IP Library › Granted Patent US 10,802,009
Granted Patent B2
US 10,802,009 · App. 15/832,745 · Granted Oct 13, 2020

Networked environmental monitoring system and method

Inventors: Ning Zeng (Silver Spring, MD); Cory Martin (Washington, DC)
G01N33/004G01N33/0006Y02A50/241
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Quick Facts
Patent No.
US 10,802,009
App. No.
15/832,745
Granted
Oct 13, 2020
Kind
B2
Abstract

A system and method for monitoring environment employ a dense network of low-cost sensor nodes. The method includes obtaining environmental information by combining a plurality of observations; wherein the plurality of observations are made with in-situ or remote sensors; wherein the sensors are of different degrees of accuracy in a way to complement each other, and of different cost, and wherein the low-cost sensors form a high-density network comprising a plurality of distributed sensors. The system can monitor gas concentrations over urban areas, industrial, forest, farm, wetland, power plants and other types of surfaces.

Claims (79)

1. An environment monitoring method, comprising:

obtaining environmental information by combining a plurality of observations based on a plurality of sensors;

wherein the plurality of sensors include a first set of sensors each of a first accuracy at a first cost, and a second set of sensors each of a second accuracy at a second cost, the second accuracy being higher than the first accuracy, and the second cost being higher than the first cost, and

wherein the first set of sensors form a network comprising a plurality of distributed sensors at a first density;

the method further comprising:

obtaining environmental data with the plurality of distributed sensors, wherein the plurality of distributed sensors are calibrated to achieve a third accuracy suitable for environmental monitoring, and wherein the third accuracy is higher than the first accuracy;

assimilating the obtained environmental data together with meteorological information to derive information on the environment with a first resolution higher than a second resolution of information obtained with a network at a density lower than the first density;

calibrating the obtained environmental data by environmental correction through a successive regressing by solving:

y=a 0 x 0 +a 1 x 1 +a 2 x 2 + . . . a n x n +b+ε n

wherein y represents reported CO 2 value from the low-cost sensors, x 0 represents true CO 2 value, x 1 , x 2 , . . . , x n represent a number of other factors such as air pressure, temperature and humidity respectively;

the residuals ε n-1 and ε n at two successive regression steps are related to environmental variables using linear regression successively as:

ε n-1 =ε n −a n x n −b n ,

wherein n=1,3 for each environmental variable pressure p, temperature T, and water vapor q, wherein the linear regression method leads to eight correction coefficients, of the form a n and b n ,

the method further comprising:

applying the correction coefficients to the equation of y along with the environmental variables to correct sensor CO 2 observations for environmental influences:

y*={y−b 0 −( a 1 x 1 +b 1 ) . . . −( a n x n +b n )}/ a 0 ;

and

displaying the derived information on the environment on a display screen.

2. The method of claim 1 , wherein second set of sensors are configured for direct measurement and calibrating the first set of sensors; and

at least some of the plurality of distributed sensors are co-located with standard monitoring stations.

3. The method of claim 1 , further comprising an in-situ zero-drift correction.

4. The method of claim 1 , further comprising a network-enabled calibration.

5. An environment monitoring method, comprising:

obtaining environmental information by combining a plurality of observations based on a plurality of sensors;

wherein the plurality of sensors include a first set of sensors each of a first accuracy at a first cost, and a second set of sensors each of a second accuracy at a second cost, the second accuracy being higher than the first accuracy, and the second cost being higher than the first cost, and

wherein the first set of sensors form a network comprising a plurality of distributed sensors at a first density;

the method further comprising:

obtaining environmental data with the plurality of distributed sensors, wherein the plurality of distributed sensors are calibrated to achieve a third accuracy suitable for environmental monitoring, and wherein the third accuracy is higher than the first accuracy;

assimilating the obtained environmental data together with meteorological information to derive information on the environment with a first resolution higher than a second resolution of information obtained with a network at a density lower than the first density; and

a computational data assimilation to invert fluxes at a third spatiotemporal resolution to combine measured gas concentrations and meteorological information to derive information on pollution sources and sinks at the first resolution, including:

obtaining inputs from observations y o , the ensemble forecast

x k b ( t )= M ( x k a ( t− 1))

with mean x b and forecast of the observation

y k b =h ( x k b ) ,

wherein M represents a full nonlinear model, k is an index for model ensemble member, h is an observation operator mapping model prediction onto observation space to compute observation model error covariance y o −h(x k b );

applying the covariance as an ensemble square-root filter in which observations are assimilated to update only an ensemble mean while ensemble perturbations x k b − x b are updated by transforming forecast ensemble perturbations through a transform matrix:

x a = x b +X b {tilde over (P)} a ( HX b ) T R −1 [y o −h ( x b )]

X a =X b [( K− 1) {tilde over (P)} a ] 1/2 ,

wherein K is total number of ensemble members, X a , X b are perturbation matrices whose columns are analysis and the forecast ensemble perturbations, respectively. X b is updated every analysis time step, therefore forecast error covariance

P

b

=

1

K

-

1

⁢

X

b

⁢

X

b

T

is flow-dependent;

{tilde over (P)} a , an analysis error covariance in ensemble space, is given by

{tilde over (P)} a =[( K− 1) I +( HX b ) T R −1 ( HX b )] −1

which has dimension K by K, smaller than both dimension of the full non-linear model and number of observations;

thereby performing matrix inverse in the ensemble space spanned by forecast ensemble members, the reducing computational cost;

the method further comprising displaying the derived information on the environment over a map on a display screen.

6. The method of claim 5 , further comprising a vertical localization of column mixed CO 2 observations.

7. The method of claim 5 , further comprising a 4D assimilation.

8. The method of claim 5 , further comprising applying a short assimilation window.

9. The method of claim 5 , further comprising a temporal smoother.

10. The method of claim 5 , further comprising a time filter that combines inverted fluxes from previous several steps of data assimilation analysis as a weighted average.

11. An environment monitoring system, comprising:

a plurality of distributed sensors at a first density configured to obtain environmental data, wherein the plurality of distributed sensors comprise a first set of sensors each of a first accuracy at a first cost, and are calibrated to achieve a third accuracy higher than the first accuracy and suitable for environmental monitoring; and

one or more processing circuits configured to assimilate the obtained environmental data together with meteorological information to derive information on the environment with a first resolution higher than a second resolution of information obtained with a network at a density lower than the first density;

wherein the plurality of sensors include a first set of sensors each of a first accuracy at a first cost, and a second set of sensors each of a second accuracy at a second cost, the second accuracy being higher than the first accuracy, and the second cost being higher than the first cost;

the one or more processing circuits are further configured to:

obtain environmental data with the plurality of distributed sensors, wherein the plurality of distributed sensors are calibrated to achieve a third accuracy suitable for environmental monitoring, and wherein the third accuracy is higher than the first accuracy; and

calibrate the obtained environmental data by environmental correction through a multivariate regression to calculate regression coefficients for each of a plurality of K30 sensors to obtain five correction coefficients a n and b n , wherein n represents each independent variable, for dry CO 2 from Los Gatos Fast Greenhouse Gas Analyzers (LGRs), pressure P, temperature T, and water vapor mixing ratio q for an equation:

y*={y−b 0 −( a 1 x 1 +b 1 ) . . . −( a n x n +b n )}/ a 0

along with original K30 data, y, and environmental variables to predict true CO 2 concentration observed;

the system further comprising one or more computers to display the true CO 2 concentration observed.

12. The system of claim 11 , further comprising a base station configured to receive data from at least a subset of the plurality of distributed sensors.

13. The system of claim 11 , wherein the one or more processing circuits are further configured to manage the plurality of distributed sensors through at least one of Ethernet, cellular, or Wi-Fi communication channels.

14. The system of claim 11 , wherein:

the second set of sensors are configured for direct measurement and calibrating the first set of sensors; and

at least some of the plurality of distributed sensors are co-located with standard monitoring stations.

Continuity (2)
Provisional Application 62430384 · Dec 6, 2016
Related Publication 20180156766A1 · Jun 7, 2018