EBR-002, DF-01 are monitored quarterly. Currently, sites EBR-003 and EBR-004 are monitored monthly. Currently, site EBR-005 is monitored in the first and third quarters of each year. At the time SMC commits to construction of the Boe Ranch facilities, chemical and physical monitoring at sites EBR-005, EBR-007, EC-01 and EBR-008 shall resume quarterly frequency.
Sampling Frequency. Sampling occurs at regular intervals, with samples being collected once every hour over 24 hours. This frequent sampling schedule allows for comprehensive monitoring of water quality parameters, capturing any fluctuations or trends that may occur throughout the day.
Sampling Frequency. The sampling frequency should be equal to at least 8 FH. In the case of analogical recording, when the recording and reading speeds are different, the sampling frequency can be divided by the speed ratio.
Sampling Frequency. The frequency of sampling is expected to correspond with the extent of conservation measures required by the adopted acres target defined for each Partner according to their adoption rate and extent of enrolled lands. Partners reporting actual adopted acres above-and-beyond their minimum target are not required to monitor any additional points above the threshold associated with their adopted acres target. Sampling frequency is intended to provide a reasonable sample size that can characterize results of conservation measures, while also being reasonably accomplished by rights-of-way and land managers who are also tasked with overseeing the safe implementation of conservation measures and covered activities, as well as sustain operations of their infrastructure. The following recommended frequency is based on expected extent of adopted acres, as well as potential Partner feedback received during development of this agreement.
Sampling Frequency. All converted Foglight™ 4 agents have a secondary ASP (usually called SamplingFreq) that controls data collection frequencies. To access that ASP, select an agent in the Administration module of the browser interface and then choose Edit Properties. XML-HTTP Agent Adapter The XML-HTTP Agent Adapter enables agents to post data in XML format over HTTP(S). By default this adapter is configured to reject posted XML text larger than 20MB. Check the agent logs for specific error messages indicating that the data was rejected due to size constraints. Open web.xml, which is located in <foglight_home>/cartridge/XmlHttpAgentAdapter-*.car, component XmlHttpAgentAdapter-5_2_4\WebApp-\foglight-xml-agent-adapter.war, file WEB- INF\web.xml, and adjust the maxContentLength parameter. Note 1 You will need to unzip the .car file, then unzip the .war file, edit the web.xml file, and then re- package the cartridge manually (using zip). After you modify the cartridge, you will have to delete
